Committed 

NMC

to Nuclence Palisades Nuclear Plant

Operated by Nuclear Management Company, LLC

May 10, 2006 10 CFR 50, Appendix I

U. S. Nuclear Regulatory Commission

ATTN: Document Control Desk

Washington, DC 20555-0001

Palisades Nuclear Plant

Docket 50-255

License No. DPR-20

2005 Radiological Environmental Operating Report

Nuclear Management Company, LLC, is submitting the attached Radiological

Environmental Operating Report for the Palisades Nuclear Plant. This report was

prepared in accordance with the requirements of 10 CFR 50, Appendix I, Sections

IV.B.2, IV.B.3, IV.C, and Technical Specification 5.6.2. The period covered by the

enclosed report is January 1, 2005 through December 31, 2005.

Summary of Commitments

This letter contains no new commitments and no revisions to existing commitments.

Paul A Harden

Site Vice President, Palisades Nuclear Plant

Nuclear Management Company, LLC

Enclosure (1)

Attachments (6)

CC Administrator, Region l1l, USNRC

Project Manager, Palisades Nuclear Plant, USNRC

Resident Inspector, Palisades Nuclear Plant, USNRC

27780 Blue Star Memorial Highway * Covert, Michigan 49043-9530

Telephone: 269.764.2000 Rap;
ENCLOSURE 1

ANNUAL RADIOLOGICAL ENVIRONMENTAL OPERATING REPORT

JANUARY 1 THROUGH DECEMBER 31, 2005

TABLE OF CONTENTS

I. INTRODUCTION .................................................. 1

II. NON-ROUTINE REPORTS. 1

III. DISCUSSION AND INTERPRETATION OF RESULTS

A. Air Samples .............................................. 2

B. Lake Water .............................................. 2

C. Drinking Water .............................................. 2

D. Milk .............................................. 3

E. TLDs - Gamma Dose ................... .......................... 3

F. Crops .............................................. 4

G. Sediment .............................................. 4

H. Fish .............................................. 5

I. Broad Leaf Vegetation ....................... ...................... 5

J. Non-Routine Samples .............................................. 5

K. Gaseous and Liquid Radwaste Effluent Composite Samples. 5

IV. ASSESSMENT OF PALISADES OPERATION

ENVIRONMENTAL IMPACT .6

V. TABLES

A. Table 10.4-1 Sampling and Analysis Summary. 7

B. Table 10.4-2 Sample Data Summary. 8

C. Table 10.4-3 Greatest Mean Sampling Location .10

VI. ATTACHMENTS

A. Sample Collection Anomalies

B. Palisades Land Use Census

C. Health Physics Procedure HP 10.10, "Palisades Radiological

Environmental Program Sample Collection and Shipment'

D. Palisades 2005 Final Report - Radiological Environmental Monitoring

Program (REMP) as provided by Environmental, Inc., Midwest Laboratory

E. Environmental, Inc., Midwest Laboratory, Interlaboratory Comparison

Program Results

Page i of ii
TABLE OF CONTENTS (CONTINUED)

F. Data Graphs

1. Palisades Air Particulate (gross beta), Operational Comparison

Graphs, 1968-1969 (pre-op) and 1999-2005

2. Palisades Lake Water (Ludington Control vs. Intake, South Haven

Treated and Raw), 1999-2005 in gross beta trending

3. Palisades TLD (gamma) Palisades Operational Comparison

Graphs, (monthly, quarterly, and annual) 1968-1969 (pre-op

monthly) and 1999-2005

Page ii of ii
I. INTRODUCTION

The Nuclear Management Company, LLC (NMC) Radiological Environmental

Operating Report provides a summary and data interpretation of the Palisades

Nuclear Plant (PNP) Radiological Environmental Monitoring Program as conducted

during the 2005 reporting period. This report was prepared in accordance with the

requirements of 10 CFR 50, Appendix I, Sections IV.B.2, IV.B.3, IV.C, and

Technical Specification 5.6.2.

Detailed sample station identification and location information can be found in

Attachment 2 of Health Physics Procedure HP 10.10, "Palisades Radiological

Environmental Program Sample Collection and Shipment." HP 10.10 is included as

Attachment C. The results of all environmental samples collected are evaluated as

follows:

A. Air iodine and particulate and thermoluminescent dosimetry (TLD) data

were statistically evaluated at the 95% confidence level. The data were

compared against two criteria. The first criterion is the statistical

difference, which indicates whether the sample results from near sites are

greater than those from control sites, and whether or not the difference is

significant (e.g., statistical "T-Test" of indicator vs. control results).

If the T-Test concludes that the control and indicator populations are

statistically different, then the evaluation level (twice the statistical

difference) is computed. This is the minimum difference in the population

means for which a corresponding difference in sample means will exceed

the statistical difference with 95% confidence. If the evaluation level is

exceeded, then correlation of the results with effluent releases is

performed.

B. If a sufficient number of positive sample results were available (e.g., >1

control and >1 indicator) then well water, lake water, sediment, fish, and

other aquatic biota samples were evaluated using data mean

comparisons (e.g., T-Test) and the PNP Offsite Dose Calculation Manual

(ODCM), Appendix A, reporting limits.

II. NON-ROUTINE REPORTS

Non-routine reportable events did not occur during this reporting period.

Page 1 of 10
Ill. DISCUSSION AND INTERPRETATION OF RESULTS

A. Air Samples

There were 260 air samples collected and analyzed for gross beta and

1-131. Air iodine/particulate samples are collected weekly from five airsampling locations. Air is metered into the sampling unit at an

approximate one cubic foot per minute flow rate through a Radeco 47-mm

air filter (air particulate) and a HI-Q air iodine cartridge. Both filters are inline with each other and are housed within the same filter holder. Weekly

samples were sent to Environmental, Inc., Midwest Laboratory for

analysis.

Statistical analysis of the airborne particulate sample data, between the

four near-site indicator locations and the control location, demonstrated

no statistical difference. The mean values of gross beta results for

indicator and control locations were 0.028 pCVm3, and 0.031 pCi/M3,

respectively. The control station 1 0-GR had the highest annual mean for

gross beta results at 0.031 pCiM 3. No trends in gross beta results are

discernable when compared to previous years' sample results.

All 1-131 activity results were below the Minimum Detectable Activity

(MDA) levels.

B. Lake Water (Surface Water)

Palisades lake water inlet (indicator), South Haven Municipal Raw

(indicator) and Ludington (control) lake water inlet water samples were

collected daily and combined into monthly composite samples. One

gallon of Palisades Lake-In (1 -ST) and Ludington Lake-in (32-LP) and two

gallons of South Haven Municipal Raw (25-SH) were sent to

Environmental, Inc., Midwest Laboratory for analysis each month. No

treatment of the water samples with preservative is required. Thirty-six

monthly lake water composite samples collected from the three locations

were analyzed for gross beta and tritium.

No statistical difference was found between the indicator and the control

location samples. In addition, no PNP ODCM Appendix A reporting limits

were exceeded.

C. Drinking Water

Water samples from South Haven Municipal Water System (25-SH

Treated) (indicator), and Ludington Lake-in (32-LP) (control), were

collected daily and combined into monthly composite samples. (The South

Haven municipal water sample is obtained at the PNP site.) One gallon of

Page 2 of 10
Ludington Lake-in and South Haven treated are sent to Environmental,

Inc., Midwest Laboratory for analysis. No treatment of water samples with

preservative is required. Twenty-four monthly drinking water samples

were collected from the two locations and were analyzed for gross beta

and tritium.

No statistical difference was found between the indicator and the control

location samples. In addition, no PNP ODCM Appendix A reporting limits

were exceeded.

D. Milk

Two one-gallon quantities of raw milk (grab sample) are obtained per

sample location per month from dairy milk holding tanks. Each sample

quantity is treated with a sodium bisulfate preservative prior to being sent

to Environmental, Inc., Midwest Laboratory for analysis.

Forty-eight monthly milk samples were collected from the four dairy farms

(stations 26-JH, 27-DH, 28-DC and 29-WS).

No milk analysis identified activity above the minimum detectable level,

with the exception of naturally occurring potassium-40.

E. TLDs - Gamma Dose

Environmental gamma doses are measured quarterly by placement of

TLDs at each designated location. Each TLD badge contains a 4-zone

Calcium Sulfate (CaSO 4) wafer (the wafer includes an additional

backup/reserve readout zone). Sensitivity for the multi-zone TLDs is 10

millirem, with a linear response of 0.1 millirem to 1000 rem.

The PNP gamma assessment program consists of 29 locations. There is

a total of 16 inner ring TLDs, including one on-site, nine near-site and six

steam generator storage facility locations. There are ten outer ring TLD

locations (1.0 to 5.5 miles out) and three control TLDs (30 to 55 miles

out). A 30W TLD is placed in a lead storage cave (location number 22),

and is used as a control for in-transit dose monitoring and subtraction.

There were 116 TLDs collected and analyzed during 2005. The one onsite TLD location (1 -ST) serves as an individual reference TLD; however,

it was evaluated along with the inner ring (site boundary) TLDs in the

statistical evaluation.

The TLD data evaluations were performed by comparing the inner ring

TLDs (site boundary locations 1, 13-21 and 33-38), and the outer ring

Page 3 of 10
TLDs (locations 2-9, 23 and 24), against the control TLD locations (10, 11,

12).

For 2005, the quarterly average gamma readings (mR) were Inner Ring -

12.0, Outer Ring - 14.1 and Control - 15.0.

The highest average dose was observed at outer ring station number 2

(5.6 miles south) with a dose of 17.2 mrem.

Statistical analysis demonstrated that inner ring vs. control TLDs were two

different populations. However, the control mean was greater than the

inner ring mean. There was no statistical difference between the outer

ring and control populations. No trends are discernable when comparing

inner ring with outer ring and control TLD results. Overall, outer ring TLD

mean results are consistently higher than inner ring TLD mean results,

and control station TLD mean results are slightly higher than outer ring

mean results. A likely reason for the lower results seen for the site

perimeter locations is that these TLDs are placed in wooded areas and

thus shielded to some degree from cosmic background radiation. A

comparison made between the Inner Ring TLDs for 2004 and 2005

showed no statistical differences between the two years.

F. Crops

Food crop samples are collected when available, and in season. Two

principal area crops, apples and blueberries, are regularly collected.

Approximately 1 kg of sample is placed in a sealable plastic bag for

shipment to Environmental, Inc., Midwest Laboratory. No special

treatment of the samples with a preservative is necessary.

Four crop samples were collected. Blueberries and apples were collected

at indicator station 4-JS (3.5 miles SE), and at a control station located in

the least prevalent wind direction, approximately 11 miles NNE.

No crop analysis identified activity above the Minimum Detectable Activity

for either 1-131 or gamma emitters.

G. Sediment

Sediment samples are collected semi-annually from each designated

location. No treatment of the samples with a preservative is necessary

prior to shipment to Environmental, Inc., Midwest Laboratory.

Three sediment samples were collected from two locations during 2005.

Two sediment samples were obtained from Palisades, 30-STN (0.5 miles

Page 4 of 10
north of discharge), and one sample from the Ludington Control Station

(32-LP).

No sediment analysis identified activity above the Minimum Detectable

Activity for gamma emitters.

H. Fish

Fish samples are collected semi-annually. Samples consist of two

species of commercially and/or recreational important species near the

PNP discharge area. One sample of the same species in an area not

influenced by plant discharge is collected. Each one-liter quantity of fish

sample is prepared for shipment to Environmental, Inc., Midwest

Laboratory. Each sample is frozen for preservation.

Eight individual fish samples were collected from three locations. Four

indicator samples were obtained from Palisades (1-ST discharge) and

four control samples obtained; three from the Ludington Station (32-LP),

and one from Lake Ontario. The same species were collected at both

indicator and control locations.

Cs-1 37 was the only gamma emitter detected and was seen at both the

indicator and control locations. The values were 0.065 ± 0.028 pCi/g and

0.035 ± 0.020 pCi/g respectively. No trends in Cs-1 37 are discernable

when compared to previous years' sample results. The ODCM reporting

limit for Cs-1 37 is 2000 pCi/kg (2 pCi/gm).

I . Broad Leaf Vegetation

No broad leaf vegetation samples were collected from the surrounding

PNP environs during 2005. The collection of broad leaf vegetation

samples serves as a backup and/or alternative sampling medium in case

any milk sampling location(s) become(s) unavailable.

J. Non-Routine Samples

Non-routine samples were not collected during this reporting period.

I

K. Gaseous and Liquid Radwaste Effluent Composite Samples

Both the gaseous and liquid radwaste effluent composite samples are

collected monthly and sent to Environmental, Inc., Midwest Laboratory for

analysis. No special sample treatment with a preservative is required

prior to laboratory analysis. The liquid effluent composite sample is based

on a specific amount of sample collected, per total batch volume release.

Page 5 of 10
For those months in which there are no liquid batch effluent releases, no

sample is sent to Environmental, Inc., Midwest Laboratory. The gaseous

radwaste effluent weekly composite sample results are based on

analyzing weekly stack gas filters.

Although not a direct reporting component in the PNP Annual Radiological

Environmental Operating Report, results of the gaseous and liquid

monthly radwaste effluent composite samples are evaluated against

overall environmental trending data. This evaluation is the basis for

determining isotopic dispersion and deposition patterns within the

surrounding environs of PNP. All gaseous and liquid effluent results are

compared to the PNP ODCM, Appendix A, reporting levels. All isotopic

lower limits of detection (LLDs) were met.

IV. ASSESSMENT OF PALISADES OPERATION ENVIRONMENTAL IMPACT

In reviewing the 2005 PNP radiological environmental monitoring data, and

comparing it to previous operational and pre-operational data, all trending

parameters continue to indicate that the operation of PNP has minimal

environmental impact. Most isotopic activity is at environmental background

levels. Evidence of an overall environmental isotopic buildup (attributable to

plant effluents) remains negligible as well. In most instances, sample analytical

results were below previously established environmental background levels.

Page 6 of 10
Palisades-Nuclear Plant, Van Buren County. Ml Docket 50-255

Annual Radiological Environmental Operating Report

January 1, 2005 to December 31, 2005

Table HP 10.4-1

Sampling and Analysis Summary

Number of

Collection Samples Frequency of

Medium Description Location Collected Type of Analysis Analysis Continuous at

approximately 1

Air cfm Stations 4, 5, 8, 9 and 10 260 Gross Beta, 1-131 Weekly Lake-in 1 gallon

composite

S.H. Raw 2 gallon Lake Intake and South Haven Gross Beta, Tritium (Tritium not done

Lake Water composite Raw 24 on South Haven Raw) Monthly Lake and

Drinking

Water - Control 1 gallon composite Ludington Lake-in 12 Gross Beta, Tritium, Sr-89 and Sr-90 Monthly

Drinking Water 1 gallon composite South Haven Municipal 12 Gross Beta, Tritium Monthly

Three sites adjacent to Interim

Well Water 2 gallons grab Steam Generator Storage Facility 9 Gross Beta, Tritium Quarterly

W Shine, D Hessey, D Carpenter Gamma isotopic, 1-131 and other

Milk 2 gallons grab & J Hay Dairy Farms 48 isotopic Monthly

TLD Continuous Inner Ring, Outer Ring, Controls 116 Gamma dose Quarterly

At time of

Food Products Grab J Samo and Control 4 Gamma isotopic and 1-131 harvest

Discharge 1/2 mile north of

Sediment Grab Palisades and Ludington Control 3 Gamma isotopic Semiannually

Fish Grab Discharge and Control 8 Gamma isotopic Semiannually

Broadleaf

Vegetation Grab NA - no samples taken

Page 7 of 10
--ralisaaes Nuclear Piant, van Buren Countv. Ml Docket bo-z55

Annual Radiological Environmental Operatina Report

January 1, 2005 to December 31, 2005

Table HP 10.4-2

Sample Data Summary

Medium or Pathwa Type/Total I Lower All Indicator Name l b b Control Number of

amPdway Number of Limit of i Locations iMean Locations REPORTAL

(Unit of Measure) Aaye Deeto M n(fb Of Greatest Mean RneMa(fb OCCURENCES Performed J (LLD) Range j_ ____ Range J_______

1-131 260 0.03 <LLD <LLD 0

Air Particulates

(pCi/m3) Gross B 0.01 0.028 Grand Rapids GR-10 0.031 (52/52) 0.031 (52/52) 0

260 (208/208) 55 miles NNE (0.018 - (0.018 - (0.013 - 0.062) 0.062)

0.062)

Gross 3 36 4.0 1.783 (24/24) South Haven SH-25 1.86 (12/12) 1.775 (12/12) 0

Lake Water (0.9 - 2.8) 51

/2 miles N 0.9 - 2.6 1.1 - 2.9

(pCi/L)

Tritium 36 500 298 (3/12) Ludington LP-32 337 (1/12) 337 (1/12) 0

241 - 397 125 miles N 337 337

Gross B 24 4.0 1.750 (12/12) Ludington LP-32 1.775 (12/12) 1.775 (12/12)

1.1 - 3.0 125 miles N 1.1 - 2.9 1.1 - 2.9

Drinking Water

(pCi/ml) Tritium 24 500 285 (3/12) Ludington LP-32 337 (1/12) 337 (1/12) 0

245 - 322 125 miles N 337 337

Gamma

Spec 48

Milk 1-131 48 1.0 <LLD -- <LLD 0

(pCVL) Cs-1 37 18.0 <LLD <LLD 0

Other 15.0 <LLD -- <LLD 0

Gamma

Inner Ring TLD Gamma 10.0 12.0 (64/64) Kalamazoo ST-11 16.7 (4/4) 12.0 (12/12) 0

(Gamma mR) Dose 76 9.6 - 14.7 35 miles E 15.9 - 17.2 12.3- 17.2

Outer Ring Gamma 10.0 14.1 (40/40) ST-02 17.2 (4/4) 15.0 (12/12) 0

(Gamma mR) Dose 52 11.1 - 18.3 5.6 miles S 15.1 - 18.3 12.3 - 17.2

Page 8 of 10
-

Table HP 10.4-2

Sample Data Summary

Type/Total Lower All Indicator Control

Medium or Pathway Number of Limit of Locations Name Mean (f~b Locations Number of

(Unit of easure)yses Detectiona Mean Distance & Direction Rang Mean RPOCCUR ENCES _________Performed (LLD) Range Range Food Products 1-131 4 0.06 <LLD <LLD 0

Gamma 0.05 - 0.10 <LLD <LLD 0

(pCi/gm wet) Spec 4

Gamma 0.05 to 0.18 <LLD -- <LLD 0

Sediment Spec 3

(pC i/gqm dry)__ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _

Gamma 0.10 to 0.26 0.065 (1/4) Plant Discharge 0.065 (1/4) 0.035 (1/4) 0

Fish Spec 8 0.065 1/2 mile N 0.065 0.035

(pCi/gm wet)

a Nominal Lower Limit of Detection (LLD) as defined in table notation c of Table E-3 of the PNP ODCM

b Mean and range based on detectable measurements only. Fraction of detectable measurements at specific locations is indicated in parenthesis (f)

Page 9 of 10
Table HP 10.4-3

January 1, 2005 to December 31, 2005

Greatest Mean Sampling Location

Medium or

Pathway

Sampled

(unit of

measurement) Type of Analysis Location High Low Mean

Air (pCi/m3) 1-131 NA NA NA NA

____________ Gross Beta GR-10 0.062 0.018 0.031

Lake Water Gross Beta 25-SH SHRAW 2.6 0.9 1.858

(pCVL)

Tritium (d) 32-LP Ludington 337 337 337

Drinking Water Gross Beta 32-LP Ludington 2.9 1.1 1.775

(pCVL)

Tritium 32-LP Ludington 337 337 337

Milk 1-131 NA NA NA NA

(pCiVL) Cs-1 37 NA NA NA NA

Other gamma NA NA NA NA

Inner Ring TLD

(gamma mR) Quarterly (e) ST-11, KZ 17.2 15.9 16.675

Outer Ring TLD

(gamma mR) Quarterly (e) ST-02 Outer Ring 18.3 11.1 17.175

Crops 1-131 NA NA NA NA

pigwe)Other Gamma NA NA NA NA

Sediment

pCigm dry) Gamma Emitters NA NA NA NA

Fish

(pCi/gm wet) Gamma Emitters Discharge 0.065 0.065 0.065

Broadleaf Gross Beta

Vegetation Cs-1 37 NA - no samples taken

Other Gamma

Page 10 of 10
ATTACHMENT A

SAMPLE COLLECTION ANOMALIES

Sample I Location Date Problem Evaluation

Affected

[Fish 1-ST, PNP 4/6/05 Required Sample not shipped to l

discharge LLDs not vendor in time to permit

attained meeting the required LLD.

i IPNP Action Request

I _ 01024272 was initiated.

Air 10-GR 6/1/05 Required LLD Sample not shipped to

(Grand Rapids not attained vendor in time to permit

Control meeting the ODCM

Location) required LLD. PNP

Action Request 01024272 1

_.__ ____ .___. _..__ ______ was initiated..

Air All 2005 Some Vendor Sample not shipped to

Environmental Required vendor in time to permit I

Locations LLDs not meeting the Vendor

Attained required LLD. PNP

Action Request 01028545 i

Lo_____............... _ _ __ _ _ _... _ w as initiated.

Note: Second quarter 2005 steam generator interim storage facility well samples were

not obtained. Although not an ODCM required sample, this information is

included here for completeness of reporting. PNP Action Request 01024275

was initiated.

Page 1 of 1
ATTACHMENT B

PALISADES LAND USE CENSUS

The attached tables contain the results of the Palisades Land Use Census conducted

on August 31, 2005. Table 10.11 -1 references the distance from PNP to the nearest

residence, garden (greater than 500 square feet), beef/dairy cattle, and goats per

meteorological sector. Table 10.11-2 identifies the locations of the nearest residence

and garden; and of all beef/dairy cattle and goats within a five (5) mile radius of PNP

per meteorological sector. Table 10.11-3 lists the critical receptor locations used in

calculation of the offsite doses by the GASPAR computer program. No differences

were identified from the 2004 Land Use Census; therefore no changes were made to

the ODCM. Palisades uses the 1992-1996 meteorological data.

Page 1 of 5
2005 PALISADES LAND USE CENSUS

TABLE 10.11-1

Distance to the nearest residence, garden, dairy/beef cattle and goats in each sector.

SECTOR RESIDENCE

NNE 1.1 mi

NE 1.2 mi

ENE 1.3 mi

E 1.0 mi

ESE 1.0 ml

SE 1.0 mi

SSE 0.7 mi

S 0.5 mi

SSW 0.7 mi

GARDEN

1.7 mi

1.2 mi

1.6 mi

2.1 mi

*1.0 mi

*1.0 mi

1.6 ml

4.0 mi

>5.Omi

BEEF CATTLE

>5 mi

>5 mi

4.0 mi

>5 ml

>5 ml

1.9 mi

>5 mi

>5 mi

>5 mi

DAIRY COW

>5 mi

>5 ml

>5 mi

>5 ml

>5 ml

4.3 mi

>5 ml

>5 mi

>5 mi

GOAT

>5mi

>5 mi

1.8 mi

3.5 ml

>5 ml

1.9 mi

4.8 mi

4.7 mi

>5 mi

* Note: Garden and Farm bisected by ESE/SE boundary line.

Page 2 of 5
2005 PALISADES LAND USE CENSUS

TABLE 10.11-2

Nearest Locations per Sector Within 5 Miles

Sector Location Description Item Number

Comment

NNE

Ruggles Rd

State Park Manager Residence 1

NNE

20th

0.1 mile south of Ruggles Rd SW

corner of 20th and 0 fire lane

Garden 1

NE

Blue Star

Highway

NE

M-43

L. Swetay, Route 3, Box 133 (East

side of highway)

M-43, N side of road, between 12th

and 16th (approximately 0.3 mile

outside of the 5-mile limit

Residence

Garden

Goats

1

1

ENE

24th avenue

Trailer-West 24th avenue, dead end

at sand dune

Residence 1

ENE

24th

ENE

72nd

ENE

76th

SE corner of 76th street and 24th

avenue

72nd St. 0.3 miles N of 20 East side

of road

76th St. 0.3 miles N of 20th East side

of road

Garden

Cattle

1

Beef

Goat

E

77th

E

72nd

E

72nd

E

75th

77th St., dead end of 77th St. near

28th Avenue intersection

C. Mims, 26200 72nd St. intersection

of 72nd & 26 Ave NW corner

72nd St. 0.2 miles N of 26th, W side

of road

27723 75th, 0.1 mile N of 28th (East

side of road)

Residence

Covert Gen Co.

Goats

Garden

Goats

Garden

1

1

1

Page 3 of 5
2005 PALISADES LAND USE CENSUS

TABLE 10.11-2

Nearest Locations per Sector Within 5 Miles

Sector Location Description Item Number

Comment

SE/ESE

28t

SE

36th

SE

76th

SE

767

SSE

SSE

77 1/2

SSE

376th

S

29th Ave

S

CR 376

S

78th

SSW

29th

77550 28th Avenue

72401 36th Avenue, 0.2 mile West

from 72nd, South side of road

SE Corner of 76th and 30th, east side

of road

0.1 mile South of 36th East side of

road

80119 29th Avenue

77 1⁄2/2 St., 0.3 mile N of 32nd Ave,

West side of 77 1/2 St.

376 th, North side of road, 0.3 mile

East of 76th

Palisades Park, 0.5 mile West of

29th Ave and Blue Star Highway

79911 46th Street (CR 376) at 80h

Street intersection

78th, 0.5 mile North of CR 376 west

side of road

29 h Ave, at dead end of Palisades

Park

Residence

Garden

Cattle

Goat

Cattle

Goat

Goat

Residence

Garden

Goat

Residence

Goat

Garden

Residence

1

1

Beef and Dairy

1

1

1

1

1

Page 4 of 5
Distance

Sector Miles

SSE 0.48

S 0.50

2005 PALISADES LAND USE CENSUS

TABLE 10.11-3

Critical Receptor Items

Location/Description Item

Site Boundary N/A

Residence, Palisades Park; Resider

1/2 mile West of 29th

Avenue and Blue Star

intersection.

77550 28th Avenue Garden

SE corner of 76th Street Beef

and 30h Cattle

72401 36th Ave. Dairy

ice

SE 1.0

SE

SE

*XIQ (sec/mr3)

2.13E-06

1.38E-06

5.87E-07

2.32E-07

6.83E-08

2.32E-07

1.9

4.3

Cow

SE 1.9 SE corner of 7 6th Street Goat

and 3 0th

*Based on Palisades 5-year composite meteorological data, 1992 -1996.

Page 5 of 5
ATTACHMENT C

HEALTH PHYSICS PROCEDURE HP 10.10

"PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT"

33 Pages Follow
Procedure No HP 10.10

Revision 9

Effective Date 7/6/05

PALISADES NUCLEAR PLANT

HEALTH PHYSICS PROCEDURE

TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

Approved: JBBurnett l 7/1/05

Procedure Sponsor Date

New Procedure/Revision Summar:

Editorial to Revision 9

Specific Changes
PALISADES NUCLEAR PLANT Proc No HP 10.10

HEALTH PHYSICS PROCEDURE Revision 9

Page i

TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

Table of Contents

1.0 PURPOSE .............................. 1

2.0 REFERENCES ..............................

2.1 SOURCE DOCUMENTS ............................. 1

2.2 REFERENCE DOCUMENTS ............................. 1

3.0 PREREQUISITES ............................. 2

4.0 PRECAUTIONS AND LIMITATIONS ............................. 2

5.0 PROCEDURE .............................. 3

5.1 CONTROL AND OVERSIGHT OF SAMPLING FOR THE

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM ................ 3

5.2 REMP AIR SAMPLE COLLECTION ............................................... 4

5.2.1 Precautions ................................................. 4

5.2.2 Prerequisites ................................................. 4

5.3 REMP LAKE (DRINKING) WATER SAMPLE COLLECTION -

SOUTH HAVEN, MICHIGAN . . 7

5.3.1 Prerequisites .7

5.4 STEAM GENERATOR STORAGE FACILITY MONITORING WELL

WATER SAMPLE COLLECTION (QUARTERLY) . . 8

5.4.1 Prerequisites .8

5.5 REMP MILK SAMPLE COLLECTION .. 8

5.5.1 Precautions .8

5.5.2 Prerequisites .9

5.6 REMP AQUATIC BIOTA COLLECTION . .9

5.6.1 Precautions .9

5.6.2 Prerequisites .10

5.7 REMP SEDIMENT SAMPLE COLLECTION . . 1

5.7.1 Prerequisites .1

5.8 REMP FOOD PRODUCT SAMPLE COLLECTION . . 1

5.9 REMP TLD SAMPLE COLLECTION .12

5.9.1 Prerequisites ........ 12
PALISADES NUCLEAR PLANT Proc No HP 10.10

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TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

Table of Contents

5.10 MISCELLANEOUS SAMPLES .. ............................ 13

5.10.1 Ludington - Control Station .............................. 13

5.10.2 Palisades Daily Samples .............................. 13

6.0 ACCEPTANCE CRITERIA ... ..................... 13

7.0 ATTACHMENTS AND RECORDS ........................ 14

7.1 ATTACHMENTS ........................ 14

7.2 RECORDS ........................ 14

8.0 SPECIAL REVIEWS .......................... 14

ATTACHMENTS

Attachment 1, "Environmental Sample Collection Schedule"

Attachment 2, "Sample Locations"

Attachment 3, "Sample Identification"

Attachment 4, "Sample Packaging and Shipment"

Attachment 5, "Palisades Sample Collection Forms and Records"
PALISADES NUCLEAR PLANT Proc No HP 10.10

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TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

USER ALERT

INFORMATION USE PROCEDURE

The activities covered by this procedure may

be performed from memory.

1.0 PURPOSE

To provide methodology for collection of environmental samples in support of the

Radiological Environmental Monitoring Program (REMP).

2.0 REFERENCES

2.1 SOURCE DOCUMENTS

2.1.1 Reg Guide 4.15(7)

2.1.2 10CFR50, Appendix I

2.1.3 Palisades Administrative Procedure 7.08, "Palisades Radiological Environmental

Monitoring Program"

2.1.4 REMP Sample Shipping Manual, Environmental Inc

2.1.5 Health Physics Procedure HP 10.1, "Radiological Environmental Monitoring Program

Surveillance"

2.1.6 Offsite Dose Calculation Manual (ODCM)

2.1.7 Branch Technical Position (Revision 1, 1979), "Radiological Portion of the

Environmental Monitoring Program"

2.2 REFERENCE DOCUMENTS

2.2.1 Palisades ODCM, Appendix A, Sections III.J, IV.C, and Tables E-1 and E-2

2.2.2 Palisades Administrative Procedure 10.46, "Plant Records"

2.2.3 Palisades Administrative Procedure 10.41, "Procedure and Policy Processes"

2.2.4 Health Physics Procedure HP 6.52, "Palisades (Onsite) Radiological Environmental

Program Sample Collection"

2.2.5 Palisades Administrative Procedure 3.19, "Technical Specifications Programs"
PALISADES NUCLEAR PLANT Proc No HP 10.10

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TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

3.0 PREREQUISITES

As indicated in procedure.

4.0 PRECAUTIONS AND LIMITATIONS

4.1 This procedure shall be applicable to Palisades/Chemistry & Radiation Protection,

Environmental Department, and any contractual personnel assigned to collect or

evaluate REMP samples.

4.2 Any revisions to this procedure shall be reviewed against Palisades ODCM

Specifications to verify compliance to all requirements.

4.3 Deviations from the required sampling schedule shall be documented in the Annual

Radiological Environmental Operating Report.

4.4 Every effort shall be made to complete corrective action on malfunctioning sampling

equipment prior to the end of the next sampling period.

4.5 If it is not possible to obtain the required samples, suitable alternative media and

locations shall be substituted within 30 days.

4.6 Samples shall be collected, prepared, and shipped for analysis in a timely manner to

preserve integrity. Other specific handling precautions for sample media are

indicated in Section 5.0 as required.

4.7 Obtain best available replacement sample for any missing sample. Some samples

are not replaceable (TLDs, air samples, etc), however, water, milk, crop samples,

etc, should be.

4.8 Document any missing samples or malfunctioning equipment on sample data

collection sheets.
PALISADES NUCLEAR PLANT Proc No HP 10.10

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TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

5.0 PROCEDURE

USER ALERT

INFORMATION USE PROCEDURE

The activities covered by this procedure may

be performed from memory.

5.1 CONTROL AND OVERSIGHT OF SAMPLING FOR THE RADIOLOGICAL

ENVIRONMENTAL MONITORING PROGRAM

5.1.1 Sampling techniques described by this procedure must be strictly adhered with.

a. This includes use of tweezers for air sample media change out to ensure the

collected media is not disturbed.

b. Recorded data should be verified including verification of transcribed data to

avoid errors.

c. All deviations from performance requirements, unavailable samples, or other

sampling anomalies must be reported to the C&RP Radiological

Environmental Contact.

5.1.2 Failure of sample collectors to comply with sampling and reporting requirements

may result in remedial training, or reassignment of sampling duties.

5.1.3 The C&RP Radiological Environmental Contact shall conduct periodic (annual)

audits of air sampling activities performed by non-Palisades C&RP personnel.

a. These audits shall include observation of collection techniques, verification of

procedural compliance, and review of equipment condition.

Included in the review of equipment condition, is to ensure that any fast

growing trees and bushes in the vicinity of the station are removed, along with

any branches extending over the top of the sampler. The goal is to keep

every station away from the drip line (with the exception of station 9, which

has an existing canopy 50 feet above the station).

b. Audits should specifically address air sample collection and should include

observation of all individuals involved in sample changeout.
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TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

c. Results of the audits and any follow up action should be documented in the

REMP file.

Collect samples using the following methodology in accordance with schedule and

location data described in Attachments 1 and 2.

5.2 REMP AIR SAMPLE COLLECTION

5.2.1 Precautions

a. New filters and cartridges should be transported and handled such that

potential contamination of them is minimized (ie, placed in clean plastic bags,

etc).

b. If an air sampling unit is discovered not operating, attempt to find the cause

and repair. If this cannot be done, replace applicable component and

document on air sample collection data sheet.

c. Airflow meters shall be calibrated annually by General Meter. All in service

calibrated meters will have affixed a valid calibration sticker/card stating date

of calibration and calibration due date.

d. Airflow meters shall be changed out prior to the expiration of calibration dates.

e. Air station leakage shall be none detectable. If the replacement of air station

components is required due to air leakage, document on air sample collection

data sheet.

5.2.2 Prerequisites

a. Glass fiber (particulate) air filters

b. Charcoal cartridges for iodine sampling (prelabeled for each air sampler)

c. Glassine or plastic envelopes (prelabeled for each air sampler)

d. REMP Air Sample Data Sheet (containing installation data)

e. Replacement air sample meters (as required)

f. Tweezers
PALISADES NUCLEAR PLANT Proc No HP 10.10

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TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

g. Stop Watch

h. Step Ladder

NOTE: The Control Station 1O-GR, is changed out weekly by an independent collector, and

mailed in separately. The prelabeling of cartridges and envelopes, detailed below, is

not required for this station as sample mix-up is not possible. In addition, for control

station, the Palisades Sample Collection Form and Records (Page 1 of

Attachment 5) is completed by the Technician changing out the four local stations by

transferring the recorded data provided by the independent collector.

5.2.3 Perform the following weekly at each sample location:

a. Open the protective cover on the air sample station and verify the sampling

location number written on the inside of the door is the same as the

prelabeled sample change-out package.

b. Verify that the meter serial number and calibration due date are correctly

documented on Palisades Plant Environmental Monitor Operability Check and

Sample Collection data form (Page 1 of Attachment 5).

c. Determine and record the "As Found Flow" rate (seconds for one cubic foot of

volume).

d. Determine and record the "As Found Leak" rate by placing hand over filter

housing inlet to form a seal. While holding hand over the inlet, determine if air

leakage is evident by checking the air flow meter needle for movement

(leakage). If no air leakage, record (N) in the "As Found Leak" column. If air

leakage is indicated, determine the cause and repair as soon as possible.

e. Unplug or turn off the air pump and record the "REMOVED

MONTH/DAY/YEAR," "REMOVED TIME," and "GAS METER READING

REMOVED."

f. Remove the prelabeled charcoal cartridge and place in zip lock bag.

9. Using tweezers, carefully remove particulate filter from the sampler head and

place in the prelabeled glassine envelope or plastic envelope.

h. Clean out any residue or moisture buildup in sampler head before

replacement filter is installed. Check the condition of the sampler head

o-rings. Replace cracked 0-rings as necessary to prevent air leakage.
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TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

i. Install new particulate filter and charcoal cartridge and ensure that both are

properly centered in sampler head to prevent air leakage. Ensure the fiber

side of the particulate filter is facing out (smooth side facing inward).

j. Restart air pump. Place hand over the filter housing inlet to form a seal,

determine if air leakage is evident by checking air flow meter needle

movement. If no air leakage, record (N) in the "As Left Leak" column. If air

leakage indicated, determine the cause of the leakage (filter not centered in

holder properly or cracked o-ring) and correct problem as soon as possible,

restoring system to no air leakage.

k. Determine and record "As Left" flow rate. If greater than 90 seconds are

required for one cubic foot of volume, the sample pump is degrading.

Replace pump as soon as possible to avoid failure to reach minimum sample

volume. (5000 ft3).

1. If an airflow meter must be replaced, record this in the "Comments" column.

Record replacement meter data in the reading on the upcoming week's

sample collection data sheet.

m. Close the protective cover on the air sample station.

n. Proceed to the next station. Date and sign the current week's data sheet

upon completion of the entry of all current data.

o. Calculate and record "SAMPLE VOL (FT3)," ALSO ensure all pertinent data

is recorded.

p. Transcribe the "REMOVED MONTHIDAYNYR" and "GAS METER READING

REMOVED" taken in Step 5.2.3e to the "INSTALLED" reading columns on the

sample collection sheet to be used for the upcoming week's air sample

collection. Also transcribe the meter serial number and calibration due date

to the upcoming week's sample collection sheet.
PALISADES NUCLEAR PLANT Proc No HP 10.10

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TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

5.3 REMP LAKE (DRINKING) WATER SAMPLE COLLECTION -

SOUTH HAVEN, MICHIGAN

5.3.1 Prerequisites

a. Two clean, one-gallon plastic containers labeled with sample type, location,

amount, and date (or collection period)

b. Data Sheet (Attachment 3)

5.3.2 Perform the following sample collection monthly:

a. Leave two containers with the plant personnel at the South Haven Municipal

Water Treatment Plant. New water sample containers should be left at the

South Haven Water Treatment Plant upon pickup of end-of-month composite

samples.

b. Instruct the plant personnel to add approximately 300 ml per day of raw water

to containers labeled "RAW."

c. Retum at end of month to collect containers. Obtain verbal verification that

Step 5.3.2b was carried out. Note any deviations in "Remarks" column of

data sheet.

d. Label containers with sample type, location, and collection period.

e. Package and ship samples per Attachment 4.

f. Record location, sample types, and amount on sample identification data

sheet (Attachment 3).
PALISADES NUCLEAR PLANT Proc No HP 10.10

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SAMPLE COLLECTION AND SHIPMENT

5.4 STEAM GENERATOR STORAGE FACILITY MONITORING WELL WATER

SAMPLE COLLECTION (QUARTERLY)

5.4.1 Prerequisites

a. Clean, one-gallon plastic containers

b. Data Sheet (Attachment 3)

5.4.2 Perform the following sample collection quarterly:

a. Begin pumping water, and allow water to run for approximately one minute to

purge the lines.

b. Fill two clean, one-gallon plastic containers with well water from each sample

location.

c. Label containers with sample type, location, and collection date.

d. Package and ship samples per Attachment 4.

e. Record on data sheet location, type, date, amount, and under "Remarks" any

pertinent information.

5.5 REMP MILK SAMPLE COLLECTION

5.5.1 Precautions

a. Milk samples shall be sent to the laboratory as soon as possible because of

the short half-life of 1-131. Any undue delay may cause ODCM, Appendix A,

Table E-3 analytical LLD requirements to be violated.

b. Obtain best available replacement sample for any missing milk sample(s).

Identify new sample location(s) and update location in Attachment 2.

c. If milk samples are unavailable, then samples of three different kinds of broad

leaf vegetation grown nearest to Palisades in each of two different offsite

locations of the highest predicted average ground level D/Q (SE or SSE

sectors near site), and one sample of each kind of similar broad leaf

vegetation grown 15-30 km distant from Palisades in the least prevalent wind

direction (NNE, NE or ENE sectors) may be used as replacement samples.

The new sample locations shall be identified and the REMP procedures

revised within 30 days to reflect sampling changes. Collect approximately

one kilogram (2.2 lb) of each sample type.
PALISADES NUCLEAR PLANT Proc No HP 10.10

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SAMPLE COLLECTION AND SHIPMENT

5.5.2 Prerequisites

a. Two clean, plastic one-gallon containers for each sample location

b. Sodium bisulfite preservative (approximately 40 gm per gallon of milk

required)

c. Data Sheet (Attachment 3)

5.5.3 Perform the following monthly at each specified sample collection location:

a. Obtain two one-gallon grab samples of raw milk as specified in Attachments 1

and 2.

b. Add approximately 40 gm of sodium bisulfite to each one-gallon container of

milk and thoroughly mix. The sodium bisulfite can either be in prepared

packets or "scooped" with a volumetric measure from its container.

c. Label containers with sample type, location, and date.

d. Package and ship samples as per Attachment 4.

e. Record on Sample Data Sheet, the location, type, date, and amount of

samples. Under "Remarks," note any other pertinent information.

5.6 REMP AQUATIC BIOTA COLLECTION

5.6.1 Precautions

a. Collection to be coordinated between Radiological Services Department

responsible Section and the Environmental Department. At least one

individual in the collection party is required to have Michigan Department of

Environmental Quality (MDEQ) Cultural and Scientific Fish Collectors Permit

if gill net is used.

b. If logistical problems prevent use of a boat to set gill nets from the lake side of

Palisades, then the nets can be set offshore from the site boundary (by

wading). Notify Security prior to using offshore wading method for beach

access.
PALISADES NUCLEAR PLANT Proc No HP 10.10

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SAMPLE COLLECTION AND SHIPMENT

5.6.2 Prerequisites

a. Boat with required safety equipment, or waders

b. Gill nets with weights and floats

c. Plastic one-liter wide-mouth bottles

d. Data Sheet (Attachment 3)

e. Fillet knives

f. Black permanent felt markers for sample identification on containers

g. Notify district MDEQ Fisheries biologist prior to sample collection

5.6.3 Collect samples twice during the season of greatest abundance (typically May

through October) as follows:

a. Gill nets are placed at the locations specified in Attachment I to collect at

least two species of commercially and/or recreationally important fish in the

vicinity of the Plant discharge area and the same species in an area not

influenced by the Plant discharge (Ludington Pump Storage Plant or other

Consumers Energy facility). One liter of flesh should be collected for each

species caught for analysis accuracy.

b. Normally fish will be collected first from the vicinity of the discharge. REMP

coordinator will then collect at least two of the same species at Ludington

(control station). Or REMP coordinator will provide the Ludington collector

with a list of the species collected in the vicinity of the discharge, with

instructions to collect at least two of the same species.

c. Label all containers with sample type, location, and date.

d. Package and ship samples per Attachment 4.

e. Record on data sheet location, type, date, amount, and under "Remarks"

indicate any pertinent information.
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SAMPLE COLLECTION AND SHIPMENT

5.7 REMP SEDIMENT SAMPLE COLLECTION

5.7.1 Prerequisites

a. One-liter, wide-mouth plastic sample bottles

b. Data Sheet (Attachment 3)

5.7.2 Collect sediment samples semiannually at station 30, 0.5 miles north of discharge,

and a control sample at the Ludington Pump Storage Plant.

a. Label containers with sample type, location, and date.

b. Package and ship samples per Attachment 4.

c. Record on Sample Data Sheet location, type, date, and amount of sample.

Note any other pertinent information in the "Remarks" section.

5.8 REMP FOOD PRODUCT SAMPLE COLLECTION

a. Sample containers

b. Data Sheet (Attachment 3)

5.8.1 Collect food samples monthly during the harvest season, as per ODCM, Appendix A,

Table E-1. One sample each of the two principal fruit crops blueberries and apples

must be collected.

a. Collect approximately one kilogram (2.2 lb) of each sample type. Samples

are not to be washed, shaken, or cleaned. Samples should not be collected

from a single source, but at random from the entire orchard or field.

b. Label all containers with sample type, location, and date.

c. Package and ship samples per Attachment 4.

d. Record on data sheet location, type, date, amount, and under "Remarks" note

any unusual conditions.
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SAMPLE COLLECTION AND SHIPMENT

5.9 REMP TLD SAMPLE COLLECTION

5.9.1 Prerequisites

a. TLDs

b. TLD Data Sheet (Attachment 5)

5.9.2 Quarterly at each sample location perform the following:

a. Upon receipt of TLDs from the laboratory contractor, all TLDs shall be

inventoried and immediately placed in the lead cave. Note date of receipt and

inventory on TLD data sheet.

b. Field TLDs shall only be removed from the lead cave for delivery to their

proper locations. All control TLDs remain in the lead cave throughout the

entire exposure period.

c. Remove and replace TLDs at each sample location.

d. For any missing TLDs, perform the following:

1. Search immediate area.

2. If lost TLD is found, collect it and perform standard change out

procedure.

3. If lost TLD is not found, post the new TLD in proper location.

4. Record in "Remarks" column of data sheet any of the above

circumstances.

e. Store collected field TLDs in lead cave along with control TLDs until ready for

mailing to laboratory contractor. Mark "Do not x-ray" on TLD package.

f. Transportation control TLDs (Shield TLDs) are to be stored in a special lead

shield provided by laboratory contractor after the field TLDs are posted.

Ensure that designated transportation control TLDs are included with the

correct TLD package being mailed to laboratory contractor. Also ensure that

laboratory contractor's TLD data sheet is completed and enclosed with

shipment.
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TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

g. Record TLD collection date and the date that the TLDs are returned to the

vendor. Initial/sign the data sheet (Attachment 5). Record the installation

date for the new TLDs on the appropriate data sheet.

h. Package and ship samples per Attachment 4.

5.10 MISCELLANEOUS SAMPLES

5.10.1 Ludington - Control Station

NOTE: Sediment samples are also collected at Ludington Pump Storage Plant per

Section 5.7 of this procedure.

a. Ludington Lake In composites are collected daily and shipped to Palisades on

a monthly basis.

b. Palisades RETS/REMP personnel record appropriate data on the Sample

Data Sheet for shipment to Environmental Inc.

5.10.2 Palisades Daily Samples

a. Palisades Lake In, Lake Out, Site Water, Service Water, and Turbine Sump

effluent samples are collected on a daily basis per Palisades per Health

Physics Procedure HP 6.52, "Palisades (Onsite) Radiological Environmental

Program Sample Collection."

b. Palisades RETS/REMP personnel record appropriate data on the Sample

Data Sheet and label all samples.

6.0 ACCEPTANCE CRITERIA

Proper completion of procedure.
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TITLE: PALISADES RADIOLOGICAL ENVIRONMENTAL PROGRAM

SAMPLE COLLECTION AND SHIPMENT

7.0 ATTACHMENTS AND RECORDS

7.1 ATTACHMENTS

7.1.1 Attachment 1, "Environmental Sample Collection Schedule"

7.1.2 Attachment 2, "Sample Locations"

7.1.3 Attachment 3, "Sample Identification"

7.1.4 Attachment 4, "Sample Packaging and Shipment"

7.1.5 Attachment 5, "Palisades Sample Collection Forms and Records"

7.2 RECORDS

7.2.1 Distribution of Sample Collection Data Sheet as per Attachment 4.

7.2.2 All Radiological Environmental Monitoring Program Records shall be considered

complete when the Annual Radiological Environmental Operating Report is

submitted to the NRC. Records shall be retained in accordance with Palisades

Administrative Procedure 10.46, "Plant Records."

8.0 SPECIAL REVIEWS

The scope of this procedure includes activities that require a PRC Review per

Palisades Administrative Procedure 3.19, "Technical Specifications Programs," but

do not require a 50.59 Review per Palisades Administrative Procedure 10.41,

"Procedure and Policy Processes." Therefore, changes to this procedure require a

PRC Review but do not require a 50.59 Review.
Proc No HP 10.10

ENVIRONMENTAL SAMPLE COLLECTION SCHEDULE Attachment I

Revision 9

Palisades Nuclear Plant Page 1 of 2

Exposure Pathway

and/or Sample

Number of Samples

and Locations*

Collection

Sample Tvpe Frequency

Airborne:

Particulates

4 -Within a 10 km

- Radius

1 - 25 to 89 km Distant

Continuous at

approximately

1 cfm (may be less

due to dust

loading)

Weekly

lodines Same as Particulates Same as

particulates

Weekly

Waterborne:

Lake Water

1 - Intake

1 - Intake (Ludington

Control)

Daily composite to

obtain a

one-gallon sample

Monthly

Drinking

Water

1 - S Haven Municipal

System - Raw

1 - Domestic Water

Well Water **3 - Plant Site Locations Two-gallon grab

sample

Quarterly I

Sediment 1 - 0.8 km North of

discharge

1 - Ludington control

One-liter grab

sample

Semiannually

I

**These are monitoring wells of the groundwater for the Steam Generator Storage

Facility, this is not part of the environmental sampling program.

*If samples are unavailable at the specified location, an attempt should be made to

sample at an alternate location (refer to Step 4.5).
Proc No HP 10.10

ENVIRONMENTAL SAMPLE COLLECTION SCHEDULE Attachment I

Revision 9

Palisades Nuclear Plant Page 2 of 2

Exposure Pathway

and/or Sample

Number of Samples

and Locations*

Collection

Sample Tvpe Frequencv

NOTE: Currently there are no dairy farms within a distance of 5 to 8 km from the

Plant. However, milk samples will be obtained at 3 locations within a distance

of 15 km when available. When milk samples are collected, broad leaf

vegetation sampling is not required.

Ingestion:

Milk

3 - From 5 to 8 km

1 - Control from

15 to 30 km

Two-gallon grab

sample

Monthly

Food Products 1 - Each of two principal

fruit crops

(blueberries and

apples).

Two-pound grab

sample

At time of

harvest

Fish 2 - Location in vicinity of

Plant discharge

2 - Ludington control

or other CMS Energy

facility

I -Onsite

16 - Site boundary

9 -Within 12 km radius

3 -Control stations

1 -Control in lead cave

One-liter fish flesh

from each

available species,

two species

required. Obtain

the same species

from the control

location.

Continuous

Twice in

season

Direct:

TLD

Quarterly I

*If samples are unavailable at the specified location, an attempt should be made to

sample at an alternate location (refer to Step 4.5).
-

Proc No HP 10.10

Attachment 2

Revision 9

SAMPLE LOCATIONS Page 1 of 9

Palisades Nuclear Plant

Air Air Lake Well Food

Station Code Location Particulates Iodine Water Water Milk Products Sediment TLD Fish

*1 ST Palisades Nudear Plant Onsite, on tree near nw comer of X x x

bag crew bldg.

2 TH RR 3 TLD located on 80th Street, west X

Coloma, Ml side on post, 200 feet south of the

5.6 miles S old air sample station.

3 HS 76182 48th Ave Along 48th Ave. 1/4 mile west of X

Covert, Ml 76th St. In barnyard 50 yds off north

5.8 miles SSE side of road.

4 JS 36197 M-140 Hwy Along 36th Ave, 1/2 mile east of X X X X

Covert, Ml M-140 15 It off south side of road.

3-1/2 miles SE TLD located in front yard of

residence.

5 PR 72723 CR 378 Along CR 378, 314 mile east of X X X

Covert, Ml M-140, 30 I off north side of road.

3-1/2 miles ESE TLD located at Paul Rood residence,

on tree in back yard just past

driveway.

6 RB RR 3 Along 12th Ave (CR 384), turn nw X

South Haven, Ml past maple grove, go 1/4 mile

4-1/2 miles NE located in orchard on north side of

road.

7a SN21 Emergency Siren 21 On Monroe Blvd, at comer of 11th X

4.1 miles NNE Street.

8 SP State Park Onsite along the dump road, north of X X X

1 mile N Plant. One mile from main gate.

Near State Park boundary, on side

of road as road turns west.

9 TP Covert Township Park Along 32nd Ave, 1/4 mile west of X X x

1.5 miles SSW Blue Star Hwy. 5 ft off south side of

road. TLD located at end of road, at

entrance to HSamo residence,

attached to emergency siren SN38.

10 GR Grand Rapids, Ml Grand Rapids Service Center, in X X X

55 miles NNE storage area. Air sample on west

side near shed. Control TLD

100 feet north of air sample station.

I

I

I

I
Proc No HP 10.10

Attachment 2

Revision 9

SAMPLE LOCATIONS Page 2 of 9

Palisades Nuclear Plant

Air Air Lake Well Food Station Code Location Particulates Iodine Water Water Milk Products Sediment TLD Fish

11 KZ Kalamazoo, Ml Kalamazoo Service Center, in X 35 miles E parking area on post in SE corner Control TLD.

12 DG Dowagiac, Ml TLD located at first farm past old air X 30 miles SSE sampler station, same side of road.

13 ST Perimeter of Palisades Past #8 along dump road. Proceed X

NNE west up dune path at right of

containment test structure. At first

crest, turn north and proceed up

adjacent hill to #13 at top (approx

50 yds from crest). Near State Park

fence line.

14 ST Perimeter of Palisades Along dump road to point where X

fence divides old Blue Star Hwy, NE 25 yds to east of road.

15 ST Perimeter of Palisades North along Blue Star Hwy, X

E 0.75 miles from access road, 10 ft

off west side of road.

16 ST Perimeter of Palisades North along Blue Star Hwy, 0.4 miles X

E from access road, 50 ft off west side

of road.

17 ST Perimeter of Palisades Along access road, 25 yds south of X

ESE southern power line, 15 yds off east side of road.

18 ST Perimeter of Palisades 20 yds from access road along south X

SE road. 40 yds off south road.

19 ST Perimeter of Palisades 0.2 miles along south road from X

SSE access road, 30 ft off north side of road.

20 ST Perimeter of Palisades 0.4 miles along south road from X S access road, 20 ft off south side of

road.

21 ST Perimeter of Palisades 0.7 miles along south road from X

SSW access road. 5 ft off east side of road. Near Lake Michigan Bluff.
Proc No HP IO.-IO

Attachment 2

Revision 9

SAMPLE LOCATIONS Page 3 of 9

Palisades Nuclear Plant

Air Air Lake Well Food Station Code Location Particulates Iodine Water Water Milk Products Sediment TLD Fish

22 MG Mike Grogan Control TLD in lead cave inside X 13 miles SSW garage at RETS/REMP residence.

23 SN19 Emergency On CR 380. x Siren 19

3 miles ENE

24 SN26 Emergency On 67th Street. X Siren 26

6 miles E

25 SH South Haven, Ml South Haven Water Treatment X

5-1/2 miles NNE Plant.

26 JH Joseph Hay X

41799 CR 681

Bangor, Ml

11.4 miles ESE

27 DH Dennis Hessey X

26959 66th St

South Haven, Ml

6.6 miles E

28 DC Danny Carpenter X

64015 M-43

Bangor, Ml

7.25 miles E

29 WS William Shine X

60364 M-43 West

Bangor, Ml

8.7 miles E

30 STN 1/2 mile N of discharge X

32 LP Ludington Pumped X X X Storage 125 Miles N

33 ST Perimeter of Palisades Onsite along south side dump road, X NE just 15 yards west of Air Station

8SP.

I
- - -

Proc No HP 10.10

Attachment 2

Revision 9

SAMPLE LOCATIONS Page 4 of 9

Palisades Nuclear Plant

Air Air Lake Well Food Station Code Location Particulates Iodine Water Water Milk Products Sediment TLD Fish

34 ST Perimeter of Palisades Along dump road to area where X NE fence divides old Blue Star Hwy, 25

yards east of road, near Station 14.

35 ST Perimeter of Palisades Located on the main post directly X ENE across the storeroom, near Training Building.

36 ST Perimeter of Palisades North along Blue Star Hwy, 0.9 miles X ENE from access road, 50 Ft off west side

of road.

37 ST Perimeter of Palisades North along Blue Star Hwy, 0.6 miles X E from access road, 50 Ft off west side

of road.

38 ST Perimeter of Palisades North along Blue Star Hwy, X SE 0.15 miles from access road, near

old RR spur, 50 Ft off west side of

road.

41 ST Plant Site Monitoring X

Well #14

42 ST Plant Site Monitoring X

Well #15

43 ST Plant Site Monitoring X

Well #16

44 CN Control Station 11-12 miles, NNE of Plant, used as X NNE control station for crops.
i I

Lus

(m2

20

.4.

* zi

= C

ID Ci

cl of) = Z

o = '

% D
Proc No HP 10.10

Attachment 2

Revision 9

Page 6 of 9

SAMPLE LOCATION

Palisades Nuclear Plant

NOT SHOWN (Control Locations)

10 Grand Rapids (55 mi NNE) 11 Kalamazoo (35 miiEL

12 Dowagiac (30 mi St) 22 Control TLD placed in lead cave off site

26 Joe Hay (JH - 11.4 mli ESE)
SAMPLE LOCATIONS

Palisades Nuclear Plant

Proc No HP 10.10

Attachment 

2

Revision 

9

Page 7 of 

9
Proc No HP 10.10

Attachment 2

Revision 9

Page 8 of 9

REMP SAMPLING

NO

NO

NO

NO

NO

NO

NUMBER

#1

#2

#3

#4

#5

#6

NO

NO

NO

NO

NO

#7

SI

Pa

WELL STATUS

Abandon

Abandon

Abandon

Abandon

Abandon

Active

Abandon

Abandon

Abandon

Abandon

Abandon

Abandon

Abandon

Active

Active

Active

AMPLE LOCATIONS

lisades Nuclear Plant

LOCATION

NA

North side of Support Building. Supports Plant site.

Across from East-Radwaste (South Side) backup for well #2.

NA

NA

Located - 145 ft west of Blue Star Hwy. Used for training trailers,

well capped when not in service and well is outside of Westerly

Groundwater Flow to Plant and interim storage facility.

Just to the west & between outage building and interim storage

facility: Water is nonpotable and used in warehouse restrooms (later

to be used for fire system only).

NA

Located at junction of access and warehouse road, domestic water

supply for warehouse when it is put in service.

NA

North of access road and east of construction road,

supplies domestic water for outage building, all

in one tie-in.

East of Interim Storage Facility, used for REMP monitoring well.

Southwest of Interim Storage Facility, used for REMP monitoring well.

Northwest of Interim Storage Facility, used for REMP monitoring well.

#8

#9

#10

#11

#12

#13

#14

#15

#16

YES

YES

YES
- SAMPLE LOCATIONS

Palisades Nuclear Plant

Proc No HP 10.10

Aftachment 2

Revision 9

Page 9 of 9

/

WEST

,4. 12'60

515fl

#15

+

/

#16

164 80'

29'

a- 129'4"

110 '

;m-- -

+ I

-;PROPOS MUMOOR

-(WEL WOCATKM

#14
Proc No HP 10.10

Attachment 3

Revision 9

SAMPLE IDENTIFICATION Page 1 of 2

Date:

Collector:

_ PLANT

Miscellaneous Radiological Environmental Samples

SAMPLE

Li DATE TIME AMOUNT REMARKS , Location j Type-

_ __ _I

I I=

.I I I I I

+ 4 4 4.

4. 4 4 4 4

4. 4. 4. 4. 4

I _____ I

I 4- 4. 4. I

9 4 4. 4. 9

=__ _I
Proc No HP 10.10

Attachment 3

Revision 9

SAMPLE IDENTIFICATION Page 2 of 2

PALISADES PLANT

Miscellaneous Radiological Environmental Samples

Date Shipped:

Location Type Date Time Amount Remarks

Allen Karr Milk 2 Gallons

Danny Carpenter Milk 2 Gallons

Dennis Hessey Milk 2 Gallons

William Shine Milk 2 Gallons

Monthly

South Haven Raw Water Composite - NA 2 Gallons

Site #14 Well Water 2 Gallons

Site #15 Well Water 2 Gallons

Site #16 Well Water 2 Gallons

Monthly

Lake In Plant Water Composite - NA 1 Gallon

Monthly

Service Water Plant Water Composite - NA 1 Gallon

Monthly

Plant Drinking Plant Water Composite - NA 1 Gallon

Water

Control Monthly

udington Lake Sample Composite - NA 1 Gallon
Proc No HP 10.10

Aftachment 4

Revision 9

Page 1 of I

SAMPLE PACKAGING AND SHIPMENT

1. Label samples clearly per Attachment 3.

2. Seal all liquid, biota, fish, and sediment sample containers with tape to prevent

leakage.

3. Ship liquid samples separately from air particulate and air iodine samples and TLDs.

4. Use sufficient packing material (ie, crumpled newspaper) to avoid possible sample

container damage during shipment.

5. Package air filters in glassine or plastic envelopes.

6. For TLD shipments, make sure that laboratory contractor's own TLD data sheet is

enclosed with package.

7. Ship milk samples as soon as possible. Be sure to add a sufficient amount of

sodium bisulfite (40 grams) as preservative to each sample.

8. Ship food products as soon as possible after collection.

9. Ship fish frozen or packed in ice, or with a 10% formaldehyde solution added

(preservative). Only 10 milliliters is required per sample. Samples should be

shipped as soon as possible after processing.

10. Distribute copies of the Sample Collection Data Sheet(s) to the:

Analytical Laboratory

Radiological Services Department Environmental Contact (Palisades)

11. Send samples to the following address:

Environmental Inc.

Att: Laboratory Manager

700 Landwehr Road

Northbrook, IL 60062

12. Ship all samples to the laboratory contractor with minimal delay after collection so as

to avoid elevated analytical levels of detection.
Proc No HP 10.10

Attachment 5

Revision 9

PALISADES SAMPLE COLLECTION FORMS AND RECORDiS Page I of 2

PALISADES PLANT

ENVIRONMENTAL MONITOR OPERABILITY CHECK

AND SAMPLE COLLECTION

F 1r *1

REPLACEMENT METER

INSTALLED I REMOVED

(MO/DA/YR) (MOIDAIYR)

REMOVED

TIME

GAS METER READING

INSTALLED I REMOVED

(Ft 3) (Ft 3)

METER

SERIAL

NO

CAL

DUE

DATE

AS FOUND

FLOW I LEAK

(SEClFt3) (Y/N)

AS LEFT

FLOW I LEAK

(SEClFt3) (Y/N)

SERIAL

NUMBER

CAL DUE

DATE

FLOW TEST

CALIB

ACCURACY

ACCEPTABLE

SAMPLE

VOL

(Ft 3) COMMENTS

4JS

5PR

8SP

9TP

10OGR

TEST PERFORMED BY:

REVIEWED BY:

DATE:_

_DATE:
PALISADES SAMPLE COLLECTION FORMS

AND RECORDS

Proc No HP 10.10

Attachment 5

Revision 9

Page 2 of 2

CONSUMERS ENERGY

PALISADES ENVIRONMENTAL TLD REPORT [1 QUARTERLY I

Collector

STATION - LOCATION INSTALLED COLLECTED

DATE TIME DATE TIME REMARKS

C -I1_ _ _ _ _ _ _ _ _ _ _ _ _

C -2_ _ _ _ _ _ _ _ _ _ _ _ _ _ _

STI ST__ _ _ _ __ _ _ _

ST2 TH

ST3 HS_____

ST4 JS

ST5 PR

ST6 RB_

ST7a SN21

ST8 SP

ST9 TP_

STIO GR ____

ST11 KZ =_===

ST12 DG

ST13 ST

ST14 ST

ST15 ST

ST16 ST

ST17 ST

ST18 STN19

ST19 ST

ST20 ST

ST21 ST

ST22 CVS _ _ _ _ _ _ _ __ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _

ST23 SN19R _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _

ST24 SN26_____

ST-33 ST _ _ _ _ _ _ _ _

ST-34 ST_____

ST-35 ST_____

ST-36 ST _ _ _ _ _ _ _ _

ST-37 ST _ _ _ _ _ _ _ _

ST-38 ST _

SH-1, SH-2 SH

Date Received From Vendor (With Intransit Date TLDs Inventoried and Placed in Lead Date TLDs Returned to Vendor For

TL-Ds) and Initials Cave (With Intransit TI-Ds) and Initials Analysis (With Intransit TLDs) and _____________________________________________________________________Initials
ATTACHMENT D

PALISADES FINAL REPORT

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (REMP)

AS PROVIDED BY ENVIRONMENTAL, INC, MIDWEST LABORATORY

31 Pages Follow
-~ Environmental, Inc.

Midwest Laboratory

an Allegheny Technologles Co.

700 Landwehr Road * Northbrook, IL 60062-2310

(847) 564-0700 fax (847' 564-4517

FINAL REPORT

TO

CONSUMERS ENERGY COMPANY

JACKSON, MICHIGAN

RADIOLOGICAL ENVIRONMENTAL MONITORING PROGRAM (REMP)

FOR

PALISADES NUCLEAR GENERATING PLANT

PREPARED AND SUBMITTED

BY

ENVIRONMENTAL INCORPORATED MIDWEST LABORATORY

Project Number: 8022

Reporting Period: January-December, 2005

Reviewed and

Approved by _ Date 02-0 o-20A

Distribution: J. Burnett (1 copy)
PALISADES

TABLE OF CONTENTS

Section Page

List of Tables.ii

1.0 INTRODUCTION ................................... iv

2.0 LISTING OF MISSED SAMPLES ................................. v

Appendices

A Interlaboratory Comparison Program Results ................................... A-1

B Data Reporting Conventions ................................... B-1

C Special Analyses ................................. C-1

ii
PALISADES

LIST OF TABLES

No. Page

I Airborne Particulates and Iodine-131

Location 4JS .............................................. 1-4

Location 5PR .............................................. 1-5

Location 8SP................................................................................................... 1-6

Location 9TP .............................................. 1-7

Location IOGR .............................................. 1-8

2 Gamma Radiation, as Measured by TLDs, Quarterly Exposure ........................ ......... 2-1

3 Lake Water, Intake and South Haven (Raw) .............................................. 3-1

4 Well Water, Palisades Drinking Water .............................................. 4-1

5 Well Water, Quarterly .............................................. 5-1

6 Water, Ludington controls .............................................. 6-1

7 In-Plant Water .............................................. 7-1

8 Milk .............................................. 8-1

9 Food Crops .............................................. 9-1

10 Fish..........................................................................................................1.0................. 10-1

11 Bottom Sediments ............ 11-1

12 Special Samples

12.1 Liquid Radwaste............................................................................................4+1-1

12.2 Stack Filters...................................................................................................4.2-1

I'7-,

iii
1.0 INTRODUCTION

The following constitutes the final 2005 Monthly Progress Report for the Radiological

Environmental Monitoring Program conducted at the Consumers Energy Company, Palisades

Nuclear Generating Plant. Results of completed analyses are presented in the attached tables.

For all gamma isotopic analyses, spectrum is computer scanned from 80 to 2048 KeV.

Specifically included are Mn-54, Fe-59, Co-58, Co-60, Zn-65, Zr-95, Nb-95,1-131, Ba-La-140,

Cs-134 and Cs-137. Naturally-occuring gamma-emitters, such as K-40 and Ra daughters, are

frequently detected but not listed here. Data listed as n<" are at the 4.66 sigma level, others are

2 sigma.

All concentrations, except gross alpha and gross beta, are decay corrected to the time of

collection.

All samples were collected within the scheduled period unless noted otherwise in the Listing

of Missed Samples.

iv
PALISADES

2.0 LISTING OF MISSED SAMPLES

Expected

Sample Type Location Collection Date Reason

LW

WW

LW

LW

LW

LW

WW

WW

LW

LW

LW

LW

WW

LW

LW

LW

WW

LW

LW

Ludington

South Haven

Treated

Ludington

Inlet

Intake

South Haven

Raw

South Haven

Treated

#14, 15, 16

Ludington

Ludington

Intake

South Haven

Raw

South Haven

Treated

Ludington

Intake

South Haven

Raw

South Haven

Treated

Ludington

March

April

April

April

June

June

June

2nd Qtr.

June

July

August

August

August

August

September

September

September

September

Sample not received.

(Sample received 06-08-05)

Sample not received.

(Sample received 06-08-05)

Sample not received.

(Sample received 06-08-05)

Sample not received.

(Sample received 06-08-05)

Sample not received.

(Sample received 08-05-05)

Sample not received.

(Sample received 08-11-05)

Sample not received.

(Sample received 08-05-05)

Sample not received.

Sample not received.

(Sample received 08-05-05)

Sample not received.

(Sample received 09-29-05)

Sample not received.

(Sample received 09-29-05)

Sample not received.

(Sample received 09-29-05)

Sample not received.

(Sample received 09-29-05)

Sample not received.

(Sample received 09-29-05)

Sample not received.

(Sample received 10-27-05)

Sample not received.

(Sample received 10-27-05)

Sample not received.

(Sample received 10-27-05)

Sample not received.

(Sample received 10-27-05)

Sample not received.

(Sample received 01-12-06.)

Ludington November

v
PALISADES

Table 1. Airbome particulates and charcoal canisters, analyses for gross beta and iodine-1 31.

Location: 4JS - Covert (3.5 mi. SE)

Units: pCim 3

Collection: Continuous, weekly exchange.

Date Volume Date Volume

Collected (m3

) Gross Beta 1-131 Collected (m3) Gross Beta 1-131

Reauired LLD 0.010 0.030 0.010 0.030

01-10-05 334

01-17-05 331

01-24-05 337

01-31-05 337

02-07-05 331

02-14-05 334

02-21-05 312

02-28-05 337

0.029 ± 0.004 < 0.015

0.028 ± 0.004 < 0.012

0.030 ± 0.003 < 0.009

0.030 ± 0.004 < 0.014

0.033 ± 0.003 < 0.013

0.021 ± 0.003 < 0.012

0.035 ± 0.004 < 0.014

0.030 ± 0.004 < 0.009

07-04-05

07-11-05

07-18-05

07-25-05

08-01-05

08-08-05

08-15-05

08-22-05

08-29-05

312

309

309

303

312

317

320

314

320

0.033 ± 0.004 < 0.022

0.028 ± 0.004 < 0.024

0.033 + 0.004 < 0.023

0.027 ± 0.004 < 0.023

0.024 + 0.004 < 0.016

0.041 ± 0.004 < 0.017

0.037 ± 0.004 < 0.011

0.034 ± 0.004 < 0.027

0.030 ± 0.004 < 0.016

03-07-05

03-14-05

03-21-05

03-28-05

331

334

337

326

0.024 ± 0.003 < 0.012

0.019 ± 0.003 < 0.013

0.022 ± 0.003 < 0.010

0.018 ± 0.003 < 0.011

0.027 ± 0.006 < 0.015

09-05-05 320

09-12-05 317

09-19-05 320

09-26-05 329

10-03-05 320

3rd Qtr. Mean ± s.d.

0.024 ± 0.004 < 0.023

0.044 ± 0.004 < 0.013

0.036 ± 0.004 < 0.014

0.036 * 0.004 < 0.008

0.023 ± 0.004 < 0.023

1 st Qtr. Mean ± s.d. 0.032 ± 0.006 < 0.027

04-04-05

04-11-05

04-18-05

04-26-05

05-02-05

05-09-05

05-16-05

05-23-05

05-31-05

06-06-05

06-13-05

06-20-05

06-27-05

326

320

320

326

323

320

320

320

360

269

303

314

306

0.024 ± 0.003 < 0.014

0.026 ± 0.003 < 0.031

0.026 ± 0.003 < 0.021

0.022 ± 0.003 < 0.012

0.018 ± 0.003 < 0.023

0.030 ± 0.003 < 0.014

0.020 ± 0.003 < 0.017

0.022 ± 0.003 < 0.029

0.018 ± 0.003 < 0.013

0.025 ± 0.004 a < 0.062

0.025 ± 0.004 a < 0.034

0.013 ± 0.003 < 0.018

0.037 ± 0.004 < 0.020

10-10-05

10-17-05

10-24-05

10-31 -05

11-07-05

11-14-05

11-21-05

11-28-05

12-05-05

12-12-05

12-19-05

12-27-05

01-02-06

323

329

329

334

331

337

337

334

348

351

348

391

295

0.022 ± 0.004 < 0.022

0.023 ± 0.003 < 0.014

0.022 ± 0.004 < 0.012

0.022 ± 0.003 < 0.021

0.040 ± 0.004 < 0.014

0.040 ± 0.004 a < 0.036

0.027 ± 0.004 < 0.012

0.026 ± 0.004 < 0.021

0.021 ± 0.003 < 0.008

0.043 ± 0.004 a < 0.046

0.036 ± 0.004 < 0.021

0.061 ± 0.004 < 0.021

0.025 i 0.004 < 0.014

2nd Qtr. Mean ± s.d. 0.024 ± 0.006 < 0.062 4th Qtr. Mean ± s.d. 0.031 ± 0.012 < 0.046

Cumulative Average

Previous Annual Average

0.029

0.027

a 1-131 LLD not reached due to age of sample.

1-1
PALISADES

Table 1. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-1 31.

Location: 5PR - Covert (3.5 mi. ESE)

Units: pCi/m3

Collection: Continuous, weekly exchange.

Date Volume Date Volume

Collected (mi3 ) Gross Beta 1-131 Collected (m3) Gross Beta 1-131

Reauired LLD 0.010 0.030 0.010 0.030

01-10-05

01-17-05

01-24-05

01-31-05

357

348

360

348

02-07-05 343

02-14-05 354

02-21-05 337

02-28-05 351

0.032 ± 0.004

0.030 ± 0.004

0.030 ± 0.003

0.026 ± 0.004

0.033 ± 0.003

0.021 ±0.003

0.027 ± 0.004

0.028 ± 0.003

0.026 ± 0.003

0.021 ± 0.003

0.019 ± 0.003

0.020 ± 0.003

< 0.014

< 0.012

< 0.008

< 0.013

< 0.013

< 0.011

< 0.013

< 0.008

< 0.012

07-04-05

07-11-05

07-18-05

07-25-05

08-01-05

326

326

323

320

334

08-08-05 329

08-15-05 329

08-22-05 329

08-29-05 334

0.028 ± 0.004 < 0.021

0.026 ± 0.004 < 0.023

0.033 ± 0.004 < 0.022

0.030 ± 0.004 < 0.022

0.023 ± 0.004 < 0.015

0.039 ± 0.004 < 0.017

0.034 ± 0.004 < 0.010

0.034 ± 0.004 < 0.026

0.024 ± 0.003 < 0.015

0.022 ± 0.003 < 0.022

0,047 ± 0.004 < 0.012

0.037 ± 0.004 < 0.013

0.032 ± 0.004 < 0.008

0.027 ± 0.004 < 0.022

0.031 ± 0.007 < 0.026

03-07-05

03-14-05

03-21-05

03-28-05

348

348

351

340

< 0.012 09-05-05 331

c 0.009 09-12-05 331

< 0.010 09-19-05 337

09-26-05 343

10-03-05 334

1 st Qtr. Mean ± s.d. 0.026 ± 0.005 < 0.014 3rd Qtr. Mean ± s.d.

04-04-05

04-11-05

04-18-05

04-26-05

05-02-05

340 0.024 ± 0.003

331 - 0.022 ± 0.003

334 0.027 ± 0.003

343 0.023 ± 0.003

334 0.019 ± 0.003

< 0.013

< 0.030

*< 0.020

< 0.011

< 0.022

10-10-05

10-17-05

10-24-05

10-31 -05

331

337

337

343

0.027 ± 0.004 < 0.022

0.023 ± 0.003 < 0.014

0.023 ± 0.004 < 0.012

0.022 ± 0.003 < 0.021

05-09-05 334

05-16-05 334

05-23-05 334

05-31-05 382

0.029 ± 0.003

0.019 ± 0.003

0.023 ± 0.003

0.017 ± 0.002

< 0.013

< 0.016

< 0.028

< 0.012

11-07-05

11-14-05

11-21-05

11-28-05

337

343

348

351

0.040 ± 0.004 < 0.014

0.037 ± 0.004 < 0.030

0.031 ± 0.004 < 0.012

0.023 ± 0.003 < 0.020

06-06-05 280 0.026 ± 0.004 a < 0.059

06-13-05 323 0.024 ± 0.003 8 < 0.032

06-20-05 327 0.016 ± 0.003 < 0.017

06-27-05 323 0.035 ± 0.004 < 0.019

12-05-05 354

12-12-05 360

12-19-05 357

12-27-05 396

01-02-06 300

0.022 ± 0.003 < 0.007

0.045 ± 0.004 a < 0.045

0.035 ± 0.004 < 0.021

0.061 ± 0.004 < 0.021

0.023 ± 0.004 < 0.014

-

2nd Qtr. Mean ± s.d. 0.023 ± 0.005 < 0.059 4th Qtr. Mean ± s.d. 0.032 ± 0.012 < 0.045

Cumulative Average

Previous Annual Average

0.028

0.025

a 1-131 LLD not reached due to age of sample.

1-2
PALISADES

Table 1. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-1 31.

Location: 8SP - State Park (1.0 mi. N)

Units: pCi/m3

Collection: Continuous, weekly exchange.

Date Volume Date Volume

Collected (mi3 ) Gross Beta 1-131 Collected (m3) Gross Beta 1-131

Required LLD 0.010 0.030 0.010 0.030

01-10-05 368

01-17-05 363

01-24-05 371

01-31-05 371

02-07-05 360

02-14-05 365

02-21-05 351

02-28-05 360

03-07-05 363

03-14-05 363

03-21-05 363

03-28-05 351

1 st Qtr. Mean + s.d.

0.029 i0.003 < 0.014

0.031 ±0.004 < 0.011

0.027 ± 0.003 < 0.008

0.028 ± 0.003 < 0.012

0.034 ± 0.003 < 0.012

0.022 ± 0.003 < 0.011

0.028 ± 0.004 < 0.012

0.028 ± 0.003 < 0.008

0.022 ± 0.003 < 0.011

0.021 ± 0.003 < 0.012

0.020 ± 0.003 < 0.009

0.019 ± 0.003 < 0.010

0.026 ± 0.005 < 0.014

07-04-05

07-11-05

07-18-05

07-25-05

08-01-05

08-08-05

08-15-05

08-22-05

08-29-05

343

340

337

337

346

346

331

340

346

0.031 ± 0.004 < 0.020

0.034 ± 0.004 < 0.022

0.035 ± 0.004 < 0.021

0.026 ± 0.004 < 0.020

0.021 ± 0.003 < 0.015

0.039 ± 0.004 <0.016

0.035 ± 0.004 < 0.010

0.033 ± 0.004 < 0.025

0.025 ± 0.003 < 0.015

0.023 ± 0.003 < 0.021

0.047 ± 0.004 < 0.012

0.038 ± 0.004 < 0.013

0.038 ± 0.004 < 0.007

0.020 ± 0.003 < 0.021

0.032 + 0.008 < 0.025

09-05-05 346

09-12-05 340

09-19-05 348

09-26-05 357

10-03-05 346

3rd Qtr. Mean ± s.d.

04-04-05 351

04-11-05 343

04-18-05 346

04-26-05 351

05-02-05 346

05-09-05 343

05-16-05 346

05-23-05 340

05-31-05 402

0.024 ± 0.003 < 0.013

0.024 ± 0.003 < 0.029

0.027 ± 0.003 < 0.020

0.021 ± 0.003 < 0.011

0.016 ± 0.003 < 0.021

0.028 ± 0.003 < 0.013

0.020 ± 0.003 < 0.016

0.021 ± 0.003 < 0.028

0.015 ± 0.002 < 0.012

0.025 ± 0.004 a < 0.056

0.026 ± 0.003 a < 0.030

0.016 ± 0.003 < 0.016

0.035 ± 0.003 < 0.018

10-10-05

10-17-05

10-24-05

10-31-05

11-07-05

11-14-05

11-21-05

11-28-05

12-05-05

12-12-05

12-19-05

12-27-05

01-02-06

351

354

360

363

357

360

371

371

391

385

379

422

320

0.029 ± 0.004 < 0.020

0.022 ± 0.003 < 0.013

0.022 ± 0.003 < 0.011

0.019 ± 0.003 < 0.020

0.036 ± 0.004 < 0.013

0.037 ±0.004 < 0.040

0.024 ± 0.003 < 0.011

0.025 ± 0.003 < 0.018

0.018 ± 0.003 < 0.007

0.042 ± 0.004 a < 0.042

0.040 ± 0.004 < 0.019

0.058 ± 0.004 < 0.020

0.022 ± 0.003 < 0.013

06-06-05

06-13-05

06-20-05

06-27-05

295

340

346

337

2nd Qtr. Mean ± s.d. 0.023 ± 0.006 < 0.056 4th Qtr. Mean ± s.d. 0.030 t 0.012 < 0.042

Cumulative Average

Previous Annual Average

0.028

0.026

a 1-131 LLD not reached due to age of sample.

1-3
PALISADES

Table 1. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-1 31.

Location: 9TP - Covert Township Park (1.5 mi. SSW)

Units: pCim 3

Collection: Continuous, weekly exchange.

Date Volume Date Volume

Collected (m 3 ) Gross Beta 1-131 Collected (m 3) Gross Beta 1-131

Required LLD 0.010 0.030 0.010 0.030

01-10-05 356

01-17-05 360

01-24-05 368

01-31-05 368

02-07-05 357

02-14-05 363

02-21-05 346

02-28-05 363

03-07-05 357

03-14-05 360

03-21-05 363

03-28-05 348

1 st Qtr. Mean i s.d.

04-04-05 346

04-11-05 340

04-18-05 343

04-26-05 348

05-02-05 343

05-09-05 340

05-16-05 334

05-23-05 343

05-31-05 385

06-06-05 269

06-13-05 *326

06-20-05 331

06-27-05 323

0.033 ± 0.004 < 0.014

0.033 ± 0.004 < 0.011

0.029 ± 0.003 < 0.008

0.029 ± 0.004 < 0.012

0.034 ± 0.003 < 0.012

0.021 ± 0.003 <0.011

0.030 ± 0.004 < 0.012

0.030 ± 0.003 < 0.008

0.023 ± 0.003 < 0.012

0.025 ± 0.003 < 0.012

0.024 ± 0.003 < 0.009

0.020 ± 0.003 < 0.010

07-04-05 329

07-11-05 329

07-18-05 329

07-25-05 320

08-01-05 329

08-08-05 329

08-15-05 272

08-22-05 286

08-29-05 337

< 0.014

09-05-05 334

09-12-05 331

09-19-05 337

09-26-05 343

10-03-05 320

0.028 ± 0.005 3rd Qtr. Mean ± s.d.

0.028 ± 0.004 < 0.021

0.031 ± 0.004 < 0.022

0.033 ± 0.003 < 0.022

0.031 ± 0.004 < 0.022

0.022 ± 0.004 < 0.016

0.036 ± 0.004 < 0.017

0.043 ± 0.005 < 0.013

0.032 ± 0.004 < 0.029

0.024 ± 0.003 < 0.015

0.025 ± 0.003 < 0.022

0.046 ± 0.004 < 0.012

0.036 ± 0.004 < 0.013

0.038 ± 0.004 < 0.008

0.024 ± 0.004 < 0.023

0.032 ± 0.007 < 0.029

0.025 ± 0.004 < 0.021

0.026 ± 0.004 < 0.014

0.023 ± 0.003 < 0.012

0.021 ± 0.003 < 0.020

0.040 ± 0.004 < 0.013

0.036 + 0.004 < 0.038

0.025 ± 0.003 < 0.012

0.026 ± 0.003 < 0.019

0.023 ± 0.003 < 0.007

0.046 ± 0.004 a < 0.044

0.034 ± 0.004 < 0.020

0.062 ± 0.004 < 0.020

0.027 ± 0.004 < 0.014

0.022 ± 0.003 < 0.013

0.023 ± 0.003 < 0.029

0.028 ± 0.003 < 0.020

0.024 ± 0.003 < 0.011

0.017 ± 0.003 < 0.021

0.031 ± 0.003 < 0.013

0.020 ± 0.003 < 0.016

0.021 ± 0.003 < 0.028

0.017 ± 0.002 < 0.012

0.031 ± 0.004 a < 0.062

0.027 ± 0.004 c < 0.032

0.014 ± 0.003 < 0.017

0.033 ± 0.003 < 0.019

10-10-05 340

10-17-05 340

10-24-05 346

10-31-05 348

11-07-05 343

11-14-05 348

11-21-05 351

11-28-05 357

12-05-05 360

12-12-05 368

12-19-05 363

12-27-05 408

01-02-06 306

2nd Qtr. Mean ± s.d. 0.024 + 0.006 < 0.062 4th Qtr. Mean ± s.d. 0.032 ± 0.012 < 0.044

Cumulative Average

Previous Annual Average

0.029

0.026

a 1-131 LLD not reached due to age of sample.

1-4
PALISADES

Table 1. Airborne particulates and charcoal canisters, analyses for gross beta and iodine-I 31.

Location: 1OGR - Grand Rapids (55 mi. NNE)

Units: pci/m3

Collection: Continuous, weekly exchange.

Date Volume Date Volume

Collected (i 3 ) Gross Beta 1-131 Collected (m 3 ) Gross Beta 1-131

Reauired LLD 0.010 0.030 0.010 0.030

01-05-05 348

01-12-05 337

01-19-05 357

01-26-05 351

02-02-05 348

02-09-05 320

02-16-05 343

02-23-05 346

03-03-05 399

03-09-05 357

03-16-05 337

03-23-05 337

03-30-05 334

0.042 ± 0.004 < 0.022

0.040 ± 0.004 < 0.019

0.030 ± 0.003 < 0.013

0.027 ± 0.004 < 0.020

0.027 ± 0.003 < 0.019

0.036 ± 0.004 <0.020

0.031 ±0.004 <0.019

0.027 ± 0.003 < 0.013

0.025 ± 0.003 < 0.015

0.027 * 0.004 c0.021

0.023 ± 0.003 c0.015

0.020 ± 0.003 < 0.016

0.023 ± 0.003 < 0.016

07-06-05 286

07-14-05 337

07-20-05 263

07-27-05 331

08-03-05 312

08-10-05 317

08-17-05 329

08-24-05 314

08-31-05 326

09-08-05 371

09-14-05 275

09-21-05 320

09-28-05 331

0.030 ± 0.004 2< 0.040

0.037 ± 0.004 a < 0.031

0.035 ± 0.005 a < 0.038

0.028 ± 0.004 < 0.024

0.036 ± 0.004 < 0.027

0.043 ± 0.004 < 0.017

0.035 ± 0.004 a < 0.039

0.026 ± 0.004 < 0.018

0.031 ± 0.004 <0.022

0.029 ± 0.003 < 0.016

0.062 ± 0.005 < 0.024

0.036 ± 0.004 < 0.013

0.033 ± 0.004 < 0.034

1st Qtr. Mean ± s.d. 0.029 ± 0.007 < 0.022 3rd Qtr. Mean i s.d. 0.035 ± 0.009 < 0.040

04-06-05 329

04-13-05 340

04-21-05 363

04-27-05 295

05-04-05 331

05-12-05 371

05-18-05 286

05-25-05 329

06-01-05 326

06-08-05 317

06-15-05 295

06-23-05 326

06-29-05 235

0.027 ± 0.003 c0.046

0.026 ± 0.003 c0.030

0.029 ± 0.003 <0.017

0.018 ± 0.003 <0.038

0.018 ± 0.003 c0.020

0.032 ± 0.003 < 0.022

0.021 ± 0.003 < 0.049

0.021 ± 0.003 c<0.023

0.020 ± 0.003 c 0.083

0.023 ± 0.004 a <0.051

0.025 ± 0.004 < 0.029

0.019 i 0.003 < 0.027

0.054 ± 0.006 a c0.044

10-05-05 323

10-12-05 334

10-19-05 331

10-26-05 340

11-02-05 337

11-09-05 331

11-16-05 343

11-23-05 340

11-30-05 351

12-07-05 346

12-14-05 354

12-22-05 402

12-28-05 286

0.035 ± 0.004 a < 0034

0.022 ± 0.003 < 0.022

0.025 ± 0.004 < 0.019

0.018 ± 0.003 < 0.032

0.026 ± 0.004 < 0.021

0.048 ± 0.005 < 0.029

0.023 ± 0.003 < 0.018

0.031 ± 0.004 a < 0.031

0.026 i 0.003 < 0.011

0.025 ± 0.003 a <0.061

0.038 ± 0.004 < 0.032

0.044 ± 0.004 a < 0.032

0.057 ± 0.005 < 0.023

2nd Qtr. Mean ± s.d. 0.026 ± 0.010 < 0.083 4th Qtr. Mean ± s.d. 0.032 ± 0.012 < 0.061

Cumulative Average

Previous Annual Average

0.031

0.028

a 1-131 LLD. not reached due to age of sample.

1-5
PALISADES

Table 2. Gamma radiation, as measured by TLDs, quarterly exposure.

Units: mR/91 daysa

Date Placed

Date Removed

Intransit (mR)

1st Qtr.

12-30-04

03-28-05

2.4 ± 0.2

2nd Qtr.

03-28-05

06-30-05

1.0 ± 0.6

3rd Qtr.

06-30-05

09-30-05

2.2 ± 0.2

4th Qtr.

09-30-05

01-03-06

1.1 ±0.5

ST-01

ST-02

ST-03

ST-04

ST-05

ST-06

ST-07A

ST-08

ST-09

ST-10

ST-1I

ST-12

ST-13

ST-14

ST-15

ST-16

ST-17

ST-18

ST-19

ST-20

ST-21

ST-22

ST-23

ST-24

ST-33

ST-34

ST-35

ST-36

ST-37

ST-38

Mean s.d.

Control 1

Control 2

11.2 ±0.7

15.1 ±0.9

12.9 ±0.3

13.6 ± 0.7

13.5 ± 0.4

12.6 ±0.4

11.8 ±0.5

11.9 ±0.5

11.1 ±0.4

12.8 ±0.6

15.9 i 1.4

12.3 ±0.5

11.2 ±0.6

10.0 ±0.5

10.8 ± 1.1

9.7 ±0.8

10.3 ±0.3

11.3 0 0.3

11.3 ±0.3

9.6 ± 0.3

11.3 ±0.4

7.2 ± 0.7

11.5 O0.6

12.2 i0.5

10.1 ±0.4

10.6 ±0.5

13.4 ± 0.5

10.7 ± 0.4

11.4 ± 0.6

10.6 ± 0.9

11.6 ± 1.7

6.6 ± 0.4

6.9 ± 0.7

12.8 ± 0.8

17.4 ± 0.7

14.6 ± 0.7

15.6 ± 0.8

15.6 ± 0.9

13.6 ± 0.6

12.6 ± 0.8

13.9 ± 0.8

13.0 ± 0.6

14.2 ± 0.7

16.9 ± 0.6

14.9 ± 0.6

13.2 ± 0.8

11.4 ±0.6

12.4 ± 0.7

12.2 ±0.7

11.9 ±0.9

13.4 ±0.9

13.4 ± 0.6

12.8 ± 0.6

11.9 ± 0.8

7.5 ± 0.6

13.9 ± 0.6

15.6 ± 0.8

11.9 ±0.8

12.4 ± 0.6

14.6 ± 0.7

12.3 ± 0.7

12.8 ± 0.8

12.5 ± 0.8

13.4 ± 1.9

7.3 ± 0.6

7.4 ± 0.6

12.0 ± 0.7

17.9 ± 0.9

15.0 ± 0.4

15.3 ± 0.7

14.9 ± 0.3

14.3 ±0.4

12.6 ±0.4

12.8 ± 0.5

11.9 ± 0.5

13.9 ± 0.4

16.7 ± 1.0

15.3 ± 0.7

12.2 ± 0.7

10.6 ± 0.5

11.2 ± 0.6

11.4 ±0.3

11.0 ±0.3

12.3 ± 0.3

12.9 ± 0.4

11.2 ± 0.3

12.5 ± 0.4

7.3 ± 0.3

13.3 ± 0.7

14.4 ± 0.4

11.1 ±0.6

11.4 ± 0.4

14.5 ± 0.6

11.7 ± 0.6

12.1 ±0.7

11.1 ±0.5

12.8 ± 2.1

6.7 ± 0.4

6.6 ± 0.3

13.1 ±0.5

18.3 ±0.7

15.1 ±0.6

15.8 ± 0.6

15.4 ± 0.6

13.9 ±0.6

13.3 ±0.6

13.7 ±0.7

13.2 ±0.5

14.8 ± 0.6

17.2 i0.8

15.2 ± 0.5

13.0 ±0.5

11.7 ±0.6

12.5 ±0.6

12.3 ± 0.6

12.3 ± 0.7

13.4 ± 0.6

13.2 ± 0.5

13.0 ± 0.5

12.1 ±0.8

7.3 ± 0.6

14.0 ±0.6

15.6 ±0.6

12.3 ±0.8

12.6 ±0.6

14.7 ±0.7

12.7 ±0.7

13.0 ±0.8

12.5 ±0.7

13.6 ±2.0

7.2 ± 0.6

7.3 ± 0.6

a Intransit exposure has been subtracted.

2-1
PALISADES

Table 3. Lake Water, analyses for gross alpha, gross beta and tritium.

Collection: Monthly composites of daily collections.

Units: pCi/L

Location

Date Collected

Required LLD

Intake

Lab Code Gross Beta H-3

4.0 500

01-13-05

02-28-05

03-31-05

04-30-05

05-31-05

06-30-05

07-31-05

08-31-05

09-30-05

10-31-05

11-30-05

12-31-05

PALW -640

PALW -1092

PALW -1788

PALW -3132

PALW -3128

PALW -4480

PALW -4484

PALW -5360

PALW -6128

PALW -6985

PALW -6988

PALW -7456

1.6 ± 0.8

1.7 ± 0.4

1.8 ± 0.7

1.3 ± 0.4

1.5 ± 0.4

2.8 ± 0.7

1.7 ± 0.7

1.6 ± 0.4

1.4 ± 0.3

2.0 ± 0.7

1.5 ± 0.4

1.6 ± 0.7

< 166

< 147

< 171

< 165

< 167

241 ± 97

255 ± 97

< 171

397 ± 99

< 166

< 166

< 184

Lake Water, analysis for gross beta.

Collection: Monthly composites of daily collections.

Units: pCi/L

Location South Haven Municipal System (Raw)

Date Collected Lab Code Gross Beta

Required LLD 4.0

01-31-05 PALW -642 2.1 ± 0.6

02-28-05 PALW -1094 1.3 ± 0.3

03-31-05 PALW -1789 2.6 ± 0.6

04-30-05 PALW -2353 2.3 ± 0.6

05-31-05 PALW -3147 1.5 ± 0.4

06-30-05 PALW -4632 2.2 ± 0.6

07-31-05 PALW -4633 2.0 ± 0.5

08-31-05 PALW -5363 0.9 ± 0.3

09-30-05 PALW -6131 1.4 ± 0.3

10-31-05 PALW -6439 2.1 ± 0.4

11-30-05 PALW -6989 1.7 ± 0.4

12-31-05 PALW -7458 2.2 ± 0.6

3-1
11CL S (q (Coo

5 c *0 IA M e- -T(Ic aL PALISADES

Table 4. AEUllstef, analyses for gross beta and tritium.

Collection: Monthly composites of daily collections.

Units: pCi/L

Location South Haven Municipal System (Treated)

Date Collected Lab Code Gross Beta H-3

Required LLD 4.0 500

01-31-05 PAWW -643 3.0 i 0.6 < 166

02-28-05 PAWW -1095 2.0 ± 0.3 < 147

03-31-05 PAWW -1790 2.4 ± 0.6 < 171

04-30-05 PAWW -3134 1.4 ± 0.4 < 165

05-31-05 PAWW -3130 1.5 ± 0.4 < 165

06-30-05 PAWW -4482 1.1 ± 0.3 287 ± 99

07-31-05 PAWW -4485 1.9 ± 0.6 245 ± 114

08-31-05 PAWW -5364 1.1 ± 0.3 < 171

09-30-05 PAWW -6132 2.5 ± 0.6 322 ± 96

10-31-05 PAWW -6986 1.1 ± 0.6 < 166

11-30-05 PAWW -6990 1.3 ± 0.3 < 181

12-31-05 PAWW -7459 1.7 ± 0.6 < 190

4-1
PALISADES

Table 5. Well water, analyses for gross beta and tritium.

Collection: Quarterly

Units: pCi/L

Location Site Well #14

Date Collected Lab Code Gross Beta H-3

Required LLD 4.0 500

03-29-05 PAWW -1348 4.2 ± 0.8 < 166

06-30-05 ND" - -

09-30-05 PAWW -6133 4.2 ± 0.7 301 ± 95

11-21-05 PAWW -6991 3.6 ± 0.5 < 181

Location Site Well #15

Date Collected Lab Code Gross Beta H-3

Required LLD 4.0 500

03-29-05 PAWW -1349 4.1 ± 0.7 < 166

06-30-05 ND" -

09-30-05 PAWW -6134 3.7 ± 0.7 316 ± 96

11-21-05 PAWW -6992 2.8 ± 0.5 < 181

NOTE: Gamma isotopic analysis required if gross beta exceeds 10 pCViL. Results listed in Appendix C.

a "ND" = No data; sample not received.

5-1
PALISADES

Table 5. Well water, analyses for gross beta and tritium.

Collection: Quarterly

Units: pCi/L

Location Site Well #16

Date Collected Lab Code Gross Beta H-3

Required LLD 4.0 500

03-29-05 PAWW -1350 6.1 ± 0.9 < 166

06-30-05 NDa - -

09-30-05 PAWW -6135 5.3 ± 0.8 364 ± 98

11-21-05 PAWW -6993 4.8 ± 0.6 < 181

NOTE: Gamma isotopic analysis required if gross beta exceeds 10 pCi/L. Results listed in Appendix C.

a"ND" = No data; sample not received.

5-2
PALISADES

Table 6. Water, Ludington controls, analyses for gross beta, tritium and strontium.

Collection: Monthly composites of daily collections.

Units: pCi/L

Location Ludington (Lake In)

Date Collected Lab Code Gross Beta H-3 Sr-89 Sr-90

Required LLD 4.0

02-08-05

03-07-05

04-11-05

05-03-05

06-01-05

07-12-05

08-01-05

09-12-05

10-11-05

10-31 -05

12-05-05

01-03-06

PALW -641

PALW

PALW

PALW

PALW

PALW

PALW

PALW

PALW

-1093

-3126

-3133

-3129

-4481

-5359

5361,2

6129,30

2.9 ± 0.8

1.3 ± 0.4

1.6 ± 0.4

1.4 * 0.4

1.4 ± 0.4

2.3 ± 0.6

1.2 ± 0.3

1.1 ± 0.2

1.6 ± 0.2

1.8 ± 0.4

1.8 ± 0.6

2.9 ± 0.6

500

< 166

< 147

< 168

< 165

< 167

< 165

< 172

< 171

337 ± 68

< 179

< 185

< 184

5.0

< 0.4

< 0.5

< 1.1

< 0.8

< 0.6

< 0.8

< 1.3

< 0.8

< 0.7

< 0.3

< 0.9

< 0.6

1.0

< 0.7

< 0.6

< 0.5

< 0.5

< 0.5

< 0.6

< 0.7

< 0.6

< 0.5

< 0.2

< 0.6

< 0.6

PALW -6438

PALW -7454

PALW -7457

a"ND" = No data; sample not received.

6-1
PALISADES

Table 7. In-Plant water, analyses for gross alpha, gross beta, strontium-89, strontium-90, tritium and

gamma emitting isotopes.

Collection: Monthly composites

Units: uCi/mL

Location Service Water

Date Collected

Lab Code

Required

LLD

01 -31-05

PACW-639

02-28-05

PACW-1091

03-31-05

PACW-1787

Gross Alpha

Gross Beta

1.0 E-07

1.0 E-09

H-3

Sr-89

Sr-90

Cs-1 37

Othersa

1.0 E-05

5.0 E-08

5.0 E-08

5.0 E-07

5.0 E-07

< 7.7 E-10

2.1 i 0.6 E-09

< 1.7 E-07

< 1.1 E-09

< 7.1 E-10

< 1.7 E-09

< 2.3 E-09

< 9.0 E-10

1.4 ± 0.4 E-09

< 1.6 E-07

< 4.5 E-10

< 4.8 E-10

< 3.5 E-09

< 2.0 E-09

< 4.6 E-10

1.6 ± 0.3 E-09

< 1.7 E-07

< 6.2 E-10

< 5.5 E-10

< 2.8 E-09

< 2.6 E-09

Date Collected

Lab Code

Required

LLD

04-30-05

PACW-3131

05-31-06

PACW-3127

06-30-05

PACW-4479

Gross Alpha

Gross Beta

1.0 E-07

1.0 E-09

< 8.3 E-10

1.5 ± 0.4 E-09

< 7.9 E-10

1.5 ± 0.4 E-09

< 9.4 E-10

3.1 ± 0.8 E-09

H-3

Sr-89

Sr-90

Cs-1 37

Othersa

1.0 E-05

5.0 E-08

5.0 E-08

5.0 E-07

5.0 E-07

1.3 ± 0.1 E-06

< 9.2 E-10

< 5.6 E-10

< 1.5 E-09

< 1.1 E-09

< 1.7 E-07

< 7.0 E-10

< 5.9 E-10

< 3.3 E-09

< 4.5 E-09

< 1.7 E-07

< 8.3 E-10

< 5.9 E-10

< 1.1 E-09

< 1.4 E-09

Date Collected

Lab Code

Required

LLD

07-31-05

PACW-4483

08-31-05

PACW-5358

09-30-05

PACW-6127

Gross Alpha

Gross Beta

1.0 E-07

1.0 E-09

< 9.0 E-10

2.0 ± 0.5 E-09

< 1.2 E-09

2.1 ± 0.8 E-09

1.1 ± 0.5 E-09

1.7 ± 0.3 E-09

H-3

Sr-89

Sr-90

1.0 E-05

5.0 E-08

5.0 E-08

5.0 E-07

5.0 E-07

< 1.7 E-07

< 7.2 E-10

< 6.7 E-10

< 2.1 E-09

< 3.5 E-09

< 1.7 E-07

< 7.3 E-10

< 6.9 E-10

< 1.5 E-09

< 1.4 E-09

2.8 ± 0.2 E-06

< 8.0 E-10

< 7.7 E-10

< 2.1 E-09

< 2.1 E-09

Cs-1 37

Othersa

Co-60

7-1
PALISADES

Table 7. In-Plant water, analyses for gross alpha, gross beta, strontium-89, strontium-90, tritium and

gamma emitting isotopes.

Collection: Monthly composites

Units: uCi/mL

Location Service Water

Date Collected

Lab Code

Required

LLD

10-31-05

PACW-6984

11-30-05

PACW-6987

12-31 -05

PACW-7455

Gross Alpha

Gross Beta

1.0 E-07

1.0 E-09

< 4.6 E-10

1.8 ± 0.4 E-09

< 1.2 E-09

3.8 ± 0.9 E-09

< 9.2 E-10

3.2 ± 0.7 E-09

H-3

Sr-89

Sr-90

Cs-1 37

Othersa

1.0 E-05

5.0 E-08

5.0 E-08

5.0 E-07

5.0 E-07

< 1.7 E-07

< 8.7 E-10

<5.3 E-10

< 1.6 E-09

< 1.1 E-09

< 1.7 E-07

< 7.1 E-10

< 6.7 E-10

< 4.9 E-09

< 2.5 E-09

2.7 ± 1.1 E-07

< 7.2 E-10

< 6.4 E-10

< 2.1 E-09

< 2.6 E-09

aCo-60

7-2
PALISADES

Table 7. In-Plant water, analyses for gross alpha, gross beta, strontium-89, strontium-90, tritium and

gamma emitting isotopes.

Collection: Monthly composites

Units: uCimL

Location Turbine Sump

Date Collected

Lab Code

Required

LLD

01-31-05

PACW-638

02-28-05

PACW-1 198

03-31-05

PACW-6369

Gross Alpha

Gross Beta

1.0 E-07

1.0 E-09

H-3

Sr-89

Sr-90

Cs-137

Othersa

1.0 E-05

5.0 E-08

5.0 E-08

5.0 E-07

5.0 E-07

< 9.9 E-10

1.3 ± 0.7 E-09

5.5 ± 0.2 E-06

< 6.8 E-10

9.4 ± 4.3 E-10

< 2.9 E-09

< 1.5 E-09

04-30-05

PACW-6370

< 6.4 E-10

< 6.0 E-10

< 7.7 E-10

9.0 ± 3.6 E-10

3.6 ± 0.2 E-06

< 2.9 E-09

3.9 ± 1.7 E-09

< 2.4 E-09

< 3.0 E-09

05-31-05

PACW-6371

< 5.9 E-10

< 5.6 E-10

< 6.7 E-10

5.7 ± 3.4 E-10

1.5 ± 0.1 E-05

< 8.4 E-09

< 3.1 E-10

< 1.6 E-09

< 1.3 E-09

06-30-05

PACW-6372

< 5.7 E-10

< 5.7 E-10

Date Collected

Lab Code

Gross Alpha

Gross Beta

Required

LLD

1.0 E-07

1.0 E-09

H-3

Sr-89

Sr-90

Cs-137

Othersa

1.0 E-05

5.0 E-08

5.0 E-08

5.0 E-07

5.0 E-07

1.8 ± 0.1 E-05

< 4.5 E-09

< 2.8 E-10

< 1.4 E-09

< 1.0 E-09

2.3 ± 0.1 E-05

< 2.7 E-09

< 2.3 E-10

< 1.4 E-09

< 1.2 E-09

1.3 ± 0.1 E-05

< 1.9 E-09

< 2.5 E-10

< 1.8 E-09

< 1.3 E-09

Date Collected

Lab Code

Gross Alpha

Gross Beta

Required

LLD

1.0 E-07

1.0 E-09

1.0 E-05

5.0 E-08

5.0 E-08

5.0 E-07

5.0 E-07

07-31-05

PACW-6373

< 6.3 E-10

< 5.7 E-10

08-31-05

PACW-6374

< 5.7 E-10

< 6.0 E-10

09-30-05

PACW-6375

< 3.8 E-10

1.5 ± 0.4 E-10

H-3

Sr-89

Sr-90

Cs-137

Othersa

2.0 ± 0.1 E-05

< 1.3 E-09

< 2.9 E-10

< 1.6 E-09

< 1.1 E-09

2.1 ± 0.1 E-05

< 9.8 E-10

< 3.0 E-10

< 1.5 E-09

< 9.2 E-10

1.6 ± 0.1 E-05

< 5.4 E-10

< 2.9 E-10

< 1.7 E-09

< 1.2 E-09 a Co-60

7-3
PALISADES

Table 7. In-Plant water, analyses for gross alpha, gross beta, strontium-89, strontium-90, tritium and

gamma emitting isotopes.

Collection: Monthly composites

Units: uCi/mL

Location Turbine Sump

Date Collected

Lab Code

Required

LLD

10-31 -05

PACW-7588

11-30-05

PACW-7589

12-311-05

PACW-7590

Gross Alpha

Gross Beta

1.0 E-07

1.0 E-09

H-3

Sr-89

Sr-90

1.0 E-05

5.0 E-08

5.0 E-08

4.5 i 2.0 E-10

6.6 i 2.0 E-10

1.0 + 0.1 E-05

< 2.1 E-09

< 4.9 E-10

< 1.2 E-09

< 1.7 E-09

< 4.1 E-10

2.3 ± 0.5 E-09

4.8 ± 0.2 E-06

< 1.3 E-09

< 5.8 E-10

< 1.1 E-09

< 1.4 E-09

< 3.7 E-10

9.7 ± 4.2 E-10

4.4 ± 0.2 E-06

< 1.0 E-09

< 6.0 E-10

< 9.6 E-10

< 1.2 E-09

Cs-1 37

Others"

5.0 E-07

5.0 E-07

a Co-60

7-4
PALISADES

Table 8. Milk, analyses for iodine-131 and gamma emitting isotopes,

Collection: Monthly

Location JH - Joseph Hay Farm

Date Lab Concentration (pCi/L)

Collected Code 1-131 K-40 Cs-134 Cs-137 Ba-La-140

Required LLD 1.0 - 15.0 18.0 15.0

01-11-05 PAMI -151 < 0.3 1416 ± 122 < 3.8 < 4.0 < 3.9

02-08-05 PAMI -566 < 0.2 1194 ± 105 < 3.1 < 2.5 < 1.2

03-08-05 PAMI -1089 <0.3 1301 ±69 <3.2 <2.4 <2.1

04-05-05 PAMI -1599 <0.2 1198 ±95 <4.0 <3.6 <3.2

05-03-05 PAMI -2263 < 0.2 1322 ± 109 < 3.5 < 4.0 < 2.6

08-07-05 PAMI -3118 <0.3 1351 ±101 <2.3 <3.4 <3.1

07-05-05 PAMI -3675 < 0.3 1229 ± 114 < 2.5 < 3.0 < 1.8

08-09-05 PAMI -4568 < 0.2 1377 ± 109 < 4.8 < 4.3 < 2.3

09-08-05 PAMI -5005 <0.5 1370 ± 84 <2.9 <3.0 <4.3

10-11-05 PAMI -5699 < 0.2 1232 ± 101 < 4.1 < 3.7 < 3.2

11-08-05 PAMI -6388 <0.3 1296 ±116 <4.8 <3.7 <2.1

12-06-05 PAMI -6934 < 0.3 1246 ± 94 < 3.9 < 4.0 < 1.5

Location DC - Danny Carpenter Farrn

Date Lab Concentration (pCi/L)

Collected Code 1-131 K-40 Cs-134 Cs-137 Ba-La-140

Reouired LLD t0 - 15.0 18.0 15.0

01-11-05 PAMI-149 <0.3 1257±219 <5.5 <6.8 <11.2

02-08-05 PAMI -563 < 0.2 1249 ± 99 < 4.6 < 3.9 < 2.8

03-08-05 PAMI -1087 <0.3 1187 ± 103 <4.6 <4.3 <3.5

04-05-05 PAMI -1597 <0.2 1321 ±113 <4.4 <2.8 <4.4

05-03-05 PAMI 2260,1 < 0.3 1117 ± 77 < 3.6 < 4.4 < 1.8

06-07-05 PAMI -3116 < 0.3 1338 ± 110 < 4.1 < 2.6 < 3.5

07-05-05 PAMI -3673 < 0.3 1250 ± 106 < 2.6 < 3.8 < 3.6

08-09-05 PAMI -4566 < 0.2 1085 ± 101 < 2.6 < 4.5 < 3.5

09-08-05 PAMI -5003 < 0.2 1373 ± 85 < 3.2 < 3.2 < 4.5

10-11-05 PAMI -5697 <0.2 1311 ± 117 <3.7 <4.5 <4.0

11-08-05 PAMI -6386 <0.3 1091 ±100 <4.5 <4.1 <2.6

12-06-05 PAMI -6932 < 0.3 1388 ± 105 < 3.0 < 4.2 < 3.1

8-1
PALISADES

Table 8. Milk, analyses for iodine-131 and gamma emitting isotopes,

Collection: Monthly

Location DH - Dennis Hessey Farm

Date Lab Concentration (pCi/L)

Collected Code 1-131 K-40 Cs-134 Cs-137 Ba-La-140

Required LLD 1.0 - 15.0 18.0 15.0

01-11-05 PAMI -150 < 0.3 1122 ± 196 < 5.7 < 8.5 < 11.4

02-08-05 PAMN 564,5 < 0.3 1304 ± 115 < 3.3 < 4.5 < 3.0

03-08-05 PAMI -1088 <0.3 1223 ±114 <2.6 <3.8 <4.5

04-05-05 PAMI -1598 < 0.2 1356 ± 113 < 3.2 < 3.7 < 3.9

05-03-05 PAMI -2262 < 0.3 1277 ± 106 < 3.2 < 3.9 < 1.6

06-07-05 PAMI -3117 < 0.3 1267 ± 109 < 3.8 < 3.8 < 2.9

07-05-05 PAMI -3674 <0.3 1397 ± 115 <4.8 <2.7 <2.2

08-09-05 PAMI -4567 < 0.2 1386 ± 113 < 4.2 < 3.9 < 2.9

09-08-05 PAMI -5004 < 0.3 1353 ± 112 < 3.0 < 2.0 < 3.1

10-11-05 PAMI -5698 < 0.3 1259 ± 108 < 3.1 < 3.2 < 3.1

11-08-05 PAM! -6387 < 0.3 1229 ± 114 < 3.3 < 3.1 < 4.3

12-06-05 PAMI -6933 < 0.2 1462 ± 106 < 4.5 < 4.4 < 1.4

Location WS - William Shine Farm

Date Lab Concentration (pCVL)

Collected Code 1-131 K-40 Cs-1 34 Cs-137 Ba-La-140

Reauired LLD 1.0 - 15.0 18.0 15.0

01-11-05 PAMN -152 < 0.3 1487 ± 219 < 8.0 < 8.1 < 8.4

02-08-05 PAMI -567 <0.2 1153 i 151 <4.6 <4.2 <2.9

03-08-05 PAMI -1090 < 0.3 1378 ± 83 < 3.5 < 3.6 < 4.0

04-05-05 PAMI -1600 < 0.2 1392 ± 85 < 3.2 < 2.8 < 4.4

05-03-05 PAMI -2264 < 0.2 1286 ± 108 < 3.4 < 4.6 < 2.7

06-07-05 PAMI -3119 <0.3 1440 ±105 <4.7 <4.9 <1.8

07-05-05 PAMI 3676,7 <0.3 1406 ±85 <2.7 < 3.3 < 2.0

08-09-05 PAMI -4569 < 0.2 1478 ± 112 < 4.5 < 1.9 < 2.1

09-08-05 PAMI -5006 < 0.2 1530 ± 84 < 3.3 < 2.6 < 2.5

10-11-05 PAM! -5700 < 0.2 1205 ± 103 < 3.4 < 3.5 < 2.8

11-08-05 PAMI-6389 <0.3 1363±118 <3.6 <3.9 <3.1

12-06-05 PAMI -6935 < 0.3 1489 ± 106 < 2.5 < 3.6 < 1.8

8-2
PALISADES

Table 9. Food Crops, analyses for gross beta and gamma-emitting isotopes.

Collection: Semiannually, at the time of harvest.

Units: pCig wet

I nration J. Samo Farm

Lab Code

Date Collected

Sample Type

Mn-54

Fe-59

Co-58

Co-60

Zn-65

Zr-Nb-95

1-131

Cs-134

Cs-I 37

PAVE-4656

8/8/2005

Blueberries

< 0.014

< 0.018

< 0.010

< 0.012

< 0.009

< 0.022

< 0.028

< 0.015

< 0.015

PAVE-6098

10/10/2005

Apples

< 0.009

< 0.048

< 0.015

< 0.009

< 0.027

< 0.019

< 0.149

< 0.012

< 0.010

Req. LLD

0.08

0.10

0.08

0.05

0.10

0.10

0.06 a

0.08

0.08

' Required for broadleaf vegetation only.

9-1
PALISADES

Table 9. Food Crops, analyses for gross beta and gamma-emitting isotopes.

Collection: Semiannually, at the time of harvest.

Units: pClg wet

Location Control Station

Lab Code

Date Collected

Sample Type

Mn-54

Fe-59

Co-58

Co-60

Zn-65

Zr-Nb-95

1-131

Cs-134

Cs-1 37

PAVE-4657

8/8/2005

Blueberries

< 0.011

< 0.017

< 0.013

< 0.015

< 0.028

< 0.012

< 0.032

< 0.011

< 0.013

PAVE-6099

10/10/2005

Apples

< 0.020

< 0.031

< 0.015

< 0.013

< 0.017

< 0.018

< 0.145

< 0.014

< 0.019

Req. LLD

0.08

0.10

0.08

0.05

0.10

0.10

0.06 a

0.08

0.08

a Required for broadleaf vegetation only.

9-2
PALISADES

Table 10. Fish, analyses for gross beta and gamma-emitting isotopes.

Collection: Semiannually

Units: pCi/g wet

Location Discharge

Lab Code

Date Collected

Sample Type

Mn-54

Fe-59

Co-58

Co-60

Zn-65

Zr-Nb-95

Cs-134

Cs-137

PAF-7118,9

4/6/2005

PAF-7120

9/7/2005

PAF-7121

9/21/2005

PAF-7123

11/25/2005

Whitefish

Req. LLD

Brown Trout Yellow Perch Chinook Salmon

< 0.034

< 1.452

< 0.225

< 0.020

< 0.048

< 2.162

< 0.015

< 0.018

< 0.020

< 0.212

< 0.050

< 0.018

< 0.029

< 0.170

<0.016

< 0.016

< 0.016

<0.188

< 0.024

<0.010

< 0.024

< 0.167

< 0.013

0.065 ± 0.028

<0.015

< 0.051

< 0.021

< 0.013

< 0.018

<0.041

< 0.015

< 0.017

0.13

0.26

0.13

0.13

0.26

0.10

0.13

0.15

Location Lake Ontario

Lab Code

Date Collected

Sample Type

PAF-7126

12/8/2005

Perch

Req. LLD

Mn-54

Fe-59

Co-58

Co-60

Zn-65

Zr-Nb-95

Cs-I 34

Cs-137

< 0.013

< 0.052

< 0.016

< 0.015

< 0.020

< 0.014

<0.015

< 0.014

0.13

0.26

0.13

0.13

0.26

0.10

0.13

0.15

Location Ludington Pumped Storage Plant (Control)

Lab Code

Date Collected

Sample Type

Mn-54

Fe-59

Co-58

Co-60

Zn-65

Zr-Nb-95.

Cs-134

Cs- 137

PAF-7122

10/13/2005

Chinook Salmon

< 0.028

<0.174

< 0.037

< 0.030

< 0.046

< 0.097

c 0.020

< 0.023

PAF-7124

12/8/2005

Whitefish

<0.017

< 0.028

<0.015

<0.013

<0.031

< 0.043

< 0.020

c 0.017

PAF-7125

12/8/2005 Req. LLD

Trout

< 0.013

< 0.059

< 0.014

< 0.011

< 0.025

< 0.023

<0.016

0.035 i 0.020

0.13

0.26

0.13

0.13

0.26

0.10

0.13

0.15

10-1
PALISADES

Table 11. Bottom sediment, analyses for gamma-emitting isotopes.

Collection: Semiannually

Units: pCi/g dry

Location Palisades North Property

Lab Code

Date Collected

PABS-3124

4/28/2005

Mn-54

Fe-59

Co-58

Co-60

Zn-65

Zr-Nb-95

Cs-134

Cs-137

< 0.013

< 0.082

< 0.020

< 0.017

< 0.052

< 0.045

< 0.021

< 0.015

PABS-6977,8

11/10/2005

< 0.019

< 0.053

< 0.028

< 0.025

< 0.062

< 0.031

< 0.021

< 0.018

Req. LLD

0.08

0.10

0.08

0.05

0.10

0.10

0.15

0.18

Location Ludington Control

Lab Code

Date Collected

PABS-7127

12/8/2005 Req. LLD

Mn-54

Fe-59

Co-58

Co-60

Zn-65

Zr-Nb-95

Cs-1 34

Cs-137

< 0.025

< 0.091

< 0.027

< 0.026

< 0.087

< 0.025

< 0.037

< 0.024

0.08

0.10

0.08

0.05

0.10

0.10

0.15

0.18

11-1
PALISADES

Table 12.1. Liquid Radwaste, analyses for gross alpha, tritium, strontium-89, strontium-90,

plutonium-239 and gamma emitting isotopes.

Collection: Monthly

Units: uCurmi

Lab Code Required

LLD

NSa NS"

02-28-05

PARW-1200

Date Collected 01 -31-05 03-12-05

Gross Alpha 1.0 E-07 9.1 ± 1.5 E-09

H-3 1.0 E-05

Sr-89

Sr-90

5.0 E-08

5.0 E-08

3.66 ± 0.01 E-01

< 2.3 E-09

7.7 ± 0.4 E-08

Pu-239 5.0 E-08 2.63 ± 1.78 E-10

Cr-51

Mn-54

Fe-59

Co-58

Co-60

Zn-65

Zr-95

Nb-95

Ag-II Om

Sb-124

Cs-134

Cs-I 37

Ba-140

La-140

Ce-141

Ce-144

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

< 7.31

< 3.94

< 2.53

8.54 ± 0.20

9.01 ± 0.17

< 2.64

< 1.93

< 1.34

3.02 ± 0.63

< 1.40

< 1.17

1.14 ± 0.09

< 7.71

< 1.26

< 1.25

< 3.86

E-08

E-08

E-08

E-07

E-07

E-08

E-08

E-08

E-08

E-08

E-08

E-07

E-08

E-08

E-08

E-08

a No sample received.

12.1-1
PALISADES

Table 12.1. Liquid Radwaste, analyses for gross alpha, tritium, strontium-89, strontium-90,

plutonium-239 and gamma emitting isotopes.

Collection: Monthly

Units: uCi/ml

Lab Code Required NSa PARW-6345 NS"

LLD

Date Collected - 04-30-05 05-31-05 06-30-05

Gross Alpha 1.0 E-07 - 4.6 ± 1.3 E-09

H-3 1.0 E-05 - 1.84 ± 0.01 E-01

Sr-89 5.0 E-08 - < 1.9 E-08

Sr-90 5.0 E-08 - 9.8 ± 0.4 E-08

Pu-239 5.0 E-08 - < 1.01 E-09

Cr-51 5.0 E-07 - < 3.80 E-06

Mn-54 5.0 E-07 - < 1.52 E-07 -

Fe-59 5.0 E-07 - < 1.53 E-07

Co-58 5.0 E-07 - 7.51 ± 0.34 E-07 -

Co-60 5.0 E-07 - 1.05 ± 0.02 E-06 -

Zn-65 5.0 E-07 - < 2.83 E-08 -

Zr-95 5.0 E-07 - < 7.37 E-08 -

Nb-95 5.0 E-07 - < 1.71 E-07 -

Ag-110m 5.0 E-07 - < 1.75 E-08 -

Sb-124 5.0 E-07 - < 8.26 E-08 -

Cs-134 5.0 E-07 - 1.60 ± 0.07 E-07 -

Cs-137 5.0 E-07 - 6.73 ± 0.12 E-07 -

Ba-140 5.0 E-07 - NDb

La-140 5.0 E-07 - NDb

Ce-141 5.0 E-07 - < 3.92 E-07

Ce-144 5.0 E-07 - < 6.85 E-08

a No sample received.

b 'ND" = No data due to age of sample; sample received 10-28-05.

12.1-2
PALISADES

Table 12.1. Liquid Radwaste, analyses for gross alpha, tritium, strontium-89, strontium-90,

plutonium-239 and gamma emitting isotopes.

Collection: Monthly

Units: uCi/ml

Lab Code Required PARW-7586 NSa PARW-6346

LLD

Date Collected - 07-05-05 08-31-05 09-26-05

Gross Alpha 1.0 E-07 5.7 ± 1.6 E-09 - 2.1 ± 0.9 E-09

H-3 1.0 E-05 2.89 ± 0.01 E-01 - 4.03 ± 0.01 E-01

Sr-89 5.0 E-08 < 3.0 E-08 - < 4.0 E-08

Sr-90 5.0 E-08 2.7 ± 0.1 E-07 - 8.6 ± 0.4 E-08

Pu-239 5.0 E-08 <2.10 E-10 - < 1.84 E-09

Cr-51 5.0 E-07 <2.00 E-05 - < 3.19 E-07

Mn-54 5.0 E-07 1.22 ± 0.04 E-06 - < 3.00 E-07

Fe-59 5.0 E-07 < 7.11 E-07 - < 6.54 E-08

Co-58 5.0 E-07 3.14 ± 0.09 E-06 - 1.38 ± 0.03 E-06

Co-60 5.0 E-07 3.27 ± 0.02 E-06 - 3.28 ± 0.05 E-06

Zn-65 5.0 E-07 1.02 ± 0.32 E-07 - < 5.13 E-08

Zr-95 5.0 E-07 < 1.72 E-07 - < 5.43 E-08

Nb-95 5.0 E-07 < 7.57 E-07 - < 4.91 E-08

Ag-110m 5.0 E-07 < 5.71 E-08 - 2.46 ± 1.17 E-08

Sb-124 5.0 E-07 < 3.57 E-07 - < 3.90 E-08

Cs-134 5.0 E-07 1.11 ±0.01 E-06 - 1.81 ± 0.12 E-07

Cs-137 5.0 E-07 4.23 ± 0.03 E-06 - 6.51 ± 0.18 E-07

Ba-140 5.0 E-07 < 5.02 E-08 b - < 4.59 E-07

La-140 5.0 E-07 < 2.50 E-09 b - < 4.61 E-08

Ce-141 5.0 E-07 < 1.89 E-06 - < 4.33 E-08

Ce-144 5.0 E-07 < 1.20 E-07 - < 7.00 E-08

a No sample received.

b Not decay corrected; result at time of counting.

12.1-3
PALISADES

Table 12.1. Liquid Radwaste, analyses for gross alpha, tritium, strontium-89, strontium-90,

plutonium-239 and gamma emitting isotopes.

Collection: Monthly

Units: uCl/ml

Lab Code Required LLD Nsa NSa PARW-7587

Date Collected 10-31-05 11-30-05 12-16-05

i Gross Alpha

i H-3

Sr-89

Sr-90

Pu-239

Cr-51

Mn-54

Fe-59

Co-58

Co-60

Zn-65

Zr-95

Nb-95

Ag-1 10m

Sb-124

Cs-134

Cs-137

Ba-140

La-140

Ce-141

Ce-144

1.0 E-07 2.7 ± 3.2 E-08

1.0 E-05 4.85 ± 0.01 E-01

5.0 E-08

5.0 E-08

< 3.3 E-09

5.0 ± 0.3 E-08

5.0 E-08 < 1.36 E-10

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

5.0 E-07

< 5.42

< 2.35

< 7.35

8.75 ± 0.05

1.01 ± 0.01

5.09 ± 0.40

< 6.40

< 5.91

3.30 ± 0.20

< 4.72

7.67 ± 2.55

3.96 ± 0.20

< 1.12

< 1.36

< 7.28

2.25 ± 0.80

E-07

E-07

E-08

E-06

E-05

E-07

E-08

E-08

E-07

E-08

E-08

E-07

E-06

E-07

E-08

E-07

a No sample received.

12.1-4
PALISADES

Table 12.2. Stack Filters, analyses for gross alpha, plutonium-239, strontium-89 and strontium-90.

Collection: Continuous, monthly exchange.

Units: pCi/filter

Location Palisades

Date Collected Lab Code Gross Alpha Sr-89 Sr-90 Pu-239

Reauired LLD 10 10 10 10

01-31-05 PASP -637 1.2 ± 0.6 < 4.1 < 3.6 < 0.2

02-28-05 PASP -1199 < 0.7 < 2.4 < 2.7 < 0.3

03-30-05 PASP -6336 0.6 ± 0.4 < 83.5 a < 3.6 < 0.2

04-27-05 PASP -6337 < 0.5 < 65.2 a < 3.5 < 0.2

05-25-05 PASP -6338 < 0.4 < 31.5 a < 3.0 < 0.2

06-29-05 PASP -6339 < 0.6 < 22.3 a < 2.8 < 0.2

07-27-05 PASP -6340 < 0.5 < 14.2 a < 2.7 < 0.1

08-31-05 PASP 6341,2 < 0.6 < 8.4 b < 2.6 < 0.1

09-28-05 PASP -6343 < 0.5 < 6.0 < 2.9 < 0.1

10-31-05 PASP -7583 < 0.6 < 9.9 < 3.1 < 0.2

11-30-05 PASP -7584 < 0.6 < 6.9 < 3.0 < 0.3

12-31-05 PASP -7585 < 0.5 < 4.8 < 4.1 < 0.6

LLD not reached due to age of sample.

D Not enough sample for strontium duplicate.

12.2-1
ATTACHMENT E

ENVIRONMENTAL, INC, MIDWEST LABORATORY,

INTERLABORATORY COMPARISON PROGRAM RESULTS

18 Pages Follow
- g Environmental, Inc.

Midwest Laboratory an Allhgheny Technologies Co.

700 Landwehr Road * Northbrook, IL 60062-2310

ph. (847) 564-0700 * fax (847) 564-4517

APPENDIX A

INTERLABORATORY COMPARISON PROGRAM RESULTS

NOTE: Environmental Inc., Midwest Laboratory participates in intercomparison studies administered by

Environmental Resources Associates, and serves as a replacement for studies conducted previously

by the U.S. EPA Environmental Monitoring Systems Laboratory, Las Vegas, Nevada. Results are

reported in Appendix A. TLD Intercomparison results, in-house spikes, blanks, duplicates and

mixed analyte performance evaluation program results are also reported. Appendix A is updated

four times a year; the complete Appendix is included in March, June, September and December

monthly progress reports only.

January, 2005 through December, 2005
Appendix A

Interlaboratorv Comparison Program Results

Environmental, Inc., Midwest Laboratory has participated in interlaboratory comparison (crosscheck)

programs since the formulation of it's quality control program in December 1971. These programs are

operated by agencies which supply environmental type samples containing concentrations of radionuclides

known to the issuing agency but not to participant laboratories. The purpose of such a program is to provide

an independent check on a laboratory's analytical procedures and to alert it of any possible problems.

Participant laboratories measure the concentration of specified radionuclides and report them to the issuing

agency. Several months later, the agency reports the known values to the participant laboratories and

specifies control limits. Results consistently higher or lower than the known values or outside the control

limits indicate a need to check the instruments or procedures used.

Results in Table A-1 were obtained through participation in the environmental sample crosscheck program

administered by Environmental Resources Associates, serving as a replacement for studies conducted

previously by the U.S. EPA Environmental Monitoring Systems Laboratory, Las Vegas, Nevada.

The results in Table A-2 list results for thermoluminescent dosimeters (TLDs), via Intemational

Intercomparison of Environmental Dosimeters, when available, and internal laboratory testing.

Table A-3 lists results of the analyses on in-house "spiked" samples for the past twelve months. All samples

are prepared using NIST traceable sources. Data for previous years available upon request.

Table A-4 lists results of the analyses on in-house "blank" samples for the past twelve months. Data for

previous years available upon request.

Table A-5 list results of the in-house "duplicate" program for the past twelve months. Acceptance is based

on the difference of the results being less than the sum of the errors. Data for previous years available upon

request.

The results in Table A-6 were obtained through participation in the Mixed Analyte Performance Evaluation

Program.

Attachment A lists acceptance criteria for "spiked" samples.

Out-of-limit results are explained directly below the result.

Al
Attachment A

ACCEPTANCE CRITERIA FOR 'SPIKED" SAMPLES

LABORATORY PRECISION: ONE STANDARD DEVIATION VALUES FOR VARIOUS ANALYSESa

One standard deviation

Analysis Level for single determination

Gamma Emitters 5 to 100 pCi/liter or kg 5.0 pCi/liter

> 100 pCi/liter or kg 5% of known value

Strontium_89b 5 to 50 pCi/liter or kg 5.0 pCi/liter

> 50 pCi/liter or kg 10% of known value

Strontium-9Ob 2 to 30 pCi/liter or kg 5.0 pCi/liter

> 30 pCi/liter or kg 10% of known value

Potassium-40 2 0.1 gAiter or kg 5% of known value

Gross alpha s 20 pCi/liter 5.0 pCiAiter

> 20 pCi/liter 25% of known value

Gross beta s 100 pCi/liter 5.0 pCi/liter

> 100 pCi/liter 5% of known value

Tritium s 4,000 pCi/liter ± 1 a = (pCiAiter) =

169.85 x (known)0 93

> 4,000 pCi/liter 10% of known value

Radium-226,-228 2 0.1 pCi/liter 15% of known value

Plutonium 2 0.1 pCiAiter, gram, or sample 10% of known value

lodine-1 31, s 55 pCiAiter 6.0 pCi/liter

lodine1 29b > 55 pCi/liter 10% of known value

Uranium-238, s 35 pCiAiter 6.0 pCi/liter

Nickel-63b > 35 pCi/liter 15% of known value

Technetium-99b

Iron-55b 50 to 100 pCi/liter 10 pCi/liter

> 100 pCi/liter 10% of known value

Othersb --- 20% of known value

a From EPA publication, 'Environmental Radioactivity Laboratory Intercomparison Studies

Program, Fiscal Year, 1981-1982, EPA-600/4-81-004.

b Laboratory limit.

A2
TABLE A-1. Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)a.

Concentration (pCi/L)

Lab Code Date Analysis Laboratory ERA Control

Resultb Resultc Limits Acceptance

STW-1051 02/15/05 Sr-89 28.0 ± 1.2 29.4 20.7 - 38.1 Pass

STW-1051 02/15/05 Sr-90 25.1 ± 0.7 24.4 15.7 - 33.1 Pass

STW-1 052 02/15/05 Ba-133 52.9 ± 2.8 53.4 44.2 - 62.6 Pass

STW-1052 02/15/05 Co-60 54.4 * 0.4 56.6 47.9 - 65.3 Pass

STW-1052 02/15/05 Cs-134 67.7 t 1.8 64.9 56.2 - 73.6 Pass

STW-1052 02/15/05 Cs-137 39.6 ± 1.8 40.2 31.5 - 48.9 Pass

STW-1052 02/15/05 Zn-65 159.7 ± 3.0 161.0 133.0 -189.0 Pass

STW-1053 02/15/05 Gr. Alpha 55.1 ± 1.8 67.9 38.5 -97.3 Pass

STW-1 053 02/15/05 Gr. Beta 46.8 ± 1.3 51.1 38.5 - 97.3 Pass

STW-1054 02/15/05 Ra-226 13.7 ± 1.5 14.1 10.4 - 17.8 Pass

STW-1054 02/15/05 Ra-228 13.3 ± 0.6 13.7 7.8 -19.6 Pass

STW-1054 02/15/05 Uranium 5.1 ± 0.2 5.0 0.0 - 10.2 Pass

STW-1055 05/17/05 Sr-89 45.1 ±4.1 41.3 32.6 -50.0 Pass

STW-1055 05/17/05 Sr-90 7.5 ±0.9 5.9 0.0 -14.6 Pass

STW-1056 05/17/05 Ba-133 87.1 ± 2.0 88.4 73.1 - 104.0 Pass

STW-1056 05/17/05 Co-60 38.4 ± 0.8 37.0 28.3 - 45.7 Pass

STW-1056 05/17/05 Cs-134 75.3 ± 0.7 78.6 69.9 - 87.3 Pass

STW-1056 05/17/05 Cs-137 201.0 ±8.4 194.0 184.0 -218.0 Pass

STW-1056 05/17/05 Zn-65 130.0 ± 6.7 118.0 97.6 - 138.0 Pass

STW-1057 05/17/05 Gr. Alpha 42.7 ± 2.9 37.0 21.0 -53.0 Pass

STW-1057 05/17/05 Gr. Beta 34.0 ± 0.4 34.2 25.5 -42.9 Pass

STW-1058 05/17/05 1-131 14.7 ± 0.5 15.5 10.3 -20.7 Pass

STW-1 059 05/17/05 Ra-226 6.6 ± 0.1 7.6 5.6 -9.5 Pass

STW-1059 05/17/05 Ra-228 19.3 ± 0.7 18.9 10.7 -27.1 Pass

STW-1059 05/17/05 Uranium 9.6 ±0.1 10.1 4.9 - 15.3 Pass

STW-1060 05/17/05 H-3 24100.0 ± 109.0 24400.0 20200.0 - 28600.0 Pass

STW-1067 08/16/05 Sr-89 29.1 ± 3.0 28.0 19.3 - 36.7 Pass

STW-1067 08/16/05 Sr-90 36.0 ± 0.6 33.8 25.1 -42.5 Pass

STW-1068 08/16/05 Ba-133 107.0 ± 1.7 106.0 87.7 - 124.0 Pass

STW-1068 08/16/05 Co-60 15.2 ± 0.2 13.5 4.8 -22.2 Pass

STW-1068 08/16/05 Cs-134 89.1 ±0.3 92.1 83.4 -101.0 Pass

STW-1068 08/16/05 Cs-137 72.1 ±1.0 72.7 64.0 -81.4 Pass

STW-1068 08/16/05 Zn-65 67.4 ± 1.4 65.7 54.3 - 77.1 Pass

STW-1069 08/16/05 Gr. Alpha 44.3 ± 1.5 55.7 31.6 - 79.8 Pass

STW-1069 08/16/05 Gr. Beta 58.4 ±2.1 61.3 44.0 -78.6 Pass

STW-1070 08/16/05 Ra-226 16.6 ± 1.5 16.6 12.3 - 20.9 Pass

STW-1070 08/16/05 Ra-228 6.2 ± 0.3 6.2 3.5 - 8.9 Pass

STW-1070 08/16/05 Uranium 4.5 ±0.1 4.5 0.0 -9.7 Pass

A1-4
TABLE A-1. Interlaboratory Comparison Crosscheck program, Environmental Resource Associates (ERA)a.

Concentration (pCi/L)

Lab Code Date Analysis Laboratory ERA Control

Resultb Resultc Limits Acceptance

STW-1072 11/15/05 Sr-89 20.6 ±0.4 19.0 10.3 -27.7 Pass

STW-1072 11/15/05 Sr-90 15.0 ±0.3 16.0 7.3 -24.7 Pass

STW-1073 11/15/05 Ba-133 31.8 ± 1.8 31.2 22.5 - 39.9 Pass

STW-1073 11/15/05 Co-60 85.0 ± 1.4 84.1 75.4 - 92.8 Pass

STW-1073 11/15/05 Cs-134 37.2 ±2.1 33.9 25.2 -42.6 Pass

STW-1073 11/15/05 Cs-137 27.8 ±0.7 28.3 19.6 - 37.0 Pass

STW-1073 11/15/05 Zn-65 109.0 ± 1.0 105.0 86.8 - 123.0 Pass

STW-1074d 11/15/05 Gr. Alpha 41.1 ± 1.2 23.3 13.2 - 33.4 Fail

STW-1074 11/15/05 Gr. Beta 42.7 ± 0.5 39.1 30.4 - 47.8 Pass

STW-1075 11/15/05 1-131 20.5 ± 0.6 17.4 12.2 -22.6 Pass

STW-1076 11/15/05 Ra-226 7.8 ± 0.6 8.3 6.2 - 10.5 Pass

STW-1076e 11/15/05 Ra-228 5.5 ± 0.6 3.5 2.0 -5.0 Fail

STW-1076 11/15/05 Uranium 15.5 ±0.3 16.1 10.9 -21.3 Pass

STW-1077 11/15/05 H-3 12500.0 ± 238.0 12200.0 10100.0 - 14300.0 Pass

a Results obtained by Environmental, Inc., Midwest Laboratory as a participant In the crosscheck program for proficiency

testing in drinking water conducted by Environmental Resources Associates (ERA).

b Unless otherwise indicated, the laboratory result is given as the mean ± standard deviation for three determinations.

c Results are presented as the known values, expected laboratory precision (1 sigma, 1 determination) and control limits

as provided by ERA.

dThe original samples were calculated using an Am-241 efficiency. The samples were spiked with Th-232. Samples

were recounted and calculated using the Th-232 efficiency. Results of the recount: 27.01 ± 2.35 pCVL.

Decay of short-lived radium daughters contributed to a higher counting rate. Delay of counting for 100 minutes provided better results.

The reported result was the average of the first cycle of 100 minutes, the average of the second cycle counts was 4.01 pCiUL

Al -5
TABLE A-2. Crosscheck program results; Thermoluminescent Dosimetry, (TLD, CaSO4: Dy Cards).

mR

Lab Code Date Known Lab Result Control

Description Value ± 2 sigma Limits Acceptance

Environmental. Inc.

2005-1

2005-1

2005-1

2005-1

2005-1

2005-1

2005-1

2005-1

2005-1

4/4/2005

4/4/2005

4/4/2005

4/4/2005

4/4/2005

4/4/2005

4/4/2005

4/4/2005

4/4/2005

30cm

60 cm

60 cm

90cm

90cm

120 cm

120 cm

150 cm

180 cm

55.01

13.75

13.75

6.11

6.11

3.44

3.44

2.2

1.53

64.02 ± 2.86

15.43 ± 1.02

14.98 ± 0.80

6.24 ± 0.16

5.45 ± 0.48

3.50 ± 0.35

3.15 ±0.18

2.31 ± 0.25

1.65 ± 0.41

38.51 - 71.51

9.63 - 17.88

9.63 - 17.88

4.28 - 7.94

4.28 - 7.94

2.41 - 4.47

2.41 - 4.47

1.54 - 2.86

1.07 - 1.99

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Environmental. Inc.

2005-2

2005-2

2005-2

2005-2

2005-2

2005-2

2005-2

2005-2

2005-2

9/12/2005

9/12/2005

9/12/2005

9/12/2005

9/12/2005

9/12/2005

9/12/2005

9/12/2005

9/12/2005

30cm

60 cm

75 cm

90 cm

90 cm

120 cm

150 cm

150 cm

180 cm

54.84

13.71

8.77

6.09

6.09

3.43

2.19

2.19

1.52

59.30 ± 2.66

17.55 ± 1.30

8.24 ± 0.38

5.94 ± 0.49

5.93 ± 0.37

3.42 ± 0.18

1.71 ± 0.14

1.87 ± 0.27

1.58 ± 0.99

38.39 - 71.29

9.60 - 17.82

6.14 - 11.40

4.26 - 7.92

4.26 - 7.92

2.40 - 4.46

1.53 - 2.85

1.53 - 2.85

1.06 - 1.98

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

A2-6
TABLE A-3. In-House Spike' Samples

Concentration (pCVL)a

Lab Code b Date Analysis Laboratory results Known Control

2s, n=1 c Activity Limits d Acceptance

W-11105

W-11105

SPW-764

SPAP-766

STW-2887

W-30105

W-30105

SPW-1836

SPW-1836

SPMI-1838

SPMI-1 838

SPMI-1838

SPMI-1838

SPMI-1838

SPMI-1838

SPVE-1932

SPCH-1935

SPAP-1966

SPAP-1966

SPAP-1966

SPAP-1 968

SPAP-1968

SPW-2098

SPW-2922

SPW-2922

SPW-2922

SPW-2922

SPAP-2892

SPW-2895

w-60105

w-60105

SPF-3089

SPF-3089

SPWSPW-47731

SPW-47732

SPW-4775

SPMI-4834

SPMI-4834

SPMI-4834

SPMI-4834

1/11/2005

1/11/2005

2118/2005

2/18/2005

2/28/2005

3/1/2005

3/1/2005

4/15/2005

4/15/2005

4/15/2005

4/15/2005

4/15/2005

4/15/2005

4/15/2005

4/15/2005

4/18/2005

4/18/2005

4/18/2005

4/18/2005

4/18/2005

4/18/2005

4/18/2005

4/26/2005

5/31/2005

5/31/2005

5/31/2005

5/31/2005

6/1/2005

6/1/2005

6/1/2005

6/1/2005

6/7/2005

6/7/2005

7/1/2005

8/24/2005

8/24/2005

8/24/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

Gr. Alpha

Gr. Beta

H-3

Gr. Beta

Tc-99

Gr. Alpha

Gr. Beta

1-131

1-131 (G)

Cs-1 34

Cs-137

1-131

1-131(G)

Sr-89

Sr-90

1-131(G)

1-131

Cs-134

Cs-1 34

Cs-137

Cs-1 34

Cs-137

Fe-55

Cs-134

Cs-134

Sr-89

Sr-90

Gr. Beta

H-3

Gr. Alpha

Gr. Beta

Cs-134

Cs-1 37

Ni-63

C-1 4

C-14

Fe-55

Cs-134

Cs-137

Sr-89

Sr-90

24.05 ± 1.01

61.59 ± 1.11

77595.00 ± 764.00

416.08 ± 5.52

32.91 ± 1.23

25.22 ± 0.45

62.27 ± 0.48

109.79 ± 0.94

110.25 ± 9.68

25.94 ± 1.28

59.31 ± 3.66

97.71 ± 0.81

109.45 ± 3.06

104.44 ± 2.89

8.97 ± 0.79

1.00 ± 0.04

382.40 ± 14.95

52.10 ± 7.27

57.28 ± 13.47

124.68 ± 18.41

52.10 ±7.27

116.79 ± 14.00

2565.20 ± 63.66

27.01 ±1.09

65.38 ± 2.92

107.90 ± 3.60

11.11 * 1.13

420.32 ± 5.55

75271.00 ± 724.00

23.69 ± 0.52

60.08 ± 0.57

1.08 ± 0.05

2.54 ± 0.10

20.57 ± 1.10

2112.30 ±9.13

2294.10 ± 10.37

2633.50 ± 62.40

49.27 ± 4.68

58.17 ± 8.18

66.39 ± 3.13

11.15 ± 1.13

20.08

65.70

80543.00

463.00

32.98

20.08

65.73

106.30

106.30

26.60

60.90

106.30

106.30

108.20

7.53

0.73

328.64

53.35

53.35

121.77

53.35

121.77

3017.60

25.54

60.71

113.90

6.90

448.00

78676.00

20.08

65.73

1.02

2.43

16.75

2370.80

2370.80

2777.50

47.02

60.37

65.90

9.60

10.04 - 30.12

55.70 - 75.70

64434.40 - 96651.60

370.40 - 509.30

20.98 - 44.98

10.04 - 30.12

55.73 - 75.73

85.04 - 127.56

95.67 - 116.93

16.60 - 36.60

50.90 - 70.90

85.04 - 127.56

95.67 - 116.93

86.56 - 129.84

0.00 - 17.53

0.44 - 1.02

262.91 - 394.37

43.35 - 63.35

43.35 - 63.35

109.59 - 133.95

43.35 - 63.35

109.59 - 133.95

2414.08 - 3621.12

15.54 - 35.54

50.71 - 70.71

91.12 - 136.68

0.00 - 16.90

358.40 - 492.80

62940.80 - 94411.20

10.04 - 30.12

55.73 - 75.73

0.61 - 1.43

1.46 - 3.40

10.05 - 23.45

1422.48 - 3319.12

1422.48 - 3319.12

2222.00 - 3333.00

37.02 - 57.02

50.37 - 70.37

52.72 - 79.08

0.00 - 19.60

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

A3-7
TABLE A-3. In-House "Spike' Samples

Concentration (pCVL)

Lab Code Date Analysis Laboratory results Known Control

2s, n=1b Activity Limitsc Acceptance

SPW-4836

SPW-4836

SPW-4836

SPW-4836

SPW-5014

W-90705

W-90705

SPW-5237

SPW-5508

SPW-6019

SPF-6293

SPF-6293

SPAP-6309

SPAP-6309

SPAP-6311

SPW-6451

W-120105

W-120105

SPW-7440

SPW-7440

SPMI-7442

SPMI-7442

8/30/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

9/7/2005

9/7/2005

9/22/2005

9/26/2005

10/24/2005

11/4/2005

11/4/2005

11/7/2005

11/7/2005

1 1 /72005

11/10/2005

12/1/2005

12/1/2005

12/30/2005

12/30/2005

12/31/2005

12/31/2005

Cs-1i34

Cs-1 37

Sr-89

Sr-90

H-3

Gr. Alpha

Gr. Beta

C-14

Ni-63

Tc-99

Cs-134

Cs-1 37

Cs-1i34

Cs-137

Gr. Beta

H-3

Gr. Alpha

Gr. Beta

Cs-134

Cs-137

Cs-134

Cs-1 37

47.35 ±5.19

62.91 ± 9.08

11.04 ± 0.98

65.89 ± 2.79

77518.20 ± 753.80

24.61 ± 0.48

58.35 ± 0.49

2387.40 ± 11.00

20.64 ± 1.23

547.99 ± 6.69

941.30 ±44.10

2570.40 ± 105.30

41.24 ± 1.91

114.03 ±5.01

1.58 ± 0.02

77126.00 ±747.00

25.16 ±0.45

74.58 ± 0.81

42.67 ± 4.22

61.19 ±7.20

40.41 ±5.66

60.05 ± 7.80

47.02

60.37

9.60

65.90

77602.52

20.08

65.73

2370.80

16.70

539.22

886.00

2400.00

44.03

120.24

1.42

76749.00

20.08

65.73

42.03

59.91

42.03

59.91

37.02 - 57.02

50.37 - 70.37

0.00 - 19.60

52.72 - 79.08

62082.02 - 93123.02

10.04 - 30.12

55.73 - 75.73

1422.48 - 3319.12

10.02 - 23.38

377.45 - 700.99

797.40 - 974.60

2160.00 - 2640.00

34.03 - 54.03

108.22 - 132.26

1.14 - 11.42

61399.20 - 92098.80

10.04 - 30.12

55.73 - 75.73

32.03 - 52.03

49.91 - 69.91

32.03 - 52.03

49.91 - 69.91

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

a Liquid sample results are reported In pCi/Liter, air filters( pCitfilter), charcoal (pCi/m3

), and solid samples (pCVg).

b Laboratory codes as follows: W (water), Ml (milk), AP (air filter), SO (soil), VE (vegetation),

CH (charcoal canister), F (fish).

c Results are based on single determinations.

d Control limits are based on Attachment A, Page A2 of this report.

NOTE: For fish, Jello is used for the Spike matrix. For Vegetation, cabbage is used for the Spike matrix.

A3-8
TABLE A-4. In-House 'Blank Samples

Concentration (pCi/L)a

Lab Code Sample Date Analysis Laboratory results (4.66<;) Acceptance

Type LLD Activityb Criteria (4.66 ;)

W-11105

W-11105

SPW-765

SPAP-766

STW-2888

W-30105

W-30105

SPW-1837

SPW-1837

SPW-1837

SPW-1837

SPMI-1 839

SPMI-1839

SPMI-1839

SPCH-1934

SPW-2097

SPW-2923

SPW-2923

SPW-2896

w-60105

w-60105

SPF-3090

SPF-3090

water

water

water

Air Filter

water

water

water

water

water

water

water

Milk

Milk

Milk

Charcoal

water

water

water

water

water

water

Fish

Fish

1/11/2005

1/11/2005

2/18/2005

2/18/2005

2/28/2005

3/1/2005

3/1/2005

4/15/2005

4/15/2005

4/15/2005

4/15/2005

4/15/2005

4/15/2005

4/15/2005

4/18/2005

4/26/2005

5/31/2005

5/31/2005

6/1/2005

6/1/2005

6/1/2005

6/7/2005

6/7/2005

Gr. Alpha

Gr. Beta

H-3

Gr. Beta

Tc-99

Gr. Alpha

Gr. Beta

Cs-134

Cs-137

1-131

1-131 (G)

1-131

Sr-89

Sr-90

1-131(G)

Fe-55

Cs-134

Cs-1 37

H-3

Gr. Alpha

Gr. Beta

Cs-1 34

Cs-1 37

0.055

0.15

165.8

0.72

1.32

0.067

0.18

4.66

5.38

0.30

6.56

0.26

0.54

0.53

2.34

859.0

3.29

3.87

138.30

0.061

0.16

15.69

11.71

0.00 ± 0.038

-0.016 ± 0.10

7.4 ± 82.5

0.29 ± 0.48

0.45 ± 0.81

-0.007 ± 0.043

-0.04 ±0.11

-0.13 ± 0.16

-0.083 ± 0.14

-0.069 ± 0.56

0.88 ± 0.34

96.1 ±528.4

48.1 ± 85.9

0.002 ± 0.043

0.056 :: 0.11

1

3.2

200

3.2

10

1

3.2

10

10

0.5

20

0.5

5

1

9.6

1000

10

10

200

1

3.2

100

100

SPWSPW-4774

SPW-4776

SPMI-4835

SPMI-4835

SPMI-4835

SPMI-4835

SPMI-4835

SPMI-4835 d

SPW-4837

SPW-4837

SPW-4837

SPW-4837

SPW-4837

SPW-5015

SPW-5238

water

water

water

Milk

Milk

Milk

Milk

Milk

Milk

water

water

water

water

water

water

water

7/1/2005

8/24/2005

8/24/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

8/30/2005

9/22/2005

Ni-63

C-14

Fe-55

Co-60

Cs-1 34

Cs-137

1-131(G)

Sr-89

Sr-90

Co-60

Cs-1 34

Cs-137

Sr-89

Sr-90

H-3

C-14

1.60

12.18

833

4.42

4.18

6.25

5.37

0.66

0.66

2.48

3.85

3.00

0.63

0.63

142.8

17.10

0.79 ± 0.99

2.84 ± 6.45

275 ± 525

-0.23 ± 0.65

1.02 ± 0.41

0.25 ± 0.53

-0.035 ± 0.29

168 ±93

3.02 * 9.04

20

200

1000

10

10

10

20

5

1

10

10

10

5

1

200

200

A4-9
TABLE A-4. In-House 'Blank' Samples

Concentration (pCi/L)a

Lab Code Sample Date Analysis Laboratory results (4.66a) Acceptance

Type LLD Activityb Criteria (4.66 a)

W-90705

W-90705

SPW-5238

SPW-5509

SPW-6020

SPF-6294

SPF-6294

SPAP-6310

SPAP-6310

SPAP-6312

W-120105

W-120105

SPMI-7419

SPMI-7419

SPMI-7419

SPW-7421

SPW-7421

SPW-7441

SPW-7441

SPMI-7443

SPMI-7443

water

water

water

water

water

Fish

Fish

Air Filter

Air Filter

Air Filter

water

water

Milk

Milk

Milk

water

water

water

water

Milk

Milk

9/7/2005

9f7/2005

9/22/2005

9/26/2005

10/24/2005

11/4/2005

11/4/2005

1 17/2005

1 17/2005

11/7/2005

12/1/2005

12/1/2005

12/22/2005

12/22/2005

12/22/2005

12/22/2005

12/22/2005

12/30/2005

12/30/2005

12/30/2005

12/30/2005

Gr. Alpha

Gr. Beta

C-14

Ni-63

Tc-99

Cs-134

Cs-137

Cs-1 34

Cs-1i37

Gr. Beta

Gr. Alpha

Gr. Beta

Co-60

Cs-137

1-131(G)

Co-60

Cs-1 37

Cs-1 34

Cs-137

Cs-134

Cs-1 37

0.056

0.16

17.10

1.25

4.81

18.60

12.99

3.23

3.86

1.22

0.05

0.15

7.24

5.61

10.96

2.43

3.12

4.25

1.63

4.74

8.53

0.034 ± 0.04

0.082 ± 0.11

3.02 ± 9.04

1.23 ± 0.79

-1.75 ± 2.90

-0.64 ± 0.64

0.033 ± 0.04

-0.043 ± 0.11

1

3.2

200

20

10

100

100

100

100

3.2

1

3.2

10

10

20

10

10

10

10

10

10

a Liquid sample results are reported in pCi/Lter, air filters( pCi/filter), charcoal (pCUcharcoal canister), and solid samples (pCi/g).

b Activity reported is a net activity result. For gamma spectroscopic analysis, activity detected below the LLD value is not reported

c 1-131(G); iodine-131 as analyzed by gamma spectroscopy.

d Low levels of Sr-90 are still detected in the environment. A concentration of (1-5 pCiL) in milk is not unusual.

A4-10
TABLE A-5. In-House "Duplicate Samples

Concentration (pCi/L)a

Averaged

Lab Code Date Analysis First Result Second Result Result Acceptance

SW-62, 63

SW-62, 63

CF-95, 96

CF-95, 96

AP-791, 792

WW-353, 354

SO-383, 384

LW-431, 432

MI-486, 487

SW-511, 512

TD-628, 629

DW-538, 539

MI-564, 565

DW-50134, 5

SWU-893, 894

SW-925, 926

SW-950, 951

SW-950, 951

SW-973, 974

DW-50248, 9

DW-1264, 1265

AP-1955, 1956

AP-1890,1891

AP-2025, 2026

Mi-1346, 1347

AP-2048, 2049

AP-2081, 2082

SWU-1521, 1522

WW-1738,1739

SW-1857, 1858

LW-1911,1912

F-1976, 1977

MI-2111,2112

SWU-2158, 2159

DW-2349, 2350

SO-2305, 2306

SO-2305, 2306

SO-2305, 2306

SO-2305, 2306

SO-2305, 2306

MI-2260, 2261

F-2630, 2631

VE-2502, 2503

1/3/2005

1/3/2005

1/3/2005

1/3/2005

1/14/2005

1/19/2005

1/19/2005

1/27/2005

2/1/2005

2/1/2005

2/1/2005

2/3/2005

2/8/2005

2/11/2005

2/22/2005

2/25/2005

3/1/2005

3/1/2005

3/1/2005

3/16/2005

3/19/2005

3/28/2005

3/29/2005

3/29/2005

3/30/2005

3/30/2005

3/30/2005

3/31/2005

4/5/2005

4/13/2005

4/14/2005

4/18/2005

4/26/2005

4/26/2005

4/29/2005

5/2/2005

5/2/2005

5/2/2005

5/2/2005

5/2/2005

5/3/2005

5/5/2005

5/10/2005

Gr. Beta

K-40

Gr. Beta

K-40

Be-7

Gr. Beta

H-3

Gr. Beta

K-40

1-131

H-3

Gr. Beta

K-40

Gr. Beta

Gr. Beta

Gr. Beta

Gr. Beta

Gr. Beta

1-131

Gr. Alpha

1-131

Be-7

Be-7

Be-7

K-40

Be-7

Be-7

Gr. Beta

Gr. Beta

Gr. Beta

Gr. Beta

K-40

K-40

Gr. Beta

1-131

Cs-1 37

Gr. Alpha

Gr. Beta

K-40

Sr-90

K-40

K-40

Gr. Alpha

3.01 * 0.57

2.00 ± 0.20

6.26 ± 0.23

5.68 ± 0.59

0.057 ± 0.017

8.37 ± 1.21

453.50 ± 107.20

2.45 ± 0.54

1319.40 ± 163.60

0.37 ± 0.22

489663 ± 1918

3.93 ± 1.18

1316.20 ± 171.10

18.41 ± 0.98

4.00 ± 0.96

5.97 ± 1.51

0.92 ± 0.27

2.06 ± 0.40

1.08 ± 0.19

5.27 ± 1.06

0.54 ± 0.21

0.071 ±0.009

0.060 ±0.013

0.063 ± 0.012

1252.80 ± 120.50

0.075 ±0.018

0.073 ±0.016

2.83 ± 1.16

11.44~± 1.17

7.04 ± 1.71

2.50 ± 0.63

3.09 ± 0.60

1291.50 ± 177.90

3.69 ± 0.74

0.58 ± 0.27

0.11 ±0.05

7.55 ± 2.88

28.74 ± 2.57

21.51 ± 1.22

32.90 ± 9.90

1028.10 ±99.36

3.08 ± 0.46

0.06 ± 0.03

2.39 ± 0.58

2.10 ± 0.20

6.28 ± 0.23

5.37 ± 0.48

0.07 ± 0.04

10.28 ± 1.34

417.90 ± 106.00

2.20 ± 0.54

1177.20 ± 179.70

0.44 ± 0.23

491225 ± 1915

3.62 ± 1.10

1292.60 *154.40

16.76 ± 0.98

4.20 ± 0.72

6.14 ± 1.55

1.21 ± 0.27

2.29 ± 0.44

0.92 ± 0.18

4.17 ± 0.90

0.73 ± 0.20

0.071 ± 0.009

0.069 ± 0.013

0.071 ± 0.011

1334.10 ± 106.60

0.071 ± 0.015

0.061 ± 0.018

3.46 ± 1.23

11.14 ± 1.62

9.96 ± 1.65

3.23 ± 0.67

3.33 ± 0.40

1323.70 ± 108.80

3.54 ± 0.66

0.49 ± 0.27

0.11 ±0.04

12.41 ± 3.38

28.17 ± 2.52

21.42 ± 1.24

29.60 ± 13.90

1206.70 ± 118.50

3.04 ± 0.51

0.07 ± 0.04

2.70 ± 0.41

2.05 t 0.14

6.27 + 0.16

5.53 ± 0.38

0.06 ± 0.02

9.32 ± 0.90

435.70 ± 75.38

2.33 + 0.38

1248.30 ± 121.51

0.40 ± 0.16

490444 ± 1355

3.78 ± 0.81

1304.40 ± 115.23

17.59 ± 0.69

4.10 t 0.60

6.06 ± 1.08

1.07 ± 0.19

2.18 ± 0.30

1.00 ±0.13

4.72 ± 0.70

0.63 ± 0.15

0.071 ± 0.006

0.065 ± 0.009

0.067 ± 0.008

1293.45 ± 80.44

0.073 ± 0.012

0.067 ± 0.012

3.14 ± 0.85

11.29 ± 1.00

8.50 ± 1.19

2.86 ± 0.46

3.21 ±0.36

1307.60 ± 104.27

3.62 ± 0.50

0.53 ± 0.19

0.11 ±0.03

9.98 ± 2.22

28.46 ± 1.80

21.47 ± 0.87

31.25 ± 8.53

1117.40 ± 77.32

3.06 ± 0.34

0.07 ± 0.03

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

A5-11
TABLE A-5. In-House 'Duplicate Samples

Concentration (pCj/L)a

Averaged

Lab Code Date Analysis First Result Second Result Result Acceptance

VE-2502, 2503

VE-2502, 2503

G-2546, 2547

G-2546, 2547

SS-2787, 2788

SS-2787, 2788

SO-3056, 3057

SO-3056, 3057 b

SS-3175, 3176

SO-2865, 2866

SO-2865, 2866

SO-2865, 2866

DW-2935, 2936

SWU-3103, 3104

G-2958, 2959

G-2958, 2959 b

G-2958, 2959

BS-4089, 4090

BS-4089, 4090

DW-50527, 8

VE-3278, 3279

MI-3299, 3300

BS-3348, 3349

BS-3348, 3349

BS-3348, 3349

DW-3486, 3487

SWT-3631, 3632

W-3507, 3508

VE-3555, 3556

VE-3555, 3556

AP-3781, 3782

LW-3610, 3611

SW-3760, 3761

5/10/2005

5/10/2005

5/11/2005

5/11/2005

5/18/2005

5/18/2005

5/19/2005

5/19/2005

5/23/2005

5/25/2005

5/25/2005

5/25/2005

5/27/2005

6/1/2005

6/1/2005

6/1/2005

6/1/2005

6/3/2005

6/3/2005

6/8/2005

6/13/2005

6/15/2005

6/17/2005

6/17/2005

6/17/2005

6/28/2005

6/28/2005

6/29/2005

6/29/2005

6/29/2005

6/29/2005

6/30/2005

6/30/2005

Gr. Beta

K-40

Be-7

K-40

Cs-137

K-40

Cs-137

K-40

K-40

Cs-1 37

Gr. Beta

K-40

1-131

Gr. Beta

Be-7

Gr. Beta

K-40

Co-60

Cs-1 37

Gr. Alpha

K-40

K-40

Co-60

Cs-1 37

K-40

Gr. Beta

Gr. Beta

H-3

Gr. Beta

K-40

Be-7

Gr. Beta

Gr. Beta

3.81 ± 0.10

3.79 ± 0.40

0.81 ± 0.39

9.43 ± 1.00

0.13 ±0.04

12.44 ±0.76

0.18 ±0.04

20.06 ± 1.10

6.06 ± 0.44

0.18 ± 0.04

32.95 ± 2.48

21.93 ± 0.97

0.51 ±0.34

3.29 ± 0.49

1.06 ± 0.40

8.06 ±0.07

5.93 ± 0.73

0.11 ±0.02

0.60 ± 0.05

11.58 ± 1.31

6.34 ± 0.59

1215.40 ± 110.20

0.20 ± 0.04

2.59 ± 0.10

11.57 ± 0.81

0.97 ± 0.54

2.12 ±0.53

38717 ±382

7.53 ±0.18

5.70 ± 0.52

0.09 ± 0.02

1.37 ± 0.35

9.70 ± 1.63

3.86 ± 0.10

4.30 ± 0.59

1.25 ± 0.38

7.96 ± 0.85

0.14 ± 0.05

13.33 ± 0.83

0.17 ± 0.01

21.73 ± 0.36

5.96 ± 0.61

0.18 ± 0.03

33.88 ± 2.36

22.32 ± 0.98

0.56 ± 0.30

3.75 ± 0.66

1.21 ± 0.28

7.79 ± 0.07

6.05 ± 0.28

0.10 ± 0.02

0.62 ± 0.05

13.52 ± 1.43

7.29 ± 0.68

1250.70 ± 106.70

0.22 ± 0.04

2.51 ± 0.07

11.82 ± 0.76

1.67 ± 0.58

1.62 ± 0.56

38017 ±535

7.56 *0.18

5.64 ± 0.53

0.08 ± 0.02

1.40 ± 0.36

9.77 ± 1.61

3.83 ± 0.07

4.04 ± 0.36

1.03 ± 0.27

8.70 ± 0.66

0.13 ± 0.03

12.88 ± 0.56

0.18 ± 0.02

20.90 ± 0.58

6.01 ± 0.38

0.18 ± 0.02

33.41 ± 1.71

22.13 ± 0.69

0.53 ± 0.23

3.52 ± 0.41

1.14 ± 0.24

7.93 ± 0.05

5.99 ± 0.39

0.11 ±0.02

0.61 ± 0.04

12.55 ± 0.97

6.81 ± 0.45

1233.05 ± 76.70

0.21 ± 0.03

2.55 ± 0.06

11.69 ± 0.56

1.32 ± 0.40

1.87 ± 0.39

38367 ± 329

7.55 ± 0.13

5.67 ± 0.37

0.09 ± 0.01

1.39 ± 0.25

9.73 ±1.15

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Fail

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Fail

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

E-3654, 3655

E-3654, 3655

MI-3676, 3677

DW-3739,3740

W-3808,3809

DW-3938,3939

VE-3896, 3897

MI-3963, 3964

DW-4068,4069

7/5/2005

7/5/2005

7/5/2005

7/5/2005

7/6/2005

7/8/2005

7/12/2005

7/13/2005

7/15/2005

Gr. Beta

K-40

K-40

1-131

H-3

1-131

K-40

K-40

1-131

1.76 ± 0.07

1.49 ± 0.25

1383.90 ± 116.20

1.93 ± 0.24

4189.61 ± 196.68

1.11 ± 0.30

3.44 ± 0.62

1438.70 ±102.80

0.64 ± 0.27

1.69 ± 0.07

1.05 ± 0.21

1428.20 ± 125.40

2.18 ± 0.23

4438.33 ± 201.39

1.26 ± 0.31

3.60 ± 0.36

1351.80 ± 100.80

0.91 ± 0.28

1.72

1.27

1406.05

2.05

4313.97

1.18

3.52

1395.25

± 0.05

± 0.16

± 85.48

±0.17

±140.75

± 0.22

± 0.36

± 71.99

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

0.78 ± 0.20 Pass

A5-12
TABLE A-5. In-House *Duplicate' Samples

Concentration (pCi/L)a

Averaged

Lab Code Date Analysis First Result Second Result Result Acceptance

VE-4290, 4291 7/26/2005

VE-4290, 4291 7/26/2005

SWU-4311, 4312 7/26/2005

SWU-4311, 4312 7/26/2005

G-4383, 4384 8/1/2005

0-4383, 4384 8/1/2005

'G-4383, 4384 8/1/2005

MI-4425, 4426 8/1/2005

TD-4446, 4447 8/1/2005

SL-4473, 4474 8/4/2005

SL-4473, 4474 8/4/2005

VE-4532, 4533 8/5/2005

VE-4618, 4619 8/9/2005

VE-4618, 4619 8/9/2005

VE-4618, 4619 8/9/2005

F-4639, 4640 8/11/2005

F-4639, 4640 8/11/2005

F-4639, 4640 8/11/2005

DW-4730, 4731 8/12/2005

MI-4855, 4856 8/28/2005

MI-4855, 4856 8/28/2005

MI-4945, 4946 8/31/2005

MI-4945, 4946 8/31/2005

TD-4921, 4922 9/1/2005

VE-4900, 4901 9/2/2005

VE-4900, 4901 9/2/2005

DW-50769, 50770 9/2/2005

VE-4990, 4991 9/6/2005

MI-5011, 5012 9/8/2005

VE-5119, 5120 9/12/2005

VE-5119, 5120 9/12/2005

VE-5119, 5120 9/12/2005

LW-5361, 5362 9/12/2005

SW-5098, 5099 9/13/2005

LW-5178, 5179 9/14/2005

DW-5239, 5240 9/16/2005

CF-5432, 5433 9/19/2005

CF-5432, 5433 9/19/2005

MI-5292, 5293 9/21/2005

BS-5340, 5341 9/23/2005

BS-5340, 5341 9/23/2005

Gr. Alpha

Gr. Beta

Gr. Beta

H-3

Be-7

Gr. Beta

K-40

K-40

H-3

Gr. Beta

K-40

Gr. Beta

Gr. Alpha

Gr. Beta

K-40

Cs-1 37

Gr. Beta

K-40

1-131

K-40

Sr-90

K-40

Sr-90

H-3

Gr. Beta

K-40

Gr. Alpha

K-40

K-40

Gr. Alpha

Gr. Beta

K-40

Gr. Beta

1-131

Gr. Beta

1-131

Be-7

K-40

K-40

Be-7

Cs-137

0.11 ±0.04

4.55 ± 0.13

2.62 ± 0.64

192.30 ± 92.90

2.06 ± 0.49

8.76 ± 0.22

6.74 ± 0.64

1358.10 ± 169.20

563.00 ± 252.00

5.44 ± 0.48

2.91 ± 0.83

31.20 ± 1.20

0.09 ± 0.05

4.60 ± 0.13

4.19 ± 0.46

0.05 ± 0.02

3.33 ± 0.11

2.62 ± 0.57

0.82 ± 0.23

1341.50 ± 107.70

0.77 ± 0.37

1388.90 ± 158.90

0.67 ± 0.34

5737.00 ± 266.00

3.40 ± 0.06

2.15 ± 0.27

6.17 ± 1.42

18.81 ± 1.12

1584.00 ± 194.00

0.10 ±0.06

6.05 ±0.18

4.61 ±0.46

1.09 ± 0.33

0.44 ± 0.22

2.92 ± 0.56

0.45 ± 0.27

0.91 ± 0.40

1.43 ± 0.34

1228.80 ± 78.13

1286.10 ± 550.80

726.97 ± 76.24

0.05 ± 0.03

4.69 ± 0.14

1.67 ± 0.37

304.60 ± 97.40

1.76 ± 0.29

8.40 ± 0.20

6.88 ± 0.92

1267.90 ± 164.40

529.00 ± 251.00

4.57 ± 0.42

2.74 ± 0.54

31.70 ± 1.20

0.09 ± 0.04

4.54 ± 0.12

4.34 ± 0.47

0.05 ± 0.02

3.37 ± 0.10

2.58 ± 0.59

0.83 ± 0.25

1340.00 ± 114.70

0.87 ± 0.37

1307.50 ± 165.20

0.82 ± 0.36

5860.00 ± 269.00

3.51 ± 0.06

2.27 ± 0.24

6.08 ± 1.46

19.52 ± 0.86

1707.60 ± 173.00

0.09 ± 0.05

5.92 ± 0.17

4.74 ± 0.69

1.18 ±0.34

0.31 ± 0.20

2.95 ± 0.59

0.55 ± 0.29

0.64 ± 0.30

1.38 ± 0.43

1297.00 ± 81.03

1222.90 ± 394.40

677.49 ± 70.03

0.08 ± 0.03

4.62 ±0.09

2.15 ± 0.37

248.45 ± 67.30

1.91 ± 0.28

8.58 ± 0.15

6.81 ± 0.56

1313.00 ± 117.96

546.00 ± 177.84

5.00 ± 0.32

2.82 ± 0.49

31.45 ± 0.85

0.09 ± 0.03

4.57 ± 0.09

4.27 ± 0.33

0.05 ± 0.02

3.35 ± 0.07

2.60 ± 0.41

0.83 ± 0.17

1340.75 ± 78.67

0.82 ± 0.26

1348.20 ± 114.61

0.75 ± 0.25

5798.50 ± 189.15

3.45 ± 0.04

2.21 ± 0.18

6.13 ± 1.02

19.17 ±0.71

1645.80 ± 129.97

0.10 ± 0.04

5.98 ± 0.12

4.68 ± 0.41

1.13 ± 0.24

0.38 ± 0.15

2.93 ± 0.41

0.50 ± 0.20

0.78 ± 0.25

1.41 ± 0.27

1262.90 ± 56.28

1254.50 ± 338.72

702.23 ± 51.76

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

A5-13
TABLE A-5. In-House Duplicate' Samples

Concentration (pCG/L)a

Averaged

Lab Code Date Analysis First Result Second Result Result Acceptance

BS-5340, 5341

DW-5382, 5383

MI-5405, 5406

AP-5769, 5770

AP-5983, 5984

AP-5878, 5879

G-5526, 5527

G-5526, 5527

G-5526, 5527

VE-5721, 5722

VE-5721, 5722

VE-5721, 5722

CF-5695, 5696

CF-5695, 5696

LW-6129, 6130

LW-6129, 6130

DW-50844, 5

LW-5748, 5749 c

AP-6485, 6486

SWU-6156, 6157

VE-6186, 6187

LW-6203, 6204

SO-6270, 6271

SO-6270, 6271

SO-6270, 6271

TD-6320, 6321

SO-6605, 6606

CF-6509, 6510

SW-6638, 6639

SO-6887, 6888

SO-6887, 6888

SO-6887, 6888

SWT-6721, 6722

VE-6775, 6776

LW-6743, 6744

DW-51023, 4

SWT-7282, 7283

9/23/2005

9/23/2005

9/27/2005

9/27/2005

9/27/2005

9/29/2005

10/3/2005

10/3/2005

10/3/2005

10/10/2005

10/10/2005

10/10/2005

10/11/2005

10/11/2005

10/11/2005

10/11/2005

10/11/2005

10/12/2005

10/20/2005

10/25/2005

10/26/2005

10/27/2005

10/28/2005

10/28/2005

10/28/2005

11/1/2005

11/11/2005

11/14/2005

11/22/2005

11/22/2005

11/22/2005

11/22/2005

11/29/2005

11/29/2005

11/30/2005

12/2/2005

12/27/2005

K-40

1-131

K-40

Be-7

Be-7

Be-7

Be-7

Gr. Beta

K-40

Gr. Alpha

Gr. Beta

K-40

Be-7

K-40

Gr. Beta

H-3

Gr. Beta

Gr. Beta

Be-7

Gr. Beta

K-40

Gr. Beta

Cs-137

Gr. Beta

K-40

H-3

Gr. Beta

K-40

1-131

Gr. Alpha

Gr. Beta

K-40

Gr. Beta

Gr. Beta

Gr. Beta

Gr. Alpha

Gr. Beta

12404 ± 1154

0.79 ± 0.31

1324.80 ± 112.20

0.08 ± 0.01

0.08 ± 0.01

0.06 ± 0.01

4.03 ± 0.62

8.10 ±0.30

4.93 ± 0.67

0.07 ± 0.05

5.09 ± 0.15

4.27 ± 0.43

2.70 ± 0.37

11.79 ± 0.86

1.34 ± 0.25

304.35 ± 95.31

5.30 ± 1.50

1.09 ± 0.25

0.10 ± 0.03

4.69 ± 1.34

2.90 ± 0.49

2.92 ± 0.62

0.33 ± 0.03

26.85 ± 2.78

13.67 ± 0.74

444202 ± 1770

18.22 ±2.23

0.85 ± 0.14

0.95 ± 0.35

6.80 ± 2.92

19.27 ±2.16

14.29 ± 1.11

0.98 ± 0.31

12.75 ± 0.28

3.19 ± 0.47

0.55 ± 1.40

1.62 ± 0.37

13033 ±983

0.53 ± 0.31

1366.80 ± 99.44

0.09 ± 0.02

0.08 ± 0.01

0.07 ± 0.01

4.07 ± 0.80

8.80 ± 0.40

6.00 ± 0.72

0.08 ± 0.06

5.00 ± 0.16

4.20 ±0.34

2.80 ± 0.34

13.11 ±0.68

1.85 ± 0.29

369.23 ± 97.88

4.20 ±1.40

1.89 ± 0.28

0.09 ± 0.03

4.18 ± 1.34

2.83 ± 0.51

3.09 ± 0.66

0.34 ± 0.04

22.25 ± 2.41

14.02 ± 0.76

446633 ± 1775

18.47 ±2.22

0.99 ± 0.22

0.67 ± 0.31

10.27 ± 3.26

18.43 ± 2.21

13.78 ±0.78

0.87 ± 0.31

13.16 ±0.21

2.50 ± 0.44

2.21 ± 1.31

1.85 ± 0.38

12719 ± 758

0.66 ± 0.22

1345.80 ± 74.96

0.08 ± 0.01

0.08 ± 0.01

0.07 ± 0.01

4.05 ± 0.51

8.41 ± 0.24

5.47 ± 0.49

0.08 ± 0.04

5.05 ± 0.11

4.23 ± 0.27

2.75 ± 0.25

12.45 ± 0.55

1.59 ± 0.19

336.79 ± 68.31

4.75 ± 1.03

1.49 ± 0.19

0.09 ± 0.02

4.44 ± 0.95

2.87 ± 0.35

3.01 ± 0.45

0.33 ± 0.03

24.55 ± 1.84

13.85 ± 0.53

445418 ± 1253

18.35 ± 1.57

0.92 ±0.13

0.81 ±0.23

8.53 ± 2.19

18.85 ± 1.54

14.03 ± 0.68

0.93 ± 0.22

12.96 ±0.18

2.85 ± 0.32

1.38 ± 0.96

1.74 ± 0.27

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Fail

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Note: Duplicate analyses are performed on every twentieth sample received in-house. Results are not listed for those

analyses with activities that measure below the LLD.

a Results are reported in units of pCVL, except for air filters (pCUFilter), food products, vegetation, soil, sediment (pCVg).

b 600 minute count time or longer, resulting in lower error.

c Recount of W-5748, 2.38 ± 0.85 pCVL Averaged result; 2.14 ± 0.45 pCVL

A5-14
A5-15
TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP)a.

Concentration b

Known Control

Lab Codec Date Analysis Laboratory result Activity Limits d Acceptance

STW-1 045 01/01/05 Gr. Alpha

STW-1045 01/01/05 Gr. Beta

0.45 ±0.10

1.90 o 0.10

0.53

1.67

0.00 - 1.05

0.84 - 2.51

Pass

Pass

STW-1046

STW-1046

STW-1046

STW-1046

STW-1046

STW-1046

STW-1 046

STW-1 046

STW-1 046

STW-1046

STW-1046

STW-1046

STW-1046

STW-1046

STW-1046

STW-1046

STVE-1 047

STVE-1 047

STVE-1047

STVE-1047

STVE-1 047

STVE-1 047

STSO-1 048

STSO-1048

STSO-1048

STSO-1048

STSO-1 048

STSO-1048

STSO-1048

STSO-1048

STSO-1048

STSO-1048

STSO-1048

STSO-1048

STSO-1048

STSO-1 048

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

Am-241

Co-57

Co-60

Cs-1 34

Cs-137

Fe-55

H-3

Mn-54

Ni-63

Pu-238

Pu-239/40

Sr-90

Tc-99

U-233/4

U-238

Zn-65

Co-57

Co-60

Cs-1i34

Cs-137

Mn-54

Zn-65

Am-241

Co-57

Co-60

Cs-134

Cs-1 37

K-40

Mn-54

Ni-63

Pu-238

Pu-239/40

Sr-90

U-23314

U-238

Zn-65

1.62 ± 0.12

239.40 ± 1.20

248.70 ± 1.00

115.50 ± 1.80

328.50 ± 1.70

64.90 ± 7.00

304.00 ± 9.70

334.80 ± 1.90

7.10 ± 1.60

0.01 ± 0.02

2.50 ±0.14

0.70 ± 0.80

43.20 ± 1.40

3.31 ±0.20

3.38 ± 0.20

538.40 ± 3.80

10.60 ±0.20

3.00 ± 0.20

4.80 ± 0.40

4.10 ± 0.30

5.10 ± 0.30

6.20 ± 0.50

96.60 ± 10.00

264.00 ± 2.00

226.50 ± 2.20

760.60 t 3.70

336.20 ± 3.60

663.70 ± 18.00

541.30 ± 3.90

924.30 ± 17.20

0.60 ± 0.80

78.00 ± 4.80

514.60 ± 18.70

47.90 ± 4.00

226.30 ± 8.60

851.30 ± 7.30

1.72

227.00

251.00

127.00

332.00

75.90

280.00

331.00

9.00

0.02

2.40

0.00

42.90

3.24

3.33

496.00

9.88

3.15

5.00

4.11

5.18

6.29

109.00

242.00

212.00

759.00

315.00

604.00

485.00

1220.00

0.48

89.50

640.00

62.50

249.00

810.00

1.20 - 2.24

158.90 - 295.10

175.70 -326.30

88.90 - 165.10

232.40 -431.60

53.13 -98.67

196.00 -364.00

231.70 - 430.30

0.00 -20.00

0.00 - 1.00

1.68 -3.12

0.00 - 5.00

30.03 - 55.77

2.27 - 4.21

2.33 - 4.33

347.20 - 644.80

6.92 - 12.84

2.21 -4.10

3.50 - 6.50

2.88 - 5.34

3.63 - 6.73

4.40 -8.18

76.30 - 141.70

169.40 -314.60

148.40 -275.60

531.30 -986.70

220.50 - 409.50

422.80 - 785.20

339.50 - 630.50

854.00 - 1586.00

0.00 - 1.00

62.65 - 116.35

448.00 - 832.00

43.75 - 81.25

174.30 - 323.70

567.00 - 1053.00

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

STAP-1050 01/01/05 Gr. Alpha

STAP-1050 01/01/05 Gr. Beta

0.11 ± 0.03

0.38 ± 0.05

0.23

0.30

0.00 - 0.46

0.15 -0.45

Pass

Pass

A6-16
TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP)a.

Concentration b

Known Control

Lab Codec Date Analysis Laboratory result Activity Limits d Acceptance

STAP-1049

STAP-1049

STAP-1049

STAP-1 049

STAP-1049

STAP-1049

STAP-1049

STAP-1049

STAP-1 049 e

STAP-1049

STAP-1 049

STAP-1 049

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

01/01/05

Am-241

Co-57

Co-60

Cs-1i34

Cs-137

Mn-54

Pu-238

Pu-239/40

Sr-90

U-23314

U-238

Zn-65

0.10 ±0.04

4.76 ± 0.64

2.84 ± 0.22

3.54 ± 0.37

2.20 ± 0.27

3.15 ± 0.21

0.16 ± 0.04

0.17 ± 0.02

2.24 ± 0.34

0.34 ± 0.02

0.35 ± 0.02

3.12 ±0.15

0.10

4.92

3.03

3.51

2.26

3.33

0.20

0.17

1.35

0.34

0.35

3.14

0.07 - 0.13

3.44 - 6.40

2.12 - 3.94

2.46 - 4.56

1.58 - 2.94

2.33 - 4.33

0.14 - 0.25

0.14 - 0.25

0.95 - 1.76

0.24 - 0.44

0.25 - 0.46

2.20 - 4.08

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Fail

Pass

Pass

Pass

STW-1061

STW-1061

STW-1061

STW-1061

STW-1061

STW-1061

STW-1061

STW-1061

STW-1061

STW-1 061

STW-1061

STW-1 061

STW-1061

STW-1 061

STW-1061

STW-1061

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

Am-241

Co-57

Co-60

Cs-134

Cs-137

Fe-55

H-3

Mn-54

Ni-63

Pu-238

Pu-239/40

Sr-90

Tc-99

U-233/4

U-238

Zn-65

STW-1062

STW-1062

STSO-1063'

STSO-1063

STSO-1063

STSO-1063

STSO-1063

STSO-1063

STSO-1063

STSO-1063

STSO-1063

STSO-1063

STSO-1063

STSO-1063

STSO-1 063

STSO-1063

2.21 ± 0.13

293.20 ± 7.30

275.70 ± 1.30

171.80 ±4.00

342.10 ± 2.20

167.80 ± 9.30

514.20 ± 12.60

437.00 ± 2.50

105.10 ±3.60

1.64 ± 0.12

2.32 ± 0.13

9.20 ± 1.30

72.30 ± 2.30

4.11 ±0.18

4.14 ±0.18

364.60 ± 4.90

0.57 ± 0.05

1.36 ± 0.05

48.40 ± 3.90

608.30 ± 2.80

322.70 ± 2.40

632.10 ± 5.20

512.40 ±4.20

720.50 ± 19.00

516.80 ± 5.10

366.50 ± 13.30

68.80 ± 15.00

0.00 ± 0.00

602.90 ± 17.20

61.50 ± 1.00

164.50 ± 16.70

874.70 ± 8.40

2.23

272.00

261.00

167.00

333.00

196.00

527.00

418.00

100.00

1.91

2.75

8.98

66.50

4.10

4.26

330.00

0.79

1.35

81.10

524.00

287.00

568.00

439.00

604.00

439.00

445.00

60.80

0.00

757.00

52.50

168.00

823.00

1.56 - 2.90

190.40 - 353.60

182.70 - 339.30

116.90 - 217.10

233.10 - 432.90

137.20 - 254.80

368.90 - 685.10

292.60 - 543.40

70.00 - 130.00

1.34 - 2.48

1.93 - 3.58

6.29 - 11.67

46.55 - 86.45

2.87 - 5.33

2.98 - 5.54

231.00 - 429.00

0.21 - 1.38

0.85 - 1.92

56.77 - 105.43

366.80 - 681.20

200.90 - 373.10

397.60 - 738.40

307.30 - 570.70

422.80 - 785.20

307.30 - 570.70

311.50 - 578.50

42.56 - 79.04

0.00 - 0.00

529.90 - 984.10

36.75 - 68.25

117.60 - 218.40

576.10 - 1070.00

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Fail

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

07/01/05 Gr. Alpha

07/01/05 Gr. Beta

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

Am-241

Co-57

Co-60

Cs-134

Cs-137

K-40

Mn-54

Ni-63

Pu-238

Pu-239/40

Sr-90

U-233/4

U-238

Zn-65

A6-17
TABLE A-6. Department of Energy's Mixed Analyte Performance Evaluation Program (MAPEP)a.

Concentration b

Known Control

Lab Codec Date Analysis Laboratory result Activity Limits d Acceptance

STVE-1064

STVE-1 064

STVE-1064

STVE-1064

STVE-1064

STVE-1 064

STVE-1064

STVE-1064

STVE-1 064

STVE-1064

STVE-1 064

STVE-1064

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

Am-241

Co-57

Co-60

Cs-1 34

Cs-1 37

Mn-54

Pu-238

Pu-239/40

Sr-90

U-233/4

U-238

Zn-65

STAP-1 065 07/01/05 Gr. Alpha

STAP-1065 07/01/05 Gr. Beta

0.18 *0.03

15.90 ± 0.20

4.80 ± 0.10

4.60 ± 0.20

5.90 ± 0.30

7.20 ±0.20

0.04 ± 0.02

0.13 ±0.02

2.80 ± 0.30

0.28 * 0.03

0.33 ± 0.04

11.00 ± 0.50

0.30 ± 0.04

0.97 ± 0.06

0.14 ±0.03

5.81 ±0.17

2.79 ±0.14

3.67 ±0.12

2.93 ± 0.23

4.11 ±0.26

0.11 ±0.02

0.10 ±0.01

2.25 ± 0.29

0.28 ± 0.02

0.28 ± 0.02

4.11 ±0.26

0.23

13.30

4.43

4.09

5.43

6.57

0.00

0.16

2.42

0.33

0.35

10.20

0.48

0.83

0.16

6.20

2.85

3.85

3.23

4.37

0.10

0.09

2.25

0.27

0.28

4.33

0.16 - 0.30

9.31 - 17.29

3.10 - 5.76

2.86 - 5.32

3.80 - 7.06

4.60 - 8.54

0.00 - 1.00

0.11 - 0.21

1.69 - 3.15

0.23 - 0.43

0.24 - 0.45

7.14 - 13.26

0.00 - 0.80

0.55 - 1.22

0.11 - 0.21

4.34 - 8.06

2.00 - 3.71

2.70 - 5.01

2.26 - 4.20

3.06 - 5.68

0.07 - 0.13

0.06 - 0.12

1.58 - 2.93

0.19 - 0.35

0.20 - 0.37

3.06 - 5.68

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

Pass

STAP-1066

STAP-1066

STAP-1 066

STAP-1066

STAP-1 066

STAP-1066

STAP-1 066

STAP-1 066

STAP-1 066

STAP-1066

STAP-1066

STAP-1066

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

07/01/05

Am-241

Co-57

Co-60

Cs-1 34

Cs-1 37

Mn-54

Pu-238

Pu-239/40

Sr-90

U-233/4

U-238

Zn-65

a Results obtained by Environmental, Inc., Midwest Laboratory as a participant in the Department of Energy's

Mixed Analyte Performance Evaluation Program, Idaho Operations office, Idaho Falls, Idaho

b Results are reported in units of Bq/kg (soil), Bq/L (water) or Bq/total sample (filters, vegetation) as requested by the

Department of Energy.

c Laboratory codes as follows: STW (water), STAP (air filter), STSO (soil), STVE (vegetation).

d MAPEP results are presented as the known values and expected laboratory precision (1 sigma, 1 determination)

and control limits as defined by the MAPEP.

e The strontium carbonate precipitates were redissolved and processed. The average of the three analyses was 1.34 1

although the recovery was only 30%. The result of a new analysis was 1.56 pCUL.

Incorrect sample weight used in calculation. Result of recalculation: 97.0 ± 7.8 Bq/kg.

A6-1i8
ATTACHMENT F

DATA GRAPHS

3 Pages Follow
Palisades Air Particulate

Gross Beta

Pre-Operational vs. Operational

00m0

0

CO)

0.E

1968-1969 1999 2000 2001 2002 2003 2004 2005

|o Control * Indicator

0)I
Lake Water Gross Beta

2000 to 2005

2.5

2.0 -

1.5 -

0

OL

1.0-

0.5 4-

0.0 -!-

2000 2001 2002 2003 2004 2005

Year

I* EPAL PAL Lake Lake In *MSH Raw O SH Treated 11 LudingtonI In ESH Raw OSH Treated EJ Ludington

co")
Palisades Monthly Thermoluminescent Dosimeters

Pre-Operational vs. Operational

10-

9

8-

1

0

_E 5 , E__

E 4 l t

0\ _T

1968-69 1999 2000 2001 2002 2003 2004 2005

* Inner Ring U Outer Ring 0 Control|

cO3