DATA REPORT FOR THE

COLLECTION OF EGGS FROM SPOTTED

SANDPIPERS, AMERICAN WOODCOCK, BELTED

KINGFISHER, AMERICAN ROBIN, RED-WINGED

BLACKBIRD, AND EASTERN PHOEBE ASSOCIATED

WITH THE HUDSON RIVER FROM HUDSON FALLS TO

SCHODACK ISLAND, NEW YORK

HUDSON RIVER NATURAL RESOURCE

DAMAGE ASSESSMENT

HUDSON RIVER NATURAL RESOURCE TRUSTEES

STATE OF NEW YORK

U.S. DEPARTMENT OF COMMERCE

U.S. DEPARTMENT OF THE INTERIOR

FINAL

SEPTEMBER 17, 2004

Available from:

U.S. Department of Commerce

National Oceanic and Atmospheric Administration

Hudson River NRDA, Lead Administrative Trustee

Damage Assessment Center, N/ORR31

1305 East-West Highway, Rm 10219

Silver Spring, MD 20910-3281

SEPTEMBER 17, 2004

PREPARED FOR HUDSON RIVER NATURAL RESOURCE TRUSTEES

STATE OF NEW YORK

U.S. DEPARTMENT OF COMMERCE

U.S. DEPARTMENT OF THE INTERIOR

DATA REPORT FOR THE COLLECTION OF

EGGS FROM SPOTTED SANDPIPERS, AMERICAN

WOODCOCK, BELTED KINGFISHER, AMERICAN

ROBIN, RED-WINGED BLACKBIRD, AND EASTERN

PHOEBE ASSOCIATED WITH THE HUDSON RIVER

FROM HUDSON FALLS TO SCHODACK ISLAND,

NEW YORK
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EXECUTIVE SUMMARY

Natural resources of the Hudson River have been contaminated through past and ongoing discharges

of polychlorinated biphenyls (PCBs). As a means of evaluating regional avian contamination, a

screening level survey of avian eggs was conducted from April - June 2002. The investigation entailed

collection of eggs from six primary species: belted kingfisher (Ceryle alcyon), American robin (Turdus

migratorius), Eastern phoebe (Sayornis phoebe), spotted sandpiper (Actitis macularia), red-winged blackbird

(Agelaius phoenicius), and American woodcock (Scolopax minor), along a contamination gradient in the

Upper Hudson River Valley, from Hudson Falls to Lower Schodack Island, New York. Active nests

of these birds in and near the Hudson River and its floodplain were identified and eggs were collected

for PCB analysis. The collection of egg samples from five additional avian species was based solely

on the opportunities for survey team members to locate the nests of these species and consisted of:

Eastern screech owl (Otus asio), common grackle (Quiscalus quiscula), northern rough-winged swallow

(Stelgidopteryx serripennis), barn swallow (Hirundo rustica), and Eastern bluebird (Sialia sialis). A total of

168 egg samples were analyzed for 48 selected PCB congeners, PCB homologue groups, total PCBs,

percent lipids, and percent moisture. Total PCB concentrations ranged from 20 parts per billion (ppb)

to about 56,200 ppb (fresh weight basis) and varied by species and collection location.
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TABLE OF CONTENTS

1.0 INTRODUCTION 1

2.0 SAMPLING 2

2.1 EGG COLLECTION ............................................................................................................ 2

2.2 EGG PROCESSING ............................................................................................................. 3

2.3 EGG ANALYSES................................................................................................................... 3

2.4 QUALITY ASSURANCE/QUALITY CONTROL ........................................................ 3

3.0 RESULTS 5

3.1 TOTAL PCB CONCENTRATIONS ................................................................................. 7

3.2 PCB HOMOLOGUES AND CONGENERS ................................................................. 8

4.0 REFERENCES 11

FIGURES 12

APPENDIX A: WORK PLAN FOR THE COLLECTION OF EGGS FROM SPOTTED SANDPIPERS, AMERICAN WOODCOCK,

BELTED KINGFISHER, AMERICAN ROBIN, RED-WINGED BLACKBIRD AND EASTERN PHOEBE ASSOCIATED

WITH THE HUDSON RIVER FROM HUDSON FALLS TO SCHODACK ISLAND, NEW YORK

APPENDIX B: DATA QUALITY ASSESSMENT REPORT, AVIAN EGG EXPOSURE STUDY

APPENDIX C: AVIAN EGG DATA SHEETS

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1.0 INTRODUCTION

Past and continuing discharges of polychlorinated biphenyls (PCBs) have contaminated the natural

resources of the Hudson River. The Hudson River Natural Resource Trustees - New York State, the

U.S. Department of Commerce, and the U.S. Department of the Interior - are conducting a natural

resource damage assessment (NRDA) to assess and restore those natural resources injured by PCBs

(Hudson River Natural Resource Trustees 2002a). This Data Report provides the results of a

preliminary investigation of PCB contamination of select Hudson River avian species conducted

pursuant to the NRDA.

The Hudson River and surrounding area support more than 150 species of birds, including waterfowl,

wading birds, shorebirds, songbirds, and rare species such as the bald eagle, peregrine falcon, and

osprey (Andrle and Carroll 1988). Birds are an integral part of the ecosystem and provide a number

of important ecosystem services such as seed distribution, plant pollination, and insect control. Birds

are also an important source of prey to other species. Birds may be exposed to PCBs through direct

ingestion of contaminated water, sediment, and soil. A more important exposure pathway is likely

their consumption of food items that contain PCBs derived from the Hudson River and its

floodplain. PCB contaminated food items linked to the river may include fish, amphibians, benthic

invertebrates, adult insects that develop from aquatic larvae, plants growing in or near the river, and

mammals that forage in the floodplain.

From April 2002 through June 2002, the Trustees conducted an avian egg exposure preliminary

investigation for the Hudson River. The investigation entailed collection of eggs from six primary

species: belted kingfisher (Ceryle alcyon), American robin (Turdus migratorius), Eastern phoebe (Sayornis

phoebe), spotted sandpiper (Actitis macularia), red-winged blackbird (Agelaius phoenicius), and American

woodcock (Scolopax minor). Active nests of these birds in and near the Hudson River and its floodplain

were identified and eggs were collected for PCB analysis.

Locating and collecting eggs from the six primary avian species provided an opportunity for collection

of eggs from other avian species, particularly from avian species with habitats in common with the

primary avian species. The collection of egg samples from five additional avian species was based

solely on the opportunities for survey team members to locate the nests of these species. The five

species for which egg samples were opportunistically collected for PCB analysis are Eastern screech

owl (Otus asio), common grackle (Quiscalus quiscula), northern rough-winged swallow (Stelgidopteryx

serripennis), barn swallow (Hirundo rustica), and Eastern bluebird (Sialia sialis).

This preliminary investigation was undertaken to assist the Trustees in determining the extent to

which avian species in the Hudson River are currently contaminated with PCBs, and to determine if

additional pathway and injury assessment studies focused on avian species should be conducted as

part of the Hudson River NRDA. This work will potentially be used to design future studies to assess

the health of these animals in the Hudson River.

As noted in the Work Plan for this preliminary investigation (Hudson River Natural Resource Trustees,

2002b), the six primary avian species in this investigation together provide a balanced approach in that

these species use different types of habitats common to the Hudson River, they consume different

types of foods and they generally represent different ecological guilds. Further, all six of these avian

species are reported to be relatively common breeders in the Hudson River floodplain (Andrle and

Carroll 1988) and use wetlands for some portion of their life cycle (DeGraaf and Yamasaki 2000).

Finally, many of the prey species consumed by these six avian species include those for which PCB

accumulation has been documented in other areas, and for which PCB accumulation in prey items

from the Hudson River is likely to exist.
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2.0 SAMPLING

Collection and processing of avian eggs were conducted in accordance with the Trustees' Work Plan

for the Collection of Eggs from Spotted Sandpipers, American Woodcock, Belted Kingfisher,

American Robin, Red-Winged Blackbird, and Eastern Phoebe Associated With the Hudson River from

Hudson Falls to Schodack Island, New York (Appendix A), including the Protocol for Avian Egg

Collection and Removal of Contents for Contaminants Analysis (Hudson River Natural Resource

Trustees, 2002b). Chemical analyses were conducted pursuant to the Trustees' Analytical Quality

Assurance Plan (Hudson River Natural Resource Trustees, 2002c).

This preliminary investigation focused on four areas of the Hudson River between Bakers Falls on

the Hudson River (in Hudson Falls, New York) and Schodack Island, New York. Avian eggs were

collected from these four geographic areas to provide samples from various portions of the river which

are known to be contaminated with PCBs at various levels. These four areas are described as follows,

and are shown on Figure 1.

Region 1: the area from Bakers Falls (at River Mile (RM) 196.9) downstream to the Fort

Miller Dam (Lock 6) at RM 186.2 (Champlain Canal); this includes the Thompson Island

Pool.

Region 2: the area from the Fort Miller Dam (Lock 6) at RM 186.2 downstream to the

Stillwater Dam (Lock 4) at RM 168.2; this includes the Stillwater Pool.

Region 3: the area below the Stillwater Dam (Lock 4) at RM 168.2 downstream to the

Federal Dam at Troy (RM 153.9), excluding Troy and its urban vicinity (approximately from

Peebles Island State Park downstream to the Federal Dam).

Region 4: the area below the Federal Dam at Troy (RM 153.9) extending south to Lower

Schodack Island (RM 132), excluding Albany and its urban vicinity.

Note that these Regions are slightly modified from those specified in the Trustees' Work Plan for this

avian egg investigation (Hudson River Natural Resource Trustees, 2002b). The avian egg exposure

investigation Regions were realigned to be consistent with the segmentation used in other work being

conducted by the Trustees.

2.1 EGG COLLECTION

Before egg collection began, the appropriate State and Federal permits were obtained. Field work

began in April 2002. At each nest suspected of being active, a survey team member checked the nest

(using a peeper probe or mirror and extension pole to peer inside the nest, when necessary) to

determine the status of the nest. After determining that eggs were available for collection, a survey

team member reached into the nest and collected an egg. Scientists wore nitrile gloves to reduce

exposure to any parasites and diseases that may have been present in the nest or on an egg. Egg

collection was documented using the Avian Egg Data Sheet specified in the Trustees' Work Plan for

this investigation.

For four of the smaller avian species in this investigation -- Eastern phoebe, Eastern bluebird, barn

swallow, and northern rough-winged swallow - it was necessary to collect two eggs from each nest to

provide the desired total sample mass (minimum of 2 grams) for analysis. One egg sample (containing

either one or two eggs depending on the species and size of the eggs) was thus collected from each

nest of the six primary avian species identified and from each nest of the five opportunistically

sampled avian species identified.
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In one instance, two eggs (BK-506-507 and BK-506-508) were collected from a single belted

kingfisher nest in Region 2. These eggs were processed and analyzed individually. In that instance,

two eggs were inadvertently extracted from the nest burrow, and both were saved and subsequently

processed and analyzed individually, as it was not possible to return one of the eggs to the nest

without potentially endangering the remaining eggs.

The collected egg(s) were marked with the sample collection nest identification (ID) number using a

graphite pencil and wrapped in a protective manner with aluminum foil that was also labeled with the

nest number. Wrapped eggs were securely placed in an egg container then into a cooler or secure box

with ice and transported to a New York State Department of Environmental Conservation

(NYSDEC) facility for processing.

The first avian egg for this investigation was collected on April 16, 2002, and the final egg for this

investigation was collected on June 20, 2002.

2.2 EGG PROCESSING

Once in the processing facility, i.e. laboratory building, each egg was measured, processed and stored

according to the Work Plan and the Protocol for Avian Egg Collection and Removal of Contents for

Contaminants Analysis (Hudson River Natural Resource Trustees, 2002b).

The majority of the eggs were processed within 24 hours and the remaining eggs were stored at

approximately 40 degrees Fahrenheit and processed within 48 hours. All eggs were processed at a

laboratory maintained by the NYSDEC.

Upon processing, egg contents were stored at -20 Celsius in a freezer at the processing facility. The

samples were transported in a cooler with ice to the NYSDEC Hale Creek laboratory, where they were

again stored at -20 Celsius until they were shipped to the program analytical laboratory for chemical

analysis.

Log forms were created for each egg collected documenting the specifics of the collection and

processing. Chain of custody forms were prepared with the appropriate signatures as the samples were

transferred from the field crew to NYSDEC staff.

2.3 EGG ANALYSES

A total of 220 eggs were submitted for analysis. Due to the small size of some of the eggs,

compositing of two eggs to form a single sample was necessary for several species (Eastern phoebe,

Eastern bluebird, barn swallow, and northern rough-winged swallow), as noted earlier. The total

number of egg samples (either one egg or a composite of two eggs, as noted) analyzed was 168.

The egg samples were grouped into 12 analytical batches by the laboratory. The eggs were analyzed

for 48 PCB congeners (Table 3 of this report contains a list of the congeners), PCB homologue

groups, total PCBs, percent lipids, and percent moisture. The egg tissue was prepped, extracted, and

analyzed using laboratory Standard Operating Procedures (SOPs) approved by the Trustees prior to

sample receipt.

Sample analysis began on August 26, 2002, and concluded on November 15, 2002.

2.4 QUALITY ASSURANCE/QUALITY CONTROL

Data validation was conducted by the Trustees and was based on the quality assurance/quality control

(QA/QC) criteria documented in the Trustees' Analytical Quality Assurance Plan for the Hudson

River Natural Resource Damage Assessment (Hudson River Natural Resource Trustees, 2002c),

USEPA (1999), and the following laboratory SOPs:
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• SOP # HR NRDA Project Tissue Prep: Tissue Preparation and Homogenization,

Revision #1.0, 9/25/02

• SOP # OP-004: Extraction of Soil, Tissue, Vegetation, and Sediment by

Pressurized Fluid Extraction, Revision #2.0, 8/15/02

• SOP # O-010: Determination of PCB Homologues and Individual Congeners by

GC/MS - SIM, Revision # 2.2, 10/24/02

• SOP # HR NRDA % Lipids: Percent Lipids Determination, Revision # 0.0, 9/9/02

• SOP # W-001: Percent Solids Determination, Revision # 2.1, 9/25/02

• Additional cleanup, sample handling, storage, custody SOPs as necessary.

The data packages submitted by the laboratory were reviewed to determine whether the analytical data

quality objectives (ADQO) specified in the Analytical Quality Assurance Plan (Hudson River Natural

Resource Trustees, 2002c) were met.

Table 1.1 of the Trustees' Analytical Quality Assurance Plan (Hudson River Natural Resource Trustees,

2002c) specifies the target Method Detection Limits (MDLs) for PCB congeners, homologues and

total PCBs. For tissue, such as avian egg samples, the target MDLs are 0.1 ng/g wet weight (equivalent

to 0.1 ppb wet weight) for individual congeners, and 10 ng/g (equivalent to 10 ppb) for PCB

homologues and total PCBs. Actual MDLs for each PCB analyte were established by the analytical

laboratory as specified in the Analytical Quality Assurance Plan. Actual MDLs are reported on the

Avian Egg Data Sheets (Appendix C) in the "Detection Limit" column.

Appendix B contains the Data Quality Assessment Report (Hudson River Natural Resource Trustees,

2003) for the avian egg exposure study. Table 1A to that appendix is a summary of standard

reference material (SRM) analytical results for each sample delivery group (SDG) that was analyzed.

A statistical evaluation of the SRM analytical results is found in Table 1B of that appendix. Table 2

of that appendix summarizes the relative percent difference in duplicates from the analyses.

Out of 10,248 individual analytical results reported by the laboratory (168 egg samples, each with 48

congeners, ten homologue groups, total PCBs, percent lipids and percent moisture), a total of 1,016

(9.91%) data points were qualified as estimated (J/UJ) because of laboratory accuracy and precision

outliers, continuing calibration percent difference outliers, and internal standard area outliers, and 110

data points were tentatively identified (NJ) due to potential interferences (see Appendix B) (Hudson

River Natural Resource Trustees, 2003). One data point was rejected based on an accuracy outlier

and is thus not included in this report. For all other data, the overall quality of the data is acceptable

and all results, as qualified, are considered usable (Hudson River Natural Resource Trustees, 2003).

The completeness level attained for the analysis of the field samples is greater than 99.9%.

A quality control table was developed. That table includes Nest ID Number, Laboratory ID,

Analytical Batch Number, Analyte, Value, Interpretive Qualifier, Value Units, Detection Limit, Analysis

Group, Basis, Extraction Date, Analysis Date, Dilution Factor, Sample Size, Sample Size Unit, and

Quality Control Types for all samples, duplicates, SRMs and rinse blanks. Due to the size of this

table, it has not been included in this report, but will be made available upon request. The quality

control table is part of the Trustees' Avian Egg Database (Hudson River Natural Resource Trustees,

2004a).
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3.0 RESUL 3.0 RESULTS

The Avian Egg Data Sheets (Appendix C) provide the results of the analyses. These Data Sheets

contain information that has been extracted from the Trustees' Avian Egg Database (Hudson River

Natural Resource Trustees, 2004a). That complete database and the accompanying Database User

Manual (Hudson River Natural Resource Trustees, 2004b) are not included in this report due to the

size of the database, but will be made available upon request.

The Avian Egg Data sheets contain the following fields:

Sampling Date - Sampling Date (mm/dd/yy format)

Field ID - The field IDs were created using the following format:

CC-NNN-EEE

where CC is the code for the common name (e.g., AR is American Robin), NNN is the nest number,

and EEE is the egg ID number. For example, AR-007-101 indicates egg ID number 101 in nest

number 007, associated with an American Robin.

Due to limited sample size, some of the eggs were composited prior to analysis. For composite egg

samples, the following field ID format was used:

CC-NNN COMP XXX/YYY

where CC is the code for the common name (e.g., EP is Eastern phoebe), NNN is the nest number,

and XXX/YYY represents the egg' ID numbers included in the composite. For example, a composite

of Eastern Phoebe eggs from nest 232 would be: EP-232 COMP 236/237.

Decimal latitude readings as reported by the GPS system.

Easting - NAD83 Universal Transverse Mercator easting coordinates (meters) Zone 18N.

Northing - NAD83 Universal Transverse Mercator northing coordinates (meters) Zone 18N.

Region - Region as delineated in section 2 of this report.

Lab ID - Laboratory IDs were created using the following format:

Sample delivery group - run sequence number (e.g., 0208031-01)

Analyte - self-explanatory.

Value, Interpretive Qualifier -

Value - Analytical result (3 significant figures).

Interpretive Qualifier - This field contains qualifiers applied to each data point after the data

validation process. Data validation qualifiers were assigned to data points when associated QC

sample results indicated the data did not meet the data quality objectives. The following

definitions provide brief explanations of the qualifiers applied to the Hudson River NRDA

data. Reasons for qualifications are explained further in the Data Quality Assessment Report

(Appendix B).

U Not detected. The analyte was not detected. The associated value represents the

detection limit.

J Estimated: The associated numerical value is an estimated quantity. The analyte was

detected, but the reported value may not be accurate or precise. The "J" qualification

indicates the data fell outside the QC limits, but the exceedance was not sufficient to

cause rejection of the data.
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UJ Estimated/Not detected: An analysis was performed for the compound or analyte, but

it was not detected and the sample quantitation or detection limit may be inaccurate or

imprecise. The associated numerical result is the detection limit.

NJ The analyte was tentatively identified and the associated numerical value is an estimated

quantity.

R Rejected: Unreliable result. Data should not be used. The values associated with R

qualifiers have been removed from the database.

The unit of measurement of the analytical result is provided (for example, μg/kg).

Detection Limit - self-explanatory; this column includes units.

Fresh Weight - results (analyte value in earlier column) corrected for moisture loss, as discussed below.

A brief description of some of the features of these data follows in sections 3.1 and 3.2 of this Data

Report. Please note that the unit "μg/kg" used in the Data Sheets is equivalent to parts per billion

(ppb) used in the discussion of these data in this Data Report.

Data fields, and data collected by the Trustees, that are not reported in this Data Report but that are

contained within the Trustees' Avian Egg Database consist of the following: Nest ID Number, Study

Name, Laboratory ID, Analytical Batch Number, Laboratory Flag, Data Validation Qualifier, Data

Validation Qualifier Reason Code, Analysis Group, Analytical Method, Extraction Date, Analysis Date,

Dilution Factor, Sample Size and Units, Biota Type, Egg Contents Weight, Whole Egg Weight, Egg

Volume, Eggshell Thickness, Nonconformance Notes, Eastings, Northings, and Region Name.

All PCB results reported below and in the figures attached to this report have been corrected for

moisture loss. This is an adjustment to compensate for the loss of moisture in avian eggs (Stickel et

al. 1973). Valid interpretation of contaminant residue data for avian eggs depends upon adjustment

for moisture loss.

To correct for moisture loss, per the method of Stickel et al. (1973), a correction factor is determined

as follows:

Correction factor (CF) = Egg contents weight (g)

 Egg volume (cm3)

The contaminant value adjusted for moisture loss is then derived by multiplying the laboratory

determined contaminant concentration by the correction factor.

For example:

CF = Egg contents weight = 6.32 grams = 0.9475

 Egg volume 6.67 cm3

CF x PCB concentration = corrected PCB concentration

0.9475 x 1,820 ppb PCBs = 1,724 ppb PCBs

In this example, the PCB value corrected for moisture loss is 1,724 ppb.

When it was not possible to determine a CF for a specific sample (because of the lack of information

on egg contents weight and/or egg volume), an average CF was determined based on CFs determined

for eggs of the same species from the same Region, and that average CF was applied to that sample as

its CF.
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For composited samples (Eastern phoebe, Eastern bluebird, barn swallow, and northern rough-winged

swallow), egg volume and egg contents weight were determined by averaging the respective sample

characteristics; those averages were used in deriving the correction factor.

Where it was impossible to determine average egg volume or contents weight for a composited

sample (e.g., RS-640 COMP 660_661), the measured egg volume and contents weight of one of the

eggs in that composite (e.g., RS-640-660) was used to calculate the CF for the composite sample.

All calculated CFs were used, and all samples were included in calculating species and Regional

average PCB concentrations. For "J" qualified results (J/UJ/NJ), the estimated value was used in the

calculations.

For the purpose of reporting PCB results below and in the figures attached to this report, all values

flagged with either a U or UJ interpretive qualifier (that is, not detected; see Appendix B) were

considered to be zero. Using zero, rather than the value reported by the laboratory for the analyte,

which represents the detection limit for the analysis, potentially underreports the true value, but

avoids overreporting the true value. This is thus a conservative result; the actual PCB concentration

could be higher.

3.1 TOTAL PCB CONCENTRATIONS

Total PCB concentrations of avian egg samples, by species, are detailed in Table 1. Total PCB

concentrations of avian egg samples, by Region, are detailed in Table 2. Values in Tables 1 and 2

are reported to three significant figures.

Table 1. Summary of Total PCBs (as sum of homologues) in Hudson River Avian Eggs, by

Species.

Species Number of Samples Concentration

Range (ppb)

Concentration

Average ±1 SD

(ppb)

American robin

American woodcock

Common grackle

Belted kingfisherA

Eastern bluebird

Eastern phoebe

40

10

2

10

5

27

20 - 11,200

91 - 101

2,030 - 42,700

702 - 16,400

196 - 1,140

144 - 17,300

1,120 ± 2,170

96 ± 7

13,900 ± 12,500

4,360 ± 4,880

520 ± 385

2,040 ± 3,350

Barn swallow

Spotted sandpiper

Red winged blackbird

Norhtern rough winged swallow

Screeech owl

13 488 - 56,200 15,200 ± 17,700

1 8,010 -

10 2,140 - 13,900 7,240 ± 4,170

40 65 - 35,000 3,670 ± 6,870

10 663 - 5,140 2,990 ± 1,730

AIncludes two eggs (BK-506-507 and BK-506-508) collected from a single belted kindfisher nest in Region 2 (See

 Section 2.1). Individual results for these two eggs are reported in Appendix C.
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Table 2. Summary of Total PCBs (as sum of homologues) in Hudson River Avian Eggs, by

Region.

Region Number of Samples

Concentration

Range (ppb)

Concentration

Average ±1 SD

(ppb)

Region 1 51 65 - 56,200 7,620 ± 11,300

Figures 2 through 12 graphically represent the ranges and averages of avian egg total PCBs for each

species by Region. Figures 13 through 16 graphically represent avian egg total PCB concentrations by

species by Region.

Please note that on these figures the vertical axis (PCB concentration (μg/kg)) is a logarithmic scale. On

a logarithmic scale, steps increase in a multiplicative fashion, not in an additive fashion as on a linear

scale. The increase of one unit on a logarithmic scale represents a tenfold increase in the value. For

instance, the first value on the scale is 101 which is equivalent to 10 μg/kg or 10 ppb; the next value on

the scale is 102, which is equivalent to 100 μg/kg or 100 ppb (note that the unit "μg/kg" used on the

figures is equivalent to ppb used in the discussion of these data in this Data Report).

For some avian species, such as American robin, barn swallow, and northern rough winged swallow, total

average PCB concentrations in eggs display a decreasing concentration gradient moving downstream

from Region 1 (Figures 2, 8 and 10).

For other avian species, such as common grackle, Eastern phoebe, red winged blackbird and spotted

sandpiper, total average PCB concentrations in eggs do not display a consistently decreasing

concentration gradient moving downstream from Region 1 (Figures 5, 7, 9 and 12). For common

grackle and red winged blackbird, the average PCB concentration in eggs from Region 3 is greater than

that for eggs from Region 1.

3.2 PCB HOMOLOGUES AND CONGENERS

PCBs are synthetic (man-made) chemicals that form a group of 209 individual compounds that have

similar chemical structures based on a biphenyl core with 1 to 10 chlorine atoms attached. PCBs have

the generic formula C12H(10-x)Clx, where x is an integer from 1 to 10.

Each individual PCB compound, called a congener, is identified by the unique number and location of

chlorine atoms that attach to the compound's base structure. Congeners differ both in their physical

properties and in their effects on fish and wildlife (Safe 1994; Van den Berg et al. 1998).

For this investigation, the avian eggs were analyzed for 48 specific target PCB congeners listed in Table

3. In addition, a total concentration for each homologue group was determined by summing all target

and non-target congener concentrations within each homologue group. For any congener reported as

non-detected, zero was used in the summation.

Region 2A 48 44 - 15,100 3,320 ± 3,870

Region 3 39 20 - 42,700 4,450 ± 8,860

Region 4 30 36 - 2,990 607 ± 718

AIncludes two eggs (BK-506-507 and BK-506-508) collected from a single belted kindfisher nest in Region 2 (See

 Section 2.1). Individual results for these two eggs are reported in Appendix C.
HUDSON RIVER

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9

8 2,4'-Dichlorobiphenyl

18 2,2',5-Trichlorobiphenyl

28 2,4,4'-Trichlorobiphenyl

31 2,4',5-Trichlorobiphenyl

44 2,2',3,5'-Tetrachlorobiphenyl

45 2,2',3,6-Tetrachlorobiphenyl

47 2,2',4,4'-Tetrachlorobiphenyl

49 2,2',4,5'-Tetrachlorobiphenyl

52 2,2',5,5'-Tetrachlorobiphenyl

56 2,3,3',4'-Tetrachlorobiphenyl

66 2,3',4,4'-Tetrachlorobiphenyl

70 2,3',4',5-Tetrachlorobiphenyl

74 2,4,4',5-Tetrachlorobiphenyl

77 3,3',4,4'-Tetrachlorobiphenyl

81 3,4,4',5-Tetrachlorobiphenyl

87 2,2',3,4,5'-Pentachlorobiphenyl

95 2,2',3,5',6-Pentachlorobiphenyl

99 2,2',4,4',5-Pentachlorobiphenyl

101 2,2',4,5,5'-Pentachlorobiphenyl

105 2,3,3',4,4'-Pentachlorobiphenyl

110 2,3,3',4',6-Pentachlorobiphenyl

114 2,3,4,4',5-Pentachlorobiphenyl

118 2,3',4,4',5-Pentachlorobiphenyl

123 2,3',4,4',5'-Pentachlorobiphenyl

126 3,3',4,4',5-Pentachlorobiphenyl

128 2,2',3,3',4,4'-Hexachlorobiphenyl

138 2,2',3,4,4',5'-Hexachlorobiphenyl

146 2,2',3,4',5,5'-Hexachlorobiphenyl

149 2,2',3,4',5',6-Hexachlorobiphenyl

151 2,2',3,5,5',6-Hexachlorobiphenyl

153 2,2',4,4',5,5'-Hexachlorobiphenyl

156 2,3,3',4,4',5-Hexachlorobiphenyl

IUPAC Name

Current Ballschmiter and Zell

(1994) and International Union

of Pure and Applied Chemistry

(IUPAC) Number

Table 3. PCB Congeners for which Avian Eggs were Analyzed.
HUDSON RIVER

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Table 3. PCB Congeners for which Avian Eggs were Analyzed (continued).

IUPAC Name

157 2,3,3',4,4',5'-Hexachlorobiphenyl

158 2,3,3',4,4',6-Hexachlorobiphenyl

167 2,3',4,4',5,5'-Hexachlorobiphenyl

169 3,3',4,4',5,5'-Hexachlorobiphenyl

170 2,2',3,3',4,4',5-Heptachlorobiphenyl

174 2,2',3,3',4,5,6'-Heptachlorobiphenyl

177 2,2',3,3',4,5',6'-Heptachlorobiphenyl

180 2,2',3,4,4',5,5'-Heptachlorobiphenyl

183 2,2',3,4,4',5',6-Heptachlorobiphenyl

187 2,2',3,4',5,5',6-Heptachlorobiphenyl

189 2,3,3',4,4',5,5'-Heptachlorobiphenyl

194 2,2',3,3',4,4',5,5'-Octachlorobiphenyl

195 2,2',3,3',4,4',5,6-Octachlorobiphenyl

201 2,2',3,3',4,5',6,6'-Octachlorobiphenyl

206 2,2',3,3',4,4',5,5',6-Nonachlorobiphenyl

209 Decachlorobiphenyl

Current Ballschmiter and Zell

(1994) and International Union

of Pure and Applied Chemistry

(IUPAC) Number

Figures 17 through 27 display the PCB homologue distributions for each sampled species by its

respective Region of collection.
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 11

4.0 REFERENCES

Andrle, R.F. and J.R. Carroll. 1988. The Atlas of Breeding Birds in New York State, Federation

of New York State Birds Club. IV. ISBN 0-8014-1691-4. New York State Department of

Environmental Conservation. Cornell University, Laboratory of Ornithology. Cornell

University, NY.

Ballschmiter, K. and M. Zell. 1994. Analysis of polychlorinated biphenyls (PCBs) by glass

capillary gas chromatography. Fresenius' Journal of Analytical Chemistry 302: 20-31.

DeGraaf, R.M. and M. Yamasaki. 2001. New England Wildlife: Habitat, Natural History, and

Distribution. Univ. Press of New England. Hanover, NH. 482pp.

Hudson River Natural Resource Trustees. 2002a. Hudson River Natural Resource Damage

Assessment Plan. September 2002. U.S. Department of Commerce, Silver Spring, MD.

Hudson River Natural Resource Trustees. 2002b. Work Plan for the Collection of Eggs from

Spotted Sandpipers, American Woodcock, Belted Kingfisher, American Robin, RedWinged Blackbird, and Eastern Phoebe Associated With the Hudson River from Hudson

Falls to Schodack Island, New York. March 2002. U.S. Department of Commerce, Silver

Spring, MD.

Hudson River Natural Resource Trustees. 2002c. Analytical Quality Assurance Plan for the

Hudson River Natural Resource Damage Assessment. Public Release Version. July 9,

2002, Version 1.0. U.S. Department of Commerce, Silver Spring, MD.

Hudson River Natural Resource Trustees. 2003. Data Quality Assessment Report. Avian Egg

Exposure Study. August 20, 2003. Version 2.0. U.S. Department of Commerce, Silver

Spring, MD.

Hudson River Natural Resource Trustees. 2004a. Avian Egg Database. Version 3.0. U.S.

Department of Commerce, Silver Spring, MD.

Hudson River Natural Resource Trustees. 2004b. Database User Manual. Avian Egg Study.

October 21, 2003. Version 3.0. U.S. Department of Commerce, Silver Spring, MD.

Safe, S.H. 1994. Polychlorinated biphenyls (PCBs): environmental impact, biochemical and toxic

responses, and implications for risk assessment. Critical Reviews in Toxicology 24: 87-149.

Stickel, L.F., S.N. Wiemeyer, and L.J. Blus. 1973. Pesticide residues in eggs of wild birds:

adjustment for loss of moisture and lipid. Bull. Environ. Contam. Toxicol. 9:193-196.

USEPA, 1999. USEPA Contract Laboratory Program National Functional Guidelines for

Organic Data Review. Office of Emergency and Remedial Response, Washington, D.C.

20460. EPA540/R-99/008, 118 pp.

Van den Berg, M., Birnbaum, L., Bosveld, A.T.C., Brunstrom, b., Cook, P., Feeley, M., Giesy, J.P.,

Hanberg, A., Hasegawa, R., Kennedy, S.W., Kubiak, T., Larsen, J.C., van Leeuwen, F.X.R.,

Liem, A.K.D., Nolt, C., Peterson, R.E., Poellinger, L., Safe, S., Schrenk, D., Tillitt, D.,

Tysklind, M., Younes, M., Waern, F. and Zacharewski, T. 1998. Toxic equivalency factors

(TEFs) for PCBs, PCDDs, PCDFs for humans and wildlife. Environmental Health

Perspectives 106: 775-792.
HUDSON RIVER

HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 12

Figure 1. Location of avian egg collection sites depicted with triangles. Lines across the river

represent dams or locks on the Hudson River. Stars represent select cities and towns.

FIGURES
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 13

Figure 2. American robin egg total PCB concentrations by region. The small dots represent

individual samples, the large dots are regional averages.

Figure 3. American woodcock egg total PCB concentrations by region.
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HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 14

Figure 4. Belted kingfisher egg total PCB concentrations by region. The small dots represent

individual samples, the large dots are regional averages.

Figure 5. Common grackle egg total PCB concentrations by region. The small dots represent

individual samples, the large dots are regional averages.
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 15

Figure 6. Eastern bluebird egg total PCB concentrations by region. The small dots represent

individual samples, the large dots are regional averages.

Figure 7. Eastern phoebe egg total PCB concentrations by region. The small dots represent

individual samples, the large dots are regional averages.
HUDSON RIVER

HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 16

Figure 8. Barn sallow egg total PCB concentrations by region. The small dots represent

individual samples, the large dots are regional averages.

Figure 9. Red winged blackbird egg total PCB concentrations by region. The small dots

represent individual samples, the large dots are regional averages.
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 17

Figure 10. Rough winged swallow egg total PCB concentrations by region. The small dots

represent individual samples, the large dots are regional averages.

Figure 11. Screech owl egg total PCB concentrations by region.
HUDSON RIVER

HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 18

Figure 12. Spotted sandpiper egg total PCB concentrations by region. The small dots

represent individual samples, the large dots are species averages.

Figure 13. Region 1 avian egg total PCB concentrations by species. The small dots represent

individual samples, the large dots are species averages.
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 19

Figure 14. Region 2 avian egg total PCB concentrations by species. Small dots represent

individual samples, the large dots are species averages.

Figure 15. Region 3 avian egg total PCB concentrations by species. Small dots represent

individual samples, the large dots are species averages.
HUDSON RIVER

HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 20

Figure 16. Region 4 avian egg total PCB concentrations by species. Small dots represent

individual samples, the large dots are species averages.
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 21

Figure 17. American robin egg PCB homologue distributions by region (+/- 1 SD).
HUDSON RIVER

HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 22

Figure 18. American woodcock egg PCB homologue by region.
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 23

Figure 19. Belted kingfisher egg PCB homologue distributions by region (+/- 1 SD).
HUDSON RIVER

HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 24

Figure 20. Common grackle egg homologue distributions by region (+/- 1 SD).
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 25

Figure 21. Eastern bluebird egg PCB homologue distributions by region (+/- 1 SD).
HUDSON RIVER

HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 26

Figure 22. Eastern phoebe egg PCB homologue distributions by region (+/- 1 SD).
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 27

Figure 23. Barn swallow egg PCB homologue distributions by region (+/- 1 SD).
HUDSON RIVER

HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 28

Figure 24. Red winged blackbird egg PCB homologue distributions by region (+/- 1 SD).
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 29

Figure 25. Rough winged swallow egg PCB homologue distributions by region (+/- 1 SD).
HUDSON RIVER

HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 30

Figure 26. Screech owl egg PCB homologue distributions by region.
HUDSON RIVER HUDSON RIVER DATA REPORT: PCB

S IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 31

Figure 27. Spotted sandpiper egg PCB homologue distributions by region (+/- 1 SD).
HUDSON RIVER

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS

HUDSON RIVER DATA REPORT: PCBS IN AVIAN EGGS 32
APPENDIX A

WORK PLAN FOR THE COLLECTION OF EGGS FROM

SPOTTED SANDPIPERS, AMERICAN WOODCOCK, BELTED

KINGFISHER, AMERICAN ROBIN, RED-WINGED

BLACKBIRD AND EASTERN PHOEBE ASSOCIATED WITH

THE HUDSON RIVER FROM HUDSON FALLS TO SCHODACK

ISLAND, NEW YORK

WORK PLAN FOR THE COLLECTION OF EGGS FROM

SPOTTED SANDPIPERS, AMERICAN WOODCOCK,

BELTED KINGFISHER, AMERICAN ROBIN, REDWINGED BLACKBIRD AND EASTERN PHOEBE

ASSOCIATED WITH THE HUDSON RIVER FROM

HUDSON FALLS TO SCHODACK ISLAND, NEW YORK

HUDSON RIVER NATURAL RESOURCE

DAMAGE ASSESSMENT

HUDSON RIVER NATURAL RESOURCE TRUSTEES

STATE OF NEW YORK

U.S. DEPARTMENT OF COMMERCE

U.S. DEPARTMENT OF THE INTERIOR

FINAL

PUBLIC RELEASE VERSION*

MARCH 2002

Available from:

U.S. Department of Commerce

National Oceanic and Atmospheric Administration

Hudson River NRDA, Lead Administrative Trustee

Damage Assessment Center, N/ORR31

1305 East-West Highway, Rm 10219

Silver Spring, MD 20910-3281

*Names of certain individuals and affiliations have been removed to maintain confidentiality

ERRATA

to

Work Plan for the Collection of Eggs from Spotted Sandpipers, American Woodcock, Belted

Kingfisher, American Robin, Red-Winged Blackbird, and Eastern Phoebe Associated With the

Hudson River from Hudson Falls to Schodack Island, New York

In Section 1.0, Introduction, S E A Consultants, Inc. (2001) should be cited as S E A Consultants

(2002):

S E A Consultants, Inc. 2002. Hudson River Natural Resources Damage Assessment,

Floodplain Soil and Biota Screening Sampling Report. S E A Consultants, Inc.,

Cambridge, Mass. Report Prepared for Industrial Economics, Inc. S E A Project No.

2000416.01-A.

In section 1.2.1.1, Drouillard and Norstrom 2001a should be Drouillard and Norstrom 2000 and

the citation for the reference in section 7.0, Literature Cited, should be as follows:

Drouillard, K.G. and R. Norstrom. 2000. Dietary absorption efficiencies and

toxicokinetics of polychlorinated biphenyls in ring doves following exposure to Aroclor

mixtures. Environ. Toxicol. & Chem. 19(11):2707-2714.

In section 1.2.1.1, Drouillard and Norstrom 2001b should be Drouillard and Norstrom 2001 and

the citation for the reference in Section 7.0, Literature Cited, should be as follows:

Drouillard, K.G. and R. Norstrom. 2001. Quantifying maternal and dietary sources of

2,2',4,4',5,5'-hexachlorobiphenyl deposited in eggs of the ring dove (Streptopelia risoria).

Environ. Toxicol. & Chem. 20:561-567.

In section 1.2.1.1, “Peakell and Peakell 1973” should be “Peakall and Peakall 1973” and the

citation for the reference in section 7.0, Literature Cited, should be as follows:

Peakall, D.B. and M.L. Peakall. 1973. Effects of polychlorinated biphenyl on the

reproduction of artificially and naturally incubated dove eggs. Journal of Applied

Ecology 10:863-868.

Also in section 7.0 the citation for Arena et al. 1999 should be as follows:

Arena, S. M., R.S. Halbrook, and C.A. Arenal. 1999. Predicting starling chick carcass

PCB concentrations from PCB concentrations in ingested animal matter. Archives of

Environ. Contamination and Toxicol. 37:548-553.

Appendix 3, Egg Collection Standard Operating Procedure, notes that, “the data sheet (Appendix

B) has adjustments for bald eagles.” The formula for calculating the volume of a bald eagle egg

based on length and width measurements was not included on the data sheet. The volume of

each egg was determined by water displacement, per Appendix 3.

Footnote 2 on the Avian Egg Data Sheet should refer to the calculated maximum egg volume in

the Conversion Factor equation.

Footnote 3 on the Avian Egg Data Sheet should read, “If you have both, use the larger.”
WORK PLAN FOR THE COLLECTION OF EGGS FROM

SPOTTED SANDPIPERS, AMERICAN WOODCOCK, BELTED KINGFISHER,

AMERICAN ROBIN, RED-WINGED BLACKBIRD, AND EASTERN PHEOBE

ASSOCIATED WITH THE HUDSON RIVER FROM

HUDSON FALLS TO SCHODACK ISLAND, NEW YORK

____________________________________ ___________________________________

Field Survey Lead Principal Scientist

___________________________________

Quality Assurance Coordinator
i March 2002

SURVEY TEAM ACKNOWLEDGEMENT OF WORK PLAN REVIEW

Name (printed): ______________________ Name (printed): ________________________

Signature: ___________________________ Signature: _____________________________

Date: _______________________________ Date: _________________________________

Title: _______________________________ Title: _________________________________

Name (printed): ______________________ Name (printed): ________________________

Signature: ___________________________ Signature: _____________________________

Date: _______________________________ Date: _________________________________

Title: _______________________________ Title: _________________________________

Name (printed): ______________________ Name (printed): ________________________

Signature: ___________________________ Signature: _____________________________

Date: _______________________________ Date: _________________________________

Title: _______________________________ Title: _________________________________

Name (printed): ______________________ Name (printed): ________________________

Signature: ___________________________ Signature: _____________________________

Date: _______________________________ Date: _________________________________

Title: _______________________________ Title: _________________________________

Name (printed): ______________________ Name (printed): ________________________

Signature: ___________________________ Signature: _____________________________

Date: _______________________________ Date: _________________________________

Title: _______________________________ Title: _________________________________
ii March 2002

Name (printed): ______________________ Name (printed): ________________________

Signature: ___________________________ Signature: _____________________________

Date: _______________________________ Date: _________________________________

Title: _______________________________ Title: _________________________________

Name (printed): ______________________ Name (printed): ________________________

Signature: ___________________________ Signature: _____________________________

Date: _______________________________ Date: _________________________________

Title: _______________________________ Title: _________________________________

Name (printed): ______________________ Name (printed): ________________________

Signature: ___________________________ Signature: _____________________________

Date: _______________________________ Date: _________________________________

Title: _______________________________ Title: _________________________________

Name (printed): ______________________ Name (printed): ________________________

Signature: ___________________________ Signature: _____________________________

Date: _______________________________ Date: _________________________________

Title: _______________________________ Title: _________________________________

Name (printed): ______________________ Name (printed): ________________________

Signature: ___________________________ Signature: _____________________________

Date: _______________________________ Date: _________________________________

Title: _______________________________ Title: _________________________________
iii March 2002

Table of Contents

1.0 INTRODUCTION .............................................................................................................. 1

1.1 Objectives ............................................................................................................... 1

1.2 Project Approach .................................................................................................... 1

1.2.1 Species Selection and Rationale ................................................................. 2

1.2.2 Survey Overview ........................................................................................ 4

2.0 METHODS ......................................................................................................................... 4

2.1 Literature Search..................................................................................................... 4

2.2 Habitat Identification .............................................................................................. 5

2.3 Landowner Contacts............................................................................................... 7

2.4 Breeding Bird Surveys and Locating Nests............................................................ 7

2.4.1 Overview..................................................................................................... 7

2.4.2 Spotted Sandpiper....................................................................................... 7

2.4.3 American Woodcock .................................................................................. 8

2.4.4 Belted Kingfisher........................................................................................ 9

2.4.5 American Robins, Eastern Phoebes, and Red-Winged Blackbirds............. 9

2.4.6 Opportunistic Collection........................................................................... 10

2.4.7 Data Location and Management ............................................................... 11

2.5 Study Species Egg Collection and Analysis......................................................... 11

2.6 Contingencies........................................................................................................ 12

2.7 Data Analysis........................................................................................................ 12

3.0 QUALITY ASSURANCE/QUALITY CONTROL ......................................................... 13

3.1 Data Quality Objectives, Indicators, and Assessment .......................................... 13

3.1.1 Overview................................................................................................... 13

3.1.2 Project Management ................................................................................. 13

3.2 Data Generation and Acquisition.......................................................................... 15

3.2.1 Data Quality Objectives............................................................................ 15

3.2.2 Study Documentation................................................................................ 18

3.2.3 Chain of Custody Procedures ................................................................... 18

3.2.4 Personnel Experience and Training .......................................................... 20

3.3 Assessment and Oversight.................................................................................... 20

3.4 Data Validation and Usability............................................................................... 20

4.0 EQUIPMENT LIST.......................................................................................................... 21

5.0 RESULTS ......................................................................................................................... 22

5.1 Breeding Bird Survey Data................................................................................... 22

5.2 Egg Data................................................................................................................ 22

6.0 SCHEDULE...................................................................................................................... 22

7.0 LITERATURE CITED..................................................................................................... 23

List of Figures

Figure 1. Reference Map of Proposed Study Area .........................................................................6

Figure 2. Project Management Structure ......................................................................................14
iv March 2002

List of Appendices

Appendix 1 Study Species Natural History Summary and Natural History Literature

Appendix 2 NYSDEC Labs Available for Egg Processing

Appendix 3 Egg Processing SOP

Appendix 4 Chain of Custody Form

Appendix 5 Schedule
1 March 2002

1.0 INTRODUCTION

The General Electric Company (GE) is believed to have discharged between 209,000 and 1.3

million pounds of polychlorinated biphenyls (PCBs) into the Hudson River between the 1940s and

1977 (Baker et al. 2001). These PCBs have been detected in the sediment, water, and biota of the

Hudson River at levels of potential ecological concern (TAMS Consultants, Inc. and Menzie-Cura

& Associates, Inc. 2000). A recent study documented elevated PCB levels in Hudson River

floodplain soils (S E A Consultants, Inc. 2001). As a result of this contamination, the Hudson River

Natural Resource Trustees (Trustees) are conducting a natural resource damage assessment

(NRDA) of the Hudson River. The Trustees include the State of New York acting through the New

York State Department of Environmental Conservation (NYSDEC), the Department of the Interior

acting through the U.S. Fish and Wildlife Service (USFWS), and the Department of Commerce

acting through the National Oceanic and Atmospheric Administration (NOAA).

The Trustees plan to conduct a survey of six avian species, including spotted sandpiper (Actitis

macularia), American woodcock (Scolopax minor), belted kingfisher (Ceryle alcyon), American

robin (Turdus migratorius), red-winged blackbird (Agelaius phoeniceus), and Eastern phoebe

(Sayornis phoebe). The Trustees plan to identify active nests of these species in and near the

Hudson River floodplain, and to further determine, through additional analysis, if eggs from each

species have elevated levels of PCBs. A limited number of nests from additional species will also

be identified on an opportunistic basis. The primary study area includes the Hudson River and its

floodplain from Hudson Falls south to Schodack Island.

1.1 Objectives

The objectives of this study are to:

• identify suitable nesting habitat for spotted sandpiper, American woodcock, belted

kingfisher, American robin, red-winged blackbird, and Eastern phoebe in the primary study

area within four general geographic zones in the study area;

• identify active nests for each species in each of four geographic zones within the study area

and collect one egg sample from each nest, up to a maximum of 40 egg samples per

species1

; and

• process egg samples to prepare them for chemical analyses.

1.2 Project Approach

In this section of the work plan we describe the rationale and overview of the approach and methods

that will be used to identify potential sampling areas per species, the approach for conducting

surveys, and the process of egg collection and analysis.

 

1

 Depending on egg mass, a single sample may consist of two eggs.
2 March 2002

1.2.1 Species Selection and Rationale

1.2.1.1 PCBs in Birds

A number of studies have documented that bird species can absorb PCBs from prey items and feed

(Drouillard and Norstrom 2001a, Custer et al. 1997 and 1999, Froese et al. 1998, Larson et al.

1996, and Secord et al. 1999). Numerous studies have further shown that a species' position within

the food chain affects the amount of PCBs that it will bioaccumulate (Focardi et al. 1988,

Senthilkhumar et al. 2002, Zimmerman et al. 1997). In particular, avian species that primarily feed

on fish or other birds tend to bioaccumulate PCBs to a greater extent than do species that feed at

lower trophic levels (Forcardi et al. 1988, Prestt et al. 1970, Senthiklumar et al. 2002).

Females can pass on PCBs to their eggs, although the degree of such maternal transfers varies

considerably amongst species. In general, altricial and semiprecocial species have lower egg to

maternal tissue ratios (0.3 to 0.7) than do precocial species (0.6 to as high as 5.0) that invest larger

quantities of lipids and energy into egg production (Drouillard and Norstrom 2001b). This suggests

that the amount of energy that goes into egg production, clutch size, and frequency of egg laying

may be important variables in the ratio of egg to maternal tissue concentrations.

In either adults or eggs, PCBs can reach concentrations that may cause toxic effects (Fernie et al.

2001, Hoffman et al. 1998, Stratus Consulting, Inc. 1999). Generally speaking, these toxic effects

can include mortality, malformations, decreased body weight, and/or reproductive impairment. The

nature and severity of the effect depends on the species, dosage, PCB congener(s), and the birds’

physiology (Barron et al. 1995, Eisler 2000, Eisler and Belisle 1996, Fernie et al. 2001,

Environment Canada 1998, and Hoffman et al. 1996a, 1996b, 1998). Effects of PCBs on adult

birds' reproductive behavior include increased amounts of time spent in the courtship phase,

reduced pair bond formation, delayed nest building, building nests of poor quality, delayed egg

laying, burying eggs in nesting material, decreased nest attentiveness, inconsistent incubation

causing fluctuations in egg temperatures, and increased nest abandonment (Arena et al. 1999,

Fernie et al. 2001, McCarty and Secord 1999a and 1999b, Peakell and Peakell 1973, Tori and

Peterle 1983).

Mortality, deformity, and other toxicological effects to embryos and nestlings have been found to be

correlated with PCB contamination in eggs; again, effects vary greatly according to species

sensitivity, levels of contamination, and composition of PCB mixtures (Brunstorm and Reutergardh

1986, Brunstorm 1989, Bush et al. 1974, Hill et al. 1975). Known effects include decreased

hatching success, delayed hatching, increased embryonic deformity rates (i.e., beak and limb

deformities, cardiovascular malformation), inhibition of lymphoid development, edema (pericardial

and subcutaneous), liver lesions, decreased organ weights, and reduced growth and survival (Barron

et al. 1995, Bosveld et al. 1995, Bosveld and Van den Berg 1994, Fernie et al. 2001, Gilbertson et

al. 1991, Hoffman et al. 1986, Hoffman et al. 1998, Larson et al. 1996, McCarty and Secord 1999a,

1999b, Powell et al. 1998, Yamashita et al. 1993).

1.2.1.2 Selected Species

The six species proposed for this study together provide a balanced approach in that they use

different types of habitats common to the Hudson River area, they consume different types of foods

and generally represent different ecological guilds (Appendix 1). The American woodcock and
3 March 2002

American robin feed extensively on earthworms (DeGraaf and Yamasaki 2001, Sheldon 1971) both

in uplands and wetlands. Robins also have a more omnivorous diet that includes fruits and insects

(Ehrlich et al. 1988), while woodcock also consume ground-dwelling insects (Ehrlich et al. 1988).

Spotted sandpipers, Eastern phoebes, and red-winged blackbirds consume extensive amounts of

insects, often from wetland or riparian habitats (Degraaf and Yamasaki 2001, Ehrlich et al. 1988).

Belted kingfishers primarily consume extensive amounts of small fish but also consume aquatic

invertebrates (Ehrlich et al. 1988).

All six species are suitable to study in that they are reported to be relatively common breeders in the

Hudson River floodplain (Andrle and Carroll 1988) and can use wetlands for some portion of their

life cycle (DeGraaf and Yamasaki 2000). For example, spotted sandpiper, American woodcock,

and belted kingfisher are substantially dependent on floodplain wetlands (DeGraaf and Yamasaki

2000). Red-winged blackbirds use emergent wetlands but may also use upland habitats (DeGraaf

and Yamasaki 2000, Ehrlich et al. 1988). American robins and Eastern phoebes are habitat

generalists that use a variety of communities, including urban settings (DeGraaf and Yamasaki

2000, Ehrlich et al. 1988, and Veit and Petersen 1993). Robin nests from the previous breeding

season were readily observed in shrubs growing immediately adjacent to the river during February

2002. PCB contamination of Hudson River floodplain soils was recently documented (S E A

Consultants, Inc. 2001). Many of the prey species consumed by the six study species include those

for which PCB accumulation has been documented in other regions, and PCB accumulation in prey

items from the Hudson River is likely to exist.

Relatively few PCB studies have been conducted to date on the six species proposed for this study.

The majority of studies involving the target species report levels of PCBs accumulated by

individuals, PCB levels in diets, and/or environmental PCB levels (McLane et al. 1971, 1976, 1978,

1984; Knupp et al. 1976; Walker 1977; NYDEC 1981; Heinz et al. 1984; Day et al. 1991; Eaton

and Carr 1991; Bishop et al. 1995; Kannan et al. 1998). Additional studies report levels of PCBs in

the carcasses of poisoned birds; however, levels were typically below reported lethal levels, and the

cause of death was attributed to other organochlorines such as DDE, DDT, dieldrin, chlordane,

heptachlor, and mirex (Stone and Okoniewski 1988, Okoniewski and Novesky 1993, Stansley and

Roscoe 1999). Stickel et al. (1984) found that the likelihood of PCB-induced mortality for common

grackles (Quiscalus quiscula), European starlings (Sturnus vulgaris), red-winged blackbirds, and

brown-headed cowbirds (Molothrus ater) increased substantially above PCB brain levels of 310

ppm.

Few field studies of the effects of PCBs on Hudson River bird populations exist. One recent set of

studies examined tree swallows (Tachycineta bicolor) in the Hudson River basin. Tree swallows

nesting along the upper Hudson River have known PCB concentrations up to 114,000 ng/g for total

PCBs based on fresh wet weight of adult whole bodies (Secord et al. 1999, Stapleton et al. 2001).

Tree swallows from the Hudson River were documented to have egg PCB concentrations ranging

from 9,320 to 29,500 ng/g, while concentrations in nestlings ranged from 3,710 to 62,200 ng/g

(McCarty and Secord 1999a). Reproductive effects observed included supernormal clutch size,

reduced hatchability due to failure of embryos to develop (presumably infertile) and death of

deformed embryos, high rates of nest abandonment, and other abnormal parental behavior (McCarty

and Secord 1999a, 1999b). Tree swallows have been able to successfully reproduce with PCB

concentrations that cause 100% embryo mortality in more sensitive species (McCarty and Secord

1999a). McCarty and Secord (1999b) also described abnormal nesting behavior of tree swallows

and inferred that chemical contamination can possibly interfere with behavior.
4 March 2002

Few data currently exist to generate definitive conclusions regarding PCB exposure and effects on

other wildlife species that inhabit the Hudson River floodplain. A recent study, however, indicates

that some small mammals collected from floodplain areas have elevated levels of PCBs in their

tissues (S E A Consultants, Inc. 2001). Avian species that inhabit the floodplain or that forage on a

prey base with an ecological connection to the floodplain may also be exposed to PCBs. Even if

nesting occurs outside the floodplain, some avian species may still have the potential to consume

prey that may be contaminated by Hudson River PCBs. This study will provide the Trustees with

information regarding PCB exposure in the eggs of six common avian species that nest in or near

floodplain areas. These data may assist the Trustees in the development of possible future natural

resource damage assessment studies.

1.2.2 Survey Overview

The primary objective of this study is to collect the egg samples of the six species and to process

those samples in anticipation that they will be analyzed to determine if they have elevated levels of

PCBs. Ultimately, these data could provide information on how PCBs transfer through the food

chain. Surveying for and locating nests of the six species will provide general information on the

location, abundance, and habitat use of each within the Hudson River floodplain. Locating nests

will require a stepwise approach that considers the specific egg-laying and incubation periods of

each species.

General reconnaissance surveys will precede the main study effort to identify potential habitats of

the study species and various logistical components related to completing the surveys. Literature

reviews and contacts with local birders or birder groups will help with identifying suitable habitats

and with identifying private landowners that may need to be contacted. Habitat maps will be

prepared on aerial photos using the reconnaissance information, which will serve as the base map

for the surveys. Avian surveys will be conducted in pre-identified habitat to locate breeding

individuals of the study species. These surveys will lead to the nest search effort, which will be

based on the locations of the breeding birds, and will result in a detailed search effort. One egg

sample from each target nest found will be collected and processed. Some samples, especially for

small eggs, may require collecting two eggs.

2.0 METHODS

In this section of the work plan we describe the methods that will be used to identify potential

breeding habitat, contact landowners for permission to access property, complete the breeding bird

surveys, collect eggs to be submitted for chemical analysis, and generate and report the results.

2.1 Literature Search

Before field surveys are performed, scientific and technical literature will be reviewed to determine

the distribution of the six study species in the Hudson River drainage system. As part of this effort,

local and regional experts will be consulted to obtain unpublished records regarding the occurrences

of these species in the area. For example, it is likely that some regional experts may have

knowledge of belted kingfisher nest locations or American woodcock display areas. This effort will

include attempting to contact individuals who performed breeding bird surveys along the Hudson
5 March 2002

River, regional biologists, and private groups and/or individuals. The New York Natural Heritage

Program, NYSDEC, and the USFWS will also be consulted to determine if records of any of the six

study species from the Hudson River drainage are available from surveys sponsored or conducted

by these agencies. The U.S. Geological Survey (USGS) (2002) maintains a database of studies on

many wildlife species. Natural history and scientific information on these species, including habitat

use, diet, home range, reproductive behavior, and effects of contaminants, will be obtained and

summarized.

2.2 Habitat Identification

Prior to conducting field surveys, the location, type, and condition of plant communities in the study

area will be reviewed through photo-interpretation. Using the descriptive nesting habitat data from

the literature (Appendix 1) and past experience, potential survey areas that appear to be suitable

breeding habitat will be identified on digital and hard copies of georeferenced aerial photos. Land

ownership patterns and access points will also be identified. Following this effort, an on-site,

reconnaissance-level habitat survey will be completed to ground-truth aerial photo- interpretation,

locate potential nesting habitat for the six study species, and identify public and private lands for

surveys.

Vegetative communities will be categorized relative to their potential to provide nesting habitat for

each species. For example, sandy banks and bluffs near water resources will be identified as

potential nesting sites for belted kingfishers. Old fields, young aspen (Populus spp.) stands, and wet

thickets that may serve as display grounds and nesting habitat for woodcock will be mapped. Open

habitat along water resources (i.e., the river, large streams, shallow emergent wetlands, and ponds

and lakes) with potential nesting habitat for spotted sandpipers will be mapped. Emergent marsh

habitat can be located on aerial photos and National Wetland Inventory maps. These areas serve as

nesting habitat for red-winged blackbirds. Upland and wetland forested habitat will be mapped,

especially those areas interspersed with small openings with potential for nesting American robins

and Eastern phoebes.

Egg samples will be collected in each of four geographic zones within the study area to provide a

balanced sample amongst various portions of the river. The four regions can be approximately

described as follows: the six-mile portion of the river known as Thompson Island Pool; Stillwater

pool; the area below Stillwater pool extending south to the Troy dam, and the area below the Troy

dam extending south to Schodack Island, excluding Albany. Figure 1 provides a reference map of

the proposed study area.

Boundaries of public lands will be overlaid onto the vegetation maps to identify study areas with

potential easy access. Habitat containing known levels of PCB contamination will also be mapped

as a data layer. This information will be used to identify sites with a greater potential for transmittal

of PCBs from sediment to the study species. The results of the photo-interpretation and

reconnaissance-level survey effort will be a set of vegetation community maps with potentially

suitable habitat mapped for each species or their food. Windshield surveys of private land for

which access has not been obtained will be completed to locate high potential breeding habitats.

These areas will then be surveyed for the study species as appropriate, once permission to access

has been obtained.
6 March 2002
7 March 2002

2.3 Landowner Contacts

Maps showing the location of areas to survey for the six study species will be compared to land

ownership maps obtained from the New York State GIS Cooperative (NYSGIS) and local

assessors' offices. The NYSGIS has ArcInfo GIS files showing the location and ownership of

public land in the study area. Accessible public lands with suitable habitat will be given priority

for study locations, although we expect that privately held lands also would be surveyed.

Owners of private land will be identified through the assessors' offices in town and city halls,

where their names and addresses will be obtained. We will work with the Trustees to coordinate

actual contacts with landowners. A priority approach will be taken as we anticipate that large

landowners with the best potential habitat will be contacted first, followed by smaller landowners

with poorer quality habitat. Methods of contact will likely include a combination of phone calls,

letters, and personal contact.

2.4 Breeding Bird Surveys and Locating Nests

2.4.1 Overview

Breeding bird surveys will be performed to locate potential nest sites of the six study species:

spotted sandpiper; American woodcock; belted kingfisher; American robin; Eastern phoebe; and

red-winged blackbird. Standard breeding bird survey techniques and methods will generally be

followed to prepare survey transects, locate survey stations, and locate breeding territories.

These techniques include silent listening and observing within suitable habitat along the river

and adjacent roads. The locations of stations will be determined by the suitability of habitat,

observations of the study species, and obtaining landowners' permission. The habitat maps and

aerial photos will be used to guide members of the survey tem to suitable areas. The techniques

will vary by species and their requisite habitat as outlined below. Survey route sites will not be

randomly located, since the objective is to locate as many active nests of the study species as

possible.

Breeding individuals of the six study species will be identified by sound and sight whenever

possible. Observers performing surveys will be trained in identifying calls of the study species

by listening to previously made recordings. Similarly, observers will be trained to identify each

species through the use of field guides, slides, and videos. Sight identification will be aided by

the use of A Field Guide to the Birds of Eastern and Central North America (Peterson and

Peterson 1980) and by the use of Field Guide to the Birds of North America (National

Geographic Society 1983). Sound identification will be aided by use of the Cornell Lab of

Ornithology A Field Guide to Bird Songs (1990) and Guide to Birds of North America, Version 3

(2001). Nests, eggs and nestlings identification will be aided by the use of A Guide to the Nests,

Eggs, and Nestlings of North American Birds (Baicich and Harrison 1997).

2.4.2 Spotted Sandpiper

Spotted sandpipers will be located by surveying the shore of the Hudson River, emergent

wetlands, streams, and any other water resources in the area. Visual observations and listening

for their alarm call will be used to locate potential breeders. Observing these individuals should
8 March 2002

help locate nests although extended observations often will be needed to follow the birds to

potential nest sites. Spotted sandpipers are polygamous with the female laying up to five

clutches and the males tending the nest (Ehrlich et al. 1988). The plumage and size of the males

and females is identical, as with most shorebirds, therefore, making nest location more difficult.

Visual observations of a female early in the egg laying process may lead to more than one nest.

Areas with more than one spotted sandpiper will be considered potential nest sites. Observers

will monitor these locations from a boat, canoe, or land to locate the nest site, which is usually

next to and concealed by a dense tuft of grasses or sedges.

2.4.3 American Woodcock

American woodcock singing ground survey data will be obtained from the USFWS for the study

areas. Potential nesting habitat, levels of known contamination, and suspected levels of

contamination (based on geomorphology, frequency of flooding, proximity to sources, etc.) will

be compared on aerials photos and maps of the potential survey sites. Areas without singing

ground survey data but with apparently suitable habitat will also be identified on photos and

maps. These data will then be compared to develop a list of prioritized sites for woodcock

surveys. Areas with the best habitat, known past occurrence of singing males, and known levels

of PCB contamination in floodplain soils will be given priority for survey. The prioritized list of

survey sites will be compared to lands for which access has been obtained, and sites will be

selected for field surveys. The initial surveys will be conducted from public roads.

Field surveys will progress in two steps: singing ground surveys, followed by nest searches.

Because the singing ground surveys will be conducted from public roads, it is not essential that

permission be obtained prior to listening for singing males. Singing ground surveys will

generally follow USFWS North American Woodcock Singing Ground Survey protocol (USFWS

1995). Surveys are expected to begin around April 1, but can start sooner if spring is early.

Surveys are expected to continue until about May 10. The timing of surveys is critical because

singing males usually display for a short period (usually 30 to 40 minutes) each night. Surveyors

will be prepared to begin each survey slightly before sunset. If the sky is clear or up to and

including 3⁄4 overcast, 22 minutes will be added to the sunset time to determine the starting time,

and 15 minutes will be added if the sky is more than 3⁄4 overcast (USFWS 1995).

At each potential singing male survey site, surveyors will stop and shut off the car, get out and

silently listen for 2 minutes. The location of each male heard singing (i.e., peenting) or flying

will be estimated using a hand compass, aerial photos, and maps of the study area. If the

location cannot be accurately located, the observer will drive closer and attempt to locate the

singing male. Once located, the observer will continue to the next location of suitable habitat

and repeat the survey procedure until dark. One singing ground survey (approximately 10 sites

spaced 1/8-mile apart) can be completed per evening per observer.

Woodcock nest searches will focus on wooded habitat within 300 to 400 feet of where singing

males were observed, as females often select nest sites within 300 feet of the males’ territory

(Sheldon 1971). Several field staff, possibly accompanied by a bird dog, will perform nest

searches. A systematic search of potential nest sites will occur by walking back and forth

through each area until a bird is flushed, or until the site has been thoroughly searched and no

birds observed. When a bird flushes, the location will be noted and a very slow search of the

flush site will be made. Incubating female woodcock will only flush when there is eminent
9 March 2002

danger of trampling, so when a female does flush, chances are that the nest is very close. Once a

nest is found, one egg will be collected using the methods described in Section 2.6. The location

of each nest will be located using GPS equipment.

2.4.4 Belted Kingfisher

The habitat survey effort will locate potentially suitable habitat along the river, along large

streams, and along lakes and ponds. Contacts made with local and regional biologists and local

birders will be used to help pinpoint known or potential nesting sites. These identified areas can

be compared to known areas of elevated PCB concentrations along the river and in floodplain

areas to identify preferred sampling areas.

Belted kingfisher nests are burrows within banks and are generally in open situations that are

fairly accessible. Males and females tend the nest; therefore, locating perched kingfishers and

observing their movements helps locate active nest sites. Potential habitat will be visually

scanned from a boat and/or canoe or from land immediately along the river. Kingfishers will be

observed to assess activity to and from a nest and hence locate the nest. Conversely, burrows

can be visually located and then observed for kingfisher activity. Using either procedure will

require dedicated and patient observation, often watching and waiting to observe kingfisher

activity.

Active nest sites will be carefully approached, since the burrows are often on sandy bluffs that

may have limited and difficult access. The bluffs may not be stable, and excessive activity could

create erosion and damage the burrow. The survey team will develop a general plan of action

before approaching the nest. Approaching a nest could require the use of a rope ladder,

extension ladder, or rope harness. The burrow will be visually inspected (a flashlight and

compact mirror may be used) first, and then a burrow scope will be used to determine the activity

status of the nest, the presence or number of eggs, and the length of the burrow. Kingfisher

burrows are normally 3 – 6 feet long but can be up to 15 feet in length. If the eggs can be readily

observed from the burrow entrance, one egg will be retrieved manually using a telescoping pole

with a small padded or blunt “J” shaped hook or “pincher” on the end. If the burrow is deep and

the eggs cannot be visually located, then the burrow scope will remain in place and the

telescoping pole used to retrieve one egg. The survey team will need to monitor the nest with the

scope and a head mounted display system to guide the telescoping pole into the burrow. Once a

nest is found, one egg will be collected using the methods described in Section 2.6. In situations

where it is unsafe to approach a burrow or for burrows that are too deep or otherwise unsuitable

for retrieving an egg, the survey team will not attempt to retrieve an egg.

2.4.5 American Robins, Eastern Phoebes, and Red-Winged Blackbirds

American robins, Eastern phoebes, and red-winged blackbirds can be located using the typical

breeding bird survey techniques. Eastern phoebes and American robins are habitat generalists

and locating the birds should be possible through habitat mapping and visual surveys. Redwinged blackbird nesting habitat should be identified as emergent wetlands with vegetative

structure to support the nest. Potential nesting habitat, levels of known contamination, and

suspected levels of contamination will be compared on aerials photos and maps of the potential

survey sites as with the other species. Suitable habitat immediately adjacent to the river,

especially near areas of known or suspected contamination, will be given the first priority for
10 March 2002

nesting surveys. Roadside ditches, man-made and natural ponds, and agricultural habitat

adjacent to the river will serve as the focal habitat for the red-winged blackbird. Priority habitats

will be located on the aerial photos based on the above criteria. Locating nests of these three

species will require close visual observation either from a distance or walking and searching

selected areas.

Early morning roadside surveys will be completed for each species to locate singing or calling

birds. Surveys will begin approximately one-half hour before sunrise and continue until late

morning when most singing and display activity has ended. Biologists may extend surveys into

the afternoon for red-winged blackbirds, as their territorial activity and communal nature may

support an extended survey time.

Robins have a very distinct territorial song, often sung by the male in an area near the nest.

Locating a singing male, along with knowledge of the typical robin nest locations, will help

focus the nest search effort (Appendix 1). Once a singing robin is located, quiet observation is

needed to observe nesting activity and locate an active nest. Upon locating a nest, a telescoping

“tree peeper” will be used to look into the nest and determine the presence of eggs. Care will be

taken to remove one egg from each nest and to minimize disturbance to the incubating robin.

Eastern phoebes are often observed perched on small trees and shrubs, utility lines, and fences

posts in open woodland, agricultural, and wetland habitats. Their habit of spreading and

pumping their tail lends them visibility. Often phoebes nest in or on a variety of human built

structures including farm buildings and under bridges (Ehrlich et al. 1988). The nest is

comprised of a mud base with other natural materials. Observers will look for these clues to

focus in on a nesting site. Locating this visible species and observing foraging trips should lead

the survey team into the proximity of the nest and, in fact, may lead to locating a nest. Nests can

also be located by scanning suitable nesting structures and carefully watching for phoebes and

following them to the nest. Each nest should be investigated visually, using a “tree peeper” as

needed. Initially, one egg can be removed from each nest; if the egg mass does not meet the

minimum mass requirement, a second egg will be collected. For some species (e.g., phoebes and

swallows) we anticipate that two eggs will need to be routinely collected.

Red-winged blackbird territories can be located based on observing displaying males generally

within emergent wetland habitat. It is not unusual for good habitat to contain numerous nesting

red-winged blackbirds, increasing the potential for locating multiple nests in close proximity

(Case and Hewitt 1963). Scanning emergent habitat around displaying males should bring the

survey team to a close nest location. Watching for female red-winged blackbirds will generally

lead to a nest. Often, walking through the habitat will cause the female to flush and make

locating the nest possible.

2.4.6 Opportunistic Collection

The location and collection of eggs for the six study species may provide opportunities for

collection of eggs from other species, especially for species with common habitats. The

collection of egg samples for 11 additional species will be based solely on the opportunities for

survey team members to locate the nests of these species. The 11 species identified for

opportunistic egg sample collection are green heron (Butorides virescens), great blue heron

(Ardea herodias), Eastern screech owl (Otus asio), American kestrel (Falco sparverius),
11 March 2002

common grackle, hooded merganser (Lophodytes cucullatus), cliff swallow (Hirundo

pyrrhonota), northern rough-winged swallow (Stelgidopteryx serripennis), bank swallow

(Riparia riparia), barn swallow (Hirundo rustica), and Eastern bluebird (Sialia sialis). Some of

these species are somewhat less associated with the riverine habitat or are thought to be more

difficult to study. For example, green heron nests are relatively difficult to locate and great blue

heron rookeries are documented in the study region, but are not common. Both species have the

potential to be affected by PCB contamination from the fish and other aquatic species that they

consume. American kestrel and Eastern bluebird egg samples can be obtained from nests in

natural sites and artificial structures. These species have a less direct ecological connection to

the river as they are largely found in (and tend to forage in) upland habitats. Common grackles

are connected to the river and are found in many wetland and upland habitats. They have a loose

colonial nesting practice, which may make obtaining egg samples relatively easy.

Biologists collecting egg samples for the six study species will observe and attempt to locate

nests of these 11 additional species. The same natural history information on habitat use, nest

site characteristics, egg size, and egg description will be used to help locate nests of these

species. The same egg sampling procedures will be used for obtaining and processing samples.

2.4.7 Data Location and Management

The location of transects, survey stations, all study species observations, and locations of nests

will be plotted on maps or georeferenced aerial photos of the study area. Each nest will be

uniquely numbered and designated by species, habitat community, vegetation located in (where

applicable), and coalesced with the egg collection data (as discussed below). GPS data will be

collected for each located nest and as needed for transects; however, because of the quality of

digital georeferenced aerial photos available (i.e., you can locate individual trees, houses, and

other landmarks) it is unlikely that transects will need to be surveyed. Notes on the approximate

numbers of each species observed per area will be recorded.

2.5 Study Species Egg Collection and Analysis

One egg sample (containing up to two eggs) will be collected from each nest of the six study

species. Before collection begins, permits from the NYSDEC, NPS, and USFWS will be

obtained to collect eggs. The USFWS will assist in the effort to obtain permits. At each nest site

suspected of having an active nest, a survey team will use a peeper probe or mirror and extension

pole to peer inside the nest to determine if an adult is still on the nest, or if any of the eggs have

hatched. These observations will be recorded in field notebooks. After determining that eggs

are available for collection, a survey team member will reach into the nest and collect an egg.

Scientists will wear nitrile gloves to reduce exposure to any parasites and diseases that may be

present in the nest or on an egg. When eggs are removed, the total clutch size before egg

removal will be recorded. Each egg will be photographed and the film roll and photo log number

will be recorded in the field notebook. This information will be logged with the georeferenced

area and other identification information. Each egg from the smaller species will be weighed

using a field balance to determine if the minimum egg mass is achieved. If the minimum mass is

not achieved with one egg then a second egg from that clutch will be collected. The collected

egg(s) will be marked with the sample collection nest identification (ID) number using a graphite

pencil and wrapped in a protective manner with aluminum foil that is also labeled with the nest

number, so that it does not break until it is placed in an egg container.
12 March 2002

Wrapped eggs that have been securely placed in an egg container will be put into a cooler or

secure box and transported to a NYSDEC lab for processing. Eggs will ideally be processed the

same day they are collected and in any event will be processed within 48 hours of collection. A

list of lab facilities available for processing eggs is in Appendix 2. Once in the lab, each egg will

be measured, processed and stored according to the Standard Operating Procedure for Egg

Harvest (Appendix 3) with the appropriate Chain of Custody (COC) (see Section 3.2.3 and

Appendix 4). Egg contents will be sent to NOAA’s archive freezer (Sand Point Archive, Seattle,

Washington) or to the DEC Hale Creek lab for storage at a temperature of minus 20 degrees

Celsius until they can be shipped to the program analytical laboratory for chemical analysis.

Conducting the chemical analyses is not part of this work plan.

2.6 Contingencies

When conducting bird studies, disturbance can create biases that affect the gathering and analysis

of data and can have effects on the birds being studied themselves (Gaunt et al. 1997). As Gaunt

et al. (1997) point out, in field ornithology, adverse affects are most commonly associated with

nest visits, which can result in biased data and decreased reproductive success. Investigators can

cause nest desertion, damage to eggs and young from frightened adults, thermo-damage to eggs

or young, mortality from missed feedings or predation, or accidental death from mishandling

(Fyfe and Olendorff 1976).

During the surveys, all efforts will be made to minimize disturbance to the nesting study species.

These efforts will include minimizing the number of surveys and nest visits and the type of nest

visits, particularly during the early parts of incubation (Grier and Fyfe 1987). To the extent

possible remote observation of nests will be performed using binoculars or spotting scopes. If

sufficient data cannot be obtained remotely, then inspection from a short distance (i.e., walking

up to the nesting tree) or direct inspection (i.e., actually climbing a tree) will occur; however,

these activities will only occur if they are not believed to be detrimental to the nesting birds.

Many raptor species are believed to be most sensitive to disturbance just prior to egg laying up to

the onset of incubation, from first hatching until the young become endothermic, and just prior to

fledging (Steenhof 1987). Nest visits during these periods will be avoided as much as

practicable, but cannot be completely avoided. Additionally, nest visits will not be performed

when weather conditions could prove detrimental to eggs or young (e.g., during a cold, rainy

day, or during the middle of a hot, sunny day). Nest visits will be also kept as short as possible.

2.7 Data Analysis

Data endpoints for the egg collection study will include egg mass and volume, egg length and

breadth, egg shell thickness, weight of the contents (fresh weight will be back calculated using

methods described in Appendix 3), fertility (i.e., fertilized or not), embryo position, embryo

deformities, and contamination level. Comparisons of data endpoints will be completed

between the four geographic areas. Two-group comparisons of data endpoints will be made

using Student’s t-test (parametric) or the Mann-Whitney U test (nonparametric). Multiple group

comparisons will rely on ANOVA (parametric) or Kruskal-Wallis (nonparametric) tests. All

analyses will be performed using the Statistica® (StatSoft 1999) software package.
13 March 2002

3.0 QUALITY ASSURANCE/QUALITY CONTROL

3.1 Data Quality Objectives, Indicators, and Assessment

3.1.1 Overview

This study is being conducted in accordance with the Quality Assurance Management Plan for

the Trustees’ Hudson River NRDA. As described in the plan, four general elements of quality

assurance/quality control (QA/QC) must be addressed for each data collection effort:

• project management

• data generation and acquisition

• assessment and oversight

• data validation and usability

This section describes the Quality Assurance Plan (QAP) for the breeding bird egg exposure

study, based on these four general elements. The objectives of the study are outlined in Section

1.1. To achieve these objectives, the following types of data will be required:

$ Breeding bird surveys, nest identification, and egg collection: Accurate species

identification is required to locate targeted species in the study area. Egg collection and

processing will require following set procedures to insure proper handling and

minimizing impacts to nesting individuals.

$ Egg contamination levels: The laboratory chosen for tissue analysis will follow the

requirements of the Hudson River NRDA Analytical QA Plan (in preparation). This

effort is not part of the current work plan and will be funded separately.

3.1.2 Project Management

The study team is organized based on tasks and levels of responsibility to ensure good

communication between all personnel (Figure 2). The Assessment Managers (Kathryn Jahn,

USFWS, and Tom Brosnan, NOAA) have overall project oversight responsibility and provide

direction to the Quality Assurance Coordinator. The Assessment Managers also provide direction

to the Principal Scientist via the Project Coordinators. The Project Coordinators are responsible

for ensuring that adequate coordination and communication occurs amongst the Assessment

Managers, Quality Assurance Coordinator, Principal Scientist, and Consulting Biologist. With

input from the Consulting Biologist, the Project Scientist is responsible for the project's design

and implementation and provides guidance and technical expertise as needed to the Field Survey

Lead.

The Field Survey Lead provides instructions to survey teams on all aspects of the project,

including quality assurance management. Field survey teams consist of a Project Scientist and a

Project Technician, as needed. The Field Survey Lead is responsible for resolving any issues

raised by Project Scientists or Technicians. The Field Survey Lead reports to the Principal

Scientist, who will work with the Project Coordinators and Quality Assurance Coordinator to

ensure that the study is consistent with the overall QA objectives of the NRDA.
14 March 2002

Figure 2: Project Management Structure

This work plan for this study was developed to provide detailed and explicit instructions for the

field crews to follow in collecting the study data. The plan has been reviewed, commented on,

and approved by key parties to the study before the beginning of sample collection. Reliance on

a detailed, explicit, and fully reviewed work plan ensures that:

• Study objectives, methods, procedures, and details are completely thought out before

sampling.

• Data will be collected in a systematic and consistent way throughout the study.

• Every member of the study team adheres to the requirements of the plan. Each field team

member is required to sign a statement that they have read the plan and understand it. In

particular, the field crew leaders must make sure that their crews adhere to the plan.

The procedures specified in this plan must be considered somewhat flexible by the field study

team. Many events can arise during field data collection that require changes to the procedures

being used. In these circumstances, deviations from the plan will be conducted only after

consultation between the Project Scientists and Field Survey Lead. Deviations from the work

plan will be carefully documented, as will a detailed explanation as to why the deviations were

necessary.

Assessment Managers

Kathryn Jahn, USFWS

Tom Brosnan, NOAA

Quality Assurance Coordinator

Consulting Biologist Principal Scientist

Project Coordinator

Field Survey Lead

Principal Scientist

Principal Technician

Principal Scientist

Principal Technician

Principal Scientist
15 March 2002

3.2 Data Generation and Acquisition

3.2.1 Data Quality Objectives

Data developed in this study must meet standards of precision, accuracy, completeness,

representativeness, comparability, and sensitivity, and be consistent with sound scientific

methodology appropriate to the data quality objectives.

Precision is defined as the level of agreement of repeated independent measurements of the same

characteristic. For this study, repeated independent measurements of species identification (e.g.,

distinguishing between a similar species) will not be possible for specimens that are not

collected, or for calls that are not recorded. However, agreement between surveyors regarding

species identification must be obtained for verification. This will occur in the field on a daily

basis as surveys are conducted. Precision may also be evaluated by assessing the degree to

which surveys are consistent among sites. The frequency and type of field checks are listed in

Table 1.

Accuracy is defined as the agreement of a measurement with its true value. For the parameters

unique to the field portion of this study, accuracy means that the target animals are correctly

identified and counted. Project Scientists and Technicians will be required to pass a test

identifying each target species visually (adults, eggs, and nests) and by call before they can

perform field surveys. The Field Survey Lead will conduct this test. Accuracy for analytical

data collected as part of egg analysis will be defined in the Hudson River NRDA Analytical

QA/QC Plan (in preparation).

Completeness is defined as the percentage of the planned samples actually collected and

processed. Although sample sizes cannot be predetermined, observations must be conducted

throughout the season when the breeding birds are present in the study area and in each habitat

that these species could use where access is granted. The full distribution of study efforts within

those parameters is a measure of the completeness of this study.

Representativeness is defined as the degree to which the data accurately reflect the

characteristics present at the sampling location at the time of sampling. Obtaining representative

data for this study will be ensured through the establishment of a thorough literature review to

identify life history characteristics, breeding habitat, and nest site descriptions, and by

completing field investigations in a manner to determine if those species are present. The study

design employs standardized breeding bird survey techniques that have been proven acceptable

for breeding bird surveys in different parts of North America.

Comparability is defined as the measure of confidence with which results from this study may be

compared to another similar data set. Because of the nature of the study, there cannot be a

duplication of effort in the same area at the same time. Comparability will be attained through

use of standardized, peer-reviewed bird survey techniques that are commonly used in bird

surveys in different parts of North America.

Sensitivity is defined as the ability of a measurement technique or instrument to operate at a level

sufficient to measure the parameter of interest. For data specific to this study, sensitivity will
16 March 2002

pertain to the ability to locate and identify the six study species and their nests. This process is a

stepwise approach that requires ornithological expertise. First, potentially suitable habitat must

be located through the use of aerial photographs, general habitat reconnaissance, and specific

habitat assessment. Once suitable breeding habitat is located, breeding bird surveys can begin.

Surveys involve using visual searches and silent listening to locate the species for which there is

potentially suitable habitat. In many cases, a bird will be identified through silent listening by a

territorial, breeding, or alarm call or song. Furthermore, the surveyor must be able to follow the

individual bird and locate the nest site and nest. Therefore, species identification includes

knowledge of songs and calls, visual identification, territorial behavior, habitat use, nest site

selection, and nest and egg identification.
17 March 2002

Table 1. QAP Type of Field Checks and Frequency.

Type of Field Activity Measurement

Minimum Frequency of

Check by Field Survey

Lead or Principal

Scientist

Acceptance Criteria

Study species identification by sight Each study species can be

identified by sight and using a

field guide for confirmation.

Once before beginning of

study, and then monthly.

Regular discussions

between staff are expected.

Photographs, slides, and

video images of the six

study species will be used

to check identification.

One hundred percent

accuracy on

identification.

Study species identification by sound Each study species can be

identified by sound.

Once before beginning of

study, and then monthly.

Regular discussions

between staff are expected.

Sound recordings will be

used to check

identification.

One hundred percent

accuracy on

identification.

Study species nest and egg

identification

Each study species nests and

eggs can be identified by sight

and using a field guide for

confirmation.

Once before beginning of

study, and then monthly.

Regular discussions

between staff are expected.

Each study species using

photographs, slides, and

video images.

One hundred percent

accuracy on

identification.

Orienteering, aerial photo

interpretation, and location plotting

Field personnel can locate

positions on an aerial photo of

the study area.

Once before beginning of

study. Staff will have

regular discussions in

regard to where work is

being completed and

where nests are found.

Personnel can locate

positions of specific

features on aerial

photos correctly.

GPS data collection and data

downloading

Field personnel can operate GPS

equipment and transfer data to

computers.

Once before beginning of

study, and then as data is

downloaded and verified.

Control point data

collected in the field

matches up to correct

locations on

georeferenced aerial

photos of the study

area.

Completion of data forms Data forms are filled out each

day correctly and completely.

Weekly. Data forms are

complete, legible,

and accurate.

Egg collection Eggs are properly labeled when

collected and then transferred to

lab for analysis.

Each day an egg is

collected.

Each egg is correctly

assigned a sample ID

number.

Egg analysis Eggs contents are processed

according to the SOP.

Each day egg contents are

processed or every 20

samples.

Egg content samples

are prepared for

shipment to NOAA's

or DEC’s archive

freezer per the SOP.
18 March 2002

3.2.2 Study Documentation

All study activities will be documented in waterproof field notebooks and data forms, which will

be placed into 3-ring binders. To the extent possible, information will be recorded on preformatted data sheets. The use of pre-formatted data sheets is a QA/QC measure designed to:

• ensure that all necessary and relevant information is recorded for each sample and each

sampling activity,

• serve as a checklist for the field crews to help ensure completeness of the data collection

effort,

• assist the field crews by making data recording more efficient, and

• minimize the problem of illegible field notebook entries.

Each field crew will have a single field data recorder responsible for recording information in

field notebooks or on data forms. Assigning this responsibility to a single person will help

ensure that documentation is complete and consistent throughout the sampling event. The field

data recorder is also responsible for the care, custody, and disposition of the field notebook.

Field notebook entries will be made in waterproof ink, and corrections will be made with a single

line through the error accompanied by the correction date and corrector’s initials. Each

completed data sheet will be reviewed, corrected (if necessary), and initialed by the field data

recorder and the appropriate field crew leader. Following completion of the study, field

notebook originals will be retained as specified in Section 3.4.

3.2.3 Chain of Custody Procedures

Strict COC procedures will be used throughout the study. The COC procedure will begin when

an egg is collected from the nest. A COC form is shown in Appendix 4. These forms will be

used to maintain records of sample collection, sample transfer between personnel, sample

shipment, and sample receipt by NOAA or DEC for storage in a freezer, or receipt by the

analytical lab. Each sample collected will be listed on the COC forms. A separate form will be

used for each cooler that is shipped. The original COC will accompany the samples. The field

personnel will maintain a copy of the COC. The signatures of the persons shipping and

receiving the samples, and the date and time of transfer, will be documented on the COC forms.

An air-bill can be used to document the transfer of a sample from the field team to the shipper,

and from the shipper to the freezer archive or the analytical lab.

All sections of the COC form will be completed with information pertaining to the sample

collection. All samples included in the sample catalog will be clearly listed. The time, date,

location, identifier (i.e., sample ID number), type of sample, and number and size of containers

will also be listed on the form. If more than one cooler is required to ship the samples, a separate

form will be used listing the samples actually held in each cooler. An indication of the number

of coolers per shipment (e.g., 1 of 3) will be listed on the form. Once the form is completely

filled out, it will be placed in a clear plastic shipping window and securely attached to the inside

of the cooler. Each cooler will be sturdy, well sealed with filament tape, and have an unbroken
19 March 2002

signed custody seal. All materials, samples, and coolers will be kept in locked locations all the

time until shipped.

All samples collected will be uniquely identified with a label attached directly to the container.

Label information will be recorded using a waterproof marker and will include the sample ID

number, species, type of sample (egg), time and date of collection, project name, sample

location, and sampler’s initials. Much of this information will be pre-filled before sampling.

 The following sample identification code will be used “SP-NES-NUM.”

“SP” will be a 2-letter code that designates the species and sample type for the six study species:

• SS = spotted sandpiper egg

• AW = American woodcock egg

• BK = belted kingfisher egg

• AR = American robin egg

• RB= red-winged blackbird egg

• EP = Eastern phoebe egg

A likewise designation is provided for each of the “opportunistic” species:

• GH = green heron egg

• BH = great blue heron egg

• AK = American kestrel egg

• SO = Eastern screech owl egg

• EB = Eastern bluebird egg

• CG = common grackle egg

• HM = hooded merganser egg

• NS = barn swallow egg

• RS = rough-winged swallow egg

• BS = bank swallow egg

• CS = cliff swallow egg

“NUM” will be a unique three-digit numerical code that corresponds to the egg sample (numbers

001 – 499). “NES” will be a unique three-digit numerical code that corresponds to the nest

number for samples (numbers 001 – 499) associated with an active nest. Each field crew team

will have designated number ranges that they can work from to avoid duplication of the

numbering sequence.

When egg samples are first removed from the nest, they will be marked with the sample type

code (e.g., SS, AW, BK), egg sample number, and nest number on the outside of the egg using a

pencil. They will then be wrapped in aluminum foil, which will also be labeled with the nest

number, using a permanent marker. Eggs will be transported to the processing facility in egg

containers or a similar box that protects from breakage. Once in the processing facility, the

labels on the foil and on the egg will be double checked against the data forms and field survey

notebooks to verify the identification code.
20 March 2002

3.2.4 Personnel Experience and Training

Field sampling crews will receive explicit instructions in the execution of this work plan. The

field crews will be instructed in the field before beginning any sampling, and the instructions will

be repeated or refreshed during the sampling period as necessary (Table 1). A senior field

scientist with experience in breeding bird survey techniques will direct all fieldwork. Field crew

members will be trained to identify each study species by sight and sound, their habitat, nests,

and eggs. Prior to conducting actual surveys, field crews will be required to study and listen to

previously recorded birdcalls, and to pass an identification test.

3.3 Assessment and Oversight

The QA management plan specifies that studies that generate data will be audited to ensure that

the project-specific plans are being properly implemented. Several mechanisms for internal

audits of the data generation process will be used for the breeding bird egg exposure study.

These mechanisms include:

• A project management structure that defines clear lines of responsibility and ensures

communication between field crews and with the Field Survey Lead. Clear

responsibilities and communication can serve as a means of providing internal audits of

the sample collection process as it proceeds.

• A requirement that field notebooks and data forms be completed daily and be reviewed

weekly by the Field Survey Lead or Principal Scientist.

• The use of pre-formatted data sheets that serve as a checklist for sampling procedures,

thereby helping to ensure that sampling is complete.

• The sampling will not begin until approval is received from the Quality Assurance

Coordinator or their delegate. The Quality Assurance Coordinator or designee will

conduct a field audit of procedures and documentation of the study.

3.4 Data Validation and Usability

This study employs standard, repeatable methodology available in the scientific literature for

collecting breeding bird occurrence data. The work plan for this survey has been extensively

reviewed for the adequacy of the sampling design and methods. The original field notebooks

will be maintained and archived for a minimum of eight years. Disposal of the notebooks will

take place after this timeframe unless a longer archive period is requested. Final reports can then

be reviewed against the sampling records to ensure that the data presented in the reports

represent complete and accurate information. Analytical data will be validated as specified in

the Analytical QA Plan.

The Field Survey Lead performing oversight of breeding bird egg collection surveys will

validate that Project Scientists and Technicians are correctly identifying the proper species and

completing data forms correctly by performing periodic checks during surveys. When possible,

data collected at each nest will be validated by photographs of eggs. Because disturbance to

nesting individuals is a study concern, and a high level of disturbance could disrupt nesting study
21 March 2002

species, care will be taken to verify nesting using photographs and videos only when absolutely

necessary. The Field Survey Lead will make this determination.

Data analysis will be performed using Statistica® (StatSoft 1999). All numeric data presented in

reports will contain basic statistical properties and uncertainty. The robustness of each parameter

studied will be presented.

4.0 EQUIPMENT LIST

The following equipment will be used during the breeding bird surveys and egg collection and

processing work.

Species Surveys and Egg Collection

C Cover type maps, digital copies of georeferenced aerial photos of the study area

C Work plan

C Cell phone

C Personal identification

C Tax maps with property owner names

C Bird visual and song field guides

C 35 mm automatic camera

C Color print film ASA 200, 24 exposure, several rolls

C White, self adhering labels

C Binoculars, spotting scope

C Mirror and extension pole

C Tree top peeper and video probe systems, and head mounted display system

C Telescoping pole with padded “J” hook

C Extension or rope ladder

C Trimble global positioning system and Pro-XR data logger

C Field notebook, data forms, pencil, and sharpie marker

C Rubber knee and hip boots

C Breeding bird calls tape or CD

C Tape or CD player

C Canoe or motor boat

C Safety equipment: hardhat, climbing rope, safety glasses, leather gloves, nitrile gloves

C Aluminum foil

C Acculab V-600 balance, accurate to 0.1 gm

C Filament tape

C Padded egg carrier

C Flashlight

Egg Processing

C Nitrile gloves

C White self-adhering labels

C Chemically clean jars (4 oz) with TFE cap-liners

C Acculab V-200 balance, weighs to nearest 0.01 gm

C Distilled-deionized water

C Volumeter
22 March 2002

C Egg candler

C Kimwipes

C Aluminum foil

C Plastic bags

C Filament tape

C Laboratory balance (to 0.01 g increments)

C Vernier caliper (graduated to 0.01 mm)

C Chemically rinsed scalpel, other solvents or acids for cleaning

C Dust mask and safety glasses

C Graphite pencil and technical pen

C Federal 35 comparator with rounded contacts (graduated to 0.01 mm – estimated to

nearest 0.001 mm)

C All lab materials and equipment listed in Appendix 3

5.0 RESULTS

5.1 Breeding Bird Survey Data

Breeding bird survey results for the study areas will be presented in tables, figures and a

narrative. Details regarding the timing of surveys, conditions, general habitat features, known

levels of PCB contamination in the floodplain and prey species, and breeding bird observations

will be presented and discussed in relation to results. Survey results can be compared across

habitat types to provide insight to habitat use and possibly preferred habitat. A summary table

will include the breeding bird species observed, number of individuals, locations of observations,

and habitats at the each survey station. Maps showing the location of survey points in the study

area will be produced. Data forms will be appended to draft and final narrative reports.

5.2 Egg Data

Breeding bird egg measurement endpoints (e.g., egg mass and volume, eggshell thickness, and

contaminant concentrations) will be presented in tabular format with the appropriate descriptive

statistics. The results of the data analysis comparing groups (e.g., regional comparisons) will

also be presented in tabular format. For all statistical tests, the results will include the test

statistic value, the level of significance (alpha), and the power (beta) of the test. Data and

analytical tables will be accompanied by narrative interpretations of the data.

6.0 SCHEDULE

A detailed schedule is included in Appendix 5. Several tasks need to be sequentially performed

while others can run a parallel course. Breeding bird surveys are best completed prior to and

during the early portion of the nesting season. This period is in the early to mid spring for all six

species (Appendix 1). Habitat reconnaissance efforts and landowner contacts will occur from

early March to early May (Appendix 5). Egg collection permits from the USFWS and NYSDEC

will need to be obtained by early April. Data analysis and report preparation will occur

following the conclusion of the field effort and receipt of PCB concentration data for eggs

collected during the study. We assume tissue analysis data will be available by September 10,

2002.
23 March 2002

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Liscinsky, S.A. 1972. The Pennsylvania Woodcock Management Study. Penn. Game Comm.

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McCarty, J.P. and A.L. Secord. 1999a. Reproductive Ecology of Tree Swallows (Tachycineta

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McCarty, J.P. and A.L. Secord. 1999b. Nest-Building Behavior in PCB-Contaminated Tree

Swallows. The Auk 116:55-63.

McLane, M.A.R., E.H. Dustman, E.R. Clark, and D.L. Hughes. 1978. Organochlorine

insecticide and polychlorinated biphenyl residues in woodcock wings, 1971-72.

Pesticides Monitoring Journal 12:22-25.

McLane M.A.R., D.L. Hughes, and G.H. Heinz. 1984. Changes in levels of organochlorins in

woodcock Philohela-minor wings from 1971-1975. Environmental Monitoring &

Assessment 4(2):105-112.

McLane, M.A.R., L.F. Stickel, E.R. Clark, and D.L. Hughes. 1976. Organochlorine residues in

woodcock wings, 11 states-1970-1971. Pesticides Monitoring Journal 7:100-103.

McLane, M.A.R., L.F. Stickel, and J.D. Newsom. 1971. Organochlorine pesticide residues in

Woodcock, soils, and earthworms in Louisiana, 1965. Pesticides Monitoring Journal

5:248-250.

Miller, J.R. and J.T. Miller. 1948. Nesting of Spotted Sandpiper at Detroit, Michigan. Auk

65:558-567.

National Geographic Society. 1983. Field Guide to the Birds of North America. National

Geographic Society, Washington, D.C. 464 pp.

Nicholson, J. 1978. Forty-first Breeding Bird Census: Mixed Forest, Old Field, and Home-site.

Am. Birds. 32:72-73.

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Fish and Wildlife.

Okoniewski, J.C. and E. Novesky. 1993. Bird poisonings with cyclodienes in suburbia: Links to

historic use on turf. Journal of Wildlife Management 57:630-639.

Owen, R.B. 1977. American woodcock (Scolopax minor). Pages 149-186. In: Sanderson, G.C.

(ed.). Management of Migratory Shore and Upland Game birds in North America.

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868.

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North America. Houghton Mifflin Company, New York. 384 pp.

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Melancon, S.D. Fitzgerald, and S. J. Bursian. 1998. Effects of 3,3’,4,4’,5-

pentachlorobiphenyl and 2,3,7,8-tetrachlorodibenzo-p-dioxin injected into the yolks of

double-crested cormorant (Phalacrocorax auritus) eggs prior to incubation. Environ.

Toxicol. & Chem. 17(10):2035-2040.

Prestt, I., D.J. Jefferies, and N.W. Moore. 1970. Polychlorinated biphenyls in wild birds in

Britain and their avian toxicity. Environmental Pollution 1:3-26.

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MA. 227pp.

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Veit, R.R. and W.R. Petersen. 1993. Birds of Massachusetts. Massachusetts Audubon Society.

Lincoln, MA. 514 pp.

Walker, W. 1977. Chlorinated Hydrocarbon Pollutants in Alaskan Gyrfalcons and their prey.

Auk 94: 442-447.

Yamashita, N., T. Shimada, J.P. Ludwig, H. Kurita, M.E. Lugwig, and R. Tatsukawa. 1993.

Embryonic abnormalities and organochlorine contamination in double-crested

cormorants (Phalacrocorax auritus) and Caspian terns (Hydroprogne caspia) from the

upper Great Lakes in 1988. Environmental Pollution 79:163-173.
30 March 2002

Young, H. 1955. Breeding Behavior and Nesting of the Eastern Robin. Am. Midl. Nat.

53:329-352.

Zimmerman, G., D.R. Dietrich, P. Schmid, and C. Schlatter. 1997. Congener-specific

bioaccumulation of PCBs in different water bird species. Chemosphere 34:1379-1388.
31 March 2002

APPENDIX 1

Breeding Bird History Summary
32

Natural History Summary Information: Spotted Sandpiper, American Woodcock, Belted Kingfisher, American Robin, Red-Winged Blackbird, and Eastern Phoebe

Species Existing Studies on PCBs Egg Laying # Eggs Hatching Nesting Habitat Nesting Density Nest Location Frequency of Occurrence in Study Area 

Spottedsandpiper(Actitismacularia)

Heinz et al. 1984 May 6 - July 26.

Incubation 20 - 22days.

4 Precocial young

hatching earlyJune-July.

Edges of ponds,rivers streams, opensof freshwater bodies.

43 pairs per 17.6acres.

On the ground, depressionlined with grass oftenunder shrubs or weeds ortall grass(3 ft)

Common breederand generallythroughout theregion.

Americanwoodcock(Scolopax minor)

McLane et al.1971, 1976, 1978,1984

March 24 - June17 in NY. Mostearly to midApril. Incubation19 - 22 days.

4 Precocial young

hatching peaklate April - earlyMay.

Young forests, oldfields, low wetthickets, moistwoodlands in earlysuccession nearfields and clearings.Often alongwoodland edge or abreak in the forestcanopy.

4 - 7 males permile. 5 - 6territorial males per100 acres.

Usually within 300 ft ofdisplay area. Under a tree,brush, or weeds. Shallowdepression lined withleaves.

Common breederthroughout theregion.

Belted kingfisher(Ceryle alcyon)

Heinz et al. 1984 May 14 - June 6

in MA and May11 - June 15 inVT. Incubation23 - 24 days.

6 to 7 Altricial young

hatching June orJuly

High steep bankswithin 1 mile ofaquatic habitat withabundant forage.

1 pair per 1.8 milesq.

Horizontal burrow 3 - 6 ft.deep, within a verticalbank, often of sandycomposition.

Uncommon, butbreedingwidespreadthroughout theregion.

American robin(Turdusmigratorius)

Knupp et al. 1976;Okoniewski &Novesky 1993;Stansley & Roscoe1999; Walker1977; NYSDECNecropsy Reports

April 12 - July 25in MA. March 23- July 19 in NY.Incubation 12 - 14days.

3 to 4 Altricial young Habitat generalist,

woodlands, forests,parks, urban areas.

41 pairs per 100acres in VT.

Conifers for early nesting.White pine, maples, appletrees, shrubs. Often nearforest edge or tree fall gap.

Common andwidespread.

Red-wingedblackbird(Agelaiusphoeniceus)

Stickel et al. 1984;

Eaton and Carr1991; Kannan et al.1998; Bishop et al.1995

May 10 - June 18in MA. April 26 -July 9 in NY.Incubation 11 - 13days.

3 to 4 Altricial young Marshes, fresh and

brackish; riparianhabitats; andagricultural landsnear wetlands.

16 pairs per 100acres in marsh. 11pairs per 100 acresin upland.

Narrow, deep cup of grass,reeds, and weed rootletsattached to emergentvegetation. Sometimes inshrubs or low in trees.

Common andwidespread.

Eastern phoebe(Sayornisphoebe)

NYSDECNecropsy Reports

Mid-May to MidJuly. April 27 -Aug 15 in MA.April 20 - Aug 4in NY.Incubation 14 - 16days.

4 to 5 Altricial young Open and riparian

woodlands,agricultural areaswith scattered trees,urban areas forestedges, rocky ravines.

6 nests per 30acres, 7 pairs per1000 acres.

On or in a variety ofhuman built structures,beneath bridges, inculverts, and wells. Oftenrenovate old nests.

Common andwidespread.

Additional references: Brooks and Davis 1987; Bull 1974; Case and Hewitt 1963; Chandler 1989; Cromwell 1963; Davis 1982; DeGraaf et al. 2001; Ehrlich et al. 1988; Ellison 19

Liscinsky 1972; Miller and Miller 1948; Nicholson 1978; Owen 1977; Richards 1988; Samson 1979; Sheldon 1971; Stewart and Robbins 1958; Veit and Petersen 1993; Young 195
33 March 2002

APPENDIX 2

NYSDEC Facilities Available for Egg Processing
34 March 2002

NYSDEC Facilities Available for Egg Processing

NYSDEC Saratoga Tree Nursery

2369 Route 50

Saratoga Springs, NY 12866

Telephone: (518) 581-1439

NYSDEC Delmar Wildlife Resource Center

108 Game Farm Road

Delmar, NY 12054

Region 5 - Warrensburg Sub-Office

Upper Hudson Street Extension

P.O. Box 220

Warrensburg, NY 12885-0220

Telephone: (518) 623-1200
35 March 2002

APPENDIX 3

Egg Collection Standard Operating Procedure
36 March 2002

Protocol for Avian Egg Collection And Removal Of Contents For Contaminants Analysis

INTRODUCTION

Avian eggs are a common sample for contaminants analysis. An accurate analysis depends upon getting

the egg contents from the shell to a clean sample jar without introducing other sources of contamination.

This protocol, which has been developed and refined by many researchers over the decades, was written

for those who have minimal experience. Your first egg should be a practice egg. It is suggested that all

field personnel practice on several pen-raised quail eggs to improve technique. Chicken eggs may be

used if quail eggs are not available.

Materials and Equipment

FIELD:

 permits

 field notebook, writing instruments (pencils/pens/permanent markers)

 padded egg collection boxes (hard-sided container, e.g., Tupperware or tackle box, with foam

padding)

 square pieces of chemically-clean (Appendix A) aluminum foil, sized to wrap around egg – 1 per

egg

 small ziploc bags

 Acculab V-600 balance, weighs to nearest 0.1 gm

 labels

LAB:

 data sheets

 paper or other towels

 green scrubby or sponge

 Acculab V-200 balance, weighs to nearest 0.01 gm

 calipers

 three graduated cylinders: 250 ml, 100 ml, 50 ml (all are of sufficient diameter to insert various

sized eggs from the study).

 Chemically-clean jars, 1 per sample

9 Make sure they are cleaned for the contaminants you are sampling, e.g., I-Chem

pesticide/PCBs Series 200 or 300.

9 Size: 4 oz.

 chemically-clean stainless steel scalpel blades (No. 21 or No. 22 with No. 4 handles work well)

 chemically-clean forceps

 chemically-clean aluminum foil sheets (approximately 30 x 30 cm square), 1 per egg
37 March 2002

 sharps container for used blades or disposable scalpels

 ball-tip micrometer

PROCEDURES

FIELD:

 Collected eggs should be whole and not cracked. Collect fresh eggs if possible. Make a notation

about the probable stage of the egg as a fresh egg will float in water (Custer et al. 1992), or could

be collected from unfinished clutches. The best eggs for contaminants analysis are not cracked,

since cracking increases variation in percent moisture, and may lead to interference with or

contamination of the contents.

 In the field, wrap eggs in rinsed aluminum foil (rinsed side next to the egg). Think of the foil as a

second skin, which you are using to keep the eggshell together and the contents inside should the

egg be cracked in transit. Label appropriately (e.g. date, species identification, egg sample

number, nest number, and collector’s initials. Put label and wrapped egg in a hard container with

sufficient padding.

 Transport to lab in hard container with sufficient padding.

 Refrigerate eggs until opened, ideally no longer than 48 hrs. Egg processing will be completed

on a daily basis as much as practical.

LAB:

 Fill out egg data form (Appendix B); use one per egg.

 If debris is present, rinse egg in cool water while gently scrubbing with green scrubby or sponge.

Do not soak the egg.

 Dry and weigh whole egg.

 Take three measurements each of egg length and maximum egg width with calipers. Compute

average of three measurements for final width and length measurements.

 Measure total egg volume by water displacement. Use the graduated cylinder method that is

closest in diameter to the largest diameter of the egg. Determine the displacement volume of the

wire holding apparatus.

 Using a graduated cylinder:

1. Fill with distilled water. Note the starting volume.

2. Immerse egg using wire loops (Fig. 1a) until top of egg is just under water surface.

3. Note the final volume, subtract starting volume and holding apparatus volume, to

determine the final egg volume.
38 March 2002

 Using an egg immersion chamber:

Volume computation may be made using an egg immersion chamber. An immersion

chamber that is specially designed for smaller eggs can be made using a small syringe, i.e. 10

cc, and using a pipette for the spout. A small paper clip is used to hold the egg for immersion

into the chamber.

a. b. c.

Figure 1. Egg immersion chamber, used to determine volume of whole eggs. A: Wire loops used to

hold the egg. B: Apparatus set up to drain into beaker on balance. C: Demonstration photograph

using ripe tomato as egg. The top bend of the spigot is high enough so that an egg can be completely

immersed below it.

 Dry the egg.

 Transfer egg contents to chemically-clean jar using the following procedure:

1. Use nitrile gloves for this part of the procedure. Avoid letting contents run over your hands

into the sample jar.

2. Create a catch basin out of the aluminum foil (rinsed side up) by turning edges up and

securing the corners. This will catch egg contents in case they spill over the edge of the jar.

Use a separate piece of foil for each sample. The foil also is a clean place to place your

instruments when they are not in use.

3. Weigh the clean empty jar with lid on, and note this tare weight on data sheet.

4. Place jar in center of aluminum foil, and loosen the lid.

5. Score equator with serrated blade or scalpel blade. Use a new, chemically-clean scalpel blade

for each egg. This part takes practice. Cradle the egg in one hand (don’t squeeze too

tightly!) and gently score while rotating the egg. Many light strokes are preferable to a fewer
39 March 2002

deeper strokes, increasing the evenness of the score and decreasing the possibility of

eggshells not separating cleanly or of punching through the shell. Continue to work on your

score until you see the membrane, which usually appears gray underneath the white of the

eggshell. When you see the first bit of membrane, remove the lid from the jar so that it will

be ready as soon as you need it. Avoid getting shell dust, or anything else besides the egg

contents, in the jar. Try to expose the membrane evenly around the entire egg. Often the

score line can be used to help pick the egg shell apart using forceps.

6. Place the egg over the jar and cut through membranes with the scalpel. A new scalpel blade

should be used at this point to reduce the potential for cross contamination and since the

blade may become dull during the cutting process. The scalpel can also be used to finish

scoring down to the membranes. Pour contents into jar, or use the scalpel to gently scrape if

that is necessary. Small stainless steel scoops are also available to help remove the contents.

Use forceps to remove any shell fragments from the jar. Cover the jar. Photograph the egg

contents in the jar with the label visible and the remaining egg shell.

7. Note where the membranes are, as this is important for thickness measurements. For fresh

eggs, both membranes often stay with the shell, but as the embryo develops, the inner

membrane tends to stick with the chick. If you cannot determine where the membranes are, it

often becomes clearer after the eggshell and membranes have dried.

8. For very small eggs, there are two procedures suggested. The first option is to use a small

chemically-clean needle or scalpel to pierce a small hole at both ends of the egg. Insert a

chemically-clean syringe into the egg to withdraw the contents. Redeposit the contents into

the jar and follow the guidelines for storage and measuring the shell thickness. The second

option is to use a sharp, non-serrated scalpel and cut around the circumference at one end of

the egg. Scoop out the contents with a tiny dry chemical scoop (stainless steel) that is small

enough to fit into the egg.

9. Note that addled eggs can be full of decomposition by-products, producing gaseous

explosions at any weak point in the shell, including where you start your score or where

membranes are first exposed. Working with a refrigerated, cool egg reduces this potential,

but be prepared for egg explosions.

10. The target for the minimum weight of egg tissue is 4 grams for analysis. It may be possible

to analyze smaller samples ranging from 1 – 2 grams. Analysis of these samples may result

in a lower detection limit due to the lack of mass. An effort must be made to maximize the

amount of each sample that is usable. The weight of each sample should be made in the

laboratory during egg processing using the following procedure:
40 March 2002

a. Place a small jar on a balance that reads to at least 1 milligram and that

has been appropriately calibrated.

b. Tare the jar or record the jar weight if the balance cannot be tared.

c. Open the egg, according to the procedures referenced above and empty

the contents into the jar.

d. Record the weight, to the nearest milligram, of the egg contents if the

balance was tared. If the balance was not tared, then record the weight

for the egg contents and the jar, then subtract the previously recorded

weight of the jar. Record the weight of the egg contents in the field

notebook and on the jar label.

e. If egg is developed, estimate age of embryo. Wet weight conversion will

be made based on the weight and volume of the egg. A photographic

record of the contents of each egg will be made. Documentation of

embryo development is very limited (Powell et al. 1998; Bird et al.

1984), therefore, documenting this phase of the egg processing is

important. Note amount of decay or anything else pertinent to your

study, and examine for deformities, particularly bill deformities such as

crossed bills or lack of jaws, but also lack of skull bones, club feet,

rotated ankles, or dwarfed appendages (Gilbertson et al. 1991).

f. Repeat these procedures for any other eggs that need to be added to the

sample jar. Using these procedures, the weight of each egg's contents

will be measured, even for eggs whose contents are combined into a

single jar.

9 Do not touch or move the jar between steps 2 and 4 above. It is preferable to add the egg

contents to the jar while the jar is still on the balance, immediately after taring the jar.

 Rinse the eggshell halves with cool water and allow to air dry for 10-30 days. Label each egg

shell with the species identification code, egg number, and nest number. Store the shell pieces in

a labeled plastic bag.

 Compute conversion factor, as explained on the data sheet. Contaminant concentrations are

multiplied by this conversion factor to get volume-adjusted residue data (Stickel et al. 1973).

 Place label on jar. Place clear tape over the label to keep it from getting wet.

 Prepare Chain of Custody records and maintain egg samples under chain of custody.
41 March 2002

 Freeze samples. Ship under Chain of Custody overnight on dry ice to the sample archive or

analytical laboratory.

 After eggshells have dried, measure at three points near the equator on each shell half using balltip micrometer. If you are comparing to museum specimen thickness measurements, which

usually include the membranes, you must either include membranes or make adjustments for the

absent membranes. The data sheet (Appendix B) has adjustments for bald eagles – you can use

these as approximations or create your own adjustments by measuring shells with and without

membranes for comparisons to the study species.
42 March 2002

References

Bird, D.M, J. Gautier, and V. Montpetit. 1984. Embryonic growth of American kestrels. Auk 101:392-

396.

Custer, T.W., G.W. Pendleton, and R.W. Roach. 1992. Determination of hatching date for eggs of blackcrowned night-heron, snowy egrets, and great egrets. J. Field. Ornithol. 63:145-154.

Gilbertson, M., T. Kubiak, J. Ludwig, G. Fox. 1991. Great Lakes embryo mortality, edema, and

deformities syndrome (GLEMEDS) in colonial fish-eating birds: similarity to chick-edema disease. J.

Toxicol. Environ. Health 33:455-520.

Powell, D.C., R.J. Aulerich, R.J. Balander, K.L. Stromborg, and S.J. Bursian. 1998. A photographic

guide to the development of double-crested cormorant embryos. Colonial Waterbirds 21(3):348-355.

Stickel, L.F., S.N. Wiemeyer, L.J. Blus. 1973. Pesticide residues in eggs of wild birds: adjustment for

loss of moisture and lipid. Bull. Environ. Contam. Toxicol. 9:193-196.

These egg-processing guidelines were developed by the U.S. Fish and Wildlife Service and modified for

the project based on consultation with the author of these guidelines and on conversations with the

Quality Assurance Coordinator for this project. For more information, or to suggest additions or

clarifications, please contact:

Angela Matz

Environmental Contaminants Specialist

U.S. Fish and Wildlife Service

101-12th Ave., Box 19, Room 110

Fairbanks, AK

(907) 456-0442

(907) 456-0208 fax

angela_matz@fws.gov
43 March 2002

Appendix A: Chemically-Clean Instruments for Collecting Contaminants Samples

To minimize cross-contamination when collecting biological samples for contaminants analysis, a

primary requirement is use of chemically-clean instruments. These are made of appropriate materials

(stainless steel or teflon) and rinsed with alcohol and solvents to remove contamination and organics.

Once rinsed, the instruments should be treated as sterile instruments, e.g. not placed on unclean surfaces.

Because every laboratory situation is different, this document tells you what to do but not how to do it.

The chemicals used for rinsing are hazardous, so you should follow proper safety and laboratory protocols

when using them. This includes proper personal protective equipment (lab coats, gloves specific to the

chemical, eye protection), proper laboratory equipment and procedures (use of hood, proper storage and

disposal methods), and knowledge of chemical hazards such as flammability, reactivity, and toxicity

(MSDS required). If this is all new to you, enlist the help of a chemist to help you make the proper

decisions and reduce your risks of exposure and accident.

For organics, rinse with a reagent-grade isopropyl alcohol, air-dry, rinse with reagent-grade hexanes, and

air-dry.

Aluminum foil can be rinsed with acetone and hexane to remove organics. Air-dry, and then fold

cleaned-side in if not using immediately. The cleaned foil can be used to store samples (e.g. very large

samples or as a substitute I-Chem jar), provide a clean work surface for dissections, or to wrap cleaned

instruments for transport or storage. (The conventional wisdom is to rinse the dull side, as the shiny side

has oils on it. The oils will probably wash away with a solvent wash but why bother if you can use the

cleaner dull side to start with.)

Rinsing should be done using glass pipettes or wash bottles (made of appropriate material for the rinsing

agent). Glass funnels, wide enough to accommodate your instruments and foil sheets, are invaluable in

directing the flow of used chemicals into disposal containers or waste jars. Use disposal containers that

are the same as your source chemical containers (e.g. brown glass). Never rinse into or pour unused

chemicals back into your source chemical bottle.
44 March 2002

Appendix B. Data Sheet
45 March 2002

Avian Egg Data Sheet

Collector’s Name: _______________________ Processor’s Name ______________________

Collector’s Signature _____________________ Processor’s Signature ___________________

Species: _______________________ Photo Roll # __________ Photo Frame # ____________

Date Collected: ________ Date Transferred: _____________ Date Processed: ______________

Nest Number or location:__________________________________________________________

Egg Number or description:________________________________________________________

Nest status at time of collection:_____________________________________________________

(laying, incubating, abandoned, with chicks - how many, post-fledging, etc.)

Egg Length (three measurements, mm):_______ , _______ , ________ Average _______

Egg Width (three measurements, mm): _______ , _______ , ________ Average _______

Whole Egg Weight (g): _________

Egg Volume: Displaced H2O: volume (cm3

): __________ OR weight1 (g): ____________

Contents weight:

Weight of jar (g) : __________

Weight of jar + contents (g): __________

Weight of contents (g): __________ 

Conversion factor3

 = contents weight OR contents weight =

calc. max. egg vol displaced H2O vol. ______________

Contents condition (age of embryo, state of decay, etc.) and other comments:

_________________________________________________________________________

_________________________________________________________________________

Where are the membranes? Inner: _______________ Outer: _______________________

Eggshell thickness (mm) after > 10 days of air drying:________________

(correction for absent membranes, bald eagles: Inner = 0.03 mm, Outer = 0.13 mm)

First eggshell half: _____ ______ _____ _____ Avg: ______ Corrected: _______

Second eggshell half:_____ ______ _____ _____ Avg: ______ Corrected: _______

 Overall Avg: ______ Corrected: _______

Dry shell weight (mg) after > 10 days of air drying: ___________________

Thickness index = weight [mg]/(length)(width)[mm]: _____________

Contaminants disposition (catalog number and date submitted, etc):

_______________________________________________________________________

1

Assume 1 g H20 = 1 cm3 2 See Stickel et al. 1973. 3 If you have both, use the large
46 March 2002

APPENDIX 4

Chain of Custody Form
47 

 CHAIN OF CUSTO

CHAIN OF CUSTODY RECORD Fed E

Pack

Project Name: Project #: Container Type (e.g., padded e

carrier, cooler, etc.):

Sampler(s): Printed Name and Signature

SP-NES-NUM

Date

Collected

Time

Collected Location

Jar size

(N/A for whole

eggs) 

Special Instructions/Comments:

Signature Print Name Company/Title 

Relinquished by: Received by: Relinquished by:Received by:Relinquished by:Received by:
48 March 2002

APPENDIX 5

Schedule
Breeding Bird Egg

Exposure Study ScheduleTask

4-Feb

11-Feb

18-Feb

25-Feb

4-Mar

11-Mar

18-Mar

25-Mar

1-Apr

8-Apr

15-Apr

22-Apr

29-Apr

6-May

13-May

20-May

27-May

3-Jun

10-Jun

17-Jun

24-Jun

1-Jul

8-Jul

15-Jul

Jl

Prepare Draft Work PlanDraft Work Plan ReviewFinalize Work PlanMobilization – PermittingLandowner ContactsBreeding Bird SurveysNest Checks - Collect EggsDemobilizationData AnalysisDraft Report Preparation*Draft Report ReviewFinal Report Preparation

*Assumes validated egg tissue data are available by September 10, 2002.
Breeding Bird Egg

Exposure Study Schedule Task

5-Aug

12-Aug

19-Aug

26-Aug

2-Sep

9-Sep

16-Sep

23-Sep

30-Sep

7-Oct

14-Oct

21-Oct

28-Oct

4-Nov

11-Nov

18-Nov

25-Nov

2-Dec

9-Dec

16-Dec

23-Dec

30-Dec

Prepare Draft Work PlanDraft Work Plan ReviewFinalize Work PlanMobilization – PermittingLandowner ContactsBreeding Bird SurveysNest Checks - Collect EggsDemobilizationData AnalysisDraft Report Preparation*Draft Report ReviewFinal Report Preparation

*Assumes validated egg tissue data are available by September 10, 2002.
APPENDIX B

DATA QUALITY ASSESSMENT REPORT

AVIAN EGG EXPOSURE STUDY

DATA QUALITY ASSESSMENT REPORT

AVIAN EGG STUDY

HUDSON RIVER NATURAL RESOURCE

DAMAGE ASSESSMENT

HUDSON RIVER NATURAL RESOURCE TRUSTEES

STATE OF NEW YORK

U.S. DEPARTMENT OF COMMERCE

U.S. DEPARTMENT OF THE INTERIOR

PUBLIC RELEASE VERSION*

VERSION 2.0

AUGUST 20, 2003

Available from:

U.S. Department of Commerce

National Oceanic and Atmospheric Administration

Hudson River NRDA, Lead Administrative Trustee

Damage Assessment Center, N/ORR31

1305 East-West Highway, Rm 10219

Silver Spring, MD 20910-3281

*Names of certain individuals and affiliations have been removed to maintain confidentiality

DATA QUALITY ASSESSMENT REPORT

VERSION 2.0

HUDSON RIVER NATURAL RESOURCE DAMAGE ASSESSMENT

Avian Egg Study

Prepared for:

State of New York

Department of Environmental Conservation

U.S. Department of Commerce

National Oceanic and Atmospheric Administration

U.S. Department of Interior

Fish and Wildlife Service

August 20, 2003
i

TABLE OF CONTENTS

1.0 INTRODUCTION ......................................................................................................... 1

2.0 DATA VALIDATION PROCEDURES.......................................................................... 1

3.0 DATA QUALITY ASSESSMENT ................................................................................ 3

3.1 Holding Times and Sample Preservation .........................................................................3

3.2 Instrument Calibration........................................................................................................3

3.2.1 Initial Calibration (ICAL) ......................................................................................................3

3.2.2 Continuing Calibration (CCAL) ...........................................................................................4

3.3 GC/MS Tune.........................................................................................................................4

3.4 Blank Analyses....................................................................................................................4

3.5 Accuracy..............................................................................................................................4

3.5.1 Surrogate Compounds........................................................................................................4

3.5.2 Standard Reference Material (SRM) Analyses......................................................................5

3.5.3 Laboratory Control Samples ..................................................................................................6

3.5.4 Matrix Spike Samples ............................................................................................................6

3.5.5 Reporting Limits and Sample Results....................................................................................7

3.6 Precision..............................................................................................................................8

3.6.1 Standard Reference Material (SRM) Analyses......................................................................8

3.6.2 Laboratory Duplicate Samples...............................................................................................8

3.7 Equipment Rinsate Samples..............................................................................................9

3.8 Internal Standards...............................................................................................................9

3.9 Completeness......................................................................................................................9

3.10 Summary of Data Usability...............................................................................................10

Attachment 1 Data Validation Reports by Sample Delivery Group ..............................1A
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1

DATA QUALITY ASSESSMENT

Hudson River Natural Resource Damage Assessment

Avian Egg Study

1.0 INTRODUCTION

This report documents the results of a quality assurance review of data from avian egg samples

collected in support of the Hudson River Natural Resource Damage Assessment. The eggs were

analyzed for PCB congeners, PCB homologue groups, total PCBs, percent lipids, and percent

moisture.

A total of 220 eggs were submitted for analysis. Due to the small size of some of the eggs, several

of the eggs were composited. The total number of eggs and composites analyzed was 168, grouped

into 12 analytical batches by the laboratory. The egg tissue was prepped, extracted, and analyzed

using laboratory Standard Operating Procedures (SOPs) that were submitted and approved prior to

sample receipt.

2.0 DATA VALIDATION PROCEDURES

Data validation was based on the quality assurance/quality control (QA/QC) criteria documented

in the Analytical Quality Assurance Plan for the Hudson River Natural Resource Damage

Assessment, Version 1.0, July 9, 2002, and USEPA National Functional Guidelines for Organic

Data Review, 1999, and the following laboratory SOPs:

• SOP # HR NRDA Project Tissue Prep: Tissue Preparation and Homogenization, Revision #1.0,

9/25/02

• SOP # OP-004: Extraction of Soil, Tissue, Vegetation, and Sediment by Pressurized Fluid

Extraction, Revision #2.0, 8/15/02

• SOP # O-010: Determination of PCB Homologues and Individual Congeners by GC/MS - SIM,

Revision # 2.2, 10/24/02

• SOP # HR NRDA % Lipids: Percent Lipids Determination, Revision # 0.0, 9/9/02

• SOP # W-001: Percent Solids Determination, Revision # 2.1, 9/25/02

• Additional cleanup, sample handling, storage, custody SOPs as necessary.

Sample results and related QC data were received in both an electronic and hard copy format.

Electronic data were verified against the hard copy data package. A minimum of 80% of the data

received a full validation and the remaining data received a summary validation.
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The following QC elements were reviewed for data packages undergoing summary validation:

• Analytical holding times

• Chain of custody and sample handling

• GC/MS tune verification (from summary forms)

• Method blank contamination (from summary forms)

• Initial and continuing calibration (from summary forms)

• Rinsate blank contamination (from sample result summaries)

• Analytical accuracy: surrogates, matrix spike samples, laboratory control samples, and standard

reference material results (from summary forms)

• Analytical precision: laboratory duplicate samples (from summary forms)

• Internal standard areas (from summary forms)

• Reported detection limits (from sample result summaries)

Full validation included review of all the items listed above for summary validation, plus the

following QC elements:

• Compound identification (from raw data)

• Compound quantitation, transcription and calculation checks performed at a frequency of 10%

from raw data. If an error was noted, 100% of the calculations and transcriptions for that data

set were verified.

This report summarizes the results of data validation as they relate to the analytical data quality

objectives (ADQO) for precision, accuracy, and completeness. The report also provides a

quantitative and qualitative assessment of the data and identifies potential sources of error,

uncertainty, and bias that may affect the overall usability.

Laboratory QC samples were used to assess the effects of homogenization procedures and to

evaluate laboratory-derived contamination, laboratory performance, and sample matrix effects.

Quality control samples included: equipment rinsate blanks, method blanks, laboratory control

samples (LCS), matrix spike (MS) samples, laboratory duplicate samples, and standard reference

material (SRM) analyses. Surrogates were added to each sample analyzed for PCB congeners to

further assess the affects of sample matrix on accuracy.

Data were qualified when associated QC sample results were outside the QC limits. The following

definitions provide brief explanations of the qualifiers assigned to results in the data validation

process:
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J Estimated: The associated numerical value is an estimated quantity. The analyte was

detected, but the reported value may not be accurate or precise. The “J” qualification indicates the

data fell outside the QC limits, but the exceedance was not sufficient to cause rejection of the data.

UJ Estimated/Not detected: An analysis was performed for the compound or analyte, but it

was not detected and the sample quantitation or detection limit may be inaccurate or

imprecise. The associated numerical result is the detection limit.

NJ The analyte was tentatively identified and the associated numerical value is an estimated

quantity.

R Rejected: Unreliable result. Data should not be used.

3.0 DATA QUALITY ASSESSMENT

The data packages submitted by the laboratory were reviewed to determine whether the analytical

data quality objectives (ADQO) specified in Tables 6.1a - 6.1c in the Analytical Quality Assurance

Plan were met. Each quality control element is discussed briefly below. More details are available

in the individual data validation reports presented in ATTACHMENT 1.

3.1 Holding Times and Sample Preservation

The primary analytes of concern for this study are persistent compounds, which have been found

to remain stable in tissue after several years of storage. Due to this, no maximum holding time

criterion was established. All samples (including reanalyses) were extracted within 195 days of

collection, and all extracts were analyzed within 30 days from sample extraction. Samples were kept

frozen by the laboratory at the required temperature of -20o

C ±2oC.

3.2 Instrument Calibration

3.2.1 Initial Calibration (ICAL)

The ADQO specification for the initial calibration is that a minimum of a five point calibration

would be performed for all analytes, and that the percent relative standard deviation (%RSD) values

for all analytes are less than 20%; however, up to 10% of the analyte %RSD values can be greater

than 20% provided that all %RSD values are less than 30%.

All submitted ICAL data met the specified ADQO, and were acceptable. A six point curve was

generated for all analytes except BZ#180, which used a five point curve. No %RSD values were

greater than 30%. A total of seven %RSD values were greater than 20% (but less than 30%) in all

of the submitted ICAL. No data were qualified based on ICAL %RSD outliers.
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3.2.2 Continuing Calibration (CCAL)

The ADQO specified for the continuing (or daily) calibrations is that a CCAL must be analyzed at

the beginning and end of each analytical sequence (or every twelve hours, whichever is more

frequent), and that all percent difference (%D) values must be less than 20%. However, up to 10%

of the analyte %D values can be greater than 20% provided that all %D values are less than 30%.

Five of the CCAL did not meet the specified ADQO, in that one analyte %D value was greater than

30% in the CCAL. For these CCAL, the affected analytes were estimated (J/UJ) in the associated

samples. A total of 48 data points were estimated based on CCAL %D outliers.

All other CCAL met the ADQO requirements. In the remaining CCAL, 19 %D values were greater

than 20% (but less than 30%). No further data were qualified based on CCAL %D outliers.

3.3 GC/MS Tune

GC/MS instrument tuning verifications were performed at the proper frequency, prior to each

analytical sequence. All GC/MS tunes met the acceptance criteria specified in the laboratory

standard operating procedures.

3.4 Blank Analyses

All method blanks were acceptable, in that no target analytes were detected in any of the method

blanks. Please see Section 3.7 Equipment Rinsate Samples for a discussion of additional blank

evaluations.

3.5 Accuracy

Accuracy is evaluated by comparison of an analytical concentration to a known (true) value.

Accuracy was monitored through the use of surrogate compounds in each sample, and standard

reference material, matrix spike and laboratory control sample (blank spike) analyses. Each QC

element is discussed below. Overall, accuracy was acceptable for all avian egg analyses.

3.5.1 Surrogate Compounds

Two surrogate compounds were added to each sample prior to extraction. For the first three

laboratory analytical batches (0208031, 0208032, and 0208033), the surrogate compounds DBOB

(4,4’-dibromooctafluorobiphenyl) and BZ#198 were used. For all remaining analytical batches the

surrogate compounds 13C-BZ#19 and 13C-BZ#202 were used. The change was made to eliminate

potential interference to the octachlorobiphenyl homologue group from BZ#198, and to allow the

use of a labeled PCB congener in place of the DBOB compound.
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The ADQO specified for surrogate compounds is that all percent recovery (%R) values would be

within the 50% - 125% acceptance window. The recovery value from the late eluting surrogate

(BZ#198 or 13C-BZ#202) is used for the quantitation of the reported target analyte concentrations.

The DBOB %R values were less than 50% in 11 of the 20 analyses submitted in the first laboratory

analytical batch, 0208031. Based on these outliers, the laboratory added an additional step to the

extraction process for all subsequent packages. With one exception, all other DBOB %R values are

acceptable in packages 0208032 and 0208033.

Since the DBOB %R values are not used in sample quantitation, no action was taken unless the

BZ#198 %R value was also outside the acceptance limits. The BZ#198 %R value was low (47%) in

one sample, AR-018-026. All positive results and detection limits were estimated (J/UJ) for this

sample.

For the labeled surrogate compounds added to the 123 samples in the other 9 laboratory analytical

batches, six %R values were greater than the 125% upper control limit. The 13C-BZ#19 %R value was

elevated in Sample CG-109-112. As the 13C-BZ#202 %R value was acceptable, no action was taken.

The 13C-BZ#202 %R value was greater than 125% in Samples RB-111-113 (at 129%), EP-639-

Comp 658/659 (at 128%), RS-637-Comp 655/656 (at 134%), RB-029-041 (134%), and AW-100-

100 (at 138%). The outliers were not judged significant enough to warrant re-extraction and

reanalysis of the samples. All reported positive results were estimated (J) in these samples. A total

of 213 data points were estimated (J/UJ) based on surrogate %R outliers.

Overall, surrogate accuracy was judged acceptable. Only 20 surrogate %R values (out of 450 total

for all samples and QC analyses) were outside the 50% - 125% control limits.

3.5.2 Standard Reference Material (SRM) Analyses

A standard reference material was extracted and analyzed with each analytical batch. The SRM

selected for the Avian Egg Study was 1974a, Organics in Mussel Tissue. This SRM has certified

values for 20 PCB congeners. Two SRM analyses were submitted with laboratory batch 210059

(one was associated with several samples that were re-extracted and reanalyzed), so a total of 13

SRM analyses were performed.

The ADQO for the SRM is that the reported value must be within ±20% of the 95% confidence

interval of the true value. This ADQO was used by the laboratory to evaluate the reported results.

However, during data validation, no data were qualified unless the reported value was greater than

±25% of the 95% confidence interval.

Overall, SRM accuracy results were acceptable. A total of 10 SRM results (of 260 total) were

outside the ±20% control limit. Three of these outliers were also greater than the upper control limit

established by ±25% of the 95% confidence interval. As this may indicate a possible high bias,

positive results associated with the three SRM outliers were estimated (J). A total of 45 data points

were estimated based on SRM outliers.
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Tables 1A and 1B summarize the SRM results for this study.

3.5.3 Laboratory Control Samples

The laboratory performed LCS analyses at the required frequency of one for every 15 samples or

analytical batch, whichever was more frequent. The ADQO for the LCS analyses is that all %R

values must be within the acceptance limits of 75% to 125%; however, if only one analyte %R value

is outside the control limits, the laboratory is not required to re-extract the associated samples.

A total of 15 LCS analyses were submitted with the avian egg samples. Each LCS included 48

target analytes, for a total of 720 data points.

For all LCS analyses, 19 %R values were outside the 75% - 125% control limits. All but three

outliers were less than the lower control limits (ranging from 62% to 74%), indicating a possible low

bias. Target analytes associated with a low LCS %R value were estimated (J/UJ) in all samples in

the same analytical batch. For the elevated LCS %R values (ranging from 126% - 139%), only the

associated positive results were estimated (J) due to the potential high bias.

A total of 271 data points were estimated (J/UJ) based on LCS %R outliers. Overall, LCS accuracy

was acceptable.

3.5.4 Matrix Spike Samples

The laboratory was to perform MS analyses at the required frequency of every 15 samples or

analytical batch, provided that sufficient sample was available for a MS. This was not always the

case; only 7 MS analyses were submitted. Each MS sample included 48 spiked analytes, for a total

of 336 data points. The ADQO for MS analyses is that all %R values should be within the 50% to

125% control limits.

Fifty of the MS %R values were less than 50%, ranging from 0% to 46%. However, 35 of these

outliers were in the MS submitted with laboratory batch 0208033, performed using Sample BK-506-

507. High levels of target analytes were present in this sample, and most of the concentrations in

the parent sample were greater than five times the spike concentration. Due to this, the MS in

laboratory batch 0208033 was judged not applicable and was not used to evaluate the associated

samples. Target analytes associated with MS %R values less than the 50% lower control limit were

estimated (J/UJ) in the parent sample only. One data point (the detection limit for BZ#169 in

Sample SS-238-244) was associated with a 0% recovery value in the MS analysis. This data point

was rejected (R) due to the potential low bias.
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For elevated %R values, 26 %R values were greater than 125%, ranging from 127% to 300%. Many

of these outliers (9) were in the MS submitted with laboratory batch 0209048. The parent sample

(SS-238-244) also contained high levels of target compounds, which affected the reported %R

values.

For MS %R outliers, no action was taken unless the %R values were outside the 50% to 125%

control limits; and the concentration in the parent sample was less than 5 times the concentration of

the MS spike solution. Qualifiers were issued only to the target analyte in the parent sample

associated with the MS %R outlier. A total of 21 data points were estimated (J/UJ). One data point

(the detection limit for BZ#169 in Sample SS-238-244) was rejected (R) due to a 0% recovery value

in the MS analysis.

3.5.5 Reporting Limits and Sample Results

Method detection limits (MDLs) were determined using low level spikes on chicken eggs following

procedures outlined in the US Code of Federal Regulations (40 CFR Part 136, Appendix B). The

detection limits for target congeners were generally in the range of 0.04 μg/Kg to 0.30 μg/Kg. There

were 11 target congeners with MDL values greater than the 0.1 μg/Kg target MDL. Of these, only

one congener MDL value was greater than 0.3 μg/Kg: PCB congener BZ#169 MDL was elevated

at 2.21 μg/Kg due to interferences which could not be resolved using the specified method.

The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.

Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.

The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21).

Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable. All other

reported results were judged to be accurate unless qualified for some other reason.
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3.6 Precision

Precision is evaluated through replicate analyses of a sample. For the avian egg study, a SRM and

a laboratory duplicate were analyzed with each analytical batch. No field duplicates were submitted.

Overall, precision was judged as acceptable for all avian egg analyses.

3.6.1 Standard Reference Material (SRM) Analyses

Section 3.5.2 describes the frequency and criteria for the SRM analyses performed with each

analytical batch. The results for the SRM analyses are summarized in Tables 1A and 1B.

Out of 13 SRM analyses, results for three data points were greater than 25% from the 95%

confidence interval for an individual congener. The outliers were for each of the following

congeners: BZ#101, BZ#118, and BZ#128. The positive results associated with the three SRM

outliers were estimated (J). A total of 45 data points were estimated based on these SRM outliers.

The overall percent difference from the certified values for the SRM results ranged from 0.03%D

to 26.3%D for each of the congeners, indicating good overall precision among analytical batches.

3.6.2 Laboratory Duplicate Samples

For samples with positive results greater than or equal to five times the method detection limit, the

AQDO specified relative percent difference (RPD) control limit for laboratory duplicates is 30%.

Ten laboratory duplicates were submitted. The duplicate was lost (due to a spill during the

extraction procedure) in laboratory batch 0209046, and no duplicate was performed for laboratory

batch 0210059 due to limited sample size.

Table 2 summarizes the results of the laboratory duplicate analyses. For the PCB congeners, a total

of 93 RPD values (out of 422 possible) were greater than 30%. However, most of the outliers (70)

were from two of the duplicate analyses, those performed with laboratory batches 0208033 and

0209043. The high number of outliers in these two samples indicates a homogenization problem

specific to those samples. Overall, laboratory precision is acceptable.

For percent lipids and percent moisture analyses, the RPD control limit is 15%. One percent

moisture RPD value is greater than 15% (at 51%). This outlier is associated with laboratory batch

0208033, which also has multiple PCB congener RPD value outliers. For percent lipids, 6 of the

RPD values are greater than 15%. One RPD value (65%) is associated with laboratory batch

0209043, which also has multiple PCB congener RPD value outliers. The remaining 5 percent lipids

RPD value outliers range from 20% to 24%. This may indicate that homogenization of egg tissue

is difficult, and a higher ADQO (such as 30%) may be more appropriate for the percent lipids.

Target analytes associated with RPD outliers were estimated (J) in the parent sample. A total of 108

values were estimated due to laboratory precision outliers.
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3.7 Equipment Rinsate Samples

A total of 8 equipment rinsate blanks were collected. The rinsate blanks were prepared by rinsing

the equipment used to homogenize the egg samples, and analyzing the rinsate as a sample. The eggs

from the first several packages were manually homogenized (using spatulas), and rinsate blanks

were not collected.

Positive results for 62 analytes and/or homologue groups were reported in the 8 rinsate blanks (of

496 possible results). However, the majority of the positive results (48) were present in the rinsate

blank submitted with laboratory batch 0209043. It was determined that this rinsate blank was cross

contaminated by the LCS during an extract transfer step of the extraction process. Due to this, the

rinsate blank from laboratory batch 0209043 was not used to evaluate the associated samples.

The remaining positive results were all at very low concentrations, ranging from 0.06 μg/Kg to

0.956 μg/Kg. Action levels were established at five times the concentrations reported in the rinsate

blanks. All results in the associated samples were greater than the action levels, so no qualification

of the data were necessary.

3.8 Internal Standards

Internal standards were added to each field and QC sample prior to injection onto the analytical

instrument. The ADQO for internal standards is that the area of the internal standards in each

analysis must be within ±50% of the area of the internal standard in the associated CCAL.

Seven internal standard areas were less than the 50% (of the area in the associated CCAL) lower

control limit. For internal standard area outliers, all associated target analytes are estimated (J). A

total of 354 data points were estimated (J/UJ) based on internal standard outliers.

3.9 Completeness

Out of 10,248 results reported by the laboratory (168 samples, each with 48 congeners, ten

homologue groups, total PCBs, percent lipids and percent moisture), a total of 1,016 (9.91%) data

points were qualified as estimated (J/UJ), and 110 data points were tentatively identified due to

potential interferences. One data point was rejected. The completeness level attained for the

analysis of the field samples is greater than 99.99%.

Due to the need for dilutions or reanalyses due to QC outliers, multiple data sets were provided for

some of the samples. As part of the data validation process, the data were reviewed to determine

which set of data would provide the data user with data of the highest possible quality. To designate

which data (of multiple data) should not be used, the data were flagged as do-not-report (DNR). All

data flagged DNR were removed from the database provided to the data users.
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As a usable data point still exists for all analytes in the affected samples, the completeness was not

affected.

3.10 Summary of Data Usability

A total of 1,016 out of 10,248 results were estimated because of laboratory accuracy and

precision outliers, continuing calibration percent difference outliers, and internal standard area

outliers. A total of 110 data points were tentatively identified due to potential interferences.

One data point was rejected based on an accuracy outlier. The rejected data point should not be

used for any purpose. For all other data, the overall quality of the data is acceptable and all

results, as qualified, are considered usable.
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ATTACHMENT 1

Data Validation Reports

by Sample Data Group (SDG)
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1-A

DATA VALIDATION REPORT - FULL REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 020831

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory. The laboratory followed adequate

corrective action processes, and all anomalies were discussed in the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check Standard Reference Material (SRM)

Initial Calibration (ICAL) * Laboratory Duplicate

Continuing Calibration (CCAL) * Internal Standards

Blanks Compound Identification

* Surrogate Compounds * Calculation Verification

* Matrix Spike (MS) * Reporting Limits and Sample Results

* Laboratory Control Samples (LCS) EDD Transcription Check

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Surrogate Compounds

The percent recovery (%R) values of the 4,4’-dibromooctafluorobiphenyl (DBOB) surrogate were

less than the 50% lower control limit in 11 of the 20 analyses. No action was taken unless the %R

value for the BZ#198 surrogate was also outside the control limits.

The %R value of the BZ#198 surrogate in Sample AR-018-026 (47%) was less than the 50% lower

control limit. The DBOB %R value was also less than the 50% lower control limit, at 42%.

Because the surrogate %R values did not meet the specified acceptance criteria, all positive values

and reporting limits were estimated (J/UJ) in Sample AR-018-026.
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Matrix Spike (MS)

Matrix spike analysis was performed using Sample AR-023-034. The %R values of congeners

BZ#138 (22%) and BZ#153 (12%) were less than the 50% lower control limit. As the recovery

values for these congeners were acceptable in both the LCS and SRM analysis, and as no trend was

noted (the recovery values for these compounds are acceptable in most of the MS analyzed with the

bird eggs in other laboratory batches), no action was taken.

Laboratory Control Sample (LCS)

The %R value of congener BZ#194 (129%) in the LCS was greater than the upper control limit of

125%. Although the BZ#194 recovery was acceptable in the matrix spike, this congener is not in

the SRM, so it is not possible to confirm whether the LCS outlier was an isolated event. Due to the

potential high bias, positive values for BZ#194 were estimated (J) in the samples. No action was

taken for BZ#194 non-detects.

Laboratory Duplicate

The relative percent difference (RPD) values for congeners BZ#66 (51%), BZ#201 (36%) and the

octachlorobiphenyl homolog group (81%) were greater than the 30% control limit. The

concentrations were estimated (J) in the parent sample, AR-024-035.

Internal Standards

The areas of the internal standard chrysene-d12 were less than the 50% control limit in the following

samples:

AR-007-011 AR-010-015

AR-023-034 AR-024-035 DUP

AR-101-101 AR-107-110

AR-202-203

The area of this internal standard is part of the calculation used to determine the concentration of

all target analytes. All positive values in the above samples were estimated (J), and reporting limits

were estimated, (UJ).

Calculation Verification

Reported results were verified by recalculation, and no errors were found.

Congener BZ#209 is the only congener in the decachlorobiphenyl homolog group. However, the

reported values for the decachlorobiphenyl homolog group do not always equal the reported values
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for congener BZ#209. This is a result of the instrument software integrating the BZ#209 peak twice,

once as BZ#209, and once as the 'calibration congener' for the decachlorobiphenyl homolog group.

At low concentrations, the peak shape is slightly irregular, causing the software to arrive at different

areas for the peak when the integrations are performed. As the differences between the BZ#209 and

decachlorobiphenyl concentrations are not significant, no action was taken.

Reporting Limits and Sample Results

The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference, but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.

Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.

The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21). PCB Congener BZ#126 was reported as detected in three samples and was

qualified NJ.

Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable.
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III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS),

standard reference material (SRM), and matrix spike (MS) percent recovery values, with the

exceptions noted above. Precision was acceptable as demonstrated by the relative percent difference

values for the duplicate analyses, with the exceptions noted above.

Data were estimated due to internal standard recoveries, surrogate recoveries, laboratory control

sample recoveries, and laboratory duplicate precision outliers. Data were qualified as tentatively

identified due to interference.

All data, as qualified, are acceptable for use.
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DATA VALIDATION REPORT - FULL REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0208032

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory, with the following exceptions. The

instrument tune summary associated with the 9/13/02 initial calibration was not submitted, and the

concentration of the solution spiked into the matrix spike sample was not reported. The necessary

information was available in the raw data. No further action was taken. The laboratory followed

adequate corrective action processes, and all anomalies were discussed in the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check * Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

* Continuing Calibration (CCAL) Internal Standards

Blanks Compound Identification

* Surrogate Compounds * Calculation Verification

Matrix Spike (MS) * Reporting Limits and Sample Results

Laboratory Control Samples (LCS) EDD Transcription Check

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Initial Calibration (ICAL)

In both the 09/12/02 and 09/13/02 ICAL the low (0.25 μg/L) point was dropped for BZ#180. Six

calibration points were still used for this congener, BZ#180 was detected in all samples, and all

concentrations were greater than the lowest calibration point used. No action was necessary.
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Continuing Calibration (CCAL)

The percent difference (%D) value for BZ#174 (at 24.7%) was outside the ±20% control limit in the

CCAL analyzed 9/13/02 at the beginning of the analytical sequence. The %D value for this

compound was less than 25% and was acceptable in the end-of-sequence CCAL, so no action was

taken.

The %D values for BZ#18 (22.9%), BZ#45 (23.7%), BZ#49 (22.2%), and BZ#52 (20.8%) were

outside the ±20% control limit in the end-of-sequence CCAL analyzed 9/13/02. All %D values were

less than 25% and were acceptable in the beginning CCAL, so no action was taken. The laboratory

case narrative notes that a new initial calibration was analyzed after this CCAL.

The %D value for BZ#28 (at 36.5%) was greater than the ±20% control limit in the CCAL analyzed

at the end of the 09/13/02 sequence. The only samples analyzed in this sequence were dilutions, and

the concentration of BZ#28 was reported from the undiluted analyses. No action was taken.

Surrogate Compounds

The percent recovery (%R) value of the 4,4’-dibromooctafluorobiphenyl (DBOB) surrogate was less

than the 50% lower control limit for Sample AR-504-505. No action was taken as the %R value for

the BZ#198 surrogate was acceptable.

Standard Reference Material (SRM)

The reported concentrations for BZ#149 and BZ#153 were outside the acceptance window [±20%

of the 95% confidence interval]. For BZ#149, the reported value was 7.69 μg/kg, and the lower

control limit is 7.77 μg/kg. For BZ#153, the reported value was 12.1 μg/kg, and the lower limit is

12.54 μg/kg.

Due to the outliers, the SRM was reanalyzed. In the reanalysis, the concentrations for BZ#149 and

BZ#153 were acceptable, however, the concentrations for BZ#66 and BZ#170 were less than the

lower control limits.

The recoveries of all compounds were acceptable in the LCS and MS analyses. No trend was noted

for these compounds (i.e., the concentrations were acceptable in most of the SRM analyzed with the

egg samples). The precision for these compounds were acceptable in the laboratory duplicate. All

outliers were within a ±25% acceptance window. The outliers were judged isolated incidents, and

no action was taken.
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Laboratory Duplicate

The relative percent difference (RPD) values for congeners BZ#74 (33%), BZ#138 (39%), and

BZ#158 (34%) were greater than the control limit of 30%. The concentrations were estimated (J)

in the parent sample, AR-505-506.

The RPD value for the sample and laboratory duplicate percent lipids determination exceeds the

control limit of 15%, at 22.6%. The lipids result was estimated (J) in Sample AR-505-506.

Calculation Verification

Reported results were verified by recalculation, and no errors were found.

Congener BZ#209 is the only congener in the decachlorobiphenyl homolog group. However, the

reported values for the decachlorobiphenyl homolog group do not always equal the reported values

for congener BZ#209. This is a result of the instrument software integrating the BZ#209 peak twice,

once as BZ#209, and once as the 'calibration congener' for the decachlorobiphenyl homolog group.

At low concentrations, the peak shape is slightly irregular, causing the software to arrive at different

areas for the peak when the integrations are performed. As the differences between the BZ#209 and

decachlorobiphenyl concentrations are not significant, no action was taken.

Reporting Limits

The concentrations of several congeners were greater than the instrument linear range in Samples

AR-210-211 and AR-209-210. The samples were reanalyzed as dilutions, and the concentrations

were within the linear range. Both analyses were reported.

To avoid reporting multiple results for these samples, the congeners (and the associated homolog

groups) with concentrations that exceeded the linear range of the instrument in the original analysis

were flagged as do-not-report (DNR). The results for these congeners should be reported from the

dilution analyses. All other results in the dilution analyses were also flagged DNR.

The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.

Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.
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The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives, or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21). PCB Congener BZ#81 was reported as detected in three samples and was

qualified NJ.

Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable.

III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS), matrix

spike (MS) and standard reference material (SRM) percent recovery values, with the exceptions

noted above. Precision was acceptable as demonstrated by the relative percent difference values for

the duplicate analyses, with the exceptions noted above.

Data were estimated due to laboratory duplicate precision outliers. Data were qualified as

tentatively identified due to interference. Data were qualified as do-not-report (DNR) due to

concentrations exceeding the linear range of the instrument, and to designate which result (of

multiple results) should be reported.

All data, as qualified, are acceptable for use.
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DATA VALIDATION REPORT - FULL REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0208033

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory, with the following exception. The

instrument tune summary associated with the 9/13/02 and 9/20/02 initial calibrations were not

submitted. The necessary information was available in the raw data. No further action was taken.

The laboratory followed adequate corrective action processes, and all anomalies were discussed in

the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check * Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

* Continuing Calibration (CCAL) Internal Standards

Blanks Compound Identification

Surrogate Compounds Calculation Verification

* Matrix Spike (MS) * Reporting Limits and Sample Results

* Laboratory Control Samples (LCS) EDD Transcription Check

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.
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Initial Calibration (ICAL)

In the 09/13/02, 09/20/02, and 09/30/02 ICAL the low (0.25 μg/L) point was dropped for BZ#180.

Six calibration points were still used for this congener, BZ#180 was detected in all samples, and all

concentrations were greater than the lowest calibration point used. No action was necessary.

The data quality objective (DQO) for initial calibrations specified in the Analytical Quality Assurance

Plan (AQAP) is that up to 10% of the analytes may have a percent relative standard deviation

(%RSD) values greater than 20%, but less than 30%. In the 09/20/02 ICAL, the %RSD value for

BZ#8 is 28.8%. In the 09/30/02 ICAL the %RSD values for BZ#28 (23%), BZ#118 (21.4%), and

BZ#167 (21.1%). No action was taken, as the DQO were met for each ICAL.

Continuing Calibration (CCAL)

The CCAL DQO stated in the AQAP is that up to 10% of the analytes may have a percent difference

(%D) value that is greater than 20%, provided that all %D values are less than 30%. All %D values

were acceptable, with the following exceptions:

The %D value for BZ#28 (at 36.5%) was greater than the ±20% control limit in the end-of-sequence

CCAL analyzed 09/13/02. Concentrations and reporting limits for BZ#28 were estimated (J/UJ) in

the associated samples.

The %D values for BZ#8 (at 32.5%) and BZ#174 (at 24.9%) were greater than the ±20% control

limit in the opening CCAL analyzed 09/20/02. The %D values for BZ#8 (at 29.7%) and BZ#70 (at

25.4%) were greater than the ±20% control limit in the end-of-sequence CCAL analyzed 09/21/02.

These CCAL are associated with the dilution analyses only. BZ#8, BZ#70, and BZ#174 are not

reported from the dilutions. No further action was necessary.

The %D value of BZ#118 (20.5%) was greater than the control limit of ±20% in the opening CCAL

on 09/30/02. In the end-of-sequence CCAL, the %D values of BZ#28 (22.3%), BZ#118 (24.6%),

and BZ#167 (20.4%) were greater than the control limit of ±20%. All %D value outliers were less

than 30%. These CCAL are associated with re-analyses that were not used. See the Laboratory

Duplicate section for more details. No further action was necessary.

Matrix Spike

A matrix spike (MS) was performed on Sample BK-506-507. Due to the high levels of congeners

present in the parent sample, most of the percent recovery (%R) values in the MS were below the

50% lower control limit or were not applicable (since the concentration in the parent sample was

greater than the concentration in the MS analysis). Although there were also outliers for congeners

that were not present in the parent sample at high concentrations (greater than 5x the concentration

spiked into the sample), these congeners usually closely eluted to a high concentration congener.
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Due to the large number of congeners present at high concentrations, the MS was judged not

applicable, and was not used to evaluate the associated samples.

No MS was performed with the re-extraction batch due to insufficient sample volume.

Laboratory Control Sample (LCS)

All percent recovery (%R) values were acceptable in the LCS associated with the 9/02/02 extraction

batch. For the 9/25/02 extraction batch, the %R value of BZ#114 was greater than the upper control

limit of 125%, at 139%. No samples associated with this extraction set were reported, so no action

was taken. See the Laboratory Duplicate section for further details.

Standard Reference Material (SRM)

The reported concentration of BZ#170 was outside the acceptance window [±20% of the 95%

confidence interval] in the SRM analyzed with the 09/02/02 extraction batch, with a reported value

of 0.385 μg/Kg and a lower control limit of 0.41 μg/Kg. The result is within a ±25% acceptance

window (lower control limit is 0.380 μg/Kg). The analyte was not recovered in the MS due to a

high concentration in the native sample. The LCS recovery value was acceptable. No trend was

noted, in that the BZ#170 concentration is acceptable in most of the SRM analyzed with the egg

samples. The outlier was judged an isolated incident, and no action was taken.

No SRM was analyzed with the 09/25/02 re-extraction batch.

Laboratory Duplicate

A laboratory duplicate was performed on Sample AR-509-511. The relative percent difference

(RPD) values for most of the individual PCB congeners and all of the homolog groups were greater

than the 30% control limit. The concentrations of all outliers were estimated (J) in the parent

sample.

The RPD between sample and duplicate for the percent lipid determination exceeded the control

limit of 15%, at 51%. A comparison of the lipids values for the MS and parent sample (BK-506-

507) resulted in an RPD value of 44%. Due to the elevated lipids RPD values, the laboratory reextracted five of the samples (BK-114-116, BK-214-216, BK-215-217, BK-216-218, and BK-506-

507) using a different homogenization method (homogenizing using a Hamilton Beach Drink Master

mixer, rather than chopping with a spatula). The five samples were reanalyzed for both lipids and

PCB congeners.

For three of the five samples, the lipids values were lower in the re-extracts, with RPD values

(compared to the original analyses) ranging from 0.25 to 60.5%. However, a comparison of lipids

values for all of the belted kingfisher (BK) samples indicates that for this species, the percent lipids
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value typically falls between 8% and 9.7%. The re-extract lipids values ranged from 4.7% to 8.05%.

Two of the re-extract lipids values confirmed the original analysis results (RPD values less than

10%). The results for the congeners were also lower in the re-extracted samples.

Since several of the re-extract lipids results are not consistent with the results for other eggs from

the same species, and since no MS or SRM was analyzed with the re-extracts, all re-extract results

were flagged do-not-report (DNR). The original analysis results (for lipids and PCB congeners)

should be reported.

Due to the elevated RPD value for the lipids in the original laboratory duplicate, the lipids result in

Sample AR-509-511 was estimated (J).

The RPD value for the percent moisture determination in the laboratory duplicate was 51%. The

percent moisture value was estimated (J) in Sample AR-509-511.

Reporting Limits

The concentrations of several congeners were greater than the instrument linear range in Samples

BK-114-116 and BK-214-216. The samples were reanalyzed as dilutions, and the concentrations

were within the linear range. Both analyses were reported.

To avoid reporting multiple results for these samples, the congeners (and the associated homolog

groups) with concentrations that exceeded the linear range of the instrument in the original analysis

were flagged as do-not-report (DNR). The results for these congeners should be reported from the

dilution analyses. All other results in the dilution analyses were also flagged DNR.

The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.

Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.

The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21). PCB Congener BZ#77 was reported as detected in six samples, BZ#81 was

reported as detected in five samples, and BZ#126 was reported as detected in one sample. These

results were qualified NJ.
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Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable.

III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS), and

standard reference material (SRM) percent recovery values, with the exceptions noted above.

The precision as indicated by the RPD values in the laboratory duplicate was not acceptable.

However, it is possible that the precision outliers were an isolated incident specific to that duplicate

analysis. To evaluate overall laboratory precision, %RSD values were calculated for the surrogate

recoveries. The %RSD values were less than 15%, indicating that the overall precision was

acceptable. Precision could not be evaluated for the 09/25/02 extraction batch.

Data were estimated due to laboratory duplicate precision outliers and continuing calibration

outliers. Data were qualified as tentatively identified due to interference. Data were qualified as

do-not-report (DNR) due to concentrations exceeding the linear range of the instrument, and to

designate which result (of multiple results) should be reported.

Data qualified as do-not-report should not be used for any purpose.

All other data, as qualified, are acceptable for use.
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DATA VALIDATION REPORT - FULL REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0208034

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory. The laboratory followed adequate

corrective action processes, and all anomalies were discussed in the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check * Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

* Continuing Calibration (CCAL) Internal Standards

* Blanks Compound Identification

* Surrogate Compounds Calculation Verification

* Matrix Spike (MS) * Reporting Limits and Sample Results

Laboratory Control Samples (LCS) EDD Transcription Check

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Initial Calibration (ICAL)

In the 09/20/02, 09/25/02, and 09/30/02 ICAL the low (0.25 μg/L) point was dropped for BZ#180.

Six calibration points were still used for this congener, BZ#180 was detected in all samples, and all

concentrations were greater than the lowest calibration point used. No action was necessary.
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In the 09/25/02 ICAL, the 2 highest concentration points were dropped for congeners BZ#126 and

BZ#169. Five calibration points were still used, and there were no positive values for these

compounds in the associated samples.

The data quality objective (DQO) for initial calibrations specified in the Analytical Quality Assurance

Plan (AQAP) is that up to 10% of the analytes may have a percent relative standard deviation

(%RSD) values greater than 20%, but less than 30%. In the 09/20/02 ICAL, the %RSD value for

BZ#8 is 28.8%. In the 9/25/02 ICAL, the %RSD value for BZ#87 is 20.7%. In the 09/30/02 ICAL

the %RSD values for BZ#28 (23%), BZ#118 (21.4%), and BZ#167 (21.1%). No action was taken,

as the DQO were met for each ICAL.

Continuing Calibration (CCAL)

The CCAL DQO stated in the AQAP is that up to 10% of the analytes may have a percent difference

(%D) value that is greater than 20%, provided that all %D values are less than 30%. All CCAL met

the DQO. All %D values were acceptable, with the following exceptions:

The %D values for BZ#8 (at 32.5%) and BZ#174 (at 24.9%) were greater than the ±20% control

limit in the opening CCAL analyzed 09/20/02. The %D values for BZ#8 (at 29.7%) and BZ#70 (at

25.4%) were greater than the ±20% control limit in the end-of-sequence CCAL analyzed 09/21/02.

These CCAL are associated with the dilution analyses only. The %D outliers for BZ#8 indicate a

possible high bias. BZ#8 was not detected in any associated sample, no action was necessary.

There are outliers for BZ#70 and BZ#174 in only one of the two CCAL. No action was taken.

The %D values for BZ#31 are outside the control limits in both CCAL analyzed on 9/25/02 and

9/26/02, at 25% and 24.5%. Although the DQO was met, the presence of a calibration outlier in

both the opening and end-of-sequence CCAL indicates a possible bias for this congener. All BZ#31

results were estimated (J) in the associated samples.

The %D value of BZ#118 (20.5%) was greater than the control limit of ±20% in the opening CCAL

on 09/30/02. In the end-of-sequence CCAL, the %D values of BZ#28 (22.3%), BZ#118 (24.6%),

and BZ#167 (20.4%) were greater than the control limit of ±20%. All %D value outliers were less

than 30%. These CCAL are only associated with a SRM analysis, no action was necessary.

Blanks

A rinsate blank from the sample homogenizer was analyzed with this batch. Positive values were

reported for a number of PCB congeners. However, all samples had positive values for these

congeners at concentrations greater than the action levels. No action was taken.
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Surrogate Compounds

The %R value of BZ#19-C13 in Sample CG-109-102 was greater than the upper control limit of

125%, at 126%. The %R values of the BZ#202-C13 surrogate was acceptable in all samples. No

action was taken.

Matrix Spike (MS)

Due to a laboratory error, no MS was associated with this SDG. Accuracy was evaluated using the

surrogate recovery values, and the LCS and SRM results.

Laboratory Control Sample (LCS)

The percent recovery (%R) value of BZ#74 (69%) was less than the lower control limit of 75% in

the LCS extracted 09/12/02. The concentration of BZ#74 was estimated (J) in all associated

samples.

Standard Reference Material (SRM)

Two SRM were reported. All results in the SRM extracted 9/12/02 were acceptable.

For the SRM extracted 9/16/02, the reported concentrations for BZ#118 and BZ#128 were greater

than the upper control limits of the acceptance window [±20% of the 95% confidence interval]. The

BZ#118 value was 19.6 μg/Kg, with an upper control limit of 18.36 μg/Kg, and the BZ#128 value

was 3.6 μg/Kg, with an upper control limit of 3.47 μg/Kg. The BZ#118 value was also outside a

±25% control limit, which has an upper control limit of 19.1 μg/Kg. The BZ#128 value was within

a ±25% control limit (upper control limit is 3.61 μg/Kg).

The accuracy for both compounds was acceptable in the LCS; the precision for both compounds was

acceptable in the laboratory duplicate. No trend was noted, in that the BZ#118 and BZ#128

concentrations are acceptable in most of the SRM analyzed with the egg samples. The outliers were

judged an isolated incident, and no action was taken.

Laboratory Duplicate

The relative percent difference (RPD) values for congeners BZ#31 (33%), BZ#47 (32%), BZ#114

(32%), BZ#170 (32%), pentachlorobiphenyls (36%), and nonachlorobiphenyls (31%) were greater

than the control limit of 30%. The concentrations were estimated (J) in the parent sample, BK-506-

508.
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The RPD value for the sample and laboratory duplicate percent lipids determination exceeds the

control limit of 15%, at 22.4%. The lipids result was estimated (J) in Sample BK-506-508.

Reporting Limits and Sample Results

The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.

Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.

The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives, or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21). PCB Congeners BZ#81 and BZ#126 were reported as detected in two

samples and were qualified NJ.

Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable.

III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS) and

standard reference material (SRM) percent recovery values, with the exceptions noted above.

Precision was acceptable as demonstrated by the relative percent difference values for the duplicate

analyses, with the exceptions noted above.

Data were estimated due to laboratory duplicate precision outliers, CCAL %D outliers, and percent

recovery outliers in the laboratory control sample. Data were qualified as tentatively identified due

to interference.

All data, as qualified, are acceptable for use.
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DATA VALIDATION REPORT - FULL REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0209038

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory. The laboratory followed adequate

corrective action processes, and all anomalies were discussed in the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check * Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

* Continuing Calibration (CCAL) Internal Standards

* Blanks Compound Identification

Surrogate Compounds Calculation Verification

* Matrix Spike (MS) Reporting Limits and Sample Results

Laboratory Control Samples (LCS) EDD Transcription Check

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Initial Calibration (ICAL)

In the 09/25/02 and 09/30/02 ICAL the low (0.25 μg/L) point was dropped for BZ#180. Six

calibration points were still used for this congener, BZ#180 was detected in all samples, and all

concentrations were greater than the lowest calibration point used. No action was necessary.
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In the 09/25/02 ICAL, the 2 highest concentration points were dropped for congeners BZ#126 and

BZ#169. Five calibration points were still used, and there were no positive values for these

compounds in the associated samples.

The data quality objective (DQO) for initial calibrations specified in the Analytical Quality Assurance

Plan (AQAP) is that up to 10% of the analytes may have a percent relative standard deviation

(%RSD) values greater than 20%, but less than 30%. In the 9/25/02 ICAL, the %RSD value for

BZ#87 is 20.7%. In the 09/30/02 ICAL the %RSD values for BZ#28 (23%), BZ#118 (21.4%), and

BZ#167 (21.1%). No action was taken, as the DQO were met for each ICAL.

Continuing Calibration (CCAL)

The %D values for BZ#31 are outside the control limits in both CCAL analyzed on 9/25/02 and

9/26/02, at 25% and 24.5%. Although the DQO was met, the presence of a calibration outlier in

both the opening and end-of-sequence CCAL indicates a possible bias for this congener. All BZ#31

results were estimated (J) in the associated samples.

The %D value of BZ#118 (20.5%) was greater than the control limit of ±20% in the opening CCAL

on 09/30/02. In the end-of-sequence CCAL, the %D values of BZ#28 (22.3%), BZ#118 (24.6%),

and BZ#167 (20.4%) were greater than the control limit of ±20%. All %D value outliers were less

than 30%. These CCAL are only associated with a SRM analysis, no action was necessary.

Blanks

A rinsate blank from the sample homogenizer was analyzed with this batch. Positive values were

reported for a number of PCB congeners. However, all samples had positive values for these

congeners at concentrations greater than the action levels. No action was taken.

Matrix Spike (MS)

A matrix spike was performed on Sample EB-008 comp-012/013. The percent recovery (%R)

values for twelve congeners were greater than the 125% upper control limit. The high recovery

equates to a high bias in the sample. Positive results for the congeners associated with %R value

outliers were estimated (J) in the parent sample. No action was taken for non-detects associated with

an outlier.

Standard Reference Material (SRM)

The reported concentrations for BZ#118 and BZ#128 were greater than the upper control limits of

the acceptance window [±20% of the 95% confidence interval]. The BZ#118 value was 19.6 μg/Kg,

with an upper control limit of 18.36 μg/Kg, and the BZ#128 value was 3.6 μg/Kg, with an upper

control limit of 3.47 μg/Kg. The BZ#118 value was also outside a ±25% control limit, which has
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an upper control limit of 19.1 μg/Kg. The BZ#128 value was within a ±25% control limit (upper

control limit is 3.61 μg/Kg).

The accuracy for both compounds was acceptable in the LCS; the precision for both compounds was

acceptable in the laboratory duplicate. No trend was noted, in that the BZ#118 and BZ#128

concentrations are acceptable in most of the SRM analyzed with the egg samples. No action was

taken based on the BZ#128 outlier. Since the BZ#118 concentration was also outside of the ±25%

control limits, all associated positive BZ#118 results were estimated (J).

Laboratory Duplicate

The relative percent difference (RPD) values for congeners BZ#157 (35%), BZ#158 (36%), and

BZ#174 (51%) were greater than the control limit of 30%. The concentrations were estimated (J)

in the parent sample, EB-627 Comp-634/635. One congener (BZ#151) was detected in the

duplicate, but was not detected in the parent sample. The concentration in the duplicate was less

than five times the reporting limit. No action taken.

The RPD value for the sample and laboratory duplicate percent lipids determination exceeds the

control limit of 15%, at 24%. The lipids result was estimated (J) in Sample EB-627-comp-634/635.

III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS) and

standard reference material (SRM) percent recovery values, with the exceptions noted above.

Precision was acceptable as demonstrated by the relative percent difference values for the duplicate

analyses, with the exceptions noted above.

Data were estimated due to laboratory duplicate precision outliers, CCAL %D outliers, and percent

recovery outliers in the matrix spike.

All data, as qualified, are acceptable for use.
Data Quality Assessment

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DATA VALIDATION REPORT - FULL REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0209043

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory. The laboratory followed adequate

corrective action processes, and all anomalies were discussed in the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check * Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

* Continuing Calibration (CCAL) Internal Standards

* Blanks Compound Identification

Surrogate Compounds * Calculation Verification

* Matrix Spike (MS) Reporting Limits and Sample Results

* Laboratory Control Samples (LCS) EDD Transcription Check

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Initial Calibration (ICAL)

In the 09/30/02 ICAL the low (0.25 μg/L) point was dropped for BZ#180. Six calibration points

were still used for this congener, BZ#180 was detected in all samples, and all concentrations were

greater than the lowest calibration point used. No action was necessary.

The data quality objective (DQO) for initial calibrations specified in the Analytical Quality Assurance

Plan (AQAP) is that up to 10% of the analytes may have percent relative standard deviation (%RSD)

values greater than 20%, but less than 30%. In the 09/30/02 ICAL, the %RSD values for BZ#28
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(23%), BZ#118 (21.4%), and BZ#167 (21.1%) were greater than 20% but less than 30%. No action

was necessary, as the DQO were met for the ICAL.

Continuing Calibration (CCAL)

The percent difference (%D) values BZ#28 (22.3%), BZ#118 (24.6%), and BZ#167 (20.4%) were

greater than the ±20% limit. The AQAP allows up to 10% of the compounds to have a %D value

of greater than 20% but less than 30%. No action was necessary.

Blanks

A rinsate blank from the sample homogenizer was analyzed with this batch. Forty-seven of the

forty-eight congeners were detected at low levels in the rinsate blank. The levels were also fairly

consistent, ranging from 0.160 to 0.445 μg/kg. The pattern of contamination in the rinsate blank was

not consistent with the pattern of PCB in the samples, rather the pattern was more consistent with

cross-contamination from the LCS. Laboratory personnel suspect that the rinsate blank extract was

cross-contaminated by the LCS during the final transfer step of the extraction process.

No target analytes were reported in the method blank. Also, very few target analytes are present in

any method or rinse blanks associated with other extraction batches. Due to this, the contamination

in the this rinsate blank was judged to be an anomaly, and the data were not used to qualify any

sample results.

Matrix Spike (MS)

Due to insufficient sample size, no matrix spike was performed with this extraction batch.

Laboratory Control Sample (LCS)

The percent recovery (%R) values of BZ#8 (62%), BZ#18 (66%), BZ#31 (68%), BZ#47 (74%),

BZ#49 (72%), and BZ#167 (66%) were less than the lower control limit of 75%. Positive values

and reporting limits for these congeners were estimated (J/UJ).

Standard Reference Material (SRM)

The reported concentration of BZ#118 was outside the acceptance window [±20% of the 95%

confidence interval] in the SRM, with a reported value of 19.0 μg/Kg and an upper control limit of

18.36 μg/Kg. The concentration is within a ±25% control limit window (with an upper control limit

of 19.13 μg/Kg. As the LCS recovery value was also acceptable, no action was taken based on the

BZ#118 SRM outlier.

The reported concentration of BZ#128 was outside the acceptance window [±20% of the 95%

confidence interval] in the SRM, with a reported value of 3.72 μg/Kg and an upper control limit of
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3.47 μg/Kg. The concentration was also outside a ±25% control limit window (with an upper

control limit of 3.61 μg/Kg. Although the LCS recovery value was acceptable, the BZ#128

concentrations were estimated (J) in the associated samples due to the elevated SRM value.

Laboratory Duplicate

The relative percent difference (RPD) values for most congeners were greater than the control limit

of 30%. The RPD value for the sample and laboratory duplicate percent lipids determination

exceeds the control limit of 15%, at 64.9%. The concentrations for the congeners and lipids were

estimated (J) in the parent sample, EP-047 Comp-063/-064.

If the duplicate congener results are lipid normalized, precision for most congeners is acceptable.

This indicates that the egg sample was not thoroughly homogenous when subsampled for the

replicate analysis. Because only a 1 gram sample was taken for analysis (due to limited sample

size), subsampling of the egg contents was reported by the laboratory as difficult.

Calculation Verification

Reported results were verified by recalculation, and no errors were found.

Congener BZ#209 is the only congener in the decachlorobiphenyl homolog group. However, the

reported values for the decachlorobiphenyl homolog group do not always equal the reported values

for congener BZ#209. This is a result of the instrument software integrating the BZ#209 peak twice,

once as BZ#209, and once as the 'calibration congener' for the decachlorobiphenyl homolog group.

At low concentrations, the peak shape is slightly irregular, causing the software to arrive at different

areas for the peak when the integrations are performed. As the differences between the BZ#209 and

decachlorobiphenyl concentrations are small, no action was taken.

III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical method.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS) and

standard reference material (SRM) percent recovery values, with the exceptions noted above. The

lipid and duplicate results indicate poor precision, possibly due to the difficulty in subsampling the

small quantity of egg contents available (less than 3 grams).

Data were estimated due to laboratory duplicate precision outliers, and percent recovery outliers in

the SRM and LCS.

All data, as qualified, are acceptable for use.
Data Quality Assessment

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DATA VALIDATION REPORT - FULL REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0209044

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory. The laboratory followed adequate

corrective action processes, and all anomalies were discussed in the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check * Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

Continuing Calibration (CCAL) Internal Standards

Blanks Compound Identification

* Surrogate Compounds Calculation Verification

* Matrix Spike (MS) * Reporting Limits and Sample Results

* Laboratory Control Samples (LCS) EDD Transcription Check

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Initial Calibration (ICAL)

In the 10/09/02 ICAL, the low (0.25 μg/L) point was dropped for BZ#180. Six calibration points

were still used for this congener, BZ#180 was detected in all samples, and all concentrations were

greater than the lowest calibration point used. No action was necessary.

The data quality objective (DQO) for initial calibrations specified in the Analytical Quality Assurance

Plan (AQAP) is that up to 10% of the analytes may have a percent relative standard deviation
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(%RSD) values greater than 20%, but less than 30%. In the 10/09/02 ICAL, the %RSD value for

BZ#28 (20.5%) was outside the control limit. No action was taken, as the DQO was met.

Surrogate Compounds

The percent recovery (%R) value of C13-BZ#202 was greater than the upper control limit of 125%,

at 128%, in Sample EP-639 comp -658/-659. Since all detected results are recovery corrected using

this surrogate, all positive values were estimated.

Matrix Spike

The %R values of BZ#28% (at 24%), BZ#47 (at 30%), BZ#66 (at 14%), BZ#74 (at 16%), BZ#99

(at 33%), and BZ#180 (at 45%) were less than the lower control limit of 50%. The positive values

of these congeners were estimated (J) in the parent sample, EP-639 comp -658/-659. The %R values

of BZ#118 (at 0%), BZ#138 (at 0%), and BZ#153 (at 0%) were also less than the lower control limit

of 50%. However, the concentrations of the congeners in the parent sample were greater than five

times the amount spiked. No action was taken.

Laboratory Control Sample (LCS)

The %R values of BZ#8 (at 66%), BZ#18 (at 70%), and BZ#31 (at 71%) were less than the lower

control limit of 75%. The concentrations of these congeners were estimated in all samples.

Standard Reference Material (SRM)

The reported concentration of BZ#153 (11.8 μg/Kg) was less than the 12.54 μg/Kg lower acceptance

[±20% of the 95% confidence interval] in the SRM analyzed with the 09/25/02 extraction batch.

The result was within a 25% window (lower limit is 11.76 μg/Kg), and the %R value of BZ#153 was

acceptable in the LCS. No trend was noted, in that the BZ#153 concentrations are acceptable in

most of the SRM analyzed with the egg samples. The outlier was judged an isolated incident, and

no action was taken.

Laboratory Duplicate

The relative percent difference (RPD) values for BZ#153 (at 33%) and BZ#156 (at 32%) were

greater than the 30% control limit. The concentrations of these congeners were estimated (J) in the

parent sample, EP-635 comp -651/-652.
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The RPD between sample and duplicate for the percent lipid determination exceeded the control

limit of 15%, at 23.8%. The lipids result was estimated (J) in Sample EP-635 comp -651/-652.

Reporting Limits and Sample Results

The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference, but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.

Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.

The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21). PCB Congener BZ#77 was reported as detected in thirteen samples and was

qualified NJ.

Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable.

III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS), matrix

spike (MS) and standard reference material (SRM) percent recovery values, with the exceptions

noted above. Precision was acceptable as demonstrated by the relative percent difference values for

the duplicate analyses, with the exceptions noted above.

Data were estimated s due to surrogate recovery outliers, laboratory duplicate precision outliers, MS

recovery outliers, and LCS recovery outliers. Data were qualified as tentatively identified due to

interference.

All data, as qualified, are acceptable for use.
Data Quality Assessment

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DATA VALIDATION REPORT - FULL REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0209045

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory. The laboratory followed adequate

corrective action processes, and all anomalies were discussed in the case narrative.

The Field Lead sent notification via email to the laboratory that the label reading RS-633-646 should

read RS-633-648. The laboratory did not make this change. The change was made during

validation and the Field ID noted as RS-633-648 in the database.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check * Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

* Continuing Calibration (CCAL) Internal Standards

Blanks Compound Identification

* Surrogate Compounds Calculation Verification

* Matrix Spike (MS) * Reporting Limits and Sample Results

* Laboratory Control Samples (LCS) EDD Transcription Check

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Initial Calibration (ICAL)

In the 10/09/02 and 10/11/02 ICAL, the low (0.25 μg/L) point was dropped for BZ#180. Six

calibration points were still used for this congener, BZ#180 was detected in all samples, and all

concentrations were greater than the lowest calibration point used. No action was necessary.

The data quality objective (DQO) for initial calibrations specified in the Analytical Quality Assurance

Plan (AQAP) is that up to 10% of the analytes may have a percent relative standard deviation
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(%RSD) values greater than 20%, but less than 30%. In the 10/09/02 ICAL, the %RSD value for

BZ#28 (20.5%) was outside the control limit. In the 10/11/02 ICAL, the %RSD value for the

monochlorobiphenyl group (29.5%) was outside the control limit. No action was taken, as the DQO

was met.

Continuing Calibration (CCAL)

The CCAL DQO stated in the AQAP is that up to 10% of the analytes may have a percent difference

(%D) value that is greater than 20%, provided that all %D values are less than 30%. All %D values

were acceptable, with the following exceptions:

The %D values of BZ#28 (at 28.0%) and BZ#123 (at 21.0 %) were greater than the control limit of

20% in the end-of-sequence CCAL analyzed 10/11/02 at 03:13. The %D value of BZ#123 (at

22.3%) was greater than the control limit of 20% in the opening CCAL analyzed 10/11/02 at 21:43.

As the %D values for each compound were acceptable in one of the CCAL and the DQO were met,

no action was taken.

Surrogate Compounds

The percent recovery (%R) value of C13-BZ#202 was greater than the 125% upper control limit in

Samples RS-637 COMP –655/-656 (at 134%) and RB-029-041 (at 134%). Since all detected results

are recovery corrected using this surrogate, all positive values were estimated in Sample RB-029-041.

Due to high levels of congeners, Sample RS-637 COMP –655/-656 was reanalyzed at a dilution. All

positive results except for BZ#123 are reported from the dilution. Due to this, only the result for

BZ#123 was estimated (J) in the original analysis due to the surrogate %R outlier. See the Sample

Results section for additional information.

Matrix Spike

Due to limited sample volume, no matrix spike was performed with this SDG.

Laboratory Control Sample (LCS)

The %R values of BZ#126 (at 72%) and BZ#169 (at 65%) were less than the 75% lower control

limit. The concentrations of these congeners were estimated in the associated samples.

Standard Reference Material (SRM)

The reported concentration of BZ#101 was 21.0 μg/Kg, which is greater than the upper acceptance

limit of 18.84 μg/Kg (established from ±20% of the 95% confidence interval). Although the
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concentration of BZ#101 was acceptable in the LCS, the concentration is also greater than

19.67 μg/Kg, which would be +25% of the 95% confidence interval. Since the SRM result is

significantly outside the acceptance range, all BZ#101 results were estimated in the associated samples.

Laboratory Duplicate

PCB BZ#189 was not reported (0.669 U) in Sample RB-032-044. However, BZ#189 was reported

at 4.22 μg/kg in the laboratory duplicate performed on this sample. The relative percent difference

(RPD) is not calculable, but the reported concentration in the duplicate is greater than five times the

detection limit. The concentration of BZ#189 was estimated in Sample RB-032-044. All other

duplicate results are acceptable.

Reporting Limits and Sample Results

The concentrations of several congeners were greater than the instrument linear range in Samples

RS-629 COMP –639/-644, RS-631 COMP –642/-643, and RS-637 COMP –655/-656. The samples

were reanalyzed as dilutions, and the concentrations were within the linear range. Both analyses

were reported.

To avoid reporting multiple results for these samples, the congeners (and the associated homolog

groups) with concentrations that exceeded the linear range of the instrument in the original analysis

were flagged as do-not-report (DNR). The results for these congeners should be reported from the

dilution analyses. All other results in the dilution analyses were also flagged DNR.

The exception to this is Sample RS-637 COMP –655/-656, where the surrogate %R value in the

initial analysis was greater than the upper control limit. To minimize the amount of qualified data,

all positive results were reported from the dilution. However, BZ#123 was detected in the original

analysis, but was not detected in the dilution. This result was reported from the original analysis,

and estimated as discussed in the Surrogate Compounds section.

The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference, but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.
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Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.

The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21). PCB Congener BZ#77 was reported as detected in 13 samples, BZ#81 was

detected in one sample, BZ#123 in 14 samples, and BZ#126 was reported as detected in 14 samples.

These results were qualified NJ.

Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable.

III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS) and

standard reference material (SRM) percent recovery values, with the exceptions noted above.

Precision was acceptable as demonstrated by the relative percent difference values for the duplicate

analyses, with the exceptions noted above.

Data were estimated s due to surrogate recovery outliers, laboratory duplicate precision outliers,

SRM recovery outliers, and LCS recovery outliers. Data were qualified as tentatively identified due

to interference. Data were qualified as do-not-report (DNR) due to concentrations exceeding the

linear range of the instrument, and to designate which result (of multiple results) should be reported.

Data qualified as do-not-report should not be used for any purpose.

All other data, as qualified, are acceptable for use.
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DATA VALIDATION REPORT - FULL REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0209046

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory. The laboratory followed adequate

corrective action processes, and all anomalies were discussed in the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

* Continuing Calibration (CCAL) * Internal Standards

Blanks Compound Identification

* Surrogate Compounds Calculation Verification

* Matrix Spike (MS) * Reporting Limits and Sample Results

* Laboratory Control Samples (LCS) EDD Transcription Check

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Initial Calibration (ICAL)

In the 10/11/02 ICAL, the low (0.25 μg/L) point was dropped for BZ#180. Six calibration points

were still used for this congener, BZ#180 was detected in all samples, and all concentrations were

greater than the lowest calibration point used. No action was necessary.
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The data quality objective (DQO) for initial calibrations specified in the Analytical Quality Assurance

Plan (AQAP) is that up to 10% of the analytes may have a percent relative standard deviation

(%RSD) values greater than 20%, but less than 30%. In the 10/11/02 ICAL, the %RSD value for

the monochlorobiphenyl group (29.5%) was outside the control limit. No action was taken, as the

DQO was met.

Continuing Calibration (CCAL)

The CCAL DQO stated in the AQAP is that up to 10% of the analytes may have a percent difference

(%D) value that is greater than 20%, provided that all %D values are less than 30%. All %D values

were acceptable, with the following exceptions:

The %D value of the monochlorobiphenyl homolog group (37.5%) was greater than the control limit

of 20% in the opening CCAL analyzed 10/11/02 at 20:30. The %D values of the

monochlorobiphenyl homolog group (at 47.8%) and BZ#123 (at 22.3%) were greater than the

control limit of 20% in the CCAL analyzed 10/11/02 at 23:43. The %D value of the

monochlorobiphenyl homlog group was 41% in the closing CCAL analyzed 10/12/02 09:37. As the

%D value for BZ#123 was greater than 20% in only one CCAL and was less than 30%, no action

was taken. The monochlorobiphenyl homolog group was not detected in any sample, the reporting

limit was estimated (UJ) in all samples.

Surrogate Compounds

The percent recovery (%R) value of C13-BZ#202 was greater than the 125% upper control limit in

Sample RB-111-113 (at 129%). Since all detected results are recovery corrected using this surrogate,

all positive values were estimated in Sample RB-111-113.

Matrix Spike

Due to limited sample volume, no matrix spike was performed with this SDG.

Laboratory Control Sample (LCS)

The %R values of BZ#8 (at 74%) and BZ#174 (at 62%) were less than the 75% lower control limit.

The concentrations of these congeners were estimated in the associated samples.
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Laboratory Duplicate

A laboratory duplicate was prepared with this SDG, but the analyst notes indicate that a problem was

encountered with the native sample during the extraction process. The percent lipids analysis

yielded a high relative percent difference value (42.7%), and the case narrative notes that the parent

sample had low surrogate recovery, but no raw data is provided. Since the data indicated that the

parent sample extract was compromised, the data were not reported. The extract prepped as the

duplicate is reported as the parent sample, and no laboratory duplicate is reported with this SDG.

Internal Standards

Sample RB-039-051 was inadvertently double spiked with internal standard solution. The internal

standard areas were double the expected values, and the laboratory correctly calculated the sample

concentrations. No action was taken.

Reporting Limits and Sample Results

The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference, but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.

Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.

The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21). PCB Congener BZ#77 was reported as detected in three samples and

BZ#126 was reported as detected in thirteen samples. These results were qualified NJ.

Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable.
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III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS) and

standard reference material (SRM) percent recovery values, with the exceptions noted above.

Precision was not assessed.

Data were estimated due to surrogate recovery outliers, continuing calibration outliers, and LCS

recovery outliers. Data were qualified as tentatively identified due to interference.

All data, as qualified, are acceptable for use.
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DATA VALIDATION REPORT - FULL REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0209047

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory. The laboratory followed adequate

corrective action processes, and all anomalies were discussed in the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check * Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

Continuing Calibration (CCAL) Internal Standards

Blanks Compound Identification

Surrogate Compounds * Calculation Verification

* Matrix Spike (MS) * Reporting Limits and Sample Results

* Laboratory Control Samples (LCS) EDD Transcription Check

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Initial Calibration (ICAL)

In the 10/17/02 ICAL, the low (0.25 μg/L) point was dropped for BZ#180. Six calibration points

were still used for this congener, BZ#180 was detected in all samples, and all concentrations were

greater than the lowest calibration point used. No action was necessary.

Matrix Spike

The percent recovery (%R) values were less than the lower control limit of 50% for BZ#28 (at 18%)

and BZ#66 (at 21%). The %R values were greater than the 125% upper control limit for BZ#31 (at
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193%), BZ#123 (at 133%), and BZ#167 (127%). The positive BZ#28, BZ#31, BZ#66, and BZ#167

results were estimated (J) in the parent sample RB-621-625. An elevated %R value indicates a

possible high bias. BZ#123 was not detected, so no action was taken.

Laboratory Control Sample (LCS)

The %R value of BZ#70 (at 126%) was greater than the upper control limit of 125%. The positive

BZ#70 results were estimated in all samples.

Standard Reference Material (SRM)

The reported concentration of BZ#101 (19 μg/Kg) was greater than the 18.84 μg/Kg upper

acceptance window [±20% of the 95% confidence interval] in the SRM analyzed with the 10/11/02

extraction batch. The result is within a 25% control limit (19.63 μg/Kg upper control limit), and the

%R value of BZ#101 was acceptable in the LCS and the MS. No trend was noted, in that the

BZ#101 concentrations are acceptable in most of the SRM analyzed with the egg samples. The

outlier was judged an isolated incident, and no action was taken.

Laboratory Duplicate

The relative percent difference (RPD) values for BZ#70 (at 56%), BZ#128 (at 34%), BZ#209 and

the decachlorobiphenyl homolog group (at 68%) were greater than the control limit of 30%. PCB

BZ#87 was not detected (reporting limit is 0.148 μg/kg) in the parent sample, but was detected at

15.3 μg/kg in the duplicate. PCB BZ#151 was detected in the parent sample at 0.983 μg/kg, but was

not detected in the duplicate (reporting limit is 0.103 μg/kg). Congeners BZ#70, BZ#87, BZ#128,

BZ# 151, BZ#209 and the decachlorobiphenyl homolog group were estimated (J/UJ) in the parent

sample, RB-229-232.

Also, the RPD value of BZ#44 (at 89%) was greater than the control limit of 30%, and PCB BZ#157

was not detected in the parent sample (reporting limit is 0.370 μg/kg), but was detected in the

duplicate at 1.24 μg/kg/. In both cases the reported values were less than five times the reporting

limit. No action was taken.

Calculation Verification

Congener BZ#209 is the only congener in the decachlorobiphenyl homolog group. However, the

reported values for the decachlorobiphenyl homolog group do not always equal the reported values

for congener BZ#209. This is a result of the instrument software integrating the BZ#209 peak twice,

once as BZ#209, and once as the 'calibration congener' for the decachlorobiphenyl homolog group.

At low concentrations, the peak shape is slightly irregular, causing the software to arrive at different

areas for the peak when the integrations are performed. As the differences between the BZ#209 and

decachlorobiphenyl concentrations are small, no action was taken.
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Reported results were verified by recalculation, and no other errors were found.

Reporting Limits and Sample Results

The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference, but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.

Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.

The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21). PCB Congener BZ#77 was reported as detected in one sample and BZ#126

was reported as detected in thirteen samples. These results were qualified NJ.

Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable.

III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS), matrix

spike (MS) and standard reference material (SRM) percent recovery values, with the exceptions

noted above. Precision was acceptable as demonstrated by the relative percent difference values for

the duplicate analyses, with the exceptions noted above.

Data were estimated due to LCS recovery outliers, MS recovery outliers, and laboratory duplicate

RPD outliers. Data were qualified as tentatively identified due to interference.

All data, as qualified, are acceptable for use.
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DATA VALIDATION REPORT - SUMMARY (LEVEL III) REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0209048

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory. The laboratory followed adequate

corrective action processes, and all anomalies were discussed in the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

* Continuing Calibration (CCAL) * Internal Standards

Blanks Compound Identification

* Surrogate Compounds * Reporting Limits and Sample Results

* Matrix Spike (MS) EDD Transcription Check

* Laboratory Control Samples (LCS)

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Initial Calibration (ICAL)

The data quality objective (DQO) for initial calibrations specified in the Analytical Quality Assurance

Plan (AQAP) is that up to 10% of the analytes may have a percent relative standard deviation

(%RSD) values greater than 20%, but less than 30%. In the 10/12/02 ICAL, the %RSD value for

the BZ#19-C13 (at 23.4%) was outside the control limit. No action was taken, as the DQO was met

and the compound is a surrogate, not a target compound.
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In the 10/23/02, 10/28/02, and 11/1/02 ICAL the low (0.25 μg/L) point was dropped for BZ#180.

Six calibration points were still used for this congener, BZ#180 was detected in all samples, and all

concentrations were greater than the lowest calibration point used. No action was necessary.

Continuing Calibration (CCAL)

The CCAL DQO stated in the AQAP is that up to 10% of the analytes may have a percent difference

(%D) value that is greater than 20%, provided that all %D values are less than 30%. All %D values

were acceptable, with the following exceptions:

• The %D value of BZ#126 (20.4%) was greater than the control limit in the middle of sequence

CCAL analyzed 10/25/02 at 05:04.

• The %D values of BZ#126 (20.3%) and BZ#169 (23.8%) were greater than the control limit in

the end of sequence CCAL analyzed 10/29/02 at 07:06.

No action was taken, as the %D values were less than 30%.

Surrogate Compounds

The percent recovery (%R) value for the surrogate BZ#202-C13 was greater than the 125% upper

control limit in the matrix spike (MS) analysis performed using Sample SS-238-244 (at 152%). The

matrix spike was diluted and re-analyzed due to an internal standard outlier. The original analysis

was not used. No action further action was necessary.

Matrix Spike

As discussed in the Surrogate Compounds and Internal Standards sections, the matrix spike was

reanalyzed at a 4x dilution due to surrogate, spike, and internal standard recovery outliers. The

original analysis was not used. The following outliers were present in the 4x dilution analysis:

The %R values were less than the 50% lower control limit for BZ#118 and BZ#169 (both at 0%).

The concentration of BZ#118 was greater than five times the spike amount in the parent sample, SS238-244. No action was taken. The BZ#169 value was rejected (R) in the parent sample.

The %R values were greater than the 125% upper control limit for BZ#47 (at 132%), BZ#74 (at

139%), BZ#87 (at 188%), BZ#99 (at 175%), BZ#101 (at 147%) BZ%138 (at 284%), BZ#146 (at

150%), BZ#153 (at 300%), and BZ#187 (at 141%). The concentrations of BZ#99, BZ#138, and

BZ#153 were greater than five times the spike amount in the parent sample. No action was taken.

The concentrations of BZ#47, BZ#74, BZ#87, BZ#101, BZ#146, and BZ#187 were estimated (J)

in the parent sample.
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Laboratory Control Sample (LCS)

The %R value of BZ#169 (at 64%) was less than the lower control limit of 75%. The reporting

limits of BZ#169 were estimated in all samples.

Laboratory Duplicate

The relative percent difference (RPD) values for BZ#56 (at 38%), BZ#126 (at 47%), BZ#128

(at35%) and BZ#177 (at 63%) were greater than the control limit of 30%. The concentrations of

these congeners were estimated in the parent sample, SS-108-110.

Internal Standards

The recovery of BZ#180-C13 in the matrix spike (MS) performed on Sample SS-238-244 was less

than the control limit of 50% of the area found in the opening CCAL. The matrix spike was diluted

and re-analyzed due to the internal standard outlier. The dilution had acceptable internal standard

recoveries. The full strength run was not used. No action was taken.

Reporting Limits and Sample Results

The concentrations of several congeners were greater than the instrument linear range in Samples

SO-002-002 and SS-235-240. The samples were reanalyzed as dilutions, and the concentrations

were within the linear range. Both analyses were reported.

To avoid reporting multiple results for these samples, the congeners (and the associated homolog

groups) with concentrations that exceeded the linear range of the instrument in the original analysis

were flagged as do-not-report (DNR). The results for these congeners should be reported from the

dilution analyses. All other results in the dilution analyses were also flagged DNR.

Sample SS-238-244 was reanalyzed at a dilution due to matrix interference evident in the MS

analysis performed using this sample. However, for the non-spiked sample, all surrogate and

internal standard recovery values were acceptable. In order to have the lowest possible detection

limits, all values were reported from the original analysis. The dilution of Sample SS-238-244 was

flagged as DNR to avoid multiple results.

Congener BZ#209 is the only congener in the decachlorobiphenyl homolog group. However, the

reported values for the decachlorobiphenyl homolog group do not always equal the reported values

for congener BZ#209. This is a result of the instrument software integrating the BZ#209 peak twice,

once as BZ#209, and once as the 'calibration congener' for the decachlorobiphenyl homolog group.

At low concentrations, the peak shape is slightly irregular, causing the software to arrive at different

areas for the peak when the integrations are performed. As the differences between the BZ#209 and

decachlorobiphenyl concentrations are small, no action was taken.
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The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.

Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.

The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21). PCB Congener BZ#126 was reported as detected in two samples. These

results were qualified NJ.

Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable.

III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS), matrix

spike (MS) and standard reference material (SRM) percent recovery values, with the exceptions

noted above. . Precision was acceptable as demonstrated by the relative percent difference values

for the duplicate analyses, with the exceptions noted above.

Data were estimated due to LCS and MS recovery outliers, and laboratory duplicate RPD outliers.

Data were qualified as do-not-report due to the existence of duplicate values. Data were qualified

as tentatively identified due to interference. One data point was rejected due to a zero percent

recovery value in the MS analysis.

Data that have been rejected or qualified as do-not-report should not be used for any purpose. All

other data, as qualified, are acceptable for use.
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DATA VALIDATION REPORT - SUMMARY (LEVEL III) REVIEW

Hudson River

Polychlorinated Biphenyl Congeners, Lipids

SDG: 0210059

This report documents the review of analytical data from the analysis of egg samples and the

associated laboratory quality control samples. Refer to the Sample Index for a list of the samples

reviewed.

I. DATA PACKAGE COMPLETENESS

All required deliverables were submitted by the laboratory. The laboratory followed adequate

corrective action processes, and all anomalies were discussed in the case narrative.

II. TECHNICAL DATA VALIDATION

The quality control (QC) requirements that were reviewed are listed below.

GC/MS Instrument Performance Check Standard Reference Material (SRM)

* Initial Calibration (ICAL) * Laboratory Duplicate

* Continuing Calibration (CCAL) * Internal Standards

Blanks Compound Identification

* Surrogate Compounds * Reporting Limits and Sample Results

* Matrix Spike (MS) EDD Transcription Check

* Laboratory Control Samples (LCS)

Those items marked with an asterisk (*) did not meet all specified QC criteria and are discussed

below. QC items not marked with an asterisk meet all QC criteria.

Initial Calibration (ICAL)

In the 10/23/02 and 11/1/02 ICAL the low (0.25 μg/L) point was dropped for BZ#180. Six

calibration points were still used for this congener, BZ#180 was detected in all samples, and all

concentrations were greater than the lowest calibration point used. No action was necessary.
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Continuing Calibration (CCAL)

The CCAL DQO stated in the AQAP is that up to 10% of the analytes may have a percent difference

(%D) value that is greater than 20%, provided that all %D values are less than 30%. All %D values

were acceptable, with the following exceptions:

• value of BZ#126 (20.4%) was greater than the control limit in the middle of sequence CCAL

analyzed 10/25/02 at 05:04.

No action was taken, as the %D value was less than 30%.

Surrogate Compounds

The %R value of BZ#202-C13 in Sample AW-100-100 was greater than the upper control limit of

125%, at 138%. The internal standard area was also outside of the control limits in this analysis.

The sample was diluted four fold and re-analyzed. The %R value of BZ#202-C13 and the internal

standard values were acceptable in the re-analysis, however the %R value of BZ#19-C13 was less

than the lower control limit of 50%, at 47%.

As all values are surrogate recovery corrected using the BZ#202-C13 values, the data from the

reanalysis were judged more accurate than the original analysis results. For this reason the initial

analysis was qualified as do-not-report, and the diluted analysis was chosen to be reported. Since

the BZ#202-C13 recovery was acceptable, no data were qualified in the dilution analysis based on

the BZ#19-C13 outlier.

Matrix Spike

No matrix spike was analyzed with this batch.

Laboratory Control Sample (LCS)

The %R value of BZ#169 (at 70%) was less than the lower control limit of 75% in the 10/18/02

LCS. The reporting limit of BZ#169 was estimated in the associated sample, AW-100-100.

Laboratory Duplicate

No laboratory duplicate was performed with this batch.
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Internal Standards

The recovery of BZ#180-C13 Sample AW-100-100 was less than the control limit of 50% of the

area found in the opening CCAL. The sample was diluted and re-analyzed due to the internal

standard outlier. The dilution had acceptable internal standard recoveries. As discussed in the

Surrogate Compound section, the full strength run was not used. No further action was taken.

Both internal standard recoveries were less than the control limit in the closing CCAL analyzed

10/25/02 at 05:04. The target analyte %D values were acceptable in the CCAL, and only the method

blank, laboratory control sample (LCS), and standard reference material (SRM) were reported from

this analytical sequence. No action was taken.

Reporting Limits and Sample Results

Congener BZ#209 is the only congener in the decachlorobiphenyl homolog group. However, the

reported values for the decachlorobiphenyl homolog group do not always equal the reported values

for congener BZ#209. This is a result of the instrument software integrating the BZ#209 peak twice,

once as BZ#209, and once as the 'calibration congener' for the decachlorobiphenyl homolog group.

At low concentrations, the peak shape is slightly irregular, causing the software to arrive at different

areas for the peak when the integrations are performed. As the differences between the BZ#209 and

decachlorobiphenyl concentrations are small, no action was taken.

The separation and spectral fit for any positive result for the coplanar congeners (BZ#77, BZ#81,

BZ#126, and BZ#169) were evaluated. BZ#87 was found to interfere with BZ#81 and BZ#110 was

found to interfere with BZ#77. The spectra for BZ#126 indicates an overall poor spectral fit. There

appears to be some interference but the source of the interference could not be determined. The

interference does not appear to be a PCB congener.

Although not a coplanar congener, interference was also noted for BZ#123. BZ#149 interferes with

the spectra for BZ#123.

The spectral match met general identification criteria for these congeners, so the laboratory correctly

reported the results as positive results. However, due to the interference, the results may be false

positives, or may be biased high. The potential interferences cannot be resolved without further

extract cleanup (e.g., carbon column cleanup). Thus, all positive results for these congeners (BZ#77,

BZ#81, BZ#123, and BZ#126) should be qualified as tentatively identified at an estimated

concentration (NJ-21). PCB Congener BZ#81 was reported as detected in one sample. This result

was qualified NJ.

Chromatography and mass spectral identification were reviewed for a minimum of 10% of all other

reported congeners. No other instances of potential interference were noted. All reported positive

results met the identification criteria and chromatographic peak shapes were acceptable.
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III OVERALL ASSESSMENT

As was determined by this evaluation, the laboratory followed the specified analytical methods.

Accuracy was acceptable, as demonstrated by the surrogate, laboratory control sample (LCS) and

standard reference material (SRM) percent recovery values, with the exceptions noted above.

Precision was not evaluated.

Data were estimated due to an LCS recovery outlier. Data were qualified as tentatively identified

due to interference. Data were qualified as do-not-report due to the existence of duplicate values.

Data that has been qualified as do-not report should not be used for any purpose. All other data, as

qualified, are acceptable for use.
STANDARD REFERENCE MATERIAL 1974a

Organic in Mussel Tissue (Mytilus edulis)Concentrations are ng/g, wet weight

SDG 208031 208032 208033 208034 208038 209043 209044 209045 209046 209047 

AnalyteCl4-BZ#44 10.4 6.72 8.38 8.86 10.2 9.58 8.92 11 7.78 9.98 Cl4-BZ#49 11 7.76 9.53 9.7 10.5 9.81 9.61 11.9 9.24 12.8 Cl4-BZ#52 14.8 10.2 12.5 13.2 13.9 13.5 13 15.2 11.8 15.3 Cl4-BZ#66 13.9 9.96 12.5 12 12.5 12.1 12.2 14.3 10.9 13.6 Cl5-BZ#95 10.6 8.37 7.33 10.1 10.7 10.3 9.77 11.5 8.81 11 Cl5-BZ#99 8.43 7.14 7.95 8.05 8.97 8.27 8.11 9.73 7.49 9.06 Cl5-BZ#101 17.8 14.7 18.2 17.6 18.9 18 17.5 21 15.9 19 Cl5-BZ#105 5.67 5.62 6.16 5.9 6.48 6.33 6.94 5.89 7.08 5.91 Cl5-BZ#110 13 11.7 13.6 13.3 14.5 14 13.7 16.2 12.5 15.5 Cl5-BZ#118 15.1 14.3 18.4 15.6 19.6 19 15.1 18 16.4 17.9 Cl6-BZ#128 1.7 2.34 2.46 2.08 3.6 3.72 2.52 2.78 2.41 2.46 Cl6-BZ#138 12.3 14.7 13 14.3 16.3 14.8 15.9 19.2 14.3 17.8 Cl6-BZ#149 9.19 7.69 8.68 8.44 9.06 8.72 8.65 10.4 7.91 9.58 Cl6-BZ#151 2.51 2.08 2.39 2.4 2.65 2.63 2.54 2.87 2.19 2.79 Cl6-BZ#153 13.6 12.1 13.9 13.3 14.8 14.5 11.8 14.1 12.5 15.6 Cl6-BZ#156 1.01 0.801 0.668 0.899 1.06 0.879 0.892 0.932 1.09 0.853 Cl7-BZ#170 0.631 0.61 0.385 0.596 0.633 0.45 0.68 0.745 0.537 0.654 Cl7-BZ#180 1.43 1.3 1.34 1.36 1.62 1.58 1.36 1.52 1.26 1.6 Cl7-BZ#183 1.63 1.47 1.57 1.53 1.8 1.74 1.58 1.86 1.42 1.82 Cl7-BZ#187 3.52 3.22 3.63 3.37 3.88 3.79 3.62 4.25 3.26 4.14 Note: Two SRM were reported with SDG 210059.SDG = Sample Delivery Group, also called analytical batch

TABLE 1A: Summary of SRM Results: Analytical Results

1 of 2
STANDARD REFERENCE MATERIAL 1974a

Summary of Analytical Performance

Analyte True Value Uncertainty

Average 

Result

Minimum 

Result

Maximum 

result Number of Number of

S

D

 ng/g From To ng/g ng/g ng/g Analysis Outliers 

Cl4-BZ#44 8.28 0.84 5.58 11.4 9.21 6.72 11.0 13 0 Cl4-BZ#49 10.1 0.59 7.15 13.4 10.3 7.76 12.8 13 0 Cl4-BZ#52 13.1 1.30 8.85 18.0 13.5 10.2 15.3 13 0 Cl4-BZ#66 11.5 0.50 8.28 15.1 12.3 9.96 14.3 13 0 Cl5-BZ#95 9.50 1.90 5.70 14.3 9.98 7.33 11.5 13 0 Cl5-BZ#99 8.08 0.46 5.72 10.7 8.37 7.14 9.73 13 0 Cl5-BZ#101 14.6 1.10 10.1 19.6 18.0 14.7 21.0 13 1 Cl5-BZ#105 6.04 0.39 4.24 8.04 6.19 5.62 7.08 13 0 Cl5-BZ#110 14.5 1.00 10.1 19.4 13.8 11.7 16.2 13 0 Cl5-BZ#118 14.9 0.40 10.9 19.1 16.8 14.3 19.6 13 1 Cl6-BZ#128 2.50 0.39 1.58 3.61 2.50 1.70 3.72 13 1 Cl6-BZ#138 15.2 1.10 10.6 20.4 15.1 12.3 19.2 13 0 Cl6-BZ#149 9.98 0.27 7.28 12.8 8.87 7.69 10.4 13 0 Cl6-BZ#151 2.91 0.40 1.88 4.14 2.49 2.08 2.87 13 0 Cl6-BZ#153 16.5 0.86 11.8 21.8 13.8 11.8 15.6 13 0 Cl6-BZ#156 0.85 0.11 0.56 1.20 0.91 0.67 1.14 13 0 Cl7-BZ#170 0.63 0.12 0.38 0.94 0.59 0.39 0.75 13 0 Cl7-BZ#180 1.95 0.43 1.14 2.98 1.44 1.26 1.62 13 0 Cl7-BZ#183 1.82 0.27 1.16 2.61 1.64 1.42 1.86 13 0 Cl7-BZ#187 3.87 0.27 2.70 5.18 3.64 3.22 4.25 13 0 %D = [(True Value - Average Result) / True Value] X 100

 +/- 25% Limits

ng/g

TABLE 1B: Summary of SRM Results: Statistical Evaluation

2 of 2
SDG: 208031 208032 208033 208034 209038 209043 209044 209045 209047 209048

ANALYTE AR-024-035 AR-505-506 AR-509-511 BK-506-508

EB-627 Comp -

634/635

EP-047 COMP -

063/-06

EP-635 COMP -

651/-652 RB-032-044 RB-229-232 SS-108-110

Cl3-BZ#28 27 63 17 0 22 21 Cl3-BZ#31 33 70 11 4 19 11 Cl4-BZ#44 25 3 Cl4-BZ#47 26 12 51 32 4 63 12 2 15 13 Cl4-BZ#49 19 27 49 15 4 75 21 2 19 11 Cl4-BZ#52 25 14 49 26 14 68 8 2 20 12 Cl4-BZ#56 28 5 60 12 1 10 38 Cl4-BZ#66 51 27 8 62 14 1 18 16 Cl4-BZ#70 29 1 65 1 56 15 Cl4-BZ#74 18 33 54 27 1 58 12 2 26 15 Cl4-BZ#77 9 Cl5-BZ#87 22 26 1 57 15 2 23 Cl5-BZ#95 21 27 21 63 15 1 22 9 Cl5-BZ#99 22 13 46 26 2 59 15 1 17 12 Cl5-BZ#101 22 15 50 27 1 63 15 1 17 11 Cl5-BZ#105 17 29 2 60 23 6 15 19 Cl5-BZ#110 9 17 38 26 8 1 24 16 Cl5-BZ#114 32 2 59 14 1 19 13 Cl5-BZ#118 22 24 53 27 4 61 17 1 15 18 Cl5-BZ#123 0 Cl5-BZ#126 115 4 13 47 Cl6-BZ#128 16 3 30 21 6 0 22 1 34 35 Cl6-BZ#138 18 39 58 27 2 62 15 1 13 17 Cl6-BZ#146 21 22 51 25 2 61 14 1 18 13 Cl6-BZ#149 26 16 53 27 5 59 14 0 13 12 Cl6-BZ#151 20 23 62 17 4 9 Cl6-BZ#153 21 19 47 26 2 61 33 0 16 19 Cl6-BZ#156 0 24 14 60 32 0 9 13 Cl6-BZ#157 28 28 35 39 18 4 Cl6-BZ#158 4 34 54 16 36 41 9 12 12 20 Cl6-BZ#167 13 26 74 28 4 132 8 2 14 4 Cl7-BZ#170 25 28 55 32 1 53 21 3 14 10 Cl7-BZ#174 6 23 51 61 0 14 9 Cl7-BZ#177 16 12 49 26 6 64 18 2 16 33 Cl7-BZ#180 24 28 40 21 4 57 24 8 16 12 Cl7-BZ#183 14 15 52 26 0 88 14 0 16 4 Cl7-BZ#187 17 19 49 26 0 61 17 1 17 12 Cl8-BZ#194 25 12 62 21 3 17 20 2 10 23 Cl8-BZ#195 15 26 1 15 12 53 12 2 16 13 Cl8-BZ#201 36 28 30 23 15 95 18 1 15 12 Cl9-BZ#206 18 11 47 27 11 28 22 0 14 16 Cl10-BZ#209 2 18 43 21 14 23 16 23 68 20 Trichlorobiphenyls 29 63 12 2 17 13 Tetrachlorobiphenyls 19 4 48 25 7 61 13 4 19 12 Pentachlorobiphenyls 14 13 64 36 2 59 15 4 18 12 Hexachlorobiphenyls 19 22 54 26 1 61 16 0 19 13 Heptachlorobiphenyls 14 19 51 25 3 59 18 0 17 13 Octachlorobiphenyls 81 8 37 9 5 5 25 1 22 12 Nonachlorobiphenyls 6 7 53 31 6 35 17 2 18 19 Decachlorobiphenyl 11 18 43 21 14 19 16 23 68 20 Percent Lipids 2 23 2 22 24 65 24 11 20 7 Percent Moisture 0 8 51 1 10 1 0 5 1 

Blank spaces indicate no RPD result, meaning the analyte is not detected in the parent sample and/or duplicate, or both reported values were less than 5 times the MDL.Note: RPD outliers are presented in bold. The RPD control limit for PCBs is 30%, and for percent lipids and percent moisture is 15%.

TABLE 2: Avian Egg Laboratory Duplicate Relative Percent Difference Summary

1 of 1

APPENDIX C

AVIAN EGG DATA SHEETS

Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

5/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#8 0.178 U ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#18 0.268 U ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#28 31.0 ug/kg 0.05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#31 8.52 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#44 3.05 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#45 0.145 U ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#47 56.6 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#49 16.2 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#52 19.9 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#56 17.8 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#66 70.5 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#70 12.7 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#74 51.6 J ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#77 0.101 U ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#81 0.134 U ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#87 24.1 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#95 3.33 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#99 76.5 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#101 35.0 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#105 31.2 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#110 9.17 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#114 6.35 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#118 123 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#123 0.116 U ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#126 0.156 U ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#128 4.32 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#138 91.1 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#146 20.5 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#149 9.79 ug/kg 0

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 1 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#151 0.878 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#153 95.8 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#156 11.0 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#157 2.01 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#158 4.71 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#167 12.0 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#169 6.17 U ug/kg 5/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#170 13.8 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#174 1.76 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#177 3.58 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#180 24.6 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#183 5.27 ug/kg 0.05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#189 0.301 U ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#187 28.7 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#194 7.21 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#195 1.69 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#201 11.2 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#206 5.04 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 BZ#209 0.924 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Monochlorobiphenyls 0.101 U ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Dichlorobiphenyls 0.178 U ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Trichlorobiphenyls 35.3 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Tetrachlorobiphenyls 299 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Pentachlorobiphenyls 499 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Hexachlorobiphenyls 288 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Heptachlorobiphenyls 66.6 ug/kg 0.05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Octachlorobiphenyls 24.0 ug/kg 0.05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Nonachlorobiphenyls 9.56 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Decachlorobiphenyl 0.924 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 2 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/1/2002 CG-009-014 615315 4768690 1 0208034-06 Total Homologs 1220 ug/kg 05/1/2002 CG-009-014 615315 4768690 1 0208034-06 Percent Lipids 7.7 % 5/1/2002 CG-009-014 615315 4768690 1 0208034-06 Percent Moisture 73 % 5/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#8 0.142 U ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#18 0.214 U ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#28 6.93 ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#31 1.55 ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#44 0.174 U ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#45 0.116 U ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#47 45.5 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#49 7.63 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#52 3.23 ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#56 5.60 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#66 25.5 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#70 0.104 U ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#74 28.9 J ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#77 0.0810 U ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#81 0.107 U ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#87 15.2 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#95 0.608 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#99 52.6 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#101 32.9 ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#105 20.2 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#110 2.29 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#114 3.21 ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#118 75.2 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#123 0.0926 U ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#126 1.51 NJ ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#128 2.64 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 3 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#138 69.6 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#146 15.5 ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#149 10.9 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#151 0.104 U ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#153 69.8 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#156 6.12 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#157 0.312 U ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#158 4.07 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#167 9.81 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#169 4.92 U ug/kg 5/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#170 8.50 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#174 1.94 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#177 3.41 ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#180 14.7 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#183 3.83 ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#189 0.240 U ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#187 24.6 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#194 4.29 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#195 1.09 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#201 7.26 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#206 3.10 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 BZ#209 0.664 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Monochlorobiphenyls 0.0810 U ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Dichlorobiphenyls 0.142 U ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Trichlorobiphenyls 7.46 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Tetrachlorobiphenyls 156 ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Pentachlorobiphenyls 329 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Hexachlorobiphenyls 222 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Heptachlorobiphenyls 49.8 ug/kg 0.0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 4 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/9/2002 CG-019-027 614763 4767871 2 0208034-07 Octachlorobiphenyls 16.3 ug/kg 0.05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Nonachlorobiphenyls 6.29 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Decachlorobiphenyl 0.664 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Total Homologs 787 ug/kg 05/9/2002 CG-019-027 614763 4767871 2 0208034-07 Percent Lipids 6.7 % 5/9/2002 CG-019-027 614763 4767871 2 0208034-07 Percent Moisture 83 % 5/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#8 0.287 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#18 0.434 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#28 152 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#31 67.4 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#44 0.352 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#45 0.234 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#47 100 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#49 143 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#52 199 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#56 69.3 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#66 294 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#70 119 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#74 141 J ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#77 0.164 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#81 0.217 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#87 77.7 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#95 25.1 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#99 173 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#101 264 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#105 122 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#110 95.2 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#114 12.0 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#118 321 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 5 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#123 0.188 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#126 0.252 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#128 11.2 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#138 380 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#146 37.1 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#149 92.1 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#151 15.0 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#153 203 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#156 24.4 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#157 4.07 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#158 16.3 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#167 45.2 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#169 9.96 U ug/kg 5/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#170 23.7 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#174 12.7 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#177 8.92 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#180 34.2 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#183 7.17 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#189 0.486 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#187 31.3 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#194 5.56 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#195 1.94 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#201 9.11 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#206 2.99 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 BZ#209 0.709 J ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Monochlorobiphenyls 0.164 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Dichlorobiphenyls 0.287 U ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Trichlorobiphenyls 200 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Tetrachlorobiphenyls 1170 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 6 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/22/2002 CG-040-052 614732 4783425 1 0208034-08 Pentachlorobiphenyls 1790 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Hexachlorobiphenyls 837 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Heptachlorobiphenyls 96.4 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Octachlorobiphenyls 21.1 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Nonachlorobiphenyls 6.34 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Decachlorobiphenyl 0.709 J ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Total Homologs 4120 ug/kg 05/22/2002 CG-040-052 614732 4783425 1 0208034-08 Percent Lipids 8.6 % 5/22/2002 CG-040-052 614732 4783425 1 0208034-08 Percent Moisture 84 % 5/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#8 0.337 U ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#18 0.509 U ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#28 99.6 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#31 27.7 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#44 6.22 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#45 0.275 U ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#47 220 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#49 87.7 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#52 121 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#56 58.6 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#66 272 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#70 27.0 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#74 150 J ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#77 0.192 U ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#81 0.254 U ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#87 59.2 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#95 35.9 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#99 168 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#101 152 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#105 88.5 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 7 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#110 38.7 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#114 11.2 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#118 252 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#123 0.220 U ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#126 0.296 U ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#128 8.27 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#138 195 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#146 35.7 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#149 90.7 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#151 19.8 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#153 186 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#156 17.0 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#157 2.89 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#158 18.6 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#167 26.4 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#169 11.7 U ug/kg 5/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#170 33.1 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#174 20.8 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#177 14.8 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#180 54.2 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#183 15.5 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#189 0.570 U ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#187 86.8 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#194 9.98 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#195 3.28 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#201 17.7 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#206 7.44 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 BZ#209 1.66 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Monochlorobiphenyls 0.192 U ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 8 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/10/2002 CG-108-111 615895 4774798 1 0208034-09 Dichlorobiphenyls 0.337 U ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Trichlorobiphenyls 127 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Tetrachlorobiphenyls 1130 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Pentachlorobiphenyls 1350 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Hexachlorobiphenyls 720 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Heptachlorobiphenyls 188 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Octachlorobiphenyls 41.8 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Nonachlorobiphenyls 16.4 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Decachlorobiphenyl 1.66 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Total Homologs 3570 ug/kg 05/10/2002 CG-108-111 615895 4774798 1 0208034-09 Percent Lipids 7.6 % 5/10/2002 CG-108-111 615895 4774798 1 0208034-09 Percent Moisture 77 % 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#8 0.885 U ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#18 1.34 U ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#28 548 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#31 66.2 J ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#44 26.2 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#45 0.723 U ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#47 865 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#49 447 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#52 336 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#56 243 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#66 989 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#70 162 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#74 887 J ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#77 0.506 U ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#81 0.668 U ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#87 171 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#95 44.9 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 9 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#99 496 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#101 404 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#105 292 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#110 104 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#114 41.5 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#118 676 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#123 0.578 U ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#126 0.777 U ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#128 19.9 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#138 520 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#146 99.8 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#149 115 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#151 5.64 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#153 445 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#156 65.6 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#157 9.44 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#158 86.1 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#167 68.0 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#169 30.7 U ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#170 83.1 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#174 13.2 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#177 25.9 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#180 157 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#183 32.1 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#189 1.50 U ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#187 147 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#194 31.3 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#195 7.94 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#201 37.6 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 10 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#206 15.3 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 BZ#209 3.11 J ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 Monochlorobiphenyls 0.506 U ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 Dichlorobiphenyls 0.885 U ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 Trichlorobiphenyls 502 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 Tetrachlorobiphenyls 4310 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 Pentachlorobiphenyls 3510 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 Hexachlorobiphenyls 1540 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 Heptachlorobiphenyls 338 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 Octachlorobiphenyls 86.2 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 Nonachlorobiphenyls 34.9 ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 Decachlorobiphenyl 3.11 J ug/kg 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 Total Homologs 10300 ug/kg 05/10/2002 CG-109-112 615838 4774754 1 0208034-10 Percent Lipids 6.3 % 5/10/2002 CG-109-112 615838 4774754 1 0208034-10 Percent Moisture 84 % 4/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#8 0.328 U ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#18 0.495 U ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#28 102 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#31 48.6 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#44 5.20 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#45 0.267 U ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#47 311 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#49 152 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#52 159 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#56 57.7 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#66 272 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#70 47.0 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#74 150 J ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#77 0.187 U ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 11 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

4/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#81 0.247 U ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#87 82.7 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#95 21.3 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#99 185 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#101 179 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#105 99.5 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#110 42.9 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#114 0.227 U ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#118 275 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#123 0.214 U ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#126 0.288 U ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#128 9.33 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#138 209 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#146 44.5 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#149 58.6 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#151 3.07 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#153 198 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#156 22.2 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#157 3.83 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#158 16.2 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#167 29.6 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#169 11.4 U ug/kg 4/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#170 43.0 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#174 10.9 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#177 13.5 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#180 79.3 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#183 18.1 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#189 0.555 U ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#187 64.9 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 12 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

4/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#194 17.9 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#195 5.32 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#201 21.9 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#206 9.67 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 BZ#209 2.04 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Monochlorobiphenyls 0.187 U ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Dichlorobiphenyls 0.328 U ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Trichlorobiphenyls 139 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Tetrachlorobiphenyls 1340 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Pentachlorobiphenyls 1480 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Hexachlorobiphenyls 717 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Heptachlorobiphenyls 189 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Octachlorobiphenyls 56.3 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Nonachlorobiphenyls 18.2 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Decachlorobiphenyl 2.04 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Total Homologs 3950 ug/kg 04/29/2002 CG-204-205 608112 4748092 3 0208034-11 Percent Lipids 6.9 % 4/29/2002 CG-204-205 608112 4748092 3 0208034-11 Percent Moisture 84 % 5/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#8 0.0683 U ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#18 0.103 U ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#28 78.6 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#31 13.7 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#44 0.693 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#45 0.0558 U ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#47 180 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#49 97.2 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#52 62.8 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#56 38.4 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#66 155 ug/kg 0.0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 13 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#70 18.1 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#74 106 J ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#77 0.0391 U ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#81 0.0516 U ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#87 42.5 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#95 5.45 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#99 100 ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#101 111 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#105 50.0 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#110 18.6 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#114 5.99 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#118 135 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#123 0.0446 U ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#126 0.0600 U ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#128 3.18 ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#138 90.3 ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#146 18.3 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#149 36.6 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#151 0.0502 U ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#153 75.3 ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#156 7.36 ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#157 0.151 U ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#158 6.12 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#167 13.0 ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#169 2.37 U ug/kg 5/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#170 8.77 ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#174 4.02 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#177 4.12 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#180 16.4 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 14 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#183 4.24 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#189 0.116 U ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#187 33.9 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#194 3.39 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#195 0.906 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#201 6.31 ug/kg 05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#206 2.03 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 BZ#209 0.533 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Monochlorobiphenyls 0.0391 U ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Dichlorobiphenyls 0.0683 U ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Trichlorobiphenyls 82.4 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Tetrachlorobiphenyls 765 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Pentachlorobiphenyls 753 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Hexachlorobiphenyls 292 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Heptachlorobiphenyls 62.2 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Octachlorobiphenyls 13.9 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Nonachlorobiphenyls 4.46 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Decachlorobiphenyl 0.533 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Total Homologs 1970 ug/kg 0.05/9/2002 CG-213-215 614784 4783163 1 0208034-12 Percent Lipids 7.6 % 5/9/2002 CG-213-215 614784 4783163 1 0208034-12 Percent Moisture 82 % 5/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#8 0.0791 U ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#18 0.120 U ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#28 71.2 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#31 28.4 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#44 1.31 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#45 0.0646 U ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#47 137 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#49 83.8 ug/kg 0.0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 15 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#52 72.9 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#56 36.4 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#66 139 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#70 25.6 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#74 91.2 J ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#77 0.0452 U ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#81 0.0597 U ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#87 41.6 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#95 6.06 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#99 97.6 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#101 80.7 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#105 54.1 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#110 20.4 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#114 5.66 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#118 148 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#123 0.0517 U ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#126 0.0694 U ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#128 3.72 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#138 86.7 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#146 16.4 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#149 20.8 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#151 0.627 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#153 82.7 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#156 9.24 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#157 0.174 U ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#158 6.21 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#167 15.7 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#169 2.74 U ug/kg 5/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#170 10.9 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 16 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#174 2.92 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#177 3.75 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#180 18.2 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#183 4.30 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#189 0.134 U ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#187 23.2 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#194 3.63 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#195 0.874 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#201 5.41 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#206 2.50 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 BZ#209 0.699 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Monochlorobiphenyls 0.0452 U ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Dichlorobiphenyls 0.0791 U ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Trichlorobiphenyls 89.6 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Tetrachlorobiphenyls 685 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Pentachlorobiphenyls 741 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Hexachlorobiphenyls 282 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Heptachlorobiphenyls 53.3 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Octachlorobiphenyls 14.0 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Nonachlorobiphenyls 5.14 ug/kg 05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Decachlorobiphenyl 0.699 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Total Homologs 1870 ug/kg 0.05/28/2002 CG-230-233 607624 4748376 3 0208034-13 Percent Lipids 6.8 % 5/28/2002 CG-230-233 607624 4748376 3 0208034-13 Percent Moisture 85 % 4/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#8 0.0810 U ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#18 0.122 U ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#28 77.1 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#31 26.4 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#44 1.43 ug/kg 0.0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 17 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

4/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#45 0.0661 U ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#47 143 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#49 85.5 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#52 65.2 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#56 37.2 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#66 142 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#70 26.4 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#74 94.0 J ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#77 0.0463 U ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#81 0.0612 U ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#87 43.6 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#95 6.35 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#99 101 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#101 83.6 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#105 56.3 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#110 21.3 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#114 5.91 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#118 152 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#123 0.0529 U ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#126 0.0711 U ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#128 4.21 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#138 90.7 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#146 17.1 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#149 21.6 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#151 0.674 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#153 86.7 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#156 9.44 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#157 0.179 U ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#158 5.57 ug/kg 0.0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 18 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

4/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#167 15.9 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#169 2.81 U ug/kg 4/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#170 11.2 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#174 2.96 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#177 4.04 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#180 19.0 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#183 4.48 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#189 0.137 U ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#187 24.5 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#194 3.73 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#195 0.937 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#201 5.89 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#206 2.53 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 BZ#209 0.727 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Monochlorobiphenyls 0.0463 U ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Dichlorobiphenyls 0.0810 U ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Trichlorobiphenyls 93.7 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Tetrachlorobiphenyls 711 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Pentachlorobiphenyls 771 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Hexachlorobiphenyls 295 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Heptachlorobiphenyls 56.2 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Octachlorobiphenyls 14.9 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Nonachlorobiphenyls 5.41 ug/kg 04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Decachlorobiphenyl 0.727 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Total Homologs 1950 ug/kg 0.04/30/2002 CG-602-602 612109 4759551 2 0208034-14 Percent Lipids 7.1 % 4/30/2002 CG-602-602 612109 4759551 2 0208034-14 Percent Moisture 87 % 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#8 0.757 U ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#18 1.14 U ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 19 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#28 402 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#31 234 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#44 136 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#45 0.618 U ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#47 980 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#49 1100 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#52 1190 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#56 389 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#66 2030 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#70 817 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#74 650 J ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#77 0.433 U ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#81 0.572 U ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#87 452 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#95 187 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#99 785 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#101 995 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#105 473 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#110 489 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#114 36.7 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#118 1020 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#123 0.495 U ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#126 0.665 U ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#128 15.3 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#138 409 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#146 74.1 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#149 227 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#151 0.556 U ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#153 310 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 20 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#156 30.8 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#157 1.67 U ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#158 43.4 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#167 71.4 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#169 26.3 U ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#170 41.0 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#174 15.0 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#177 17.1 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#180 61.8 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#183 17.7 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#189 1.28 U ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#187 117 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#194 12.0 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#195 3.94 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#201 27.6 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#206 12.8 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 BZ#209 2.76 J ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Monochlorobiphenyls 0.433 U ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Dichlorobiphenyls 0.757 U ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Trichlorobiphenyls 608 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Tetrachlorobiphenyls 8480 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Pentachlorobiphenyls 7510 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Hexachlorobiphenyls 1450 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Heptachlorobiphenyls 236 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Octachlorobiphenyls 60.2 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Nonachlorobiphenyls 25.7 ug/kg 5/7/2002 CG-607-608 608112 4748092 3 0208034-15 Decachlorobiphenyl 2.76 J ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Total Homologs 18400 ug/kg 05/7/2002 CG-607-608 608112 4748092 3 0208034-15 Percent Lipids 6.5 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 21 of 22
Common Grackle (Quiscalus quiscula) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DE

(wet w

5/7/2002 CG-607-608 608112 4748092 3 0208034-15 Percent Moisture 75 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 22 of 22
Eastern Screech Owl (Otus asio) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

 SAMPLING 

DATE FIELD ID 

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#8 0.0683 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#18 0.103 U ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#28 12.0 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#31 32.5 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#44 0.0836 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#45 0.0557 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#47 270 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#49 0.0683 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#52 0.0418 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#56 71.9 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#66 143 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#70 0.0502 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#74 406 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#77 0.0390 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#81 0.0516 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#87 59.1 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#95 0.0529 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#99 585 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#101 52.8 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#105 280 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#110 16.3 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#114 38.9 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#118 674 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#123 0.0446 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#126 0.0599 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#128 31.5 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#138 939 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#146 153 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#149 13.2 ug/kg 0

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(wet 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 1 of 3
Eastern Screech Owl (Otus asio) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

 SAMPLING 

DATE FIELD ID 

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(wet 

4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#151 0.0502 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#153 1250 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#156 124 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#157 23.8 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#158 82.8 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#167 96.9 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#169 2.37 UJ ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#170 155 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#174 0.0752 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#177 15.7 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#180 284 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#183 55.4 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#189 0.116 U ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#187 152 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#194 37.7 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#195 9.22 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#201 35.6 ug/kg 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#206 17.6 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 BZ#209 3.02 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Monochlorobiphenyls 0.0390 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Dichlorobiphenyls 0.0683 U ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Trichlorobiphenyls 45.3 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Tetrachlorobiphenyls 1230 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Pentachlorobiphenyls 3110 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Hexachlorobiphenyls 3220 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Heptachlorobiphenyls 568 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Octachlorobiphenyls 83.1 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Nonachlorobiphenyls 23.9 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Decachlorobiphenyl 3.06 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 2 of 3
Eastern Screech Owl (Otus asio) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

 SAMPLING 

DATE FIELD ID 

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(wet 

4/24/2002 SO-002-002 614491 4790348 1 0209048-03 Total Homologs 8290 ug/kg 04/24/2002 SO-002-002 614491 4790348 1 0209048-03 Percent Lipids 13 % 4/24/2002 SO-002-002 614491 4790348 1 0209048-03 Percent Moisture 83 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 3 of 3
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

5/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#8 0.270 U ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#18 10.6 ug/kg 0.45/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#28 406 ug/kg 0.095/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#31 413 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#44 7.38 ug/kg 0.35/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#45 0.221 U ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#47 1290 ug/kg 0.35/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#49 587 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#52 292 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#56 159 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#66 631 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#70 145 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#74 508 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#77 12.8 NJ ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#81 5.09 NJ ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#87 230 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#95 37.6 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#99 405 ug/kg 0.45/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#101 376 J ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#105 198 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#110 150 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#114 26.6 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#118 556 ug/kg 0.35/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#123 69.2 NJ ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#126 12.5 NJ ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#128 24.4 ug/kg 0.45/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#138 582 ug/kg 0.45/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#146 111 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#149 111 ug/kg 0.2

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 1 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#151 4.18 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#153 370 ug/kg 0.55/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#156 41.7 ug/kg 0.55/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#157 0.596 U ug/kg 0.55/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#158 37.2 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#167 77.4 ug/kg 0.65/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#169 9.38 UJ ug/kg 95/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#170 72.8 ug/kg 0.55/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#174 12.8 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#177 37.1 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#180 97.7 ug/kg 0.55/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#183 27.9 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#189 3.20 ug/kg 0.45/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#187 129 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#194 23.8 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#195 7.87 ug/kg 0.35/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#201 46.8 ug/kg 0.45/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#206 23.2 ug/kg 0.35/20/2002 RB-026-038 608227 4751887 2 0209045-08 BZ#209 7.10 ug/kg 0.35/20/2002 RB-026-038 608227 4751887 2 0209045-08 Monochlorobiphenyls 0.154 U ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 Dichlorobiphenyls 0.270 U ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 Trichlorobiphenyls 877 ug/kg 0.35/20/2002 RB-026-038 608227 4751887 2 0209045-08 Tetrachlorobiphenyls 4390 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 Pentachlorobiphenyls 3470 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 Hexachlorobiphenyls 1660 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 Heptachlorobiphenyls 329 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 Octachlorobiphenyls 92.6 ug/kg 0.15/20/2002 RB-026-038 608227 4751887 2 0209045-08 Nonachlorobiphenyls 41.0 ug/kg 0.35/20/2002 RB-026-038 608227 4751887 2 0209045-08 Decachlorobiphenyl 7.10 ug/kg 0.3

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 2 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/20/2002 RB-026-038 608227 4751887 2 0209045-08 Total Homologs 10900 ug/kg 0.25/20/2002 RB-026-038 608227 4751887 2 0209045-08 Percent Lipids 10 % 0.5/20/2002 RB-026-038 608227 4751887 2 0209045-08 Percent Moisture 76 % 05/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#8 0.0854 U ug/kg 0.085/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#18 0.129 U ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#28 56.3 ug/kg 0.035/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#31 44.7 ug/kg 0.055/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#44 9.28 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#45 0.0697 U ug/kg 0.065/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#47 123 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#49 37.3 ug/kg 0.085/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#52 25.0 ug/kg 0.055/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#56 60.5 ug/kg 0.075/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#66 247 ug/kg 0.065/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#70 38.3 ug/kg 0.065/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#74 194 ug/kg 0.065/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#77 3.85 NJ ug/kg 0.045/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#81 0.0645 U ug/kg 0.065/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#87 52.9 ug/kg 0.075/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#95 3.40 ug/kg 0.065/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#99 149 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#101 107 J ug/kg 0.055/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#105 111 ug/kg 0.085/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#110 17.5 ug/kg 0.065/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#114 11.9 ug/kg 0.055/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#118 259 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#123 27.8 NJ ug/kg 0.055/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#126 5.15 NJ ug/kg 0.075/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#128 10.8 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 3 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#138 188 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#146 37.6 ug/kg 0.055/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#149 21.4 ug/kg 0.085/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#151 1.34 ug/kg 0.065/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#153 155 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#156 20.8 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#157 3.32 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#158 10.9 ug/kg 0.065/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#167 14.6 ug/kg 0.25/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#169 2.96 UJ ug/kg 25/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#170 18.8 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#174 3.08 ug/kg 0.095/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#177 6.57 ug/kg 0.055/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#180 30.9 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#183 7.15 ug/kg 0.035/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#189 0.145 U ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#187 45.4 ug/kg 0.085/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#194 7.39 ug/kg 0.095/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#195 1.45 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#201 13.0 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#206 4.52 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 BZ#209 0.677 ug/kg 0.095/20/2002 RB-027-039 615337 4768790 2 0209045-09 Monochlorobiphenyls 0.0488 U ug/kg 0.045/20/2002 RB-027-039 615337 4768790 2 0209045-09 Dichlorobiphenyls 0.0854 U ug/kg 0.085/20/2002 RB-027-039 615337 4768790 2 0209045-09 Trichlorobiphenyls 98.2 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 Tetrachlorobiphenyls 820 ug/kg 0.055/20/2002 RB-027-039 615337 4768790 2 0209045-09 Pentachlorobiphenyls 1210 ug/kg 0.075/20/2002 RB-027-039 615337 4768790 2 0209045-09 Hexachlorobiphenyls 560 ug/kg 0.095/20/2002 RB-027-039 615337 4768790 2 0209045-09 Heptachlorobiphenyls 107 ug/kg 0.04

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 4 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/20/2002 RB-027-039 615337 4768790 2 0209045-09 Octachlorobiphenyls 27.3 ug/kg 0.035/20/2002 RB-027-039 615337 4768790 2 0209045-09 Nonachlorobiphenyls 8.10 ug/kg 0.15/20/2002 RB-027-039 615337 4768790 2 0209045-09 Decachlorobiphenyl 0.677 ug/kg 0.095/20/2002 RB-027-039 615337 4768790 2 0209045-09 Total Homologs 2830 ug/kg 0.085/20/2002 RB-027-039 615337 4768790 2 0209045-09 Percent Lipids 5.6 % 0.5/20/2002 RB-027-039 615337 4768790 2 0209045-09 Percent Moisture 81 % 05/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#8 3.64 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#18 17.2 ug/kg 0.25/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#28 345 ug/kg 0.055/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#31 336 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#44 19.0 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#45 0.129 U ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#47 481 ug/kg 0.25/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#49 466 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#52 382 ug/kg 0.095/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#56 147 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#66 671 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#70 169 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#74 424 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#77 13.9 NJ ug/kg 0.095/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#81 0.119 U ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#87 135 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#95 66.1 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#99 325 ug/kg 0.25/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#101 321 J ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#105 181 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#110 134 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#114 17.1 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#118 424 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 5 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#123 49.6 NJ ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#126 5.90 NJ ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#128 15.8 ug/kg 0.25/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#138 289 ug/kg 0.25/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#146 47.7 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#149 103 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#151 10.1 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#153 202 ug/kg 0.35/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#156 28.8 ug/kg 0.35/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#157 4.65 ug/kg 0.35/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#158 21.8 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#167 33.8 ug/kg 0.35/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#169 5.49 UJ ug/kg 55/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#170 28.0 ug/kg 0.35/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#174 9.62 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#177 12.8 ug/kg 0.095/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#180 41.5 ug/kg 0.35/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#183 10.2 ug/kg 0.065/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#189 1.52 ug/kg 0.25/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#187 56.1 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#194 11.3 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#195 2.75 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#201 20.7 ug/kg 0.25/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#206 8.74 ug/kg 0.25/21/2002 RB-028-040 611502 4756036 2 0209045-10 BZ#209 1.46 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 Monochlorobiphenyls 0.0904 U ug/kg 0.095/21/2002 RB-028-040 611502 4756036 2 0209045-10 Dichlorobiphenyls 3.43 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 Trichlorobiphenyls 748 ug/kg 0.25/21/2002 RB-028-040 611502 4756036 2 0209045-10 Tetrachlorobiphenyls 3270 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 6 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-028-040 611502 4756036 2 0209045-10 Pentachlorobiphenyls 2860 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 Hexachlorobiphenyls 899 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 Heptachlorobiphenyls 144 ug/kg 0.085/21/2002 RB-028-040 611502 4756036 2 0209045-10 Octachlorobiphenyls 43.6 ug/kg 0.065/21/2002 RB-028-040 611502 4756036 2 0209045-10 Nonachlorobiphenyls 15.7 ug/kg 0.25/21/2002 RB-028-040 611502 4756036 2 0209045-10 Decachlorobiphenyl 1.46 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 Total Homologs 7990 ug/kg 0.15/21/2002 RB-028-040 611502 4756036 2 0209045-10 Percent Lipids 6.6 % 0.5/21/2002 RB-028-040 611502 4756036 2 0209045-10 Percent Moisture 82 % 05/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#8 0.0818 U ug/kg 0.085/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#18 0.124 U ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#28 19.9 J ug/kg 0.035/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#31 11.6 J ug/kg 0.055/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#44 1.53 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#45 0.0668 U ug/kg 0.065/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#47 68.0 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#49 9.64 J ug/kg 0.085/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#52 7.44 J ug/kg 0.055/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#56 24.6 J ug/kg 0.075/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#66 117 J ug/kg 0.065/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#70 6.16 J ug/kg 0.065/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#74 105 J ug/kg 0.065/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#77 0.0467 U ug/kg 0.045/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#81 0.0618 U ug/kg 0.065/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#87 29.7 J ug/kg 0.075/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#95 0.914 J ug/kg 0.065/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#99 85.7 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#101 45.4 J ug/kg 0.055/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#105 51.7 J ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 7 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#110 4.73 J ug/kg 0.065/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#114 6.22 J ug/kg 0.055/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#118 175 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#123 15.7 NJ ug/kg 0.055/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#126 3.53 NJ ug/kg 0.075/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#128 8.62 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#138 120 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#146 29.4 J ug/kg 0.055/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#149 7.40 J ug/kg 0.085/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#151 0.0601 U ug/kg 0.065/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#153 111 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#156 17.2 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#157 2.66 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#158 8.05 J ug/kg 0.065/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#167 11.6 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#169 2.84 UJ ug/kg 25/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#170 15.0 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#174 1.61 J ug/kg 0.095/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#177 5.31 J ug/kg 0.055/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#180 33.5 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#183 6.22 J ug/kg 0.035/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#189 0.139 U ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#187 38.0 J ug/kg 0.075/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#194 6.69 J ug/kg 0.085/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#195 1.23 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#201 13.8 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#206 4.12 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 BZ#209 1.31 J ug/kg 0.095/21/2002 RB-029-041 607710 4748204 3 0209045-11 Monochlorobiphenyls 0.0467 U ug/kg 0.04

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 8 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-029-041 607710 4748204 3 0209045-11 Dichlorobiphenyls 0.0818 U ug/kg 0.085/21/2002 RB-029-041 607710 4748204 3 0209045-11 Trichlorobiphenyls 30.9 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 Tetrachlorobiphenyls 362 J ug/kg 0.045/21/2002 RB-029-041 607710 4748204 3 0209045-11 Pentachlorobiphenyls 664 J ug/kg 0.075/21/2002 RB-029-041 607710 4748204 3 0209045-11 Hexachlorobiphenyls 372 J ug/kg 0.085/21/2002 RB-029-041 607710 4748204 3 0209045-11 Heptachlorobiphenyls 91.9 J ug/kg 0.045/21/2002 RB-029-041 607710 4748204 3 0209045-11 Octachlorobiphenyls 25.9 J ug/kg 0.035/21/2002 RB-029-041 607710 4748204 3 0209045-11 Nonachlorobiphenyls 7.74 J ug/kg 0.15/21/2002 RB-029-041 607710 4748204 3 0209045-11 Decachlorobiphenyl 1.31 J ug/kg 0.095/21/2002 RB-029-041 607710 4748204 3 0209045-11 Total Homologs 1560 J ug/kg 0.085/21/2002 RB-029-041 607710 4748204 3 0209045-11 Percent Lipids 7.0 % 0.5/21/2002 RB-029-041 607710 4748204 3 0209045-11 Percent Moisture 79 % 05/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#8 0.162 U ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#18 0.245 U ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#28 33.2 ug/kg 0.055/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#31 21.0 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#44 2.30 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#45 0.133 U ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#47 69.3 ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#49 36.9 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#52 46.4 ug/kg 0.095/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#56 21.5 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#66 84.2 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#70 34.4 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#74 72.1 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#77 3.53 NJ ug/kg 0.095/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#81 0.123 U ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#87 30.7 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#95 6.46 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 9 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#99 50.0 ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#101 63.6 J ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#105 37.1 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#110 31.4 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#114 5.39 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#118 110 ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#123 11.2 NJ ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#126 3.82 NJ ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#128 5.64 ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#138 83.4 ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#146 18.6 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#149 16.9 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#151 2.96 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#153 67.2 ug/kg 0.35/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#156 11.6 ug/kg 0.35/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#157 1.88 ug/kg 0.35/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#158 6.86 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#167 7.58 ug/kg 0.35/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#169 5.64 UJ ug/kg 55/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#170 12.1 ug/kg 0.35/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#174 3.34 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#177 4.22 ug/kg 0.095/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#180 23.4 ug/kg 0.35/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#183 3.70 ug/kg 0.065/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#189 0.275 U ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#187 25.9 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#194 6.57 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#195 1.16 ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#201 10.4 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 10 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#206 3.30 ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 BZ#209 1.84 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 Monochlorobiphenyls 0.0929 U ug/kg 0.095/21/2002 RB-030-042 607664 4748326 3 0209045-12 Dichlorobiphenyls 0.162 U ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 Trichlorobiphenyls 55.3 ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 Tetrachlorobiphenyls 437 ug/kg 0.095/21/2002 RB-030-042 607664 4748326 3 0209045-12 Pentachlorobiphenyls 602 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 Hexachlorobiphenyls 265 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 Heptachlorobiphenyls 65.2 ug/kg 0.085/21/2002 RB-030-042 607664 4748326 3 0209045-12 Octachlorobiphenyls 49.8 ug/kg 0.065/21/2002 RB-030-042 607664 4748326 3 0209045-12 Nonachlorobiphenyls 6.42 ug/kg 0.25/21/2002 RB-030-042 607664 4748326 3 0209045-12 Decachlorobiphenyl 1.84 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 Total Homologs 1480 ug/kg 0.15/21/2002 RB-030-042 607664 4748326 3 0209045-12 Percent Lipids 9.1 % 0.5/21/2002 RB-030-042 607664 4748326 3 0209045-12 Percent Moisture 79 % 05/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#8 0.0995 U ug/kg 0.095/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#18 0.150 U ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#28 3.49 ug/kg 0.035/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#31 4.10 ug/kg 0.065/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#44 0.233 J ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#45 0.0813 U ug/kg 0.085/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#47 12.7 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#49 5.03 ug/kg 0.095/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#52 5.40 ug/kg 0.065/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#56 2.90 ug/kg 0.085/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#66 8.68 ug/kg 0.075/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#70 3.39 ug/kg 0.075/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#74 9.46 ug/kg 0.075/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#77 0.0569 U ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 11 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#81 0.0752 U ug/kg 0.075/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#87 5.51 ug/kg 0.085/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#95 0.725 ug/kg 0.075/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#99 9.82 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#101 7.88 J ug/kg 0.065/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#105 6.62 ug/kg 0.095/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#110 2.94 ug/kg 0.075/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#114 0.0691 U ug/kg 0.065/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#118 18.6 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#123 2.08 NJ ug/kg 0.065/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#126 0.0874 UJ ug/kg 0.085/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#128 1.07 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#138 23.6 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#146 5.40 ug/kg 0.065/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#149 2.60 ug/kg 0.095/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#151 0.427 ug/kg 0.075/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#153 22.0 ug/kg 0.25/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#156 2.61 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#157 0.440 J ug/kg 0.25/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#158 1.67 ug/kg 0.075/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#167 2.08 ug/kg 0.25/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#169 3.45 UJ ug/kg 35/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#170 4.39 ug/kg 0.25/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#174 0.776 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#177 2.11 ug/kg 0.065/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#180 7.65 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#183 2.10 ug/kg 0.035/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#189 0.169 U ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#187 8.29 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 12 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#194 2.39 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#195 0.479 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#201 2.78 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#206 1.36 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 BZ#209 0.996 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 Monochlorobiphenyls 0.0569 U ug/kg 0.055/21/2002 RB-031-043 612128 4758348 2 0209045-13 Dichlorobiphenyls 0.0995 U ug/kg 0.095/21/2002 RB-031-043 612128 4758348 2 0209045-13 Trichlorobiphenyls 7.80 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 Tetrachlorobiphenyls 54.2 ug/kg 0.055/21/2002 RB-031-043 612128 4758348 2 0209045-13 Pentachlorobiphenyls 93.1 ug/kg 0.085/21/2002 RB-031-043 612128 4758348 2 0209045-13 Hexachlorobiphenyls 73.2 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 Heptachlorobiphenyls 21.8 ug/kg 0.055/21/2002 RB-031-043 612128 4758348 2 0209045-13 Octachlorobiphenyls 9.28 ug/kg 0.035/21/2002 RB-031-043 612128 4758348 2 0209045-13 Nonachlorobiphenyls 2.41 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 Decachlorobiphenyl 0.996 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 Total Homologs 263 ug/kg 0.15/21/2002 RB-031-043 612128 4758348 2 0209045-13 Percent Lipids 6.8 % 0.5/21/2002 RB-031-043 612128 4758348 2 0209045-13 Percent Moisture 70 % 05/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#8 0.395 U ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#18 0.718 J ug/kg 0.55/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#28 248 ug/kg 0.15/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#31 214 ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#44 25.2 ug/kg 0.45/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#45 0.322 U ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#47 424 ug/kg 0.45/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#49 271 ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#52 263 ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#56 278 ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#66 1280 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 13 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#70 219 ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#74 853 ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#77 12.5 NJ ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#81 0.298 U ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#87 231 ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#95 42.4 ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#99 564 ug/kg 0.55/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#101 599 J ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#105 294 ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#110 170 ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#114 35.2 ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#118 969 ug/kg 0.55/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#123 93.7 NJ ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#126 10.8 NJ ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#128 40.4 ug/kg 0.75/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#138 654 ug/kg 0.65/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#146 119 ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#149 143 ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#151 7.08 ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#153 534 ug/kg 0.85/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#156 56.9 ug/kg 0.75/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#157 10.2 ug/kg 0.85/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#158 41.8 ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#167 65.0 ug/kg 0.95/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#169 13.7 UJ ug/kg 15/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#170 55.5 ug/kg 0.85/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#174 13.5 ug/kg 0.45/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#177 22.0 ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#180 91.9 ug/kg 0.7

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 14 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#183 21.9 ug/kg 0.15/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#189 0.669 UJ ug/kg 0.65/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#187 135 ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#194 19.9 ug/kg 0.45/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#195 4.46 ug/kg 0.45/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#201 39.9 ug/kg 0.75/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#206 15.5 ug/kg 0.55/21/2002 RB-032-044 615646 4769212 2 0209045-14 BZ#209 2.98 ug/kg 0.45/21/2002 RB-032-044 615646 4769212 2 0209045-14 Monochlorobiphenyls 0.226 U ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 Dichlorobiphenyls 0.395 U ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 Trichlorobiphenyls 453 ug/kg 0.55/21/2002 RB-032-044 615646 4769212 2 0209045-14 Tetrachlorobiphenyls 4200 ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 Pentachlorobiphenyls 4830 ug/kg 0.35/21/2002 RB-032-044 615646 4769212 2 0209045-14 Hexachlorobiphenyls 2020 ug/kg 0.45/21/2002 RB-032-044 615646 4769212 2 0209045-14 Heptachlorobiphenyls 319 ug/kg 0.25/21/2002 RB-032-044 615646 4769212 2 0209045-14 Octachlorobiphenyls 81.9 ug/kg 0.15/21/2002 RB-032-044 615646 4769212 2 0209045-14 Nonachlorobiphenyls 28.3 ug/kg 0.55/21/2002 RB-032-044 615646 4769212 2 0209045-14 Decachlorobiphenyl 2.98 ug/kg 0.45/21/2002 RB-032-044 615646 4769212 2 0209045-14 Total Homologs 11900 ug/kg 0.45/21/2002 RB-032-044 615646 4769212 2 0209045-14 Percent Lipids 6.4 % 0.5/21/2002 RB-032-044 615646 4769212 2 0209045-14 Percent Moisture 84 % 05/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#8 0.362 U ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#18 4.19 ug/kg 0.55/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#28 233 ug/kg 0.15/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#31 510 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#44 69.3 ug/kg 0.45/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#45 0.296 U ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#47 1050 ug/kg 0.45/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#49 543 ug/kg 0.3

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 15 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#52 367 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#56 147 ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#66 615 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#70 175 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#74 631 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#77 19.4 NJ ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#81 0.274 U ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#87 341 ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#95 35.9 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#99 465 ug/kg 0.55/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#101 450 J ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#105 250 ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#110 137 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#114 43.8 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#118 1030 ug/kg 0.55/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#123 0.237 U ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#126 24.1 NJ ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#128 53.1 ug/kg 0.65/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#138 755 ug/kg 0.65/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#146 199 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#149 128 ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#151 9.89 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#153 707 ug/kg 0.75/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#156 98.7 ug/kg 0.75/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#157 14.2 ug/kg 0.75/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#158 45.4 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#167 60.0 ug/kg 0.85/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#169 12.6 UJ ug/kg 125/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#170 96.1 ug/kg 0.7

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 16 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#174 13.3 ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#177 32.9 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#180 212 ug/kg 0.65/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#183 41.8 ug/kg 0.15/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#189 0.614 U ug/kg 0.65/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#187 252 ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#194 49.6 ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#195 7.72 ug/kg 0.45/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#201 86.2 ug/kg 0.65/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#206 27.1 ug/kg 0.55/21/2002 RB-033-045 614789 4766139 2 0209045-15 BZ#209 3.25 ug/kg 0.45/21/2002 RB-033-045 614789 4766139 2 0209045-15 Monochlorobiphenyls 0.207 U ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 Dichlorobiphenyls 0.362 U ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 Trichlorobiphenyls 961 ug/kg 0.45/21/2002 RB-033-045 614789 4766139 2 0209045-15 Tetrachlorobiphenyls 4640 ug/kg 0.25/21/2002 RB-033-045 614789 4766139 2 0209045-15 Pentachlorobiphenyls 4120 ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 Hexachlorobiphenyls 2290 ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 Heptachlorobiphenyls 624 ug/kg 0.15/21/2002 RB-033-045 614789 4766139 2 0209045-15 Octachlorobiphenyls 176 ug/kg 0.15/21/2002 RB-033-045 614789 4766139 2 0209045-15 Nonachlorobiphenyls 45.7 ug/kg 0.55/21/2002 RB-033-045 614789 4766139 2 0209045-15 Decachlorobiphenyl 3.25 ug/kg 0.45/21/2002 RB-033-045 614789 4766139 2 0209045-15 Total Homologs 12900 ug/kg 0.35/21/2002 RB-033-045 614789 4766139 2 0209045-15 Percent Lipids 7.5 % 0.5/21/2002 RB-033-045 614789 4766139 2 0209045-15 Percent Moisture 79 % 05/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#8 7.52 J ug/kg 0.65/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#18 14.8 ug/kg 0.95/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#28 293 ug/kg 0.25/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#31 325 ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#44 15.4 ug/kg 0.7

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 17 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#45 0.513 U ug/kg 0.55/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#47 534 ug/kg 0.75/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#49 349 ug/kg 0.65/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#52 353 ug/kg 0.35/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#56 188 ug/kg 0.55/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#66 683 ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#70 251 ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#74 574 ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#77 20.5 NJ ug/kg 0.35/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#81 0.475 U ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#87 233 ug/kg 0.55/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#95 54.5 ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#99 411 ug/kg 0.95/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#101 426 ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#105 249 ug/kg 0.55/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#110 158 ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#114 44.1 ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#118 1030 ug/kg 0.85/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#123 0.411 U ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#126 15.9 NJ ug/kg 0.55/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#128 63.6 ug/kg 15/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#138 761 ug/kg 15/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#146 176 ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#149 117 ug/kg 0.65/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#151 17.6 ug/kg 0.45/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#153 718 ug/kg 15/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#156 117 ug/kg 15/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#157 16.5 ug/kg 15/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#158 51.6 ug/kg 0.4

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 18 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#167 71.4 ug/kg 15/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#169 21.8 U ug/kg 25/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#170 94.9 ug/kg 15/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#174 19.0 J ug/kg 0.65/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#177 24.4 ug/kg 0.35/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#180 219 ug/kg 15/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#183 38.0 ug/kg 0.25/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#189 7.43 ug/kg 15/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#187 199 ug/kg 0.65/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#194 47.6 ug/kg 0.65/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#195 7.35 ug/kg 0.75/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#201 67.9 ug/kg 15/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#206 24.1 ug/kg 0.85/21/2002 RB-034-046 615313 4767576 2 0209046-01 BZ#209 3.27 ug/kg 0.75/21/2002 RB-034-046 615313 4767576 2 0209046-01 Monochlorobiphenyls 0.359 UJ ug/kg 0.35/21/2002 RB-034-046 615313 4767576 2 0209046-01 Dichlorobiphenyls 7.52 ug/kg 0.65/21/2002 RB-034-046 615313 4767576 2 0209046-01 Trichlorobiphenyls 699 ug/kg 0.85/21/2002 RB-034-046 615313 4767576 2 0209046-01 Tetrachlorobiphenyls 3850 ug/kg 0.35/21/2002 RB-034-046 615313 4767576 2 0209046-01 Pentachlorobiphenyls 4230 ug/kg 0.55/21/2002 RB-034-046 615313 4767576 2 0209046-01 Hexachlorobiphenyls 2410 ug/kg 0.65/21/2002 RB-034-046 615313 4767576 2 0209046-01 Heptachlorobiphenyls 539 ug/kg 0.35/21/2002 RB-034-046 615313 4767576 2 0209046-01 Octachlorobiphenyls 157 ug/kg 0.25/21/2002 RB-034-046 615313 4767576 2 0209046-01 Nonachlorobiphenyls 40.7 ug/kg 0.85/21/2002 RB-034-046 615313 4767576 2 0209046-01 Decachlorobiphenyl 3.27 ug/kg 0.75/21/2002 RB-034-046 615313 4767576 2 0209046-01 Total Homologs 11900 ug/kg 0.65/21/2002 RB-034-046 615313 4767576 2 0209046-01 Percent Lipids 5.2 % 0.5/21/2002 RB-034-046 615313 4767576 2 0209046-01 Percent Moisture 79 % 05/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#8 0.190 UJ ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#18 0.287 U ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 19 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#28 7.82 ug/kg 0.065/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#31 7.40 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#44 0.232 U ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#45 0.155 U ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#47 19.6 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#49 6.14 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#52 3.45 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#56 6.14 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#66 25.8 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#70 5.20 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#74 25.2 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#77 0.108 U ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#81 0.143 U ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#87 9.96 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#95 0.691 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#99 31.0 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#101 17.0 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#105 18.5 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#110 3.45 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#114 2.64 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#118 71.8 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#123 0.124 U ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#126 1.70 NJ ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#128 5.15 ug/kg 0.35/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#138 64.6 ug/kg 0.35/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#146 16.5 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#149 4.88 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#151 0.139 U ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#153 88.8 ug/kg 0.3

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 20 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#156 8.58 ug/kg 0.35/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#157 2.29 ug/kg 0.45/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#158 5.92 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#167 8.02 ug/kg 0.45/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#169 6.58 U ug/kg 65/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#170 15.5 ug/kg 0.35/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#174 1.50 J ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#177 2.59 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#180 28.3 ug/kg 0.35/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#183 6.88 ug/kg 0.075/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#189 0.321 U ug/kg 0.35/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#187 18.9 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#194 10.1 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#195 1.58 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#201 7.50 ug/kg 0.35/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#206 5.20 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 BZ#209 1.18 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 Monochlorobiphenyls 0.108 UJ ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 Dichlorobiphenyls 0.190 U ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 Trichlorobiphenyls 13.6 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 Tetrachlorobiphenyls 107 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 Pentachlorobiphenyls 238 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 Hexachlorobiphenyls 230 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 Heptachlorobiphenyls 65.3 ug/kg 0.095/22/2002 RB-035-047 611297 4755957 2 0209046-02 Octachlorobiphenyls 30.7 ug/kg 0.075/22/2002 RB-035-047 611297 4755957 2 0209046-02 Nonachlorobiphenyls 8.46 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 Decachlorobiphenyl 1.18 ug/kg 0.25/22/2002 RB-035-047 611297 4755957 2 0209046-02 Total Homologs 695 ug/kg 0.15/22/2002 RB-035-047 611297 4755957 2 0209046-02 Percent Lipids 7.5 % 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 21 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-035-047 611297 4755957 2 0209046-02 Percent Moisture 82 % 05/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#8 0.118 UJ ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#18 0.178 U ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#28 2.17 ug/kg 0.045/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#31 1.56 ug/kg 0.085/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#44 0.144 U ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#45 0.0960 U ug/kg 0.095/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#47 1.79 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#49 0.811 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#52 0.704 ug/kg 0.075/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#56 0.103 U ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#66 5.49 ug/kg 0.085/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#70 1.50 ug/kg 0.085/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#74 3.26 ug/kg 0.095/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#77 0.0672 U ug/kg 0.065/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#81 0.0888 U ug/kg 0.085/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#87 1.21 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#95 0.0912 U ug/kg 0.095/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#99 3.47 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#101 2.36 ug/kg 0.085/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#105 3.66 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#110 0.765 ug/kg 0.085/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#114 0.0816 U ug/kg 0.085/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#118 9.60 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#123 0.0768 U ug/kg 0.075/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#126 0.103 U ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#128 0.734 ug/kg 0.25/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#138 8.56 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#146 1.85 ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 22 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#149 0.826 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#151 0.0864 U ug/kg 0.085/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#153 11.7 ug/kg 0.25/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#156 1.91 ug/kg 0.25/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#157 0.259 U ug/kg 0.25/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#158 0.551 ug/kg 0.095/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#167 0.841 J ug/kg 0.25/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#169 4.08 U ug/kg 45/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#170 1.99 ug/kg 0.25/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#174 0.130 UJ ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#177 0.0720 U ug/kg 0.075/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#180 3.38 ug/kg 0.25/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#183 0.673 ug/kg 0.045/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#189 0.199 U ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#187 3.24 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#194 0.673 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#195 0.168 J ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#201 1.32 ug/kg 0.25/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#206 0.566 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 BZ#209 0.214 J ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 Monochlorobiphenyls 0.0672 UJ ug/kg 0.065/22/2002 RB-036-048 614540 4764635 2 0209046-03 Dichlorobiphenyls 0.118 U ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 Trichlorobiphenyls 4.79 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 Tetrachlorobiphenyls 13.1 ug/kg 0.065/22/2002 RB-036-048 614540 4764635 2 0209046-03 Pentachlorobiphenyls 32.8 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 Hexachlorobiphenyls 29.5 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 Heptachlorobiphenyls 9.45 ug/kg 0.065/22/2002 RB-036-048 614540 4764635 2 0209046-03 Octachlorobiphenyls 7.23 ug/kg 0.045/22/2002 RB-036-048 614540 4764635 2 0209046-03 Nonachlorobiphenyls 0.673 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 23 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-036-048 614540 4764635 2 0209046-03 Decachlorobiphenyl 0.214 J ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 Total Homologs 97.7 ug/kg 0.15/22/2002 RB-036-048 614540 4764635 2 0209046-03 Percent Lipids 4.0 % 0.5/22/2002 RB-036-048 614540 4764635 2 0209046-03 Percent Moisture 84 % 05/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#8 0.131 UJ ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#18 0.443 J ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#28 47.8 ug/kg 0.045/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#31 77.4 ug/kg 0.095/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#44 1.94 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#45 0.107 U ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#47 186 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#49 92.3 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#52 69.4 ug/kg 0.085/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#56 36.4 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#66 288 ug/kg 0.095/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#70 59.0 ug/kg 0.095/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#74 298 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#77 5.87 NJ ug/kg 0.075/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#81 0.0991 U ug/kg 0.095/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#87 73.9 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#95 9.77 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#99 171 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#101 164 ug/kg 0.095/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#105 99.8 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#110 60.1 ug/kg 0.095/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#114 11.4 ug/kg 0.095/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#118 439 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#123 0.0857 U ug/kg 0.085/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#126 7.21 NJ ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 24 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#128 17.8 ug/kg 0.25/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#138 253 ug/kg 0.25/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#146 66.5 ug/kg 0.085/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#149 49.6 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#151 3.91 ug/kg 0.095/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#153 304 ug/kg 0.25/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#156 30.0 ug/kg 0.25/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#157 5.54 ug/kg 0.25/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#158 23.2 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#167 34.9 ug/kg 0.35/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#169 4.55 U ug/kg 45/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#170 31.6 ug/kg 0.25/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#174 8.37 J ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#177 13.0 ug/kg 0.085/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#180 53.0 ug/kg 0.25/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#183 14.4 ug/kg 0.055/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#189 3.96 ug/kg 0.25/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#187 68.5 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#194 13.1 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#195 2.68 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#201 19.8 ug/kg 0.25/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#206 8.97 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 BZ#209 4.02 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 Monochlorobiphenyls 0.0750 UJ ug/kg 0.075/22/2002 RB-037-049 615155 4776122 1 0209046-04 Dichlorobiphenyls 0.131 U ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 Trichlorobiphenyls 124 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 Tetrachlorobiphenyls 1300 ug/kg 0.075/22/2002 RB-037-049 615155 4776122 1 0209046-04 Pentachlorobiphenyls 1590 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 Hexachlorobiphenyls 871 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 25 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-037-049 615155 4776122 1 0209046-04 Heptachlorobiphenyls 175 ug/kg 0.065/22/2002 RB-037-049 615155 4776122 1 0209046-04 Octachlorobiphenyls 48.7 ug/kg 0.055/22/2002 RB-037-049 615155 4776122 1 0209046-04 Nonachlorobiphenyls 16.5 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 Decachlorobiphenyl 4.02 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 Total Homologs 4130 ug/kg 0.15/22/2002 RB-037-049 615155 4776122 1 0209046-04 Percent Lipids 6.2 % 0.5/22/2002 RB-037-049 615155 4776122 1 0209046-04 Percent Moisture 78 % 05/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#8 0.127 UJ ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#18 0.191 U ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#28 12.1 ug/kg 0.045/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#31 15.0 ug/kg 0.085/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#44 0.155 U ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#45 0.103 U ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#47 25.2 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#49 7.15 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#52 5.99 ug/kg 0.075/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#56 8.37 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#66 31.9 ug/kg 0.095/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#70 8.00 ug/kg 0.095/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#74 27.9 ug/kg 0.095/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#77 0.0724 U ug/kg 0.075/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#81 0.0957 U ug/kg 0.095/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#87 9.78 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#95 0.642 ug/kg 0.095/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#99 19.4 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#101 20.3 ug/kg 0.085/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#105 16.5 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#110 4.31 ug/kg 0.095/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#114 1.43 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 26 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#118 54.9 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#123 0.0827 U ug/kg 0.085/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#126 1.93 NJ ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#128 2.62 ug/kg 0.25/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#138 34.4 ug/kg 0.25/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#146 8.50 ug/kg 0.085/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#149 4.10 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#151 0.0931 U ug/kg 0.095/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#153 41.3 ug/kg 0.25/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#156 4.81 ug/kg 0.25/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#157 0.279 U ug/kg 0.25/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#158 2.67 ug/kg 0.095/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#167 3.20 ug/kg 0.35/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#169 4.40 U ug/kg 45/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#170 5.09 ug/kg 0.25/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#174 0.972 J ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#177 1.88 ug/kg 0.075/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#180 10.7 ug/kg 0.25/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#183 2.32 ug/kg 0.045/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#189 0.215 U ug/kg 0.25/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#187 11.8 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#194 3.21 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#195 0.511 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#201 4.66 ug/kg 0.25/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#206 2.03 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 BZ#209 0.544 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 Monochlorobiphenyls 0.0724 UJ ug/kg 0.075/22/2002 RB-038-050 614473 4790129 1 0209046-05 Dichlorobiphenyls 0.127 U ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 Trichlorobiphenyls 24.8 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 27 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-038-050 614473 4790129 1 0209046-05 Tetrachlorobiphenyls 135 ug/kg 0.075/22/2002 RB-038-050 614473 4790129 1 0209046-05 Pentachlorobiphenyls 201 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 Hexachlorobiphenyls 111 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 Heptachlorobiphenyls 30.1 ug/kg 0.065/22/2002 RB-038-050 614473 4790129 1 0209046-05 Octachlorobiphenyls 20.3 ug/kg 0.045/22/2002 RB-038-050 614473 4790129 1 0209046-05 Nonachlorobiphenyls 3.23 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 Decachlorobiphenyl 0.544 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 Total Homologs 525 ug/kg 0.15/22/2002 RB-038-050 614473 4790129 1 0209046-05 Percent Lipids 5.9 % 0.5/22/2002 RB-038-050 614473 4790129 1 0209046-05 Percent Moisture 84 % 05/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#8 0.141 UJ ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#18 0.213 U ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#28 6.22 ug/kg 0.055/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#31 7.23 ug/kg 0.095/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#44 0.173 U ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#45 0.115 U ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#47 25.5 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#49 9.13 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#52 5.01 ug/kg 0.085/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#56 8.03 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#66 34.2 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#70 6.57 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#74 31.9 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#77 0.0806 U ug/kg 0.085/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#81 0.107 U ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#87 17.9 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#95 0.899 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#99 42.4 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#101 17.0 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 28 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#105 32.5 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#110 4.40 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#114 4.31 ug/kg 0.095/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#118 105 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#123 0.0922 U ug/kg 0.095/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#126 4.81 NJ ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#128 6.75 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#138 101 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#146 25.5 ug/kg 0.095/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#149 4.82 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#151 0.104 U ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#153 96.5 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#156 13.2 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#157 2.15 ug/kg 0.35/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#158 7.74 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#167 10.8 ug/kg 0.35/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#169 4.90 U ug/kg 45/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#170 20.4 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#174 0.156 UJ ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#177 4.93 ug/kg 0.085/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#180 39.7 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#183 9.94 ug/kg 0.055/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#189 0.239 U ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#187 35.0 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#194 10.7 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#195 2.82 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#201 14.6 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#206 7.21 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 BZ#209 1.52 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 29 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-039-051 614013 4789462 1 0209046-06 Monochlorobiphenyls 0.0806 UJ ug/kg 0.085/22/2002 RB-039-051 614013 4789462 1 0209046-06 Dichlorobiphenyls 0.141 U ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 Trichlorobiphenyls 12.3 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 Tetrachlorobiphenyls 124 ug/kg 0.085/22/2002 RB-039-051 614013 4789462 1 0209046-06 Pentachlorobiphenyls 335 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 Hexachlorobiphenyls 304 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 Heptachlorobiphenyls 103 ug/kg 0.075/22/2002 RB-039-051 614013 4789462 1 0209046-06 Octachlorobiphenyls 41.8 ug/kg 0.055/22/2002 RB-039-051 614013 4789462 1 0209046-06 Nonachlorobiphenyls 12.9 ug/kg 0.25/22/2002 RB-039-051 614013 4789462 1 0209046-06 Decachlorobiphenyl 1.52 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 Total Homologs 934 ug/kg 0.15/22/2002 RB-039-051 614013 4789462 1 0209046-06 Percent Lipids 6.7 % 0.5/22/2002 RB-039-051 614013 4789462 1 0209046-06 Percent Moisture 83 % 05/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#8 0.142 UJ ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#18 0.215 U ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#28 1.50 ug/kg 0.055/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#31 1.56 ug/kg 0.095/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#44 0.174 U ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#45 0.116 U ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#47 8.82 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#49 0.982 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#52 0.556 ug/kg 0.085/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#56 0.125 U ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#66 7.84 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#70 1.19 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#74 8.65 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#77 0.0814 U ug/kg 0.085/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#81 0.108 U ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#87 0.125 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 30 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#95 0.130 J ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#99 9.02 ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#101 5.19 ug/kg 0.095/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#105 6.74 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#110 0.834 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#114 0.834 ug/kg 0.095/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#118 21.8 ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#123 0.0931 U ug/kg 0.095/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#126 0.722 NJ ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#128 1.43 ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#138 18.8 ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#146 4.80 ug/kg 0.095/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#149 1.48 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#151 0.105 U ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#153 22.7 ug/kg 0.35/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#156 2.78 ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#157 0.778 J ug/kg 0.35/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#158 1.30 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#167 1.85 ug/kg 0.35/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#169 4.94 U ug/kg 45/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#170 3.48 ug/kg 0.35/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#174 0.157 UJ ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#177 0.945 ug/kg 0.085/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#180 6.28 ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#183 1.35 ug/kg 0.055/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#189 0.241 U ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#187 5.65 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#194 1.80 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#195 0.389 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 31 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#201 2.17 ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#206 1.02 ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 BZ#209 0.259 J ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 Monochlorobiphenyls 0.0814 UJ ug/kg 0.085/22/2002 RB-041-053 614696 4783391 1 0209046-07 Dichlorobiphenyls 0.142 U ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 Trichlorobiphenyls 3.07 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 Tetrachlorobiphenyls 37.7 ug/kg 0.085/22/2002 RB-041-053 614696 4783391 1 0209046-07 Pentachlorobiphenyls 73.8 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 Hexachlorobiphenyls 63.2 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 Heptachlorobiphenyls 16.2 ug/kg 0.075/22/2002 RB-041-053 614696 4783391 1 0209046-07 Octachlorobiphenyls 6.78 ug/kg 0.055/22/2002 RB-041-053 614696 4783391 1 0209046-07 Nonachlorobiphenyls 1.85 ug/kg 0.25/22/2002 RB-041-053 614696 4783391 1 0209046-07 Decachlorobiphenyl 0.259 J ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 Total Homologs 203 ug/kg 0.15/22/2002 RB-041-053 614696 4783391 1 0209046-07 Percent Lipids 3.7 % 0.5/22/2002 RB-041-053 614696 4783391 1 0209046-07 Percent Moisture 80 % 05/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#8 0.127 UJ ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#18 0.191 U ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#28 29.9 ug/kg 0.045/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#31 51.0 ug/kg 0.085/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#44 0.155 U ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#45 0.103 U ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#47 114 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#49 45.6 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#52 15.0 ug/kg 0.075/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#56 19.0 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#66 62.2 ug/kg 0.095/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#70 14.3 ug/kg 0.095/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#74 57.2 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 32 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#77 0.0724 U ug/kg 0.075/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#81 0.0956 U ug/kg 0.095/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#87 33.2 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#95 1.47 ug/kg 0.095/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#99 43.8 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#101 36.7 ug/kg 0.085/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#105 31.2 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#110 7.80 ug/kg 0.095/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#114 3.46 ug/kg 0.085/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#118 86.8 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#123 0.0827 U ug/kg 0.085/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#126 4.38 NJ ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#128 4.91 ug/kg 0.25/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#138 87.7 ug/kg 0.25/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#146 21.9 ug/kg 0.085/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#149 7.48 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#151 0.0931 U ug/kg 0.095/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#153 68.3 ug/kg 0.25/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#156 8.12 ug/kg 0.25/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#157 1.73 ug/kg 0.25/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#158 6.65 ug/kg 0.095/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#167 8.83 ug/kg 0.35/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#169 4.39 U ug/kg 45/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#170 11.2 ug/kg 0.25/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#174 1.43 J ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#177 6.54 ug/kg 0.075/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#180 17.6 ug/kg 0.25/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#183 4.68 ug/kg 0.045/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#189 0.215 U ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 33 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#187 22.3 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#194 4.77 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#195 1.22 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#201 7.28 ug/kg 0.25/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#206 3.39 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 BZ#209 0.856 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 Monochlorobiphenyls 0.0724 UJ ug/kg 0.075/23/2002 RB-042-054 615589 4785064 1 0209046-08 Dichlorobiphenyls 0.127 U ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 Trichlorobiphenyls 73.3 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 Tetrachlorobiphenyls 413 ug/kg 0.075/23/2002 RB-042-054 615589 4785064 1 0209046-08 Pentachlorobiphenyls 376 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 Hexachlorobiphenyls 245 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 Heptachlorobiphenyls 63.6 ug/kg 0.065/23/2002 RB-042-054 615589 4785064 1 0209046-08 Octachlorobiphenyls 18.7 ug/kg 0.045/23/2002 RB-042-054 615589 4785064 1 0209046-08 Nonachlorobiphenyls 5.86 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 Decachlorobiphenyl 0.856 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 Total Homologs 1200 ug/kg 0.15/23/2002 RB-042-054 615589 4785064 1 0209046-08 Percent Lipids 4.4 % 0.5/23/2002 RB-042-054 615589 4785064 1 0209046-08 Percent Moisture 86 % 05/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#8 0.142 UJ ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#18 0.215 U ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#28 36.9 ug/kg 0.055/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#31 46.0 ug/kg 0.095/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#44 0.174 U ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#45 0.116 U ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#47 138 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#49 56.8 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#52 56.1 ug/kg 0.085/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#56 28.1 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 34 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#66 118 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#70 31.2 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#74 142 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#77 0.0813 U ug/kg 0.085/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#81 0.107 U ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#87 40.5 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#95 7.47 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#99 76.6 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#101 83.7 ug/kg 0.095/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#105 52.5 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#110 29.9 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#114 8.14 ug/kg 0.095/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#118 175 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#123 0.0929 U ug/kg 0.095/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#126 5.57 NJ ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#128 7.40 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#138 126 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#146 31.3 ug/kg 0.095/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#149 24.0 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#151 3.42 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#153 125 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#156 14.0 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#157 2.42 ug/kg 0.35/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#158 7.64 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#167 12.1 ug/kg 0.35/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#169 4.94 U ug/kg 45/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#170 16.5 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#174 4.51 J ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#177 6.75 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 35 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#180 33.5 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#183 7.08 ug/kg 0.055/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#189 0.241 U ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#187 43.3 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#194 8.23 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#195 1.41 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#201 14.0 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#206 6.21 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 BZ#209 1.35 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 Monochlorobiphenyls 0.0813 UJ ug/kg 0.085/23/2002 RB-109-111 608021 4748989 3 0209046-09 Dichlorobiphenyls 0.142 U ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 Trichlorobiphenyls 77.5 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 Tetrachlorobiphenyls 630 ug/kg 0.085/23/2002 RB-109-111 608021 4748989 3 0209046-09 Pentachlorobiphenyls 754 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 Hexachlorobiphenyls 399 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 Heptachlorobiphenyls 102 ug/kg 0.075/23/2002 RB-109-111 608021 4748989 3 0209046-09 Octachlorobiphenyls 33.5 ug/kg 0.055/23/2002 RB-109-111 608021 4748989 3 0209046-09 Nonachlorobiphenyls 10.4 ug/kg 0.25/23/2002 RB-109-111 608021 4748989 3 0209046-09 Decachlorobiphenyl 1.35 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 Total Homologs 2010 ug/kg 0.15/23/2002 RB-109-111 608021 4748989 3 0209046-09 Percent Lipids 5.9 % 0.5/23/2002 RB-109-111 608021 4748989 3 0209046-09 Percent Moisture 73 % 05/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#8 0.158 UJ ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#18 0.238 U ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#28 85.4 ug/kg 0.055/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#31 110 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#44 3.53 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#45 0.129 U ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#47 352 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 36 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#49 122 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#52 81.3 ug/kg 0.095/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#56 50.5 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#66 212 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#70 30.8 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#74 199 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#77 4.94 NJ ug/kg 0.095/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#81 0.119 U ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#87 75.7 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#95 13.2 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#99 170 ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#101 124 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#105 87.9 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#110 30.3 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#114 12.7 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#118 326 ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#123 0.103 U ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#126 8.69 NJ ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#128 14.2 ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#138 250 ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#146 67.2 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#149 36.3 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#151 3.59 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#153 259 ug/kg 0.35/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#156 28.6 ug/kg 0.35/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#157 4.53 ug/kg 0.35/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#158 18.4 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#167 26.4 ug/kg 0.35/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#169 5.47 U ug/kg 5

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 37 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#170 35.8 ug/kg 0.35/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#174 6.32 J ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#177 15.3 ug/kg 0.095/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#180 61.1 ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#183 17.4 ug/kg 0.065/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#189 2.17 ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#187 83.1 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#194 16.8 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#195 3.28 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#201 24.7 ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#206 10.9 ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 BZ#209 1.66 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 Monochlorobiphenyls 0.0901 UJ ug/kg 0.095/23/2002 RB-110-112 607978 4749034 3 0209046-10 Dichlorobiphenyls 0.158 U ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 Trichlorobiphenyls 188 ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 Tetrachlorobiphenyls 1390 ug/kg 0.095/23/2002 RB-110-112 607978 4749034 3 0209046-10 Pentachlorobiphenyls 1310 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 Hexachlorobiphenyls 813 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 Heptachlorobiphenyls 208 ug/kg 0.085/23/2002 RB-110-112 607978 4749034 3 0209046-10 Octachlorobiphenyls 61.3 ug/kg 0.065/23/2002 RB-110-112 607978 4749034 3 0209046-10 Nonachlorobiphenyls 18.3 ug/kg 0.25/23/2002 RB-110-112 607978 4749034 3 0209046-10 Decachlorobiphenyl 1.66 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 Total Homologs 3990 ug/kg 0.15/23/2002 RB-110-112 607978 4749034 3 0209046-10 Percent Lipids 4.9 % 0.5/23/2002 RB-110-112 607978 4749034 3 0209046-10 Percent Moisture 82 % 05/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#8 16.3 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#18 113 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#28 199 J ug/kg 0.035/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#31 632 J ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 38 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#44 45.0 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#45 0.0860 UJ ug/kg 0.085/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#47 626 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#49 511 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#52 596 J ug/kg 0.065/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#56 92.5 J ug/kg 0.095/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#66 359 J ug/kg 0.075/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#70 99.4 J ug/kg 0.075/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#74 291 J ug/kg 0.085/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#77 0.0602 UJ ug/kg 0.065/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#81 0.0795 UJ ug/kg 0.075/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#87 106 J ug/kg 0.095/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#95 78.7 J ug/kg 0.085/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#99 186 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#101 200 J ug/kg 0.075/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#105 108 J ug/kg 0.095/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#110 112 J ug/kg 0.075/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#114 13.0 J ug/kg 0.075/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#118 328 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#123 0.0688 UJ ug/kg 0.065/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#126 8.33 NJ ug/kg 0.095/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#128 12.4 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#138 222 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#146 54.7 J ug/kg 0.075/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#149 63.4 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#151 15.9 J ug/kg 0.075/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#153 196 J ug/kg 0.25/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#156 23.9 J ug/kg 0.25/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#157 4.01 J ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 39 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#158 14.2 J ug/kg 0.085/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#167 21.6 J ug/kg 0.25/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#169 3.66 UJ ug/kg 35/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#170 26.4 J ug/kg 0.25/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#174 8.22 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#177 14.1 J ug/kg 0.065/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#180 46.1 J ug/kg 0.25/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#183 11.3 J ug/kg 0.045/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#189 0.178 UJ ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#187 69.1 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#194 9.07 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#195 2.14 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#201 18.1 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#206 6.12 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 BZ#209 1.30 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 Monochlorobiphenyls 0.0602 UJ ug/kg 0.065/23/2002 RB-111-113 607329 4750588 3 0209046-11 Dichlorobiphenyls 38.6 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 Trichlorobiphenyls 1230 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 Tetrachlorobiphenyls 3230 J ug/kg 0.065/23/2002 RB-111-113 607329 4750588 3 0209046-11 Pentachlorobiphenyls 1840 J ug/kg 0.095/23/2002 RB-111-113 607329 4750588 3 0209046-11 Hexachlorobiphenyls 752 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 Heptachlorobiphenyls 162 J ug/kg 0.055/23/2002 RB-111-113 607329 4750588 3 0209046-11 Octachlorobiphenyls 39.5 J ug/kg 0.045/23/2002 RB-111-113 607329 4750588 3 0209046-11 Nonachlorobiphenyls 11.0 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 Decachlorobiphenyl 1.30 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 Total Homologs 7310 J ug/kg 0.15/23/2002 RB-111-113 607329 4750588 3 0209046-11 Percent Lipids 8.1 % 0.5/23/2002 RB-111-113 607329 4750588 3 0209046-11 Percent Moisture 82 % 05/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#8 2.54 J ug/kg 1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 40 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#18 11.3 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#28 1050 ug/kg 0.45/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#31 1310 ug/kg 0.85/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#44 36.7 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#45 0.998 U ug/kg 0.95/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#47 2080 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#49 1440 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#52 991 ug/kg 0.75/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#56 720 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#66 2960 ug/kg 0.85/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#70 791 ug/kg 0.85/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#74 2300 ug/kg 0.95/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#77 0.699 U ug/kg 0.65/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#81 0.923 U ug/kg 0.95/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#87 669 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#95 54.4 ug/kg 0.95/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#99 1510 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#101 1460 ug/kg 0.85/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#105 918 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#110 615 ug/kg 0.95/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#114 99.0 ug/kg 0.85/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#118 2730 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#123 0.798 U ug/kg 0.75/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#126 25.6 NJ ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#128 90.1 ug/kg 25/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#138 1660 ug/kg 25/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#146 305 ug/kg 0.85/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#149 309 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#151 20.7 ug/kg 0.8

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 41 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#153 1570 ug/kg 25/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#156 197 ug/kg 25/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#157 30.7 ug/kg 25/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#158 181 ug/kg 0.95/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#167 251 ug/kg 25/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#169 42.4 U ug/kg 425/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#170 233 ug/kg 25/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#174 40.8 J ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#177 58.5 ug/kg 0.75/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#180 465 ug/kg 25/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#183 102 ug/kg 0.45/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#189 13.7 ug/kg 25/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#187 318 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#194 97.1 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#195 22.6 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#201 146 ug/kg 25/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#206 63.3 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 BZ#209 6.52 ug/kg 15/23/2002 RB-112-114 607774 4748213 3 0209046-12 Monochlorobiphenyls 0.699 UJ ug/kg 0.65/23/2002 RB-112-114 607774 4748213 3 0209046-12 Dichlorobiphenyls 2.38 J ug/kg 1.5/23/2002 RB-112-114 607774 4748213 3 0209046-12 Trichlorobiphenyls 2120 ug/kg 1.5/23/2002 RB-112-114 607774 4748213 3 0209046-12 Tetrachlorobiphenyls 13200 ug/kg 0.75/23/2002 RB-112-114 607774 4748213 3 0209046-12 Pentachlorobiphenyls 12600 ug/kg 1.5/23/2002 RB-112-114 607774 4748213 3 0209046-12 Hexachlorobiphenyls 5250 ug/kg 1.5/23/2002 RB-112-114 607774 4748213 3 0209046-12 Heptachlorobiphenyls 1120 ug/kg 0.65/23/2002 RB-112-114 607774 4748213 3 0209046-12 Octachlorobiphenyls 402 ug/kg 0.45/23/2002 RB-112-114 607774 4748213 3 0209046-12 Nonachlorobiphenyls 101 ug/kg 1.5/23/2002 RB-112-114 607774 4748213 3 0209046-12 Decachlorobiphenyl 6.52 ug/kg 1.5/23/2002 RB-112-114 607774 4748213 3 0209046-12 Total Homologs 34800 ug/kg 1.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 42 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-112-114 607774 4748213 3 0209046-12 Percent Lipids 5.2 % 0.5/23/2002 RB-112-114 607774 4748213 3 0209046-12 Percent Moisture 79 % 05/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#8 0.143 UJ ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#18 0.216 U ug/kg 0.25/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#28 48.7 ug/kg 0.055/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#31 67.4 ug/kg 0.095/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#44 2.70 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#45 0.117 U ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#47 105 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#49 75.3 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#52 52.4 ug/kg 0.085/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#56 33.2 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#66 138 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#70 49.6 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#74 114 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#77 0.0818 U ug/kg 0.085/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#81 0.108 U ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#87 34.7 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#95 6.53 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#99 65.7 ug/kg 0.25/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#101 79.8 ug/kg 0.095/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#105 52.6 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#110 38.5 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#114 5.42 ug/kg 0.095/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#118 149 ug/kg 0.25/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#123 0.0935 U ug/kg 0.095/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#126 2.07 NJ ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#128 6.10 ug/kg 0.25/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#138 81.8 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 43 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#146 17.4 ug/kg 0.095/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#149 20.0 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#151 1.38 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#153 82.9 ug/kg 0.35/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#156 11.8 ug/kg 0.25/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#157 0.316 U ug/kg 0.35/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#158 5.81 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#167 10.2 ug/kg 0.35/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#169 4.97 U ug/kg 45/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#170 10.2 ug/kg 0.35/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#174 3.00 J ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#177 3.67 ug/kg 0.085/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#180 17.7 ug/kg 0.25/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#183 4.09 ug/kg 0.055/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#189 0.242 U ug/kg 0.25/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#187 20.2 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#194 3.50 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#195 0.744 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#201 7.78 ug/kg 0.25/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#206 2.85 ug/kg 0.25/23/2002 RB-113-115 607694 4748257 3 0209046-13 BZ#209 0.744 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 Monochlorobiphenyls 0.0818 UJ ug/kg 0.085/23/2002 RB-113-115 607694 4748257 3 0209046-13 Dichlorobiphenyls 0.143 U ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 Trichlorobiphenyls 112 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 Tetrachlorobiphenyls 659 ug/kg 0.085/23/2002 RB-113-115 607694 4748257 3 0209046-13 Pentachlorobiphenyls 678 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 Hexachlorobiphenyls 264 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 Heptachlorobiphenyls 52.4 ug/kg 0.075/23/2002 RB-113-115 607694 4748257 3 0209046-13 Octachlorobiphenyls 16.7 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 44 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-113-115 607694 4748257 3 0209046-13 Nonachlorobiphenyls 5.30 ug/kg 0.25/23/2002 RB-113-115 607694 4748257 3 0209046-13 Decachlorobiphenyl 0.744 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 Total Homologs 1790 ug/kg 0.15/23/2002 RB-113-115 607694 4748257 3 0209046-13 Percent Lipids 8.6 % 0.5/23/2002 RB-113-115 607694 4748257 3 0209046-13 Percent Moisture 68 % 05/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#8 0.597 UJ ug/kg 0.55/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#18 18.2 ug/kg 0.95/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#28 984 ug/kg 0.25/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#31 1220 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#44 77.5 ug/kg 0.75/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#45 0.487 U ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#47 2610 ug/kg 0.75/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#49 680 ug/kg 0.55/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#52 783 ug/kg 0.35/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#56 599 ug/kg 0.55/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#66 2370 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#70 433 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#74 1910 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#77 0.341 U ug/kg 0.35/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#81 0.451 U ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#87 578 ug/kg 0.55/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#95 145 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#99 1150 ug/kg 0.85/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#101 1000 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#105 672 ug/kg 0.55/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#110 393 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#114 86.3 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#118 1990 ug/kg 0.85/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#123 0.390 U ug/kg 0.3

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 45 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#126 47.0 NJ ug/kg 0.55/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#128 79.4 ug/kg 15/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#138 1240 ug/kg 0.95/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#146 345 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#149 259 ug/kg 0.55/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#151 60.9 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#153 1170 ug/kg 15/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#156 139 ug/kg 15/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#157 24.3 ug/kg 15/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#158 114 ug/kg 0.45/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#167 125 ug/kg 15/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#169 20.7 U ug/kg 205/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#170 162 ug/kg 15/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#174 35.5 J ug/kg 0.65/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#177 80.0 ug/kg 0.35/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#180 305 ug/kg 15/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#183 65.1 ug/kg 0.25/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#189 10.3 ug/kg 15/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#187 430 ug/kg 0.55/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#194 70.1 ug/kg 0.65/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#195 14.6 ug/kg 0.75/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#201 120 ug/kg 15/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#206 34.9 ug/kg 0.85/23/2002 RB-115-117 614917 4781109 1 0209046-14 BZ#209 4.97 ug/kg 0.65/23/2002 RB-115-117 614917 4781109 1 0209046-14 Monochlorobiphenyls 0.341 UJ ug/kg 0.35/23/2002 RB-115-117 614917 4781109 1 0209046-14 Dichlorobiphenyls 0.597 U ug/kg 0.55/23/2002 RB-115-117 614917 4781109 1 0209046-14 Trichlorobiphenyls 2080 ug/kg 0.75/23/2002 RB-115-117 614917 4781109 1 0209046-14 Tetrachlorobiphenyls 11500 ug/kg 0.35/23/2002 RB-115-117 614917 4781109 1 0209046-14 Pentachlorobiphenyls 9860 ug/kg 0.5

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 46 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-115-117 614917 4781109 1 0209046-14 Hexachlorobiphenyls 4000 ug/kg 0.65/23/2002 RB-115-117 614917 4781109 1 0209046-14 Heptachlorobiphenyls 1040 ug/kg 0.35/23/2002 RB-115-117 614917 4781109 1 0209046-14 Octachlorobiphenyls 265 ug/kg 0.25/23/2002 RB-115-117 614917 4781109 1 0209046-14 Nonachlorobiphenyls 62.6 ug/kg 0.85/23/2002 RB-115-117 614917 4781109 1 0209046-14 Decachlorobiphenyl 4.97 ug/kg 0.65/23/2002 RB-115-117 614917 4781109 1 0209046-14 Total Homologs 28800 ug/kg 0.65/23/2002 RB-115-117 614917 4781109 1 0209046-14 Percent Lipids 6.6 % 0.5/23/2002 RB-115-117 614917 4781109 1 0209046-14 Percent Moisture 80 % 05/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#8 0.183 UJ ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#18 0.276 U ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#28 11.1 ug/kg 0.065/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#31 8.90 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#44 0.224 U ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#45 0.149 U ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#47 14.3 ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#49 12.5 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#52 13.9 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#56 0.161 U ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#66 8.06 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#70 2.62 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#74 6.23 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#77 0.105 U ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#81 0.138 U ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#87 0.161 U ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#95 1.93 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#99 5.45 ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#101 5.71 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#105 3.64 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#110 3.35 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 47 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#114 0.127 U ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#118 11.1 ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#123 0.120 U ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#126 0.161 U ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#128 0.880 J ug/kg 0.35/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#138 10.8 ug/kg 0.35/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#146 2.40 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#149 2.21 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#151 0.428 J ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#153 12.0 ug/kg 0.35/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#156 2.26 ug/kg 0.35/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#157 0.403 U ug/kg 0.45/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#158 0.904 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#167 1.24 J ug/kg 0.45/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#169 6.35 U ug/kg 65/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#170 0.385 U ug/kg 0.35/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#174 0.452 J ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#177 0.738 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#180 5.76 ug/kg 0.35/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#183 1.21 ug/kg 0.075/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#189 0.31 U ug/kg 0.35/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#187 4.78 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#194 1.45 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#195 0.333 J ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#201 2.16 ug/kg 0.35/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#206 1.07 ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 BZ#209 0.856 ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 Monochlorobiphenyls 0.105 UJ ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 Dichlorobiphenyls 0.183 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 48 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-221-223 601075 4718030 4 0209046-15 Trichlorobiphenyls 23.7 ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 Tetrachlorobiphenyls 80.0 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 Pentachlorobiphenyls 57.9 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 Hexachlorobiphenyls 36.5 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 Heptachlorobiphenyls 12.0 ug/kg 0.095/23/2002 RB-221-223 601075 4718030 4 0209046-15 Octachlorobiphenyls 15.1 ug/kg 0.075/23/2002 RB-221-223 601075 4718030 4 0209046-15 Nonachlorobiphenyls 2.07 ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 Decachlorobiphenyl 0.856 ug/kg 0.25/23/2002 RB-221-223 601075 4718030 4 0209046-15 Total Homologs 228 ug/kg 0.15/23/2002 RB-221-223 601075 4718030 4 0209046-15 Percent Lipids 4.8 % 0.5/23/2002 RB-221-223 601075 4718030 4 0209046-15 Percent Moisture 74 % 05/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#8 0.167 U ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#18 0.253 U ug/kg 0.25/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#28 11.2 ug/kg 0.065/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#31 16.3 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#44 0.414 J ug/kg 0.25/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#45 0.137 U ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#47 42 ug/kg 0.25/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#49 16.3 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#52 7.29 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#56 4.11 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#66 30.2 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#70 7.07 J ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#74 28.3 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#77 0.0957 U ug/kg 0.095/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#81 0.126 U ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#87 12.6 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#95 2.24 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#99 51.4 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 49 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#101 30.2 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#105 10.3 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#110 6.81 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#114 1.46 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#118 55.1 ug/kg 0.25/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#123 0.109 U ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#126 2.48 NJ ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#128 5.55 ug/kg 0.25/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#138 84.8 ug/kg 0.25/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#146 23.7 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#149 13.8 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#151 0.5 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#153 117 ug/kg 0.35/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#156 6.55 ug/kg 0.35/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#157 1.61 ug/kg 0.35/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#158 7.75 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#167 11.3 ug/kg 0.45/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#169 5.81 U ug/kg 55/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#170 19.4 ug/kg 0.35/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#174 1.83 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#177 5.42 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#180 46.5 ug/kg 0.35/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#183 10.6 ug/kg 0.065/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#189 0.284 U ug/kg 0.25/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#187 30.0 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#194 8.49 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#195 2.07 ug/kg 0.25/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#201 12.0 ug/kg 0.35/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#206 4.92 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 50 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-222-231 600690 4704669 4 0209047-01 BZ#209 1.33 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 Monochlorobiphenyls 0.0957 U ug/kg 0.095/23/2002 RB-222-231 600690 4704669 4 0209047-01 Dichlorobiphenyls 0.167 U ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 Trichlorobiphenyls 21.8 ug/kg 0.25/23/2002 RB-222-231 600690 4704669 4 0209047-01 Tetrachlorobiphenyls 147 ug/kg 0.095/23/2002 RB-222-231 600690 4704669 4 0209047-01 Pentachlorobiphenyls 299 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 Hexachlorobiphenyls 316 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 Heptachlorobiphenyls 99.5 ug/kg 0.085/23/2002 RB-222-231 600690 4704669 4 0209047-01 Octachlorobiphenyls 29.5 ug/kg 0.065/23/2002 RB-222-231 600690 4704669 4 0209047-01 Nonachlorobiphenyls 8.77 ug/kg 0.25/23/2002 RB-222-231 600690 4704669 4 0209047-01 Decachlorobiphenyl 1.33 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 Total Homologs 924 ug/kg 0.15/23/2002 RB-222-231 600690 4704669 4 0209047-01 Percent Lipids 5.0 % 0.5/23/2002 RB-222-231 600690 4704669 4 0209047-01 Percent Moisture 84 % 05/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#8 0.162 U ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#18 0.245 U ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#28 16.4 ug/kg 0.055/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#31 23.4 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#44 0.485 J ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#45 0.132 U ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#47 65.4 ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#49 27.5 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#52 12.4 ug/kg 0.095/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#56 5.69 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#66 40.3 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#70 7.56 J ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#74 39.9 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#77 1.39 NJ ug/kg 0.095/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#81 0.122 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 51 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#87 16.4 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#95 3.83 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#99 64.7 ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#101 48.0 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#105 12.9 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#110 8.66 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#114 2.17 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#118 67.6 ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#123 0.106 U ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#126 3.29 NJ ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#128 3.79 ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#138 106 ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#146 29.6 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#149 21.6 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#151 1.05 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#153 145 ug/kg 0.35/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#156 7.63 ug/kg 0.35/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#157 1.56 ug/kg 0.35/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#158 7.06 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#167 16.7 ug/kg 0.35/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#169 5.62 U ug/kg 55/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#170 24.2 ug/kg 0.35/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#174 3.20 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#177 7.25 ug/kg 0.095/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#180 59.4 ug/kg 0.35/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#183 14.0 ug/kg 0.065/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#189 0.275 U ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#187 42.1 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#194 10.7 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 52 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#195 2.74 ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#201 14.9 ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#206 5.71 ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 BZ#209 1.66 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 Monochlorobiphenyls 0.0926 U ug/kg 0.095/22/2002 RB-223-225 600710 4704499 4 0209047-02 Dichlorobiphenyls 0.162 U ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 Trichlorobiphenyls 37.1 ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 Tetrachlorobiphenyls 216 ug/kg 0.095/22/2002 RB-223-225 600710 4704499 4 0209047-02 Pentachlorobiphenyls 401 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 Hexachlorobiphenyls 405 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 Heptachlorobiphenyls 131 ug/kg 0.085/22/2002 RB-223-225 600710 4704499 4 0209047-02 Octachlorobiphenyls 34.3 ug/kg 0.065/22/2002 RB-223-225 600710 4704499 4 0209047-02 Nonachlorobiphenyls 10.4 ug/kg 0.25/22/2002 RB-223-225 600710 4704499 4 0209047-02 Decachlorobiphenyl 1.66 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 Total Homologs 1240 ug/kg 0.15/22/2002 RB-223-225 600710 4704499 4 0209047-02 Percent Lipids 4.2 % 0.5/22/2002 RB-223-225 600710 4704499 4 0209047-02 Percent Moisture 83 % 05/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#8 0.144 U ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#18 0.218 U ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#28 9.59 ug/kg 0.055/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#31 12.5 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#44 0.413 J ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#45 0.118 U ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#47 38.7 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#49 16.2 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#52 10.2 ug/kg 0.085/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#56 4.24 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#66 28.8 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#70 8.09 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 53 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#74 34.8 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#77 0.0825 U ug/kg 0.085/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#81 0.109 U ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#87 21.4 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#95 3.10 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#99 54 ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#101 42.6 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#105 15.6 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#110 14.0 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#114 2.40 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#118 66.2 ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#123 0.0943 U ug/kg 0.095/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#126 2.81 NJ ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#128 5.08 ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#138 95.1 ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#146 24.8 ug/kg 0.095/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#149 28.0 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#151 1.16 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#153 109 ug/kg 0.35/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#156 7.45 ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#157 1.20 ug/kg 0.35/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#158 7.92 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#167 15.3 ug/kg 0.35/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#169 5.01 U ug/kg 55/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#170 16.2 ug/kg 0.35/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#174 5.33 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#177 7.02 ug/kg 0.085/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#180 37.2 ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#183 8.65 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 54 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#189 0.244 U ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#187 38.9 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#194 7.69 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#195 1.67 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#201 14.3 ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#206 5.83 ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 BZ#209 1.89 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 Monochlorobiphenyls 0.0825 U ug/kg 0.085/22/2002 RB-224-226 600462 4701077 4 0209047-03 Dichlorobiphenyls 0.144 U ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 Trichlorobiphenyls 19.5 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 Tetrachlorobiphenyls 161 ug/kg 0.085/22/2002 RB-224-226 600462 4701077 4 0209047-03 Pentachlorobiphenyls 389 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 Hexachlorobiphenyls 345 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 Heptachlorobiphenyls 95.3 ug/kg 0.075/22/2002 RB-224-226 600462 4701077 4 0209047-03 Octachlorobiphenyls 27.4 ug/kg 0.055/22/2002 RB-224-226 600462 4701077 4 0209047-03 Nonachlorobiphenyls 10.7 ug/kg 0.25/22/2002 RB-224-226 600462 4701077 4 0209047-03 Decachlorobiphenyl 1.89 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 Total Homologs 1050 ug/kg 0.15/22/2002 RB-224-226 600462 4701077 4 0209047-03 Percent Lipids 6.6 % 0.5/22/2002 RB-224-226 600462 4701077 4 0209047-03 Percent Moisture 78 % 05/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#8 0.108 U ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#18 0.163 U ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#28 23.2 ug/kg 0.035/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#31 27.6 ug/kg 0.075/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#44 1.11 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#45 0.0883 U ug/kg 0.085/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#47 88.9 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#49 37.7 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#52 23.6 ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 55 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#56 11.1 ug/kg 0.095/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#66 72.3 ug/kg 0.075/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#70 16.7 J ug/kg 0.075/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#74 81.8 ug/kg 0.085/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#77 0.0618 U ug/kg 0.065/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#81 0.0817 U ug/kg 0.085/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#87 35.7 ug/kg 0.095/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#95 5.93 ug/kg 0.085/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#99 113 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#101 85.4 ug/kg 0.075/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#105 32 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#110 29.5 ug/kg 0.085/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#114 5.37 ug/kg 0.075/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#118 131 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#123 0.0707 U ug/kg 0.075/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#126 5.81 NJ ug/kg 0.095/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#128 13.7 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#138 179 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#146 43.4 ug/kg 0.075/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#149 50.4 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#151 2.95 ug/kg 0.075/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#153 186 ug/kg 0.25/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#156 11.7 ug/kg 0.25/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#157 1.87 ug/kg 0.25/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#158 10.8 ug/kg 0.085/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#167 26.1 ug/kg 0.25/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#169 3.75 U ug/kg 35/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#170 23 ug/kg 0.25/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#174 5.91 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 56 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#177 11.6 ug/kg 0.065/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#180 51.4 ug/kg 0.25/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#183 14.1 ug/kg 0.045/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#189 0.183 U ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#187 56.9 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#194 8.31 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#195 2.33 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#201 17.7 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#206 6.41 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 BZ#209 2.35 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 Monochlorobiphenyls 0.0618 U ug/kg 0.065/22/2002 RB-225-227 600547 4701173 4 0209047-04 Dichlorobiphenyls 0.108 U ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 Trichlorobiphenyls 46.0 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 Tetrachlorobiphenyls 356 ug/kg 0.065/22/2002 RB-225-227 600547 4701173 4 0209047-04 Pentachlorobiphenyls 769 ug/kg 0.095/22/2002 RB-225-227 600547 4701173 4 0209047-04 Hexachlorobiphenyls 613 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 Heptachlorobiphenyls 142 ug/kg 0.055/22/2002 RB-225-227 600547 4701173 4 0209047-04 Octachlorobiphenyls 35.2 ug/kg 0.045/22/2002 RB-225-227 600547 4701173 4 0209047-04 Nonachlorobiphenyls 12.1 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 Decachlorobiphenyl 2.35 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 Total Homologs 1980 ug/kg 0.15/22/2002 RB-225-227 600547 4701173 4 0209047-04 Percent Lipids 6.6 % 0.5/22/2002 RB-225-227 600547 4701173 4 0209047-04 Percent Moisture 73 % 05/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#8 0.150 U ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#18 0.226 U ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#28 1.17 ug/kg 0.055/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#31 6.75 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#44 0.183 U ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#45 0.122 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 57 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#47 8.46 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#49 4.69 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#52 4.30 ug/kg 0.095/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#56 0.131 U ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#66 6.77 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#70 2.29 J ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#74 6.57 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#77 0.0855 U ug/kg 0.085/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#81 0.113 U ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#87 0.131 U ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#95 0.116 U ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#99 8.01 ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#101 12.0 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#105 2.78 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#110 2.16 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#114 0.104 U ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#118 17.0 ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#123 0.0977 U ug/kg 0.095/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#126 0.131 U ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#128 1.32 ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#138 22.0 ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#146 7.58 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#149 4.61 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#151 0.110 U ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#153 36.4 ug/kg 0.35/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#156 2.14 ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#157 0.33 U ug/kg 0.35/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#158 1.79 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#167 2.39 ug/kg 0.3

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 58 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#169 5.19 U ug/kg 55/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#170 5.19 ug/kg 0.35/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#174 0.856 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#177 2.08 ug/kg 0.095/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#180 15.8 ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#183 3.05 ug/kg 0.055/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#189 0.253 U ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#187 14.9 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#194 3.71 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#195 0.72 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#201 7.66 ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#206 4.01 ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 BZ#209 1.56 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 Monochlorobiphenyls 0.0855 U ug/kg 0.085/22/2002 RB-226-228 599481 4702730 4 0209047-05 Dichlorobiphenyls 0.150 U ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 Trichlorobiphenyls 6.42 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 Tetrachlorobiphenyls 41.9 ug/kg 0.085/22/2002 RB-226-228 599481 4702730 4 0209047-05 Pentachlorobiphenyls 83.8 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 Hexachlorobiphenyls 93.5 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 Heptachlorobiphenyls 37.1 ug/kg 0.075/22/2002 RB-226-228 599481 4702730 4 0209047-05 Octachlorobiphenyls 14.2 ug/kg 0.055/22/2002 RB-226-228 599481 4702730 4 0209047-05 Nonachlorobiphenyls 8.50 ug/kg 0.25/22/2002 RB-226-228 599481 4702730 4 0209047-05 Decachlorobiphenyl 1.56 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 Total Homologs 287 ug/kg 0.15/22/2002 RB-226-228 599481 4702730 4 0209047-05 Percent Lipids 4.7 % 0.5/22/2002 RB-226-228 599481 4702730 4 0209047-05 Percent Moisture 82 % 05/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#8 0.0956 U ug/kg 0.095/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#18 0.144 U ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#28 13.1 ug/kg 0.03

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 59 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#31 21.8 ug/kg 0.065/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#44 0.117 U ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#45 0.0781 U ug/kg 0.075/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#47 62.0 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#49 19.6 ug/kg 0.095/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#52 8.83 ug/kg 0.055/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#56 8.62 ug/kg 0.085/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#66 40.9 ug/kg 0.075/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#70 7.2 J ug/kg 0.075/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#74 35.9 ug/kg 0.075/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#77 0.0547 U ug/kg 0.055/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#81 0.0722 U ug/kg 0.075/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#87 22.6 ug/kg 0.085/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#95 2.41 ug/kg 0.075/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#99 59.1 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#101 55.9 ug/kg 0.065/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#105 12.1 ug/kg 0.085/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#110 10.5 ug/kg 0.075/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#114 0.0664 U ug/kg 0.065/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#118 56.1 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#123 0.0625 U ug/kg 0.065/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#126 2.45 NJ ug/kg 0.085/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#128 7.14 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#138 99.6 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#146 22.0 ug/kg 0.065/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#149 21.8 ug/kg 0.095/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#151 0.684 ug/kg 0.075/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#153 126 ug/kg 0.25/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#156 5.01 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 60 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#157 1.17 ug/kg 0.25/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#158 5.72 ug/kg 0.075/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#167 8.33 ug/kg 0.25/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#169 3.32 U ug/kg 35/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#170 14.8 ug/kg 0.25/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#174 3.38 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#177 8.39 ug/kg 0.055/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#180 36.8 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#183 9.01 ug/kg 0.035/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#189 0.162 U ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#187 36.5 ug/kg 0.095/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#194 6.55 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#195 1.85 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#201 16.3 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#206 7.50 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 BZ#209 2.5 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 Monochlorobiphenyls 0.0547 U ug/kg 0.055/22/2002 RB-227-229 599576 4702721 4 0209047-06 Dichlorobiphenyls 0.0956 U ug/kg 0.095/22/2002 RB-227-229 599576 4702721 4 0209047-06 Trichlorobiphenyls 31.6 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 Tetrachlorobiphenyls 206 ug/kg 0.055/22/2002 RB-227-229 599576 4702721 4 0209047-06 Pentachlorobiphenyls 404 ug/kg 0.085/22/2002 RB-227-229 599576 4702721 4 0209047-06 Hexachlorobiphenyls 356 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 Heptachlorobiphenyls 94.8 ug/kg 0.045/22/2002 RB-227-229 599576 4702721 4 0209047-06 Octachlorobiphenyls 33.9 ug/kg 0.035/22/2002 RB-227-229 599576 4702721 4 0209047-06 Nonachlorobiphenyls 15.2 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 Decachlorobiphenyl 2.5 ug/kg 0.15/22/2002 RB-227-229 599576 4702721 4 0209047-06 Total Homologs 1140 ug/kg 0.095/22/2002 RB-227-229 599576 4702721 4 0209047-06 Percent Lipids 5.7 % 0.5/22/2002 RB-227-229 599576 4702721 4 0209047-06 Percent Moisture 84 % 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 61 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#8 0.161 U ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#18 0.243 U ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#28 58 ug/kg 0.055/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#31 64.1 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#44 1.19 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#45 0.131 U ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#47 209 ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#49 57.7 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#52 31.8 ug/kg 0.095/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#56 10.2 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#66 103 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#70 23.3 J ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#74 133 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#77 0.0920 U ug/kg 0.095/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#81 0.122 U ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#87 0.141 U ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#95 7.09 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#99 129 ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#101 86.4 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#105 26.6 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#110 26.8 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#114 5.11 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#118 159 ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#123 0.105 U ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#126 4.54 NJ ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#128 6.65 ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#138 147 ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#146 41.6 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#149 35.0 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 62 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#151 0.962 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#153 177 ug/kg 0.35/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#156 11.1 ug/kg 0.35/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#157 2.13 ug/kg 0.35/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#158 11.0 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#167 18.6 ug/kg 0.35/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#169 5.58 U ug/kg 55/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#170 24.8 ug/kg 0.35/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#174 4.62 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#177 10.9 ug/kg 0.095/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#180 63.5 ug/kg 0.35/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#183 14.8 ug/kg 0.065/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#189 0.273 U ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#187 52.6 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#194 11.3 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#195 2.70 ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#201 18.0 ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#206 6.65 ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 BZ#209 2.36 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 Monochlorobiphenyls 0.0920 U ug/kg 0.095/23/2002 RB-228-230 603014 4712778 4 0209047-07 Dichlorobiphenyls 0.161 U ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 Trichlorobiphenyls 111 ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 Tetrachlorobiphenyls 621 ug/kg 0.095/23/2002 RB-228-230 603014 4712778 4 0209047-07 Pentachlorobiphenyls 824 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 Hexachlorobiphenyls 530 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 Heptachlorobiphenyls 147 ug/kg 0.085/23/2002 RB-228-230 603014 4712778 4 0209047-07 Octachlorobiphenyls 39.7 ug/kg 0.065/23/2002 RB-228-230 603014 4712778 4 0209047-07 Nonachlorobiphenyls 11.8 ug/kg 0.25/23/2002 RB-228-230 603014 4712778 4 0209047-07 Decachlorobiphenyl 2.39 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 63 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/23/2002 RB-228-230 603014 4712778 4 0209047-07 Total Homologs 2290 ug/kg 0.15/23/2002 RB-228-230 603014 4712778 4 0209047-07 Percent Lipids 6.2 % 0.5/23/2002 RB-228-230 603014 4712778 4 0209047-07 Percent Moisture 77 % 05/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#8 0.168 U ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#18 0.254 U ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#28 28.1 ug/kg 0.065/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#31 38.4 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#44 1.05 ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#45 0.137 U ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#47 111 ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#49 26.2 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#52 9.11 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#56 7.04 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#66 61.8 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#70 9.55 J ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#74 51.6 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#77 0.0960 U ug/kg 0.095/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#81 0.127 U ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#87 0.148 UJ ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#95 3.43 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#99 76.8 ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#101 46.0 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#105 15.7 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#110 5.37 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#114 2.99 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#118 79.6 ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#123 0.110 U ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#126 3.15 NJ ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#128 5.05 J ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 64 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#138 86.7 ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#146 25.3 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#149 18.4 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#151 0.983 J ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#153 114 ug/kg 0.35/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#156 5.94 ug/kg 0.35/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#157 0.370 U ug/kg 0.35/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#158 9.24 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#167 12.0 ug/kg 0.45/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#169 5.83 U ug/kg 55/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#170 15.9 ug/kg 0.35/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#174 2.88 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#177 6.47 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#180 40 ug/kg 0.35/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#183 10.4 ug/kg 0.065/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#189 0.285 U ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#187 35.7 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#194 6.69 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#195 1.88 ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#201 11.0 ug/kg 0.35/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#206 3.89 ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 BZ#209 1.86 J ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 Monochlorobiphenyls 0.0960 U ug/kg 0.095/28/2002 RB-229-232 602956 4711998 4 0209047-08 Dichlorobiphenyls 0.168 U ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 Trichlorobiphenyls 58.4 ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 Tetrachlorobiphenyls 313 ug/kg 0.095/28/2002 RB-229-232 602956 4711998 4 0209047-08 Pentachlorobiphenyls 434 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 Hexachlorobiphenyls 331 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 Heptachlorobiphenyls 100 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 65 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/28/2002 RB-229-232 602956 4711998 4 0209047-08 Octachlorobiphenyls 30.3 ug/kg 0.065/28/2002 RB-229-232 602956 4711998 4 0209047-08 Nonachlorobiphenyls 7.21 ug/kg 0.25/28/2002 RB-229-232 602956 4711998 4 0209047-08 Decachlorobiphenyl 1.86 J ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 Total Homologs 1280 ug/kg 0.15/28/2002 RB-229-232 602956 4711998 4 0209047-08 Percent Lipids 6.1 % 0.5/28/2002 RB-229-232 602956 4711998 4 0209047-08 Percent Moisture 77 % 05/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#8 0.186 U ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#18 0.280 U ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#28 311 ug/kg 0.065/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#31 407 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#44 4.78 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#45 0.152 U ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#47 383 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#49 267 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#52 195 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#56 50.4 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#66 195 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#70 50.2 J ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#74 175 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#77 0.106 U ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#81 0.140 U ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#87 71.6 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#95 13.4 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#99 120 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#101 126 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#105 69.4 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#110 59.4 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#114 7.02 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#118 191 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 66 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#123 0.121 U ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#126 5.02 NJ ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#128 6.27 ug/kg 0.35/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#138 177 ug/kg 0.35/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#146 37.3 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#149 41.1 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#151 2.37 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#153 151 ug/kg 0.35/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#156 16.0 ug/kg 0.35/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#157 2.97 ug/kg 0.45/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#158 17.0 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#167 28.6 ug/kg 0.45/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#169 6.44 U ug/kg 65/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#170 25.7 ug/kg 0.35/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#174 2.90 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#177 12.2 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#180 46.2 ug/kg 0.35/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#183 10.4 ug/kg 0.075/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#189 0.314 U ug/kg 0.35/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#187 46.8 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#194 11.7 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#195 2.90 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#201 19.7 ug/kg 0.35/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#206 13.2 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 BZ#209 5.45 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 Monochlorobiphenyls 0.106 U ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 Dichlorobiphenyls 0.186 U ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 Trichlorobiphenyls 328 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 Tetrachlorobiphenyls 1470 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 67 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/20/2002 RB-614-618 608279 4752022 2 0209047-09 Pentachlorobiphenyls 1170 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 Hexachlorobiphenyls 584 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 Heptachlorobiphenyls 127 ug/kg 0.095/20/2002 RB-614-618 608279 4752022 2 0209047-09 Octachlorobiphenyls 42.5 ug/kg 0.075/20/2002 RB-614-618 608279 4752022 2 0209047-09 Nonachlorobiphenyls 23.1 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 Decachlorobiphenyl 5.45 ug/kg 0.25/20/2002 RB-614-618 608279 4752022 2 0209047-09 Total Homologs 3750 ug/kg 0.15/20/2002 RB-614-618 608279 4752022 2 0209047-09 Percent Lipids 6.0 % 0.5/20/2002 RB-614-618 608279 4752022 2 0209047-09 Percent Moisture 75 % 05/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#8 0.145 U ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#18 0.218 U ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#28 7.49 ug/kg 0.055/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#31 14.6 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#44 0.177 U ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#45 0.118 U ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#47 35.3 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#49 27.8 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#52 21.4 ug/kg 0.085/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#56 0.127 U ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#66 46.7 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#70 11.5 J ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#74 31.1 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#77 0.0827 U ug/kg 0.085/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#81 0.109 U ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#87 11.6 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#95 2.26 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#99 30.6 ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#101 27.3 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#105 21.1 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 68 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#110 7.05 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#114 2.01 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#118 68.7 ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#123 0.0945 U ug/kg 0.095/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#126 1.39 NJ ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#128 3.12 ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#138 44.1 ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#146 11.0 ug/kg 0.095/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#149 7.09 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#151 0.106 U ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#153 54.8 ug/kg 0.35/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#156 5.42 ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#157 1.18 ug/kg 0.35/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#158 4.53 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#167 5.13 ug/kg 0.35/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#169 5.02 U ug/kg 55/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#170 7.18 ug/kg 0.35/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#174 0.583 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#177 1.92 ug/kg 0.085/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#180 15.2 ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#183 2.67 ug/kg 0.055/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#189 0.245 U ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#187 11.9 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#194 2.93 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#195 0.583 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#201 5.92 ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#206 3.52 ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 BZ#209 0.696 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 Monochlorobiphenyls 0.0827 U ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 69 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-615-619 614667 4783089 1 0209047-10 Dichlorobiphenyls 0.145 U ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 Trichlorobiphenyls 11.3 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 Tetrachlorobiphenyls 179 ug/kg 0.085/21/2002 RB-615-619 614667 4783089 1 0209047-10 Pentachlorobiphenyls 295 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 Hexachlorobiphenyls 164 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 Heptachlorobiphenyls 36.8 ug/kg 0.075/21/2002 RB-615-619 614667 4783089 1 0209047-10 Octachlorobiphenyls 11.6 ug/kg 0.055/21/2002 RB-615-619 614667 4783089 1 0209047-10 Nonachlorobiphenyls 6.06 ug/kg 0.25/21/2002 RB-615-619 614667 4783089 1 0209047-10 Decachlorobiphenyl 0.715 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 Total Homologs 705 ug/kg 0.15/21/2002 RB-615-619 614667 4783089 1 0209047-10 Percent Lipids 4.9 % 0.5/21/2002 RB-615-619 614667 4783089 1 0209047-10 Percent Moisture 70 % 05/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#8 0.103 U ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#18 0.155 U ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#28 14.5 ug/kg 0.035/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#31 33.7 ug/kg 0.075/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#44 0.126 U ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#45 0.0837 U ug/kg 0.085/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#47 134 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#49 0.103 U ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#52 0.0628 U ug/kg 0.065/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#56 22.6 ug/kg 0.095/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#66 91.6 ug/kg 0.075/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#70 6.99 ug/kg 0.075/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#74 92.6 ug/kg 0.075/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#77 0.0586 U ug/kg 0.055/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#81 0.0774 U ug/kg 0.075/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#87 41.4 ug/kg 0.095/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#95 0.0795 U ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 70 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#99 92.9 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#101 52.1 ug/kg 0.075/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#105 47.9 ug/kg 0.095/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#110 2.21 ug/kg 0.075/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#114 7.05 ug/kg 0.075/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#118 146 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#123 0.0670 U ug/kg 0.065/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#126 4.03 NJ ug/kg 0.095/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#128 7.08 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#138 130 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#146 32.8 ug/kg 0.065/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#149 11.1 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#151 0.0753 U ug/kg 0.075/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#153 128 ug/kg 0.25/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#156 12.0 ug/kg 0.25/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#157 2.23 ug/kg 0.25/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#158 15.8 ug/kg 0.075/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#167 15.2 ug/kg 0.25/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#169 3.56 UJ ug/kg 35/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#170 19.5 ug/kg 0.25/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#174 1.76 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#177 10.6 ug/kg 0.065/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#180 32.6 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#183 9.08 ug/kg 0.035/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#189 0.174 U ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#187 41.5 ug/kg 0.095/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#194 6.32 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#195 0.128 U ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#201 12.0 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 71 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#206 4.08 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 BZ#209 0.760 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 Monochlorobiphenyls 0.0586 U ug/kg 0.055/21/2002 RB-616-620 615439 4785550 1 0209048-02 Dichlorobiphenyls 0.103 U ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 Trichlorobiphenyls 46.0 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 Tetrachlorobiphenyls 466 ug/kg 0.065/21/2002 RB-616-620 615439 4785550 1 0209048-02 Pentachlorobiphenyls 593 ug/kg 0.095/21/2002 RB-616-620 615439 4785550 1 0209048-02 Hexachlorobiphenyls 432 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 Heptachlorobiphenyls 113 ug/kg 0.055/21/2002 RB-616-620 615439 4785550 1 0209048-02 Octachlorobiphenyls 27.3 ug/kg 0.035/21/2002 RB-616-620 615439 4785550 1 0209048-02 Nonachlorobiphenyls 8.01 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 Decachlorobiphenyl 0.760 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 Total Homologs 1690 ug/kg 0.15/21/2002 RB-616-620 615439 4785550 1 0209048-02 Percent Lipids 4.8 % 0.5/21/2002 RB-616-620 615439 4785550 1 0209048-02 Percent Moisture 81 % 05/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#8 0.109 U ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#18 0.165 U ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#28 0.739 ug/kg 0.045/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#31 1.17 ug/kg 0.075/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#44 0.134 U ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#45 0.0893 U ug/kg 0.085/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#47 2.16 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#49 1.21 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#52 1.05 ug/kg 0.065/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#56 0.0960 U ug/kg 0.095/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#66 1.92 ug/kg 0.085/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#70 0.654 J ug/kg 0.085/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#74 2.53 ug/kg 0.085/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#77 0.0625 U ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 72 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#81 0.0826 U ug/kg 0.085/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#87 0.0960 U ug/kg 0.095/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#95 0.0848 U ug/kg 0.085/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#99 2.63 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#101 1.49 ug/kg 0.075/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#105 0.91 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#110 0.455 ug/kg 0.085/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#114 0.0759 U ug/kg 0.075/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#118 6.21 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#123 0.0714 U ug/kg 0.075/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#126 0.426 NJ ug/kg 0.095/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#128 0.611 J ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#138 7.26 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#146 2.30 ug/kg 0.075/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#149 0.398 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#151 0.0804 U ug/kg 0.085/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#153 9.82 ug/kg 0.25/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#156 1.38 ug/kg 0.25/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#157 0.241 U ug/kg 0.25/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#158 0.54 ug/kg 0.085/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#167 0.796 J ug/kg 0.25/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#169 3.79 U ug/kg 35/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#170 1.75 ug/kg 0.25/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#174 0.120 U ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#177 0.398 ug/kg 0.065/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#180 3.77 ug/kg 0.25/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#183 0.654 ug/kg 0.045/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#189 0.185 U ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#187 2.83 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 73 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#194 1.07 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#195 0.185 J ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#201 1.22 ug/kg 0.25/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#206 0.569 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 BZ#209 0.185 J ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 Monochlorobiphenyls 0.0625 U ug/kg 0.065/21/2002 RB-617-621 615513 4785434 1 0209047-11 Dichlorobiphenyls 0.109 U ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 Trichlorobiphenyls 2.77 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 Tetrachlorobiphenyls 8.81 ug/kg 0.065/21/2002 RB-617-621 615513 4785434 1 0209047-11 Pentachlorobiphenyls 24.6 ug/kg 0.095/21/2002 RB-617-621 615513 4785434 1 0209047-11 Hexachlorobiphenyls 26.9 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 Heptachlorobiphenyls 8.42 ug/kg 0.055/21/2002 RB-617-621 615513 4785434 1 0209047-11 Octachlorobiphenyls 4.28 ug/kg 0.045/21/2002 RB-617-621 615513 4785434 1 0209047-11 Nonachlorobiphenyls 1.01 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 Decachlorobiphenyl 0.185 J ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 Total Homologs 76.9 ug/kg 0.15/21/2002 RB-617-621 615513 4785434 1 0209047-11 Percent Lipids 4.7 % 0.5/21/2002 RB-617-621 615513 4785434 1 0209047-11 Percent Moisture 85 % 05/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#8 0.122 U ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#18 0.184 U ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#28 3.77 ug/kg 0.045/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#31 4.36 ug/kg 0.085/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#44 0.149 U ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#45 0.0996 U ug/kg 0.095/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#47 12.4 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#49 3.28 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#52 1.19 ug/kg 0.075/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#56 2.28 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#66 10.3 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 74 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#70 1.93 J ug/kg 0.085/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#74 12.4 ug/kg 0.095/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#77 0.0697 U ug/kg 0.065/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#81 0.0921 U ug/kg 0.095/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#87 0.107 U ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#95 0.412 ug/kg 0.095/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#99 15.2 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#101 7.06 ug/kg 0.085/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#105 6.52 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#110 1.03 ug/kg 0.095/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#114 1.81 ug/kg 0.085/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#118 31.4 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#123 0.0797 U ug/kg 0.075/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#126 2.51 NJ ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#128 2.74 ug/kg 0.25/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#138 45.1 ug/kg 0.25/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#146 13.1 ug/kg 0.085/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#149 2.16 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#151 0.0896 U ug/kg 0.085/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#153 53.9 ug/kg 0.25/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#156 4.39 ug/kg 0.25/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#157 0.269 U ug/kg 0.25/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#158 4.82 ug/kg 0.095/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#167 4.57 ug/kg 0.25/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#169 4.23 U ug/kg 45/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#170 10.0 ug/kg 0.25/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#174 0.428 J ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#177 3.77 ug/kg 0.075/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#180 24.1 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 75 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#183 5.52 ug/kg 0.045/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#189 0.207 U ug/kg 0.25/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#187 27.7 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#194 9.23 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#195 1.44 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#201 29.7 ug/kg 0.25/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#206 22.8 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 BZ#209 3.81 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 Monochlorobiphenyls 0.0697 U ug/kg 0.065/21/2002 RB-618-622 614699 4787523 1 0209047-12 Dichlorobiphenyls 0.122 U ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 Trichlorobiphenyls 7.56 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 Tetrachlorobiphenyls 51.3 ug/kg 0.075/21/2002 RB-618-622 614699 4787523 1 0209047-12 Pentachlorobiphenyls 126 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 Hexachlorobiphenyls 151 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 Heptachlorobiphenyls 61 ug/kg 0.065/21/2002 RB-618-622 614699 4787523 1 0209047-12 Octachlorobiphenyls 58.9 ug/kg 0.045/21/2002 RB-618-622 614699 4787523 1 0209047-12 Nonachlorobiphenyls 40.6 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 Decachlorobiphenyl 3.76 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 Total Homologs 500 ug/kg 0.15/21/2002 RB-618-622 614699 4787523 1 0209047-12 Percent Lipids 4.8 % 0.5/21/2002 RB-618-622 614699 4787523 1 0209047-12 Percent Moisture 85 % 05/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#8 0.127 U ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#18 0.191 U ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#28 7.49 ug/kg 0.045/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#31 8.29 ug/kg 0.085/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#44 0.155 U ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#45 0.103 U ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#47 32.7 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#49 7.55 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 76 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#52 2.94 ug/kg 0.075/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#56 6.75 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#66 33.0 ug/kg 0.095/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#70 4.24 J ug/kg 0.095/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#74 28.1 ug/kg 0.095/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#77 0.0723 U ug/kg 0.075/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#81 0.0956 U ug/kg 0.095/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#87 9.56 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#95 0.0982 U ug/kg 0.095/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#99 25.3 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#101 15.8 ug/kg 0.085/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#105 18.4 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#110 1.96 ug/kg 0.095/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#114 1.53 ug/kg 0.085/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#118 55 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#123 0.0827 U ug/kg 0.085/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#126 1.1 NJ ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#128 2.94 ug/kg 0.25/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#138 43.1 ug/kg 0.25/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#146 10.0 ug/kg 0.085/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#149 3.19 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#151 0.0930 U ug/kg 0.095/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#153 46.4 ug/kg 0.25/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#156 4.85 ug/kg 0.25/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#157 0.79 J ug/kg 0.25/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#158 4.31 ug/kg 0.095/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#167 5.07 ug/kg 0.35/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#169 4.39 U ug/kg 45/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#170 5.69 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 77 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#174 0.313 J ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#177 1.88 ug/kg 0.075/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#180 10.8 ug/kg 0.25/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#183 2.2 ug/kg 0.045/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#189 0.214 U ug/kg 0.25/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#187 11.7 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#194 2.14 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#195 0.411 J ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#201 3.65 ug/kg 0.25/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#206 1.30 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 BZ#209 0.428 J ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 Monochlorobiphenyls 0.0723 U ug/kg 0.075/21/2002 RB-619-623 614116 4788748 1 0209047-13 Dichlorobiphenyls 0.127 U ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 Trichlorobiphenyls 15.7 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 Tetrachlorobiphenyls 125 ug/kg 0.075/21/2002 RB-619-623 614116 4788748 1 0209047-13 Pentachlorobiphenyls 217 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 Hexachlorobiphenyls 138 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 Heptachlorobiphenyls 29.1 ug/kg 0.065/21/2002 RB-619-623 614116 4788748 1 0209047-13 Octachlorobiphenyls 7.47 ug/kg 0.045/21/2002 RB-619-623 614116 4788748 1 0209047-13 Nonachlorobiphenyls 2.48 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 Decachlorobiphenyl 0.395 J ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 Total Homologs 535 ug/kg 0.15/21/2002 RB-619-623 614116 4788748 1 0209047-13 Percent Lipids 5.8 % 0.5/21/2002 RB-619-623 614116 4788748 1 0209047-13 Percent Moisture 81 % 05/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#8 0.146 U ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#18 0.221 U ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#28 1.81 ug/kg 0.055/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#31 3.36 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#44 0.179 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 78 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#45 0.119 U ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#47 4.31 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#49 2.36 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#52 0.95 ug/kg 0.085/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#56 0.128 U ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#66 4.41 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#70 1.88 J ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#74 4.05 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#77 0.0835 U ug/kg 0.085/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#81 0.110 U ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#87 1.79 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#95 0.152 J ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#99 2.85 ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#101 2.07 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#105 2.22 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#110 1.05 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#114 0.101 U ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#118 8.23 ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#123 0.0955 U ug/kg 0.095/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#126 0.128 U ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#128 0.627 J ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#138 8.19 ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#146 2.03 ug/kg 0.095/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#149 1.08 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#151 0.107 U ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#153 9.67 ug/kg 0.35/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#156 1.43 ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#157 0.322 U ug/kg 0.35/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#158 0.836 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 79 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#167 1.08 J ug/kg 0.35/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#169 5.07 U ug/kg 55/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#170 1.82 ug/kg 0.35/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#174 0.161 U ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#177 0.475 ug/kg 0.085/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#180 3.84 ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#183 0.703 ug/kg 0.055/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#189 0.248 U ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#187 3.12 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#194 1.03 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#195 0.182 U ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#201 1.41 ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#206 0.722 ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 BZ#209 0.247 J ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 Monochlorobiphenyls 0.0835 U ug/kg 0.085/22/2002 RB-620-624 609318 4743355 3 0209047-14 Dichlorobiphenyls 0.146 U ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 Trichlorobiphenyls 4.62 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 Tetrachlorobiphenyls 23.6 ug/kg 0.085/22/2002 RB-620-624 609318 4743355 3 0209047-14 Pentachlorobiphenyls 35.7 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 Hexachlorobiphenyls 31.8 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 Heptachlorobiphenyls 8.95 ug/kg 0.075/22/2002 RB-620-624 609318 4743355 3 0209047-14 Octachlorobiphenyls 3.48 ug/kg 0.055/22/2002 RB-620-624 609318 4743355 3 0209047-14 Nonachlorobiphenyls 1.58 ug/kg 0.25/22/2002 RB-620-624 609318 4743355 3 0209047-14 Decachlorobiphenyl 0.247 J ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 Total Homologs 110 ug/kg 0.15/22/2002 RB-620-624 609318 4743355 3 0209047-14 Percent Lipids 4.9 % 0.5/22/2002 RB-620-624 609318 4743355 3 0209047-14 Percent Moisture 85 % 05/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#8 0.130 U ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#18 0.196 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 80 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#28 36.7 J ug/kg 0.045/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#31 34.9 J ug/kg 0.095/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#44 0.159 U ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#45 0.106 U ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#47 61.5 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#49 4.53 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#52 3.45 ug/kg 0.075/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#56 31.9 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#66 111 J ug/kg 0.095/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#70 10.1 J ug/kg 0.095/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#74 87 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#77 0.0744 U ug/kg 0.075/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#81 0.0983 U ug/kg 0.095/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#87 11.8 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#95 0.101 U ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#99 42.5 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#101 30.2 ug/kg 0.095/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#105 20.3 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#110 2.83 ug/kg 0.095/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#114 2.64 ug/kg 0.095/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#118 55.3 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#123 0.0850 U ug/kg 0.085/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#126 1.12 NJ ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#128 2.17 ug/kg 0.25/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#138 32.4 ug/kg 0.25/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#146 7.85 ug/kg 0.085/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#149 7.43 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#151 0.0956 U ug/kg 0.095/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#153 37.9 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 81 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#156 4.72 ug/kg 0.25/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#157 0.287 U ug/kg 0.25/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#158 3.79 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#167 4.33 J ug/kg 0.35/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#169 4.52 U ug/kg 45/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#170 5.40 ug/kg 0.25/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#174 0.541 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#177 1.69 ug/kg 0.075/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#180 13.7 ug/kg 0.25/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#183 2.39 ug/kg 0.055/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#189 0.220 U ug/kg 0.25/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#187 11.3 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#194 2.94 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#195 0.609 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#201 5.09 ug/kg 0.25/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#206 2.32 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 BZ#209 0.71 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 Monochlorobiphenyls 0.0744 U ug/kg 0.075/21/2002 RB-621-625 609318 4743345 3 0209047-15 Dichlorobiphenyls 0.130 U ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 Trichlorobiphenyls 64.3 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 Tetrachlorobiphenyls 395 ug/kg 0.075/21/2002 RB-621-625 609318 4743345 3 0209047-15 Pentachlorobiphenyls 282 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 Hexachlorobiphenyls 120 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 Heptachlorobiphenyls 30.7 ug/kg 0.065/21/2002 RB-621-625 609318 4743345 3 0209047-15 Octachlorobiphenyls 10.6 ug/kg 0.055/21/2002 RB-621-625 609318 4743345 3 0209047-15 Nonachlorobiphenyls 4.35 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 Decachlorobiphenyl 0.728 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 Total Homologs 908 ug/kg 0.15/21/2002 RB-621-625 609318 4743345 3 0209047-15 Percent Lipids 5.7 % 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 82 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/21/2002 RB-621-625 609318 4743345 3 0209047-15 Percent Moisture 77 % 05/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#8 0.148 U ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#18 0.224 U ug/kg 0.25/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#28 2.60 ug/kg 0.055/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#31 5.96 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#44 0.181 U ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#45 0.121 U ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#47 18.8 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#49 2.89 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#52 2.5 ug/kg 0.095/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#56 4.35 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#66 18.9 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#70 3.04 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#74 17.2 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#77 0.0846 U ug/kg 0.085/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#81 0.112 U ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#87 7.50 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#95 0.115 U ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#99 20.0 ug/kg 0.25/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#101 12.0 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#105 12.5 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#110 2.04 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#114 1.67 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#118 43.2 ug/kg 0.25/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#123 0.0966 U ug/kg 0.095/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#126 0.130 U ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#128 2.71 ug/kg 0.25/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#138 33.8 ug/kg 0.25/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#146 8.73 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 83 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#149 2.94 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#151 0.109 U ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#153 43.6 ug/kg 0.35/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#156 4.44 ug/kg 0.25/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#157 0.326 U ug/kg 0.35/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#158 4.29 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#167 3.56 ug/kg 0.35/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#169 5.13 UJ ug/kg 55/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#170 5.92 ug/kg 0.35/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#174 0.923 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#177 2.10 ug/kg 0.095/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#180 15.3 ug/kg 0.25/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#183 2.77 ug/kg 0.055/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#189 0.251 U ug/kg 0.25/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#187 13.0 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#194 3.87 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#195 0.184 U ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#201 4.94 ug/kg 0.25/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#206 2.02 ug/kg 0.25/22/2002 RB-622-626 608803 4744320 3 0209048-01 BZ#209 0.75 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 Monochlorobiphenyls 0.0846 U ug/kg 0.085/22/2002 RB-622-626 608803 4744320 3 0209048-01 Dichlorobiphenyls 0.148 U ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 Trichlorobiphenyls 8.93 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 Tetrachlorobiphenyls 86.1 ug/kg 0.085/22/2002 RB-622-626 608803 4744320 3 0209048-01 Pentachlorobiphenyls 158 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 Hexachlorobiphenyls 127 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 Heptachlorobiphenyls 37.3 ug/kg 0.075/22/2002 RB-622-626 608803 4744320 3 0209048-01 Octachlorobiphenyls 12.3 ug/kg 0.055/22/2002 RB-622-626 608803 4744320 3 0209048-01 Nonachlorobiphenyls 3.94 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 84 of 85
Red-winged Blackbird (Agelaius phoeniceus) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(we

5/22/2002 RB-622-626 608803 4744320 3 0209048-01 Decachlorobiphenyl 0.75 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 Total Homologs 434 ug/kg 0.15/22/2002 RB-622-626 608803 4744320 3 0209048-01 Percent Lipids 5.3 % 0.5/22/2002 RB-622-626 608803 4744320 3 0209048-01 Percent Moisture 78 % 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 85 of 85
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

5/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#8 0.0871 U ug/kg 0.085/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#18 0.132 U ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#28 465 ug/kg 0.25/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#31 535 ug/kg 0.065/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#44 208 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#45 0.0711 U ug/kg 0.075/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#47 1700 ug/kg 1.5/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#49 1030 ug/kg 0.85/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#52 1820 ug/kg 0.45/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#56 353 ug/kg 0.075/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#66 927 ug/kg 0.55/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#70 323 ug/kg 0.065/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#74 747 ug/kg 0.65/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#77 49.1 NJ ug/kg 0.045/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#81 25.0 NJ ug/kg 0.065/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#87 542 ug/kg 0.75/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#95 423 ug/kg 0.065/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#99 809 ug/kg 1.5/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#101 1040 ug/kg 0.55/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#105 529 ug/kg 0.085/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#110 751 ug/kg 0.65/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#114 68.2 ug/kg 0.065/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#118 1030 ug/kg 1.5/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#123 0.0569 U ug/kg 0.055/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#126 0.0765 U ug/kg 0.075/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#128 57.3 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#138 1610 ug/kg 1.5/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#146 346 ug/kg 0.055/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#149 557 ug/kg 0.7

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 1 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#151 237 ug/kg 0.065/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#153 912 ug/kg 1.5/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#156 79.2 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#157 21.7 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#158 94.6 ug/kg 0.065/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#167 139 ug/kg 0.25/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#169 3.02 U ug/kg 3.5/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#170 236 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#174 100 ug/kg 0.095/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#177 159 ug/kg 0.055/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#180 282 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#183 110 ug/kg 0.035/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#189 11.3 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#187 459 ug/kg 0.085/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#194 63.8 ug/kg 0.095/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#195 33.7 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#201 135 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#206 44.6 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 BZ#209 5.74 ug/kg 0.15/24/2002 BK-114-116 615035 4779712 1 0208033-11 Monochlorobiphenyls 0.465 U ug/kg 0.45/24/2002 BK-114-116 615035 4779712 1 0208033-11 Dichlorobiphenyls 0.814 U ug/kg 0.85/24/2002 BK-114-116 615035 4779712 1 0208033-11 Trichlorobiphenyls 753 ug/kg 1.5/24/2002 BK-114-116 615035 4779712 1 0208033-11 Tetrachlorobiphenyls 8780 ug/kg 0.45/24/2002 BK-114-116 615035 4779712 1 0208033-11 Pentachlorobiphenyls 8670 ug/kg 0.75/24/2002 BK-114-116 615035 4779712 1 0208033-11 Hexachlorobiphenyls 4170 ug/kg 0.85/24/2002 BK-114-116 615035 4779712 1 0208033-11 Heptachlorobiphenyls 980 ug/kg 0.45/24/2002 BK-114-116 615035 4779712 1 0208033-11 Octachlorobiphenyls 237 ug/kg 0.35/24/2002 BK-114-116 615035 4779712 1 0208033-11 Nonachlorobiphenyls 59.0 ug/kg 1.5/24/2002 BK-114-116 615035 4779712 1 0208033-11 Decachlorobiphenyl 4.23 ug/kg 0.9

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 2 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/24/2002 BK-114-116 615035 4779712 1 0208033-11 Total Homologs 23700 ug/kg 0.85/24/2002 BK-114-116 615035 4779712 1 0208033-11 Percent Lipids 8.9 % 0.5/24/2002 BK-114-116 615035 4779712 1 0208033-11 Percent Moisture 85 % 05/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#8 0.0962 U ug/kg 0.095/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#18 0.145 U ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#28 290 ug/kg 0.45/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#31 232 ug/kg 0.85/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#44 288 ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#45 0.0785 U ug/kg 0.075/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#47 1170 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#49 515 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#52 769 ug/kg 0.75/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#56 324 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#66 1040 ug/kg 0.85/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#70 462 ug/kg 0.075/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#74 923 ug/kg 0.95/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#77 76.5 NJ ug/kg 0.055/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#81 31.2 NJ ug/kg 0.075/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#87 581 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#95 427 ug/kg 0.075/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#99 1260 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#101 794 ug/kg 0.85/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#105 685 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#110 406 ug/kg 0.95/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#114 243 ug/kg 0.065/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#118 1890 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#123 0.0628 U ug/kg 0.065/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#126 0.0844 U ug/kg 0.085/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#128 113 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 3 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#138 1880 ug/kg 2.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#146 360 ug/kg 0.85/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#149 324 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#151 151 ug/kg 0.075/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#153 1360 ug/kg 2.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#156 248 ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#157 65.6 ug/kg 0.25/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#158 375 ug/kg 0.075/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#167 609 ug/kg 0.25/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#169 3.34 U ug/kg 3.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#170 500 ug/kg 0.25/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#174 84.7 ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#177 329 ug/kg 0.055/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#180 441 ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#183 289 ug/kg 0.035/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#189 0.163 U ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#187 513 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#194 137 ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#195 64.7 ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#201 281 ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#206 113 ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 BZ#209 14.1 ug/kg 0.15/11/2002 BK-214-216 614291 4787634 1 0208033-12 Monochlorobiphenyls 0.686 U ug/kg 0.65/11/2002 BK-214-216 614291 4787634 1 0208033-12 Dichlorobiphenyls 1.20 U ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 Trichlorobiphenyls 488 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 Tetrachlorobiphenyls 6400 ug/kg 0.75/11/2002 BK-214-216 614291 4787634 1 0208033-12 Pentachlorobiphenyls 10100 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 Hexachlorobiphenyls 5650 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 Heptachlorobiphenyls 1270 ug/kg 0.6

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 4 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/11/2002 BK-214-216 614291 4787634 1 0208033-12 Octachlorobiphenyls 324 ug/kg 0.45/11/2002 BK-214-216 614291 4787634 1 0208033-12 Nonachlorobiphenyls 99.7 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 Decachlorobiphenyl 6.40 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 Total Homologs 24300 ug/kg 1.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 Percent Lipids 9.7 % 0.5/11/2002 BK-214-216 614291 4787634 1 0208033-12 Percent Moisture 81 % 05/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#8 0.0924 U ug/kg 0.095/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#18 0.140 U ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#28 72.5 J ug/kg 0.035/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#31 51.7 ug/kg 0.065/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#44 6.93 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#45 0.0755 U ug/kg 0.075/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#47 162 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#49 82.5 ug/kg 0.095/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#52 180 ug/kg 0.055/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#56 38.0 ug/kg 0.085/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#66 174 ug/kg 0.065/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#70 47.1 ug/kg 0.065/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#74 129 ug/kg 0.075/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#77 3.28 NJ ug/kg 0.055/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#81 1.50 NJ ug/kg 0.065/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#87 64.8 ug/kg 0.085/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#95 21.6 ug/kg 0.075/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#99 132 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#101 131 ug/kg 0.065/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#105 83.4 ug/kg 0.085/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#110 64.1 ug/kg 0.065/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#114 8.51 ug/kg 0.065/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#118 284 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 5 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#123 0.0604 U ug/kg 0.065/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#126 0.0811 U ug/kg 0.085/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#128 11.1 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#138 247 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#146 49.3 ug/kg 0.065/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#149 62.4 ug/kg 0.095/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#151 12.0 ug/kg 0.065/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#153 301 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#156 14.2 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#157 3.97 ug/kg 0.25/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#158 15.8 ug/kg 0.075/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#167 22.8 ug/kg 0.25/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#169 3.21 U ug/kg 3.5/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#170 66.2 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#174 10.6 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#177 29.8 ug/kg 0.055/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#180 104 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#183 25.9 ug/kg 0.035/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#189 0.157 U ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#187 108 ug/kg 0.085/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#194 22.8 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#195 8.50 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#201 30.1 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#206 9.91 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 BZ#209 2.08 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 Monochlorobiphenyls 0.0528 U ug/kg 0.055/11/2002 BK-215-217 614292 4762448 2 0208033-13 Dichlorobiphenyls 0.0924 U ug/kg 0.095/11/2002 BK-215-217 614292 4762448 2 0208033-13 Trichlorobiphenyls 111 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 Tetrachlorobiphenyls 1140 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 6 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/11/2002 BK-215-217 614292 4762448 2 0208033-13 Pentachlorobiphenyls 1240 ug/kg 0.085/11/2002 BK-215-217 614292 4762448 2 0208033-13 Hexachlorobiphenyls 821 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 Heptachlorobiphenyls 294 ug/kg 0.045/11/2002 BK-215-217 614292 4762448 2 0208033-13 Octachlorobiphenyls 64.7 ug/kg 0.035/11/2002 BK-215-217 614292 4762448 2 0208033-13 Nonachlorobiphenyls 18.2 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 Decachlorobiphenyl 2.08 ug/kg 0.15/11/2002 BK-215-217 614292 4762448 2 0208033-13 Total Homologs 3690 ug/kg 0.095/11/2002 BK-215-217 614292 4762448 2 0208033-13 Percent Lipids 8.1 % 0.5/11/2002 BK-215-217 614292 4762448 2 0208033-13 Percent Moisture 79 % 05/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#8 0.0743 U ug/kg 0.075/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#18 0.112 U ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#28 108 J ug/kg 0.025/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#31 157 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#44 23.3 ug/kg 0.095/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#45 0.0607 U ug/kg 0.065/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#47 374 ug/kg 0.095/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#49 263 ug/kg 0.075/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#52 468 ug/kg 0.045/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#56 64.9 ug/kg 0.065/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#66 271 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#70 98.4 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#74 222 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#77 10.7 NJ ug/kg 0.045/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#81 0.0561 U ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#87 140 ug/kg 0.065/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#95 62.9 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#99 214 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#101 277 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#105 107 ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 7 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#110 176 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#114 12.3 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#118 345 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#123 0.0485 U ug/kg 0.045/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#126 0.0652 U ug/kg 0.065/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#128 9.24 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#138 230 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#146 58.6 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#149 140 ug/kg 0.075/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#151 35.4 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#153 218 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#156 12.9 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#157 3.46 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#158 16.6 ug/kg 0.055/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#167 25.4 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#169 2.58 U ug/kg 2.5/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#170 35.2 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#174 13.1 ug/kg 0.085/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#177 21.4 ug/kg 0.045/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#180 49.0 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#183 15.4 ug/kg 0.025/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#189 0.126 U ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#187 79.5 ug/kg 0.075/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#194 11.1 ug/kg 0.085/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#195 4.91 ug/kg 0.095/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#201 24.2 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#206 13.0 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 BZ#209 2.57 ug/kg 0.085/11/2002 BK-216-218 611666 4757404 2 0208033-14 Monochlorobiphenyls 0.0425 U ug/kg 0.04

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 8 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/11/2002 BK-216-218 611666 4757404 2 0208033-14 Dichlorobiphenyls 0.0743 U ug/kg 0.075/11/2002 BK-216-218 611666 4757404 2 0208033-14 Trichlorobiphenyls 251 ug/kg 0.095/11/2002 BK-216-218 611666 4757404 2 0208033-14 Tetrachlorobiphenyls 2500 ug/kg 0.045/11/2002 BK-216-218 611666 4757404 2 0208033-14 Pentachlorobiphenyls 2200 ug/kg 0.065/11/2002 BK-216-218 611666 4757404 2 0208033-14 Hexachlorobiphenyls 887 ug/kg 0.085/11/2002 BK-216-218 611666 4757404 2 0208033-14 Heptachlorobiphenyls 207 ug/kg 0.035/11/2002 BK-216-218 611666 4757404 2 0208033-14 Octachlorobiphenyls 49.8 ug/kg 0.025/11/2002 BK-216-218 611666 4757404 2 0208033-14 Nonachlorobiphenyls 22.8 ug/kg 0.15/11/2002 BK-216-218 611666 4757404 2 0208033-14 Decachlorobiphenyl 2.57 ug/kg 0.085/11/2002 BK-216-218 611666 4757404 2 0208033-14 Total Homologs 6120 ug/kg 0.075/11/2002 BK-216-218 611666 4757404 2 0208033-14 Percent Lipids 8.8 % 0.5/11/2002 BK-216-218 611666 4757404 2 0208033-14 Percent Moisture 80 % 05/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#8 0.0907 U ug/kg 0.095/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#18 0.137 U ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#28 225 J ug/kg 0.035/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#31 227 ug/kg 0.065/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#44 13.5 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#45 0.0740 U ug/kg 0.075/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#47 489 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#49 300 ug/kg 0.095/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#52 580 ug/kg 0.055/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#56 104 ug/kg 0.075/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#66 513 ug/kg 0.065/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#70 150 ug/kg 0.065/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#74 385 ug/kg 0.075/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#77 14.9 NJ ug/kg 0.055/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#81 0.0685 U ug/kg 0.065/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#87 177 ug/kg 0.075/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#95 61.6 ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 9 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#99 332 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#101 407 ug/kg 0.065/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#105 171 ug/kg 0.085/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#110 216 ug/kg 0.065/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#114 17.3 ug/kg 0.065/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#118 585 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#123 0.0592 U ug/kg 0.055/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#126 0.0796 U ug/kg 0.075/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#128 12.7 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#138 360 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#146 70.4 ug/kg 0.065/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#149 165 ug/kg 0.085/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#151 24.9 ug/kg 0.065/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#153 344 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#156 19.4 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#157 4.77 ug/kg 0.25/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#158 30.2 ug/kg 0.075/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#167 41.7 ug/kg 0.25/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#169 3.15 U ug/kg 3.5/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#170 45.6 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#174 17.7 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#177 25.7 ug/kg 0.055/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#180 53.3 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#183 24.1 ug/kg 0.035/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#189 0.154 U ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#187 87.9 ug/kg 0.085/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#194 16.1 ug/kg 0.095/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#195 6.22 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#201 28.5 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 10 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#206 23.6 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 BZ#209 9.09 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 Monochlorobiphenyls 0.0518 U ug/kg 0.055/11/2002 BK-506-507 615110 4768744 2 0208033-15 Dichlorobiphenyls 0.0907 U ug/kg 0.095/11/2002 BK-506-507 615110 4768744 2 0208033-15 Trichlorobiphenyls 428 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 Tetrachlorobiphenyls 3500 ug/kg 0.055/11/2002 BK-506-507 615110 4768744 2 0208033-15 Pentachlorobiphenyls 3130 ug/kg 0.075/11/2002 BK-506-507 615110 4768744 2 0208033-15 Hexachlorobiphenyls 1230 ug/kg 0.095/11/2002 BK-506-507 615110 4768744 2 0208033-15 Heptachlorobiphenyls 236 ug/kg 0.045/11/2002 BK-506-507 615110 4768744 2 0208033-15 Octachlorobiphenyls 64.1 ug/kg 0.035/11/2002 BK-506-507 615110 4768744 2 0208033-15 Nonachlorobiphenyls 40.4 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 Decachlorobiphenyl 9.09 ug/kg 0.15/11/2002 BK-506-507 615110 4768744 2 0208033-15 Total Homologs 8630 ug/kg 0.095/11/2002 BK-506-507 615110 4768744 2 0208033-15 Percent Lipids 12 % 0.5/11/2002 BK-506-507 615110 4768744 2 0208033-15 Percent Moisture 81 % 05/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#8 0.380 U ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#18 0.574 U ug/kg 0.55/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#28 207 ug/kg 0.15/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#31 85.3 J ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#44 5.13 ug/kg 0.45/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#45 0.310 U ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#47 337 J ug/kg 0.45/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#49 165 ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#52 365 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#56 65.6 ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#66 321 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#70 80.7 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#74 151 J ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#77 0.217 U ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 11 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#81 0.287 U ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#87 102 ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#95 44.1 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#99 221 ug/kg 0.55/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#101 252 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#105 101 ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#110 125 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#114 11.6 J ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#118 300 ug/kg 0.55/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#123 0.248 U ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#126 0.333 U ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#128 8.69 ug/kg 0.65/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#138 261 ug/kg 0.65/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#146 46.8 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#149 106 ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#151 16.2 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#153 223 ug/kg 0.75/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#156 18.9 ug/kg 0.75/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#157 4.00 ug/kg 0.85/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#158 23.7 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#167 45.7 ug/kg 0.95/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#169 13.2 U ug/kg 135/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#170 34.1 J ug/kg 0.75/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#174 17.2 ug/kg 0.45/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#177 15.9 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#180 56.4 ug/kg 0.75/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#183 15.1 ug/kg 0.15/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#189 0.643 U ug/kg 0.65/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#187 54.8 ug/kg 0.3

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 12 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#194 10.8 ug/kg 0.45/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#195 4.15 ug/kg 0.45/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#201 18.0 ug/kg 0.65/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#206 9.68 ug/kg 0.55/1/2002 BK-506-508 615110 4768744 2 0208034-01 BZ#209 3.70 ug/kg 0.45/1/2002 BK-506-508 615110 4768744 2 0208034-01 Monochlorobiphenyls 0.217 U ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 Dichlorobiphenyls 0.380 U ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 Trichlorobiphenyls 266 ug/kg 0.45/1/2002 BK-506-508 615110 4768744 2 0208034-01 Tetrachlorobiphenyls 1770 ug/kg 0.25/1/2002 BK-506-508 615110 4768744 2 0208034-01 Pentachlorobiphenyls 1810 J ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 Hexachlorobiphenyls 922 ug/kg 0.45/1/2002 BK-506-508 615110 4768744 2 0208034-01 Heptachlorobiphenyls 159 ug/kg 0.15/1/2002 BK-506-508 615110 4768744 2 0208034-01 Octachlorobiphenyls 50.8 ug/kg 0.15/1/2002 BK-506-508 615110 4768744 2 0208034-01 Nonachlorobiphenyls 20.1 J ug/kg 0.55/1/2002 BK-506-508 615110 4768744 2 0208034-01 Decachlorobiphenyl 3.70 ug/kg 0.45/1/2002 BK-506-508 615110 4768744 2 0208034-01 Total Homologs 5010 ug/kg 0.35/1/2002 BK-506-508 615110 4768744 2 0208034-01 Percent Lipids 7.7 J % 0.5/1/2002 BK-506-508 615110 4768744 2 0208034-01 Percent Moisture 82 % 05/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#8 2.45 U ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#18 3.70 U ug/kg 3.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#28 1810 ug/kg 0.85/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#31 128 J ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#44 52.5 ug/kg 3.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#45 2.00 U ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#47 3560 ug/kg 3.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#49 794 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#52 1240 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#56 744 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#66 2950 ug/kg 1.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 13 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#70 1.80 U ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#74 2470 J ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#77 1.40 U ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#81 31.8 NJ ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#87 844 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#95 134 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#99 2490 ug/kg 3.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#101 2110 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#105 1230 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#110 1030 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#114 152 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#118 3060 ug/kg 3.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#123 1.60 U ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#126 2.15 U ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#128 113 ug/kg 4.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#138 3480 ug/kg 4.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#146 570 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#149 825 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#151 15.3 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#153 2460 ug/kg 5.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#156 224 ug/kg 4.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#157 42.7 ug/kg 5.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#158 454 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#167 425 ug/kg 5.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#169 85.0 U ug/kg 855/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#170 504 ug/kg 5.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#174 114 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#177 197 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#180 819 ug/kg 4.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 14 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#183 204 ug/kg 0.95/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#189 4.15 U ug/kg 4.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#187 670 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#194 149 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#195 52.5 ug/kg 3.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#201 227 ug/kg 4.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#206 134 ug/kg 3.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 BZ#209 28.6 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Monochlorobiphenyls 1.40 U ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Dichlorobiphenyls 2.45 U ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Trichlorobiphenyls 1550 ug/kg 3.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Tetrachlorobiphenyls 13200 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Pentachlorobiphenyls 17100 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Hexachlorobiphenyls 9200 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Heptachlorobiphenyls 1820 ug/kg 1.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Octachlorobiphenyls 502 ug/kg 0.95/1/2002 BK-507-509 609257 4741678 3 0208034-02 Nonachlorobiphenyls 277 ug/kg 3.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Decachlorobiphenyl 28.6 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Total Homologs 43700 ug/kg 2.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Percent Lipids 5.7 % 0.5/1/2002 BK-507-509 609257 4741678 3 0208034-02 Percent Moisture 85 % 05/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#8 0.199 U ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#18 0.301 U ug/kg 0.35/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#28 24.3 ug/kg 0.075/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#31 10.7 J ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#44 4.72 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#45 0.163 U ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#47 44.6 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#49 31.0 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 15 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#52 57.5 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#56 5.36 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#66 38.4 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#70 12.4 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#74 38.1 J ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#77 0.114 U ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#81 0.150 U ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#87 27.8 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#95 13.3 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#99 114 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#101 44.4 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#105 41.6 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#110 27.5 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#114 0.138 U ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#118 160 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#123 0.130 U ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#126 0.175 U ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#128 11.7 ug/kg 0.35/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#138 331 ug/kg 0.35/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#146 52.0 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#149 33.4 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#151 6.06 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#153 330 ug/kg 0.45/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#156 26.6 ug/kg 0.35/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#157 0.439 U ug/kg 0.45/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#158 32.6 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#167 40.7 ug/kg 0.45/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#169 6.92 U ug/kg 6.5/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#170 79.1 ug/kg 0.4

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 16 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#174 8.27 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#177 22.3 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#180 138 ug/kg 0.35/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#183 31.4 ug/kg 0.075/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#189 0.338 U ug/kg 0.35/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#187 78.6 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#194 24.2 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#195 8.63 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#201 30.9 ug/kg 0.35/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#206 13.1 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 BZ#209 3.34 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 Monochlorobiphenyls 0.114 U ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 Dichlorobiphenyls 0.199 U ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 Trichlorobiphenyls 30.3 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 Tetrachlorobiphenyls 246 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 Pentachlorobiphenyls 674 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 Hexachlorobiphenyls 877 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 Heptachlorobiphenyls 252 ug/kg 0.15/8/2002 BK-511-513 601220 4717936 4 0208034-03 Octachlorobiphenyls 69.6 ug/kg 0.075/8/2002 BK-511-513 601220 4717936 4 0208034-03 Nonachlorobiphenyls 30.3 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 Decachlorobiphenyl 3.34 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 Total Homologs 2180 ug/kg 0.25/8/2002 BK-511-513 601220 4717936 4 0208034-03 Percent Lipids 8.1 % 0.5/8/2002 BK-511-513 601220 4717936 4 0208034-03 Percent Moisture 80 % 05/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#8 0.718 U ug/kg 0.75/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#18 16.6 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#28 404 ug/kg 0.25/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#31 506 ug/kg 0.45/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#44 108 ug/kg 0.8

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 17 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#45 0.586 U ug/kg 0.55/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#47 1250 ug/kg 0.95/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#49 984 ug/kg 0.75/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#52 1630 ug/kg 0.45/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#56 133 ug/kg 0.65/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#66 588 ug/kg 0.55/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#70 217 ug/kg 0.55/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#74 315 J ug/kg 0.55/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#77 0.410 U ug/kg 0.45/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#81 0.542 U ug/kg 0.55/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#87 333 ug/kg 0.65/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#95 319 ug/kg 0.55/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#99 485 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#101 632 ug/kg 0.45/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#105 195 ug/kg 0.65/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#110 492 ug/kg 0.55/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#114 25.1 ug/kg 0.45/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#118 583 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#123 0.469 U ug/kg 0.45/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#126 19.7 NJ ug/kg 0.65/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#128 17.1 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#138 582 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#146 127 ug/kg 0.45/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#149 287 ug/kg 0.75/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#151 101 ug/kg 0.55/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#153 434 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#156 36.7 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#157 8.12 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#158 36.1 ug/kg 0.5

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 18 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#167 87.7 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#169 24.9 U ug/kg 245/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#170 82.3 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#174 51.3 ug/kg 0.75/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#177 52.1 ug/kg 0.45/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#180 123 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#183 38.2 ug/kg 0.25/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#189 3.27 J ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#187 166 ug/kg 0.65/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#194 34.7 ug/kg 0.75/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#195 12.6 ug/kg 0.85/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#201 57.2 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#206 28.0 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 BZ#209 5.79 ug/kg 0.85/9/2002 BK-513-516 615076 4786136 1 0208034-04 Monochlorobiphenyls 0.410 U ug/kg 0.45/9/2002 BK-513-516 615076 4786136 1 0208034-04 Dichlorobiphenyls 0.718 U ug/kg 0.75/9/2002 BK-513-516 615076 4786136 1 0208034-04 Trichlorobiphenyls 1070 ug/kg 0.95/9/2002 BK-513-516 615076 4786136 1 0208034-04 Tetrachlorobiphenyls 6520 ug/kg 0.45/9/2002 BK-513-516 615076 4786136 1 0208034-04 Pentachlorobiphenyls 5590 ug/kg 0.65/9/2002 BK-513-516 615076 4786136 1 0208034-04 Hexachlorobiphenyls 2240 ug/kg 0.75/9/2002 BK-513-516 615076 4786136 1 0208034-04 Heptachlorobiphenyls 475 ug/kg 0.35/9/2002 BK-513-516 615076 4786136 1 0208034-04 Octachlorobiphenyls 135 ug/kg 0.25/9/2002 BK-513-516 615076 4786136 1 0208034-04 Nonachlorobiphenyls 56.5 ug/kg 1.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 Decachlorobiphenyl 5.79 ug/kg 0.85/9/2002 BK-513-516 615076 4786136 1 0208034-04 Total Homologs 16100 ug/kg 0.75/9/2002 BK-513-516 615076 4786136 1 0208034-04 Percent Lipids 8.7 % 0.5/9/2002 BK-513-516 615076 4786136 1 0208034-04 Percent Moisture 82 % 06/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#8 1.47 U ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#18 2.21 U ug/kg 2.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 19 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#28 371 ug/kg 0.56/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#31 171 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#44 19.2 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#45 1.20 U ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#47 1020 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#49 361 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#52 771 ug/kg 0.86/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#56 202 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#66 846 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#70 96.0 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#74 437 J ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#77 0.838 U ug/kg 0.86/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#81 8.76 NJ ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#87 341 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#95 106 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#99 823 ug/kg 2.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#101 675 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#105 399 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#110 339 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#114 54.5 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#118 1260 ug/kg 2.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#123 0.957 U ug/kg 0.96/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#126 1.29 U ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#128 49.7 ug/kg 2.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#138 1260 ug/kg 2.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#146 234 ug/kg 0.96/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#149 305 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#151 24.8 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#153 1200 ug/kg 3.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 20 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#156 118 ug/kg 2.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#157 20.4 ug/kg 3.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#158 89.5 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#167 191 ug/kg 3.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#169 50.9 U ug/kg 506/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#170 208 ug/kg 3.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#174 48.6 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#177 76.2 ug/kg 0.86/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#180 348 ug/kg 2.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#183 75.6 ug/kg 0.56/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#189 9.14 ug/kg 2.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#187 300 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#194 67.8 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#195 23.1 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#201 122 ug/kg 2.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#206 56.2 ug/kg 2.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 BZ#209 11.4 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 Monochlorobiphenyls 0.838 U ug/kg 0.86/4/2002 BK-638-657 610111 4754688 2 0208034-05 Dichlorobiphenyls 1.47 U ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 Trichlorobiphenyls 507 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 Tetrachlorobiphenyls 4600 ug/kg 0.86/4/2002 BK-638-657 610111 4754688 2 0208034-05 Pentachlorobiphenyls 6550 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 Hexachlorobiphenyls 4180 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 Heptachlorobiphenyls 847 ug/kg 0.76/4/2002 BK-638-657 610111 4754688 2 0208034-05 Octachlorobiphenyls 260 ug/kg 0.56/4/2002 BK-638-657 610111 4754688 2 0208034-05 Nonachlorobiphenyls 112 ug/kg 2.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 Decachlorobiphenyl 11.4 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 Total Homologs 17100 ug/kg 1.6/4/2002 BK-638-657 610111 4754688 2 0208034-05 Percent Lipids 8.7 % 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 21 of 22
Belted Kingfisher (Ceryle alcyon) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet 

b

6/4/2002 BK-638-657 610111 4754688 2 0208034-05 Percent Moisture 81 % 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 22 of 22
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

4/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#8 0.131 UJ ug/kg 0.1

4/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#18 0.198 UJ ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#28 7.84 J ug/kg 0.044/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#31 5.05 J ug/kg 0.094/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#44 0.161 UJ ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#45 0.107 UJ ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#47 53.2 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#49 41.0 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#52 83.9 J ug/kg 0.084/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#56 0.115 UJ ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#66 19.7 J ug/kg 0.094/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#70 6.21 J ug/kg 0.094/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#74 62.1 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#77 0.0750 UJ ug/kg 0.074/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#81 0.0990 UJ ug/kg 0.094/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#87 23.7 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#95 19.2 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#99 67.9 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#101 71.7 J ug/kg 0.094/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#105 9.65 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#110 10.6 J ug/kg 0.094/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#114 0.0910 UJ ug/kg 0.094/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#118 48.1 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#123 0.0860 UJ ug/kg 0.084/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#126 2.61 NJ ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#128 0.233 UJ ug/kg 0.24/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#138 151 J ug/kg 0.24/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#146 72.5 J ug/kg 0.08

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 1 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#149 31.6 J ug/kg 0.1

4/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#151 5.71 J ug/kg 0.094/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#153 180 J ug/kg 0.24/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#156 8.83 J ug/kg 0.24/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#157 0.289 UJ ug/kg 0.24/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#158 8.51 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#167 24.4 J ug/kg 0.34/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#169 4.55 UJ ug/kg 44/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#170 38.0 J ug/kg 0.24/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#174 0.145 UJ ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#177 12.9 J ug/kg 0.084/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#180 66.2 J ug/kg 0.24/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#183 17.5 J ug/kg 0.054/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#189 0.222 UJ ug/kg 0.24/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#187 247 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#194 14.8 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#195 5.18 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#201 38.1 J ug/kg 0.24/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#206 13.8 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 BZ#209 3.00 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 Monochlorobiphenyls 0.0750 UJ ug/kg 0.074/25/2002 AR-007-011 613517 4792342 1 0208031-01 Dichlorobiphenyls 0.131 UJ ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 Trichlorobiphenyls 10.9 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 Tetrachlorobiphenyls 349 J ug/kg 0.074/25/2002 AR-007-011 613517 4792342 1 0208031-01 Pentachlorobiphenyls 400 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 Hexachlorobiphenyls 596 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 Heptachlorobiphenyls 372 J ug/kg 0.064/25/2002 AR-007-011 613517 4792342 1 0208031-01 Octachlorobiphenyls 66.7 J ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 2 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/25/2002 AR-007-011 613517 4792342 1 0208031-01 Nonachlorobiphenyls 22.9 J ug/kg 0.1

4/25/2002 AR-007-011 613517 4792342 1 0208031-01 Decachlorobiphenyl 3.17 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 Total Homologs 1820 J ug/kg 0.14/25/2002 AR-007-011 613517 4792342 1 0208031-01 Percent Lipids 5.1 % 04/25/2002 AR-007-011 613517 4792342 1 0208031-01 Percent Moisture 89 % 5/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#8 0.130 UJ ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#18 0.197 UJ ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#28 0.0480 UJ ug/kg 0.045/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#31 0.0900 UJ ug/kg 0.095/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#44 0.159 UJ ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#45 0.106 UJ ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#47 0.643 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#49 0.288 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#52 0.745 J ug/kg 0.085/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#56 0.114 UJ ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#66 0.0960 UJ ug/kg 0.095/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#70 0.0960 UJ ug/kg 0.095/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#74 0.101 UJ ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#77 0.0740 UJ ug/kg 0.075/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#81 0.0980 UJ ug/kg 0.095/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#87 0.114 UJ ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#95 0.609 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#99 2.34 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#101 2.59 J ug/kg 0.095/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#105 0.122 UJ ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#110 0.339 J ug/kg 0.095/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#114 0.0900 UJ ug/kg 0.095/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#118 1.61 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 3 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#123 0.0850 UJ ug/kg 0.08

5/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#126 0.114 UJ ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#128 0.254 J ug/kg 0.25/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#138 9.04 J ug/kg 0.25/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#146 2.69 J ug/kg 0.085/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#149 4.00 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#151 0.728 J ug/kg 0.095/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#153 10.1 J ug/kg 0.25/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#156 0.863 J ug/kg 0.25/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#157 0.287 UJ ug/kg 0.25/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#158 0.694 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#167 1.34 J ug/kg 0.35/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#169 4.52 UJ ug/kg 45/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#170 3.23 J ug/kg 0.25/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#174 1.05 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#177 1.59 J ug/kg 0.085/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#180 6.65 J ug/kg 0.25/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#183 1.51 J ug/kg 0.055/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#189 0.221 UJ ug/kg 0.25/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#187 13.8 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#194 1.18 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#195 0.440 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#201 3.93 J ug/kg 0.25/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#206 1.95 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 BZ#209 1.18 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 Monochlorobiphenyls 0.0740 UJ ug/kg 0.075/6/2002 AR-010-015 599469 4703944 4 0208031-02 Dichlorobiphenyls 0.130 UJ ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 Trichlorobiphenyls 0.170 UJ ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 4 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/6/2002 AR-010-015 599469 4703944 4 0208031-02 Tetrachlorobiphenyls 1.86 J ug/kg 0.07

5/6/2002 AR-010-015 599469 4703944 4 0208031-02 Pentachlorobiphenyls 15.0 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 Hexachlorobiphenyls 40.3 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 Heptachlorobiphenyls 29.4 J ug/kg 0.065/6/2002 AR-010-015 599469 4703944 4 0208031-02 Octachlorobiphenyls 6.79 J ug/kg 0.055/6/2002 AR-010-015 599469 4703944 4 0208031-02 Nonachlorobiphenyls 3.98 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 Decachlorobiphenyl 1.18 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 Total Homologs 98.5 J ug/kg 0.15/6/2002 AR-010-015 599469 4703944 4 0208031-02 Percent Lipids 5.8 % 05/6/2002 AR-010-015 599469 4703944 4 0208031-02 Percent Moisture 88 % 5/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#8 0.152 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#18 0.229 U ug/kg 0.25/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#28 0.0560 U ug/kg 0.055/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#31 0.105 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#44 2.07 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#45 0.124 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#47 1.93 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#49 0.375 J ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#52 1.32 ug/kg 0.095/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#56 0.133 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#66 0.111 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#70 0.111 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#74 1.28 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#77 0.0870 U ug/kg 0.085/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#81 0.115 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#87 0.133 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#95 0.355 J ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#99 4.00 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 5 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#101 3.22 ug/kg 0.1

5/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#105 0.142 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#110 0.473 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#114 0.105 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#118 1.74 ug/kg 0.25/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#123 0.0990 U ug/kg 0.095/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#126 0.572 NJ ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#128 0.375 J ug/kg 0.25/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#138 14.0 ug/kg 0.25/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#146 3.96 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#149 1.62 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#151 0.611 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#153 18.8 ug/kg 0.35/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#156 1.18 ug/kg 0.35/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#157 0.334 U ug/kg 0.35/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#158 1.04 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#167 2.64 ug/kg 0.35/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#169 5.26 U ug/kg 55/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#170 4.40 ug/kg 0.35/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#174 0.167 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#177 1.66 ug/kg 0.095/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#180 10.0 ug/kg 0.25/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#183 2.01 ug/kg 0.055/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#189 0.257 U ug/kg 0.25/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#187 14.0 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#194 1.72 J ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#195 0.651 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#201 4.83 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 6 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#206 1.95 ug/kg 0.2

5/7/2002 AR-013-020 599308 4702162 4 0208031-04 BZ#209 1.46 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 Monochlorobiphenyls 0.0870 U ug/kg 0.085/7/2002 AR-013-020 599308 4702162 4 0208031-04 Dichlorobiphenyls 0.152 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 Trichlorobiphenyls 0.198 U ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 Tetrachlorobiphenyls 3.83 ug/kg 0.095/7/2002 AR-013-020 599308 4702162 4 0208031-04 Pentachlorobiphenyls 22.5 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 Hexachlorobiphenyls 58.3 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 Heptachlorobiphenyls 34.6 ug/kg 0.075/7/2002 AR-013-020 599308 4702162 4 0208031-04 Octachlorobiphenyls 11.8 ug/kg 0.055/7/2002 AR-013-020 599308 4702162 4 0208031-04 Nonachlorobiphenyls 4.71 ug/kg 0.25/7/2002 AR-013-020 599308 4702162 4 0208031-04 Decachlorobiphenyl 1.46 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 Total Homologs 140 ug/kg 0.15/7/2002 AR-013-020 599308 4702162 4 0208031-04 Percent Lipids 10 % 05/7/2002 AR-013-020 599308 4702162 4 0208031-04 Percent Moisture 86 % 5/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#8 0.141 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#18 0.212 U ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#28 0.0520 U ug/kg 0.055/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#31 0.0980 U ug/kg 0.095/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#44 0.172 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#45 0.115 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#47 0.859 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#49 0.896 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#52 2.63 ug/kg 0.085/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#56 0.123 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#66 0.103 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#70 0.103 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#74 0.109 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 7 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#77 0.0800 U ug/kg 0.08

5/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#81 0.106 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#87 1.81 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#95 1.64 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#99 4.90 ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#101 9.18 ug/kg 0.095/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#105 0.132 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#110 1.17 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#114 0.0980 U ug/kg 0.095/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#118 4.40 ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#123 0.0920 U ug/kg 0.095/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#126 0.123 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#128 0.713 J ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#138 21.8 ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#146 6.20 ug/kg 0.095/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#149 7.24 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#151 1.13 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#153 19.0 ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#156 1.15 ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#157 0.585 J ug/kg 0.35/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#158 1.41 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#167 3.60 ug/kg 0.35/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#169 4.88 U ug/kg 45/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#170 4.83 ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#174 0.155 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#177 2.67 ug/kg 0.085/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#180 8.24 ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#183 1.83 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 8 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#189 0.238 U ug/kg 0.2

5/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#187 27.2 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#194 2.05 J ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#195 0.896 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#201 8.70 ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#206 8.15 ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 BZ#209 9.74 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 Monochlorobiphenyls 0.0800 U ug/kg 0.085/7/2002 AR-014-021 599444 4702959 4 0208031-03 Dichlorobiphenyls 0.141 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 Trichlorobiphenyls 0.184 U ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 Tetrachlorobiphenyls 4.57 ug/kg 0.085/7/2002 AR-014-021 599444 4702959 4 0208031-03 Pentachlorobiphenyls 39.3 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 Hexachlorobiphenyls 85.4 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 Heptachlorobiphenyls 46.7 ug/kg 0.075/7/2002 AR-014-021 599444 4702959 4 0208031-03 Octachlorobiphenyls 15.6 ug/kg 0.055/7/2002 AR-014-021 599444 4702959 4 0208031-03 Nonachlorobiphenyls 17.2 ug/kg 0.25/7/2002 AR-014-021 599444 4702959 4 0208031-03 Decachlorobiphenyl 9.74 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 Total Homologs 219 ug/kg 0.15/7/2002 AR-014-021 599444 4702959 4 0208031-03 Percent Lipids 8.7 % 05/7/2002 AR-014-021 599444 4702959 4 0208031-03 Percent Moisture 89 % 5/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#8 0.178 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#18 0.268 UJ ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#28 0.0650 UJ ug/kg 0.065/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#31 0.123 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#44 0.217 UJ ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#45 0.145 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#47 0.716 J ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#49 0.646 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 9 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#52 2.54 J ug/kg 0.1

5/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#56 0.156 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#66 0.130 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#70 0.130 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#74 0.693 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#77 0.101 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#81 0.134 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#87 1.66 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#95 1.64 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#99 4.85 J ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#101 8.22 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#105 0.600 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#110 0.134 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#114 0.123 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#118 4.85 J ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#123 0.116 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#126 0.156 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#128 0.623 J ug/kg 0.35/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#138 17.5 J ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#146 4.09 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#149 7.55 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#151 1.50 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#153 13.3 J ug/kg 0.35/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#156 2.56 J ug/kg 0.35/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#157 0.391 UJ ug/kg 0.35/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#158 1.20 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#167 3.12 J ug/kg 0.45/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#169 6.16 UJ ug/kg 6

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 10 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#170 2.96 J ug/kg 0.3

5/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#174 0.693 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#177 1.20 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#180 4.13 J ug/kg 0.35/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#183 1.08 J ug/kg 0.065/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#189 0.301 UJ ug/kg 0.35/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#187 12.3 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#194 1.15 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#195 0.369 J ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#201 3.62 J ug/kg 0.35/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#206 3.67 J ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 BZ#209 4.92 J ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 Monochlorobiphenyls 0.101 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 Dichlorobiphenyls 0.178 UJ ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 Trichlorobiphenyls 0.232 UJ ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 Tetrachlorobiphenyls 4.18 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 Pentachlorobiphenyls 37.5 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 Hexachlorobiphenyls 74.4 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 Heptachlorobiphenyls 21.4 J ug/kg 0.095/8/2002 AR-018-026 608863 4742783 3 0208031-05 Octachlorobiphenyls 8.68 J ug/kg 0.065/8/2002 AR-018-026 608863 4742783 3 0208031-05 Nonachlorobiphenyls 9.42 J ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 Decachlorobiphenyl 5.10 J ug/kg 0.25/8/2002 AR-018-026 608863 4742783 3 0208031-05 Total Homologs 152 J ug/kg 0.15/8/2002 AR-018-026 608863 4742783 3 0208031-05 Percent Lipids 4.4 % 05/8/2002 AR-018-026 608863 4742783 3 0208031-05 Percent Moisture 83 % 5/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#8 0.273 UJ ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#18 0.412 UJ ug/kg 0.45/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#28 0.100 UJ ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 11 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#31 0.189 UJ ug/kg 0.1

5/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#44 0.334 UJ ug/kg 0.35/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#45 0.223 UJ ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#47 9.18 J ug/kg 0.35/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#49 2.06 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#52 4.08 J ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#56 0.239 UJ ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#66 1.52 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#70 0.200 UJ ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#74 15.9 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#77 0.156 UJ ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#81 0.206 UJ ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#87 6.91 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#95 1.38 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#99 20.3 J ug/kg 0.45/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#101 14.7 J ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#105 3.22 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#110 1.03 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#114 0.189 UJ ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#118 21.1 J ug/kg 0.35/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#123 0.178 UJ ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#126 1.52 NJ ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#128 1.77 J ug/kg 0.45/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#138 54.6 J ug/kg 0.45/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#146 15.7 J ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#149 7.30 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#151 1.45 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#153 63.5 J ug/kg 0.5

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 12 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#156 6.84 J ug/kg 0.5

5/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#157 1.28 J ug/kg 0.65/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#158 3.54 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#167 7.48 J ug/kg 0.65/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#169 9.46 UJ ug/kg 95/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#170 10.6 J ug/kg 0.55/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#174 1.45 J ug/kg 0.35/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#177 3.26 J ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#180 18.8 J ug/kg 0.55/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#183 3.51 J ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#189 0.462 UJ ug/kg 0.45/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#187 33.0 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#194 3.44 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#195 1.03 J ug/kg 0.35/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#201 6.77 J ug/kg 0.55/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#206 2.69 J ug/kg 0.35/15/2002 AR-023-034 615265 4783867 1 0208031-06 BZ#209 1.42 J ug/kg 0.35/15/2002 AR-023-034 615265 4783867 1 0208031-06 Monochlorobiphenyls 0.156 UJ ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 Dichlorobiphenyls 0.273 UJ ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 Trichlorobiphenyls 0.356 UJ ug/kg 0.35/15/2002 AR-023-034 615265 4783867 1 0208031-06 Tetrachlorobiphenyls 48.0 J ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 Pentachlorobiphenyls 130 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 Hexachlorobiphenyls 211 J ug/kg 0.25/15/2002 AR-023-034 615265 4783867 1 0208031-06 Heptachlorobiphenyls 77.2 J ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 Octachlorobiphenyls 15.9 J ug/kg 0.15/15/2002 AR-023-034 615265 4783867 1 0208031-06 Nonachlorobiphenyls 4.75 J ug/kg 0.35/15/2002 AR-023-034 615265 4783867 1 0208031-06 Decachlorobiphenyl 1.45 J ug/kg 0.35/15/2002 AR-023-034 615265 4783867 1 0208031-06 Total Homologs 487 J ug/kg 0.4

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 13 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/15/2002 AR-023-034 615265 4783867 1 0208031-06 Percent Lipids 5.4 % 0

5/15/2002 AR-023-034 615265 4783867 1 0208031-06 Percent Moisture 90 % 5/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#8 0.194 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#18 0.293 U ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#28 0.0710 U ug/kg 0.075/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#31 0.135 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#44 0.238 U ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#45 0.158 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#47 6.45 ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#49 2.85 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#52 9.68 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#56 0.170 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#66 1.08 J ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#70 0.143 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#74 6.15 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#77 0.111 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#81 0.146 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#87 4.94 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#95 2.07 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#99 15.3 ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#101 15.8 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#105 1.29 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#110 1.06 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#114 0.135 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#118 9.00 ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#123 0.127 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#126 0.170 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#128 0.857 J ug/kg 0.3

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 14 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#138 37.1 ug/kg 0.3

5/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#146 10.6 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#149 8.30 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#151 1.36 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#153 37.1 ug/kg 0.45/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#156 3.88 ug/kg 0.35/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#157 2.52 ug/kg 0.45/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#158 2.17 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#167 5.40 ug/kg 0.45/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#169 6.73 U ug/kg 65/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#170 6.68 ug/kg 0.45/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#174 0.882 ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#177 2.82 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#180 10.4 ug/kg 0.35/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#183 2.02 ug/kg 0.075/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#189 0.329 U ug/kg 0.35/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#187 26.4 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#194 1.76 J ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#195 0.681 J ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#201 5.14 J ug/kg 0.35/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#206 2.04 ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 BZ#209 1.26 ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 Monochlorobiphenyls 0.111 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 Dichlorobiphenyls 0.194 U ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 Trichlorobiphenyls 0.253 U ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 Tetrachlorobiphenyls 35.4 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 Pentachlorobiphenyls 79.0 ug/kg 0.15/15/2002 AR-024-035 615239 4790549 1 0208031-07 Hexachlorobiphenyls 137 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 15 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/15/2002 AR-024-035 615239 4790549 1 0208031-07 Heptachlorobiphenyls 48.6 ug/kg 0.09

5/15/2002 AR-024-035 615239 4790549 1 0208031-07 Octachlorobiphenyls 12.3 J ug/kg 0.075/15/2002 AR-024-035 615239 4790549 1 0208031-07 Nonachlorobiphenyls 4.08 ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 Decachlorobiphenyl 1.31 ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 Total Homologs 318 ug/kg 0.25/15/2002 AR-024-035 615239 4790549 1 0208031-07 Percent Lipids 6.1 % 05/15/2002 AR-024-035 615239 4790549 1 0208031-07 Percent Moisture 83 % 4/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#8 0.117 UJ ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#18 0.177 UJ ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#28 0.0430 UJ ug/kg 0.044/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#31 0.0810 UJ ug/kg 0.084/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#44 0.143 UJ ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#45 0.0950 UJ ug/kg 0.094/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#47 0.410 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#49 0.319 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#52 1.75 J ug/kg 0.074/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#56 0.103 UJ ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#66 0.0860 UJ ug/kg 0.084/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#70 0.0860 UJ ug/kg 0.084/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#74 0.577 J ug/kg 0.094/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#77 0.0670 UJ ug/kg 0.064/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#81 0.0880 UJ ug/kg 0.084/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#87 1.09 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#95 1.78 J ug/kg 0.094/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#99 3.01 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#101 4.95 J ug/kg 0.084/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#105 0.547 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#110 0.760 J ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 16 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#114 0.0810 UJ ug/kg 0.08

4/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#118 2.93 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#123 0.0760 UJ ug/kg 0.074/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#126 0.103 UJ ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#128 0.395 J ug/kg 0.24/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#138 15.1 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#146 4.33 J ug/kg 0.074/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#149 5.47 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#151 1.06 J ug/kg 0.084/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#153 19.9 J ug/kg 0.24/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#156 1.09 J ug/kg 0.24/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#157 0.258 UJ ug/kg 0.24/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#158 1.52 J ug/kg 0.094/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#167 2.74 J ug/kg 0.24/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#169 4.06 UJ ug/kg 44/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#170 4.94 J ug/kg 0.24/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#174 1.09 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#177 1.76 J ug/kg 0.074/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#180 13.2 J ug/kg 0.24/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#183 3.07 J ug/kg 0.044/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#189 0.198 UJ ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#187 22.9 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#194 1.82 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#195 0.912 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#201 4.53 J ug/kg 0.24/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#206 0.167 UJ ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 BZ#209 0.136 UJ ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 Monochlorobiphenyls 0.0670 UJ ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 17 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/18/2002 AR-101-101 612607 4758345 2 0208031-08 Dichlorobiphenyls 0.117 UJ ug/kg 0.1

4/18/2002 AR-101-101 612607 4758345 2 0208031-08 Trichlorobiphenyls 0.153 UJ ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 Tetrachlorobiphenyls 2.64 J ug/kg 0.064/18/2002 AR-101-101 612607 4758345 2 0208031-08 Pentachlorobiphenyls 28.1 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 Hexachlorobiphenyls 69.3 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 Heptachlorobiphenyls 47.8 J ug/kg 0.064/18/2002 AR-101-101 612607 4758345 2 0208031-08 Octachlorobiphenyls 8.74 J ug/kg 0.044/18/2002 AR-101-101 612607 4758345 2 0208031-08 Nonachlorobiphenyls 0.608 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 Decachlorobiphenyl 0.136 UJ ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 Total Homologs 157 J ug/kg 0.14/18/2002 AR-101-101 612607 4758345 2 0208031-08 Percent Lipids 8.7 % 04/18/2002 AR-101-101 612607 4758345 2 0208031-08 Percent Moisture 78 % 4/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#8 0.126 U ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#18 0.190 U ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#28 0.555 ug/kg 0.044/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#31 0.326 ug/kg 0.084/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#44 0.154 U ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#45 0.103 U ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#47 31.7 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#49 3.95 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#52 8.16 ug/kg 0.074/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#56 0.110 U ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#66 2.55 ug/kg 0.094/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#70 0.0920 U ug/kg 0.094/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#74 27.0 ug/kg 0.094/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#77 0.0720 U ug/kg 0.074/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#81 0.0950 U ug/kg 0.094/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#87 16.7 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 18 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#95 2.01 ug/kg 0.09

4/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#99 31.0 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#101 22.3 ug/kg 0.084/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#105 6.90 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#110 2.42 ug/kg 0.094/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#114 1.71 ug/kg 0.084/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#118 38.3 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#123 0.0820 U ug/kg 0.084/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#126 0.110 U ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#128 2.58 ug/kg 0.24/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#138 59.0 ug/kg 0.24/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#146 16.0 ug/kg 0.084/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#149 7.28 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#151 2.25 ug/kg 0.094/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#153 60.6 ug/kg 0.24/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#156 7.00 ug/kg 0.24/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#157 1.49 ug/kg 0.24/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#158 4.41 ug/kg 0.094/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#167 8.70 ug/kg 0.34/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#169 4.36 U ug/kg 44/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#170 8.75 ug/kg 0.24/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#174 1.34 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#177 3.82 ug/kg 0.074/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#180 14.7 ug/kg 0.24/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#183 3.18 ug/kg 0.044/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#189 0.213 U ug/kg 0.24/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#187 26.1 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#194 2.78 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 19 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#195 0.816 ug/kg 0.1

4/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#201 6.02 ug/kg 0.24/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#206 2.28 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 BZ#209 1.18 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 Monochlorobiphenyls 0.0720 U ug/kg 0.074/23/2002 AR-102-102 615269 4783913 1 0208031-09 Dichlorobiphenyls 0.126 U ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 Trichlorobiphenyls 0.718 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 Tetrachlorobiphenyls 105 ug/kg 0.074/23/2002 AR-102-102 615269 4783913 1 0208031-09 Pentachlorobiphenyls 207 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 Hexachlorobiphenyls 223 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 Heptachlorobiphenyls 56.2 ug/kg 0.064/23/2002 AR-102-102 615269 4783913 1 0208031-09 Octachlorobiphenyls 12.5 ug/kg 0.044/23/2002 AR-102-102 615269 4783913 1 0208031-09 Nonachlorobiphenyls 4.29 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 Decachlorobiphenyl 1.18 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 Total Homologs 610 ug/kg 0.14/23/2002 AR-102-102 615269 4783913 1 0208031-09 Percent Lipids 5.1 % 04/23/2002 AR-102-102 615269 4783913 1 0208031-09 Percent Moisture 88 % 4/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#8 0.145 U ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#18 0.220 U ug/kg 0.24/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#28 0.907 ug/kg 0.054/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#31 0.586 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#44 0.178 U ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#45 0.119 U ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#47 18.0 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#49 7.05 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#52 23.8 ug/kg 0.084/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#56 0.128 U ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#66 1.72 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 20 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#70 0.107 U ug/kg 0.1

4/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#74 13.6 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#77 0.0830 U ug/kg 0.084/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#81 0.110 U ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#87 7.92 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#95 4.55 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#99 25.9 ug/kg 0.24/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#101 29.2 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#105 1.57 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#110 1.68 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#114 0.101 U ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#118 11.7 ug/kg 0.24/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#123 0.0950 U ug/kg 0.094/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#126 0.128 U ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#128 1.21 ug/kg 0.24/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#138 54.6 ug/kg 0.24/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#146 17.4 ug/kg 0.094/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#149 14.2 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#151 1.83 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#153 42.5 ug/kg 0.34/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#156 3.00 ug/kg 0.24/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#157 1.00 J ug/kg 0.34/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#158 2.65 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#167 7.10 ug/kg 0.34/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#169 5.04 U ug/kg 54/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#170 7.69 ug/kg 0.34/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#174 0.160 U ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#177 4.65 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 21 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#180 12.0 ug/kg 0.2

4/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#183 2.55 ug/kg 0.054/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#189 0.246 U ug/kg 0.24/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#187 45.5 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#194 2.70 J ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#195 1.12 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#201 6.97 ug/kg 0.24/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#206 4.33 ug/kg 0.24/23/2002 AR-103-103 615168 4790668 1 0208031-10 BZ#209 3.10 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 Monochlorobiphenyls 0.0830 U ug/kg 0.084/23/2002 AR-103-103 615168 4790668 1 0208031-10 Dichlorobiphenyls 0.145 U ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 Trichlorobiphenyls 1.34 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 Tetrachlorobiphenyls 85.8 ug/kg 0.084/23/2002 AR-103-103 615168 4790668 1 0208031-10 Pentachlorobiphenyls 143 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 Hexachlorobiphenyls 194 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 Heptachlorobiphenyls 72.6 ug/kg 0.074/23/2002 AR-103-103 615168 4790668 1 0208031-10 Octachlorobiphenyls 14.9 ug/kg 0.054/23/2002 AR-103-103 615168 4790668 1 0208031-10 Nonachlorobiphenyls 10.1 ug/kg 0.24/23/2002 AR-103-103 615168 4790668 1 0208031-10 Decachlorobiphenyl 3.10 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 Total Homologs 525 ug/kg 0.14/23/2002 AR-103-103 615168 4790668 1 0208031-10 Percent Lipids 5.3 % 04/23/2002 AR-103-103 615168 4790668 1 0208031-10 Percent Moisture 86 % 5/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#8 0.0930 UJ ug/kg 0.095/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#18 0.141 UJ ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#28 0.522 J ug/kg 0.035/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#31 0.291 J ug/kg 0.065/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#44 0.114 UJ ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#45 0.0760 UJ ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 22 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#47 13.0 J ug/kg 0.1

5/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#49 5.83 J ug/kg 0.095/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#52 10.0 J ug/kg 0.055/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#56 0.0820 UJ ug/kg 0.085/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#66 2.77 J ug/kg 0.065/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#70 0.0690 UJ ug/kg 0.065/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#74 14.1 J ug/kg 0.075/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#77 0.0530 UJ ug/kg 0.055/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#81 0.0710 UJ ug/kg 0.075/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#87 5.81 J ug/kg 0.085/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#95 2.06 J ug/kg 0.075/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#99 12.2 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#101 11.1 J ug/kg 0.065/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#105 3.41 J ug/kg 0.085/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#110 0.837 J ug/kg 0.075/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#114 0.0650 UJ ug/kg 0.065/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#118 15.6 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#123 0.0610 UJ ug/kg 0.065/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#126 0.0820 UJ ug/kg 0.085/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#128 1.03 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#138 27.7 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#146 9.33 J ug/kg 0.065/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#149 5.06 J ug/kg 0.095/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#151 1.31 J ug/kg 0.065/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#153 45.3 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#156 3.34 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#157 0.692 J ug/kg 0.25/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#158 2.02 J ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 23 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#167 3.25 J ug/kg 0.2

5/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#169 3.24 UJ ug/kg 35/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#170 10.3 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#174 0.692 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#177 2.02 J ug/kg 0.055/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#180 23.9 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#183 4.39 J ug/kg 0.035/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#189 0.158 UJ ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#187 26.7 J ug/kg 0.095/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#194 4.38 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#195 1.26 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#201 6.30 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#206 3.46 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 BZ#209 1.46 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 Monochlorobiphenyls 0.0530 UJ ug/kg 0.055/8/2002 AR-107-110 615052 4783124 1 0208031-11 Dichlorobiphenyls 0.0930 UJ ug/kg 0.095/8/2002 AR-107-110 615052 4783124 1 0208031-11 Trichlorobiphenyls 0.619 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 Tetrachlorobiphenyls 64.6 J ug/kg 0.055/8/2002 AR-107-110 615052 4783124 1 0208031-11 Pentachlorobiphenyls 96.3 J ug/kg 0.085/8/2002 AR-107-110 615052 4783124 1 0208031-11 Hexachlorobiphenyls 124 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 Heptachlorobiphenyls 64.6 J ug/kg 0.045/8/2002 AR-107-110 615052 4783124 1 0208031-11 Octachlorobiphenyls 13.3 J ug/kg 0.035/8/2002 AR-107-110 615052 4783124 1 0208031-11 Nonachlorobiphenyls 4.53 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 Decachlorobiphenyl 1.41 J ug/kg 0.15/8/2002 AR-107-110 615052 4783124 1 0208031-11 Total Homologs 369 J ug/kg 0.075/8/2002 AR-107-110 615052 4783124 1 0208031-11 Percent Lipids 6.1 % 05/8/2002 AR-107-110 615052 4783124 1 0208031-11 Percent Moisture 83 % 4/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#8 0.131 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 24 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#18 0.197 U ug/kg 0.1

4/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#28 0.0480 U ug/kg 0.044/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#31 0.0910 U ug/kg 0.094/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#44 0.160 U ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#45 0.107 U ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#47 0.424 J ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#49 0.288 J ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#52 0.526 ug/kg 0.084/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#56 0.115 U ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#66 0.0960 U ug/kg 0.094/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#70 0.0960 U ug/kg 0.094/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#74 0.984 ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#77 0.0750 U ug/kg 0.074/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#81 0.0990 U ug/kg 0.094/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#87 0.543 ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#95 0.119 J ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#99 1.31 ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#101 1.37 ug/kg 0.094/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#105 0.123 U ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#110 0.187 J ug/kg 0.094/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#114 0.0910 U ug/kg 0.094/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#118 2.39 ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#123 0.0850 U ug/kg 0.084/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#126 0.115 U ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#128 0.254 J ug/kg 0.24/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#138 4.43 ug/kg 0.24/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#146 1.34 ug/kg 0.084/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#149 0.611 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 25 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#151 0.136 J ug/kg 0.09

4/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#153 5.77 ug/kg 0.24/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#156 1.24 ug/kg 0.24/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#157 0.373 J ug/kg 0.24/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#158 0.271 J ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#167 0.560 J ug/kg 0.34/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#169 4.53 U ug/kg 44/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#170 1.22 ug/kg 0.24/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#174 0.144 U ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#177 0.543 ug/kg 0.084/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#180 2.04 ug/kg 0.24/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#183 0.305 ug/kg 0.054/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#189 0.221 U ug/kg 0.24/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#187 3.78 ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#194 0.509 J ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#195 0.162 U ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#201 1.27 ug/kg 0.24/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#206 0.662 ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 BZ#209 0.492 ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 Monochlorobiphenyls 0.0750 U ug/kg 0.074/24/2002 AR-200-200 615772 4767020 2 0208031-12 Dichlorobiphenyls 0.131 U ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 Trichlorobiphenyls 0.170 U ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 Tetrachlorobiphenyls 2.94 ug/kg 0.074/24/2002 AR-200-200 615772 4767020 2 0208031-12 Pentachlorobiphenyls 11.1 ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 Hexachlorobiphenyls 19.9 ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 Heptachlorobiphenyls 9.92 ug/kg 0.064/24/2002 AR-200-200 615772 4767020 2 0208031-12 Octachlorobiphenyls 3.75 ug/kg 0.054/24/2002 AR-200-200 615772 4767020 2 0208031-12 Nonachlorobiphenyls 0.475 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 26 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 AR-200-200 615772 4767020 2 0208031-12 Decachlorobiphenyl 0.441 J ug/kg 0.1

4/24/2002 AR-200-200 615772 4767020 2 0208031-12 Total Homologs 48.1 ug/kg 0.14/24/2002 AR-200-200 615772 4767020 2 0208031-12 Percent Lipids 6.3 % 04/24/2002 AR-200-200 615772 4767020 2 0208031-12 Percent Moisture 87 % 4/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#8 0.0990 UJ ug/kg 0.094/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#18 0.149 UJ ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#28 0.0360 UJ ug/kg 0.034/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#31 0.0690 UJ ug/kg 0.064/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#44 0.121 UJ ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#45 0.0810 UJ ug/kg 0.084/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#47 0.784 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#49 0.784 J ug/kg 0.094/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#52 2.56 J ug/kg 0.064/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#56 0.167 J ug/kg 0.084/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#66 0.334 J ug/kg 0.074/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#70 0.0730 UJ ug/kg 0.074/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#74 1.13 J ug/kg 0.074/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#77 0.0560 UJ ug/kg 0.054/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#81 0.0750 UJ ug/kg 0.074/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#87 1.62 J ug/kg 0.084/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#95 1.64 J ug/kg 0.074/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#99 5.65 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#101 8.00 J ug/kg 0.064/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#105 0.462 J ug/kg 0.094/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#110 0.0750 UJ ug/kg 0.074/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#114 0.0690 UJ ug/kg 0.064/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#118 3.52 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#123 0.0650 UJ ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 27 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#126 0.0870 UJ ug/kg 0.08

4/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#128 0.385 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#138 21.3 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#146 5.55 J ug/kg 0.064/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#149 6.99 J ug/kg 0.094/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#151 1.40 J ug/kg 0.074/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#153 17.1 J ug/kg 0.24/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#156 1.57 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#157 0.540 J ug/kg 0.24/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#158 1.68 J ug/kg 0.074/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#167 3.46 J ug/kg 0.24/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#169 3.43 UJ ug/kg 34/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#170 4.54 J ug/kg 0.24/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#174 1.61 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#177 2.58 J ug/kg 0.064/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#180 7.07 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#183 1.85 J ug/kg 0.034/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#189 0.167 UJ ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#187 22.7 J ug/kg 0.094/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#194 1.57 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#195 0.578 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#201 2.97 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#206 2.00 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 BZ#209 4.54 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 Monochlorobiphenyls 0.0560 UJ ug/kg 0.054/27/2002 AR-202-203 607953 4737820 3 0208031-13 Dichlorobiphenyls 0.0990 UJ ug/kg 0.094/27/2002 AR-202-203 607953 4737820 3 0208031-13 Trichlorobiphenyls 0.129 UJ ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 Tetrachlorobiphenyls 6.46 J ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 28 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/27/2002 AR-202-203 607953 4737820 3 0208031-13 Pentachlorobiphenyls 42.4 J ug/kg 0.08

4/27/2002 AR-202-203 607953 4737820 3 0208031-13 Hexachlorobiphenyls 78.8 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 Heptachlorobiphenyls 39.1 J ug/kg 0.054/27/2002 AR-202-203 607953 4737820 3 0208031-13 Octachlorobiphenyls 7.67 J ug/kg 0.034/27/2002 AR-202-203 607953 4737820 3 0208031-13 Nonachlorobiphenyls 3.26 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 Decachlorobiphenyl 4.56 J ug/kg 0.14/27/2002 AR-202-203 607953 4737820 3 0208031-13 Total Homologs 182 J ug/kg 0.074/27/2002 AR-202-203 607953 4737820 3 0208031-13 Percent Lipids 6.9 % 04/27/2002 AR-202-203 607953 4737820 3 0208031-13 Percent Moisture 90 % 4/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#8 0.131 U ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#18 0.198 U ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#28 2.54 ug/kg 0.044/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#31 3.32 ug/kg 0.094/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#44 0.161 U ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#45 0.107 U ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#47 27.0 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#49 36.5 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#52 63.9 ug/kg 0.084/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#56 0.115 U ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#66 5.38 ug/kg 0.094/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#70 4.64 ug/kg 0.094/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#74 23.4 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#77 0.0750 U ug/kg 0.074/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#81 0.0990 U ug/kg 0.094/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#87 18.1 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#95 19.2 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#99 43.8 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#101 64.8 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 29 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#105 5.08 ug/kg 0.1

4/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#110 11.9 ug/kg 0.094/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#114 0.0910 U ug/kg 0.094/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#118 33.8 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#123 0.0860 U ug/kg 0.084/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#126 0.115 U ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#128 2.57 ug/kg 0.24/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#138 76.6 ug/kg 0.24/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#146 20.7 ug/kg 0.084/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#149 47.1 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#151 9.46 ug/kg 0.094/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#153 63.5 ug/kg 0.24/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#156 7.00 ug/kg 0.24/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#157 1.88 ug/kg 0.24/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#158 4.30 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#167 11.7 ug/kg 0.34/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#169 4.55 U ug/kg 44/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#170 8.52 ug/kg 0.24/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#174 2.93 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#177 4.28 ug/kg 0.084/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#180 12.7 ug/kg 0.24/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#183 2.88 ug/kg 0.054/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#189 0.222 U ug/kg 0.24/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#187 50.5 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#194 1.89 J ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#195 0.614 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#201 8.25 ug/kg 0.24/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#206 4.60 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 30 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/29/2002 AR-203-204 607494 4748588 3 0208031-14 BZ#209 2.15 ug/kg 0.1

4/29/2002 AR-203-204 607494 4748588 3 0208031-14 Monochlorobiphenyls 0.0750 U ug/kg 0.074/29/2002 AR-203-204 607494 4748588 3 0208031-14 Dichlorobiphenyls 0.131 U ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 Trichlorobiphenyls 0.171 U ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 Tetrachlorobiphenyls 208 ug/kg 0.074/29/2002 AR-203-204 607494 4748588 3 0208031-14 Pentachlorobiphenyls 336 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 Hexachlorobiphenyls 310 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 Heptachlorobiphenyls 81.6 ug/kg 0.064/29/2002 AR-203-204 607494 4748588 3 0208031-14 Octachlorobiphenyls 12.5 ug/kg 0.054/29/2002 AR-203-204 607494 4748588 3 0208031-14 Nonachlorobiphenyls 5.66 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 Decachlorobiphenyl 2.56 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 Total Homologs 956 ug/kg 0.14/29/2002 AR-203-204 607494 4748588 3 0208031-14 Percent Lipids 9.6 % 04/29/2002 AR-203-204 607494 4748588 3 0208031-14 Percent Moisture 89 % 5/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#8 0.258 U ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#18 0.389 U ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#28 12.1 ug/kg 0.095/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#31 14.2 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#44 0.315 U ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#45 0.210 U ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#47 161 ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#49 206 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#52 443 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#56 9.04 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#66 37.0 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#70 27.2 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#74 183 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#77 0.147 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 31 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#81 0.195 U ug/kg 0.1

5/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#87 115 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#95 71.5 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#99 271 ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#101 364 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#105 21.7 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#110 37.7 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#114 7.50 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#118 177 ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#123 0.168 U ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#126 0.226 U ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#128 8.04 ug/kg 0.45/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#138 438 ug/kg 0.45/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#146 118 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#149 209 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#151 69.8 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#153 298 ug/kg 0.55/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#156 22.6 ug/kg 0.55/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#157 5.56 ug/kg 0.55/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#158 15.7 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#167 55.6 ug/kg 0.65/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#169 8.94 U ug/kg 85/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#170 48.2 ug/kg 0.55/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#174 17.7 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#177 31.0 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#180 73.0 ug/kg 0.45/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#183 12.9 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#189 2.34 ug/kg 0.4

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 32 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#187 366 ug/kg 0.2

5/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#194 13.9 J ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#195 6.50 ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#201 65.0 ug/kg 0.45/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#206 28.2 ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 BZ#209 8.60 ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 Monochlorobiphenyls 0.147 U ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 Dichlorobiphenyls 0.258 U ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 Trichlorobiphenyls 25.7 ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 Tetrachlorobiphenyls 1400 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 Pentachlorobiphenyls 1910 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 Hexachlorobiphenyls 1610 ug/kg 0.25/1/2002 AR-205-206 609801 4741849 3 0208031-15 Heptachlorobiphenyls 542 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 Octachlorobiphenyls 111 ug/kg 0.15/1/2002 AR-205-206 609801 4741849 3 0208031-15 Nonachlorobiphenyls 48.0 ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 Decachlorobiphenyl 8.60 ug/kg 0.35/1/2002 AR-205-206 609801 4741849 3 0208031-15 Total Homologs 5660 ug/kg 0.55/1/2002 AR-205-206 609801 4741849 3 0208031-15 Percent Lipids 13 % 05/1/2002 AR-205-206 609801 4741849 3 0208031-15 Percent Moisture 77 % 5/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#8 0.0666 U ug/kg 0.065/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#18 0.101 U ug/kg 0.15/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#28 5.36 ug/kg 0.025/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#31 5.54 ug/kg 0.045/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#44 3.65 ug/kg 0.085/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#45 0.0544 U ug/kg 0.055/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#47 33.1 ug/kg 0.085/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#49 32.5 ug/kg 0.065/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#52 61.2 ug/kg 0.04

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 33 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#56 2.53 ug/kg 0.05

5/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#66 27.6 ug/kg 0.045/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#70 42.8 ug/kg 0.045/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#74 45.3 ug/kg 0.055/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#77 0.0381 U ug/kg 0.035/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#81 0.0503 U ug/kg 0.055/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#87 24.5 ug/kg 0.055/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#95 10.3 ug/kg 0.055/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#99 61.4 ug/kg 0.095/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#101 86.8 ug/kg 0.045/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#105 20.0 ug/kg 0.065/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#110 14.1 ug/kg 0.055/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#114 3.44 ug/kg 0.045/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#118 83.4 ug/kg 0.095/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#123 0.0435 U ug/kg 0.045/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#126 0.0584 U ug/kg 0.055/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#128 5.45 ug/kg 0.15/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#138 181 ug/kg 0.15/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#146 34.6 ug/kg 0.045/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#149 78.3 ug/kg 0.065/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#151 16.5 ug/kg 0.045/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#153 96.3 ug/kg 0.15/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#156 8.30 ug/kg 0.15/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#157 0.147 U ug/kg 0.15/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#158 8.21 ug/kg 0.055/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#167 20.7 ug/kg 0.15/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#169 2.31 U ug/kg 25/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#170 16.4 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 34 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#174 6.94 ug/kg 0.07

5/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#177 10.3 ug/kg 0.045/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#180 18.0 ug/kg 0.15/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#183 5.01 ug/kg 0.025/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#189 0.113 U ug/kg 0.15/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#187 110 ug/kg 0.065/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#194 5.28 ug/kg 0.075/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#195 2.15 ug/kg 0.085/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#201 21.5 ug/kg 0.15/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#206 10.1 ug/kg 0.095/1/2002 AR-206-207 609915 4741451 3 0208032-01 BZ#209 2.84 ug/kg 0.075/1/2002 AR-206-207 609915 4741451 3 0208032-01 Monochlorobiphenyls 0.0381 U ug/kg 0.035/1/2002 AR-206-207 609915 4741451 3 0208032-01 Dichlorobiphenyls 0.0666 U ug/kg 0.065/1/2002 AR-206-207 609915 4741451 3 0208032-01 Trichlorobiphenyls 11.0 ug/kg 0.085/1/2002 AR-206-207 609915 4741451 3 0208032-01 Tetrachlorobiphenyls 248 ug/kg 0.035/1/2002 AR-206-207 609915 4741451 3 0208032-01 Pentachlorobiphenyls 524 ug/kg 0.055/1/2002 AR-206-207 609915 4741451 3 0208032-01 Hexachlorobiphenyls 440 ug/kg 0.075/1/2002 AR-206-207 609915 4741451 3 0208032-01 Heptachlorobiphenyls 144 ug/kg 0.035/1/2002 AR-206-207 609915 4741451 3 0208032-01 Octachlorobiphenyls 30.8 ug/kg 0.025/1/2002 AR-206-207 609915 4741451 3 0208032-01 Nonachlorobiphenyls 20.3 ug/kg 0.095/1/2002 AR-206-207 609915 4741451 3 0208032-01 Decachlorobiphenyl 2.84 ug/kg 0.075/1/2002 AR-206-207 609915 4741451 3 0208032-01 Total Homologs 1420 ug/kg 0.065/1/2002 AR-206-207 609915 4741451 3 0208032-01 Percent Lipids 6.9 % 05/1/2002 AR-206-207 609915 4741451 3 0208032-01 Percent Moisture 76 % 5/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#8 0.0837 U ug/kg 0.085/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#18 0.126 U ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#28 18.4 ug/kg 0.035/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#31 9.18 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 35 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#44 0.102 U ug/kg 0.1

5/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#45 0.0683 U ug/kg 0.065/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#47 128 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#49 88.5 ug/kg 0.085/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#52 211 ug/kg 0.055/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#56 4.85 ug/kg 0.075/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#66 49.4 ug/kg 0.065/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#70 13.0 ug/kg 0.065/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#74 109 ug/kg 0.065/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#77 0.0478 U ug/kg 0.045/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#81 0.0632 U ug/kg 0.065/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#87 45.2 ug/kg 0.075/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#95 31.3 ug/kg 0.065/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#99 114 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#101 135 ug/kg 0.055/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#105 29.0 ug/kg 0.075/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#110 17.1 ug/kg 0.065/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#114 5.72 ug/kg 0.055/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#118 116 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#123 0.0547 U ug/kg 0.055/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#126 0.0734 U ug/kg 0.075/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#128 4.62 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#138 182 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#146 41.0 ug/kg 0.055/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#149 69.0 ug/kg 0.085/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#151 25.3 ug/kg 0.065/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#153 97.8 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#156 7.44 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 36 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#157 2.11 ug/kg 0.1

5/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#158 9.49 ug/kg 0.065/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#167 18.5 ug/kg 0.25/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#169 2.90 U ug/kg 25/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#170 19.3 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#174 5.24 ug/kg 0.095/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#177 12.0 ug/kg 0.055/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#180 23.7 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#183 6.97 ug/kg 0.035/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#189 0.142 U ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#187 135 ug/kg 0.085/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#194 7.54 ug/kg 0.095/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#195 2.43 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#201 27.1 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#206 12.8 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 BZ#209 3.79 ug/kg 0.095/1/2002 AR-207-208 609763 4741194 3 0208032-02 Monochlorobiphenyls 0.0478 U ug/kg 0.045/1/2002 AR-207-208 609763 4741194 3 0208032-02 Dichlorobiphenyls 0.0837 U ug/kg 0.085/1/2002 AR-207-208 609763 4741194 3 0208032-02 Trichlorobiphenyls 24.1 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 Tetrachlorobiphenyls 648 ug/kg 0.045/1/2002 AR-207-208 609763 4741194 3 0208032-02 Pentachlorobiphenyls 866 ug/kg 0.075/1/2002 AR-207-208 609763 4741194 3 0208032-02 Hexachlorobiphenyls 426 ug/kg 0.095/1/2002 AR-207-208 609763 4741194 3 0208032-02 Heptachlorobiphenyls 173 ug/kg 0.045/1/2002 AR-207-208 609763 4741194 3 0208032-02 Octachlorobiphenyls 37.7 ug/kg 0.035/1/2002 AR-207-208 609763 4741194 3 0208032-02 Nonachlorobiphenyls 23.7 ug/kg 0.15/1/2002 AR-207-208 609763 4741194 3 0208032-02 Decachlorobiphenyl 3.79 ug/kg 0.095/1/2002 AR-207-208 609763 4741194 3 0208032-02 Total Homologs 2200 ug/kg 0.085/1/2002 AR-207-208 609763 4741194 3 0208032-02 Percent Lipids 5.9 % 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 37 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-207-208 609763 4741194 3 0208032-02 Percent Moisture 76 % 

5/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#8 0.0755 U ug/kg 0.075/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#18 0.114 U ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#28 13.8 ug/kg 0.025/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#31 10.6 ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#44 0.0924 U ug/kg 0.095/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#45 0.0616 U ug/kg 0.065/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#47 83.6 ug/kg 0.095/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#49 175 ug/kg 0.075/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#52 215 ug/kg 0.045/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#56 4.12 ug/kg 0.065/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#66 43.0 ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#70 18.7 ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#74 85.8 ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#77 0.0431 U ug/kg 0.045/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#81 0.0570 U ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#87 51.8 ug/kg 0.065/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#95 56.0 ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#99 97.4 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#101 168 ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#105 21.4 ug/kg 0.075/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#110 52.3 ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#114 3.40 ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#118 79.1 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#123 0.0493 U ug/kg 0.045/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#126 0.0662 U ug/kg 0.065/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#128 2.24 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#138 134 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 38 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#146 27.0 ug/kg 0.05

5/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#149 111 ug/kg 0.075/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#151 27.4 ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#153 55.1 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#156 2.45 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#157 1.07 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#158 3.00 ug/kg 0.055/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#167 12.1 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#169 2.62 U ug/kg 25/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#170 7.49 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#174 6.04 ug/kg 0.085/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#177 7.80 ug/kg 0.045/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#180 13.6 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#183 4.15 ug/kg 0.025/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#189 0.128 U ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#187 133 ug/kg 0.075/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#194 4.43 ug/kg 0.085/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#195 0.706 ug/kg 0.095/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#201 54.8 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#206 25.5 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 BZ#209 6.54 ug/kg 0.085/1/2002 AR-208-209 615981 4774104 1 0208032-03 Monochlorobiphenyls 0.0431 U ug/kg 0.045/1/2002 AR-208-209 615981 4774104 1 0208032-03 Dichlorobiphenyls 0.0755 U ug/kg 0.075/1/2002 AR-208-209 615981 4774104 1 0208032-03 Trichlorobiphenyls 22.4 ug/kg 0.095/1/2002 AR-208-209 615981 4774104 1 0208032-03 Tetrachlorobiphenyls 736 ug/kg 0.045/1/2002 AR-208-209 615981 4774104 1 0208032-03 Pentachlorobiphenyls 961 ug/kg 0.065/1/2002 AR-208-209 615981 4774104 1 0208032-03 Hexachlorobiphenyls 394 ug/kg 0.085/1/2002 AR-208-209 615981 4774104 1 0208032-03 Heptachlorobiphenyls 146 ug/kg 0.03

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 39 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-208-209 615981 4774104 1 0208032-03 Octachlorobiphenyls 58.1 ug/kg 0.02

5/1/2002 AR-208-209 615981 4774104 1 0208032-03 Nonachlorobiphenyls 53.6 ug/kg 0.15/1/2002 AR-208-209 615981 4774104 1 0208032-03 Decachlorobiphenyl 6.54 ug/kg 0.085/1/2002 AR-208-209 615981 4774104 1 0208032-03 Total Homologs 2380 ug/kg 0.075/1/2002 AR-208-209 615981 4774104 1 0208032-03 Percent Lipids 5.4 % 05/1/2002 AR-208-209 615981 4774104 1 0208032-03 Percent Moisture 83 % 5/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#8 0.0763 U ug/kg 0.075/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#18 0.115 U ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#28 12.1 ug/kg 0.025/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#31 12.3 ug/kg 0.055/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#44 0.0935 U ug/kg 0.095/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#45 0.0623 U ug/kg 0.065/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#47 434 ug/kg 0.095/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#49 368 ug/kg 0.075/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#52 776 ug/kg 0.25/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#56 8.10 ug/kg 0.065/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#66 91.6 ug/kg 0.055/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#70 34.9 ug/kg 0.055/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#74 554 ug/kg 0.35/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#77 0.0436 U ug/kg 0.045/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#81 0.0576 U ug/kg 0.055/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#87 158 ug/kg 0.065/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#95 97.3 ug/kg 0.055/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#99 367 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#101 439 ug/kg 0.055/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#105 74.4 ug/kg 0.075/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#110 67.4 ug/kg 0.055/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#114 15.5 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 40 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#118 340 ug/kg 0.1

5/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#123 0.0499 U ug/kg 0.045/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#126 0.0670 U ug/kg 0.065/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#128 7.81 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#138 314 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#146 53.7 ug/kg 0.055/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#149 165 ug/kg 0.075/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#151 33.6 ug/kg 0.055/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#153 156 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#156 10.9 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#157 3.32 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#158 16.8 ug/kg 0.055/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#167 38.3 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#169 2.65 U ug/kg 25/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#170 20.0 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#174 11.3 ug/kg 0.085/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#177 16.6 ug/kg 0.045/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#180 27.2 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#183 7.66 ug/kg 0.025/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#189 0.129 U ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#187 141 ug/kg 0.075/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#194 5.58 ug/kg 0.085/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#195 0.357 ug/kg 0.095/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#201 36.6 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#206 16.3 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 BZ#209 3.36 ug/kg 0.085/1/2002 AR-209-210 616079 4774362 1 0208032-04 Monochlorobiphenyls 0.0436 U ug/kg 0.045/1/2002 AR-209-210 616079 4774362 1 0208032-04 Dichlorobiphenyls 0.0763 U ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 41 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-209-210 616079 4774362 1 0208032-04 Trichlorobiphenyls 22.7 ug/kg 0.09

5/1/2002 AR-209-210 616079 4774362 1 0208032-04 Tetrachlorobiphenyls 3290 ug/kg 0.25/1/2002 AR-209-210 616079 4774362 1 0208032-04 Pentachlorobiphenyls 2680 ug/kg 0.065/1/2002 AR-209-210 616079 4774362 1 0208032-04 Hexachlorobiphenyls 816 ug/kg 0.085/1/2002 AR-209-210 616079 4774362 1 0208032-04 Heptachlorobiphenyls 195 ug/kg 0.035/1/2002 AR-209-210 616079 4774362 1 0208032-04 Octachlorobiphenyls 46.0 ug/kg 0.025/1/2002 AR-209-210 616079 4774362 1 0208032-04 Nonachlorobiphenyls 34.0 ug/kg 0.15/1/2002 AR-209-210 616079 4774362 1 0208032-04 Decachlorobiphenyl 3.51 ug/kg 0.085/1/2002 AR-209-210 616079 4774362 1 0208032-04 Total Homologs 7700 ug/kg 0.45/1/2002 AR-209-210 616079 4774362 1 0208032-04 Percent Lipids 8.4 % 05/1/2002 AR-209-210 616079 4774362 1 0208032-04 Percent Moisture 82 % 5/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#8 0.0677 U ug/kg 0.065/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#18 0.102 U ug/kg 0.15/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#28 101 ug/kg 0.025/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#31 48.4 ug/kg 0.045/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#44 14.4 ug/kg 0.085/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#45 0.0553 U ug/kg 0.055/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#47 821 ug/kg 0.55/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#49 568 ug/kg 0.45/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#52 834 ug/kg 0.25/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#56 48.3 ug/kg 0.055/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#66 357 ug/kg 0.045/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#70 105 ug/kg 0.045/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#74 898 ug/kg 0.35/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#77 0.0387 U ug/kg 0.035/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#81 4.76 NJ ug/kg 0.055/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#87 226 ug/kg 0.055/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#95 172 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 42 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#99 521 ug/kg 0.6

5/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#101 587 ug/kg 0.25/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#105 161 ug/kg 0.065/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#110 213 ug/kg 0.055/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#114 28.4 ug/kg 0.045/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#118 641 ug/kg 0.65/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#123 0.0442 U ug/kg 0.045/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#126 0.0594 U ug/kg 0.055/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#128 13.6 ug/kg 0.15/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#138 393 ug/kg 0.75/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#146 110 ug/kg 0.045/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#149 293 ug/kg 0.065/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#151 63.6 ug/kg 0.045/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#153 391 ug/kg 0.15/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#156 21.6 ug/kg 0.15/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#157 6.05 ug/kg 0.15/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#158 21.3 ug/kg 0.055/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#167 65.7 ug/kg 0.15/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#169 2.35 U ug/kg 25/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#170 67.3 ug/kg 0.15/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#174 18.5 ug/kg 0.075/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#177 26.7 ug/kg 0.045/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#180 97.0 ug/kg 0.15/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#183 29.5 ug/kg 0.025/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#189 3.12 ug/kg 0.15/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#187 355 ug/kg 0.065/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#194 23.7 ug/kg 0.075/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#195 6.98 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 43 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#201 62.0 ug/kg 0.1

5/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#206 24.2 ug/kg 0.095/1/2002 AR-210-211 615871 4770860 2 0208032-05 BZ#209 7.48 ug/kg 0.075/1/2002 AR-210-211 615871 4770860 2 0208032-05 Monochlorobiphenyls 0.0387 U ug/kg 0.035/1/2002 AR-210-211 615871 4770860 2 0208032-05 Dichlorobiphenyls 0.0677 U ug/kg 0.065/1/2002 AR-210-211 615871 4770860 2 0208032-05 Trichlorobiphenyls 135 ug/kg 0.085/1/2002 AR-210-211 615871 4770860 2 0208032-05 Tetrachlorobiphenyls 5090 ug/kg 0.25/1/2002 AR-210-211 615871 4770860 2 0208032-05 Pentachlorobiphenyls 4410 ug/kg 0.35/1/2002 AR-210-211 615871 4770860 2 0208032-05 Hexachlorobiphenyls 1670 ug/kg 0.45/1/2002 AR-210-211 615871 4770860 2 0208032-05 Heptachlorobiphenyls 478 ug/kg 0.035/1/2002 AR-210-211 615871 4770860 2 0208032-05 Octachlorobiphenyls 91.5 ug/kg 0.025/1/2002 AR-210-211 615871 4770860 2 0208032-05 Nonachlorobiphenyls 43.9 ug/kg 0.095/1/2002 AR-210-211 615871 4770860 2 0208032-05 Decachlorobiphenyl 7.48 ug/kg 0.075/1/2002 AR-210-211 615871 4770860 2 0208032-05 Total Homologs 12100 ug/kg 0.45/1/2002 AR-210-211 615871 4770860 2 0208032-05 Percent Lipids 5.7 % 05/1/2002 AR-210-211 615871 4770860 2 0208032-05 Percent Moisture 84 % 5/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#8 0.0818 U ug/kg 0.085/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#18 0.124 U ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#28 16.5 ug/kg 0.035/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#31 8.35 ug/kg 0.055/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#44 0.100 U ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#45 0.0668 U ug/kg 0.065/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#47 132 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#49 55.4 ug/kg 0.085/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#52 108 ug/kg 0.055/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#56 6.32 ug/kg 0.075/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#66 36.4 ug/kg 0.065/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#70 17.4 ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 44 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#74 145 ug/kg 0.06

5/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#77 0.0468 U ug/kg 0.045/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#81 0.0618 U ug/kg 0.065/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#87 45.5 ug/kg 0.075/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#95 20.7 ug/kg 0.065/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#99 155 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#101 133 ug/kg 0.055/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#105 19.5 ug/kg 0.075/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#110 21.6 ug/kg 0.065/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#114 7.31 ug/kg 0.055/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#118 113 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#123 0.0534 U ug/kg 0.055/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#126 0.0718 U ug/kg 0.075/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#128 4.97 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#138 168 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#146 37.2 ug/kg 0.055/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#149 41.0 ug/kg 0.085/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#151 8.03 ug/kg 0.065/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#153 116 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#156 8.72 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#157 2.12 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#158 10.9 ug/kg 0.065/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#167 18.6 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#169 2.84 U ug/kg 25/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#170 18.9 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#174 2.93 ug/kg 0.095/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#177 8.28 ug/kg 0.055/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#180 27.4 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 45 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#183 7.32 ug/kg 0.03

5/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#189 0.139 U ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#187 98.0 ug/kg 0.075/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#194 6.83 ug/kg 0.085/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#195 2.14 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#201 14.0 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#206 6.98 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 BZ#209 2.53 ug/kg 0.095/9/2002 AR-211-212 614012 4788437 1 0208032-06 Monochlorobiphenyls 0.0468 U ug/kg 0.045/9/2002 AR-211-212 614012 4788437 1 0208032-06 Dichlorobiphenyls 0.0818 U ug/kg 0.085/9/2002 AR-211-212 614012 4788437 1 0208032-06 Trichlorobiphenyls 22.6 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 Tetrachlorobiphenyls 610 ug/kg 0.045/9/2002 AR-211-212 614012 4788437 1 0208032-06 Pentachlorobiphenyls 844 ug/kg 0.075/9/2002 AR-211-212 614012 4788437 1 0208032-06 Hexachlorobiphenyls 417 ug/kg 0.085/9/2002 AR-211-212 614012 4788437 1 0208032-06 Heptachlorobiphenyls 137 ug/kg 0.045/9/2002 AR-211-212 614012 4788437 1 0208032-06 Octachlorobiphenyls 23.4 ug/kg 0.035/9/2002 AR-211-212 614012 4788437 1 0208032-06 Nonachlorobiphenyls 12.0 ug/kg 0.15/9/2002 AR-211-212 614012 4788437 1 0208032-06 Decachlorobiphenyl 2.53 ug/kg 0.095/9/2002 AR-211-212 614012 4788437 1 0208032-06 Total Homologs 2070 ug/kg 0.085/9/2002 AR-211-212 614012 4788437 1 0208032-06 Percent Lipids 5.1 % 05/9/2002 AR-211-212 614012 4788437 1 0208032-06 Percent Moisture 80 % 5/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#8 0.132 U ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#18 0.199 U ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#28 9.77 ug/kg 0.045/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#31 8.34 ug/kg 0.095/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#44 0.161 U ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#45 0.108 U ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#47 181 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 46 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#49 98.6 ug/kg 0.1

5/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#52 304 ug/kg 0.085/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#56 1.34 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#66 14.4 ug/kg 0.095/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#70 9.14 ug/kg 0.095/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#74 134 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#77 0.0752 U ug/kg 0.075/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#81 0.599 NJ ug/kg 0.095/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#87 39.1 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#95 27.7 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#99 129 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#101 151 ug/kg 0.095/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#105 8.22 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#110 7.94 ug/kg 0.095/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#114 5.05 ug/kg 0.095/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#118 65.8 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#123 0.0860 U ug/kg 0.085/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#126 0.116 U ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#128 1.81 ug/kg 0.25/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#138 131 ug/kg 0.25/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#146 32.7 ug/kg 0.085/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#149 44.9 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#151 13.0 ug/kg 0.095/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#153 104 ug/kg 0.25/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#156 3.44 ug/kg 0.25/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#157 1.01 ug/kg 0.25/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#158 10.1 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#167 17.0 ug/kg 0.3

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 47 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#169 4.57 U ug/kg 4

5/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#170 0.277 U ug/kg 0.25/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#174 3.01 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#177 7.21 ug/kg 0.085/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#180 8.25 ug/kg 0.25/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#183 7.10 ug/kg 0.055/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#189 0.223 U ug/kg 0.25/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#187 72.5 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#194 0.142 U ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#195 0.164 U ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#201 25.4 ug/kg 0.25/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#206 0.188 U ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 BZ#209 1.32 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 Monochlorobiphenyls 0.0752 U ug/kg 0.075/13/2002 AR-217-219 614434 4790040 1 0208032-07 Dichlorobiphenyls 0.132 U ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 Trichlorobiphenyls 17.4 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 Tetrachlorobiphenyls 916 ug/kg 0.075/13/2002 AR-217-219 614434 4790040 1 0208032-07 Pentachlorobiphenyls 764 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 Hexachlorobiphenyls 368 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 Heptachlorobiphenyls 90.7 ug/kg 0.065/13/2002 AR-217-219 614434 4790040 1 0208032-07 Octachlorobiphenyls 25.4 ug/kg 0.055/13/2002 AR-217-219 614434 4790040 1 0208032-07 Nonachlorobiphenyls 2.62 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 Decachlorobiphenyl 1.32 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 Total Homologs 2190 ug/kg 0.15/13/2002 AR-217-219 614434 4790040 1 0208032-07 Percent Lipids 4.5 % 05/13/2002 AR-217-219 614434 4790040 1 0208032-07 Percent Moisture 74 % 5/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#8 0.0801 U ug/kg 0.085/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#18 0.121 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 48 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#28 0.0294 U ug/kg 0.02

5/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#31 0.0556 U ug/kg 0.055/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#44 0.0980 U ug/kg 0.095/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#45 0.0654 U ug/kg 0.065/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#47 2.84 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#49 2.47 ug/kg 0.085/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#52 7.88 ug/kg 0.045/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#56 0.0703 U ug/kg 0.075/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#66 0.874 ug/kg 0.055/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#70 0.635 ug/kg 0.055/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#74 5.96 ug/kg 0.065/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#77 0.0458 U ug/kg 0.045/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#81 0.0605 U ug/kg 0.065/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#87 5.41 ug/kg 0.075/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#95 1.31 ug/kg 0.065/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#99 10.9 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#101 12.1 ug/kg 0.055/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#105 2.06 ug/kg 0.075/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#110 1.25 ug/kg 0.065/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#114 0.0556 U ug/kg 0.055/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#118 9.87 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#123 0.0523 U ug/kg 0.055/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#126 0.0703 U ug/kg 0.075/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#128 0.593 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#138 28.3 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#146 5.54 ug/kg 0.055/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#149 5.76 ug/kg 0.075/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#151 1.44 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 49 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#153 14.9 ug/kg 0.1

5/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#156 1.01 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#157 0.176 U ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#158 1.50 ug/kg 0.065/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#167 2.72 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#169 2.78 U ug/kg 25/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#170 3.28 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#174 0.552 ug/kg 0.085/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#177 1.61 ug/kg 0.045/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#180 3.88 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#183 1.09 ug/kg 0.035/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#189 0.136 U ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#187 19.6 ug/kg 0.075/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#194 1.27 ug/kg 0.085/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#195 0.375 ug/kg 0.095/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#201 2.47 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#206 0.822 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 BZ#209 0.801 ug/kg 0.095/14/2002 AR-218-220 614473 4768339 2 0208032-08 Monochlorobiphenyls 0.0458 U ug/kg 0.045/14/2002 AR-218-220 614473 4768339 2 0208032-08 Dichlorobiphenyls 0.0801 U ug/kg 0.085/14/2002 AR-218-220 614473 4768339 2 0208032-08 Trichlorobiphenyls 0.105 U ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 Tetrachlorobiphenyls 25.1 ug/kg 0.045/14/2002 AR-218-220 614473 4768339 2 0208032-08 Pentachlorobiphenyls 75.8 ug/kg 0.075/14/2002 AR-218-220 614473 4768339 2 0208032-08 Hexachlorobiphenyls 60.5 ug/kg 0.085/14/2002 AR-218-220 614473 4768339 2 0208032-08 Heptachlorobiphenyls 25.8 ug/kg 0.045/14/2002 AR-218-220 614473 4768339 2 0208032-08 Octachlorobiphenyls 5.28 ug/kg 0.035/14/2002 AR-218-220 614473 4768339 2 0208032-08 Nonachlorobiphenyls 0.624 ug/kg 0.15/14/2002 AR-218-220 614473 4768339 2 0208032-08 Decachlorobiphenyl 0.801 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 50 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/14/2002 AR-218-220 614473 4768339 2 0208032-08 Total Homologs 194 ug/kg 0.08

5/14/2002 AR-218-220 614473 4768339 2 0208032-08 Percent Lipids 3.4 % 05/14/2002 AR-218-220 614473 4768339 2 0208032-08 Percent Moisture 72 % 5/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#8 0.0926 U ug/kg 0.095/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#18 0.140 U ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#28 3.03 ug/kg 0.035/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#31 3.00 ug/kg 0.065/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#44 0.113 U ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#45 0.0756 U ug/kg 0.075/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#47 55.4 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#49 31.4 ug/kg 0.095/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#52 62.4 ug/kg 0.055/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#56 1.29 ug/kg 0.085/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#66 6.59 ug/kg 0.065/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#70 6.15 ug/kg 0.065/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#74 44.1 ug/kg 0.075/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#77 0.0529 U ug/kg 0.055/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#81 0.0699 U ug/kg 0.065/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#87 26.1 ug/kg 0.085/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#95 13.6 ug/kg 0.075/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#99 78.8 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#101 80.9 ug/kg 0.065/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#105 7.89 ug/kg 0.085/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#110 15.5 ug/kg 0.065/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#114 1.40 ug/kg 0.065/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#118 49.2 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#123 0.0605 U ug/kg 0.065/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#126 0.0813 U ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 51 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#128 2.99 ug/kg 0.1

5/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#138 172 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#146 37.0 ug/kg 0.065/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#149 57.0 ug/kg 0.095/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#151 13.3 ug/kg 0.065/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#153 136 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#156 0.185 U ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#157 1.22 ug/kg 0.25/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#158 9.76 ug/kg 0.075/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#167 15.6 ug/kg 0.25/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#169 3.21 U ug/kg 35/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#170 30.6 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#174 10.0 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#177 20.4 ug/kg 0.055/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#180 37.4 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#183 17.9 ug/kg 0.035/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#189 0.157 U ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#187 188 ug/kg 0.085/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#194 7.25 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#195 4.88 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#201 29.5 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#206 12.9 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 BZ#209 2.89 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 Monochlorobiphenyls 0.0529 U ug/kg 0.055/14/2002 AR-219-221 607999 4751888 2 0208032-09 Dichlorobiphenyls 0.0926 U ug/kg 0.095/14/2002 AR-219-221 607999 4751888 2 0208032-09 Trichlorobiphenyls 5.57 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 Tetrachlorobiphenyls 253 ug/kg 0.055/14/2002 AR-219-221 607999 4751888 2 0208032-09 Pentachlorobiphenyls 506 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 52 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/14/2002 AR-219-221 607999 4751888 2 0208032-09 Hexachlorobiphenyls 470 ug/kg 0.1

5/14/2002 AR-219-221 607999 4751888 2 0208032-09 Heptachlorobiphenyls 269 ug/kg 0.045/14/2002 AR-219-221 607999 4751888 2 0208032-09 Octachlorobiphenyls 43.7 ug/kg 0.035/14/2002 AR-219-221 607999 4751888 2 0208032-09 Nonachlorobiphenyls 20.9 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 Decachlorobiphenyl 2.89 ug/kg 0.15/14/2002 AR-219-221 607999 4751888 2 0208032-09 Total Homologs 1570 ug/kg 0.095/14/2002 AR-219-221 607999 4751888 2 0208032-09 Percent Lipids 9.7 % 05/14/2002 AR-219-221 607999 4751888 2 0208032-09 Percent Moisture 69 % 5/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#8 0.0728 U ug/kg 0.075/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#18 0.110 U ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#28 0.662 ug/kg 0.025/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#31 0.435 ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#44 0.0891 U ug/kg 0.085/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#45 0.0594 U ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#47 55.6 ug/kg 0.095/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#49 29.3 ug/kg 0.075/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#52 57.6 ug/kg 0.045/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#56 0.0639 U ug/kg 0.065/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#66 3.34 ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#70 4.15 ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#74 75.0 ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#77 0.0416 U ug/kg 0.045/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#81 0.331 NJ ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#87 24.6 ug/kg 0.065/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#95 7.15 ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#99 76.5 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#101 98.0 ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#105 6.93 ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 53 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#110 4.69 ug/kg 0.05

5/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#114 3.64 ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#118 59.2 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#123 0.0475 U ug/kg 0.045/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#126 0.0639 U ug/kg 0.065/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#128 2.59 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#138 109 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#146 19.6 ug/kg 0.045/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#149 37.8 ug/kg 0.075/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#151 6.09 ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#153 62.3 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#156 6.06 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#157 1.40 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#158 7.28 ug/kg 0.055/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#167 14.5 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#169 2.53 U ug/kg 25/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#170 11.9 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#174 3.61 ug/kg 0.085/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#177 6.59 ug/kg 0.045/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#180 13.5 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#183 4.16 ug/kg 0.025/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#189 0.123 U ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#187 60.2 ug/kg 0.065/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#194 4.79 ug/kg 0.075/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#195 1.24 ug/kg 0.095/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#201 10.9 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#206 3.62 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 BZ#209 1.05 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 54 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/14/2002 AR-220-222 612325 4758816 2 0208032-10 Monochlorobiphenyls 0.0416 U ug/kg 0.04

5/14/2002 AR-220-222 612325 4758816 2 0208032-10 Dichlorobiphenyls 0.0728 U ug/kg 0.075/14/2002 AR-220-222 612325 4758816 2 0208032-10 Trichlorobiphenyls 1.03 ug/kg 0.095/14/2002 AR-220-222 612325 4758816 2 0208032-10 Tetrachlorobiphenyls 298 ug/kg 0.045/14/2002 AR-220-222 612325 4758816 2 0208032-10 Pentachlorobiphenyls 472 ug/kg 0.065/14/2002 AR-220-222 612325 4758816 2 0208032-10 Hexachlorobiphenyls 269 ug/kg 0.075/14/2002 AR-220-222 612325 4758816 2 0208032-10 Heptachlorobiphenyls 85.8 ug/kg 0.035/14/2002 AR-220-222 612325 4758816 2 0208032-10 Octachlorobiphenyls 10.4 ug/kg 0.025/14/2002 AR-220-222 612325 4758816 2 0208032-10 Nonachlorobiphenyls 6.77 ug/kg 0.15/14/2002 AR-220-222 612325 4758816 2 0208032-10 Decachlorobiphenyl 1.05 ug/kg 0.085/14/2002 AR-220-222 612325 4758816 2 0208032-10 Total Homologs 1140 ug/kg 0.075/14/2002 AR-220-222 612325 4758816 2 0208032-10 Percent Lipids 4.2 % 05/14/2002 AR-220-222 612325 4758816 2 0208032-10 Percent Moisture 67 % 4/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#8 0.0755 U ug/kg 0.074/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#18 0.114 U ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#28 0.0277 U ug/kg 0.024/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#31 0.0524 U ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#44 0.0924 U ug/kg 0.094/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#45 0.0616 U ug/kg 0.064/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#47 1.32 ug/kg 0.094/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#49 0.952 ug/kg 0.074/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#52 2.73 ug/kg 0.044/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#56 0.0662 U ug/kg 0.064/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#66 0.236 ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#70 0.226 ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#74 1.82 ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#77 0.0431 U ug/kg 0.044/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#81 0.0570 U ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 55 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#87 1.04 ug/kg 0.06

4/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#95 0.559 ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#99 3.61 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#101 4.24 ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#105 0.589 ug/kg 0.074/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#110 0.334 ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#114 0.0524 U ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#118 3.34 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#123 0.0493 U ug/kg 0.044/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#126 0.0662 U ug/kg 0.064/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#128 0.5 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#138 13.7 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#146 3.13 ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#149 2.52 ug/kg 0.074/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#151 0.432 ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#153 20.0 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#156 0.151 U ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#157 0.166 U ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#158 0.854 ug/kg 0.054/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#167 1.29 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#169 2.62 U ug/kg 24/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#170 5.58 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#174 0.589 ug/kg 0.084/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#177 1.18 ug/kg 0.044/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#180 10.7 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#183 3.31 ug/kg 0.024/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#189 0.128 U ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#187 25.7 ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 56 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#194 2.04 ug/kg 0.08

4/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#195 0.736 ug/kg 0.094/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#201 5.97 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#206 1.46 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 BZ#209 1.6 ug/kg 0.084/24/2002 AR-502-503 602694 4710886 4 0208032-11 Monochlorobiphenyls 0.0431 U ug/kg 0.044/24/2002 AR-502-503 602694 4710886 4 0208032-11 Dichlorobiphenyls 0.0755 U ug/kg 0.074/24/2002 AR-502-503 602694 4710886 4 0208032-11 Trichlorobiphenyls 0.0986 U ug/kg 0.094/24/2002 AR-502-503 602694 4710886 4 0208032-11 Tetrachlorobiphenyls 8.9 ug/kg 0.044/24/2002 AR-502-503 602694 4710886 4 0208032-11 Pentachlorobiphenyls 26 ug/kg 0.064/24/2002 AR-502-503 602694 4710886 4 0208032-11 Hexachlorobiphenyls 42.8 ug/kg 0.084/24/2002 AR-502-503 602694 4710886 4 0208032-11 Heptachlorobiphenyls 40.9 ug/kg 0.034/24/2002 AR-502-503 602694 4710886 4 0208032-11 Octachlorobiphenyls 10.8 ug/kg 0.024/24/2002 AR-502-503 602694 4710886 4 0208032-11 Nonachlorobiphenyls 2.73 ug/kg 0.14/24/2002 AR-502-503 602694 4710886 4 0208032-11 Decachlorobiphenyl 1.6 ug/kg 0.084/24/2002 AR-502-503 602694 4710886 4 0208032-11 Total Homologs 134 ug/kg 0.074/24/2002 AR-502-503 602694 4710886 4 0208032-11 Percent Lipids 7.3 % 04/24/2002 AR-502-503 602694 4710886 4 0208032-11 Percent Moisture 69 % 4/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#8 0.0611 U ug/kg 0.064/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#18 0.0922 U ug/kg 0.094/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#28 0.0224 U ug/kg 0.024/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#31 0.0424 U ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#44 0.0748 U ug/kg 0.074/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#45 0.0499 U ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#47 0.318 ug/kg 0.074/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#49 0.278 ug/kg 0.064/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#52 0.445 ug/kg 0.034/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#56 0.0536 U ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 57 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#66 0.0873 J ug/kg 0.04

4/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#70 0.0953 J ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#74 0.238 ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#77 0.0349 U ug/kg 0.034/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#81 0.0461 U ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#87 0.0536 U ug/kg 0.054/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#95 0.183 ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#99 1.68 ug/kg 0.094/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#101 1.8 ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#105 0.0573 U ug/kg 0.054/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#110 0.0461 U ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#114 0.0424 U ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#118 1.18 ug/kg 0.084/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#123 0.0399 U ug/kg 0.034/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#126 0.0536 U ug/kg 0.054/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#128 0.262 J ug/kg 0.14/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#138 8.63 ug/kg 0.14/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#146 2.1 ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#149 1.75 ug/kg 0.054/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#151 0.333 ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#153 7.12 ug/kg 0.14/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#156 0.122 U ug/kg 0.14/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#157 0.135 U ug/kg 0.14/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#158 0.683 ug/kg 0.044/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#167 1.15 ug/kg 0.14/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#169 2.12 U ug/kg 24/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#170 0.128 U ug/kg 0.14/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#174 0.524 ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 58 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#177 0.992 ug/kg 0.03

4/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#180 3.07 ug/kg 0.14/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#183 0.778 ug/kg 0.024/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#189 0.103 U ug/kg 0.14/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#187 10.5 ug/kg 0.054/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#194 0.0661 U ug/kg 0.064/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#195 0.254 ug/kg 0.074/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#201 2.69 ug/kg 0.14/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#206 0.849 ug/kg 0.084/30/2002 AR-503-504 601297 4703830 4 0208032-12 BZ#209 0.841 ug/kg 0.074/30/2002 AR-503-504 601297 4703830 4 0208032-12 Monochlorobiphenyls 0.0349 U ug/kg 0.034/30/2002 AR-503-504 601297 4703830 4 0208032-12 Dichlorobiphenyls 0.0611 U ug/kg 0.064/30/2002 AR-503-504 601297 4703830 4 0208032-12 Trichlorobiphenyls 0.0798 U ug/kg 0.074/30/2002 AR-503-504 601297 4703830 4 0208032-12 Tetrachlorobiphenyls 2.6 ug/kg 0.034/30/2002 AR-503-504 601297 4703830 4 0208032-12 Pentachlorobiphenyls 19.9 ug/kg 0.054/30/2002 AR-503-504 601297 4703830 4 0208032-12 Hexachlorobiphenyls 20.3 ug/kg 0.064/30/2002 AR-503-504 601297 4703830 4 0208032-12 Heptachlorobiphenyls 11.4 ug/kg 0.034/30/2002 AR-503-504 601297 4703830 4 0208032-12 Octachlorobiphenyls 4.35 ug/kg 0.024/30/2002 AR-503-504 601297 4703830 4 0208032-12 Nonachlorobiphenyls 1.74 ug/kg 0.084/30/2002 AR-503-504 601297 4703830 4 0208032-12 Decachlorobiphenyl 0.841 ug/kg 0.074/30/2002 AR-503-504 601297 4703830 4 0208032-12 Total Homologs 61.2 ug/kg 0.064/30/2002 AR-503-504 601297 4703830 4 0208032-12 Percent Lipids 7.5 % 04/30/2002 AR-503-504 601297 4703830 4 0208032-12 Percent Moisture 86 % 4/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#8 0.0906 U ug/kg 0.094/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#18 0.137 U ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#28 0.0333 U ug/kg 0.034/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#31 0.0629 U ug/kg 0.064/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#44 0.111 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 59 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#45 0.0740 U ug/kg 0.07

4/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#47 0.224 J ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#49 0.141 J ug/kg 0.094/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#52 0.259 ug/kg 0.054/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#56 0.0795 U ug/kg 0.074/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#66 0.0666 U ug/kg 0.064/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#70 0.0666 U ug/kg 0.064/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#74 0.177 J ug/kg 0.074/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#77 0.0518 U ug/kg 0.054/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#81 0.0684 U ug/kg 0.064/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#87 0.0795 U ug/kg 0.074/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#95 0.165 J ug/kg 0.074/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#99 0.884 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#101 1.12 ug/kg 0.064/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#105 0.0851 U ug/kg 0.084/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#110 0.0684 U ug/kg 0.064/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#114 0.0629 U ug/kg 0.064/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#118 0.848 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#123 0.0592 U ug/kg 0.054/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#126 0.0795 U ug/kg 0.074/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#128 0.247 J ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#138 5.42 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#146 1.30 ug/kg 0.064/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#149 1.32 ug/kg 0.084/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#151 0.0666 U ug/kg 0.064/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#153 4.31 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#156 0.181 U ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#157 0.200 U ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 60 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#158 0.354 ug/kg 0.07

4/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#167 0.99 ug/kg 0.24/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#169 3.14 U ug/kg 34/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#170 1.6 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#174 0.342 ug/kg 0.094/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#177 0.707 ug/kg 0.054/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#180 2.8 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#183 0.554 ug/kg 0.034/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#189 0.154 U ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#187 7.42 ug/kg 0.084/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#194 1.40 ug/kg 0.094/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#195 0.318 J ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#201 2.1 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#206 1.85 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 BZ#209 2.07 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 Monochlorobiphenyls 0.0518 U ug/kg 0.054/30/2002 AR-504-505 601264 4703894 4 0208032-13 Dichlorobiphenyls 0.0906 U ug/kg 0.094/30/2002 AR-504-505 601264 4703894 4 0208032-13 Trichlorobiphenyls 0.118 U ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 Tetrachlorobiphenyls 1.45 ug/kg 0.054/30/2002 AR-504-505 601264 4703894 4 0208032-13 Pentachlorobiphenyls 6.82 ug/kg 0.074/30/2002 AR-504-505 601264 4703894 4 0208032-13 Hexachlorobiphenyls 13.5 ug/kg 0.094/30/2002 AR-504-505 601264 4703894 4 0208032-13 Heptachlorobiphenyls 11.7 ug/kg 0.044/30/2002 AR-504-505 601264 4703894 4 0208032-13 Octachlorobiphenyls 4.60 ug/kg 0.034/30/2002 AR-504-505 601264 4703894 4 0208032-13 Nonachlorobiphenyls 4.98 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 Decachlorobiphenyl 2.07 ug/kg 0.14/30/2002 AR-504-505 601264 4703894 4 0208032-13 Total Homologs 45.1 ug/kg 0.094/30/2002 AR-504-505 601264 4703894 4 0208032-13 Percent Lipids 4.3 % 04/30/2002 AR-504-505 601264 4703894 4 0208032-13 Percent Moisture 82 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 61 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#8 0.0706 U ug/kg 0.07

4/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#18 0.107 U ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#28 0.0259 U ug/kg 0.024/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#31 0.049 U ug/kg 0.044/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#44 0.0864 U ug/kg 0.084/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#45 0.0576 U ug/kg 0.054/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#47 0.248 J ug/kg 0.084/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#49 0.183 J ug/kg 0.074/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#52 0.248 ug/kg 0.044/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#56 0.0619 U ug/kg 0.064/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#66 0.0518 U ug/kg 0.054/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#70 0.0518 U ug/kg 0.054/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#74 0.174 J ug/kg 0.054/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#77 0.0403 U ug/kg 0.044/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#81 0.0533 U ug/kg 0.054/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#87 0.0619 U ug/kg 0.064/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#95 0.0547 U ug/kg 0.054/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#99 1.66 ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#101 1.16 ug/kg 0.044/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#105 0.0662 U ug/kg 0.064/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#110 0.110 J ug/kg 0.054/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#114 0.049 U ug/kg 0.044/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#118 0.569 ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#123 0.0461 U ug/kg 0.044/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#126 0.0619 U ug/kg 0.064/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#128 0.202 J ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#138 7.75 J ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#146 2.61 ug/kg 0.04

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 62 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#149 0.697 ug/kg 0.06

4/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#151 0.0518 U ug/kg 0.054/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#153 11.0 ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#156 0.141 U ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#157 0.156 U ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#158 0.477 J ug/kg 0.054/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#167 1.12 ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#169 2.45 U ug/kg 24/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#170 2.48 ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#174 0.0778 U ug/kg 0.074/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#177 0.954 ug/kg 0.044/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#180 4.65 ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#183 1.13 ug/kg 0.024/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#189 0.12 U ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#187 11.4 ug/kg 0.064/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#194 1.99 ug/kg 0.074/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#195 0.394 ug/kg 0.084/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#201 3.76 ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#206 3.78 ug/kg 0.14/30/2002 AR-505-506 601286 4704041 4 0208032-14 BZ#209 2.36 ug/kg 0.084/30/2002 AR-505-506 601286 4704041 4 0208032-14 Monochlorobiphenyls 0.0403 U ug/kg 0.044/30/2002 AR-505-506 601286 4704041 4 0208032-14 Dichlorobiphenyls 0.0706 U ug/kg 0.074/30/2002 AR-505-506 601286 4704041 4 0208032-14 Trichlorobiphenyls 0.0922 U ug/kg 0.094/30/2002 AR-505-506 601286 4704041 4 0208032-14 Tetrachlorobiphenyls 1.43 ug/kg 0.044/30/2002 AR-505-506 601286 4704041 4 0208032-14 Pentachlorobiphenyls 7.47 ug/kg 0.064/30/2002 AR-505-506 601286 4704041 4 0208032-14 Hexachlorobiphenyls 23.7 ug/kg 0.074/30/2002 AR-505-506 601286 4704041 4 0208032-14 Heptachlorobiphenyls 18.5 ug/kg 0.034/30/2002 AR-505-506 601286 4704041 4 0208032-14 Octachlorobiphenyls 7.35 ug/kg 0.02

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 63 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-505-506 601286 4704041 4 0208032-14 Nonachlorobiphenyls 7.25 ug/kg 0.1

4/30/2002 AR-505-506 601286 4704041 4 0208032-14 Decachlorobiphenyl 2.36 ug/kg 0.084/30/2002 AR-505-506 601286 4704041 4 0208032-14 Total Homologs 68.1 ug/kg 0.074/30/2002 AR-505-506 601286 4704041 4 0208032-14 Percent Lipids 4.9 J % 04/30/2002 AR-505-506 601286 4704041 4 0208032-14 Percent Moisture 76 % 5/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#8 0.0850 U ug/kg 0.085/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#18 0.128 U ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#28 0.0312 U ug/kg 0.035/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#31 0.059 U ug/kg 0.055/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#44 0.104 U ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#45 0.0694 U ug/kg 0.065/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#47 0.332 J ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#49 0.155 J ug/kg 0.085/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#52 0.387 ug/kg 0.055/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#56 0.0746 U ug/kg 0.075/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#66 0.0625 U ug/kg 0.065/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#70 0.0625 U ug/kg 0.065/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#74 0.199 J ug/kg 0.065/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#77 0.0486 U ug/kg 0.045/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#81 0.0642 U ug/kg 0.065/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#87 0.0746 U ug/kg 0.075/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#95 0.0659 U ug/kg 0.065/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#99 1.16 ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#101 1.03 ug/kg 0.055/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#105 0.0798 U ug/kg 0.075/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#110 0.0642 U ug/kg 0.065/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#114 0.059 U ug/kg 0.055/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#118 0.641 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 64 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#123 0.0555 U ug/kg 0.05

5/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#126 0.0746 U ug/kg 0.075/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#128 0.151 U ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#138 5.23 ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#146 1.45 ug/kg 0.055/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#149 0.862 ug/kg 0.085/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#151 0.155 J ug/kg 0.065/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#153 6.17 ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#156 0.170 U ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#157 0.187 U ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#158 0.332 ug/kg 0.065/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#167 0.619 J ug/kg 0.25/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#169 2.95 U ug/kg 25/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#170 1.75 ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#174 0.199 J ug/kg 0.095/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#177 0.652 ug/kg 0.055/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#180 2.8 ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#183 0.663 ug/kg 0.035/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#189 0.144 U ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#187 6.69 ug/kg 0.085/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#194 1.07 ug/kg 0.095/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#195 0.232 J ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#201 2.06 ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#206 1.66 ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 BZ#209 0.995 ug/kg 0.095/7/2002 AR-508-510 600245 4704752 4 0208032-15 Monochlorobiphenyls 0.0486 U ug/kg 0.045/7/2002 AR-508-510 600245 4704752 4 0208032-15 Dichlorobiphenyls 0.0850 U ug/kg 0.085/7/2002 AR-508-510 600245 4704752 4 0208032-15 Trichlorobiphenyls 0.111 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 65 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-508-510 600245 4704752 4 0208032-15 Tetrachlorobiphenyls 1.65 ug/kg 0.05

5/7/2002 AR-508-510 600245 4704752 4 0208032-15 Pentachlorobiphenyls 5.41 ug/kg 0.075/7/2002 AR-508-510 600245 4704752 4 0208032-15 Hexachlorobiphenyls 14.1 ug/kg 0.095/7/2002 AR-508-510 600245 4704752 4 0208032-15 Heptachlorobiphenyls 11.1 ug/kg 0.045/7/2002 AR-508-510 600245 4704752 4 0208032-15 Octachlorobiphenyls 4.52 ug/kg 0.035/7/2002 AR-508-510 600245 4704752 4 0208032-15 Nonachlorobiphenyls 3.69 ug/kg 0.15/7/2002 AR-508-510 600245 4704752 4 0208032-15 Decachlorobiphenyl 1.01 ug/kg 0.095/7/2002 AR-508-510 600245 4704752 4 0208032-15 Total Homologs 41.5 ug/kg 0.085/7/2002 AR-508-510 600245 4704752 4 0208032-15 Percent Lipids 4.5 % 05/7/2002 AR-508-510 600245 4704752 4 0208032-15 Percent Moisture 79 % 5/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#8 0.0849 U ug/kg 0.085/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#18 0.128 U ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#28 0.0312 UJ ug/kg 0.035/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#31 0.0589 U ug/kg 0.055/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#44 0.104 U ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#45 0.0693 U ug/kg 0.065/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#47 0.243 J ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#49 0.199 J ug/kg 0.085/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#52 0.397 J ug/kg 0.055/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#56 0.0745 U ug/kg 0.075/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#66 0.0624 U ug/kg 0.065/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#70 0.0624 U ug/kg 0.065/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#74 0.210 J ug/kg 0.065/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#77 0.0485 U ug/kg 0.045/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#81 0.0641 U ug/kg 0.065/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#87 0.0745 U ug/kg 0.075/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#95 0.0659 U ug/kg 0.065/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#99 1.81 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 66 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#101 1.35 J ug/kg 0.05

5/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#105 0.0797 U ug/kg 0.075/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#110 0.177 J ug/kg 0.065/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#114 0.0589 U ug/kg 0.055/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#118 1.18 J ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#123 0.0555 U ug/kg 0.055/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#126 1.44 NJ ug/kg 0.075/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#128 0.276 J ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#138 8.41 J ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#146 2.85 J ug/kg 0.055/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#149 1.26 J ug/kg 0.085/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#151 0.0624 U ug/kg 0.065/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#153 12.8 J ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#156 0.508 J ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#157 0.187 U ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#158 0.629 J ug/kg 0.065/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#167 0.806 J ug/kg 0.25/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#169 2.95 U ug/kg 25/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#170 4.13 J ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#174 0.0936 U ug/kg 0.095/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#177 1.38 J ug/kg 0.055/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#180 6.86 J ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#183 1.7 J ug/kg 0.035/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#189 0.144 U ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#187 19.1 J ug/kg 0.085/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#194 2.75 J ug/kg 0.095/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#195 0.629 ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#201 5.26 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 67 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#206 4.92 J ug/kg 0.1

5/7/2002 AR-509-511 600193 4704684 4 0208033-01 BZ#209 4.06 J ug/kg 0.095/7/2002 AR-509-511 600193 4704684 4 0208033-01 Monochlorobiphenyls 0.0485 U ug/kg 0.045/7/2002 AR-509-511 600193 4704684 4 0208033-01 Dichlorobiphenyls 0.0849 U ug/kg 0.085/7/2002 AR-509-511 600193 4704684 4 0208033-01 Trichlorobiphenyls 0.111 U ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 Tetrachlorobiphenyls 2.35 J ug/kg 0.055/7/2002 AR-509-511 600193 4704684 4 0208033-01 Pentachlorobiphenyls 16.0 J ug/kg 0.075/7/2002 AR-509-511 600193 4704684 4 0208033-01 Hexachlorobiphenyls 29.1 J ug/kg 0.095/7/2002 AR-509-511 600193 4704684 4 0208033-01 Heptachlorobiphenyls 32.7 J ug/kg 0.045/7/2002 AR-509-511 600193 4704684 4 0208033-01 Octachlorobiphenyls 11.1 J ug/kg 0.035/7/2002 AR-509-511 600193 4704684 4 0208033-01 Nonachlorobiphenyls 10.4 J ug/kg 0.15/7/2002 AR-509-511 600193 4704684 4 0208033-01 Decachlorobiphenyl 4.06 J ug/kg 0.095/7/2002 AR-509-511 600193 4704684 4 0208033-01 Total Homologs 106 J ug/kg 0.085/7/2002 AR-509-511 600193 4704684 4 0208033-01 Percent Lipids 6.8 J % 05/7/2002 AR-509-511 600193 4704684 4 0208033-01 Percent Moisture 89 J % 5/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#8 0.0734 U ug/kg 0.075/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#18 0.111 U ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#28 0.0270 UJ ug/kg 0.025/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#31 0.0509 U ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#44 0.0899 U ug/kg 0.085/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#45 0.0599 U ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#47 4.51 ug/kg 0.095/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#49 2.62 ug/kg 0.075/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#52 5.40 ug/kg 0.045/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#56 0.0644 U ug/kg 0.065/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#66 0.515 ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#70 0.248 ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#74 3.31 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 68 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#77 0.0419 U ug/kg 0.04

5/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#81 0.0554 U ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#87 2.76 ug/kg 0.065/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#95 1.31 ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#99 8.43 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#101 7.32 ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#105 1.07 ug/kg 0.065/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#110 1.11 ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#114 0.0509 U ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#118 7.31 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#123 0.0479 U ug/kg 0.045/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#126 0.0644 U ug/kg 0.065/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#128 0.716 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#138 21.6 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#146 5.23 ug/kg 0.045/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#149 3.49 ug/kg 0.075/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#151 0.84 ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#153 29.5 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#156 0.147 U ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#157 0.162 U ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#158 1.65 ug/kg 0.055/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#167 2.42 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#169 2.55 U ug/kg 25/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#170 5.5 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#174 0.515 ug/kg 0.085/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#177 1.55 ug/kg 0.045/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#180 7.07 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#183 1.71 ug/kg 0.02

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 69 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#189 0.124 U ug/kg 0.1

5/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#187 12.5 ug/kg 0.075/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#194 2.00 ug/kg 0.075/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#195 0.487 ug/kg 0.095/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#201 3.11 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#206 1.99 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 BZ#209 1.05 ug/kg 0.085/7/2002 AR-510-512 607386 4749333 3 0208033-02 Monochlorobiphenyls 0.0419 U ug/kg 0.045/7/2002 AR-510-512 607386 4749333 3 0208033-02 Dichlorobiphenyls 0.0734 U ug/kg 0.075/7/2002 AR-510-512 607386 4749333 3 0208033-02 Trichlorobiphenyls 0.0959 U ug/kg 0.095/7/2002 AR-510-512 607386 4749333 3 0208033-02 Tetrachlorobiphenyls 23.7 ug/kg 0.045/7/2002 AR-510-512 607386 4749333 3 0208033-02 Pentachlorobiphenyls 50.9 ug/kg 0.065/7/2002 AR-510-512 607386 4749333 3 0208033-02 Hexachlorobiphenyls 85.4 ug/kg 0.075/7/2002 AR-510-512 607386 4749333 3 0208033-02 Heptachlorobiphenyls 28.3 ug/kg 0.035/7/2002 AR-510-512 607386 4749333 3 0208033-02 Octachlorobiphenyls 7.91 ug/kg 0.025/7/2002 AR-510-512 607386 4749333 3 0208033-02 Nonachlorobiphenyls 3.58 ug/kg 0.15/7/2002 AR-510-512 607386 4749333 3 0208033-02 Decachlorobiphenyl 1.05 ug/kg 0.085/7/2002 AR-510-512 607386 4749333 3 0208033-02 Total Homologs 201 ug/kg 0.075/7/2002 AR-510-512 607386 4749333 3 0208033-02 Percent Lipids 5.2 % 05/7/2002 AR-510-512 607386 4749333 3 0208033-02 Percent Moisture 83 % 4/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#8 0.0866 U ug/kg 0.084/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#18 0.131 U ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#28 0.0318 UJ ug/kg 0.034/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#31 0.0601 U ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#44 0.106 U ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#45 0.0707 U ug/kg 0.074/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#47 0.338 J ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#49 0.236 J ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 70 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#52 0.810 ug/kg 0.05

4/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#56 0.0760 U ug/kg 0.074/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#66 0.0636 U ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#70 0.0636 U ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#74 0.248 ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#77 0.0495 U ug/kg 0.044/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#81 0.0654 U ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#87 0.540 ug/kg 0.074/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#95 0.968 ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#99 1.9 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#101 3.33 ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#105 0.0813 U ug/kg 0.084/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#110 0.349 ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#114 0.0601 U ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#118 1.71 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#123 0.0565 U ug/kg 0.054/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#126 0.0760 U ug/kg 0.074/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#128 0.382 J ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#138 10.1 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#146 3.48 ug/kg 0.054/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#149 6.26 ug/kg 0.084/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#151 1.37 ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#153 14.0 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#156 0.529 J ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#157 0.191 U ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#158 0.788 ug/kg 0.064/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#167 0.889 ug/kg 0.24/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#169 3.00 U ug/kg 3

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 71 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#170 4.61 ug/kg 0.1

4/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#174 1.26 ug/kg 0.094/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#177 2.26 ug/kg 0.054/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#180 7.94 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#183 2.28 ug/kg 0.034/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#189 0.147 U ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#187 23.1 ug/kg 0.084/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#194 2.57 ug/kg 0.094/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#195 0.641 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#201 5.10 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#206 4.26 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 BZ#209 4.60 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 Monochlorobiphenyls 0.0495 U ug/kg 0.044/29/2002 AR-600-600 601229 4717045 4 0208033-03 Dichlorobiphenyls 0.0866 U ug/kg 0.084/29/2002 AR-600-600 601229 4717045 4 0208033-03 Trichlorobiphenyls 0.113 U ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 Tetrachlorobiphenyls 2.51 ug/kg 0.054/29/2002 AR-600-600 601229 4717045 4 0208033-03 Pentachlorobiphenyls 17.6 ug/kg 0.074/29/2002 AR-600-600 601229 4717045 4 0208033-03 Hexachlorobiphenyls 40.5 ug/kg 0.094/29/2002 AR-600-600 601229 4717045 4 0208033-03 Heptachlorobiphenyls 38.8 ug/kg 0.044/29/2002 AR-600-600 601229 4717045 4 0208033-03 Octachlorobiphenyls 9.82 ug/kg 0.034/29/2002 AR-600-600 601229 4717045 4 0208033-03 Nonachlorobiphenyls 9.35 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 Decachlorobiphenyl 4.60 ug/kg 0.14/29/2002 AR-600-600 601229 4717045 4 0208033-03 Total Homologs 103 ug/kg 0.084/29/2002 AR-600-600 601229 4717045 4 0208033-03 Percent Lipids 6.1 % 04/29/2002 AR-600-600 601229 4717045 4 0208033-03 Percent Moisture 81 % 4/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#8 0.0762 U ug/kg 0.074/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#18 0.115 U ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#28 0.0280 UJ ug/kg 0.02

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 72 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#31 0.0529 U ug/kg 0.05

4/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#44 0.0933 U ug/kg 0.094/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#45 0.0622 U ug/kg 0.064/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#47 0.673 ug/kg 0.094/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#49 0.644 ug/kg 0.074/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#52 1.37 ug/kg 0.044/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#56 0.0668 U ug/kg 0.064/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#66 0.139 J ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#70 0.0560 U ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#74 0.713 ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#77 0.0435 U ug/kg 0.044/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#81 0.0575 U ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#87 0.713 ug/kg 0.064/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#95 0.624 ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#99 2.36 ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#101 2.49 ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#105 0.366 ug/kg 0.074/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#110 0.0575 U ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#114 0.0529 U ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#118 1.75 ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#123 0.0497 U ug/kg 0.044/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#126 0.0668 U ug/kg 0.064/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#128 0.135 U ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#138 6.85 ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#146 2.11 ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#149 1.42 ug/kg 0.074/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#151 0.396 ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#153 8.85 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 73 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#156 0.152 U ug/kg 0.1

4/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#157 0.168 U ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#158 0.614 ug/kg 0.054/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#167 0.871 ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#169 2.64 U ug/kg 24/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#170 2.21 ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#174 0.084 U ug/kg 0.084/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#177 0.941 ug/kg 0.044/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#180 3.06 ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#183 0.842 ug/kg 0.024/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#189 0.129 U ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#187 8.79 ug/kg 0.074/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#194 0.0824 U ug/kg 0.084/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#195 0.0948 U ug/kg 0.094/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#201 1.55 ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#206 1.04 ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 BZ#209 0.792 ug/kg 0.084/30/2002 AR-601-601 612153 4759531 2 0208033-04 Monochlorobiphenyls 0.0435 U ug/kg 0.044/30/2002 AR-601-601 612153 4759531 2 0208033-04 Dichlorobiphenyls 0.0762 U ug/kg 0.074/30/2002 AR-601-601 612153 4759531 2 0208033-04 Trichlorobiphenyls 0.0995 U ug/kg 0.094/30/2002 AR-601-601 612153 4759531 2 0208033-04 Tetrachlorobiphenyls 4.60 ug/kg 0.044/30/2002 AR-601-601 612153 4759531 2 0208033-04 Pentachlorobiphenyls 16.1 ug/kg 0.064/30/2002 AR-601-601 612153 4759531 2 0208033-04 Hexachlorobiphenyls 25.6 ug/kg 0.084/30/2002 AR-601-601 612153 4759531 2 0208033-04 Heptachlorobiphenyls 16.9 ug/kg 0.034/30/2002 AR-601-601 612153 4759531 2 0208033-04 Octachlorobiphenyls 3.52 ug/kg 0.024/30/2002 AR-601-601 612153 4759531 2 0208033-04 Nonachlorobiphenyls 2.12 ug/kg 0.14/30/2002 AR-601-601 612153 4759531 2 0208033-04 Decachlorobiphenyl 0.792 ug/kg 0.084/30/2002 AR-601-601 612153 4759531 2 0208033-04 Total Homologs 69.7 ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 74 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-601-601 612153 4759531 2 0208033-04 Percent Lipids 6.9 % 0

4/30/2002 AR-601-601 612153 4759531 2 0208033-04 Percent Moisture 82 % 4/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#8 0.0830 U ug/kg 0.084/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#18 0.125 U ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#28 0.0305 UJ ug/kg 0.034/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#31 0.0576 U ug/kg 0.054/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#44 0.102 U ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#45 0.0677 U ug/kg 0.064/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#47 0.226 J ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#49 0.162 J ug/kg 0.084/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#52 0.615 ug/kg 0.054/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#56 0.0728 U ug/kg 0.074/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#66 0.0609 U ug/kg 0.064/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#70 0.0609 U ug/kg 0.064/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#74 0.194 J ug/kg 0.064/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#77 0.0474 U ug/kg 0.044/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#81 0.0626 U ug/kg 0.064/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#87 0.291 ug/kg 0.074/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#95 0.226 ug/kg 0.064/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#99 1.08 ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#101 1.37 ug/kg 0.054/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#105 0.0779 U ug/kg 0.074/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#110 0.0626 U ug/kg 0.064/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#114 0.0576 U ug/kg 0.054/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#118 0.841 ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#123 0.0542 U ug/kg 0.054/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#126 0.0728 U ug/kg 0.074/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#128 0.162 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 75 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#138 3.02 ug/kg 0.1

4/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#146 0.906 ug/kg 0.054/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#149 1.11 ug/kg 0.084/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#151 0.28 ug/kg 0.064/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#153 3.82 ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#156 0.226 J ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#157 0.183 U ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#158 0.226 ug/kg 0.064/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#167 0.345 J ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#169 2.88 U ug/kg 24/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#170 1.08 ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#174 0.205 J ug/kg 0.094/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#177 0.442 ug/kg 0.054/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#180 1.67 ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#183 0.42 ug/kg 0.034/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#189 0.140 U ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#187 4.44 ug/kg 0.074/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#194 0.539 ug/kg 0.084/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#195 0.103 U ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#201 1.46 ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#206 1.04 ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 BZ#209 1.16 ug/kg 0.094/30/2002 AR-603-603 608791 4742804 3 0208033-05 Monochlorobiphenyls 0.0474 U ug/kg 0.044/30/2002 AR-603-603 608791 4742804 3 0208033-05 Dichlorobiphenyls 0.0830 U ug/kg 0.084/30/2002 AR-603-603 608791 4742804 3 0208033-05 Trichlorobiphenyls 0.108 U ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 Tetrachlorobiphenyls 1.87 ug/kg 0.044/30/2002 AR-603-603 608791 4742804 3 0208033-05 Pentachlorobiphenyls 7.52 ug/kg 0.074/30/2002 AR-603-603 608791 4742804 3 0208033-05 Hexachlorobiphenyls 12.0 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 76 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-603-603 608791 4742804 3 0208033-05 Heptachlorobiphenyls 8.76 ug/kg 0.04

4/30/2002 AR-603-603 608791 4742804 3 0208033-05 Octachlorobiphenyls 3.87 ug/kg 0.034/30/2002 AR-603-603 608791 4742804 3 0208033-05 Nonachlorobiphenyls 2.62 ug/kg 0.14/30/2002 AR-603-603 608791 4742804 3 0208033-05 Decachlorobiphenyl 1.16 ug/kg 0.094/30/2002 AR-603-603 608791 4742804 3 0208033-05 Total Homologs 22.2 ug/kg 0.084/30/2002 AR-603-603 608791 4742804 3 0208033-05 Percent Lipids 4.6 % 04/30/2002 AR-603-603 608791 4742804 3 0208033-05 Percent Moisture 83 % 4/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#8 0.101 U ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#18 0.152 U ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#28 0.0370 UJ ug/kg 0.034/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#31 0.0698 U ug/kg 0.064/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#44 0.123 U ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#45 0.0821 U ug/kg 0.084/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#47 2.58 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#49 1.06 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#52 3.37 ug/kg 0.064/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#56 0.0883 U ug/kg 0.084/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#66 0.0739 U ug/kg 0.074/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#70 0.0739 U ug/kg 0.074/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#74 1.86 ug/kg 0.074/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#77 0.0575 U ug/kg 0.054/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#81 0.0760 U ug/kg 0.074/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#87 0.0883 U ug/kg 0.084/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#95 0.432 ug/kg 0.074/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#99 3.66 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#101 4.07 ug/kg 0.064/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#105 0.693 ug/kg 0.094/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#110 0.0760 U ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 77 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#114 0.0698 U ug/kg 0.06

4/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#118 4.33 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#123 0.0657 U ug/kg 0.064/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#126 0.0883 U ug/kg 0.084/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#128 0.549 J ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#138 9.08 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#146 2.88 ug/kg 0.064/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#149 1.78 ug/kg 0.094/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#151 0.366 ug/kg 0.074/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#153 11.2 ug/kg 0.24/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#156 0.201 U ug/kg 0.24/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#157 0.222 U ug/kg 0.24/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#158 0.811 ug/kg 0.074/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#167 1.14 ug/kg 0.24/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#169 3.49 U ug/kg 34/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#170 2.13 ug/kg 0.24/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#174 0.209 J ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#177 0.628 ug/kg 0.064/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#180 3.18 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#183 0.785 ug/kg 0.034/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#189 1.94 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#187 9.32 ug/kg 0.094/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#194 0.109 U ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#195 0.125 U ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#201 5.77 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#206 1.14 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 BZ#209 0.51 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 Monochlorobiphenyls 0.0575 U ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 78 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/30/2002 AR-604-604 610753 4754598 2 0208033-06 Dichlorobiphenyls 0.101 U ug/kg 0.1

4/30/2002 AR-604-604 610753 4754598 2 0208033-06 Trichlorobiphenyls 0.131 U ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 Tetrachlorobiphenyls 11.9 ug/kg 0.054/30/2002 AR-604-604 610753 4754598 2 0208033-06 Pentachlorobiphenyls 32.4 ug/kg 0.084/30/2002 AR-604-604 610753 4754598 2 0208033-06 Hexachlorobiphenyls 35 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 Heptachlorobiphenyls 16.8 ug/kg 0.054/30/2002 AR-604-604 610753 4754598 2 0208033-06 Octachlorobiphenyls 8.96 ug/kg 0.034/30/2002 AR-604-604 610753 4754598 2 0208033-06 Nonachlorobiphenyls 1.91 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 Decachlorobiphenyl 0.523 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 Total Homologs 89.5 ug/kg 0.14/30/2002 AR-604-604 610753 4754598 2 0208033-06 Percent Lipids 6.9 % 04/30/2002 AR-604-604 610753 4754598 2 0208033-06 Percent Moisture 82 % 5/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#8 0.0960 U ug/kg 0.095/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#18 0.145 U ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#28 7.59 J ug/kg 0.035/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#31 8.14 ug/kg 0.065/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#44 0.118 U ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#45 0.0784 U ug/kg 0.075/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#47 69.5 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#49 88.8 ug/kg 0.095/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#52 143 ug/kg 0.055/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#56 2.2 ug/kg 0.085/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#66 21.9 ug/kg 0.075/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#70 13.1 ug/kg 0.075/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#74 52.9 ug/kg 0.075/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#77 1.06 NJ ug/kg 0.055/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#81 0.686 NJ ug/kg 0.075/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#87 32.9 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 79 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#95 41.9 ug/kg 0.07

5/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#99 66.5 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#101 97.0 ug/kg 0.065/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#105 10.5 ug/kg 0.095/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#110 27.5 ug/kg 0.075/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#114 1.75 ug/kg 0.065/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#118 60.3 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#123 0.0627 U ug/kg 0.065/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#126 0.0842 U ug/kg 0.085/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#128 1.8 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#138 85.4 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#146 24.9 ug/kg 0.065/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#149 77 ug/kg 0.095/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#151 16.6 ug/kg 0.075/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#153 66.7 ug/kg 0.25/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#156 3.29 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#157 1.07 ug/kg 0.25/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#158 4.85 ug/kg 0.075/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#167 8.45 ug/kg 0.25/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#169 3.33 U ug/kg 35/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#170 11.3 ug/kg 0.25/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#174 4.14 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#177 6.38 ug/kg 0.055/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#180 15.6 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#183 4.59 ug/kg 0.035/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#189 0.163 U ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#187 90.1 ug/kg 0.095/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#194 5.67 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 80 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#195 1.41 ug/kg 0.1

5/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#201 18.6 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#206 7.45 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 BZ#209 2.57 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 Monochlorobiphenyls 0.0549 U ug/kg 0.055/7/2002 AR-605-605 607499 4749655 3 0208033-07 Dichlorobiphenyls 0.0960 U ug/kg 0.095/7/2002 AR-605-605 607499 4749655 3 0208033-07 Trichlorobiphenyls 14.3 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 Tetrachlorobiphenyls 517 ug/kg 0.055/7/2002 AR-605-605 607499 4749655 3 0208033-07 Pentachlorobiphenyls 571 ug/kg 0.085/7/2002 AR-605-605 607499 4749655 3 0208033-07 Hexachlorobiphenyls 320 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 Heptachlorobiphenyls 124 ug/kg 0.045/7/2002 AR-605-605 607499 4749655 3 0208033-07 Octachlorobiphenyls 28 ug/kg 0.035/7/2002 AR-605-605 607499 4749655 3 0208033-07 Nonachlorobiphenyls 14.4 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 Decachlorobiphenyl 2.57 ug/kg 0.15/7/2002 AR-605-605 607499 4749655 3 0208033-07 Total Homologs 1580 ug/kg 0.095/7/2002 AR-605-605 607499 4749655 3 0208033-07 Percent Lipids 4.9 % 05/7/2002 AR-605-605 607499 4749655 3 0208033-07 Percent Moisture 82 % 5/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#8 0.0841 U ug/kg 0.085/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#18 0.127 U ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#28 0.0309 UJ ug/kg 0.035/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#31 0.0583 U ug/kg 0.055/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#44 0.103 U ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#45 0.0686 U ug/kg 0.065/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#47 1.20 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#49 1.06 ug/kg 0.085/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#52 4.27 ug/kg 0.055/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#56 0.0738 U ug/kg 0.075/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#66 0.186 J ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 81 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#70 0.317 ug/kg 0.06

5/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#74 1.18 ug/kg 0.065/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#77 0.0480 U ug/kg 0.045/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#81 0.0635 U ug/kg 0.065/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#87 2.73 ug/kg 0.075/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#95 3.41 ug/kg 0.065/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#99 7.73 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#101 13.2 ug/kg 0.055/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#105 0.0789 U ug/kg 0.075/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#110 1.77 ug/kg 0.065/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#114 0.0583 U ug/kg 0.055/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#118 7.55 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#123 0.0549 U ug/kg 0.055/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#126 0.0738 U ug/kg 0.075/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#128 0.459 J ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#138 22.4 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#146 7.55 ug/kg 0.055/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#149 11.5 ug/kg 0.085/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#151 2.23 ug/kg 0.065/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#153 25.3 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#156 1.99 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#157 1.06 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#158 1.75 ug/kg 0.065/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#167 3.16 ug/kg 0.25/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#169 2.92 U ug/kg 25/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#170 5.81 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#174 1.05 ug/kg 0.095/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#177 3.05 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 82 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#180 8.57 ug/kg 0.1

5/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#183 2.66 ug/kg 0.035/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#189 0.142 U ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#187 30 ug/kg 0.085/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#194 3.2 ug/kg 0.095/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#195 0.71 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#201 5.10 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#206 2.93 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 BZ#209 3.13 ug/kg 0.095/8/2002 AR-609-611 607937 4737655 3 0208033-08 Monochlorobiphenyls 0.0480 U ug/kg 0.045/8/2002 AR-609-611 607937 4737655 3 0208033-08 Dichlorobiphenyls 0.0841 U ug/kg 0.085/8/2002 AR-609-611 607937 4737655 3 0208033-08 Trichlorobiphenyls 0.110 U ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 Tetrachlorobiphenyls 10.0 ug/kg 0.045/8/2002 AR-609-611 607937 4737655 3 0208033-08 Pentachlorobiphenyls 60.1 ug/kg 0.075/8/2002 AR-609-611 607937 4737655 3 0208033-08 Hexachlorobiphenyls 86.7 ug/kg 0.095/8/2002 AR-609-611 607937 4737655 3 0208033-08 Heptachlorobiphenyls 51.4 ug/kg 0.045/8/2002 AR-609-611 607937 4737655 3 0208033-08 Octachlorobiphenyls 10.2 ug/kg 0.035/8/2002 AR-609-611 607937 4737655 3 0208033-08 Nonachlorobiphenyls 6.27 ug/kg 0.15/8/2002 AR-609-611 607937 4737655 3 0208033-08 Decachlorobiphenyl 3.13 ug/kg 0.095/8/2002 AR-609-611 607937 4737655 3 0208033-08 Total Homologs 218 ug/kg 0.085/8/2002 AR-609-611 607937 4737655 3 0208033-08 Percent Lipids 5.9 % 05/8/2002 AR-609-611 607937 4737655 3 0208033-08 Percent Moisture 82 % 5/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#8 0.0910 U ug/kg 0.095/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#18 0.137 U ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#28 0.0334 UJ ug/kg 0.035/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#31 0.0631 U ug/kg 0.065/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#44 0.111 U ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#45 0.0743 U ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 83 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#47 1.43 ug/kg 0.1

5/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#49 0.591 ug/kg 0.095/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#52 2.28 ug/kg 0.055/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#56 0.0798 U ug/kg 0.075/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#66 0.248 ug/kg 0.065/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#70 0.319 ug/kg 0.065/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#74 1.34 ug/kg 0.075/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#77 0.0520 U ug/kg 0.055/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#81 0.0687 U ug/kg 0.065/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#87 1.19 ug/kg 0.075/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#95 0.308 ug/kg 0.075/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#99 4.13 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#101 3.00 ug/kg 0.065/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#105 0.0854 U ug/kg 0.085/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#110 0.0687 U ug/kg 0.065/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#114 0.0631 U ug/kg 0.065/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#118 1.49 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#123 0.0594 U ug/kg 0.055/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#126 0.0798 U ug/kg 0.075/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#128 0.162 U ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#138 9.83 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#146 3.28 ug/kg 0.065/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#149 1.73 ug/kg 0.085/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#151 0.402 ug/kg 0.065/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#153 10.5 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#156 0.532 J ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#157 0.200 U ug/kg 0.25/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#158 0.84 ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 84 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#167 0.946 ug/kg 0.2

5/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#169 3.16 U ug/kg 35/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#170 2.65 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#174 0.100 U ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#177 1.11 ug/kg 0.055/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#180 3.35 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#183 0.78 ug/kg 0.035/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#189 0.154 U ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#187 11.8 ug/kg 0.085/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#194 1.11 ug/kg 0.095/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#195 0.319 J ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#201 2.41 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#206 1.35 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 BZ#209 0.78 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 Monochlorobiphenyls 0.0520 U ug/kg 0.055/9/2002 AR-612-616 612144 4759477 2 0208033-09 Dichlorobiphenyls 0.0910 U ug/kg 0.095/9/2002 AR-612-616 612144 4759477 2 0208033-09 Trichlorobiphenyls 0.119 U ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 Tetrachlorobiphenyls 9.95 ug/kg 0.055/9/2002 AR-612-616 612144 4759477 2 0208033-09 Pentachlorobiphenyls 14.2 ug/kg 0.075/9/2002 AR-612-616 612144 4759477 2 0208033-09 Hexachlorobiphenyls 35.7 ug/kg 0.095/9/2002 AR-612-616 612144 4759477 2 0208033-09 Heptachlorobiphenyls 22.1 ug/kg 0.045/9/2002 AR-612-616 612144 4759477 2 0208033-09 Octachlorobiphenyls 4.93 ug/kg 0.035/9/2002 AR-612-616 612144 4759477 2 0208033-09 Nonachlorobiphenyls 2.54 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 Decachlorobiphenyl 0.78 ug/kg 0.15/9/2002 AR-612-616 612144 4759477 2 0208033-09 Total Homologs 90.1 ug/kg 0.095/9/2002 AR-612-616 612144 4759477 2 0208033-09 Percent Lipids 5.7 % 05/9/2002 AR-612-616 612144 4759477 2 0208033-09 Percent Moisture 81 % 5/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#8 0.0880 U ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 85 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#18 0.133 U ug/kg 0.1

5/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#28 3.11 J ug/kg 0.035/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#31 4.93 ug/kg 0.065/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#44 0.108 U ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#45 0.0718 U ug/kg 0.075/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#47 44.9 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#49 52.9 ug/kg 0.085/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#52 104 ug/kg 0.055/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#56 2.33 ug/kg 0.075/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#66 22.4 ug/kg 0.065/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#70 15.0 ug/kg 0.065/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#74 88.1 ug/kg 0.065/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#77 0.0503 U ug/kg 0.055/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#81 0.881 NJ ug/kg 0.065/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#87 48.8 ug/kg 0.075/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#95 23.3 ug/kg 0.065/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#99 106 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#101 130 ug/kg 0.065/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#105 18.5 ug/kg 0.085/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#110 22 ug/kg 0.065/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#114 5.58 ug/kg 0.065/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#118 113 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#123 0.0575 U ug/kg 0.055/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#126 0.0772 U ug/kg 0.075/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#128 4.06 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#138 136 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#146 39 ug/kg 0.055/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#149 52.5 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 86 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#151 14.4 ug/kg 0.06

5/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#153 111 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#156 8.45 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#157 2.00 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#158 8.67 ug/kg 0.065/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#167 13.3 ug/kg 0.25/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#169 3.05 U ug/kg 35/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#170 16.6 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#174 2.90 ug/kg 0.095/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#177 9.32 ug/kg 0.055/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#180 21.2 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#183 5.83 ug/kg 0.035/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#189 0.149 U ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#187 85.7 ug/kg 0.085/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#194 6.31 ug/kg 0.095/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#195 1.44 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#201 14.0 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#206 4.73 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 BZ#209 1.08 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 Monochlorobiphenyls 0.0503 U ug/kg 0.055/16/2002 AR-613-617 615221 4768778 2 0208033-10 Dichlorobiphenyls 0.0880 U ug/kg 0.085/16/2002 AR-613-617 615221 4768778 2 0208033-10 Trichlorobiphenyls 7.66 ug/kg 0.15/16/2002 AR-613-617 615221 4768778 2 0208033-10 Tetrachlorobiphenyls 456 ug/kg 0.055/16/2002 AR-613-617 615221 4768778 2 0208033-10 Pentachlorobiphenyls 811 ug/kg 0.075/16/2002 AR-613-617 615221 4768778 2 0208033-10 Hexachlorobiphenyls 431 ug/kg 0.095/16/2002 AR-613-617 615221 4768778 2 0208033-10 Heptachlorobiphenyls 134 ug/kg 0.045/16/2002 AR-613-617 615221 4768778 2 0208033-10 Octachlorobiphenyls 22.7 ug/kg 0.035/16/2002 AR-613-617 615221 4768778 2 0208033-10 Nonachlorobiphenyls 8.84 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 87 of 88
American Robin (Turdus migratorius) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/16/2002 AR-613-617 615221 4768778 2 0208033-10 Decachlorobiphenyl 1.08 ug/kg 0.1

5/16/2002 AR-613-617 615221 4768778 2 0208033-10 Total Homologs 1870 ug/kg 0.085/16/2002 AR-613-617 615221 4768778 2 0208033-10 Percent Lipids 8.0 % 05/16/2002 AR-613-617 615221 4768778 2 0208033-10 Percent Moisture 81 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 88 of 88
American Woodcock (Scolopax minor) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

4/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#8 0.0572 U ug/kg 0.057

4/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#18 0.0864 U ug/kg 0.0864/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#28 0.982 ug/kg 0.0214/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#31 1.76 ug/kg 0.0394/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#44 0.0701 U ug/kg 0.0704/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#45 0.0467 U ug/kg 0.0464/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#47 4.14 ug/kg 0.0724/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#49 1.96 ug/kg 0.0574/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#52 2.19 ug/kg 0.0354/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#56 1.21 ug/kg 0.0504/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#66 3.22 ug/kg 0.0424/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#70 0.848 ug/kg 0.0424/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#74 2.37 ug/kg 0.0444/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#77 0.0327 U ug/kg 0.0324/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#81 0.0432 U ug/kg 0.0434/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#87 1.13 ug/kg 0.0504/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#95 0.573 ug/kg 0.0444/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#99 2.77 ug/kg 0.0854/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#101 2.62 ug/kg 0.0394/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#105 2.11 ug/kg 0.0534/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#110 1.20 ug/kg 0.0434/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#114 0.164 ug/kg 0.0394/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#118 5.21 ug/kg 0.0814/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#123 0.0374 U ug/kg 0.0374/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#126 0.0502 U ug/kg 0.0504/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#128 0.618 ug/kg 0.104/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#138 7.75 ug/kg 0.0954/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#146 2.22 ug/kg 0.0384/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#149 1.79 ug/kg 0.056

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet we

1BZ# = PCB congener Ballschmiter & Zell number

 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 1 of 5
American Woodcock (Scolopax minor) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet we

4/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#151 0.350 ug/kg 0.042

4/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#153 8.94 ug/kg 0.124/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#156 0.625 ug/kg 0.114/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#157 0.126 U ug/kg 0.124/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#158 0.439 ug/kg 0.0444/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#167 1.00 ug/kg 0.134/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#169 1.99 U ug/kg 1.94/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#170 1.38 ug/kg 0.124/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#174 0.283 ug/kg 0.0634/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#177 0.499 ug/kg 0.0354/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#180 3.45 ug/kg 0.104/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#183 0.804 ug/kg 0.0224/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#189 0.0969 U ug/kg 0.0964/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#187 9.02 ug/kg 0.0544/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#194 1.96 ug/kg 0.0614/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#195 0.0713 U ug/kg 0.0714/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#201 2.32 ug/kg 0.104/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#206 0.536 ug/kg 0.0814/16/2002 AW-001-001 612718 4758659 2 0210059-02 BZ#209 0.283 ug/kg 0.0664/16/2002 AW-001-001 612718 4758659 2 0210059-02 Monochlorobiphenyls 0.0327 U ug/kg 0.0324/16/2002 AW-001-001 612718 4758659 2 0210059-02 Dichlorobiphenyls 0.0572 U ug/kg 0.0574/16/2002 AW-001-001 612718 4758659 2 0210059-02 Trichlorobiphenyls 2.99 ug/kg 0.0744/16/2002 AW-001-001 612718 4758659 2 0210059-02 Tetrachlorobiphenyls 24.9 ug/kg 0.0334/16/2002 AW-001-001 612718 4758659 2 0210059-02 Pentachlorobiphenyls 26.4 ug/kg 0.0504/16/2002 AW-001-001 612718 4758659 2 0210059-02 Hexachlorobiphenyls 30.3 ug/kg 0.0614/16/2002 AW-001-001 612718 4758659 2 0210059-02 Heptachlorobiphenyls 14.3 ug/kg 0.0294/16/2002 AW-001-001 612718 4758659 2 0210059-02 Octachlorobiphenyls 5.17 ug/kg 0.0224/16/2002 AW-001-001 612718 4758659 2 0210059-02 Nonachlorobiphenyls 1.71 ug/kg 0.0814/16/2002 AW-001-001 612718 4758659 2 0210059-02 Decachlorobiphenyl 0.275 ug/kg 0.066

1BZ# = PCB congener Ballschmiter & Zell number

 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 2 of 5
American Woodcock (Scolopax minor) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet we

4/16/2002 AW-001-001 612718 4758659 2 0210059-02 Total Homologs 106 ug/kg 0.058

4/16/2002 AW-001-001 612718 4758659 2 0210059-02 Percent Lipids 11 % 0.04/16/2002 AW-001-001 612718 4758659 2 0210059-02 Percent Moisture 74.8 % 04/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#8 0.213 U ug/kg 0.214/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#18 0.322 U ug/kg 0.324/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#28 3.77 ug/kg 0.0784/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#31 1.69 ug/kg 0.144/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#44 0.261 U ug/kg 0.264/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#45 0.174 U ug/kg 0.174/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#47 1.61 ug/kg 0.274/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#49 2.19 ug/kg 0.214/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#52 3.82 ug/kg 0.134/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#56 0.187 U ug/kg 0.184/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#66 3.21 ug/kg 0.154/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#70 1.91 ug/kg 0.154/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#74 1.63 ug/kg 0.164/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#77 0.122 U ug/kg 0.124/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#81 0.161 U ug/kg 0.164/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#87 0.499 J ug/kg 0.184/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#95 1.27 ug/kg 0.164/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#99 2.44 ug/kg 0.314/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#101 1.86 ug/kg 0.144/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#105 1.91 ug/kg 0.204/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#110 1.41 ug/kg 0.164/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#114 0.148 U ug/kg 0.144/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#118 5.51 ug/kg 0.304/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#123 0.139 U ug/kg 0.134/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#126 0.187 U ug/kg 0.184/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#128 0.378 U ug/kg 0.37

1BZ# = PCB congener Ballschmiter & Zell number

 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 3 of 5
American Woodcock (Scolopax minor) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet we

4/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#138 6.87 ug/kg 0.35

4/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#146 1.38 ug/kg 0.144/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#149 1.33 ug/kg 0.204/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#151 0.305 J ug/kg 0.154/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#153 7.56 ug/kg 0.444/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#156 0.426 U ug/kg 0.424/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#157 0.470 U ug/kg 0.474/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#158 0.471 J ug/kg 0.164/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#167 0.554 J ug/kg 0.504/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#169 7.39 UJ ug/kg 7.34/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#170 1.36 J ug/kg 0.444/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#174 0.277 J ug/kg 0.234/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#177 0.388 J ug/kg 0.134/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#180 3.30 ug/kg 0.404/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#183 0.776 ug/kg 0.0824/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#189 0.361 U ug/kg 0.364/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#187 6.43 ug/kg 0.204/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#194 1.63 ug/kg 0.234/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#195 0.265 U ug/kg 0.264/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#201 2.33 ug/kg 0.394/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#206 1.58 ug/kg 0.304/16/2002 AW-100-100 614438 4790506 1 0210059-03 BZ#209 1.50 ug/kg 0.244/16/2002 AW-100-100 614438 4790506 1 0210059-03 Monochlorobiphenyls 0.122 U ug/kg 0.124/16/2002 AW-100-100 614438 4790506 1 0210059-03 Dichlorobiphenyls 0.213 U ug/kg 0.214/16/2002 AW-100-100 614438 4790506 1 0210059-03 Trichlorobiphenyls 4.85 ug/kg 0.274/16/2002 AW-100-100 614438 4790506 1 0210059-03 Tetrachlorobiphenyls 27.7 ug/kg 0.124/16/2002 AW-100-100 614438 4790506 1 0210059-03 Pentachlorobiphenyls 27.0 ug/kg 0.184/16/2002 AW-100-100 614438 4790506 1 0210059-03 Hexachlorobiphenyls 26.7 ug/kg 0.234/16/2002 AW-100-100 614438 4790506 1 0210059-03 Heptachlorobiphenyls 14.2 ug/kg 0.10

1BZ# = PCB congener Ballschmiter & Zell number

 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 4 of 5
American Woodcock (Scolopax minor) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

L

(wet we

4/16/2002 AW-100-100 614438 4790506 1 0210059-03 Octachlorobiphenyls 4.76 ug/kg 0.082

4/16/2002 AW-100-100 614438 4790506 1 0210059-03 Nonachlorobiphenyls 2.60 ug/kg 0.304/16/2002 AW-100-100 614438 4790506 1 0210059-03 Decachlorobiphenyl 1.50 ug/kg 0.244/16/2002 AW-100-100 614438 4790506 1 0210059-03 Total Homologs 109 ug/kg 0.214/16/2002 AW-100-100 614438 4790506 1 0210059-03 Percent Lipids 6.6 % 0.04/16/2002 AW-100-100 614438 4790506 1 0210059-03 Percent Moisture 70.1 % 0

1BZ# = PCB congener Ballschmiter & Zell number

 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 5 of 5
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

4/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl2-BZ#8 0.127 U ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl3-BZ#18 0.192 U ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl3-BZ#28 42.7 ug/kg 0.044/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl3-BZ#31 14.8 J ug/kg 0.084/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#44 0.156 U ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#45 0.104 U ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#47 68.8 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#49 8.80 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#52 6.82 ug/kg 0.074/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#56 20.5 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#66 79.6 ug/kg 0.094/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#70 9.45 ug/kg 0.094/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#74 80.9 ug/kg 0.094/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#77 0.0727 U ug/kg 0.074/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl4-BZ#81 0.0961 U ug/kg 0.094/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl5-BZ#87 24.7 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl5-BZ#95 4.55 ug/kg 0.094/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl5-BZ#99 66.6 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl5-BZ#101 13.4 ug/kg 0.084/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl5-BZ#105 55.6 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl5-BZ#110 2.66 ug/kg 0.094/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl5-BZ#114 7.84 ug/kg 0.084/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl5-BZ#118 175 J ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl5-BZ#123 0.0831 U ug/kg 0.084/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl5-BZ#126 0.112 U ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#128 16.6 ug/kg 0.24/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#138 130 ug/kg 0.24/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#146 22.5 ug/kg 0.084/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#149 8.40 ug/kg 0.1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 1 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#151 1.46 ug/kg 0.094/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#153 181 ug/kg 0.24/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#156 28.5 ug/kg 0.24/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#157 3.80 ug/kg 0.24/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#158 5.64 ug/kg 0.094/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#167 13.0 ug/kg 0.34/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl6-BZ#169 4.42 U ug/kg 44/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl7-BZ#170 34.2 ug/kg 0.24/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl7-BZ#174 1.65 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl7-BZ#177 4.25 ug/kg 0.074/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl7-BZ#180 65.1 ug/kg 0.24/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl7-BZ#183 9.89 ug/kg 0.044/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl7-BZ#189 0.216 U ug/kg 0.24/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl7-BZ#187 28.4 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl8-BZ#194 16.8 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl8-BZ#195 3.39 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl8-BZ#201 12.9 ug/kg 0.24/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl9-BZ#206 5.97 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Cl10-BZ#209 0.695 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Monochlorobiphenyls 0.0727 U ug/kg 0.074/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Dichlorobiphenyls 0.127 U ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Trichlorobiphenyls 51.6 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Tetrachlorobiphenyls 300 ug/kg 0.074/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Pentachlorobiphenyls 519 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Hexachlorobiphenyls 399 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Heptachlorobiphenyls 96.3 ug/kg 0.064/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Octachlorobiphenyls 34.4 ug/kg 0.044/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Nonachlorobiphenyls 11.7 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Decachlorobiphenyl 0.695 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 2 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Total Homologs 1410 ug/kg 0.14/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Percent Lipids 15 % 04/24/2002 EP-003 COMP 003_004 615291 4783861 1 0209038-06 Percent Moisture 75 % 4/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl2-BZ#8 0.0823 U ug/kg 0.084/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl3-BZ#18 0.124 U ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl3-BZ#28 23.9 ug/kg 0.034/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl3-BZ#31 2.97 J ug/kg 0.054/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#44 0.257 J ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#45 0.0672 U ug/kg 0.064/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#47 14.3 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#49 1.39 ug/kg 0.084/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#52 1.11 ug/kg 0.054/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#56 6.38 ug/kg 0.074/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#66 35.8 ug/kg 0.064/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#70 3.46 ug/kg 0.064/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#74 35.1 ug/kg 0.064/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#77 0.0470 U ug/kg 0.044/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl4-BZ#81 0.0622 U ug/kg 0.064/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl5-BZ#87 11.8 ug/kg 0.074/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl5-BZ#95 4.27 ug/kg 0.064/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl5-BZ#99 44.0 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl5-BZ#101 5.40 ug/kg 0.054/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl5-BZ#105 39.1 ug/kg 0.074/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl5-BZ#110 0.0622 U ug/kg 0.064/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl5-BZ#114 3.79 ug/kg 0.054/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl5-BZ#118 147 J ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl5-BZ#123 0.0538 U ug/kg 0.054/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl5-BZ#126 0.0722 U ug/kg 0.074/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#128 6.14 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 3 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#138 107 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#146 15.3 ug/kg 0.054/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#149 11.4 ug/kg 0.084/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#151 1.54 ug/kg 0.064/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#153 118 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#156 12.6 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#157 3.60 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#158 6.38 ug/kg 0.064/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#167 12.6 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl6-BZ#169 2.86 U ug/kg 24/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl7-BZ#170 23.1 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl7-BZ#174 5.45 ug/kg 0.094/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl7-BZ#177 9.88 ug/kg 0.054/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl7-BZ#180 57.1 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl7-BZ#183 16.1 ug/kg 0.034/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl7-BZ#189 0.139 U ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl7-BZ#187 47.7 ug/kg 0.074/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl8-BZ#194 11.7 ug/kg 0.084/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl8-BZ#195 4.55 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl8-BZ#201 25.4 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl9-BZ#206 4.83 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Cl10-BZ#209 0.417 ug/kg 0.094/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Monochlorobiphenyls 0.0470 U ug/kg 0.044/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Dichlorobiphenyls 0.0823 U ug/kg 0.084/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Trichlorobiphenyls 23.3 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Tetrachlorobiphenyls 101 ug/kg 0.044/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Pentachlorobiphenyls 377 ug/kg 0.074/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Hexachlorobiphenyls 296 ug/kg 0.084/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Heptachlorobiphenyls 114 ug/kg 0.04

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 4 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Octachlorobiphenyls 57.6 ug/kg 0.034/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Nonachlorobiphenyls 14.1 ug/kg 0.14/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Decachlorobiphenyl 0.417 ug/kg 0.094/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Total Homologs 984 ug/kg 0.084/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Percent Lipids 6.84 % 04/24/2002 EP-004 COMP 005_006 612607 4758345 2 0209038-07 Percent Moisture 79 % 4/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl2-BZ#8 0.0755 U ug/kg 0.074/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl3-BZ#18 0.114 U ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl3-BZ#28 0.0277 U ug/kg 0.024/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl3-BZ#31 0.0524 UJ ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#44 0.0924 U ug/kg 0.094/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#45 0.0616 U ug/kg 0.064/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#47 6.04 ug/kg 0.094/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#49 0.569 ug/kg 0.074/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#52 0.579 ug/kg 0.044/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#56 1.71 ug/kg 0.064/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#66 9.55 ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#70 0.0555 U ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#74 13.7 ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#77 0.0431 U ug/kg 0.044/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl4-BZ#81 0.0570 U ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl5-BZ#87 3.05 ug/kg 0.064/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl5-BZ#95 0.520 ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl5-BZ#99 11.9 ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl5-BZ#101 2.27 ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl5-BZ#105 10.8 ug/kg 0.074/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl5-BZ#110 0.0570 U ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl5-BZ#114 0.0524 U ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl5-BZ#118 36.6 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 5 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl5-BZ#123 0.0493 U ug/kg 0.044/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl5-BZ#126 0.0662 U ug/kg 0.064/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#128 0.746 ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#138 21.4 ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#146 3.28 ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#149 1.74 ug/kg 0.074/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#151 0.216 ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#153 31.1 ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#156 0.151 U ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#157 0.166 U ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#158 1.46 ug/kg 0.054/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#167 1.83 ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl6-BZ#169 2.62 U ug/kg 24/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl7-BZ#170 3.82 ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl7-BZ#174 0.304 ug/kg 0.084/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl7-BZ#177 0.785 ug/kg 0.044/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl7-BZ#180 8.97 ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl7-BZ#183 1.92 ug/kg 0.024/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl7-BZ#189 0.128 U ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl7-BZ#187 7.82 ug/kg 0.074/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl8-BZ#194 1.79 ug/kg 0.084/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl8-BZ#195 0.422 ug/kg 0.094/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl8-BZ#201 2.25 ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl9-BZ#206 0.795 ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Cl10-BZ#209 0.294 ug/kg 0.084/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Monochlorobiphenyls 0.0431 U ug/kg 0.044/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Dichlorobiphenyls 0.0755 U ug/kg 0.074/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Trichlorobiphenyls 0.0986 U ug/kg 0.094/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Tetrachlorobiphenyls 38.3 ug/kg 0.04

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 6 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Pentachlorobiphenyls 130 ug/kg 0.064/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Hexachlorobiphenyls 64.9 ug/kg 0.084/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Heptachlorobiphenyls 17.9 ug/kg 0.034/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Octachlorobiphenyls 6.37 ug/kg 0.024/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Nonachlorobiphenyls 2.39 ug/kg 0.14/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Decachlorobiphenyl 0.294 ug/kg 0.084/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Total Homologs 260 ug/kg 0.074/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Percent Lipids 10 % 04/24/2002 EP-005 COMP 007_008 614792 4761994 2 0209038-08 Percent Moisture 79 % 4/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl2-BZ#8 0.0881 U ug/kg 0.084/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl3-BZ#18 0.133 U ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl3-BZ#28 136 ug/kg 0.034/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl3-BZ#31 31.8 J ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#44 0.950 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#45 0.0719 U ug/kg 0.074/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#47 55.8 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#49 7.81 ug/kg 0.084/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#52 4.66 ug/kg 0.054/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#56 39.0 ug/kg 0.074/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#66 133 ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#70 11.9 ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#74 114 ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#77 0.0503 U ug/kg 0.054/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl4-BZ#81 0.0665 U ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl5-BZ#87 0.0773 U ug/kg 0.074/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl5-BZ#95 4.07 ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl5-BZ#99 70.3 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl5-BZ#101 76.5 ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl5-BZ#105 53.0 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 7 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl5-BZ#110 0.0665 U ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl5-BZ#114 11.8 ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl5-BZ#118 210 J ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl5-BZ#123 0.0575 U ug/kg 0.054/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl5-BZ#126 0.0773 U ug/kg 0.074/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#128 8.64 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#138 112 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#146 18.9 ug/kg 0.054/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#149 4.38 ug/kg 0.084/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#151 0.538 ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#153 282 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#156 31.5 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#157 4.32 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#158 9.91 ug/kg 0.064/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#167 45.9 ug/kg 0.24/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl6-BZ#169 3.05 U ug/kg 34/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl7-BZ#170 30.4 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl7-BZ#174 0.675 ug/kg 0.094/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl7-BZ#177 2.55 ug/kg 0.054/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl7-BZ#180 56.8 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl7-BZ#183 9.37 ug/kg 0.034/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl7-BZ#189 0.149 U ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl7-BZ#187 25.6 ug/kg 0.084/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl8-BZ#194 7.12 ug/kg 0.094/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl8-BZ#195 1.45 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl8-BZ#201 10.6 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl9-BZ#206 2.51 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Cl10-BZ#209 0.492 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Monochlorobiphenyls 0.0503 U ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 8 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Dichlorobiphenyls 0.0881 U ug/kg 0.084/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Trichlorobiphenyls 149 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Tetrachlorobiphenyls 376 ug/kg 0.054/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Pentachlorobiphenyls 695 ug/kg 0.074/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Hexachlorobiphenyls 480 ug/kg 0.094/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Heptachlorobiphenyls 83.1 ug/kg 0.044/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Octachlorobiphenyls 21.0 ug/kg 0.034/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Nonachlorobiphenyls 5.86 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Decachlorobiphenyl 0.492 ug/kg 0.14/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Total Homologs 1810 ug/kg 0.084/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Percent Lipids 12 % 04/25/2002 EP-006 COMP 009_010 613517 4792342 1 0209038-09 Percent Moisture 78 % 5/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl2-BZ#8 0.137 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl3-BZ#18 0.207 U ug/kg 0.25/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl3-BZ#28 0.0503 U ug/kg 0.055/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl3-BZ#31 0.0951 UJ ug/kg 0.095/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#44 0.168 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#45 0.112 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#47 2.03 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#49 0.178 J ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#52 0.196 J ug/kg 0.085/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#56 0.730 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#66 3.55 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#70 0.101 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#74 4.77 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#77 0.0783 U ug/kg 0.075/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl4-BZ#81 0.103 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl5-BZ#87 0.120 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl5-BZ#95 0.106 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 9 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl5-BZ#99 8.39 ug/kg 0.25/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl5-BZ#101 0.730 ug/kg 0.095/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl5-BZ#105 5.36 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl5-BZ#110 0.103 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl5-BZ#114 0.748 ug/kg 0.095/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl5-BZ#118 22.4 J ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl5-BZ#123 0.0895 U ug/kg 0.085/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl5-BZ#126 0.120 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#128 5.42 ug/kg 0.25/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#138 36.3 ug/kg 0.25/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#146 9.39 ug/kg 0.095/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#149 0.570 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#151 0.101 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#153 78.2 ug/kg 0.25/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#156 6.61 ug/kg 0.25/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#157 1.05 ug/kg 0.35/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#158 1.76 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#167 3.24 ug/kg 0.35/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl6-BZ#169 4.75 U ug/kg 45/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl7-BZ#170 16.8 ug/kg 0.25/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl7-BZ#174 0.196 J ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl7-BZ#177 2.19 ug/kg 0.085/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl7-BZ#180 48.9 ug/kg 0.25/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl7-BZ#183 5.68 ug/kg 0.055/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl7-BZ#189 0.232 U ug/kg 0.25/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl7-BZ#187 25.2 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl8-BZ#194 11.0 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl8-BZ#195 1.46 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl8-BZ#201 11.6 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 10 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl9-BZ#206 7.75 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Cl10-BZ#209 1.92 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Monochlorobiphenyls 0.0783 U ug/kg 0.075/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Dichlorobiphenyls 0.137 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Trichlorobiphenyls 0.179 U ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Tetrachlorobiphenyls 16.5 ug/kg 0.085/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Pentachlorobiphenyls 148 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Hexachlorobiphenyls 144 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Heptachlorobiphenyls 68.1 ug/kg 0.065/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Octachlorobiphenyls 28.6 ug/kg 0.055/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Nonachlorobiphenyls 16.5 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Decachlorobiphenyl 1.92 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Total Homologs 424 ug/kg 0.15/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Percent Lipids 9.6 % 05/7/2002 EP-011 COMP 016_017 599308 4702162 4 0209038-10 Percent Moisture 78 % 5/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl2-BZ#8 0.0962 U ug/kg 0.095/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl3-BZ#18 0.145 U ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl3-BZ#28 0.0353 U ug/kg 0.035/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl3-BZ#31 0.0667 UJ ug/kg 0.065/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#44 0.118 U ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#45 0.0785 U ug/kg 0.075/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#47 2.18 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#49 0.300 J ug/kg 0.095/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#52 0.338 ug/kg 0.055/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#56 0.650 ug/kg 0.085/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#66 3.20 ug/kg 0.075/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#70 0.200 J ug/kg 0.075/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#74 3.26 ug/kg 0.075/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#77 0.0550 U ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 11 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl4-BZ#81 0.0726 U ug/kg 0.075/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl5-BZ#87 1.45 ug/kg 0.085/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl5-BZ#95 0.338 ug/kg 0.075/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl5-BZ#99 5.40 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl5-BZ#101 0.763 ug/kg 0.065/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl5-BZ#105 4.18 ug/kg 0.095/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl5-BZ#110 0.0726 U ug/kg 0.075/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl5-BZ#114 0.0667 U ug/kg 0.065/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl5-BZ#118 16.4 J ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl5-BZ#123 0.0628 U ug/kg 0.065/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl5-BZ#126 0.0844 U ug/kg 0.085/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#128 2.74 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#138 21.4 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#146 5.11 ug/kg 0.065/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#149 0.975 ug/kg 0.095/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#151 0.125 J ug/kg 0.075/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#153 45.9 ug/kg 0.25/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#156 3.95 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#157 0.400 J ug/kg 0.25/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#158 1.15 ug/kg 0.075/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#167 2.38 ug/kg 0.25/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl6-BZ#169 3.34 U ug/kg 35/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl7-BZ#170 8.64 ug/kg 0.25/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl7-BZ#174 0.350 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl7-BZ#177 1.36 ug/kg 0.055/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl7-BZ#180 20.2 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl7-BZ#183 3.44 ug/kg 0.035/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl7-BZ#189 0.163 U ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl7-BZ#187 14.1 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 12 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl8-BZ#194 3.68 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl8-BZ#195 0.738 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl8-BZ#201 5.64 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl9-BZ#206 2.26 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Cl10-BZ#209 0.463 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Monochlorobiphenyls 0.0550 U ug/kg 0.055/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Dichlorobiphenyls 0.0962 U ug/kg 0.095/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Trichlorobiphenyls 0.126 U ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Tetrachlorobiphenyls 14.9 ug/kg 0.055/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Pentachlorobiphenyls 111 ug/kg 0.085/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Hexachlorobiphenyls 84.5 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Heptachlorobiphenyls 34.6 ug/kg 0.045/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Octachlorobiphenyls 12.7 ug/kg 0.035/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Nonachlorobiphenyls 5.39 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Decachlorobiphenyl 0.463 ug/kg 0.15/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Total Homologs 263 ug/kg 0.095/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Percent Lipids 10 % 05/7/2002 EP-012 COMP 018_019 599308 4702162 4 0209038-11 Percent Moisture 78 % 5/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl2-BZ#8 0.0773 U ug/kg 0.075/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl3-BZ#18 0.117 U ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl3-BZ#28 0.0284 U ug/kg 0.025/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl3-BZ#31 0.0536 UJ ug/kg 0.055/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#44 0.0947 U ug/kg 0.095/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#45 0.0631 U ug/kg 0.065/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#47 0.613 ug/kg 0.095/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#49 0.0773 U ug/kg 0.075/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#52 0.0473 U ug/kg 0.045/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#56 0.211 J ug/kg 0.065/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#66 1.60 ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 13 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#70 0.0568 U ug/kg 0.055/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#74 2.60 ug/kg 0.065/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#77 0.0442 U ug/kg 0.045/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl4-BZ#81 0.0584 U ug/kg 0.055/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl5-BZ#87 0.0678 U ug/kg 0.065/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl5-BZ#95 0.100 J ug/kg 0.065/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl5-BZ#99 3.44 ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl5-BZ#101 0.342 ug/kg 0.055/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl5-BZ#105 2.93 ug/kg 0.075/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl5-BZ#110 0.0584 U ug/kg 0.055/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl5-BZ#114 0.0536 U ug/kg 0.055/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl5-BZ#118 11.0 J ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl5-BZ#123 0.0505 U ug/kg 0.055/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl5-BZ#126 0.0678 U ug/kg 0.065/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#128 2.09 ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#138 14.9 ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#146 4.05 ug/kg 0.055/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#149 0.322 ug/kg 0.075/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#151 0.191 ug/kg 0.055/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#153 32.8 ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#156 3.45 ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#157 0.512 J ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#158 0.714 ug/kg 0.065/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#167 1.34 ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl6-BZ#169 2.68 U ug/kg 25/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl7-BZ#170 7.25 ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl7-BZ#174 0.131 J ug/kg 0.085/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl7-BZ#177 0.935 ug/kg 0.045/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl7-BZ#180 20.2 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 14 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl7-BZ#183 2.58 ug/kg 0.035/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl7-BZ#189 0.131 U ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl7-BZ#187 10.1 ug/kg 0.075/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl8-BZ#194 4.86 ug/kg 0.085/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl8-BZ#195 0.764 ug/kg 0.095/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl8-BZ#201 4.33 ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl9-BZ#206 3.45 ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Cl10-BZ#209 0.844 ug/kg 0.085/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Monochlorobiphenyls 0.0442 U ug/kg 0.045/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Dichlorobiphenyls 0.0773 U ug/kg 0.075/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Trichlorobiphenyls 0.101 U ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Tetrachlorobiphenyls 7.66 ug/kg 0.045/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Pentachlorobiphenyls 74.4 ug/kg 0.065/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Hexachlorobiphenyls 61.9 ug/kg 0.085/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Heptachlorobiphenyls 28.3 ug/kg 0.035/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Octachlorobiphenyls 14.8 ug/kg 0.035/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Nonachlorobiphenyls 7.25 ug/kg 0.15/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Decachlorobiphenyl 0.844 ug/kg 0.085/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Total Homologs 195 ug/kg 0.075/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Percent Lipids 7.7 % 05/13/2002 EP-020 COMP 028_029 601867 4707944 4 0209038-12 Percent Moisture 79 % 5/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl2-BZ#8 0.126 U ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl3-BZ#18 0.190 U ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl3-BZ#28 0.0463 U ug/kg 0.045/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl3-BZ#31 0.0875 UJ ug/kg 0.085/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#44 0.154 U ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#45 0.103 U ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#47 5.10 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#49 0.344 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 15 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#52 6.57 ug/kg 0.075/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#56 0.951 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#66 4.87 ug/kg 0.095/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#70 0.0927 U ug/kg 0.095/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#74 5.90 ug/kg 0.095/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#77 0.0721 U ug/kg 0.075/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl4-BZ#81 0.0952 U ug/kg 0.095/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl5-BZ#87 0.111 U ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl5-BZ#95 0.0978 U ug/kg 0.095/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl5-BZ#99 8.12 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl5-BZ#101 0.967 ug/kg 0.085/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl5-BZ#105 5.66 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl5-BZ#110 0.0952 U ug/kg 0.095/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl5-BZ#114 0.0875 U ug/kg 0.085/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl5-BZ#118 21.2 J ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl5-BZ#123 0.0824 U ug/kg 0.085/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl5-BZ#126 0.111 U ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#128 2.43 ug/kg 0.25/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#138 27.9 ug/kg 0.25/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#146 5.08 ug/kg 0.085/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#149 0.607 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#151 0.0927 U ug/kg 0.095/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#153 41.6 ug/kg 0.25/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#156 4.03 ug/kg 0.25/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#157 0.607 J ug/kg 0.25/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#158 1.38 ug/kg 0.095/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#167 3.23 ug/kg 0.35/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl6-BZ#169 4.38 U ug/kg 45/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl7-BZ#170 9.41 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 16 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl7-BZ#174 0.148 J ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl7-BZ#177 1.51 ug/kg 0.075/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl7-BZ#180 21.3 ug/kg 0.25/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl7-BZ#183 3.23 ug/kg 0.045/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl7-BZ#189 0.214 U ug/kg 0.25/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl7-BZ#187 10.3 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl8-BZ#194 4.12 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl8-BZ#195 0.787 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl8-BZ#201 4.82 ug/kg 0.25/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl9-BZ#206 2.92 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Cl10-BZ#209 0.672 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Monochlorobiphenyls 0.0721 U ug/kg 0.075/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Dichlorobiphenyls 0.126 U ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Trichlorobiphenyls 0.165 U ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Tetrachlorobiphenyls 21.8 ug/kg 0.075/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Pentachlorobiphenyls 106 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Hexachlorobiphenyls 86.4 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Heptachlorobiphenyls 31.1 ug/kg 0.065/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Octachlorobiphenyls 13.3 ug/kg 0.045/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Nonachlorobiphenyls 6.48 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Decachlorobiphenyl 0.672 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Total Homologs 266 ug/kg 0.15/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Percent Lipids 7.5 % 05/17/2002 EP-025 COMP 036_037 601104 4700696 4 0209038-13 Percent Moisture 61 % 5/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl2-BZ#8 0.116 U ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl3-BZ#18 0.176 U ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl3-BZ#28 412 ug/kg 0.045/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl3-BZ#31 102 J ug/kg 0.085/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#44 0.143 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 17 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#45 0.0951 U ug/kg 0.095/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#47 276 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#49 14.4 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#52 5.65 ug/kg 0.075/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#56 131 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#66 537 ug/kg 0.085/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#70 0.0856 U ug/kg 0.085/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#74 488 ug/kg 0.095/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#77 0.0666 U ug/kg 0.065/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl4-BZ#81 0.0880 U ug/kg 0.085/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl5-BZ#87 75.2 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl5-BZ#95 8.65 ug/kg 0.095/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl5-BZ#99 223 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl5-BZ#101 33.4 ug/kg 0.085/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl5-BZ#105 193 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl5-BZ#110 0.0880 U ug/kg 0.085/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl5-BZ#114 27.4 ug/kg 0.085/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl5-BZ#118 477 J ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl5-BZ#123 0.0761 U ug/kg 0.075/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl5-BZ#126 0.102 U ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#128 28.1 ug/kg 0.25/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#138 334 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#146 61.1 ug/kg 0.075/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#149 18.0 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#151 1.67 ug/kg 0.085/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#153 361 ug/kg 0.25/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#156 49.1 ug/kg 0.25/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#157 7.18 ug/kg 0.25/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#158 17.6 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 18 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#167 32.4 ug/kg 0.25/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl6-BZ#169 4.04 U ug/kg 45/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl7-BZ#170 81.7 ug/kg 0.25/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl7-BZ#174 2.83 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl7-BZ#177 15.9 ug/kg 0.075/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl7-BZ#180 146 ug/kg 0.25/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl7-BZ#183 25.8 ug/kg 0.045/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl7-BZ#189 0.197 U ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl7-BZ#187 99.2 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl8-BZ#194 29.1 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl8-BZ#195 7.54 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl8-BZ#201 33.5 ug/kg 0.25/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl9-BZ#206 11.3 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Cl10-BZ#209 1.65 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Monochlorobiphenyls 0.0666 U ug/kg 0.065/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Dichlorobiphenyls 0.116 U ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Trichlorobiphenyls 430 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Tetrachlorobiphenyls 1520 ug/kg 0.065/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Pentachlorobiphenyls 1530 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Hexachlorobiphenyls 900 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Heptachlorobiphenyls 254 ug/kg 0.055/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Octachlorobiphenyls 79.0 ug/kg 0.045/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Nonachlorobiphenyls 26.0 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Decachlorobiphenyl 1.65 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Total Homologs 4740 ug/kg 0.15/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Percent Lipids 9.0 % 05/23/2002 EP-043 COMP 055_056 607453 4749152 3 0209038-14 Percent Moisture 73 % 5/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl2-BZ#8 0.109 U ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl3-BZ#18 0.164 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 19 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl3-BZ#28 69.3 ug/kg 0.045/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl3-BZ#31 11.5 J ug/kg 0.075/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#44 0.133 U ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#45 0.0889 U ug/kg 0.085/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#47 62.2 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#49 2.53 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#52 1.25 ug/kg 0.065/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#56 14.8 ug/kg 0.095/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#66 118 ug/kg 0.085/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#70 0.0800 U ug/kg 0.085/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#74 128 ug/kg 0.085/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#77 0.0622 U ug/kg 0.065/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl4-BZ#81 0.0822 U ug/kg 0.085/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl5-BZ#87 30.5 ug/kg 0.095/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl5-BZ#95 1.23 ug/kg 0.085/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl5-BZ#99 74.2 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl5-BZ#101 9.19 ug/kg 0.075/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl5-BZ#105 52.1 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl5-BZ#110 0.0822 U ug/kg 0.085/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl5-BZ#114 6.85 ug/kg 0.075/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl5-BZ#118 172 J ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl5-BZ#123 0.0711 U ug/kg 0.075/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl5-BZ#126 0.0956 U ug/kg 0.095/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#128 8.10 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#138 119 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#146 22.1 ug/kg 0.075/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#149 3.20 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#151 0.524 ug/kg 0.085/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#153 105 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 20 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#156 19.6 ug/kg 0.25/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#157 2.08 ug/kg 0.25/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#158 4.84 ug/kg 0.085/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#167 13.9 ug/kg 0.25/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl6-BZ#169 3.78 U ug/kg 35/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl7-BZ#170 13.4 ug/kg 0.25/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl7-BZ#174 0.538 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl7-BZ#177 3.37 ug/kg 0.065/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl7-BZ#180 29.2 ug/kg 0.25/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl7-BZ#183 4.90 ug/kg 0.045/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl7-BZ#189 0.184 U ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl7-BZ#187 25.8 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl8-BZ#194 5.36 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl8-BZ#195 1.00 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl8-BZ#201 7.77 ug/kg 0.25/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl9-BZ#206 2.21 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Cl10-BZ#209 0.594 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Monochlorobiphenyls 0.0622 U ug/kg 0.065/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Dichlorobiphenyls 0.109 U ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Trichlorobiphenyls 69.3 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Tetrachlorobiphenyls 359 ug/kg 0.065/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Pentachlorobiphenyls 499 ug/kg 0.095/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Hexachlorobiphenyls 287 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Heptachlorobiphenyls 56.0 ug/kg 0.055/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Octachlorobiphenyls 16.6 ug/kg 0.045/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Nonachlorobiphenyls 5.11 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Decachlorobiphenyl 0.594 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Total Homologs 1290 ug/kg 0.15/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Percent Lipids 9.0 % 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 21 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/29/2002 EP-044 COMP 057_058 614563 4768376 2 0209038-15 Percent Moisture 75 % 5/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl2-BZ#8 0.177 UJ ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl3-BZ#18 0.267 UJ ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl3-BZ#28 212 J ug/kg 0.065/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl3-BZ#31 50.8 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#44 0.216 U ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#45 0.144 U ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#47 196 J ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#49 10.5 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#52 6.04 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#56 95.2 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#66 297 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#70 34.2 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#74 228 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#77 0.101 U ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl4-BZ#81 0.134 U ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl5-BZ#87 121 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl5-BZ#95 11.9 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl5-BZ#99 192 J ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl5-BZ#101 50.0 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl5-BZ#105 112 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl5-BZ#110 0.134 U ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl5-BZ#114 19.3 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl5-BZ#118 520 J ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl5-BZ#123 0.115 U ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl5-BZ#126 0.155 U ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#128 8.64 J ug/kg 0.35/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#138 307 J ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#146 76.9 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 22 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#149 26.6 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#151 7.40 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#153 356 J ug/kg 0.35/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#156 38.0 J ug/kg 0.35/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#157 4.80 J ug/kg 0.35/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#158 15.7 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#167 52.2 J ug/kg 0.45/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl6-BZ#169 6.13 U ug/kg 65/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl7-BZ#170 61.3 J ug/kg 0.35/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl7-BZ#174 3.51 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl7-BZ#177 23.9 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl7-BZ#180 104 J ug/kg 0.35/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl7-BZ#183 28.3 J ug/kg 0.065/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl7-BZ#189 0.299 U ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl7-BZ#187 121 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl8-BZ#194 23.0 ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl8-BZ#195 6.29 J ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl8-BZ#201 85.7 J ug/kg 0.35/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl9-BZ#206 16.9 ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Cl10-BZ#209 2.94 ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Monochlorobiphenyls 0.101 U ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Dichlorobiphenyls 0.177 U ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Trichlorobiphenyls 209 J ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Tetrachlorobiphenyls 1190 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Pentachlorobiphenyls 1620 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Hexachlorobiphenyls 1060 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Heptachlorobiphenyls 294 J ug/kg 0.095/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Octachlorobiphenyls 66.4 J ug/kg 0.065/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Nonachlorobiphenyls 33.3 J ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 23 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Decachlorobiphenyl 2.92 ug/kg 0.25/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Total Homologs 4480 J ug/kg 0.15/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Percent Lipids 12 J % 05/31/2002 EP-047 COMP 063_064 611893 4757090 2 0209043-01 Percent Moisture 74 % 4/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl2-BZ#8 0.137 UJ ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl3-BZ#18 0.207 UJ ug/kg 0.24/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl3-BZ#28 27.5 ug/kg 0.054/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl3-BZ#31 5.05 J ug/kg 0.094/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#44 0.168 U ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#45 0.112 U ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#47 28.0 J ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#49 3.74 J ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#52 1.99 ug/kg 0.084/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#56 13.1 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#66 54.2 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#70 3.58 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#74 39.2 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#77 0.0782 U ug/kg 0.074/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl4-BZ#81 0.103 U ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl5-BZ#87 13.3 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl5-BZ#95 3.11 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl5-BZ#99 43.7 ug/kg 0.24/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl5-BZ#101 7.42 ug/kg 0.094/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl5-BZ#105 27.2 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl5-BZ#110 0.103 U ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl5-BZ#114 3.26 ug/kg 0.094/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl5-BZ#118 104 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl5-BZ#123 0.0894 U ug/kg 0.084/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl5-BZ#126 0.120 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 24 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#128 3.61 J ug/kg 0.24/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#138 56.6 ug/kg 0.24/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#146 11.7 ug/kg 0.094/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#149 6.35 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#151 0.605 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#153 82.1 ug/kg 0.24/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#156 7.54 ug/kg 0.24/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#157 1.28 ug/kg 0.34/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#158 6.07 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#167 10.8 J ug/kg 0.34/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl6-BZ#169 4.75 U ug/kg 44/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl7-BZ#170 14.0 ug/kg 0.24/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl7-BZ#174 0.925 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl7-BZ#177 2.70 ug/kg 0.084/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl7-BZ#180 26.4 ug/kg 0.24/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl7-BZ#183 4.13 ug/kg 0.054/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl7-BZ#189 0.232 U ug/kg 0.24/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl7-BZ#187 16.6 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl8-BZ#194 5.46 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl8-BZ#195 0.978 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl8-BZ#201 14.0 ug/kg 0.24/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl9-BZ#206 2.83 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Cl10-BZ#209 0.356 J ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Monochlorobiphenyls 0.0782 U ug/kg 0.074/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Dichlorobiphenyls 0.137 U ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Trichlorobiphenyls 25.5 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Tetrachlorobiphenyls 175 ug/kg 0.084/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Pentachlorobiphenyls 326 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Hexachlorobiphenyls 220 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 25 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Heptachlorobiphenyls 57.0 ug/kg 0.064/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Octachlorobiphenyls 22.0 ug/kg 0.054/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Nonachlorobiphenyls 5.30 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Decachlorobiphenyl 0.391 J ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Total Homologs 831 ug/kg 0.14/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Percent Lipids 7.7 % 04/27/2002 EP-104 COMP 104_105 607996 4746462 3 0209043-02 Percent Moisture 81 % 4/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl2-BZ#8 0.164 UJ ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl3-BZ#18 0.247 UJ ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl3-BZ#28 75.5 ug/kg 0.064/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl3-BZ#31 19.6 J ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#44 0.200 U ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#45 0.134 U ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#47 121 J ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#49 10.6 J ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#52 6.02 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#56 26.5 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#66 144 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#70 0.120 U ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#74 169 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#77 0.0935 U ug/kg 0.094/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl4-BZ#81 0.124 U ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl5-BZ#87 40.0 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl5-BZ#95 7.51 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl5-BZ#99 162 ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl5-BZ#101 22.0 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl5-BZ#105 76.9 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl5-BZ#110 0.124 U ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl5-BZ#114 10.4 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 26 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl5-BZ#118 432 ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl5-BZ#123 0.107 U ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl5-BZ#126 0.144 U ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#128 10.2 J ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#138 179 ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#146 26.0 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#149 12.9 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#151 1.38 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#153 270 ug/kg 0.34/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#156 23.8 ug/kg 0.34/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#157 4.55 ug/kg 0.34/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#158 142 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#167 35.2 J ug/kg 0.34/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl6-BZ#169 5.68 U ug/kg 54/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl7-BZ#170 37.1 ug/kg 0.34/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl7-BZ#174 2.02 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl7-BZ#177 5.79 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl7-BZ#180 63.2 ug/kg 0.34/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl7-BZ#183 11.1 ug/kg 0.064/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl7-BZ#189 0.277 U ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl7-BZ#187 57.5 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl8-BZ#194 13.5 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl8-BZ#195 3.17 ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl8-BZ#201 26.8 ug/kg 0.34/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl9-BZ#206 8.21 ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Cl10-BZ#209 1.43 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Monochlorobiphenyls 0.0935 U ug/kg 0.094/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Dichlorobiphenyls 0.164 U ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Trichlorobiphenyls 78.1 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 27 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Tetrachlorobiphenyls 610 ug/kg 0.094/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Pentachlorobiphenyls 1170 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Hexachlorobiphenyls 649 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Heptachlorobiphenyls 158 ug/kg 0.084/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Octachlorobiphenyls 53.2 ug/kg 0.064/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Nonachlorobiphenyls 14.1 ug/kg 0.24/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Decachlorobiphenyl 1.43 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Total Homologs 2730 ug/kg 0.14/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Percent Lipids 14 % 04/27/2002 EP-105 COMP 106_107 611403 4755012 2 0209043-03 Percent Moisture 69 % 5/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl2-BZ#8 0.113 UJ ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl3-BZ#18 0.170 UJ ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl3-BZ#28 75.6 ug/kg 0.045/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl3-BZ#31 21.0 J ug/kg 0.075/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#44 0.138 U ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#45 0.0921 U ug/kg 0.095/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#47 99.9 J ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#49 2.98 J ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#52 2.74 ug/kg 0.065/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#56 33.0 ug/kg 0.095/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#66 133 ug/kg 0.085/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#70 0.0829 U ug/kg 0.085/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#74 113 ug/kg 0.085/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#77 0.0645 U ug/kg 0.065/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl4-BZ#81 0.0852 U ug/kg 0.085/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl5-BZ#87 33.6 ug/kg 0.095/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl5-BZ#95 4.30 ug/kg 0.085/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl5-BZ#99 105 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl5-BZ#101 13.8 ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 28 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl5-BZ#105 59.1 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl5-BZ#110 0.0852 U ug/kg 0.085/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl5-BZ#114 7.74 ug/kg 0.075/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl5-BZ#118 276 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl5-BZ#123 0.0737 U ug/kg 0.075/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl5-BZ#126 0.0990 U ug/kg 0.095/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#128 11.7 J ug/kg 0.25/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#138 128 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#146 26.2 ug/kg 0.075/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#149 9.06 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#151 1.03 ug/kg 0.085/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#153 257 ug/kg 0.25/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#156 17.9 ug/kg 0.25/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#157 4.41 ug/kg 0.25/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#158 9.75 ug/kg 0.085/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#167 28.7 J ug/kg 0.25/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl6-BZ#169 3.91 U ug/kg 35/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl7-BZ#170 37.8 ug/kg 0.25/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl7-BZ#174 1.41 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl7-BZ#177 4.57 ug/kg 0.065/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl7-BZ#180 63.5 ug/kg 0.25/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl7-BZ#183 18.4 ug/kg 0.045/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl7-BZ#189 0.191 U ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl7-BZ#187 34.3 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl8-BZ#194 9.52 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl8-BZ#195 2.62 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl8-BZ#201 14.9 ug/kg 0.25/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl9-BZ#206 3.18 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Cl10-BZ#209 0.381 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 29 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Monochlorobiphenyls 0.0645 U ug/kg 0.065/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Dichlorobiphenyls 0.113 U ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Trichlorobiphenyls 81.6 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Tetrachlorobiphenyls 486 ug/kg 0.065/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Pentachlorobiphenyls 787 ug/kg 0.095/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Hexachlorobiphenyls 561 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Heptachlorobiphenyls 133 ug/kg 0.055/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Octachlorobiphenyls 35.3 ug/kg 0.045/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Nonachlorobiphenyls 5.53 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Decachlorobiphenyl 0.381 J ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Total Homologs 2090 ug/kg 0.15/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Percent Lipids 8.2 % 05/8/2002 EP-106 COMP 108_109 614240 4787396 1 0209043-04 Percent Moisture 79 % 4/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl2-BZ#8 0.0697 UJ ug/kg 0.064/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl3-BZ#18 0.105 UJ ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl3-BZ#28 55.4 ug/kg 0.024/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl3-BZ#31 11.9 J ug/kg 0.044/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#44 0.0854 U ug/kg 0.084/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#45 0.0569 U ug/kg 0.054/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#47 30.6 J ug/kg 0.084/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#49 1.63 J ug/kg 0.064/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#52 0.843 ug/kg 0.044/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#56 14.1 ug/kg 0.064/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#66 86.8 ug/kg 0.054/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#70 0.0512 U ug/kg 0.054/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#74 127 ug/kg 0.054/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#77 0.0398 U ug/kg 0.034/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl4-BZ#81 0.0526 U ug/kg 0.054/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl5-BZ#87 15.7 ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 30 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl5-BZ#95 1.14 ug/kg 0.054/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl5-BZ#99 99.7 ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl5-BZ#101 5.44 ug/kg 0.044/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl5-BZ#105 52.6 ug/kg 0.064/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl5-BZ#110 0.0526 U ug/kg 0.054/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl5-BZ#114 50.2 ug/kg 0.044/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl5-BZ#118 334 ug/kg 0.094/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl5-BZ#123 0.0455 U ug/kg 0.044/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl5-BZ#126 0.0612 U ug/kg 0.064/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#128 3.94 J ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#138 88.2 ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#146 11.8 ug/kg 0.044/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#149 3.63 ug/kg 0.064/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#151 0.263 ug/kg 0.054/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#153 177 ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#156 13.7 ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#157 3.04 ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#158 5.94 ug/kg 0.054/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#167 25.6 J ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl6-BZ#169 2.42 U ug/kg 24/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl7-BZ#170 15.4 ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl7-BZ#174 0.498 ug/kg 0.074/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl7-BZ#177 1.75 ug/kg 0.044/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl7-BZ#180 29.7 ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl7-BZ#183 6.77 ug/kg 0.024/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl7-BZ#189 0.118 U ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl7-BZ#187 27.8 ug/kg 0.064/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl8-BZ#194 4.32 ug/kg 0.074/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl8-BZ#195 0.988 ug/kg 0.08

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 31 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl8-BZ#201 6.65 ug/kg 0.14/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl9-BZ#206 1.97 ug/kg 0.094/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Cl10-BZ#209 0.317 ug/kg 0.084/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Monochlorobiphenyls 0.0398 U ug/kg 0.034/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Dichlorobiphenyls 0.0697 U ug/kg 0.064/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Trichlorobiphenyls 53.6 ug/kg 0.094/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Tetrachlorobiphenyls 317 ug/kg 0.044/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Pentachlorobiphenyls 767 ug/kg 0.064/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Hexachlorobiphenyls 375 ug/kg 0.074/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Heptachlorobiphenyls 69.8 ug/kg 0.034/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Octachlorobiphenyls 15.9 ug/kg 0.024/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Nonachlorobiphenyls 3.14 ug/kg 0.094/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Decachlorobiphenyl 0.362 ug/kg 0.084/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Total Homologs 1600 ug/kg 0.074/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Percent Lipids 8.7 % 04/25/2002 EP-201 COMP 201_202 615772 4767020 2 0209043-05 Percent Moisture 63 % 5/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl2-BZ#8 0.118 UJ ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl3-BZ#18 0.177 UJ ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl3-BZ#28 115 ug/kg 0.045/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl3-BZ#31 17.9 J ug/kg 0.085/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#44 0.144 U ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#45 0.0959 U ug/kg 0.095/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#47 133 J ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#49 15.1 J ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#52 11.6 ug/kg 0.075/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#56 37.7 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#66 171 ug/kg 0.085/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#70 0.0863 U ug/kg 0.085/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#74 187 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 32 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#77 0.0671 U ug/kg 0.065/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl4-BZ#81 0.0887 U ug/kg 0.085/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl5-BZ#87 63.0 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl5-BZ#95 10.6 ug/kg 0.095/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl5-BZ#99 169 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl5-BZ#101 26.7 ug/kg 0.085/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl5-BZ#105 88.1 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl5-BZ#110 0.0887 U ug/kg 0.085/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl5-BZ#114 17.7 ug/kg 0.085/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl5-BZ#118 505 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl5-BZ#123 0.0767 U ug/kg 0.075/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl5-BZ#126 0.103 U ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#128 13.7 J ug/kg 0.25/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#138 233 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#146 46.8 ug/kg 0.075/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#149 16.2 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#151 3.25 ug/kg 0.085/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#153 498 ug/kg 0.25/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#156 57.9 ug/kg 0.25/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#157 8.84 ug/kg 0.25/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#158 16.7 ug/kg 0.095/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#167 54.8 J ug/kg 0.25/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl6-BZ#169 4.08 U ug/kg 45/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl7-BZ#170 95.1 ug/kg 0.25/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl7-BZ#174 3.27 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl7-BZ#177 9.33 ug/kg 0.075/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl7-BZ#180 178 ug/kg 0.25/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl7-BZ#183 28.3 ug/kg 0.045/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl7-BZ#189 0.199 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 33 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl7-BZ#187 64.1 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl8-BZ#194 41.1 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl8-BZ#195 9.90 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl8-BZ#201 33.2 ug/kg 0.25/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl9-BZ#206 15.6 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Cl10-BZ#209 1.18 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Monochlorobiphenyls 0.0671 U ug/kg 0.065/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Dichlorobiphenyls 0.118 U ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Trichlorobiphenyls 104 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Tetrachlorobiphenyls 707 ug/kg 0.065/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Pentachlorobiphenyls 1320 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Hexachlorobiphenyls 1090 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Heptachlorobiphenyls 313 ug/kg 0.055/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Octachlorobiphenyls 112 ug/kg 0.045/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Nonachlorobiphenyls 23.9 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Decachlorobiphenyl 1.19 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Total Homologs 3670 ug/kg 0.15/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Percent Lipids 8.4 % 05/9/2002 EP-212 COMP 213_214 615322 4782846 1 0209043-06 Percent Moisture 73 % 6/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl2-BZ#8 0.106 UJ ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl3-BZ#18 0.160 UJ ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl3-BZ#28 202 ug/kg 0.036/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl3-BZ#31 39.8 J ug/kg 0.076/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#44 0.130 U ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#45 0.0864 U ug/kg 0.086/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#47 159 J ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#49 2.78 J ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#52 2.55 ug/kg 0.066/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#56 32.0 ug/kg 0.09

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 34 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

6/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#66 212 ug/kg 0.076/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#70 0.0778 U ug/kg 0.076/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#74 253 ug/kg 0.086/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#77 0.0605 U ug/kg 0.066/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl4-BZ#81 0.0799 U ug/kg 0.076/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl5-BZ#87 95.7 ug/kg 0.096/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl5-BZ#95 2.44 ug/kg 0.086/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl5-BZ#99 193 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl5-BZ#101 34.4 ug/kg 0.076/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl5-BZ#105 119 ug/kg 0.096/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl5-BZ#110 0.0799 U ug/kg 0.076/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl5-BZ#114 21.3 ug/kg 0.076/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl5-BZ#118 482 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl5-BZ#123 0.0691 U ug/kg 0.066/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl5-BZ#126 0.0929 U ug/kg 0.096/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#128 11.7 J ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#138 291 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#146 77.5 ug/kg 0.076/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#149 11.6 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#151 0.509 ug/kg 0.076/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#153 402 ug/kg 0.26/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#156 41.5 ug/kg 0.26/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#157 6.69 ug/kg 0.26/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#158 23.1 ug/kg 0.086/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#167 60.6 J ug/kg 0.26/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl6-BZ#169 3.67 U ug/kg 36/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl7-BZ#170 73.6 ug/kg 0.26/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl7-BZ#174 1.35 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl7-BZ#177 21.8 ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 35 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

6/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl7-BZ#180 124 ug/kg 0.26/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl7-BZ#183 34.7 ug/kg 0.046/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl7-BZ#189 0.179 U ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl7-BZ#187 105 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl8-BZ#194 26.3 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl8-BZ#195 6.67 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl8-BZ#201 35.1 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl9-BZ#206 0.151 U ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Cl10-BZ#209 2.08 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Monochlorobiphenyls 0.0605 U ug/kg 0.066/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Dichlorobiphenyls 0.106 U ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Trichlorobiphenyls 190 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Tetrachlorobiphenyls 822 ug/kg 0.066/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Pentachlorobiphenyls 1430 ug/kg 0.096/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Hexachlorobiphenyls 1090 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Heptachlorobiphenyls 306 ug/kg 0.056/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Octachlorobiphenyls 90.5 ug/kg 0.046/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Nonachlorobiphenyls 27.3 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Decachlorobiphenyl 2.11 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Total Homologs 3960 ug/kg 0.16/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Percent Lipids 8.1 % 06/11/2002 EP-232 COMP 236_237 609194 4743245 3 0209043-07 Percent Moisture 81 % 6/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl2-BZ#8 0.117 UJ ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl3-BZ#18 0.177 UJ ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl3-BZ#28 8.55 ug/kg 0.046/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl3-BZ#31 1.97 J ug/kg 0.086/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#44 0.144 U ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#45 0.0957 U ug/kg 0.096/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#47 5.06 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 36 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

6/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#49 0.229 J ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#52 0.152 J ug/kg 0.076/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#56 3.26 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#66 16.3 ug/kg 0.086/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#70 0.0862 U ug/kg 0.086/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#74 13.8 ug/kg 0.096/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#77 0.0670 U ug/kg 0.066/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl4-BZ#81 0.0886 U ug/kg 0.086/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl5-BZ#87 0.103 U ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl5-BZ#95 0.183 J ug/kg 0.096/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl5-BZ#99 17.7 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl5-BZ#101 1.27 ug/kg 0.086/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl5-BZ#105 12.6 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl5-BZ#110 0.0886 U ug/kg 0.086/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl5-BZ#114 1.94 ug/kg 0.086/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl5-BZ#118 51.1 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl5-BZ#123 0.0766 U ug/kg 0.076/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl5-BZ#126 0.103 U ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#128 1.27 J ug/kg 0.26/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#138 28.4 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#146 5.95 ug/kg 0.076/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#149 0.778 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#151 0.0862 U ug/kg 0.086/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#153 48.1 ug/kg 0.26/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#156 3.86 ug/kg 0.26/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#157 0.625 J ug/kg 0.26/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#158 3.28 ug/kg 0.096/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#167 6.43 J ug/kg 0.26/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl6-BZ#169 4.07 U ug/kg 4

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 37 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

6/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl7-BZ#170 9.15 ug/kg 0.26/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl7-BZ#174 0.381 J ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl7-BZ#177 1.20 ug/kg 0.076/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl7-BZ#180 14.2 ug/kg 0.26/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl7-BZ#183 3.64 ug/kg 0.046/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl7-BZ#189 0.199 U ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl7-BZ#187 11.2 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl8-BZ#194 3.00 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl8-BZ#195 0.762 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl8-BZ#201 11.9 ug/kg 0.26/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl9-BZ#206 1.57 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Cl10-BZ#209 0.351 J ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Monochlorobiphenyls 0.0670 U ug/kg 0.066/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Dichlorobiphenyls 0.117 U ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Trichlorobiphenyls 8.39 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Tetrachlorobiphenyls 62.4 ug/kg 0.066/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Pentachlorobiphenyls 179 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Hexachlorobiphenyls 115 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Heptachlorobiphenyls 34.2 ug/kg 0.056/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Octachlorobiphenyls 17.9 ug/kg 0.046/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Nonachlorobiphenyls 2.73 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Decachlorobiphenyl 0.351 J ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Total Homologs 421 ug/kg 0.16/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Percent Lipids 9.7 % 06/19/2002 EP-237 COMP 242_243 615438 4763988 2 0209043-08 Percent Moisture 80 % 4/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl2-BZ#8 0.0826 UJ ug/kg 0.084/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl3-BZ#18 0.125 UJ ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl3-BZ#28 0.945 ug/kg 0.034/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl3-BZ#31 0.268 J ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 38 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#44 0.101 U ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#45 0.0674 U ug/kg 0.064/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#47 1.40 J ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#49 0.0826 UJ ug/kg 0.084/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#52 0.0506 U ug/kg 0.054/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#56 0.0725 U ug/kg 0.074/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#66 1.85 ug/kg 0.064/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#70 0.0607 U ug/kg 0.064/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#74 1.13 ug/kg 0.064/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#77 0.0472 U ug/kg 0.044/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl4-BZ#81 0.0624 U ug/kg 0.064/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl5-BZ#87 0.0725 U ug/kg 0.074/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl5-BZ#95 0.193 J ug/kg 0.064/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl5-BZ#99 4.64 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl5-BZ#101 0.558 ug/kg 0.054/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl5-BZ#105 1.90 ug/kg 0.074/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl5-BZ#110 0.0624 U ug/kg 0.064/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl5-BZ#114 0.279 ug/kg 0.054/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl5-BZ#118 10.7 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl5-BZ#123 0.0540 U ug/kg 0.054/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl5-BZ#126 0.0725 U ug/kg 0.074/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#128 0.773 J ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#138 9.50 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#146 2.86 ug/kg 0.054/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#149 0.558 ug/kg 0.084/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#151 0.0607 U ug/kg 0.064/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#153 25.4 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#156 1.83 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#157 0.182 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 39 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

4/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#158 1.03 ug/kg 0.064/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#167 1.72 J ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl6-BZ#169 2.87 U ug/kg 24/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl7-BZ#170 7.00 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl7-BZ#174 0.333 ug/kg 0.094/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl7-BZ#177 0.698 ug/kg 0.054/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl7-BZ#180 13.4 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl7-BZ#183 1.88 ug/kg 0.034/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl7-BZ#189 0.140 U ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl7-BZ#187 6.70 ug/kg 0.074/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl8-BZ#194 2.73 ug/kg 0.084/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl8-BZ#195 0.494 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl8-BZ#201 9.05 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl9-BZ#206 1.57 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Cl10-BZ#209 0.462 ug/kg 0.094/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Monochlorobiphenyls 0.0472 U ug/kg 0.044/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Dichlorobiphenyls 0.0826 U ug/kg 0.084/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Trichlorobiphenyls 1.02 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Tetrachlorobiphenyls 8.66 ug/kg 0.044/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Pentachlorobiphenyls 45.0 ug/kg 0.074/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Hexachlorobiphenyls 52.1 ug/kg 0.084/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Heptachlorobiphenyls 25.2 ug/kg 0.044/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Octachlorobiphenyls 13.9 ug/kg 0.034/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Nonachlorobiphenyls 2.36 ug/kg 0.14/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Decachlorobiphenyl 0.451 ug/kg 0.094/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Total Homologs 149 ug/kg 0.084/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Percent Lipids 8.8 % 04/24/2002 EP-501 COMP 501_502 601085 4702111 4 0209043-09 Percent Moisture 75 % 5/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl2-BZ#8 0.443 UJ ug/kg 0.4

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 40 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl3-BZ#18 0.669 UJ ug/kg 0.65/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl3-BZ#28 598 ug/kg 0.15/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl3-BZ#31 212 J ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#44 8.00 ug/kg 0.55/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#45 0.362 U ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#47 335 J ug/kg 0.55/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#49 103 J ug/kg 0.45/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#52 47.6 ug/kg 0.25/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#56 231 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#66 945 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#70 115 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#74 660 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#77 0.253 U ug/kg 0.25/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl4-BZ#81 0.334 U ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl5-BZ#87 124 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl5-BZ#95 16.8 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl5-BZ#99 300 ug/kg 0.65/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl5-BZ#101 79.5 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl5-BZ#105 248 ug/kg 0.45/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl5-BZ#110 30.6 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl5-BZ#114 21.9 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl5-BZ#118 793 ug/kg 0.65/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl5-BZ#123 0.289 U ug/kg 0.25/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl5-BZ#126 0.389 U ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#128 18.9 J ug/kg 0.75/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#138 344 ug/kg 0.75/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#146 66.5 ug/kg 0.25/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#149 44.1 ug/kg 0.45/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#151 11.3 ug/kg 0.3

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 41 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#153 342 ug/kg 0.95/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#156 43.4 ug/kg 0.85/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#157 8.18 ug/kg 0.95/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#158 42.4 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#167 28.6 J ug/kg 15/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl6-BZ#169 15.4 U ug/kg 15/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl7-BZ#170 50.7 ug/kg 0.95/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl7-BZ#174 7.89 ug/kg 0.45/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl7-BZ#177 15.5 ug/kg 0.25/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl7-BZ#180 106 ug/kg 0.85/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl7-BZ#183 19.5 ug/kg 0.15/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl7-BZ#189 0.750 U ug/kg 0.75/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl7-BZ#187 116 ug/kg 0.45/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl8-BZ#194 26.4 ug/kg 0.45/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl8-BZ#195 4.49 ug/kg 0.55/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl8-BZ#201 34.1 ug/kg 0.85/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl9-BZ#206 12.3 ug/kg 0.65/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Cl10-BZ#209 1.84 ug/kg 0.55/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Monochlorobiphenyls 0.253 U ug/kg 0.25/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Dichlorobiphenyls 0.443 U ug/kg 0.45/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Trichlorobiphenyls 702 ug/kg 0.55/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Tetrachlorobiphenyls 2760 ug/kg 0.25/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Pentachlorobiphenyls 2530 ug/kg 0.35/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Hexachlorobiphenyls 1150 ug/kg 0.45/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Heptachlorobiphenyls 284 ug/kg 0.25/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Octachlorobiphenyls 81.0 ug/kg 0.15/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Nonachlorobiphenyls 22.2 ug/kg 0.65/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Decachlorobiphenyl 1.84 ug/kg 0.55/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Total Homologs 7530 ug/kg 0.4

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 42 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Percent Lipids 9.0 % 05/9/2002 EP-512 COMP 514_515 614349 4791082 1 0209043-10 Percent Moisture 77 % 5/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl2-BZ#8 0.117 UJ ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl3-BZ#18 0.176 UJ ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl3-BZ#28 27.9 ug/kg 0.045/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl3-BZ#31 4.09 J ug/kg 0.085/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#44 0.143 U ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#45 0.0952 U ug/kg 0.095/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#47 33.6 J ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#49 1.52 J ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#52 1.30 ug/kg 0.075/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#56 8.72 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#66 35.3 ug/kg 0.085/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#70 0.0857 U ug/kg 0.085/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#74 30.1 ug/kg 0.095/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#77 0.0667 U ug/kg 0.065/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl4-BZ#81 0.0881 U ug/kg 0.085/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl5-BZ#87 15.0 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl5-BZ#95 2.84 ug/kg 0.095/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl5-BZ#99 39.2 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl5-BZ#101 7.13 ug/kg 0.085/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl5-BZ#105 24.4 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl5-BZ#110 0.0881 U ug/kg 0.085/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl5-BZ#114 3.21 ug/kg 0.085/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl5-BZ#118 98.4 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl5-BZ#123 0.0762 U ug/kg 0.075/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl5-BZ#126 0.102 U ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#128 3.26 J ug/kg 0.25/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#138 61.3 ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 43 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#146 13.8 ug/kg 0.075/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#149 5.05 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#151 0.516 ug/kg 0.085/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#153 101 ug/kg 0.25/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#156 10.1 ug/kg 0.25/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#157 1.47 ug/kg 0.25/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#158 8.40 ug/kg 0.095/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#167 14.0 J ug/kg 0.25/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl6-BZ#169 4.05 U ug/kg 45/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl7-BZ#170 18.5 ug/kg 0.25/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl7-BZ#174 0.970 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl7-BZ#177 3.26 ug/kg 0.075/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl7-BZ#180 32.9 ug/kg 0.25/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl7-BZ#183 5.38 ug/kg 0.045/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl7-BZ#189 0.198 U ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl7-BZ#187 17.7 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl8-BZ#194 6.41 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl8-BZ#195 1.52 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl8-BZ#201 11.4 ug/kg 0.25/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl9-BZ#206 3.12 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Cl10-BZ#209 0.576 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Monochlorobiphenyls 0.0667 U ug/kg 0.065/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Dichlorobiphenyls 0.117 U ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Trichlorobiphenyls 24.3 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Tetrachlorobiphenyls 144 ug/kg 0.065/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Pentachlorobiphenyls 320 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Hexachlorobiphenyls 252 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Heptachlorobiphenyls 66.1 ug/kg 0.055/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Octachlorobiphenyls 25.9 ug/kg 0.04

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 44 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Nonachlorobiphenyls 5.47 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Decachlorobiphenyl 0.576 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Total Homologs 839 ug/kg 0.15/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Percent Lipids 10 % 05/7/2002 EP-608 COMP 609_610 608499 4745770 3 0209043-11 Percent Moisture 74 % 5/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl2-BZ#8 0.0706 UJ ug/kg 0.075/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl3-BZ#18 0.107 UJ ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl3-BZ#28 3.79 ug/kg 0.025/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl3-BZ#31 1.11 J ug/kg 0.045/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#44 0.0864 U ug/kg 0.085/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#45 0.0576 U ug/kg 0.055/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#47 3.31 J ug/kg 0.085/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#49 0.184 J ug/kg 0.075/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#52 0.266 ug/kg 0.045/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#56 1.48 ug/kg 0.065/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#66 6.79 ug/kg 0.055/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#70 0.0519 U ug/kg 0.055/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#74 6.66 ug/kg 0.055/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#77 0.0403 U ug/kg 0.045/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl4-BZ#81 0.0533 U ug/kg 0.055/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl5-BZ#87 3.17 ug/kg 0.065/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl5-BZ#95 0.0547 U ug/kg 0.055/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl5-BZ#99 12.2 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl5-BZ#101 0.844 ug/kg 0.045/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl5-BZ#105 8.05 ug/kg 0.065/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl5-BZ#110 0.0533 U ug/kg 0.055/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl5-BZ#114 1.20 ug/kg 0.045/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl5-BZ#118 39.2 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl5-BZ#123 0.0461 U ug/kg 0.04

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 45 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl5-BZ#126 0.0619 U ug/kg 0.065/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#128 1.26 J ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#138 27.1 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#146 5.85 ug/kg 0.045/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#149 0.945 ug/kg 0.065/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#151 0.119 J ug/kg 0.055/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#153 55.2 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#156 3.87 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#157 2.70 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#158 2.43 ug/kg 0.055/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#167 6.56 J ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl6-BZ#169 2.45 U ug/kg 25/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl7-BZ#170 9.61 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl7-BZ#174 0.0778 U ug/kg 0.075/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl7-BZ#177 1.30 ug/kg 0.045/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl7-BZ#180 21.2 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl7-BZ#183 5.49 ug/kg 0.025/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl7-BZ#189 0.120 U ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl7-BZ#187 12.8 ug/kg 0.065/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl8-BZ#194 3.68 ug/kg 0.075/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl8-BZ#195 0.716 ug/kg 0.085/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl8-BZ#201 7.13 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl9-BZ#206 2.24 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Cl10-BZ#209 0.973 ug/kg 0.085/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Monochlorobiphenyls 0.0403 U ug/kg 0.045/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Dichlorobiphenyls 0.0706 U ug/kg 0.075/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Trichlorobiphenyls 3.98 ug/kg 0.095/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Tetrachlorobiphenyls 30.7 ug/kg 0.045/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Pentachlorobiphenyls 134 ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 46 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Hexachlorobiphenyls 122 ug/kg 0.075/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Heptachlorobiphenyls 42.9 ug/kg 0.035/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Octachlorobiphenyls 16.0 ug/kg 0.025/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Nonachlorobiphenyls 4.31 ug/kg 0.15/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Decachlorobiphenyl 0.973 ug/kg 0.085/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Total Homologs 354 ug/kg 0.075/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Percent Lipids 9.9 % 05/8/2002 EP-610 COMP 612_613 608817 4742840 3 0209043-12 Percent Moisture 81 % 5/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl2-BZ#8 0.0670 UJ ug/kg 0.065/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl3-BZ#18 0.101 UJ ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl3-BZ#28 14.8 ug/kg 0.025/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl3-BZ#31 12.8 J ug/kg 0.045/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#44 0.0820 U ug/kg 0.085/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#45 0.0547 U ug/kg 0.055/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#47 15.7 J ug/kg 0.085/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#49 2.05 J ug/kg 0.065/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#52 1.30 ug/kg 0.045/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#56 7.34 ug/kg 0.055/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#66 33.1 ug/kg 0.045/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#70 0.0492 U ug/kg 0.045/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#74 26.9 ug/kg 0.055/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#77 0.0383 U ug/kg 0.035/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl4-BZ#81 0.0506 U ug/kg 0.055/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl5-BZ#87 9.54 ug/kg 0.055/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl5-BZ#95 0.784 ug/kg 0.055/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl5-BZ#99 25.0 ug/kg 0.095/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl5-BZ#101 4.01 ug/kg 0.045/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl5-BZ#105 21.6 ug/kg 0.065/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl5-BZ#110 0.0506 U ug/kg 0.05

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 47 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl5-BZ#114 2.03 ug/kg 0.045/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl5-BZ#118 77.2 ug/kg 0.095/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl5-BZ#123 0.0437 U ug/kg 0.045/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl5-BZ#126 0.0588 U ug/kg 0.055/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#128 1.54 J ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#138 43.0 ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#146 10.3 ug/kg 0.045/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#149 2.49 ug/kg 0.065/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#151 0.305 ug/kg 0.045/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#153 55.0 ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#156 7.13 ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#157 4.18 ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#158 4.21 ug/kg 0.055/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#167 8.68 J ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl6-BZ#169 2.32 U ug/kg 25/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl7-BZ#170 10.3 ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl7-BZ#174 2.37 ug/kg 0.075/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl7-BZ#177 0.679 ug/kg 0.045/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl7-BZ#180 19.6 ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl7-BZ#183 4.49 ug/kg 0.025/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl7-BZ#189 0.113 U ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl7-BZ#187 17.0 ug/kg 0.065/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl8-BZ#194 3.76 ug/kg 0.075/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl8-BZ#195 0.871 ug/kg 0.085/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl8-BZ#201 5.39 ug/kg 0.15/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl9-BZ#206 2.32 ug/kg 0.095/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Cl10-BZ#209 0.548 ug/kg 0.075/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Monochlorobiphenyls 0.0383 U ug/kg 0.035/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Dichlorobiphenyls 0.0670 U ug/kg 0.06

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 48 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Trichlorobiphenyls 14.7 ug/kg 0.085/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Tetrachlorobiphenyls 111 ug/kg 0.035/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Pentachlorobiphenyls 273 ug/kg 0.055/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Hexachlorobiphenyls 153 ug/kg 0.075/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Heptachlorobiphenyls 47.2 ug/kg 0.035/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Octachlorobiphenyls 15.7 ug/kg 0.025/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Nonachlorobiphenyls 4.70 ug/kg 0.095/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Decachlorobiphenyl 0.548 ug/kg 0.075/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Total Homologs 620 ug/kg 0.065/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Percent Lipids 8.9 % 05/8/2002 EP-611 COMP 614_615 615712 4772865 2 0209043-13 Percent Moisture 58 % 5/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl2-BZ#8 0.164 UJ ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl3-BZ#18 0.248 UJ ug/kg 0.25/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl3-BZ#28 44.2 ug/kg 0.065/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl3-BZ#31 8.49 J ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#44 0.201 U ug/kg 0.25/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#45 0.134 U ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#47 43.6 J ug/kg 0.25/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#49 2.03 J ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#52 1.37 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#56 12.3 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#66 66.8 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#70 0.121 U ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#74 64.2 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#77 0.0940 U ug/kg 0.095/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl4-BZ#81 0.124 U ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl5-BZ#87 26.0 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl5-BZ#95 2.01 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl5-BZ#99 82.7 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 49 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl5-BZ#101 9.58 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl5-BZ#105 48.5 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl5-BZ#110 0.124 U ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl5-BZ#114 6.67 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl5-BZ#118 226 ug/kg 0.25/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl5-BZ#123 0.107 U ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl5-BZ#126 0.144 U ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#128 10.2 J ug/kg 0.25/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#138 136 ug/kg 0.25/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#146 29.4 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#149 6.52 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#151 0.62 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#153 253 ug/kg 0.35/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#156 28.7 ug/kg 0.35/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#157 4.49 ug/kg 0.35/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#158 16.1 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#167 14.5 J ug/kg 0.35/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl6-BZ#169 5.71 U ug/kg 55/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl7-BZ#170 50.5 ug/kg 0.35/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl7-BZ#174 1.45 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl7-BZ#177 6.80 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl7-BZ#180 97.4 ug/kg 0.35/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl7-BZ#183 15.5 ug/kg 0.065/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl7-BZ#189 0.279 U ug/kg 0.25/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl7-BZ#187 43.0 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl8-BZ#194 22.3 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl8-BZ#195 4.36 ug/kg 0.25/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl8-BZ#201 24.5 ug/kg 0.35/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl9-BZ#206 24.5 ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 50 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Cl10-BZ#209 7.91 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Monochlorobiphenyls 0.0940 U ug/kg 0.095/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Dichlorobiphenyls 0.164 U ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Trichlorobiphenyls 41 ug/kg 0.25/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Tetrachlorobiphenyls 242 ug/kg 0.095/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Pentachlorobiphenyls 616 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Hexachlorobiphenyls 605 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Heptachlorobiphenyls 186 ug/kg 0.085/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Octachlorobiphenyls 66.7 ug/kg 0.065/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Nonachlorobiphenyls 35.5 ug/kg 0.25/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Decachlorobiphenyl 7.95 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Total Homologs 1800 ug/kg 0.15/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Percent Lipids 8.3 % 05/22/2002 EP-623 COMP 627_628 609001 4742737 3 0209043-14 Percent Moisture 71 % 5/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl2-BZ#8 1.15 UJ ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl3-BZ#18 1.74 UJ ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl3-BZ#28 1120 ug/kg 0.45/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl3-BZ#31 201 J ug/kg 0.75/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#44 1.41 U ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#45 0.939 U ug/kg 0.95/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#47 1830 J ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#49 84.3 J ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#52 22.3 ug/kg 0.75/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#56 427 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#66 1930 ug/kg 0.85/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#70 0.845 U ug/kg 0.85/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#74 1550 ug/kg 0.85/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#77 0.657 U ug/kg 0.65/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl4-BZ#81 0.869 U ug/kg 0.8

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 51 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl5-BZ#87 425 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl5-BZ#95 23.8 ug/kg 0.85/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl5-BZ#99 1130 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl5-BZ#101 215 ug/kg 0.75/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl5-BZ#105 624 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl5-BZ#110 0.869 U ug/kg 0.85/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl5-BZ#114 75.5 ug/kg 0.75/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl5-BZ#118 2240 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl5-BZ#123 0.751 U ug/kg 0.75/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl5-BZ#126 1.01 U ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#128 47.4 J ug/kg 25/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#138 1140 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#146 252 ug/kg 0.75/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#149 88.4 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#151 6.88 ug/kg 0.85/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#153 1120 ug/kg 25/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#156 121 ug/kg 25/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#157 23.5 ug/kg 25/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#158 103 ug/kg 0.85/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#167 109 J ug/kg 25/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl6-BZ#169 39.9 U ug/kg 35/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl7-BZ#170 147 ug/kg 25/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl7-BZ#174 14.1 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl7-BZ#177 47.7 ug/kg 0.75/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl7-BZ#180 269 ug/kg 25/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl7-BZ#183 62.6 ug/kg 0.45/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl7-BZ#189 8.52 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl7-BZ#187 252 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl8-BZ#194 49.6 ug/kg 1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 52 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

5/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl8-BZ#195 13.6 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl8-BZ#201 64.1 ug/kg 25/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl9-BZ#206 23.9 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Cl10-BZ#209 3.59 J ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Monochlorobiphenyls 0.657 U ug/kg 0.65/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Dichlorobiphenyls 1.15 U ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Trichlorobiphenyls 1040 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Tetrachlorobiphenyls 7250 ug/kg 0.65/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Pentachlorobiphenyls 7410 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Hexachlorobiphenyls 3700 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Heptachlorobiphenyls 708 ug/kg 0.55/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Octachlorobiphenyls 177 ug/kg 0.45/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Nonachlorobiphenyls 40.5 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Decachlorobiphenyl 3.59 J ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Total Homologs 20300 ug/kg 15/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Percent Lipids 4.3 % 05/30/2002 EP-632 COMP 645_646 615007 4785657 1 0209043-15 Percent Moisture 83 % 6/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl2-BZ#8 0.192 UJ ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl3-BZ#18 0.289 UJ ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl3-BZ#28 77.2 ug/kg 0.076/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl3-BZ#31 28.7 J ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#44 0.234 U ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#45 0.156 U ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#47 139 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#49 2.29 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#52 0.796 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#56 27.2 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#66 132 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#70 0.141 U ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 53 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

6/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#74 135 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#77 0.109 U ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl4-BZ#81 0.145 U ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl5-BZ#87 54.9 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl5-BZ#95 4.28 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl5-BZ#99 96.8 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl5-BZ#101 24.8 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl5-BZ#105 67.7 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl5-BZ#110 0.145 U ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl5-BZ#114 11.2 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl5-BZ#118 203 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl5-BZ#123 0.125 U ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl5-BZ#126 0.168 U ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#128 10.8 ug/kg 0.36/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#138 181 ug/kg 0.36/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#146 44.7 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#149 12.5 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#151 0.423 J ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#153 185 J ug/kg 0.46/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#156 21.0 J ug/kg 0.36/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#157 4.13 ug/kg 0.46/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#158 10.3 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#167 19.2 ug/kg 0.46/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl6-BZ#169 6.64 U ug/kg 66/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl7-BZ#170 35.4 ug/kg 0.46/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl7-BZ#174 0.211 U ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl7-BZ#177 12.1 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl7-BZ#180 46.7 ug/kg 0.36/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl7-BZ#183 12.4 ug/kg 0.07

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 54 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

6/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl7-BZ#189 0.324 U ug/kg 0.36/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl7-BZ#187 57.1 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl8-BZ#194 11.9 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl8-BZ#195 3.43 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl8-BZ#201 15.8 ug/kg 0.36/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl9-BZ#206 6.67 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Cl10-BZ#209 0.896 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Monochlorobiphenyls 0.109 U ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Dichlorobiphenyls 0.192 U ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Trichlorobiphenyls 95.2 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Tetrachlorobiphenyls 510 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Pentachlorobiphenyls 772 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Hexachlorobiphenyls 595 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Heptachlorobiphenyls 144 ug/kg 0.096/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Octachlorobiphenyls 38.6 ug/kg 0.076/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Nonachlorobiphenyls 12.2 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Decachlorobiphenyl 0.896 ug/kg 0.26/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Total Homologs 2170 ug/kg 0.16/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Percent Lipids 6.0 J % 06/4/2002 EP-635 COMP 651_652 613313 4759871 2 0209044-01 Percent Moisture 74 % 6/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl2-BZ#8 0.192 UJ ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl3-BZ#18 0.291 UJ ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl3-BZ#28 55.9 J ug/kg 0.076/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl3-BZ#31 18.1 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#44 0.236 U ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#45 0.157 U ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#47 75.7 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#49 1.25 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#52 1.23 J ug/kg 0.1

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 55 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

6/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#56 20.7 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#66 97.9 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#70 0.141 U ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#74 103 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#77 0.11 U ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl4-BZ#81 0.145 U ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl5-BZ#87 47.4 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl5-BZ#95 3.93 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl5-BZ#99 76.7 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl5-BZ#101 23.9 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl5-BZ#105 58.3 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl5-BZ#110 0.145 U ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl5-BZ#114 8.36 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl5-BZ#118 179 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl5-BZ#123 0.126 U ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl5-BZ#126 0.169 U ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#128 8.23 J ug/kg 0.36/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#138 147 J ug/kg 0.36/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#146 33.6 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#149 13.3 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#151 0.826 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#153 141 J ug/kg 0.46/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#156 18.8 J ug/kg 0.36/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#157 2.9 J ug/kg 0.46/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#158 9.58 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#167 17.1 J ug/kg 0.46/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl6-BZ#169 6.68 U ug/kg 66/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl7-BZ#170 24.6 J ug/kg 0.46/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl7-BZ#174 1.33 J ug/kg 0.2

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 56 of 57
Eastern Phoebe (Sayornis phoebe) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

DET

(wet w

6/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl7-BZ#177 8.91 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl7-BZ#180 33.4 J ug/kg 0.36/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl7-BZ#183 8.38 J ug/kg 0.076/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl7-BZ#189 0.326 U ug/kg 0.36/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl7-BZ#187 41.2 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl8-BZ#194 7.91 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl8-BZ#195 2.13 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl8-BZ#201 11.1 J ug/kg 0.36/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl9-BZ#206 4.73 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Cl10-BZ#209 0.650 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Monochlorobiphenyls 0.11 U ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Dichlorobiphenyls 0.192 U ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Trichlorobiphenyls 67.4 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Tetrachlorobiphenyls 351 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Pentachlorobiphenyls 678 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Hexachlorobiphenyls 475 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Heptachlorobiphenyls 102 J ug/kg 0.096/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Octachlorobiphenyls 28.4 J ug/kg 0.076/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Nonachlorobiphenyls 8.38 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Decachlorobiphenyl 0.650 J ug/kg 0.26/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Total Homologs 1710 J ug/kg 0.16/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Percent Lipids 7.4 % 06/4/2002 EP-639 COMP 658_659 612325 4758816 2 0209044-02 Percent Moisture 70 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 57 of 57
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#151 4.57 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#153 129 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#156 29.6 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#157 5.48 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#158 13.9 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#167 31.3 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#169 11.6 U ug/kg 15/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl7-BZ#170 51.5 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl7-BZ#174 3.70 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl7-BZ#177 13.8 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl7-BZ#180 80.1 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl7-BZ#183 17.0 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl7-BZ#189 0.567 U ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl7-BZ#187 68.4 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl8-BZ#194 20.6 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl8-BZ#195 6.05 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl8-BZ#201 27.2 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl9-BZ#206 15.3 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl10-BZ#209 3.40 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Monochlorobiphenyls 0.191 U ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Dichlorobiphenyls 14.8 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Trichlorobiphenyls 387 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Tetrachlorobiphenyls 981 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Pentachlorobiphenyls 906 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Hexachlorobiphenyls 698 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Heptachlorobiphenyls 205 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Octachlorobiphenyls 70.1 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Nonachlorobiphenyls 26.5 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Decachlorobiphenyl 3.40 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 2 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Total Homologs 3290 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Percent Lipids 8.8 % 05/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Percent Moisture 63 % 5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl2-BZ#8 0.212 UJ ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl3-BZ#18 0.467 J ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl3-BZ#28 141 ug/kg 0.05/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl3-BZ#31 286 J ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#44 1.24 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#45 0.173 U ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#47 413 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#49 360 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#52 131 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#56 48.3 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#66 164 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#70 99.8 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#74 175 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#77 24.7 NJ ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl4-BZ#81 0.160 U ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl5-BZ#87 107 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl5-BZ#95 16.6 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl5-BZ#99 137 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl5-BZ#101 140 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl5-BZ#105 103 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl5-BZ#110 65.4 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl5-BZ#114 12.3 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl5-BZ#118 272 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl5-BZ#123 0.138 U ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl5-BZ#126 0.186 U ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#128 17.3 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 3 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#138 321 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#146 84.0 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#149 33.3 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#151 7.72 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#153 189 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#156 28.2 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#157 5.64 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#158 17.8 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#167 39.8 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl6-BZ#169 7.34 U ug/kg 75/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl7-BZ#170 48.7 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl7-BZ#174 4.48 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl7-BZ#177 15.7 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl7-BZ#180 67.6 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl7-BZ#183 17.4 ug/kg 0.05/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl7-BZ#189 0.358 U ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl7-BZ#187 76.3 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl8-BZ#194 18.5 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl8-BZ#195 5.75 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl8-BZ#201 26.4 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl9-BZ#206 13.2 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Cl10-BZ#209 2.83 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Monochlorobiphenyls 0.121 U ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Dichlorobiphenyls 32.6 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Trichlorobiphenyls 888 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Tetrachlorobiphenyls 1870 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Pentachlorobiphenyls 1520 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Hexachlorobiphenyls 895 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Heptachlorobiphenyls 205 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 4 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Octachlorobiphenyls 61.2 ug/kg 0.05/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Nonachlorobiphenyls 21.9 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Decachlorobiphenyl 2.83 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Total Homologs 5490 ug/kg 0.5/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Percent Lipids 7.2 % 05/15/2002 NS-022 COMP 032_033 615290 4783914 1 0209044-04 Percent Moisture 73 % 5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl2-BZ#8 0.263 UJ ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl3-BZ#18 0.398 UJ ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl3-BZ#28 156 ug/kg 0.05/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl3-BZ#31 199 J ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#44 0.856 J ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#45 0.215 U ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#47 432 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#49 307 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#52 179 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#56 53.4 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#66 179 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#70 47.0 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#74 205 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#77 23.6 NJ ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl4-BZ#81 0.199 U ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl5-BZ#87 110 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl5-BZ#95 18.9 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl5-BZ#99 151 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl5-BZ#101 142 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl5-BZ#105 97.6 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl5-BZ#110 53.1 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl5-BZ#114 13.0 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl5-BZ#118 241 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 5 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl5-BZ#123 0.172 U ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl5-BZ#126 0.231 U ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#128 13.7 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#138 286 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#146 77.3 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#149 32.8 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#151 8.15 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#153 165 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#156 24.9 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#157 4.83 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#158 16.4 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#167 38.9 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl6-BZ#169 9.14 U ug/kg 95/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl7-BZ#170 43.0 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl7-BZ#174 4.38 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl7-BZ#177 18.4 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl7-BZ#180 62.5 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl7-BZ#183 15.9 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl7-BZ#189 0.446 U ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl7-BZ#187 67.5 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl8-BZ#194 14.0 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl8-BZ#195 4.62 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl8-BZ#201 21.8 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl9-BZ#206 10.3 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Cl10-BZ#209 2.43 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Monochlorobiphenyls 0.150 U ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Dichlorobiphenyls 25.8 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Trichlorobiphenyls 1430 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Tetrachlorobiphenyls 1840 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 6 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Pentachlorobiphenyls 1450 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Hexachlorobiphenyls 816 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Heptachlorobiphenyls 187 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Octachlorobiphenyls 52.7 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Nonachlorobiphenyls 17.3 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Decachlorobiphenyl 2.43 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Total Homologs 5820 ug/kg 0.5/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Percent Lipids 8.2 % 05/30/2002 NS-045 COMP 059_060 615290 4783914 1 0209044-05 Percent Moisture 72 % 5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl2-BZ#8 0.145 UJ ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl3-BZ#18 0.219 UJ ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl3-BZ#28 131 ug/kg 0.05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl3-BZ#31 156 J ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#44 0.177 U ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#45 0.118 U ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#47 402 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#49 258 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#52 169 ug/kg 0.05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#56 57.3 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#66 184 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#70 44.6 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#74 203 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#77 25.4 NJ ug/kg 0.05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl4-BZ#81 0.109 U ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl5-BZ#87 107 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl5-BZ#95 16.6 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl5-BZ#99 145 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl5-BZ#101 145 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl5-BZ#105 98.8 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 7 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl5-BZ#110 50.8 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl5-BZ#114 12.9 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl5-BZ#118 256 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl5-BZ#123 0.0945 U ug/kg 0.05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl5-BZ#126 0.127 U ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#128 9.41 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#138 265 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#146 65.3 ug/kg 0.05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#149 29.9 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#151 7.88 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#153 148 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#156 21.9 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#157 4.12 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#158 14.8 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#167 37.1 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl6-BZ#169 5.02 U ug/kg 55/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl7-BZ#170 32.0 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl7-BZ#174 3.59 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl7-BZ#177 14.0 ug/kg 0.05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl7-BZ#180 44.5 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl7-BZ#183 12.5 ug/kg 0.05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl7-BZ#189 0.245 U ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl7-BZ#187 59.3 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl8-BZ#194 10.0 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl8-BZ#195 3.39 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl8-BZ#201 15.7 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl9-BZ#206 6.32 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Cl10-BZ#209 1.54 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Monochlorobiphenyls 0.0827 U ug/kg 0.0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 8 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Dichlorobiphenyls 13.5 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Trichlorobiphenyls 605 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Tetrachlorobiphenyls 1710 ug/kg 0.05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Pentachlorobiphenyls 1450 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Hexachlorobiphenyls 730 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Heptachlorobiphenyls 150 ug/kg 0.05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Octachlorobiphenyls 37.9 ug/kg 0.05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Nonachlorobiphenyls 11.1 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Decachlorobiphenyl 1.54 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Total Homologs 4720 ug/kg 0.5/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Percent Lipids 5.3 % 05/30/2002 NS-046 COMP 061_062 615290 4783914 1 0209044-06 Percent Moisture 73 % 6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl2-BZ#8 0.238 UJ ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl3-BZ#18 0.360 UJ ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl3-BZ#28 161 ug/kg 0.06/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl3-BZ#31 212 J ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#44 1.52 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#45 0.195 U ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#47 512 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#49 354 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#52 307 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#56 81.7 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#66 266 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#70 63.7 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#74 277 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#77 31.7 NJ ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl4-BZ#81 0.180 U ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl5-BZ#87 144 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl5-BZ#95 27.8 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 9 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl5-BZ#99 195 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl5-BZ#101 200 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl5-BZ#105 127 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl5-BZ#110 78.2 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl5-BZ#114 13.9 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl5-BZ#118 302 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl5-BZ#123 0.156 U ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl5-BZ#126 0.209 U ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#128 14.3 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#138 317 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#146 80.9 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#149 42.7 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#151 13.2 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#153 171 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#156 24.8 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#157 5.08 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#158 18.5 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#167 37.9 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl6-BZ#169 8.27 U ug/kg 86/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl7-BZ#170 41.0 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl7-BZ#174 5.36 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl7-BZ#177 20.7 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl7-BZ#180 59.1 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl7-BZ#183 16.5 ug/kg 0.06/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl7-BZ#189 0.404 U ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl7-BZ#187 77.1 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl8-BZ#194 14.6 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl8-BZ#195 4.62 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl8-BZ#201 22.6 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 10 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl9-BZ#206 9.67 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Cl10-BZ#209 2.45 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Monochlorobiphenyls 0.136 U ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Dichlorobiphenyls 16.2 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Trichlorobiphenyls 1180 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Tetrachlorobiphenyls 2410 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Pentachlorobiphenyls 1930 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Hexachlorobiphenyls 899 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Heptachlorobiphenyls 199 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Octachlorobiphenyls 55.3 ug/kg 0.06/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Nonachlorobiphenyls 17.2 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Decachlorobiphenyl 2.45 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Total Homologs 6710 ug/kg 0.6/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Percent Lipids 6.4 % 06/6/2002 NS-049 COMP 067_068 615290 4783914 1 0209044-07 Percent Moisture 81 % 6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl2-BZ#8 0.953 UJ ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl3-BZ#18 1.44 UJ ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl3-BZ#28 154 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl3-BZ#31 94.2 J ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#44 3.97 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#45 0.778 U ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#47 360 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#49 209 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#52 334 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#56 80.4 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#66 281 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#70 43.9 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#74 231 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#77 28.1 NJ ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 11 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl4-BZ#81 0.720 U ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl5-BZ#87 137 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl5-BZ#95 59.2 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl5-BZ#99 213 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl5-BZ#101 257 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl5-BZ#105 163 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl5-BZ#110 81.7 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl5-BZ#114 20.8 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl5-BZ#118 345 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl5-BZ#123 0.623 U ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl5-BZ#126 0.837 U ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#128 21.4 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#138 414 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#146 89.6 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#149 132 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#151 21.1 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#153 225 ug/kg 26/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#156 39.3 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#157 7.43 ug/kg 26/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#158 24.4 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#167 55.6 ug/kg 26/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl6-BZ#169 33.1 U ug/kg 36/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl7-BZ#170 65.2 ug/kg 26/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl7-BZ#174 19.5 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl7-BZ#177 25.7 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl7-BZ#180 103 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl7-BZ#183 19.2 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl7-BZ#189 1.61 U ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl7-BZ#187 102 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 12 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl8-BZ#194 23.3 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl8-BZ#195 6.69 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl8-BZ#201 34.8 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl9-BZ#206 15.7 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Cl10-BZ#209 2.35 J ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Monochlorobiphenyls 0.545 U ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Dichlorobiphenyls 13.1 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Trichlorobiphenyls 226 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Tetrachlorobiphenyls 1980 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Pentachlorobiphenyls 2270 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Hexachlorobiphenyls 1260 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Heptachlorobiphenyls 292 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Octachlorobiphenyls 86.2 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Nonachlorobiphenyls 26.0 ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Decachlorobiphenyl 2.35 J ug/kg 16/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Total Homologs 6160 ug/kg 0.6/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Percent Lipids 10.8 % 06/20/2002 NS-121 COMP 125_126 612607 4758345 2 0209044-08 Percent Moisture 63 % 5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl2-BZ#8 0.313 UJ ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl3-BZ#18 0.473 UJ ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl3-BZ#28 16.1 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl3-BZ#31 13.9 J ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#44 0.384 U ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#45 0.256 U ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#47 32.1 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#49 17.8 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#52 15.2 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#56 5.74 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#66 18.5 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 13 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#70 4.73 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#74 21.6 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#77 3.91 NJ ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl4-BZ#81 0.237 U ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl5-BZ#87 12.6 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl5-BZ#95 2.04 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl5-BZ#99 24.1 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl5-BZ#101 19.8 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl5-BZ#105 15.6 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl5-BZ#110 13.7 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl5-BZ#114 0.217 U ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl5-BZ#118 40.9 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl5-BZ#123 0.205 U ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl5-BZ#126 0.275 U ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#128 3.95 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#138 77.0 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#146 16.5 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#149 5.87 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#151 1.10 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#153 57.5 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#156 7.25 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#157 1.83 J ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#158 5.26 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#167 9.70 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl6-BZ#169 10.9 U ug/kg 15/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl7-BZ#170 18.3 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl7-BZ#174 1.67 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl7-BZ#177 5.01 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl7-BZ#180 34.0 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 14 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl7-BZ#183 8.31 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl7-BZ#189 0.531 U ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl7-BZ#187 22.0 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl8-BZ#194 8.15 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl8-BZ#195 2.28 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl8-BZ#201 10.2 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl9-BZ#206 6.07 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Cl10-BZ#209 3.02 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Monochlorobiphenyls 0.179 U ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Dichlorobiphenyls 0.313 U ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Trichlorobiphenyls 29.7 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Tetrachlorobiphenyls 155 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Pentachlorobiphenyls 278 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Hexachlorobiphenyls 219 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Heptachlorobiphenyls 81.7 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Octachlorobiphenyls 201 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Nonachlorobiphenyls 12.5 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Decachlorobiphenyl 3.02 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Total Homologs 981 ug/kg 0.5/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Percent Lipids 9.0 % 05/28/2002 NS-625 COMP 630_631 601746 4716030 4 0209044-09 Percent Moisture 70 % 5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl2-BZ#8 0.367 UJ ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl3-BZ#18 0.555 UJ ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl3-BZ#28 24.0 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl3-BZ#31 13.8 J ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#44 0.450 U ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#45 0.300 U ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#47 39.6 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#49 21.3 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 15 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#52 16.4 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#56 7.07 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#66 26.8 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#70 5.39 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#74 28.1 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#77 4.82 NJ ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl4-BZ#81 0.277 U ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl5-BZ#87 19.5 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl5-BZ#95 2.24 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl5-BZ#99 37.2 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl5-BZ#101 31.4 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl5-BZ#105 29.9 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl5-BZ#110 7.30 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl5-BZ#114 0.255 U ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl5-BZ#118 78.1 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl5-BZ#123 0.240 U ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl5-BZ#126 0.322 U ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#128 8.02 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#138 152 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#146 34.7 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#149 10.4 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#151 1.34 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#153 118 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#156 13.3 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#157 3.01 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#158 10.9 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#167 21.0 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl6-BZ#169 12.7 U ug/kg 15/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl7-BZ#170 42.1 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 16 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl7-BZ#174 2.82 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl7-BZ#177 9.88 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl7-BZ#180 75.4 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl7-BZ#183 17.9 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl7-BZ#189 0.622 U ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl7-BZ#187 52.7 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl8-BZ#194 19.1 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl8-BZ#195 4.49 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl8-BZ#201 24.2 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl9-BZ#206 14.7 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Cl10-BZ#209 4.73 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Monochlorobiphenyls 0.210 U ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Dichlorobiphenyls 0.367 U ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Trichlorobiphenyls 36.1 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Tetrachlorobiphenyls 197 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Pentachlorobiphenyls 411 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Hexachlorobiphenyls 453 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Heptachlorobiphenyls 179 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Octachlorobiphenyls 86.0 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Nonachlorobiphenyls 25.2 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Decachlorobiphenyl 4.73 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Total Homologs 1390 ug/kg 0.5/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Percent Lipids 7.9 % 05/28/2002 NS-626 COMP 632_633 601746 4716030 4 0209044-10 Percent Moisture 62 % 5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl2-BZ#8 0.328 UJ ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl3-BZ#18 0.495 UJ ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl3-BZ#28 118 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl3-BZ#31 96.6 J ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#44 0.402 U ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 17 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#45 0.268 U ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#47 230 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#49 160 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#52 224 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#56 39.5 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#66 123 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#70 26.8 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#74 106 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#77 11.2 NJ ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl4-BZ#81 0.248 U ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl5-BZ#87 52.7 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl5-BZ#95 22.9 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl5-BZ#99 82.4 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl5-BZ#101 98.0 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl5-BZ#105 55.8 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl5-BZ#110 45.4 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl5-BZ#114 6.82 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl5-BZ#118 118 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl5-BZ#123 0.214 U ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl5-BZ#126 0.288 U ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#128 6.91 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#138 139 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#146 30.9 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#149 39.5 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#151 5.12 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#153 73.1 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#156 12.9 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#157 2.77 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#158 9.04 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 18 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#167 20.2 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl6-BZ#169 11.4 U ug/kg 15/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl7-BZ#170 22.6 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl7-BZ#174 4.90 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl7-BZ#177 8.65 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl7-BZ#180 36.7 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl7-BZ#183 7.72 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl7-BZ#189 0.556 U ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl7-BZ#187 34.2 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl8-BZ#194 8.44 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl8-BZ#195 2.52 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl8-BZ#201 11.4 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl9-BZ#206 8.01 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Cl10-BZ#209 2.52 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Monochlorobiphenyls 0.187 U ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Dichlorobiphenyls 25.7 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Trichlorobiphenyls 197 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Tetrachlorobiphenyls 1140 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Pentachlorobiphenyls 874 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Hexachlorobiphenyls 420 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Heptachlorobiphenyls 100 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Octachlorobiphenyls 35.2 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Nonachlorobiphenyls 13.3 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Decachlorobiphenyl 2.52 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Total Homologs 2810 ug/kg 0.5/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Percent Lipids 7.9 % 05/30/2002 NS-630 COMP 640_641 612607 4758345 2 0209044-11 Percent Moisture 88 % 6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl2-BZ#8 0.291 UJ ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl3-BZ#18 1.02 J ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 19 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl3-BZ#28 26.3 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl3-BZ#31 37.5 J ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#44 0.795 J ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#45 0.238 U ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#47 39.7 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#49 44.3 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#52 53.8 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#56 7.99 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#66 27.4 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#70 15.3 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#74 18.9 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#77 2.54 NJ ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl4-BZ#81 0.220 U ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl5-BZ#87 13.7 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl5-BZ#95 12.2 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl5-BZ#99 14.9 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl5-BZ#101 24.0 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl5-BZ#105 13.0 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl5-BZ#110 17.5 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl5-BZ#114 0.202 U ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl5-BZ#118 26.1 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl5-BZ#123 0.190 U ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl5-BZ#126 0.256 U ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#128 1.70 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#138 33.1 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#146 7.91 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#149 11.1 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#151 4.62 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#153 21.1 ug/kg 0.

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 20 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#156 3.29 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#157 0.909 J ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#158 1.89 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#167 3.56 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl6-BZ#169 10.1 U ug/kg 16/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl7-BZ#170 7.65 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl7-BZ#174 2.35 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl7-BZ#177 3.48 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl7-BZ#180 11.1 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl7-BZ#183 2.12 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl7-BZ#189 0.493 U ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl7-BZ#187 13.9 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl8-BZ#194 3.45 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl8-BZ#195 0.644 J ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl8-BZ#201 5.79 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl9-BZ#206 3.71 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Cl10-BZ#209 2.01 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Monochlorobiphenyls 0.166 U ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Dichlorobiphenyls 5.95 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Trichlorobiphenyls 68.8 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Tetrachlorobiphenyls 282 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Pentachlorobiphenyls 265 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Hexachlorobiphenyls 113 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Heptachlorobiphenyls 35.9 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Octachlorobiphenyls 15.8 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Nonachlorobiphenyls 6.44 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Decachlorobiphenyl 2.01 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Total Homologs 795 ug/kg 0.6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Percent Lipids 7.1 % 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 21 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl2-BZ#8 0.335 UJ ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl3-BZ#18 0.784 J ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl3-BZ#28 92.3 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl3-BZ#31 139 J ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#44 1.83 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#45 0.273 U ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#47 196 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#49 155 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#52 91.3 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#56 32.3 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#66 85.7 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#70 59.3 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#74 86.2 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#77 13.0 NJ ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl4-BZ#81 0.253 U ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl5-BZ#87 61.9 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl5-BZ#95 10.4 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl5-BZ#99 70.1 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl5-BZ#101 73.8 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl5-BZ#105 79.8 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl5-BZ#110 35.6 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl5-BZ#114 10.4 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl5-BZ#118 165 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl5-BZ#123 0.219 U ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl5-BZ#126 0.294 U ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#128 17.5 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#138 255 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#146 75.9 ug/kg 0.5/15/2002 NS-021 COMP 030_031 615290 4783914 1 0209044-03 Cl6-BZ#149 15.9 ug/kg 0.

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 1 of 22
Barn Swallow (Hirundo rustica) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

(

6/3/2002 NS-634 COMP 649_650 612054 4759483 2 0209044-12 Percent Moisture 64 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 22 of 22
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl2-BZ#8 0.0730 U ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl3-BZ#18 0.110 U ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl3-BZ#28 9.42 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl3-BZ#31 2.55 J ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#44 0.0894 U ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#45 0.0596 U ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#47 13.3 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#49 2.19 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#52 1.58 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#56 2.63 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#66 9.66 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#70 1.28 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#74 8.25 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#77 0.0417 U ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl4-BZ#81 0.0552 U ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl5-BZ#87 4.06 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl5-BZ#95 0.551 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl5-BZ#99 8.74 ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl5-BZ#101 6.12 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl5-BZ#105 6.23 J ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl5-BZ#110 1.91 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl5-BZ#114 0.0507 U ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl5-BZ#118 16.9 J ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl5-BZ#123 0.0477 U ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl5-BZ#126 0.0641 U ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#128 2.01 J ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#138 22.1 ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#146 5.02 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#149 2.63 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#151 0.351 ug/kg 0

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 1 of 11
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#153 22.0 ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#156 3.00 J ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#157 0.161 U ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#158 1.66 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#167 2.38 ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl6-BZ#169 2.53 U ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl7-BZ#170 4.44 J ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl7-BZ#174 0.722 J ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl7-BZ#177 2.05 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl7-BZ#180 9.25 ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl7-BZ#183 2.32 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl7-BZ#189 0.124 U ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl7-BZ#187 9.15 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl8-BZ#194 1.91 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl8-BZ#195 0.855 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl8-BZ#201 3.67 ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl9-BZ#206 1.66 ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Cl10-BZ#209 0.807 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Monochlorobiphenyls 0.0417 U ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Dichlorobiphenyls 0.0730 U ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Trichlorobiphenyls 11.1 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Tetrachlorobiphenyls 44.5 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Pentachlorobiphenyls 76.4 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Hexachlorobiphenyls 62.9 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Heptachlorobiphenyls 21.4 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Octachlorobiphenyls 8.58 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Nonachlorobiphenyls 4.96 ug/kg 4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Decachlorobiphenyl 0.807 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Total Homologs 231 ug/kg 04/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Percent Lipids 6.7 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 2 of 11
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

4/30/2002 EB-008 COMP 012_013 600586 4705859 4 0209038-01 Percent Moisture 82 % 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl2-BZ#8 0.115 U ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl3-BZ#18 0.174 U ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl3-BZ#28 0.0424 U ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl3-BZ#31 0.0801 UJ ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#44 0.141 U ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#45 0.0942 U ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#47 46.2 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#49 22.0 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#52 2.73 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#56 0.101 U ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#66 7.77 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#70 0.0848 U ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#74 57.2 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#77 0.0659 U ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl4-BZ#81 0.0871 U ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl5-BZ#87 17.7 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl5-BZ#95 0.585 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl5-BZ#99 43.6 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl5-BZ#101 39.0 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl5-BZ#105 8.18 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl5-BZ#110 5.44 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl5-BZ#114 5.10 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl5-BZ#118 65.8 J ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl5-BZ#123 0.0754 U ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl5-BZ#126 0.101 U ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#128 3.50 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#138 109 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#146 20.6 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#149 7.72 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 3 of 11
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#151 0.315 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#153 83.6 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#156 11.2 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#157 2.14 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#158 5.60 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#167 9.96 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl6-BZ#169 4.00 U ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl7-BZ#170 13.2 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl7-BZ#174 1.06 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl7-BZ#177 4.80 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl7-BZ#180 26.4 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl7-BZ#183 4.65 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl7-BZ#189 0.196 U ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl7-BZ#187 37.1 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl8-BZ#194 5.24 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl8-BZ#195 1.23 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl8-BZ#201 11.7 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl9-BZ#206 3.72 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Cl10-BZ#209 1.17 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Monochlorobiphenyls 0.0659 U ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Dichlorobiphenyls 0.115 U ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Trichlorobiphenyls 0.151 U ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Tetrachlorobiphenyls 148 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Pentachlorobiphenyls 291 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Hexachlorobiphenyls 263 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Heptachlorobiphenyls 66.5 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Octachlorobiphenyls 21.2 ug/kg 06/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Nonachlorobiphenyls 10.2 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Decachlorobiphenyl 1.17 ug/kg 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Total Homologs 802 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 4 of 11
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Percent Lipids 7.5 % 6/3/2002 EB-048 COMP 065_066 616105 4769250 2 0209038-02 Percent Moisture 80 % 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl2-BZ#8 0.0711 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl3-BZ#18 0.107 U ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl3-BZ#28 0.0261 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl3-BZ#31 0.0493 UJ ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#44 0.0870 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#45 0.0580 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#47 4.81 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#49 2.98 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#52 1.59 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#56 0.0624 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#66 1.71 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#70 0.905 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#74 7.32 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#77 0.0406 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl4-BZ#81 0.0537 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl5-BZ#87 5.87 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl5-BZ#95 0.240 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl5-BZ#99 10.3 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl5-BZ#101 10.9 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl5-BZ#105 3.64 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl5-BZ#110 1.64 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl5-BZ#114 0.0493 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl5-BZ#118 19.1 J ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl5-BZ#123 0.0464 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl5-BZ#126 0.0624 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#128 1.41 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#138 48.3 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#146 11.1 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 5 of 11
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#149 2.35 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#151 0.111 J ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#153 44.7 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#156 5.39 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#157 0.868 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#158 2.38 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#167 3.95 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl6-BZ#169 2.47 U ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl7-BZ#170 7.87 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl7-BZ#174 0.443 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl7-BZ#177 1.85 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl7-BZ#180 16.2 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl7-BZ#183 2.43 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl7-BZ#189 0.120 U ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl7-BZ#187 17.4 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl8-BZ#194 5.14 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl8-BZ#195 0.536 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl8-BZ#201 6.60 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl9-BZ#206 2.75 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Cl10-BZ#209 0.517 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Monochlorobiphenyls 0.0406 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Dichlorobiphenyls 0.0711 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Trichlorobiphenyls 0.0928 U ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Tetrachlorobiphenyls 22.8 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Pentachlorobiphenyls 99.2 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Hexachlorobiphenyls 123 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Heptachlorobiphenyls 35.1 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Octachlorobiphenyls 13.8 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Nonachlorobiphenyls 5.85 ug/kg 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Decachlorobiphenyl 0.517 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 6 of 11
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Total Homologs 301 ug/kg 06/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Percent Lipids 10 % 6/3/2002 EB-231 COMP 234_235 611672 4757186 2 0209038-03 Percent Moisture 77 % 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl2-BZ#8 0.0699 U ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl3-BZ#18 0.106 U ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl3-BZ#28 37.5 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl3-BZ#31 23.4 J ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#44 0.0856 U ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#45 0.0571 U ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#47 86.0 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#49 67.0 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#52 42.3 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#56 13.2 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#66 69.3 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#70 27.5 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#74 89.2 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#77 0.0400 U ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl4-BZ#81 0.0528 U ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl5-BZ#87 41.7 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl5-BZ#95 3.81 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl5-BZ#99 62.1 ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl5-BZ#101 83.0 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl5-BZ#105 35.6 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl5-BZ#110 33.4 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl5-BZ#114 6.65 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl5-BZ#118 123 J ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl5-BZ#123 0.0457 U ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl5-BZ#126 0.0614 U ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#128 6.78 ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#138 139 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 7 of 11
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#146 29.4 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#149 24.8 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#151 0.891 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#153 95.2 ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#156 12.8 ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#157 0.154 U ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#158 6.13 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#167 13.9 ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl6-BZ#169 2.43 U ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl7-BZ#170 14.5 ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl7-BZ#174 3.52 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl7-BZ#177 7.32 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl7-BZ#180 34.0 ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl7-BZ#183 5.73 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl7-BZ#189 0.118 U ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl7-BZ#187 48.1 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl8-BZ#194 6.40 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl8-BZ#195 1.18 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl8-BZ#201 15.2 ug/kg 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl9-BZ#206 5.47 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Cl10-BZ#209 1.15 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Monochlorobiphenyls 0.0400 U ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Dichlorobiphenyls 0.0699 U ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Trichlorobiphenyls 53.9 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Tetrachlorobiphenyls 441 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Pentachlorobiphenyls 599 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Hexachlorobiphenyls 347 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Heptachlorobiphenyls 86.3 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Octachlorobiphenyls 27.7 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Nonachlorobiphenyls 14.2 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 8 of 11
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Decachlorobiphenyl 1.15 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Total Homologs 1570 ug/kg 05/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Percent Lipids 5.9 % 5/7/2002 EB-606 COMP 606_607 607573 4749769 3 0209038-04 Percent Moisture 82 % 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl2-BZ#8 0.132 U ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl3-BZ#18 0.199 U ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl3-BZ#28 0.0483 U ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl3-BZ#31 0.0913 UJ ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#44 0.161 U ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#45 0.107 U ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#47 7.39 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#49 2.45 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#52 1.86 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#56 2.74 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#66 14.7 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#70 2.43 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#74 23.4 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#77 0.0752 U ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl4-BZ#81 0.0993 U ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl5-BZ#87 9.63 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl5-BZ#95 0.239 J ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl5-BZ#99 25.9 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl5-BZ#101 13.6 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl5-BZ#105 11.7 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl5-BZ#110 6.51 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl5-BZ#114 2.70 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl5-BZ#118 38.7 J ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl5-BZ#123 0.0859 U ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl5-BZ#126 0.115 U ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#128 2.33 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 9 of 11
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#138 70.3 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#146 13.7 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#149 5.13 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#151 0.0966 U ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#153 69.4 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#156 8.86 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#157 1.61 J ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#158 4.00 J ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#167 7.10 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl6-BZ#169 4.56 U ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl7-BZ#170 16.0 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl7-BZ#174 0.889 J ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl7-BZ#177 3.13 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl7-BZ#180 37.2 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl7-BZ#183 6.12 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl7-BZ#189 0.223 U ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl7-BZ#187 24.6 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl8-BZ#194 8.09 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl8-BZ#195 1.54 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl8-BZ#201 12.0 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl9-BZ#206 4.12 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Cl10-BZ#209 0.752 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Monochlorobiphenyls 0.0752 U ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Dichlorobiphenyls 0.132 U ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Trichlorobiphenyls 0.172 U ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Tetrachlorobiphenyls 62.9 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Pentachlorobiphenyls 175 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Hexachlorobiphenyls 183 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Heptachlorobiphenyls 64.1 ug/kg 05/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Octachlorobiphenyls 24.0 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 10 of 11
Eastern Bluebird (Sialia sialis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation:Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Nonachlorobiphenyls 8.69 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Decachlorobiphenyl 0.752 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Total Homologs 519 ug/kg 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Percent Lipids 14 J % 5/29/2002 EB-627 COMP 634_635 609111 4742104 3 0209038-05 Percent Moisture 82 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 11 of 11
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl2-BZ#8 0.130 UJ ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl3-BZ#18 4.20 J ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl3-BZ#28 167 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl3-BZ#31 99.4 J ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#44 11.5 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#45 0.106 U ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#47 319 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#49 181 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#52 192 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#56 75.6 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#66 212 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#70 36.6 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#74 177 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#77 15.7 NJ ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl4-BZ#81 0.0981 U ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl5-BZ#87 77.6 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl5-BZ#95 33.7 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl5-BZ#99 128 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl5-BZ#101 148 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl5-BZ#105 79.6 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl5-BZ#110 63.1 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl5-BZ#114 8.07 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl5-BZ#118 188 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl5-BZ#123 0.0848 U ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl5-BZ#126 0.114 U ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#128 8.10 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#138 204 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#146 38.4 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#149 50.7 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#151 8.31 ug/kg 0

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 1 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#153 135 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#156 14.7 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#157 2.80 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#158 13.7 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#167 23.3 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl6-BZ#169 4.51 U ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl7-BZ#170 25.8 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl7-BZ#174 6.30 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl7-BZ#177 10.5 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl7-BZ#180 36.5 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl7-BZ#183 11.0 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl7-BZ#189 0.220 U ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl7-BZ#187 42.0 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl8-BZ#194 7.21 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl8-BZ#195 2.33 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl8-BZ#201 11.9 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl9-BZ#206 4.90 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Cl10-BZ#209 1.23 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Monochlorobiphenyls 0.0742 U ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Dichlorobiphenyls 5.57 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Trichlorobiphenyls 1040 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Tetrachlorobiphenyls 1490 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Pentachlorobiphenyls 1320 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Hexachlorobiphenyls 610 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Heptachlorobiphenyls 119 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Octachlorobiphenyls 27.6 ug/kg 05/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Nonachlorobiphenyls 8.37 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Decachlorobiphenyl 1.23 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Total Homologs 4620 ug/kg 5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Percent Lipids 7.2 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 2 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/30/2002 RS-117 COMP 119_120 607287 4750931 3 0209044-13 Percent Moisture 66 % 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl2-BZ#8 0.228 UJ ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl3-BZ#18 7.26 J ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl3-BZ#28 125 ug/kg 06/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl3-BZ#31 124 J ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#44 5.96 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#45 0.186 U ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#47 264 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#49 184 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#52 116 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#56 27.3 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#66 114 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#70 52.1 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#74 107 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#77 11.8 NJ ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl4-BZ#81 0.172 U ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl5-BZ#87 69.4 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl5-BZ#95 20.3 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl5-BZ#99 149 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl5-BZ#101 168 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl5-BZ#105 54.2 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl5-BZ#110 61.9 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl5-BZ#114 4.36 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl5-BZ#118 168 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl5-BZ#123 0.149 U ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl5-BZ#126 0.200 U ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#128 7.12 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#138 266 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#146 56.1 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#149 60.1 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 3 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#151 8.75 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#153 198 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#156 15.9 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#157 3.11 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#158 16.5 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#167 37.6 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl6-BZ#169 7.91 U ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl7-BZ#170 42.7 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl7-BZ#174 9.90 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl7-BZ#177 20.5 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl7-BZ#180 65.7 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl7-BZ#183 20.5 ug/kg 06/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl7-BZ#189 0.386 U ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl7-BZ#187 71.2 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl8-BZ#194 12.2 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl8-BZ#195 4.15 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl8-BZ#201 25.6 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl9-BZ#206 10.7 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Cl10-BZ#209 3.62 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Monochlorobiphenyls 0.130 U ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Dichlorobiphenyls 6.97 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Trichlorobiphenyls 607 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Tetrachlorobiphenyls 1120 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Pentachlorobiphenyls 1270 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Hexachlorobiphenyls 808 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Heptachlorobiphenyls 202 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Octachlorobiphenyls 55.4 ug/kg 06/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Nonachlorobiphenyls 20.5 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Decachlorobiphenyl 3.62 ug/kg 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Total Homologs 4090 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 4 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Percent Lipids 7.3 % 6/6/2002 RS-118 COMP 121_122 599428 4703276 4 0209044-14 Percent Moisture 61 % 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl2-BZ#8 0.315 UJ ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl3-BZ#18 4.71 J ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl3-BZ#28 146 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl3-BZ#31 92.6 J ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#44 7.70 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#45 0.257 U ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#47 284 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#49 178 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#52 244 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#56 65.1 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#66 212 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#70 40.9 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#74 164 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#77 17.6 NJ ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl4-BZ#81 0.238 U ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl5-BZ#87 85.1 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl5-BZ#95 46.9 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl5-BZ#99 146 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl5-BZ#101 185 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl5-BZ#105 96.7 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl5-BZ#110 61.0 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl5-BZ#114 14.3 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl5-BZ#118 270 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl5-BZ#123 0.206 U ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl5-BZ#126 0.277 U ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#128 14.1 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#138 378 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#146 82.4 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 5 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#149 64.6 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#151 9.42 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#153 278 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#156 34.8 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#157 5.45 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#158 25.8 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#167 52.2 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl6-BZ#169 10.9 U ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl7-BZ#170 64.4 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl7-BZ#174 8.60 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl7-BZ#177 14.5 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl7-BZ#180 98.7 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl7-BZ#183 24.7 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl7-BZ#189 0.534 U ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl7-BZ#187 71.3 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl8-BZ#194 17.8 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl8-BZ#195 5.74 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl8-BZ#201 23.1 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl9-BZ#206 11.8 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Cl10-BZ#209 2.95 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Monochlorobiphenyls 0.180 U ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Dichlorobiphenyls 9.87 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Trichlorobiphenyls 561 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Tetrachlorobiphenyls 1490 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Pentachlorobiphenyls 1620 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Hexachlorobiphenyls 1130 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Heptachlorobiphenyls 249 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Octachlorobiphenyls 63.3 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Nonachlorobiphenyls 20.0 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Decachlorobiphenyl 2.95 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 6 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Total Homologs 5140 ug/kg 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Percent Lipids 6.7 % 5/29/2002 RS-628 COMP 636_637 609388 4741788 3 0209044-15 Percent Moisture 80 % 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl2-BZ#8 0.255 U ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl3-BZ#18 9.08 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl3-BZ#28 510 ug/kg 05/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl3-BZ#31 514 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#44 0.312 U ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#45 0.208 U ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#47 1920 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#49 1210 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#52 752 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#56 256 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#66 877 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#70 174 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#74 856 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#77 90.9 NJ ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl4-BZ#81 0.192 U ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl5-BZ#87 487 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl5-BZ#95 71.1 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl5-BZ#99 665 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl5-BZ#101 737 J ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl5-BZ#105 330 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl5-BZ#110 189 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl5-BZ#114 47.6 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl5-BZ#118 954 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl5-BZ#123 124 NJ ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl5-BZ#126 19.5 NJ ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#128 34.3 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#138 1010 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 7 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#146 256 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#149 149 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#151 31.1 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#153 553 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#156 84.0 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#157 14.3 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#158 53.6 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#167 153 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl6-BZ#169 8.84 UJ ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl7-BZ#170 132 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl7-BZ#174 13.9 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl7-BZ#177 48.5 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl7-BZ#180 175 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl7-BZ#183 51.1 ug/kg 05/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl7-BZ#189 35.3 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl7-BZ#187 194 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl8-BZ#194 43.3 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl8-BZ#195 14.0 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl8-BZ#201 53.8 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl9-BZ#206 22.5 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Cl10-BZ#209 3.68 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Monochlorobiphenyls 0.287 U ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Dichlorobiphenyls 16.9 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Trichlorobiphenyls 1300 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Tetrachlorobiphenyls 7620 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Pentachlorobiphenyls 5070 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Hexachlorobiphenyls 2390 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Heptachlorobiphenyls 496 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Octachlorobiphenyls 132 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Nonachlorobiphenyls 34.8 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 8 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Decachlorobiphenyl 3.26 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Total Homologs 17100 ug/kg 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Percent Lipids 7.0 % 5/29/2002 RS-629 COMP 639_644 615076 4786141 1 0209045-01 Percent Moisture 72 % 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl2-BZ#8 2.82 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl3-BZ#18 13.7 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl3-BZ#28 189 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl3-BZ#31 213 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#44 39.4 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#45 0.0653 U ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#47 705 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#49 514 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#52 600 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#56 132 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#66 376 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#70 112 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#74 293 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#77 34.4 NJ ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl4-BZ#81 0.0604 U ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl5-BZ#87 181 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl5-BZ#95 89.2 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl5-BZ#99 242 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl5-BZ#101 302 J ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl5-BZ#105 146 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl5-BZ#110 128 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl5-BZ#114 21.0 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl5-BZ#118 350 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl5-BZ#123 45.9 NJ ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl5-BZ#126 7.17 NJ ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#128 17.7 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 9 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#138 371 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#146 88.1 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#149 81.4 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#151 15.4 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#153 213 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#156 33.9 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#157 5.47 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#158 29.9 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#167 38.1 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl6-BZ#169 2.78 U ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl7-BZ#170 47.7 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl7-BZ#174 7.87 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl7-BZ#177 18.1 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl7-BZ#180 73.1 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl7-BZ#183 19.9 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl7-BZ#189 0.136 U ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl7-BZ#187 66.7 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl8-BZ#194 12.4 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl8-BZ#195 4.35 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl8-BZ#201 15.8 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl9-BZ#206 5.73 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Cl10-BZ#209 1.06 ug/kg 05/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Monochlorobiphenyls 0.130 U ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Dichlorobiphenyls 10.8 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Trichlorobiphenyls 766 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Tetrachlorobiphenyls 3880 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Pentachlorobiphenyls 2700 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Hexachlorobiphenyls 1170 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Heptachlorobiphenyls 244 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Octachlorobiphenyls 55.3 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 10 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Nonachlorobiphenyls 15.0 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Decachlorobiphenyl 1.89 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Total Homologs 8850 ug/kg 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Percent Lipids 6.5 % 5/30/2002 RS-631 COMP 642_643 615034 4779714 1 0209045-02 Percent Moisture 65 % 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl2-BZ#8 0.267 U ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl3-BZ#18 6.93 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl3-BZ#28 436 ug/kg 05/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl3-BZ#31 373 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#44 130 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#45 0.218 U ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#47 1450 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#49 640 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#52 615 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#56 266 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#66 768 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#70 134 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#74 758 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#77 69.6 NJ ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl4-BZ#81 0.201 U ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl5-BZ#87 383 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl5-BZ#95 47.3 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl5-BZ#99 536 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl5-BZ#101 536 J ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl5-BZ#105 292 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl5-BZ#110 126 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl5-BZ#114 46.1 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl5-BZ#118 828 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl5-BZ#123 95.9 NJ ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl5-BZ#126 33.4 NJ ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 11 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#128 37.5 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#138 968 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#146 232 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#149 96.0 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#151 23.4 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#153 555 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#156 79.3 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#157 14.0 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#158 58.4 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#167 110 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl6-BZ#169 9.25 UJ ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl7-BZ#170 116 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl7-BZ#174 10.5 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl7-BZ#177 62.2 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl7-BZ#180 175 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl7-BZ#183 54.5 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl7-BZ#189 0.452 U ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl7-BZ#187 217 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl8-BZ#194 56.5 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl8-BZ#195 15.9 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl8-BZ#201 72.9 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl9-BZ#206 40.1 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Cl10-BZ#209 9.67 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Monochlorobiphenyls 1.35 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Dichlorobiphenyls 45.2 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Trichlorobiphenyls 882 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Tetrachlorobiphenyls 5720 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Pentachlorobiphenyls 4930 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Hexachlorobiphenyls 2680 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Heptachlorobiphenyls 608 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 12 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Octachlorobiphenyls 168 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Nonachlorobiphenyls 69.9 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Decachlorobiphenyl 9.67 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Total Homologs 15100 ug/kg 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Percent Lipids 8.5 % 5/31/2002 RS-633 COMP 647_648 615035 4783553 1 0209045-03 Percent Moisture 77 % 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl2-BZ#8 0.118 U ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl3-BZ#18 4.92 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl3-BZ#28 273 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl3-BZ#31 268 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#44 63.7 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#45 0.0959 U ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#47 682 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#49 313 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#52 338 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#56 147 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#66 395 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#70 83.9 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#74 269 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#77 28.9 NJ ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl4-BZ#81 0.0887 U ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl5-BZ#87 150 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl5-BZ#95 37.1 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl5-BZ#99 218 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl5-BZ#101 280 J ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl5-BZ#105 168 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl5-BZ#110 99.9 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl5-BZ#114 18.8 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl5-BZ#118 347 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl5-BZ#123 362 NJ ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 13 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl5-BZ#126 8.26 NJ ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#128 59.7 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#138 447 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#146 90.0 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#149 86.4 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#151 9.27 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#153 236 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#156 38.5 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#157 6.14 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#158 334 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#167 103 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl6-BZ#169 4.08 UJ ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl7-BZ#170 51.8 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl7-BZ#174 6.73 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl7-BZ#177 22.3 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl7-BZ#180 83.0 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl7-BZ#183 19.7 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl7-BZ#189 20.7 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl7-BZ#187 84.6 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl8-BZ#194 15.1 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl8-BZ#195 4.46 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl8-BZ#201 28.4 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl9-BZ#206 13.8 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Cl10-BZ#209 2.86 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Monochlorobiphenyls 0.0671 U ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Dichlorobiphenyls 22.1 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Trichlorobiphenyls 594 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Tetrachlorobiphenyls 2710 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Pentachlorobiphenyls 2290 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Hexachlorobiphenyls 1130 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 14 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Heptachlorobiphenyls 259 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Octachlorobiphenyls 60.5 ug/kg 06/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Nonachlorobiphenyls 22.9 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Decachlorobiphenyl 2.86 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Total Homologs 7090 ug/kg 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Percent Lipids 9.9 % 6/4/2002 RS-636 COMP 653_654 611666 4757404 2 0209045-04 Percent Moisture 78 % 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl2-BZ#8 0.0961 U ug/kg 06/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl3-BZ#18 9.79 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl3-BZ#28 262 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl3-BZ#31 461 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#44 22.5 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#45 0.0785 U ug/kg 06/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#47 917 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#49 719 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#52 780 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#56 183 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#66 609 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#70 146 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#74 441 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#77 52.4 NJ ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl4-BZ#81 0.0726 U ug/kg 06/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl5-BZ#87 219 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl5-BZ#95 109 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl5-BZ#99 348 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl5-BZ#101 463 J ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl5-BZ#105 247 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl5-BZ#110 221 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl5-BZ#114 24.5 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl5-BZ#118 611 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 15 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl5-BZ#123 55.2 NJ ug/kg 06/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl5-BZ#126 9.33 NJ ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#128 23.7 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#138 484 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#146 93.7 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#149 134 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#151 22.7 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#153 355 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#156 42.9 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#157 6.93 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#158 47.3 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#167 59.1 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl6-BZ#169 3.33 UJ ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl7-BZ#170 72.2 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl7-BZ#174 17.4 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl7-BZ#177 23.4 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl7-BZ#180 115 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl7-BZ#183 28.7 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl7-BZ#189 0.163 U ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl7-BZ#187 92.8 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl8-BZ#194 19.8 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl8-BZ#195 5.98 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl8-BZ#201 30.0 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl9-BZ#206 13.7 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Cl10-BZ#209 3.24 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Monochlorobiphenyls 0.167 U ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Dichlorobiphenyls 13.9 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Trichlorobiphenyls 1280 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Tetrachlorobiphenyls 4950 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Pentachlorobiphenyls 3690 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 16 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Hexachlorobiphenyls 1460 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Heptachlorobiphenyls 300 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Octachlorobiphenyls 85.2 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Nonachlorobiphenyls 23.2 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Decachlorobiphenyl 3.24 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Total Homologs 11800 ug/kg 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Percent Lipids 9.3 % 6/4/2002 RS-637 COMP 655_656 608484 4752507 2 0209045-05 Percent Moisture 71 % 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl2-BZ#8 0.140 U ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl3-BZ#18 14.3 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl3-BZ#28 282 ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl3-BZ#31 446 ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#44 13.1 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#45 0.115 U ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#47 745 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#49 663 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#52 600 ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#56 120 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#66 388 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#70 147 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#74 371 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#77 38.5 NJ ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl4-BZ#81 0.106 U ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl5-BZ#87 176 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl5-BZ#95 71.2 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl5-BZ#99 253 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl5-BZ#101 288 J ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl5-BZ#105 164 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl5-BZ#110 156 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl5-BZ#114 19.6 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 17 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl5-BZ#118 381 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl5-BZ#123 41.6 NJ ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl5-BZ#126 6.75 NJ ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#128 18.7 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#138 358 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#146 72.9 ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#149 101 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#151 19.2 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#153 227 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#156 36.2 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#157 6.02 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#158 23.7 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#167 49.4 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl6-BZ#169 4.87 UJ ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl7-BZ#170 48.9 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl7-BZ#174 5.20 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl7-BZ#177 18.7 ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl7-BZ#180 72.3 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl7-BZ#183 20.5 ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl7-BZ#189 0.238 U ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl7-BZ#187 75.0 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl8-BZ#194 15.9 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl8-BZ#195 5.00 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl8-BZ#201 27.7 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl9-BZ#206 15.6 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Cl10-BZ#209 3.29 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Monochlorobiphenyls 0.0803 U ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Dichlorobiphenyls 31.2 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Trichlorobiphenyls 1220 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Tetrachlorobiphenyls 3740 ug/kg 0

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 18 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Pentachlorobiphenyls 2680 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Hexachlorobiphenyls 1070 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Heptachlorobiphenyls 213 ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Octachlorobiphenyls 60.7 ug/kg 06/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Nonachlorobiphenyls 26.8 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Decachlorobiphenyl 3.29 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Total Homologs 9040 ug/kg 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Percent Lipids 9.6 % 6/5/2002 RS-640 COMP 660_661 614620 4765469 2 0209045-06 Percent Moisture 80 % 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl2-BZ#8 0.136 U ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl3-BZ#18 0.206 U ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl3-BZ#28 75.5 ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl3-BZ#31 49.3 ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#44 1.37 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#45 0.111 U ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#47 194 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#49 68.5 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#52 121 ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#56 43.8 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#66 146 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#70 13.8 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#74 118 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#77 12.3 NJ ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl4-BZ#81 0.103 U ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl5-BZ#87 49.3 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl5-BZ#95 18.0 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl5-BZ#99 96.9 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl5-BZ#101 113 J ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl5-BZ#105 65.0 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl5-BZ#110 16.3 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 19 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl5-BZ#114 0.0947 U ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl5-BZ#118 147 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl5-BZ#123 18.0 NJ ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl5-BZ#126 3.60 NJ ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#128 7.90 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#138 165 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#146 34.1 ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#149 37.3 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#151 4.88 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#153 118 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#156 15.5 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#157 2.54 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#158 11.1 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#167 21.2 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl6-BZ#169 4.74 UJ ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl7-BZ#170 24.3 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl7-BZ#174 4.13 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl7-BZ#177 8.61 ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl7-BZ#180 35.5 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl7-BZ#183 9.16 ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl7-BZ#189 0.231 U ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl7-BZ#187 35.8 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl8-BZ#194 6.42 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl8-BZ#195 2.09 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl8-BZ#201 10.5 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl9-BZ#206 4.47 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Cl10-BZ#209 1.26 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Monochlorobiphenyls 0.0780 U ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Dichlorobiphenyls 2.25 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Trichlorobiphenyls 114 ug/kg 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 20 of 21
Northern Rough-winged Swallow (Stelgidopteryx serripennis) Eggs H

The Fresh Weight (Correction for Moisture Loss [CF]) factors were determined by the following equation: Egg Contents Weight (g) / Egg Volume (cm3) = CF CF x Analyte Value = Fresh Weight

Fresh Weight Values 'J' qualified (estimated) if: a) egg contents weight or egg volume were not available, then CF = average of region for species; Or b) CF derived for composited eggs (see Data Report).

SAMPLING 

DATE FIELD ID

EASTING

(NAD 83

UTM 18)

NORTHING

(NAD 83UTM 18) REGION LAB ID ANALYTE1

VALUE AND 

INTERPRETIVE 

QUALIFIER2

(wet weight basis)

D

6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Tetrachlorobiphenyls 844 ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Pentachlorobiphenyls 936 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Hexachlorobiphenyls 494 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Heptachlorobiphenyls 105 ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Octachlorobiphenyls 25.7 ug/kg 06/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Nonachlorobiphenyls 8.25 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Decachlorobiphenyl 1.26 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Total Homologs 2530 ug/kg 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Percent Lipids 7.9 % 6/7/2002 RS-641 COMP 662_665 609404 4741759 3 0209045-07 Percent Moisture 76 % 

 1BZ# = PCB congener Ballschmiter & Zell number 2U = Non-detected result at detection limit

 J/UJ/NJ = Estimated result or detection limit; see Data Quality Assessment Report 21 of 21