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Final Close Out Report Dix Area Sanitary Landfill 

JB MDL, New Jersey 

i

TABLE OF CONTENTS

I. Introduction ......................................................................................................................................... 1 

II. Summary of Site Conditions .............................................................................................................. 1 

A. Background Summary ...................................................................................................................... 1 

B. Remedial Investigation/Feasibility Study ......................................................................................... 3 

C. Selected Remedy Remedial Action and Objectives .......................................................................... 3 

D. Institutional Controls ........................................................................................................................ 5 

E. Final Site Inspection ......................................................................................................................... 5 

III. Monitoring Results .............................................................................................................................. 5 

A. Air Monitoring .................................................................................................................................. 5 

B. Groundwater Monitoring .................................................................................................................. 6 

C. Surface Water Monitoring ................................................................................................................ 6 

D. Sediment Monitoring ........................................................................................................................ 7 

IV. Summary of Operation and Maintenance ........................................................................................ 7 

V. Clean-up Activity Quality Assurance/Quality Control ................................................................... 8 

VI. Five-year Review ................................................................................................................................. 8 

A. Five-year Review Process ................................................................................................................. 8 

B. Summary of the Third Five-year Review (Plexus, 2010) ................................................................. 9 

VII. Site Completion Criteria .................................................................................................................... 9 

VIII.Bibliography...................................................................................................................................... 10 

ATTACHMENTS

Attachment A – Tables

Attachment B – Figures

Attachment C – 2009 Ecological Risk Assessment.
Final Close Out Report Dix Area Sanitary Landfill 

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ACRONYMS

ACO Administrative Consent Order 

ARARs Applicable or Relevant and Appropriate Requirements 

CEA Classification Exemption Area 

CERCLA Comprehensive Environmental Response, Compensation, and Liability Act 

COCs contaminants of concern 

DDE Dichlorodiphenyldichloroethylene 

DDT Dichlorodiphenyltrichloroethane 

FFA Federal Facility Agreement 

FCOR Final Close Out Report 

FY fiscal year 

ICs institutional controls 

JB MDL Joint Base McGuire-Dix-Lakehurst 

LTM long-term monitoring 

LTMP long-term monitoring plan 

LUC land use control 

NJDEP New Jersey Department of Environmental Protection 

NJPDES New Jersey Pollutant Discharge Elimination System 

NJSA New Jersey Statutes Annotated 

NPL National Priorities List 

O&M Operation and Maintenance 

PDO Property Disposal Office 

Plexus Plexus Scientific Corporation 

RCRA Resource Conservation and Recovery Act 

RI/FS Remedial Investigation/Feasibility Study 

ROD Record of Decision 

SVOC Semi-Volatile Organic Compound 

USACE United States Army Corps of Engineers 

USAEC United States Army Environmental Command 

USEPA United States Environmental Protection Agency 

VOC Volatile Organic Compound 
Final Close Out Report Dix Area Sanitary Landfill 

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I. Introduction

Plexus Scientific Corporation (Plexus), under contract to the United States Army Environmental 

Command (USAEC), was tasked to prepare the Final Close Out Report (FCOR) for the Dix Area Sanitary 

Landfill, Joint Base McGuire-Dix-Lakehurst (JB MDL), New Jersey. This FCOR includes one Operable 

Unit, the Dix Area Sanitary Landfill, JB MDL, New Jersey. This site is in long-term monitoring (LTM) 

which includes monitoring of hazardous substances, pollutants, or contaminants remaining above levels 

that allow for unlimited use and unrestricted exposure. The site was proposed to the National Priorities 

List (NPL) in 1984 and finalized in 1987.

This FCOR documents that JB MDL has completed all remedial actions at the Dix Area Sanitary Landfill. 

The selected remedy at the Dix Area Sanitary Landfill includes construction of a landfill cap and venting 

system, installation of a secured perimeter fence, long-term Operation and Maintenance (O&M), LTM, 

and institutional controls (ICs) in the form of Master Plan Amendments and water restrictions. In order to 

ensure the selected remedy continues to provide long-term protection, the site will be incorporated into 

the New Jersey Classification Exemption Area (CEA).

II. Summary of Site Conditions 

A. Background Summary 

The Dix Area Sanitary Landfill is located in the southwest section of the JB MDL in Pemberton 

Township, Burlington County, New Jersey. The landfill covers approximately 126 acres and is located 

about 2,200 feet from the post boundary. Two streams flow near the landfill: Cannon Run is located on 

the east side of the landfill, and flows south into the North Branch of Rancocas Creek; and an unnamed

stream is located northwest of the landfill, and flows to the west into the North Branch of Rancocas 

Creek. A swamp that drains into Budd’s Run is located to the west of Pipeline Road. 

The area immediately surrounding the Dix Area Sanitary Landfill consists of a hardwood swamp and 

densely vegetated hardwood forest. The town of Browns Mills is immediately to the east of the Military 

Reservation. To the south of the Dix Area Sanitary Landfill are two abandoned farms, approximately 12

homes, several county buildings, the County Hospital, and the Burlington County Juvenile Detention 

Center and shelter. Pemberton Township municipal buildings, sewage disposal plant, public water supply 

wells, and several homes are located to the southwest of the landfill. 

The surficial aquifer consists of a fine to silty sand unit (Cohansey and Kirkwood Formations) that 

overlies the fine grained silts and clays of the Manasquan, Hornerstown, and Navesink Formations. The

Cohansey and Kirkwood Formations form a single unconfined aquifer at the site. Groundwater flow in 

this aquifer is to the south and southwest. The underlying Manasquan, Hornerstown, and Navesink 

Formations form a confining layer that limits downward vertical groundwater flow from the landfill site. 

The Dix Area Sanitary Landfill began operation in 1950; it was officially closed on July 6, 1984. Prior to 

landfill development, the area was used for Army training. Between 1950 and 1984, the landfill was used 

and operated by the Fort Dix Military Reservation. McGuire Air Force Base also used the landfill from 

1968 until it was closed. Access to the landfill was not controlled until 1980; therefore, records of
Final Close Out Report Dix Area Sanitary Landfill 

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disposal practices, waste types, and quantities are incomplete. Wastes that have been reportedly disposed 

of at the landfill include domestic waste, paints and thinners, demolition debris, ash, and solvents. 

An interim New Jersey Pollutant Discharge Elimination System (NJPDES) permit was issued for the Dix 

Area Sanitary Landfill on May 29, 1984. On July 6, 1984, the Army ceased the disposal of waste at the

landfill in compliance with the landfill closure date. The landfill was ranked for inclusion on the NPL on 

September 14, 1984. On September 16, 1985, the Army entered into an Administrative Consent Order 

(ACO) with the New Jersey Department of Environmental Protection (NJDEP). The ACO required the 

Army to conduct a Remedial Investigation/Feasibility Study (RI/FS) and to implement the selected 

remedial alternative approved by NJDEP and United States Environmental Protection Agency (USEPA). 

The Dix Area Sanitary Landfill Site was placed on the NPL on July 1, 1987. 

On July 19, 1991, the Army entered into an interagency agreement, under Comprehensive Environmental 

Response, Compensation, and Liability Act (CERCLA) Section 120, known as the Federal Facility 

Agreement (FFA) with USEPA. The FFA superseded the ACO and provided the formal basis for 

selection of the remedy and the implementation of the Record of Decision (ROD) at the Dix Area 

Sanitary Landfill Site at JB MDL. 

The ROD outlined the requirements for the Dix Area Sanitary Landfill site in two phases, encompassing 

the entire landfill with a 6-foot perimeter chain link fence, and providing monitoring for 30 years. In 

Phase I, a 6-foot security fence was installed around the entire landfill, and erosion control measures and 

drainage improvements were made for the northern 78 acres of the landfill. The newer, southernmost 53

acres were covered with a multi-layer impermeable cap in Phase II. In addition, Phase II included the

installation of drainage facilities, a surface water infiltration pond, access roads, and permanent erosion 

control measures. 

The site chronology for the Dix Area Sanitary Landfill site is presented in the table below: 

Event Date 

Site proposed for placement on the NPL October 1984

Final placement on the NPL Ju1y 1,1987 

RI/FS completed September 1987 

Army and USEPA sign Federal Facility Agreement July 1991 

ROD signed October 1991 

Phase I Remedial Design completed July 1992 

Phase I Construction completed 1992

Phase II Remedial Design completed February 1994 

Phase II Construction completed August 1996 

Construction Completion Report September l997 

First Five-year Review Report completed September 1999 

Air monitoring termination approved 2000

Second Five-year Review Report completed September 2005 

Third Five-year Review Report completed September 2010 
Final Close Out Report Dix Area Sanitary Landfill 

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B. Remedial Investigation/Feasibility Study 

The RI/FS was completed in 1987. The RI/FS included a risk assessment to determine the potential for 

impact to public health and the environment, which may result if the contamination associated with the

Dix Area Sanitary Landfill, was not controlled. In conducting this assessment, the focus was on the 

human health and environmental effects that could result from exposure to contaminants associated with

the landfill in various media (air, surface water, sediment, soil, and groundwater). During the evaluation 

of site risks, chemicals detected at the site were screened to select indicator chemicals for the Dix Area 

Sanitary Landfill site. These chemicals were selected as most representative of site conditions and 

expected to contribute the greatest risks to human health and the environment. The indicator chemicals 

for the site include: 1,2-dichloroethane, benzene, vinyl chloride, trichloroethylene, tetrachloroethylene, 

chlorobenzene, 2-butanone, toluene, trans-1,2-dichloroethylene, bis(2-ethylhexyl)phthalate, 1,4-

dichloroethylene, 1,1,1-trichloroethane, ethylbenzene, nickel, mercury, cadmium, zinc, chromium, and 

manganese. 

Based on an evaluation of the data obtained during the RI, the ROD summarizes the following remedial 

objectives:

! To prevent contaminants migrating from the landfill from affecting drinking water supplies of the 

local population; 

! To prevent landfill contaminant migration/exposure via Cannon Run and Budd’s Run (swamp) 

from restricting State-designated downstream surface water uses on the North Branch of 

Rancocas Creek (i.e., fishing, swimming, and future water supply); 

! To protect people who perform military-related or unauthorized recreational activities on the JB 

MDL property from potentially harmful effects due to landfill contaminants; 

! To satisfy all appropriate local, State, and Federal requirements for landfill closure; 

! To prevent significant adverse environmental impacts on the surrounding flora and fauna caused 

by contaminant release from the Dix Area Sanitary Landfill; and

! To satisfy all site-specific Applicable or Relevant and Appropriate Requirements (ARARs) as 

practicable.

C. Selected Remedy and Implementation 

The selected remedy provided in the ROD consists of the following requirements: 

! Installation of a cap on the southern 53 acres of the landfill consisting of vegetative, drainage, and

low-permeability layers. Maintenance of 2 ft of existing final cover on the remaining portion of 

the landfill. 

This action was completed in 1992 and maintenance is ongoing. 

! Installation of a landfill gas venting and air monitoring system to determine if methane gas and 

VOC emissions require treatment. 

This action was completed in August 1996. Air monitoring was discontinued, with approval from 

all stake holders, in the year 2000. 

! Installation of a chain link fence around the perimeter of the landfill to restrict access. 

Implementation of landfill closure requirements in accordance with New Jersey Closure 

Requirements, New Jersey Administration Code (NJAC) 7:26-2A et seq., and Resource 

Conservation and Recovery Act (RCRA) guidance. 
Final Close Out Report Dix Area Sanitary Landfill 

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This action was completed in August 1996 and maintenance is ongoing. 

! Perform long-term groundwater, surface water, sediment and air monitoring (30 years) pursuant 

to the New Jersey State closure requirements. Perform a yearly statistical analysis on the 

chemical analysis results to determine the trend of the overall contamination levels. 

This action is ongoing and is reviewed every 5 years. Groundwater samples are collected from 

the network of groundwater monitoring wells, surface water and sediment samples are collected 

from the existing streams and air monitoring was conducted at the landfill vents. Termination of 

air monitoring was approved in the year 2000. 

! Long-term O&M to provide inspection of and repairs to the landfill cap. 

This action is ongoing and is reviewed every 5 years. 

! Implementation of ICs in the form of deed and water restrictions on future uses of the landfill and 

groundwater in the immediate vicinity of the landfill. 

This action has been completed under the current Dix Area Master Plan. 

! Development and implementation of a Soil Erosion and Sediment Control Plan in accordance 

with the Soil Erosion and Sediment Control Act Regulations of 1975 - New Jersey Statutes 

Annotated (NJSA) 4:24-40 et seq., and NJAC 2:90-1.1 et seq. 

This action was completed in August 1996. 

! Using the data obtained in the monitoring program, review the risk assessment and subsequently 

revise the risk assessment if the trend shows significant changes in water quality. These reviews 

and revisions will be performed within three years of commencement of a remedial action and at 

least every five years thereafter. Any changes in actual exposure scenarios will be addressed in 

the revised risk assessments. Risk assessments will use USEPA guidance and policy effective at 

the time of the review. 

This action is ongoing and has been included in each of the Five-Year Reviews. 

Except for monitoring, no groundwater remedy was specified because the contaminant plume could not 

be defined beyond isolated “hot spots". The U.S. Army Corps of Engineers (USACE) acted on behalf of 

the Army at Fort Dix for both phases of the project and supervised all engineering and construction 

contracts required for completion of the work. Professional engineering services' for both phases were 

provided by Law Engineering and Environmental Services, Inc. (Law Environmental). 

Phase I encompassed the approximately 126 acre Landfill with a six-foot perimeter chain link fence and

provided two feet of soil cover to the northernmost 73 acres, This was completed early in fiscal year (FY) 

1992. The contractor for Phases I and II was the George Hanus Co. 

Phase II included covering of the southernmost 50 acres with a multilayer impermeable cap. The contract 

for the construction requirements of Phase II Remedial Action was awarded on June 30, 1994. 

Construction was completed in FY 97. In September, 1997 Law Environmental provided a Construction 

Completion Report to USACE. It was prepared and certified by C. Keith Brasher, a Professional 

Engineer licensed in the State of New Jersey. 

The remedial design, work plans, performance standards, construction quality control measures, O&M, 

and long-term monitoring plans (LTMPs) were submitted to and approved by USEPA and NJDEP. The 

Army, its design contractor, the USACE, NJDEP, and USEPA reviewed, monitored, and inspected all 

design and construction activities, and have determined all activities were completed in accordance with 

the approved documents. USEPA made a final inspection of the completed work on March 28, 1998. 
Final Close Out Report Dix Area Sanitary Landfill 

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D. Institutional Controls 

ICs in the form of Master Plan Amendments that are equivalent to deed restrictions on future uses of the 

Dix Area Sanitary Landfill have been implemented since the property is under the control and ownership

of the Federal government. The Dix Area Master Plan restricts Army use of the Dix Area Sanitary 

Landfill site including the surrounding impacted areas. In the event the landfill property were no longer 

under the control and ownership of the Federal Government, implementation of appropriate deed 

restrictions or additional remediation to meet non-restricted use standards would be required to ensure 

the remedy remains protective of human health and the environment. In addition to the Dix Area Master 

Plan, the site is currently enrolled in the NJDEP Classification Exception Area (CEA) program. The CEA 

program is established as a groundwater land use control (LUC) that serves to restrict the use of 

groundwater until regulatory standards have been achieved. 

E. Final Site Inspection 

As part of the LTMP, the Dix Area Sanitary Landfill is inspected quarterly; for the purpose of the Third 

Five-year Review, an additional site inspection was conducted by Plexus on March 9, 2010. The purpose

of the additional site inspection was to assess the physical condition of the site, including drainage

features, cap integrity, site security, and site maintenance. 

In general, the site was found to be in excellent condition. Site security was maintained with a 6-foot 

high chain link fence topped with three-strand barbed wire and locked gates. Warning signs were 

attached to the security fence at regular intervals around the perimeter of the site. All landfill vents and 

monitoring wells were in good condition and secure.

During 2009 site inspections, an invasive species of weed was found growing on the cap, and the invasive 

weed was subsequently treated (Plexus, 2009b). It was noted on the site inspection checklist that large 

areas of dead vegetation occurred where the cap was treated for invasive weeds. In April 2010, the entire 

landfill cap was reseeded.

Minor erosion features were noted on the western slope of the landfill cap that occurred between the 

Fourth Quarter 2009 and First Quarter 2010 inspections. The inspection highlighted small gullies in the 

landfill cap and areas where the eroded material had deposited silt in the perimeter drainage swale. 

During the April 2010 cap reseeding event the gullies were repaired and drainage swales were cleared of 

silt.

A portion of the northern perimeter fence had been significantly damaged due to a fallen tree. In Spring 

2010, the tree was removed and the fence was rebuilt. 

III. Monitoring Results 

A. Air Monitoring 

With concurrence from USEPA and NJDEP, the Dix Area Sanitary Landfill gas venting and air 

monitoring system is no longer sampled and analyzed after it was determined there was no longer a need

to monitor for methane gas or VOC emissions. Approval to terminate the air monitoring was received by

NJDEP and USEPA in 2000. 
Final Close Out Report Dix Area Sanitary Landfill 

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B. Groundwater Monitoring 

Nutrient metals are the only analytes exceeding screening criteria and exhibiting increasing concentration 

trends according to the Mann-Kendall Analysis. These exceedances and increasing trends occur both 

upgradient and downgradient of the landfill. 

In reviewing historical analytical data for this site, it has been noted that nutrient metals have been 

consistently present at concentrations above screening criteria. In an effort to understand the geochemical 

make-up of the local hydrogeology, several studies were reviewed. Following this review, it was evident 

that several naturally-occurring characteristics of the local hydrogeology are contributing to the elevated 

concentrations of nutrient metals in groundwater. 

Fresh, uncontaminated groundwater in the Kirkwood-Cohansey aquifer system has naturally-occurring 

low pH. During the groundwater sampling program, pH levels were measured between 3 and 6 at both 

upgradient and downgradient locations. In the Kirkwood-Cohansey aquifer, calcium and bicarbonate are 

usually dominant ions in solution, with smaller amounts of sodium, potassium, magnesium sulfate, 

manganese and chloride. The surficial aquifer underlying and adjacent to the Dix Area Sanitary Landfill 

exhibits persistent exceedances of calcium, magnesium, manganese, sodium, and potassium that are 

attributed to this naturally-occurring condition. In 1988, the USEPA determined that concentrations of 

iron and manganese present a problem near the water table because the groundwater tends to have a low 

pH. Elevated concentrations of manganese and iron are also attributed to reductive dissolution by metalreducing bacteria feeding on petroleum contaminants. The reduced form of both iron and manganese are 

more water soluble than their oxidized counterparts. During the Spring 2010 and Fall 2010 sampling 

events, water quality data collected indicated a sporadic distribution of anaerobic and aerobic 

groundwater conditions. The data show both acid leaching and anaerobic degradation of gasoline 

contamination that is a waste of concern at the landfill, leading to elevated concentrations of manganese 

and iron. 

Since the last five-year review, eight sentinel wells were evaluated (Plexus 2011) and established 

downgradient of the landfill cap. These groundwater monitoring locations were sampled for five 

continuous quarters and groundwater was analyzed for all contaminants of concern (COCs). Table 1

(Attachment A) presents the groundwater results for all COCs. With the exception of manganese, the 

results show no screening criteria exceedances were observed downgradient of the landfill and that COCs 

are below screening criteria at the landfill unit boundary. The Addendum to the 2005 CERCLA FiveYear Review (Plexus, 2009) concluded that manganese is naturally occurring and was removed as a COC 

from the program. After the evaluation of the proposed sentinel wells, JBMDL proposed nine alternative 

wells, closer to the landfill, that are currently in the LTMP, to make up the sentinel well network. NJDEP 

concurred that this site may now be deleted from the National Priorities List of Superfund and moved to 

the site-wide Groundwater Classification Exception Area & Well Restriction Area Program. Wells LTM9, 10, 12, 13, 14, 17, 18, 34 & 36 are now designated as sentinel wells and shall be used for compliance 

determination (Figure 1, Attachment B). 

C. Surface Water Monitoring 

The majority of the surface water location samples that exceed analyte concentrations contain nutrient

metals that are not COCs for surface water at the Dix Area Sanitary Landfill. Table 2 (Attachment A)

presents the COC analytical results for the last three years. As part of the five-year review process an 
Final Close Out Report Dix Area Sanitary Landfill 

JB MDL, New Jersey 

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Ecological Risk Assessment (ERA [Attachment C]) was completed evaluating surface water analytical

data up to and including September 2009. With the exception of manganese and mercury, there have 

been no COC screening criteria exceedances at the landfill in the last three years (Table 2). The 

Addendum to the 2005 CERCLA Five-Year Review (Plexus, 2009) concluded that manganese is 

naturally occurring and was removed as a COC from the program. During the Spring 2010 and Fall 2010 

sampling events, mercury exceeded screening criteria at three surface water locations (SW-1, SW-2, and

SW-9). All three of these locations are situated northwest of the Dix Area Sanitary Landfill, along 

Budd’s Run and immediately downgradient of the PDO Landfill, where mercury is the main COC. The 

issue of mercury exceedances along Budd’s Run (the body of water that contains these surface water 

locations) has been addressed in the 2005 CERCLA Five-year Review Addendum. The five year review 

addendum concluded that the mercury exceedances are attributed to a separate site upgradient of the Dix 

Area Sanitary Landfill. The results of the ERA illustrate that in September 2009 only one COC (zinc) at 

SW-2 exceeded ecological screening criteria (ESC). Since this ESC exceedance, the concentration of 

zinc at SW-2 has reduced in concentration below the ESC. 

D. Sediment Monitoring 

The majority of the sediment location samples that exceed analyte concentrations contain nutrient metals 

that are not COCs for sediment at the Dix Area Sanitary Landfill. Table 3 (Attachment A) presents the 

COC analytical results for the last three years. As part of the five-year review process an Ecological Risk 

Assessment (ERA [Attachment C]) was completed evaluating sediment analytical data up to and 

including September 2009. With the exception of chlorobenzene, manganese and mercury, there have 

been no COC screening criteria exceedances at the landfill in the last three years (Table 3). Although 

chlorobenzene exceeds the screening criteria, it does not exceed its respective ecological benchmark 

(Attachment C). The Addendum to the 2005 CERCLA Five-Year Review (Plexus, 2009) concluded that 

manganese is naturally occurring and was removed as a COC from the program. Since April 2010 the 

only sample location that exceeds screening criteria is SD-9. SD-9 is situated northwest of the Dix Area 

Sanitary Landfill, along Budd’s Run and immediately downgradient of the PDO Landfill, where mercury 

is the main COC. The issue of mercury exceedances along Budd’s Run (the body of water associated 

with this sediment location) has been addressed in the 2005 CERCLA Five-year Review Addendum. The 

five year review addendum concluded that the mercury exceedance is attributed to a separate site 

upgradient of the Dix Area Sanitary Landfill. 

Low-level pesticide exceedances of dichlorodiphenyldichloroethylene (DDE) and dichlorodiphenyltrichloroethane (DDT) occur at locations SD-5 and SD-6, but do not occur at the landfill boundary. DDE 

and DDT are ubiquitous to Fort Dix and are not considered COCs for the Dix Area Sanitary Landfill. 

The results of the ERA illustrate that in September 2009 only one COC (mercury) at SD-9 exceeded ESC. 

Since this ESC exceedance, the concentration of zinc at SW-2 has reduced in concentration below the 

ESC. The 2005 CERCLA Five-year Review Addendum concluded that the mercury exceedances at this 

location are attributed to a separate site upgradient of the Dix Area Sanitary Landfill. 

IV. Summary of Operation and Maintenance 

In general, O&M of the Dix Area Sanitary Landfill consists of the collection and analysis of groundwater, 

sediment, and surface water samples; routine mowing; limiting erosion; and maintaining site security. 
Final Close Out Report Dix Area Sanitary Landfill 

JB MDL, New Jersey 

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Site inspections are performed by a JB MDL representative every 30 days and after large rain events or

episodes of severe weather. The O&M contractor also performs a separate inspection on a quarterly 

basis. A compilation of these quarterly inspection reports is submitted to the regulatory agencies for 

review on annual basis. 

For areas that do not have a landfill cap installed, visual observations are made to ensure run-on and runoff controls are performing as intended. Any exposed waste in these areas is covered with compacted 

soil.

On the landfill cap, tree and brush growth is not allowed for protection of the cap's liner system. Areas of 

settlement and damage by burrowing animals are repaired as needed. The sediment and erosion control 

features are maintained by cleaning debris and accumulated sediment to maintain proper infiltration and 

prevent clogging of the outlet control structure and emergency spillway. Since the last Five-year Review, 

there has been evidence of minor burrowing activity; however, the effects of the burrowing activity have 

not impacted the landfill cap or the protectiveness of the remedy. When located, burrows are routinely 

destroyed during the inspection process. 

NJDEP will assume lead regulatory responsibility for all future O&M, implementation of ICs, and 

ensuring that the remedy remains protective into the future. Site LUCs will continue under the current 

NJDEP CEA program for the site. 

V. Clean-up Activity Quality Assurance/Quality Control

All construction, O&M, remediation and monitoring activities associated with the Dix Area Sanitary 

Landfill were completed under direction of a Quality Assurance Project Plan, which provided quality 

assurance and quality control requirements and set forth site specific mechanisms to evaluate the 

performance of the remedial activities. After completion of an individual construction segment, the 

Quality Control Officer verified that the tasks were performed in compliance with the final plans and 

specifications and then provided a Compliance Report 

The Quality Control activities implemented used standardized quality control procedures and provided the 

necessary tests and observations for the construction, sampling and monitoring process at the Dix Area

Sanitary Landfill. 

VI. Five-year Review 

A. Five-year Review Process 

The CERCLA five-year review process is required as waste will be left in place at the Dix Area Sanitary 

Landfill at levels that will not allow for unrestricted use. CERCLA Five-year Reviews will continue for 

which the USEPA will retain lead regulatory responsibility. The next Five-year Review for the Dix Area 

Sanitary Landfill is required by September 2015. Long Term Monitoring of groundwater, surface water 

and sediment will continue in accordance with Long-Term Monitoring Plan. 
Final Close Out Report Dix Area Sanitary Landfill 

JB MDL, New Jersey 

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B. Summary of the Third Five-year Review (Plexus, 2010) 

The technical assessment summary from the Third Five-year Review Report concluded that the remedy is 

functioning as intended and remains protective of human health and the environment. According to the 

data reviewed, the site inspection, and the interviews, the remedy is functioning as intended in the ROD. 

There were three issues highlighted in the review: 

Issue Remedy 

Evidence of erosion along the western slope of the 

landfill.

Erosion was stabilized and vegetation cover was 

restored.

Fallen tree along the northern boundary perimeter 

fence. 

Tree was removed and fence was restored. 

Lack of sentinel wells to delineate groundwater 

COCs. 

Sentinel wells were selected or installed. 

There have been no changes in the physical condition of the Dix Area Sanitary Landfill site that would

affect the protectiveness of the remedy. Most ARARs cited in the ROD have been met. There have been 

no changes in the toxicity factors for the COCs, and there have been no changes to the standardized risk 

assessment methodology that may affect the protectiveness of the remedy. 

VII. Site Completion Criteria 

The remedial objectives set forth by the ROD include: 

! To prevent contaminants migrating from the Dix Area Sanitary Landfill from affecting drinking 

water supplies of the local population; 

! To prevent Dix Area Sanitary Landfill contaminant migration/exposure via Cannon Run and 

Budd’s Run (swamp) from restricting State-designated downstream surface water uses on the 

North Branch of Rancocas Creek (i.e., fishing, swimming, and future water supply); 

! To protect people who perform military-related or unauthorized recreational activities on the JB 

MDL property from potentially harmful effects due to landfill contaminants; 

! To satisfy all appropriate local, State, and Federal requirements for landfill closure; 

! To prevent significant adverse environmental impacts on the surrounding flora and fauna caused 

by contaminant release from the Dix Area Sanitary Landfill; and

! To satisfy all site-specific ARARs as practicable.

The Dix Area Sanitary Landfill site meets all the site completion requirements as specified in the ROD, 

and all of the remedial actions at the site have been implemented. The implemented remedy achieves the 

degree of clean-up and protection specified in the ROD for all pathways of exposure. All remedial and

removal actions, remedial action objectives, and associated clean-up goals are consistent with USEPA 
Final Close Out Report Dix Area Sanitary Landfill 

JB MDL, New Jersey 

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and NJDEP policy and guidance. No further Superfund response is needed to protect human health and 

the environment. 

Continued implementation of the ICs and LTMP will ensure the long-term protectiveness of the remedy. 

Currently, none of the COCs outlined in the ROD have migrated past the landfill unit boundary as 

evidenced by groundwater, surface water and sediment data collected. 

VIII. Bibliography

Advanced Sciences, Inc. (1993). Long-Term Monitoring Plan for the Fort Dix Landfill, Fort Dix, NJ. 

Draft Final. US Army Corps of Engineers Baltimore District. 

Barringer, Julia L. et. al. (1993). Corrosiveness of Ground Water in the Kirkwood-Cohansey Aquifer 

System of the New Jersey Coastal Plain. Water Resources Investigations Report 90-4180. US 

Geological Survey, West Trenton, NJ. 

Camp Dresser & McKee. (1985). Remedial Investigation/Feasibility Study for Fort Dix Sanitary Landfill,

Pemberton Township, New Jersey. Interim Report. US Army Corps of Engineers Philadelphia 

District. 

Camp Dresser & McKee. (1986). Remedial Investigation/Feasibility Study for Fort Dix Sanitary Landfill,

Pemberton Township, New Jersey. Proposed Response. US Army Corps of Engineers 

Philadelphia District. 

Dames & Moore, LTD. (1991). Remedial Investigation Report, Fort Dix, New Jersey. Commander, U.S. 

Army Toxic and Hazardous Materials Agency, Aberdeen Proving Ground, MD. 

EA Engineering, Science, & Technologies, Inc. (2007). 2006 Sampling and Analysis Report for 

Groundwater, Surface Water, and Sediment for the Fort Dix Sanitary Landfill, Fort Dix, NJ. 

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Groundwater, Surface Water, and Sediment for the Fort Dix Sanitary Landfill, Fort Dix, NJ. 

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the Fort Dix Sanitary Landfill, Fort Dix, NJ. US Army Corps of Engineers Baltimore District. 

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the Fort Dix Sanitary Landfill, Fort Dix, NJ. US Army Corps of Engineers Baltimore District. 

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Collected at the Fort Dix Sanitary Landfill, Fort Dix, NJ. US Army Corps of Engineers Baltimore 

District. 

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Log# 01-93-4497. 

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the Fort Dix Sanitary Landfill, Fort Dix, NJ. US Army Corps of Engineers Baltimore District. 

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(NPL) Landfill. US Army Corps of Engineers Omaha District. 

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Hughey, Commissioner. 
Final Close Out Report Dix Area Sanitary Landfill 

JB MDL, New Jersey 

11 

Plexus Scientific Corporation. (2009). Biennial Certification Monitoring Report Form for a Deed Notice 

& Engineering Control. 

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Groundwater, Surface water, and Sediment. 

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Sanitary Landfill at Fort Dix, New Jersey. 

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FS-062-98.
ATTACHMENT A 

TABLES 
Table 1 - Sentinel Well Analytical Results

2009 - 2011

Screening

Analyte Value Unit Sep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-11 Sep-09 Nov-09 Apr-10 May-10 O

1,1,1-Trichloroethane 30 μg/L 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.24 U 0.26 UJ 0.26 U 0.26 U 0.26 U 01,1-Dichloroethane 50 μg/L 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.19 U 0.29 U 0.29 U 0.29 U 0.29 U 01,2-Dichloroethane 2 μg/L 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.18 U 0.33 UJ 0.33 U 0.33 U 0.33 U 02-Butanone (MEK) 300 μg/L 43.3 1.6 U 1.6 U 1.6 U 1.6 U 1.6 R 1.6 R 2.9 U 1.6 U 1.6 U 1.6 U 1.6 U 1Benzene 1 μg/L 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.22 U 0.23 U 0.23 U 0.23 U 0.23 U 0Chlorobenzene 50 μg/L 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.22 U 0.39 U 0.39 U 0.39 U 0.39 U 0Ethylbenzene 700 μg/L 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.21 U 0.27 U 0.27 U 0.27 U 0.27 U 0Tetrachloroethene 1 μg/L 0.27 U 0.27 U 0.27 U 0.27 U 0.27 UJ 0.27 U 0.27 U 0.32 U 0.27 U 0.27 U 0.27 U 0.27 U 0.2Toluene 1000 μg/L 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.15 U 0.3 U 0.3 U 0.3 U 0.3 U 0trans-1,2-Dichloroethene 100 μg/L 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.31 U 0.25 U 0.25 U 0.25 U 0.25 U 0Trichloroethene 1 μg/L 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.21 U 0.24 U 0.24 U 0.24 U 0.24 U 0Vinyl chloride 1 μg/L 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.27 U 0.44 U 0.44 U 0.44 U 0.44 U 01,4-Dichlorobenzene 75 μg/L 0.39 U 0.39 U 0.41 U 0.39 U 0.4 U 0.4 U 0.39 U 0.4 U 21.8 0.39 U 0.39 U 0.39 U 0bis(2-Ethylhexyl)phthalate 3 μg/L 0.33 U 0.33 U 0.35 U 0.33 U 1.5 J 1.1 J 0.33 U 0.34 U 0.36 U 0.33 U 0.33 U 0.33 U 1Cadmium 4 μg/L 0.4 U 0.4 U 0.35 U 0.35 U 0.35 U 0.17 U 0.2 U 0.17 U 0.4 U 0.4 U 0.35 U 0.35 U 0Chromium 70 μg/L 0.9 U 0.9 U 0.59 U 10 U 10 U 1.4 J 1.6 U 0.9 U 0.9 U 0.9 U 0.59 U 10 U 1Manganese 92.6 μg/L 15 U 11 J 15 U 15 U 15 U 13.3 U 11.5 J 8.8 J 15.3 15 U 15 U 11.2 J 1Mercury 2 μg/L 0.082 U 0.082 U 0.082 U 0.082 U 0.088 UJ 0.088 U 0.088 U 0.088 U 0.082 U 0.082 U 0.082 U 0.082 U 0Nickel 100 μg/L 10 U 1.2 J 0.51 U 10 U 10 U 1.8 U 1.2 J 0.7 J 10 U 0.6 U 0.51 U 10 U 0Zinc 2000 μg/L 11.9 J 20 U 20 U 20 U 20 U 15.9 J 35.3 7.8 J 7.1 J 2.9 U 1.4 U 20 U 2

Indicates the analyte is not detected or not sampled

!g/L - Micrograms per Liter

A Cell Highlighted and Bold Indicates a detected

analyte that exceeds the screening criteria

A cell highlighted and not bold Inidcates a detected 

l t that does not exceed the screening criteria

R - Rejected DataQualifier Key:

U - Analyte not detected in the sample. Value 

t the quantitation/detection limit.

UJ - Analyte was not detected in the sample, actual quantitation/detection limit may be higher than reported value.J - Result reported is a quantitative estimate

Volatile Organic Compounds

Semivolatile Organic Compounds

Metals

LTM-31 LTM-38

12/21/2011 7:22 PM 
Table 1 - Sentinel Well Analytical Results

2009 - 2011

Screening

Analyte Value Unit

1,1,1-Trichloroethane 30 μg/L1,1-Dichloroethane 50 μg/L1,2-Dichloroethane 2 μg/L2-Butanone (MEK) 300 μg/LBenzene 1 μg/LChlorobenzene 50 μg/LEthylbenzene 700 μg/LTetrachloroethene 1 μg/LToluene 1000 μg/Ltrans-1,2-Dichloroethene 100 μg/LTrichloroethene 1 μg/LVinyl chloride 1 μg/L1,4-Dichlorobenzene 75 μg/Lbis(2-Ethylhexyl)phthalate 3 μg/LCadmium 4 μg/LChromium 70 μg/LManganese 92.6 μg/LMercury 2 μg/LNickel 100 μg/LZinc 2000 μg/L

Indicates the analyte is not detected or not sampled

!g/L - Micrograms per Liter

A Cell Highlighted and Bold Indicates a detected

analyte that exceeds the screening criteria

A cell highlighted and not bold Inidcates a detected 

l t that does not exceed the screening criteria

R - Rejected DataQualifier Key:

U - Analyte not detected in the sample. Value 

t the quantitation/detection limit.

UJ - Analyte was not detected in the sample, actual quantitation/detection limit may be higher than reported value.J - Result reported is a quantitative estimate

Volatile Organic Compounds

Semivolatile Organic Compounds

Metals

Sep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-11 Sep-09 Nov-09 Apr-10 May-10 Oc

0.26 U 0.26 U 0.51 U 0.26 U 0.51 U 0.26 U 0.26 U 0.24 U 0.26 UJ 0.26 U 0.26 U 0.26 U 0.0.29 U 0.29 U 0.57 U 0.29 U 0.57 U 0.29 U 0.29 U 0.19 U 0.29 U 0.29 U 0.29 U 0.29 U 0.0.33 U 0.33 U 0.67 U 0.33 U 0.67 U 0.33 U 0.33 U 0.18 U 0.33 UJ 0.33 U 0.33 U 0.33 U 0.

1.6 U 1.6 U 3.2 U 1.6 U 3.2 U 1.6 R 1.6 R 2.9 U 1.6 U 1.6 R 1.6 U 1.6 U 1

0.23 U 0.23 U 0.47 U 0.23 U 0.47 U 0.23 U 0.23 U 0.22 U 0.23 U 0.23 U 0.23 U 0.23 U 0.0.39 U 0.39 U 0.78 U 0.39 U 0.78 U 0.39 U 0.39 U 0.22 U 0.39 U 0.39 U 0.39 U 0.39 U 0.0.27 U 0.27 U 0.54 U 0.27 U 0.54 U 0.27 U 0.27 U 0.21 U 0.27 U 0.27 U 0.27 U 0.27 U 0.0.27 U 0.27 U 0.53 U 0.27 U 0.53 U 0.27 U 0.27 U 0.32 U 0.27 U 0.27 U 0.27 U 0.27 U 0.

1.7 0.3 U 0.6 U 0.3 U 0.6 U 0.3 U 0.3 U 0.15 U 0.38 J 0.3 U 0.3 U 0.3 U 0

0.25 U 0.25 U 0.5 U 0.25 U 0.5 U 0.25 U 0.25 U 0.31 U 0.25 U 0.25 U 0.25 U 0.25 U 0.0.24 U 0.24 U 0.48 U 0.24 U 0.48 U 0.24 U 0.24 U 0.21 U 0.24 U 0.24 U 0.24 U 0.24 U 0.0.44 U 0.44 U 0.89 U 0.44 U 0.89 U 0.44 U 0.44 U 0.27 U 0.44 U 0.44 U 0.44 U 0.44 U 0.16.9 U 0.42 U 0.4 U 0.39 U 0.41 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.43 U 0.39 U 0.

2 U 0.36 U 0.34 U 0.33 U 0.35 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.36 U 0.33 U 0.

0.4 U 0.4 U 0.35 U 0.35 U 0.35 U 0.17 U 0.17 U 0.17 U 0.4 U 0.4 U 0.35 U 0.35 U 0.

35.3 31.5 23.7 25.9 10.4 8.8 J 4.6 U 10 U 1.7 J 0.9 U 10 U 10 U 1

128 76.4 48.9 62.6 154 128 123 229 29.5 18.7 18.6 17.2 1

0.082 U 0.082 U 0.082 U 0.082 U 0.11 J 0.088 U 0.088 U 0.11 J 0.082 U 0.082 U 0.082 U 0.082 U 0.0

10.1 10 U 1.7 J 10 U 10 U 2.6 U 1.6 J 4 J 10 U 0.9 J 0.51 U 10 U 152.6 20 U 52.9 20 U 20 U 20.3 13.8 U 32.2 9.9 J 20 U 20 U 20 U 

LTM-40 LTM-41

12/21/2011 7:22 PM 
Table 1 - Sentinel Well Analytical Results

2009 - 2011

Screening

Analyte Value Unit

1,1,1-Trichloroethane 30 μg/L1,1-Dichloroethane 50 μg/L1,2-Dichloroethane 2 μg/L2-Butanone (MEK) 300 μg/LBenzene 1 μg/LChlorobenzene 50 μg/LEthylbenzene 700 μg/LTetrachloroethene 1 μg/LToluene 1000 μg/Ltrans-1,2-Dichloroethene 100 μg/LTrichloroethene 1 μg/LVinyl chloride 1 μg/L1,4-Dichlorobenzene 75 μg/Lbis(2-Ethylhexyl)phthalate 3 μg/LCadmium 4 μg/LChromium 70 μg/LManganese 92.6 μg/LMercury 2 μg/LNickel 100 μg/LZinc 2000 μg/L

Indicates the analyte is not detected or not sampled

!g/L - Micrograms per Liter

A Cell Highlighted and Bold Indicates a detected

analyte that exceeds the screening criteria

A cell highlighted and not bold Inidcates a detected 

l t that does not exceed the screening criteria

R - Rejected DataQualifier Key:

U - Analyte not detected in the sample. Value 

t the quantitation/detection limit.

UJ - Analyte was not detected in the sample, actual quantitation/detection limit may be higher than reported value.J - Result reported is a quantitative estimate

Volatile Organic Compounds

Semivolatile Organic Compounds

Metals

Sep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-11 Sep-09 Nov-09 Apr-10 May-10 

0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.24 U 0.26 U 0.26 U 0.26 U 0.26 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.19 U 0.29 U 0.29 U 0.29 U 0.29 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.18 U 0.33 U 0.33 U 0.33 U 0.33 U 

1.6 U 1.6 R 1.6 U 1.6 U 1.6 U 1.6 R 1.6 R 2.9 U 1.6 U 1.6 U 1.6 U 1.6 U 

0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.22 U 0.23 U 0.23 U 0.23 U 0.23 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.22 U 0.39 U 0.39 U 0.39 U 0.39 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.21 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.44 J 0.27 U 0.27 U 0.27 U 0.32 U 0.27 U 0.27 U 0.27 U 0.27 U 

0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.15 U 0.3 U 0.3 U 0.3 U 0.3 U 

0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.31 U 0.25 U 0.25 U 0.25 U 0.25 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.21 U 0.24 U 0.24 U 0.24 U 0.24 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.27 U 0.44 U 0.44 U 0.44 U 0.44 U 0.42 U 0.39 U 0.39 U 0.39 U 0.39 U 0.46 U 0.43 U 0.4 U 0.39 U 0.42 U 0.44 U 0.39 U 0.36 U 0.33 U 0.33 U 0.33 U 0.33 U 0.38 U 0.36 U 0.34 U 0.33 U 0.35 U 0.37 U 0.33 U 

0.4 U 0.4 U 0.35 U 0.35 U 0.35 U 0.17 U 0.17 U 0.17 U 0.4 U 0.4 U 3 U 3 U 

10 U 2.2 J 10 U 10 U 10 U 1.4 J 1.1 J 10 U 1 J 2.6 J 0.59 U 10 U 

15.7 17.1 15 U 15 U 15.1 15.8 15 U 15 U 23.5 23.1 100 69.4 

0.082 U 0.082 U 0.082 U 0.082 U 0.14 J 0.088 U 0.088 U 0.11 J 0.082 U 0.082 U 0.082 U 0.082 U 

10 U 2 J 10 U 10 U 2.4 J 1.8 U 10 U 1.3 J 0.6 U 1.4 J 6.2 J 10 U 

11.7 J 20 U 20 U 20 U 95.7 28.4 9 J 28.3 7.6 J 20 U 23.6 20 U 

LTM-42 LTM-43

12/21/2011 7:22 PM 
Table 1 - Sentinel Well Analytical Results

2009 - 2011

Screening

Analyte Value Unit

1,1,1-Trichloroethane 30 μg/L1,1-Dichloroethane 50 μg/L1,2-Dichloroethane 2 μg/L2-Butanone (MEK) 300 μg/LBenzene 1 μg/LChlorobenzene 50 μg/LEthylbenzene 700 μg/LTetrachloroethene 1 μg/LToluene 1000 μg/Ltrans-1,2-Dichloroethene 100 μg/LTrichloroethene 1 μg/LVinyl chloride 1 μg/L1,4-Dichlorobenzene 75 μg/Lbis(2-Ethylhexyl)phthalate 3 μg/LCadmium 4 μg/LChromium 70 μg/LManganese 92.6 μg/LMercury 2 μg/LNickel 100 μg/LZinc 2000 μg/L

Indicates the analyte is not detected or not sampled

!g/L - Micrograms per Liter

A Cell Highlighted and Bold Indicates a detected

analyte that exceeds the screening criteria

A cell highlighted and not bold Inidcates a detected 

l t that does not exceed the screening criteria

R - Rejected DataQualifier Key:

U - Analyte not detected in the sample. Value 

t the quantitation/detection limit.

UJ - Analyte was not detected in the sample, actual quantitation/detection limit may be higher than reported value.J - Result reported is a quantitative estimate

Volatile Organic Compounds

Semivolatile Organic Compounds

Metals

Sep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-11 Sep-09 Nov-09 Apr-10 May-10 O

0.26 UJ 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.24 U 0.26 U 0.26 U 0.26 U 0.26 U 0

0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.19 U 0.29 U 0.29 U 0.29 U 0.29 U 0

0.33 UJ 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.18 U 0.33 U 0.33 U 0.33 U 0.33 U 0

1.6 U 1.6 U 1.6 U 1.6 U 1.6 U 1.6 R 1.6 R 2.9 U 1.6 U 1.6 R 1.6 U 1.6 U 1

0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.22 U 0.23 U 0.23 U 0.23 U 0.23 U 00.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.22 U 0.39 U 0.39 U 0.39 U 0.39 U 00.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.21 U 0.27 U 0.27 U 0.27 U 0.27 U 00.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.32 U 0.27 U 0.27 U 0.27 U 0.27 U 0

0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.15 U 0.3 U 0.3 U 0.3 U 0.3 U 0

0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.31 U 0.25 U 0.25 U 0.25 U 0.25 U 00.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.21 U 0.24 U 0.24 U 0.24 U 0.24 U 00.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.27 U 0.44 U 0.44 U 0.44 U 0.44 U 0

0.4 U 0.39 U 0.4 U 0.39 U 0.44 U 0.42 U 0.39 U 0.39 U 0.39 U 0.39 U 0.42 U 0.4 U 0

0.33 U 1.3 J 0.34 U 0.33 U 0.37 U 0.36 U 0.33 U 0.33 U 0.33 U 0.33 U 0.35 U 0.33 U 0

0.4 U 0.4 U 0.35 U 0.35 U 0.35 U 0.2 U 3 U 0.17 U 3 U 3 U 0.52 U 3 U 0.9 U 10.8 13.6 10 U 10 U 3.9 J 10 U 5 J 0.9 U 1.2 J 10 U 10 U 1

58.7 62.9 86.7 73.7 57.6 66.1 75.1 50 39.4 33.4 49.4 33.1 2

0.082 U 0.082 U 0.082 U 0.082 U 0.19 J 0.088 U 0.088 U 0.088 U 0.082 U 0.082 U 0.082 U 0.082 U 0

10 U 0.6 U 1.1 J 10 U 0.51 U 0.5 U 10 U 2 J 10 U 3.9 J 10 U 10 U 3

7.4 J 20 U 20 U 20 U 10 U 26.6 20 U 20 U 10.2 J 20 U 20 U 20 U 2

LTM-44 LTM-45

12/21/2011 7:22 PM 
Table 2 - Surface Water Analytical Results

2009 - 2011

Screening

Analyte Value Unit Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 

1,1,1-Trichloroethane 120 μg/L NS NS NS NS NS NS NS NS NS NS NS NS 1,1-Dichloroethane 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS 1,2-Dichloroethane 2 μg/L NS NS NS NS NS NS NS NS NS NS NS NS 1,2-Dichloroethene (total) μg/L NS NS NS NS NS NS NS NS NS NS NS NS 2-Butanone (MEK) 2 μg/L NS NS NS NS NS NS NS NS NS NS NS NS Benzene 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS Chlorobenzene 100 μg/L NS NS NS NS NS NS NS NS NS NS NS NS Ethylbenzene 530 μg/L NS NS NS NS NS NS NS NS NS NS NS NS Tetrachloroethene 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS Toluene 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS Trichloroethene 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS Vinyl chloride 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS 1,4-Dichlorobenzene 75 μg/L NS NS NS NS NS NS NS NS NS NS NS NS bis(2-Ethylhexyl)phthalate 3 μg/L NS NS NS NS NS NS NS NS NS NS NS NS Cadmium 3.4 μg/L 0.4 U 0.35 U 3 U 0.2 U 0.4 U 0.4 U 0.4 J 0.35 U 0.17 U 0.4 U 0.4 U 0.35 U Chromium 92 μg/L 0.9 J 1.8 J 10 U 1 U 0.9 U 1.5 J 1.3 J 10 U 0.9 U 1.1 J 0.9 U 0.8 J Manganese 50 μg/L 38.5 38.5 35.5 32 35.3 36.2 29.6 45.7 35.1 70.8 29.1 49.5 

Mercury 0.05 μg/L 0.23 0.082 U 0.19 J 0.18 J 0.14 J 0.3 0.15 J 0.12 J 0.14 J NS NS NS 

Nickel 500 μg/L 10 U 1.8 J 1.9 J 2.1 J 1.5 J 10 U 4.7 J 10 U 1.7 J 2.1 J 10 U 1.4 J Zinc 7,400 μg/L 19.5 J 25.9 20 U 22.9 18.6 J 248 41.2 20 U 17.1 J 13.1 J 4.6 J 30.6 J pCi/L - Picocuries per LiterR - Rejected DataIndicates the analyte is not detected or not sampledNS - Not Sampled!g/L - Micrograms per LiterA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriaA cell highlighted and not bold Inidcates a detected analytethat does not exceed the screening criteria the quantitation/detection limit.UJ - Analyte was not detected in the sample, actual quantitation/detection limit may be higher than reported value.J - Result reported is a quantitative estimate

Metals

Qualifier Key:

U - Analyte not detected in the sample. Value represents

Volatile Organic Compounds

Semivolatile Organic Compounds

SW-1 SW-2 SW-3

12/21/2011 7:35 PM 
Table 2 - Surface Water Analytical Results

2009 - 2011

Screening

Analyte Value Unit

1,1,1-Trichloroethane 120 μg/L1,1-Dichloroethane 1 μg/L1,2-Dichloroethane 2 μg/L1,2-Dichloroethene (total) μg/L2-Butanone (MEK) 2 μg/LBenzene 1 μg/LChlorobenzene 100 μg/LEthylbenzene 530 μg/LTetrachloroethene 1 μg/LToluene 1 μg/LTrichloroethene 1 μg/LVinyl chloride 1 μg/L1,4-Dichlorobenzene 75 μg/Lbis(2-Ethylhexyl)phthalate 3 μg/LCadmium 3.4 μg/LChromium 92 μg/LManganese 50 μg/LMercury 0.05 μg/LNickel 500 μg/LZinc 7,400 μg/LpCi/L - Picocuries per LiterR - Rejected DataIndicates the analyte is not detected or not sampledNS - Not Sampled!g/L - Micrograms per LiterA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriaA cell highlighted and not bold Inidcates a detected analytethat does not exceed the screening criteria the quantitation/detection limit.UJ - Analyte was not detected in the sample, actual quantitation/detection limit may be higher than reported value.J - Result reported is a quantitative estimate

Metals

Qualifier Key:U - Analyte not detected in the sample. Value represents

Volatile Organic Compounds

Semivolatile Organic Compounds

May-09 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 

NS NS NS NS NS NS 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U NS NS NS NS NS NS 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U NS NS NS NS NS NS 0.33 U 0.33 U 0.33 U 0.33 UJ 0.33 U 0.33 U 0.33 U NS NS NS NS NS NS 0.22 U 0.22 U 0.22 U 0.22 U 0.22 U 0.22 U 0.22 U NS NS NS NS NS NS NS 1.6 U NS NS NS NS NS NS NS NS NS NS NS 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U NS NS NS NS NS NS 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U NS NS NS NS NS NS 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U NS NS NS NS NS NS 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U NS NS NS NS NS NS 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 1 NS NS NS NS NS NS 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U NS NS NS NS NS NS 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 

0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.4 U 0.39 U 0.39 U NS NS 0.33 U 1.2 J 0.33 U 0.33 U 0.33 U 1.2 J 1.4 J 0.33 U 0.34 U 0.33 U 0.33 U NS NS 

0.4 U 0.4 U 0.4 U 0.35 U 0.35 U 0.17 U 0.4 U 0.4 U 0.35 U 0.35 U 0.17 U 0.4 U 0.4 U 

2.4 J 1.3 J 10 U 1 J 10 U 0.9 U 1.1 J 10 U 0.9 J 10 U 0.9 U 1.2 J 10 U 

167 173 100 42.2 145 63.5 205 145 56.5 505 46.9 134 158 

0.049 U 0.049 U 0.082 U 0.082 U NS 0.088 U NS NS NS NS 0.088 U NS NS 

2.2 J 1.9 J 10 U 0.51 U 10 U 0.9 U 1.6 J 10 U 2 J 10 U 0.9 U 2.7 J 10 U 

22.7 36.3 18.4 J 5.4 J 20 U 3.6 U 9.5 J 12.8 J 60.8 20 U 6.7 U 28.3 114 

SW-4 SW-5 

12/21/2011 7:35 PM 
Table 2 - Surface Water Analytical Results

2009 - 2011

Screening

Analyte Value Unit

1,1,1-Trichloroethane 120 μg/L1,1-Dichloroethane 1 μg/L1,2-Dichloroethane 2 μg/L1,2-Dichloroethene (total) μg/L2-Butanone (MEK) 2 μg/LBenzene 1 μg/LChlorobenzene 100 μg/LEthylbenzene 530 μg/LTetrachloroethene 1 μg/LToluene 1 μg/LTrichloroethene 1 μg/LVinyl chloride 1 μg/L1,4-Dichlorobenzene 75 μg/Lbis(2-Ethylhexyl)phthalate 3 μg/LCadmium 3.4 μg/LChromium 92 μg/LManganese 50 μg/LMercury 0.05 μg/LNickel 500 μg/LZinc 7,400 μg/LpCi/L - Picocuries per LiterR - Rejected DataIndicates the analyte is not detected or not sampledNS - Not Sampled!g/L - Micrograms per LiterA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriaA cell highlighted and not bold Inidcates a detected analytethat does not exceed the screening criteria the quantitation/detection limit.UJ - Analyte was not detected in the sample, actual quantitation/detection limit may be higher than reported value.J - Result reported is a quantitative estimate

Metals

Qualifier Key:

U - Analyte not detected in the sample. Value represents

Volatile Organic Compounds

Semivolatile Organic Compounds

Sep-09 Apr-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 Sep-09 Apr-10 Oct-10 May-11 Sep-09 

NS NS NS 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U NS NS NS NS NS NS NS NS 0.44 J 0.29 U 0.29 U 0.29 U 0.29 U NS NS NS NS NS NS NS NS 0.33 U 0.33 U 0.33 U 0.33 UJ 0.33 U NS NS NS NS NS NS NS NS 0.22 U 0.62 J 0.51 J 0.53 J 0.22 U NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NS 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U NS NS NS NS NS NS NS NS 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U NS NS NS NS NS NS NS NS 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U NS NS NS NS NS NS NS NS 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U NS NS NS NS NS NS NS NS 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U NS NS NS NS NS NS NS NS 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U NS NS NS NS NS NS NS NS 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U NS NS NS NS NS 

0.43 U 0.44 U 0.4 U NS NS NS NS NS NS NS NS NS 0.39 U 0.36 U 0.37 U 1.1 J NS NS NS NS NS NS NS NS NS 0.33 U 

0.4 U 0.35 U 1.2 J 0.4 U 0.4 U 0.35 U 0.35 U 0.17 U 0.4 U 0.35 U 0.35 U 0.17 U 0.4 U 0.9 U 1.2 J 4.5 J 5.6 J 0.9 U 2 J 10 U 0.9 U 0.9 U 10 U 10 U 1.3 U 0.9 U 

47.4 13.7 J 566 465 316 189 479 88 46.8 18.2 31 29.6 29 

0.082 U 0.082 U 0.088 U 0.049 U 0.082 U 0.082 U 0.088 U 0.088 U 0.48 0.85 0.28 0.37 0.082 U 

1.1 J 10 U 4.2 U 6.8 J 1.7 J 10 U 10 U 1.3 U 10 U 10 U 10 U 1.9 U 10 U 

19.9 J 136 465 48.1 3.2 J 54.8 28.7 3 U 3.5 J 36.6 20 U 13.8 U 7.9 J 

SW-7 SW-8 SW-9 

12/21/2011 7:35 PM 
Table 3 - Sediment Analytical Results

2009 - 2011

Screening

Analyte Value Unit May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 

1,1,1-Trichloroethane 4.4 μg/kg 0.15 U 0.14 U 0.13 U 0.17 U 0.12 U 0.17 U 0.14 U 0.14 U 0.098 U 0.12 U 0.2 U 0.081 U 1,1-Dichloroethane 2.3 μg/kg 0.17 U 0.15 U 0.14 U 0.18 U 0.13 U 0.18 U 0.16 U 0.15 U 0.11 U 0.13 U 0.21 U 0.088 U 1,2-Dichloroethane 1.7 μg/kg 0.41 U 0.38 U 0.35 U 0.46 U 0.33 U 0.45 U 0.39 U 0.37 U 0.26 U 0.33 U 0.54 U 0.22 U 1,2-Dichloroethene (total) μg/kg 0.29 U 0.26 U 0.24 U 0.32 U 0.23 U 0.31 U 0.27 U 0.26 U 0.18 U 0.23 U 0.37 U 0.15 U 2-Butanone (MEK) 70 μg/kg NS NS 2 U NS 1.9 U NS NS 2.1 U 1.5 U 1.9 U NS NS Benzene 340 μg/kg 0.41 U 0.37 U 0.34 U 0.45 U 0.32 U 0.44 U 0.38 U 0.37 U 0.26 U 0.33 U 0.53 U 0.22 U Chlorobenzene 0.86 μg/kg 0.41 U 0.37 U 0.34 U 0.45 U 0.32 U 0.44 U 0.38 U 0.37 U 0.26 U 0.33 U 0.53 U 0.22 U Ethylbenzene 1,400 μg/kg 0.44 U 0.4 U 0.37 U 0.49 U 0.35 U 0.48 U 0.42 U 0.4 U 0.28 U 0.36 U 0.58 U 0.24 U Tetrachloroethene 450 μg/kg 0.17 U 0.16 U 0.15 U 0.19 U 0.14 U 0.19 U 0.16 U 0.16 U 0.11 U 0.14 U 0.22 U 0.092 U Toluene 2,500 μg/kg 0.35 U 0.32 U 0.73 J 0.39 U 0.28 U 0.38 U 0.33 U 1.5 0.22 U 0.28 U 0.93 J 0.19 U Trichloroethene 1,600 μg/kg 0.63 U 0.57 U 0.53 U 0.7 U 0.5 U 0.68 U 0.59 U 0.57 U 0.4 U 0.51 U 0.82 U 0.33 U Vinyl chloride 6.2 μg/kg 0.21 U 0.19 U 0.18 U 0.24 U 0.17 U 0.23 U 0.2 U 0.19 U 0.14 U 0.17 U 0.28 U 0.11 U 1,4-Dichlorobenzene 98 μg/kg 15 U 13 U 7.8 U 7.6 U 7.6 U 17 U 14 U 8 U 7.4 U 7.5 U 20 U 7.7 U bis(2-Ethylhexyl)phthalate 620 μg/kg 21 U 18 U 31 U 30 U 30 U 23 U 19 U 32 U 29 U 30 U 28 U 31 U Cadmium 0.6 mg/kg 0.034 U 0.037 U 0.05 U 0.028 U 0.041 U 0.04 U 0.036 U 0.051 U 0.027 U 0.04 U 0.2 J 0.036 U Chromium 26 mg/kg 7.4 1.5 1.3 U 1.3 U 0.98 J 2 1 J 1.3 U 1.2 U 3.5 8.1 1.8 Manganese 8.04 mg/kg 5.1 J 5.1 1.9 U 4.1 3.5 11 J 10.2 3.1 5 14.5 45.1 J 8.9 

Mercury 0.2 mg/kg 0.047 0.026 J 0.014 U 0.03 J 0.024 J 0.034 J 0.063 0.039 0.07 0.091 NS NS Nickel 16 mg/kg 4.6 U 0.17 J 0.2 J 0.28 J 0.21 J 5.4 U 0.24 J 0.12 U 0.11 J 0.33 J 6.7 U 0.38 J Zinc 120 mg/kg 9.8 J 3.3 2.9 2.9 2.2 J 4.4 J 2.5 1.6 J 2.5 U 2.8 18.6 J 3.2 R - Rejected Data

A cell highlighted and not bold Inidcates a detected analyte

that does not exceed the screening criteria

Indicates the analyte is not detected or not sampled

NS - Not Sampledmg/kg - Milligrams per Kilograms!g/kg - Micrograms per Kilograms

A Cell Highlighted and Bold Indicates a detected

analyte that exceeds the screening criteria

 the quantitation/detection limit.UJ - Analyte was not detected in the sample, actual quantitation/detection limit may be higher than reported value.J - Result reported is a quantitative estimate

Metals

Qualifier Key:

U - Analyte not detected in the sample. Value represents

Volatile Organic Compounds

Semivolatile Organic Compounds

SD-1 SD-2 

12/21/2011 7:54 PM 
Table 3 - Sediment Analytical Results

2009 - 2011

Screening

Analyte Value Unit

1,1,1-Trichloroethane 4.4 μg/kg1,1-Dichloroethane 2.3 μg/kg1,2-Dichloroethane 1.7 μg/kg1,2-Dichloroethene (total) μg/kg2-Butanone (MEK) 70 μg/kgBenzene 340 μg/kgChlorobenzene 0.86 μg/kgEthylbenzene 1,400 μg/kgTetrachloroethene 450 μg/kgToluene 2,500 μg/kgTrichloroethene 1,600 μg/kgVinyl chloride 6.2 μg/kg1,4-Dichlorobenzene 98 μg/kgbis(2-Ethylhexyl)phthalate 620 μg/kgCadmium 0.6 mg/kgChromium 26 mg/kgManganese 8.04 mg/kgMercury 0.2 mg/kgNickel 16 mg/kgZinc 120 mg/kgR - Rejected Data

A cell highlighted and not bold Inidcates a detected analyte

that does not exceed the screening criteria

Indicates the analyte is not detected or not sampled

NS - Not Sampledmg/kg - Milligrams per Kilograms!g/kg - Micrograms per Kilograms

A Cell Highlighted and Bold Indicates a detected

analyte that exceeds the screening criteria

 the quantitation/detection limit.UJ - Analyte was not detected in the sample, actual quantitation/detection limit may be higher than reported value.J - Result reported is a quantitative estimate

Metals

Qualifier Key:

U - Analyte not detected in the sample. Value represents

Volatile Organic Compounds

Semivolatile Organic Compounds

May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 

0.19 U 0.11 U 0.14 U 0.14 U 0.14 U 0.17 U 0.1 U 0.17 U 0.29 UJ 0.17 U 0.39 U 0.099 U 0.12 U 0.12 U 0.21 U 0.12 U 0.15 U 0.15 U 0.15 U 0.19 U 0.11 U 0.18 U 0.31 UJ 0.18 U 0.42 U 0.11 U 0.13 U 0.13 U 0.52 U 0.3 U 0.38 U 0.37 U 0.37 U 0.47 U 0.27 U 0.44 U 0.77 UJ 0.45 U 1.1 U 0.27 U 0.34 U 0.33 U 0.36 U 0.21 U 0.26 U 0.26 U 0.26 U 0.32 U 0.19 U 0.31 U 0.54 UJ 0.31 U 0.73 U 0.19 U 0.23 U 0.23 U 

NS NS 2.2 U 2.1 U 2.1 U NS NS 2.5 U 4.4 UJ 2.6 U 57.2 J NS 1.9 U 1.9 U 

0.51 U 0.29 U 0.38 U 0.37 U 0.37 U 0.46 U 0.27 U 0.44 U 0.76 UJ 0.44 U 1 U 0.26 U 0.33 U 0.32 U 

2 J 0.59 J 5.8 1 J 7.6 0.46 U 0.26 U 0.44 U 0.76 UJ 0.44 U 1 U 0.26 U 0.33 U 0.32 U 

0.56 U 0.32 U 0.41 U 0.4 U 0.4 U 0.5 U 0.29 U 0.48 U 0.83 UJ 0.48 U 1.1 U 0.29 U 0.36 U 0.35 U 0.22 U 0.13 U 0.16 U 0.16 U 0.16 U 0.2 U 0.11 U 0.19 U 0.32 UJ 0.19 U 0.44 U 0.11 U 0.14 U 0.14 U 

1.3 J 0.25 U 1.1 1.4 0.99 J 0.4 U 0.23 U 1.3 0.65 UJ 0.38 U 0.89 U 0.23 U 0.78 J 5 

0.79 U 0.45 U 0.58 U 0.57 U 0.57 U 0.71 U 0.41 U 0.68 U 1.2 UJ 0.68 U 1.6 U 0.41 U 0.51 U 0.5 U 0.27 U 0.15 U 0.2 U 0.19 U 0.19 U 0.24 U 0.14 U 0.23 U 0.4 UJ 0.23 U 0.54 U 0.14 U 0.17 U 0.17 U 

19 U 8.4 U 7.9 U 9.2 U 8.5 U 18 U 9.7 U 7.9 U 98.8 J 8.9 U 42 U 19 U 7.8 U 8.6 U 

26 U 33 U 31 U 37 U 34 U 24 U 38 U 31 U 54 UJ 77.6 J 57 U 25 U 31 U 34 U 

7.7 J 0.63 U 0.05 U 0.03 J 0.047 U 0.042 J 0.047 U 0.049 U 0.64 J 0.049 U 0.22 J 0.86 U 0.047 U 0.49 U 0

4.2 1.7 11.4 1.4 0.96 J 1.4 U 1.6 U 2.3 1.5 J 1.1 J 4.9 J 3.4 2.6 12.6 

20.6 J 15 4.3 9.7 5.1 2.6 J 6.2 4.1 51.9 J 4.5 30.5 J 14.4 2.8 45.5 

0.042 J 0.015 U 0.47 0.069 0.018 U 0.017 U 0.017 U 0.014 U 0.092 J 0.019 U 0.039 UJ 0.019 U 0.013 U 0.031 J 0

6.2 U 0.52 J 0.28 J 0.42 J 0.42 J 5.5 U 0.31 J 0.57 J 2.4 J 0.4 J 13 U 4.9 J 0.76 J 3.4 J 

10.5 J 5.3 3.2 2.6 22.9 5.3 J 6.2 34.4 77 J 2.7 J 53.6 J 27.5 24.3 400 

SD-4 SD-5 SD-6 

12/21/2011 7:54 PM 
Table 3 - Sediment Analytical Results

2009 - 2011

Screening

Analyte Value Unit

1,1,1-Trichloroethane 4.4 μg/kg1,1-Dichloroethane 2.3 μg/kg1,2-Dichloroethane 1.7 μg/kg1,2-Dichloroethene (total) μg/kg2-Butanone (MEK) 70 μg/kgBenzene 340 μg/kgChlorobenzene 0.86 μg/kgEthylbenzene 1,400 μg/kgTetrachloroethene 450 μg/kgToluene 2,500 μg/kgTrichloroethene 1,600 μg/kgVinyl chloride 6.2 μg/kg1,4-Dichlorobenzene 98 μg/kgbis(2-Ethylhexyl)phthalate 620 μg/kgCadmium 0.6 mg/kgChromium 26 mg/kgManganese 8.04 mg/kgMercury 0.2 mg/kgNickel 16 mg/kgZinc 120 mg/kgR - Rejected Data

A cell highlighted and not bold Inidcates a detected analyte

that does not exceed the screening criteria

Indicates the analyte is not detected or not sampled

NS - Not Sampledmg/kg - Milligrams per Kilograms!g/kg - Micrograms per Kilograms

A Cell Highlighted and Bold Indicates a detected

analyte that exceeds the screening criteria

 the quantitation/detection limit.UJ - Analyte was not detected in the sample, actual quantitation/detection limit may be higher than reported value.J - Result reported is a quantitative estimate

Metals

Qualifier Key:

U - Analyte not detected in the sample. Value represents

Volatile Organic Compounds

Semivolatile Organic Compounds

May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 Sep-09 Apr-10 Oct-10 

0.88 UJ 0.11 U 0.14 U 0.13 U 0.16 U 0.67 U 0.12 U 0.13 U 0.12 U 0.13 U 0.057 U 0.13 U 0.11 U 0.95 UJ 0.12 U 0.15 U 0.14 U 0.18 U 0.72 U 0.13 U 0.14 U 0.12 U 0.14 U 0.061 U 0.14 U 0.11 U 

2.4 UJ 0.3 U 0.37 U 0.36 U 0.44 U 1.8 U 0.33 U 0.36 U 0.31 U 0.36 U 0.15 U 0.34 U 0.29 U 1.6 UJ 0.21 U 0.48 J 0.25 U 0.31 U 1.2 U 0.23 U 0.25 U 0.22 U 0.25 U 0.11 U 0.24 U 0.2 U 

NS NS 2.1 U 2 U 2.5 U NS NS 2 U 1.8 U 2.1 U NS 2 U 1.6 U 

2.3 UJ 0.3 U 0.37 U 0.35 U 0.44 U 1.8 U 0.32 U 0.35 U 0.31 U 0.36 U 0.15 U 0.34 U 0.28 U 2.3 UJ 0.3 U 0.37 U 0.35 U 0.43 U 1.8 U 0.32 U 0.35 U 0.31 U 0.36 U 0.15 U 0.34 U 0.28 U 2.5 UJ 0.33 U 0.4 U 0.38 U 0.48 U 1.9 U 0.35 U 0.39 U 0.34 U 0.39 U 0.16 U 0.37 U 0.31 U 

0.99 UJ 0.13 U 0.16 U 0.15 U 0.19 U 0.75 U 0.14 U 0.15 U 0.13 U 0.15 U 0.064 U 0.14 U 0.12 U 

2 UJ 0.26 U 0.83 J 0.3 U 0.37 U 1.5 U 0.28 U 0.92 J 0.26 U 0.31 U 0.13 U 0.84 J 0.24 U 

3.6 UJ 0.46 U 0.57 U 0.54 U 0.67 U 2.7 U 0.5 U 0.55 U 0.48 U 0.55 U 0.23 U 0.52 U 0.44 U 1.2 UJ 0.16 U 0.19 U 0.18 U 0.23 U 0.93 U 0.17 U 0.19 U 0.16 U 0.19 U 0.079 U 0.18 U 0.15 U 

88 UJ 15 U 9.3 U 8.8 U 8.8 U NS NS 7.5 U NS NS 7.6 U 7.9 U 7.9 U 

120 UJ 20 U 37 U 35 U 35 U NS NS 30 U NS NS 30 U 31 U 31 U 

0.22 UJ 0.66 U 0.058 U 0.5 U 0.049 U 0.26 J 0.035 U 0.044 U 0.027 U 0.038 U 0.59 U 0.057 J 0.026 U 

9.6 J 3.2 4.2 4.1 5.3 9 J 0.34 J 1.1 U 1.2 U 1.2 2.1 2.2 1.5 

518 J 13.3 11 9.9 19.2 21.3 J 1.8 U 1.7 1.8 U 4.1 122 38.7 22.2 

0.082 UJ 0.016 U 0.017 J 0.07 0.019 J 0.17 J 0.37 0.3 0.39 1.5 0.013 U 0.013 U 0.018 J 

29 U 1.3 J 1.2 J 1.2 J 5.7 U 13 U 0.071 U 0.1 U 0.098 J 0.26 J 2 J 1.2 J 0.88 J 

52.4 J 6.4 7.3 7.3 13.1 61.4 J 0.9 J 0.87 J 2.4 U 1.2 J 13.9 10.9 8.2 

SD-8 SD-9 SD-10

12/21/2011 7:54 PM 
ATTACHMENT B 

FIGURES
%,D %,D

%,D %,D

%,D %,D %,D

%,D

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%,D %,D %,D %, %,D %,D

D %, %,D

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POINTVILLE RD

Cannon Run

SW!9

SW!8

SW!7

SW!6

SW!5

SW!4

SW!2

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SD!9

SD!8

SD!7

SD!6

SD!5

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SD!10

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LTM!7

LTM!6

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LTM!3

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LTM!39

LTM!37

LTM!36

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LTM!32

LTM!30

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SW!3

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LTM!15

LTM!41

LTM!44

LTM!42

LTM!43

LTM!38

LTM!40

LTM!45

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JULIUSTOWN RD

PEMBERTON BROWNS MILL RD

Budd's Run

Legend

A@ Monitoring Wells

&% Sediment/Surface Water Sample Location

%,D Gas Vents

Water Bodies

Streams

NPL Sanitary Landfill Boundary

FIGURE

Sampling Locations Map

1

Created By: AES

Date: February 2012

4501 Ford Ave.

Suite 1200

Alexandria, VA 22302

(P) 703.820.3339

(F) 703.845.8568

0 900 1800 2700

Feet

Ü

Final Close Out Report

JB!MDL, New Jersey
ATTACHMENT C 

2009 ECOLOGICAL RISK ASSESSMENT 
/-$!,&

,*'>#"'$%&4*4(-$#/+4&

)+-!$'*&6$,*-&$#/&)*/"4*#,&*'(%(<"'$%&*7$%+$,"(#Y&&

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!(-,&/"05&#*6&2*-)*1&

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Plexus Scientific

4501 Ford Ave, Ste. 1200 

Alexandria, VA 22302 

)E[\HJJCQ&[XY&

AVATAR Environmental, LLC 

107 South Church Street 

West Chester, PA 19382 

A;&4OMGZ&8;P;&
i

,$3%*&(!&'(#,*#,)&

)CGJHLI& .O]C&

1. INTRODUCTION .................................................................................................................. 1

2. SURFACE WATER AND SEDIMENT SAMPLING LOCATIONS ................................... 2

3. COMPARISON TO ECOLOGICAL SCREENING BENCHMARKS ................................. 4

3.1 Sediment ........................................................................................................................... 5

3.2 Surface Water ................................................................................................................. 10

4. CHEMICAL TRENDS IN SURFACE WATER AND SEDIMENT, AND ANY 

ANOMALIES ............................................................................................................................... 12

4.1 Chemical Trends ............................................................................................................ 12

4.1.1 Sediment Screening ................................................................................................ 13

4.1.2 Surface Water Screening ......................................................................................... 13

4.2 Anomalies ....................................................................................................................... 14

5. UNCERTAINTY ANALYSIS AND CONCLUSIONS ....................................................... 14

5.1 Sediment Benchmark Uncertainty ................................................................................. 16

5.1.1 PAHs ....................................................................................................................... 16

5.1.2 Pesticides................................................................................................................. 17

5.1.3 PCBs ....................................................................................................................... 17

5.1.4 Inorganics ................................................................................................................ 17

5.2 Surface Water Benchmark Uncertainty .......................................................................... 17

5.2.1 Semivolatiles ........................................................................................................... 18

5.2.2 Pesticides................................................................................................................. 19

5.2.3 Inorganics ................................................................................................................ 19

5.3 Conclusions .................................................................................................................... 19

6. REFERENCES ..................................................................................................................... 20

APPENDIX A – SAMPLE BY SAMPLE COMPARISONS TO BENCHMARKS 

,O[BCF&

Table 1 – Summary of Detected Concentrations Exceeding Sediment ESCs 

Table 2 – Summary of Detected Concentrations Exceeding Surface Water ESCs 

!H]EMC&

Figure 1 – Sediment and Surface Water Locations and Direction of Surface Water Flow 
1

PS& "#,-(/+',"(#&

The following document presents the an update of the results of the ecological screening 

evaluation for surface water and sediment data collected in Cannon Run and Budd’s Run, first 

performed in August 2009 (Avatar, 2009a). That document was prepared in response to EPA’s 

comments to the CERCLA Five-Year Review: Ft. Dix Sanitary Landfill (USACE, 2005) in a 

letter dated 29 September 2005 from George Pavlou (EPA) to Colonel R. David McNeil (U.S. 

Army, Ft. Dix) and as a result of discussions between Region 2 EPA and Ft. Dix staff and 

consultants on 11 June 2009. The screening assessment was conducted using the most recent 

NJDEP Ecological Screening Criteria (NJDEP, 2009; as found at 

www.state.nj.us/dep/srp/guidance/ecoscreening). In addition to the aforementioned benchmark 

screening, EPA requested that the following information be provided where possible: 

! Provide justification for current surface water and sediment sampling location based on 

historical records 

! Discuss any chemical trends in surface water and sediment data based on recently 

collected semi-annual surface water and sediment sampling

! Present any unique sampling issues (such as data anomalies) associated with any of the 

recent sampling events 

! Discuss the results of comparisons of recent surface water and sediment data to 

recommended benchmarks 

The remainder of this ecological screening evaluation is broken down into the following sections 

based on EPA specific information requests. It should be noted that this screening evaluation 

should not be construed as a complete screening-level or baseline ecological risk assessment. 

Rather, the primary objective of this report is to update the report that provided additional 

information as requested by Region 2 EPA during an 11 June 2009 meeting. 

The remainder of this evaluation is divided into the following sections: 

Section 2 – Surface Water and Sediment Sampling Locations 

Section 3 – Comparison to Ecological Screening Benchmarks 

Section 4 – Chemical Trends in Surface Water and Sediment, and Any Anomalies 

Section 5 – Uncertainty Analysis and Conclusions 

Section 6 – References 
2

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Surface water, sediment, and leachate sampling was originally performed in 1986 as part of the 

RI/FS Report (CDM, 1986 and 1987) to determine the impact of discharges from the Fort Dix 

Sanitary Landfill on the water quality of an unnamed stream (later referred to as Bud’s Run) 

north of the landfill and on Cannon Run, east and southeast of the landfill. Both water bodies 

eventually discharge into the North Branch of Rancocas Creek (CDM, 1985). In general, 

groundwater beneath the landfill runs in south-easterly direction toward Cannon Run (CDM, 

1986). Surface water and sediment samples were initially collected from two locations along 

Bud’s Run (SD/SW1 and SD/SW2) and five locations along Cannon Run (SD/SW3-SD/SW7) – 

see Figure 1 for sampling locations. The Long Term Monitoring Plan (LTMP) for the site was 

initiated in 1994 with quarterly groundwater, surface water, sediment and air sampling through 

the fall of 1995 followed by biannual sampling in subsequent years. 

Station 1 (SD/SW1) is situated to the east of the boundary of the Army Reservation and south of 

Pointville Road (upstream of a residential gardening area). Station 2 (SD/SW2) is located to the 

east, upstream approximately 50 feet from Pipeline Road. Both locations on Buds Run have 

course organic material and iron oxide present in the sediments. Surface waters at these 

locations are typically clear with a slight amber tint. 

Station 3, 4 and 5 are situated along Canon Run. Station 3 (SD/SW3) is the most downstream 

location and is about 40 feet north of Mills Road. Because it was believed that Station 3 surface 

water and sediment results were being impacted by run-off from the road, Station 3 was 

relocated for the Fall 2009 sampling event approximately 1100 feet upstream of the original 

location. Station 4 (SD/SW4) is located near a former beaver dam at the southern boundary of 

the landfill. Station 5 (SD/SW5) is sited south of the conduit along the mid-eastern boundary of 

the landfill. Sediment and surface water conditions at these locations are similar to those found 

at SD/SW1 and SD/SW2. 

Stations 6 and 7 (SD/SW6 and SD/SW7) are leachate seeps flowing in to Cannon Run from the 

eastern portion of the landfill, surface water samples have only been collected at these locations 

during season of heavy precipitation, sediment samples have been collected at these stations 
&%

&%

&%

&%

&%

&%

&%

&%

&%

&%

POINTVILLE RD

SW!9

SD!9

SW!8

SD!8

SW!7

SD!7

SW!6

SD!6

SW!5

SD!5

SW!4

SD!4

SW!2

SD!2

SW!1

SD!1

SW!10

SD!10

SW!3

SD!3

JULIUSTOWN RD

PEMBERTON BROWNS MILL RD

Budd's Run

H BRANCH RANCOCAS CREEK (GAUNTS

NPL Sanitary Landfill

EPIC 8 Landfill

PDO Landfill

Legend

&% Sediment/Surface Water Sample Location

Water Bodies

Streams

EPIC 8 Landfill

NPL Sanitary Landfill

PDO Landfill

FIGURE

Sediment and Surface Water

Locations and Direction of

Surface Water Flow

1

Created By: MJB

Date: May 2011

4501 Ford Ave.

Suite 1200

Alexandria, VA 22302

(P) 703.820.3339

(F) 703.845.8568

0 900 1800 2700

Feet

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Surface Water and Sediment

Ecological Evaluation

Surface Water Flow Direction
4

during each sampling round. Sediments at both these locations are heavy in organic debris and 

iron oxide deposits. Surface water, when available tends to contain iron floc and oily sheen. 

Station 8 (SD/SW8) is located in a wetland area southwest of the landfill and was first added to 

the surface water and sediment sampling program in the fall of 1994 to evaluate potential 

groundwater discharge for the grease pit area of the landfill. Surface water and sediment 

samples collected at S8 are typically organic rich with a heavy oily sheen. 

Station 9 (SD/SW9) is located approximately 1200 feet upstream from S2 and has had surface 

water and sediment samples collected since 2005. Station 10 (SD/SW10) is situated along 

Canon Run. This location was added to the sampling program in the Fall 2009 to address a 

potential data gap between Stations 4 and 5.

During each sampling event, samples were always taken, in order, from downstream to upstream 

sampling locations so that samples and sample locations would remain undisturbed by sampling 

events at other locations upstream. At each sampling location surface water samples were taken 

before sediment samples. Water samples were collected by submerging laboratory-cleaned 

sample bottles into the center portion of the stream. Sample bottles containing preservatives were 

not submerged. Sediment samples were collected slightly upstream of the surface water sampling 

location by pushing a sample jar into the sediments until a sufficient amount of sample had been 

collected.

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Appendix Tables A-1 and A-2 present sample by sample comparisons of detected concentrations 

at the Fort Dix NPL Landfill Site to ecological sediment and surface water benchmarks, 

respectively (Spring and Fall of 2008 and 2009 were included in this analysis). The Ecological

Screening Criteria (ESC) table developed by the New Jersey Department of Environmental 

Protection (NJDEP), Site Remediation Program (SRP), Environmental Toxicology and Risk 

Assessment (ETRA) Unit was used for both the sediment and surface water benchmarks 

(NJDEP, 2009). The ESC table is a compilation of various benchmark sources to allow ease of 

reference for ecological screening criteria. The primary source for both sediment and surface 

water values in the NJDEP ESC table is the EPA Region 5 RCRA Ecological Screening Level 
5

(ESL) table (EPA, 2003). The ESLs (previously known as ecological data quality levels or 

EDQLs) are the initial tool utilized in assessing adverse risk to the environment through the 

RCRA Corrective Action and Permit programs within Region 5. The ESLs provide protective 

benchmarks for 223 contaminants and four environmental media, including air, water, sediment, 

and soil. 

For the calculation of several inorganic surface water ESCs including chromium, copper, lead, 

nickel, and zinc, site-specific hardness values were calculated and used to derive hardnessdependent ESC values. Calcium and magnesium surface water concentrations were used in the 

following equation to arrive at sample-specific hardness values (EPA, 1999): 

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Once sample-specific hardness values were calculated, they were applied to the equations 

presented in footnotes (f)3 and (f)4 in the ESC table in order to arrive at hardness-dependent 

surface water ESCs.

Tables 1 and 2 present a summary of those detected sediment and surface water concentrations 

that exceeded their respective ESC values, as well as the magnitude of those exceedances. 

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Table A-1 presents a sample by sample comparison of detected sediment concentrations to 

sediment ESCs. In this evaluation, risks were estimated by comparing individual detected 

concentrations with the appropriate medium-specific ESC value as presented below: 

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The results of the screening process indicate that none of the volatile organic compounds (VOCs) 

had concentrations in exceedance of their respective sediment ESC. Note that 2-butanone, 

acetone, and carbon disulfide did not have available sediment ESCs for comparison. 

The following 12 of 22 detected semivolatile organic compounds (SVOCs) and polycyclic 

aromatic hydrocarbons (PAHs) had concentrations that exceeded their respective sediment ESC 

(samples exceeding/samples detected; ratio) (see Tables 1 and A-1): 
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Frequency of Number of ESC Number of ESC Number of ESC

Detected Concentrations Exceedances Exceedances Exceedances

Chemical Exceeding ESC > 1 < 10 > 10 < 100 > 100

Volatiles

2-Butanone NBA --- --- ---

Acetone NBA --- --- ---

Benzene 0/1 --- --- ---

Carbon disulfide NBA --- --- ---

Chlorobenzene 0/2 --- --- ---

Chloroform 0/1 --- --- ---

Ethylbenzene 0/2 --- --- ---

Methylene chloride 0/1 --- --- ---

Styrene 0/2 --- --- ---

Tetrachloroethene 0/3 --- --- ---

Toluene 0/5 --- --- ---

Xylenes (total) 0/3 --- --- ---

Semivolatiles

1,4-Dichlorobenzene 0/3 --- --- ---

Bis(2-ethylhexyl)phthalate 0/1 --- --- ---

Dibenzofuran NBA --- --- ---

Di-n-butyl phthalate 0/2 --- --- ---

Polycyclic Aromatic Hydrocarbons

2-Methylnaphthalene 1/1 --- 1 ---

Acenaphthene 1/1 1 --- ---

Acenaphthylene 4/4 4 --- ---

Anthracene 0/2 --- --- ---

Benzo(a)anthracene 2/12 2 --- ---

Benzo(a)pyrene 2/10 2 --- ---

Benzo(b)fluoranthene 0/9 --- --- ---

Benzo(k)fluoranthene 2/9 2 --- ---

Benzo(g,h,i)perylene 2/10 2 --- ---

Carbazole NBA --- --- ---

Chrysene 2/13 2 --- ---

Dibenzo(a,h)anthracene 1/3 1 --- ---

Fluoranthene 2/17 2 --- ---

Fluorene 0/1 --- --- ---

Indeno(1,2,3-cd)pyrene 2/10 2 --- ---

Naphthalene 0/1 --- --- ---

Phenanthrene 0/10 --- --- ---

Pyrene 2/16 2 --- ---

PAHs, total 5/20 5 --- ---

Pesticides

4,4'-DDD 13/17 11 2 ---

4,4'-DDE 22/24 15 6 1

4,4'-DDT 14/17 11 3 ---

DDT and Metabolites 20/21 12 6 2

Dieldrin 1/1 1 --- ---

Endosulfan-II NBA --- --- ---

gamma-Chlordane 0/1 --- --- ---

Polychlorinated Biphenyls

Aroclor 1254 1/1 --- 1 ---

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\March_2010_Tables_valued (3)
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Frequency of Number of ESC Number of ESC Number of ESC

Detected Concentrations Exceedances Exceedances Exceedances

Chemical Exceeding ESC > 1 < 10 > 10 < 100 > 100

Inorganics

Aluminum 0/36 --- --- ---

Antimony NBA --- --- ---

Arsenic 3/12 3 --- ---

Barium NBA --- --- ---

Beryllium NBA --- --- ---

Cadmium 3/10 3 --- ---

Calcium NBA --- --- ---

Chromium 0/33 --- --- ---

Cobalt 0/14 --- --- ---

Copper 9/29 9 --- ---

Cyanide 3/3 3 --- ---

Iron NBA --- --- ---

Lead 13/36 11 2 ---

Magnesium NBA --- --- ---

Manganese 1/39 1 --- ---

Mercury 6/27 6 --- ---

Nickel 1/19 1 --- ---

Potassium NBA --- --- ---

Selenium NBA --- --- ---

Silver 2/17 2 --- ---

Sodium NBA --- --- ---

Thallium NBA --- --- ---

Tin NBA --- --- ---

Vanadium NBA --- --- ---

Zinc 4/39 4 --- ---

ESC = Ecological Screening Criteria.

NBA = No benchmark available.

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\March_2010_Tables_valued (3)
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Frequency of Number of ESC Number of ESC Number of ESC

Detected Concentrations Exceedances Exceedances Exceedances

Chemical Exceeding ESC > 1 < 10 > 10 < 100 > 100

Volatiles

1,1-Dichloroethane NBA --- --- ---

Acetone NBA --- --- ---

Carbon Disulfide NBA --- --- ---

Chloromethane NBA --- --- ---

cis-1,2-Dichloroethene NBA --- --- ---

trans-1,2-Dichloroethene 0/1 --- --- ---

1,2-Dichloroethene (total) NBA --- --- ---

Toluene 0/1 --- --- ---

Semivolatiles

3-Methylphenol & 4-Methylphenol NBA --- --- ---

Bis(2-ethylhexyl)phthalate 2/2 2 --- ---

Butyl Benzyl Phthalate 0/1 --- --- ---

Phenol 0/1 --- --- ---

Polycyclic Aromatic Hydrocarbons

Anthracene 1/1 1 --- ---

Benzo(a)anthracene 1/1 --- 1 ---

Benzo(a)pyrene 1/1 --- 1 ---

Benzo(b)fluoranthene 0/1 --- --- ---

Benzo(k)fluoranthene NBA --- --- ---

Benzo(g,h,i)perylene 0/1 --- --- ---

Chrysene NBA --- --- ---

Fluoranthene 0/2 --- --- ---

Fluorene 0/1 --- --- ---

Indeno(1,2,3-cd)pyrene 0/1 --- --- ---

Phenanthrene 0/3 --- --- ---

Pyrene 1/2 1 --- ---

Pesticides

4,4'-DDD NBA --- --- ---

4 4' DDE 4,4'-DDE 1/1 --- --- 1

Inorganics

Aluminum NBA --- --- ---

Antimony 1/1 1 --- ---

Arsenic 1/3 1 --- ---

Barium 2/19 2 --- ---

Beryllium 1/1 1 --- ---

Calcium NBA --- --- ---

Chromium 0/11 --- --- ---

Cobalt 1/8 1 --- ---

Copper 6/8 5 1 ---

Iron NBA --- --- ---

Lead 9/9 8 1 ---

Magnesium NBA --- --- ---

Manganese NBA --- --- ---

Mercury 0/6 --- --- ---

Nickel 0/11 --- --- ---

Potassium NBA --- --- ---

Selenium 1/1 --- 1 ---

Sodium NBA --- --- ---

Thallium 0/3 --- --- ---

Tin 0/1 --- --- ---

Vanadium 1/1 --- 1 ---

Zinc 2/22 2 --- ---

ESC = Ecological Screening Criteria.

NBA = No benchmark available.

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\March_2010_Tables_valued (3)
9

! 2-Methylnaphthalene (1/1; ratio of 13.8) 

! Acenaphthene (1/1; ratio of 3.4) 

! Acenaphthylene (4/4; maximum ratio of 9.2) 

! Benzo(a)anthracene (2/12; maximum ratio of 2.9) 

! Benzo(a)pyrene (2/10; maximum ratio of 3.1) 

! Benzo(k)fluoranthene (2/9; maximum ratio of 3.7) 

! Benzo(g,h,i)perylene (2/10; maximum ratio of 5.4) 

! Chrysene (2/13; maximum ratio of 3.0) 

! Dibenzo(a,h)anthracene (1/3; ratio of 4.9) 

! Fluoranthene (2/17; maximum ratio of 1.9) 

! Indeno(1,2,3-cd)pyrene (2/10; maximum ratio of 3.9) 

! Pyrene (2/16; maximum ratio of 2.7) 

Both dibenzofuran and carbazole did not have available sediment ESCs for comparison. In 

addition to the comparison of individual PAHs to ESCs, total PAHs were also compared. Five of 

the 20 detected total PAH concentrations exceeded the total PAHs sediment ESC with a 

maximum ratio of 6.3. As presented in Table 1, with the exception of 2-methylnaphthalene, all 

of the above SVOCs and PAHs exceeded the sediment ESC by less than a factor of 10. 

Of the 6 detected pesticides detected in sediments, the following had concentrations that 

exceeded their respective sediment ESC (samples exceeding/samples detected; ratio) (see Tables 

1 and A-1): 

! 4,4’-DDD (13/17; maximum ratio of 36) 

! 4,4’-DDE (22/24; maximum ratio of 154) 

! 4,4’-DDT (14/17; maximum ratio of 94.5) 

! Dieldrin (1/1; ratio of 4.4) 

Endosulfan-II did not have an available sediment ESC for comparison. In addition to the 

comparison of 4,4’-DDD, 4,4’-DDE, and 4,4’-DDT to ESCs, DDT and metabolites were also 

compared. Twenty of the 21 detected DDT and metabolites concentrations exceeded the 

sediment ESC with a maximum ratio of 223. Eight of these 21 detected concentrations exceeded 

the sediment ESC with a ratio greater than 10 and 2 exceeded the sediment ESC with a ratio 

greater than 100. The remaining 12 DDT and metabolites concentrations exceeded the sediment 

ESC by less than a factor of 10. As presented in Table 1, 2 of the 17 detected 4,4’-DDD 

concentrations, 6 of the 24 detected 4,4’-DDE concentrations, and 3 of the 17 detected 4,4’-DDT 

concentrations exceeded the sediment ESC with a ratio greater than 10. One of the detected 4,4’-
10

DDE concentrations exceeded the sediment ESC with a ratio greater than 100. The remaining 

concentrations exceeded the sediment ESC by less than a factor of 10. 

Aroclor 1254 had a single detection which exceeded the sediment ESC with a ratio of 18.7. 

Ten of the 25 detected inorganics had detected sediment concentrations that exceeded their 

respective sediment ESC (see Table 1). Compounds for which no sediment ESC was available 

include antimony, barium, beryllium, calcium, iron, magnesium, potassium, selenium, sodium, 

thallium, tin, and vanadium. Calcium, iron, magnesium, potassium, and sodium are trace 

essential nutrients and are not expected to pose any substantial ecological risk to receptors at the 

site. The following 10 inorganics had concentrations that exceeded their respective sediment 

ESC (samples exceeding/samples detected; ratio) (see Tables 1 and A-1): 

! Arsenic (3/12; maximum ratio of 4.0) 

! Cadmium (3/10; maximum ratio of 2.5) 

! Copper (9/29; maximum ratio of 5.1) 

! Cyanide (3/3; maximum ratio of 7.2) 

! Lead (13/36; maximum ratio of 29) 

! Manganese (1/39; ratio of 1.3) 

! Mercury (6/27; maximum ratio of 7.5) 

! Nickel (1/19; ratio of 1.1) 

! Silver (2/17; ratio of 1.2) 

! Zinc (4/39; maximum ratio of 5.8) 

With the exception of 2 out of 36 detected lead concentrations, all of the above inorganics 

exceeded the sediment ESC by less than a factor of 10. 

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Table A-2 presents a sample by sample comparison of detected surface water concentrations to 

surface water ESCs. As mentioned previously, risks were estimated by comparing individual 

detected concentrations with the appropriate medium-specific ESC value as presented below: 

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11

The results of the screening process indicate that none of the volatile organic compounds (VOCs) 

had concentrations in exceedance of their respective surface water ESC. Note that only trans1,2-dichloroethene and toluene had available surface water ESCs for comparison. 

The following 5 of 16 detected SVOCs and PAHs had concentrations that exceeded their 

respective surface water ESC (samples exceeding/samples detected; ratio) (see Tables 2 and A2):

! Bis(2-ethylhexyl)phthalate (2/2; maximum ratio of 4.7) 

! Anthracene (1/1; ratio of 5.1) 

! Benzo(a)anthracene (1/1; ratio of 23) 

! Benzo(a)pyrene (1/1; ratio of 31) 

! Pyrene (1/2; ratio of 3.1) 

One SVOC (3&4-Methylphenol) and 2 PAHs (benzo(k)fluoranthene and chrysene) did not have 

available surface water ESCs for comparison. Total PAHs was not evaluated in surface water 

due to a lack of an available ESC. As presented in Table 2, with the exception of 

benzo(a)anthracene and benzo(a)pyrene, all of above SVOCs and PAHs exceeded the surface 

water ESC by less than a factor of 10. 

Of the 2 detected pesticides (4,4’-DDD and 4,4’-DDE) detected in surface water, only 4,4’-DDE 

had a benchmark available. 4,4’-DDE had a single concentration that exceeded the surface water 

ESC with a ratio of 4,878,049. A DDT and metabolites concentration was not calculated for 

surface water due to a lack of an available ESC. 

Ten of the 22 detected inorganics had detected surface water concentrations that exceeded their 

respective surface water ESC (see Table 2). Compounds for which no surface water ESC was 

available include aluminum, calcium, iron, magnesium, manganese, potassium, and sodium. 

Calcium, iron, magnesium, potassium, and sodium are trace essential nutrients and are not 

expected to pose any substantial ecological risk to receptors at the site. The following 10 

inorganics had concentrations that exceeded their respective surface water ESC (samples 

exceeding/samples detected; ratio) (see Tables 2 and A-2): 

! Antimony (1/1; ratio of 2.9) 

! Arsenic (1/3; ratio of 2.4) 
12

! Barium (2/19; maximum ratio of 8.0) 

! Beryllium (1/1; ratio of 1.5) 

! Cobalt (1/8; ratio of 2.3) 

! Copper (6/8; maximum ratio of 10.2) 

! Lead (9/9; maximum ratio of 39) 

! Selenium (1/1; ratio of 33) 

! Vanadium (1/1; ratio of 16) 

! Zinc (2/22; ratio of 4.8) 

With the exception of copper, lead, selenium, and vanadium, all of the above inorganics 

exceeded the surface water ESC by less than a factor of 10. As presented in Table 2, 1 of the 8 

detected copper concentrations, 1 of the 9 detected lead concentrations, the only detected 

selenium concentration, and the only detected vanadium concentration all exceeded the surface 

water ESC with a ratio greater than 10. The remaining copper and lead concentrations exceeded 

the surface water ESC by less than a factor of 10. 

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Prior to discussing the trends analysis (Plexus, 2010) as it relates to the aquatic screening results,

it is important to note the differences in data handling between the two exercises. It should be 

noted that the trends analysis approach has been used and accepted in previous reports for 

regulatory review (e.g., EA, 2007 and 2008). 

Trends Analysis Benchmark Screening 

Data from November 1994 to October 2009 May and October 2008; May and September 2009 

Only primary samples used. Primary and field duplicate samples considered. 

Non-detected samples set to zero. Non-detected samples assumed to be present at the 

reporting limit. 

All detected samples within a LAP that were less than 

the highest reporting limit were set to zero. 

All detected concentrations were retained as-was. 

Only LAPs with at least four unique non-zero 

concentrations from the reduced data set were run 

through the Mann-Kendall analysis. 

All detected chemicals were screened against 

benchmarks. 

LAP = Location-Analyte Pair. LAPs are a combination of the location and chemical name. For example SD-1 

Aluminum represents sediment sample location #1 aluminum analyses.
13

4.1.1 Several detected chemicals had recent concentrations that exceeded 

benchmarks. However, because of the data set characteristics (e.g., small 

number of detects), some of the detected chemicals that exceeded benchmarks 

were not able to be evaluated in the trends analysis. Sediment Screening 

Of detected chemicals with recent concentrations that exceed benchmarks, only the following 

LAPs had trends analysis performed. 

! Acenaphthylene (SD-7) 

! Cadmium (SD-4) 

! Copper (SD-6 through 9) 

! 4,4’-DDE (SD-1 and SD-4 through SD-9) 

! 4,4’-DDT (SD-1 and SD-6 through 9) 

! Lead (SD-6, SD-7, and SD-9) 

! Manganese (SD-2 through 4 and SD-6 through 9) 

! Mercury (SD-7 and SD-9) 

! 2-Methylnaphthalene (SD-7) 

Increasing trends were noted for the following: 

! Copper (SD-6) 

! 4,4’-DDE (SD-1 and SD-4 through 7) 

! 4,4’-DDT (SD-1, SD-6, and SD-7) 

! Lead (SD-6) 

! Manganese (SD-4 and SD-6) 

Note that although there is an increasing trend for manganese in sediments at locations SD-4 and 

SD-6, the most recent concentrations in these areas did not exceed the LEL. No other trends 

were identified for the pairs called out above. 

4.1.2 Surface Water Screening 

Of detected chemicals with recent concentrations that exceed benchmarks, only the following 

LAPs had trends analysis performed. 

! Arsenic (SW-6 and SW-8) 

! Barium (SW-8) 

! Benzo(a)pyrene (SW-5) 

! Copper (SW-2, SW-6, and SW-8) 

! Lead (SW-2, SW-4 through 6, and SW-8) 

! Zinc (SW-2, SW-6, and SW-8) 
14

An increasing trend was noted for copper in SW-6. No other trends were identified for these 

pairs.

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As specifically requested by Region 2 EPA, the surface water and sediment database for the Ft. 

Dix Landfill (years 2004-2009) was queried to identify the presence and frequency of detection 

of chemicals of special ecological concern (i.e., chemicals that are highly bioaccumulative and 

eco-toxic). The database was searched for the presence of mercury and PCBs (note: dioxins 

were not included in any surface water and sediment analysis and therefore were not included in 

this evaluation). 

PCBs were only detected in sediment samples twice during the past five years: Aroclor 1260 was 

detected in sediment in the fall of 2004 at sample station SD-7 (18 μg/kg) and Aroclor 1254 was 

detected in sediment at location SD-7 (1120 μg/kg) in the fall of 2008; there were no PCBs 

detected in any of the surface water samples collected. 

Mercury was frequently detected in most of the surface water and sediment sampling location 

from 2004-2009; however there was no apparently pattern or trend associated with these 

detections. While mercury detected concentrations were typically low, concentrations in 

sediments exceeded 1 mg/kg on four occasions at the following locations: 

! SD-8, Sept. 04, 1.1 mg/kg; 

! SD-9, Apr. 05, 2.9 mg/kg; 

! SD-2, May 08, 1.2 mg/kg; and 

! SD-7, May 09, 1.5 mg/kg. 

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Environmental conditions at the time of sampling could have an effect on what concentrations of 

contaminants are found in the surface water and sediment. In areas along the streams where 

contaminated groundwater recharge is not in the immediate vicinity, taking samples during high 

water or storm events could lead to decreases in observed concentration (i.e., dilution from 

increased non-contaminated surface run-off). However, in areas of the seeps, taking samples 

after rain events could lead to increases in the observed concentrations as increased groundwater 
15

volume could force the flow of contaminants from under the landfill to the seep areas. During 

the LTMP program the effect rainfall events does not impact the protectiveness of the remedy. 

Because of the diversity of sediment types, surface water environs, test species, chemical forms, 

and test procedures, it is not possible to estimate benchmarks that would constitute thresholds for 

toxic effects on all organisms under all environmental conditions. 

The use of benchmark values for evaluating the potential impacts of reported contaminant 

concentrations in sediments and surface water has the following associated uncertainties: 

! Benchmarks do not address possible synergistic, antagonistic, or additive effects of 

contaminant mixtures. The risk may be over- or under-estimated, depending on the 

interactions among the various chemicals present at the site.

! The test conditions used in the toxicological studies used to develop chemicalspecific benchmarks may not match the conditions in the stream downgradient from 

the landfill; therefore, the benchmarks may over- or under-estimate risk at the site. 

Testing conditions may have differed from the site in the following ways: 

- The form in which a chemical was added to the medium in deriving the 

benchmark may not be representative of the form the chemical is found in at 

the site. This is particularly true where the metallic salts added for toxicity 

testing purposes enhance the bioavailability of the metal relative to the metal 

species present under equilibrium conditions (i.e., complexed or strongly 

bound forms present). 

- The stream conditions (soil type, pH, temperature, and percent total organic 

carbon [TOC]) in the studies from which the benchmarks were derived may 

not mimic those conditions found on-site. 

- Studies from which chemical-specific benchmarks were derived reflect the 

complex physicochemical processes and mineral complexes of the soil, 

sediments, and surface water in which the study was conducted. It is unlikely 

that the specific nutrient and mineral composition of these mixtures match the 

conditions in the stream. 

! Benchmarks and guidelines do not exist for all contaminants detected at the site. For 

contaminants that do not have benchmarks, the potential for risk cannot be 

ascertained. 

! The benchmarks used do not consider factors that influence chemical bioavailability 

(e.g., site-specific organic carbon concentrations, redox potential [Eh], pH). 

Particularly for metals, the use of total concentration, rather than an estimate of the 
16

bioavailable fraction, represents a conservative estimate of exposure, and may overestimate risk. 

! Different species of plants and animals exhibit varying degrees of sensitivity to 

chemical stressors. The species used to derive the screening benchmarks do not 

necessarily have the same sensitivities as those found at the site. Consequently, the 

risk to ecological receptors at the site may be over- or under-estimated. 

:SP& )CQH\CIJ&3CIGZ\OM_&+IGCMJOHIJX&

In general, sediment benchmarks do not address possible synergistic, antagonistic, or additive 

effects of contaminant mixtures; do not consider unmeasured chemicals; and are not useful for 

chemicals for which little or no toxicological information is available (Giesy and Hoke, 1990). 

Studies used to develop chemical-specific sediment guidelines involved a complex mixture of 

contaminants. These mixtures most likely do not match the conditions in the stream. Sediment 

quality guidelines are generally based on overt toxicity to benthic invertebrates and do not 

consider other potential effects such as bioaccumulation and subsequent effects on longer-lived 

species. These uncertainties can result in under- or over-estimation of risks. 

The following paragraphs address uncertainty associated with the specific sediment guidelines 

and benchmarks used in this screening. 

Sediment benchmarks were not available for 2-butanone, acetone, carbon disulfide, 

dibenzofuran, carbazole, endosulfan II, antimony, barium, beryllium, calcium, iron, magnesium, 

potassium, selenium, sodium, thallium, tin, or vanadium; therefore some potential risks are not 

evaluated herein. However, potential effects from carbazole are considered in the total PAH 

comparison. The endosulfan sulfate (0.0346 mg/kg) value can be used as a surrogate for 

endosulfan II. The maximum detected concentration of endosulfan II is 0.0041 mg/kg, 

approximately an order of magnitude lower than the endosulfan sulfate LEL. Lastly, calcium, 

iron, magnesium, potassium, and sodium can be considered essential nutrients and are generally 

not evaluated in ecological risk assessments. 

5.1.1 PAHs 

As noted previously, 12 of the 19 detected PAHs were detected in at least one sample at 

concentrations that exceeded the LEL-based ESC values. These values generally represent 

concentrations at which no toxic effects are expected. Associated severe effect levels (SELs) 
17

were examined, and of the PAHs, only 2-methylnaphthalene had a concentration exceeding the 

levels at which effects are probable. That is, 0.28 mg/kg (at SD-7 in May 09) versus the 

Environment Canada (CCME, 2002) Probable Effects Level (PEL) of 0.201 mg/kg. Note that 

this value is actually for marine organisms as a freshwater value was not available. 

5.1.2 Pesticides 

Sediment concentrations of DDT and its metabolites (individually and as a group) and dieldrin 

exceeded the sediment LEL-based ESCs. As noted previously, these values generally represent 

concentrations at which no toxic effects are expected. Associated SELs were examined, and the 

one detected concentration of dieldrin (0.0087 mg/kg) was below the SEL value (0.91 mg/kg 

assuming a TOC of 1%). DDT and its metabolites had maximum detected concentrations 

exceeding the SELs. 

5.1.3 PCBs 

Aroclor 1254 was detected in 1 of 17 samples. The detected concentration, 1.1 mg/kg exceeded 

both the LEL (0.06 mg/kg) and SEL (0.34 mg/kg assuming a TOC of 1%) values. Aroclor 1260 

was not positively identified in any sample. 

5.1.4 Inorganics 

All inorganics with upper-bound benchmarks available had concentrations lower than their 

respective upper-bound benchmark, with the exception of lead. Two of the 36 samples with 

detected concentrations of lead had concentrations higher than the SEL of 250 mg/kg. Cyanide 

and silver did not have an upper bound benchmark available. 

EPA Region 2 asked specifically for a discussion regarding mercury. Mercury was detected in 

25 of 33 samples. Detected concentrations in six samples exceeded the LEL (0.2 mg/kg); with 

the maximum detected concentration (1.5 mg/kg) to LEL ratio of 7.5. None of the 

concentrations exceeded the SEL (2 mg/kg). 

:S8& )EMKOGC&6OJCM&3CIGZ\OM_&+IGCMJOHIJX&

The use of surface water benchmarks for evaluating the potential impacts of reported 

contaminant concentrations in surface water has the following general associated uncertainties: 
18

! The use of the benchmarks as a screening tool cannot be interpreted as a direct 

measurement of site-specific bioavailability.

! There may be differences between the species with toxicological data used to develop the 

surface water benchmark and those present in the stream. 

! Most benchmarks are based on a threshold for statistical significance rather than 

biological significance. 

! There is uncertainty surrounding the extrapolation of laboratory data (used to develop 

criteria) to field conditions.

! Acute and subchronic laboratory toxicity tests frequently do not measure the most 

sensitive ecological endpoints; in particular, fecundity is often not measured (Suter, 

1996a).

! Chronic ambient water quality criteria (AWQC) and benchmarks derived in like ways are 

based on the most statistically sensitive of the measured response parameters in each 

chronic or subchronic test. Therefore, cumulative effects over the life cycle of fish and 

invertebrates are not considered (Suter, 1996b). This would tend to underestimate risk. 

The following paragraphs address uncertainty associated with the specific sediment guidelines 

and benchmarks used in this screening. 

Surface water benchmarks were not available for the following detected VOCs (1,1-

dichloroethane, acetone, carbon disulfide, chloromethane, cis-1,2-dichloroethene, and total 1,2-

dichloroethene), 3&4-methylphenol, benzo(k)fluoranthene, chrysene, 4,4’-DDD, aluminum, 

calcium, iron, magnesium, manganese, potassium, and sodium; therefore some potential risks are 

not evaluated herein. However, calcium, iron, magnesium, potassium, and sodium can be 

considered essential nutrients and are generally not evaluated in ecological risk assessments. 

5.2.1 Semivolatiles 

Both detected concentrations of bis(2-ethylhexyl)phthalate exceeded the freshwater chronic 

criteria, which was the EPA Region V ESL for phthalate esters. However, according to USEPA 

(2006), “There is a full set of aquatic life toxicity data that show that DEHP is not toxic to 

aquatic organisms at or below its solubility limit.” 
19

5.2.2 Pesticides 

As noted above, 4,4’-DDD did not have an N.J.A.C. freshwater criterion. In addition, 4,4’-DDE 

had a criterion of 4.51E-09 μg/L. This value is the Region V ESL based on modeled exposures 

to a kingfisher and is not appropriate for evaluating freshwater aquatic community (e.g., fish) 

risks. The chronic national AWQC for DDT and metabolites is 0.001 μg/L. The sum of the 

DDD, DDE, and DDT concentrations should not exceed this value. The maximum DDT and 

metabolites concentration calculated for samples in which at least one of the compounds is 

detected is 0.0728 μg/L (range = 0.0258 to 0.0728 μg/L). Therefore, it is likely that HQ for the 

aquatic community exposed to 4,4’-DDE is highly overestimated. 

5.2.3 Inorganics 

The benchmark values are derived for dissolved concentrations. Comparing total recoverable 

concentrations with dissolved benchmarks is conservative and likely overestimates potential 

risks.

The values for antimony, barium, beryllium, cobalt, and vanadium are Tier II values that are 

derived from data sets that are not robust enough from which to derive criteria. It is not known if 

the use of these values would under- or over-estimate risk. 

The only detected beryllium concentration exceeded the surface water benchmark with a ratio of 

1.48. However, the benchmark is the EPA Region V ESL, which is a hardness-based value 

assuming a hardness of 50 mg/L. Equations to recalculate the ESL using site-specific hardness 

values are not provided; but given that the sample-specific hardness associated with the detected 

concentration of beryllium is 233 mg/L, it is likely that the HQ for the aquatic community 

exposed to beryllium is overestimated. 

:SA& 'LIGBEFHLIF&&

The most frequent and substantial exceedances of sediment benchmarks were associated with 

4,4’-DDT and its metabolites, which are ubiquitous within the study area. Several PAHs were 

detected at concentrations exceeding sediment benchmark values, with most of those 

exceedances associated with SD/SW3 (the most downstream sample in Cannon Run) and 

leachate sample SD/SW7. A majority of the metals sediment benchmark exceedances occurred 
20

at SD/SW9 (the most upstream location in Budd’s Run), SD/SW7 and SD/SW8 (the wetland 

area located southwest of the landfill). 

There was a limited number of surface water benchmark exceedances observed in the 2008 and 

2009 samples. Semivolatile exceedances were limited to SD/SW4 (near a former beaver dam in 

Cannon Run at the southern boundary of the landfill) and SD/SW5 (in Cannon Run south of the 

conduit along the mid-eastern boundary of the landfill). Inorganic exceedances were most 

frequent at leachate sample SD/SW6 in Oct. 08 and SD/SW4 and SD/SW8 in May 09. 

Sediment and surface water exceedances of benchmarks and screening criteria continue to occur 

in Budd’s and Cannon Run. In addition, the most recent trend analysis indicates that for site 

related chemicals exceeding ecological benchmarks, increasing trends of 4,4’-DDE, 4,4’-DDT, 

copper, and lead in sediment and of copper and mercury in surface water were observed. 

=S& -*!*-*#'*)&

Avatar (Avatar Environmental, LLC). 2009a. Technical Memorandum: Surface Water and 

Sediment Ecological Evaluation: Fort Dix Sanitary Landfill, Fort Dix, New Jersey. 

Submitted to Plexus Scientific, Alexandria, VA. August 2009. 

Avatar (Avatar Environmental, LLC). 2009b. NPL Sanitary Landfill Long Term Monitoring 

Program Statistical Analyses of Temporal Trends of Chemical Levels in Groundwater, 

Surface Water and Sediment: Fort Dix, New Jersey. Submitted to Plexus Scientific, 

Alexandria, VA. February 2009. 

CCME (Canadian Council of Ministers of the Environment). 2002. Canadian Sediment Quality 

Guidelines for the Protection of Aquatic Life. Summary Tables. Update 2002. 

Camp Dresser & McGee, Inc. 1987. Remedial Investigation Report Study for Fort Dix Sanitary 

Landfill, Pemberton Township, New Jersey -Proposed Response Addendum 1. January 

Camp Dresser & McGee, Inc. 1986. Remedial Investigation Report for Fort Dix Sanitary Landfill, 

Pemberton Township, New Jersey -Proposed Response. September. 

Camp Dresser & McGee, Inc. 1985. Remedial Investigation/ Feasibility Study for Fort Dix Sanitary 

Landfill, Pemberton Township, New Jersey –Interim Report. December. 

EA (EA Engineering, Science, and Technology, Inc.). 2008. 2007 Sampling and Analysis Report 

for Groundwater, Surface Water, and Sediment for the Fort Dix Sanitary Landfill. Draft. 

March 2008. 
21

EA Engineering, Science and Technology, Inc. 2007. 2006 Sampling and Analysis Report for 

Groundwater, Surface Water, and Sediment for the Fort Dix Sanitary Landfill. March. 

EA Engineering, Science and Technology, Inc. 2002. Addendum to the Long-Term Monitoring 

Plan for the Sanitary Landfill, Fort Dix, New Jersey. April.

EPA (U.S. Environmental Protection Agency). 2006. National Recommended Water Quality 

Criteria. Office of Water. Office of Science and Technology. (4304T). 

EPA (U.S. Environmental Protection Agency) Region V. 2003. RCRA Ecological Screening 

Levels. 22 August 2003. Available online: http://www.epa.gov/reg5rcra/ca/ESL.pdf

EPA (U.S. Environmental Protection Agency). 1999. Standard Operating Procedure for the 

Analysis of the Hardness of Water by Calculation from ICP Metals Data. 15 December 

1999.

Geisy, J.P. and R.A. Hoke. 1990. Freshwater Sediment Quality Criteria: Toxicity Bioassessment. 

In: R. Baudo, J. Geisy, and H. Muntau (Eds.) Sediments: Chemistry and Toxicity of In-place 

Pollutants. Lewis Publ. Inc., Chelsea, MI. 

NJDEP (New Jersey Department of Environmental Protection). 2009. Ecological Screening 

Criteria. 10 March 2009. Available online: 

http://www.state.nj.us/dep/srp/guidance/ecoscreening/

Plexus Scientific, Inc. 2009. 2008 Sampling and Analysis Report for Groundwater, Surface Water, 

and Sediment for the Fort Dix Sanitary Landfill. March.

Plexus Scientific, Inc. 2010. Sanitary Landfill 2009 Sampling and Analysis Report at Fort Dix 

Sanitary Landfill. July.

Suter, G.W. 1996a. Toxicological benchmarks for screening contaminants of potential concern for 

effects on freshwater biota. Enviro. Tox. Chem. 15:1232-124. 

Suter, G.W. 1996b. Abuse of hypothesis testing statistics in ecological risk assessments. Human 

and Ecological Risk Assessment. 2:331-347. 

U.S. Army Corps of Engineers (USACE). 2005. Second Five-Year Review Report for U.S. Army 

Fort Dix (NPL Landfill Site) Fort Dix, New Jersey. September. 
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Fresh water Ratio of Ratio of Ratio of 

Frequency Criteriaa SD-1 May-08 Detected SD-1 Oct-08 Detected SD-1 May-09 Detected 

of LEL May-08 Concentration to Oct-08 Concentration to May-09 Concentration to 

Chemical Detection (mg/kg) (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria 

Volatiles

2-Butanone 5/18 3.7E-02 - 1.6E-01 NBA ND --- ND --- NA --- Acetone 22/33 7.5E-03 - 4.6E+00 NBA 1.00E-01 J --- 2.43E-01 J --- 1.31E-02 J --- Benzene 1/33 1.9E-03 - 1.9E-03 1.42E-01 ND --- ND --- ND --- Carbon disulfide 8/33 3.5E-04 - 2.6E-02 NBA ND --- ND --- ND --- Chlorobenzene 2/33 5.9E-04 - 2.0E-03 2.91E-01 ND --- ND --- ND --- Chloroform 1/33 1.0E-02 - 1.0E-02 1.21E-01 ND --- ND --- ND --- Ethylbenzene 2/33 6.1E-04 - 7.4E-04 1.75E-01 ND --- ND --- ND --- Methylene chloride 1/33 1.1E-02 - 1.1E-02 1.59E-01 ND --- ND --- ND --- Styrene 2/33 1.1E-02 - 1.2E-02 2.54E-01 1.10E-02 J 4.33E-02 ND --- ND --- Tetrachloroethene 3/33 4.3E-03 - 3.9E-02 9.90E-01 3.90E-02 J 3.94E-02 ND --- ND --- Toluene 5/33 9.3E-04 - 2.1E-03 1.22E+00 ND --- ND --- ND --- Xylenes (total) 3/33 7.8E-04 - 1.3E-02 4.33E-01 ND --- ND --- ND --- 

Semivolatiles

1,4-Dichlorobenzene 3/33 5.4E-03 - 1.5E-02 3.18E-01 ND --- ND --- ND --- 

Bis(2-ethylhexyl)phthalate 1/33 4.3E-02 - 1.2E-01 1.82E-01 ND --- ND --- ND --- Dibenzofuran 1/33 7.6E-02 - 7.6E-02 NBA ND --- ND --- ND --- Di-n-butyl phthalate 2/33 4.2E-02 - 1.6E-01 1.11E+00 ND --- ND --- ND --- Polycyclic Aromatic Hydrocarbons2-Methylnaphthalene 1/24 2.8E-01 - 2.8E-01 2.02E-02 NA --- ND --- ND --- Acenaphthene 1/33 2.3E-02 - 2.3E-02 6.71E-03 ND --- ND --- ND --- Acenaphthylene 4/33 1.1E-02 - 5.4E-02 5.87E-03 ND --- ND --- ND --- Anthracene 2/33 6.8E-02 - 1.3E-01 2.20E-01 ND --- ND --- ND --- Benzo(a)anthracene 11/33 1.4E-02 - 9.4E-01 3.20E-01 ND --- 2.89E-02 J 9.03E-02 5.37E-02 1.68E-01 Benzo(a)pyrene 9/33 1.8E-02 - 1.1E+00 3.70E-01 ND --- 3.09E-02 J 8.35E-02 4.71E-02 1.27E-01 Benzo(b)fluoranthene 9/33 2.5E-02 - 1.1E+00 1.04E+01 ND --- 3.28E-02 J 3.15E-03 3.98E-02 J 3.83E-03 Benzo(k)fluoranthene 9/33 2.2E-02 - 9.0E-01 2.40E-01 ND --- 2.20E-02 J 9.17E-02 4.11E-02 1.71E-01 Benzo(g,h,i)perylene 9/33 1.9E-02 - 9.2E-01 1.70E-01 ND --- 2.32E-02 J 1.36E-01 3.14E-02 J 1.85E-01 Carbazole 2/33 2.8E-02 - 5.3E-02 NBA ND --- ND --- ND --- Chrysene 12/33 1.4E-02 - 1.0E+00 3.40E-01 ND --- 3.53E-02 J 1.04E-01 5.15E-02 1.51E-01 Dibenzo(a,h)anthracene 3/33 1.4E-02 - 2.9E-01 6.00E-02 ND --- ND --- ND --- Fluoranthene 14/33 1.8E-02 - 1.5E+00 7.50E-01 1.10E-01 J 1.47E-01 5.70E-02 7.60E-02 8.48E-02 1.13E-01 Fluorene 1/33 2.7E-02 - 2.7E-02 1.90E-01 ND --- ND --- ND --- Indeno(1,2,3-cd)pyrene 9/33 1.7E-02 - 7.7E-01 2.00E-01 ND --- 1.98E-02 J 9.90E-02 3.26E-02 J 1.63E-01 Naphthalene 1/33 1.7E-01 - 1.7E-01 1.76E-01 ND --- ND --- ND --- Phenanthrene 10/33 2.7E-02 - 5.0E-01 5.60E-01 7.80E-02 J 1.39E-01 3.88E-02 6.93E-02 3.07E-02 J 5.48E-02 Pyrene 13/33 1.6E-02 - 1.3E+00 4.90E-01 8.10E-02 J 1.65E-01 5.09E-02 1.04E-01 7.98E-02 1.63E-01 PAHs, total 17/33 2.5E-01 - 2.5E+01 4.00E+00 9.27E+00 2.32E+00 4.36E-01 1.09E-01 6.06E-01 1.51E-01 

Concentrations 

(mg/kg)

Range of Detected SD-1 SD-1 SD-1 

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Fresh water Ratio of Ratio of Ratio of 

Frequency Criteriaa SD-1 May-08 Detected SD-1 Oct-08 Detected SD-1 May-09 Detected 

of LEL May-08 Concentration to Oct-08 Concentration to May-09 Concentration to 

Chemical Detection (mg/kg) (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria 

Concentrations 

(mg/kg)

Range of Detected SD-1 SD-1 SD-1 

Pesticides

4,4'-DDD 15/33 2.9E-03 - 2.9E-01 8.00E-03 ND --- ND --- ND --- 

4,4'-DDE 21/33 3.0E-03 - 7.7E-01 5.00E-03 ND --- 1.41E-02 2.82E+00 1.24E-02 2.48E+00 4,4'-DDT 15/33 3.7E-03 - 7.6E-01 8.00E-03 ND --- 2.79E-02 3.49E+00 1.73E-02 2.16E+00 DDT and Metabolites 20/27 6.8E-03 - 1.6E+00 7.00E-03 ND --- 4.23E-02 6.04E+00 3.00E-02 4.28E+00 Dieldrin 1/33 8.7E-03 - 8.7E-03 2.00E-03 ND --- ND --- ND --- Endosulfan-II 1/33 4.1E-03 - 4.1E-03 NBA ND --- ND --- ND --- gamma-Chlordane 1/32 2.3E-03 - 2.3E-03 7.00E-03 b ND --- ND --- ND --- 

Polychlorinated Biphenyls

Aroclor 1254 1/17 1.1E+00 - 1.1E+00 6.00E-02 ND --- ND --- NA --- 

Inorganics

Aluminum 36/36 4.8E+01 - 8.7E+03 2.55E+04 2.11E+03 J 8.27E-02 1.91E+03 7.49E-02 3.19E+03 1.25E-01 Antimony 7/36 3.5E-01 - 3.9E+01 NBA ND --- 7.00E-01 J --- ND --- 

Arsenic 11/36 3.3E-01 - 2.4E+01 6.00E+00 ND --- 2.10E+00 J 3.50E-01 2.70E+00 4.50E-01 Barium 23/36 6.7E+00 - 2.6E+02 NBA 5.31E+01 J --- ND --- 7.00E+00 J --- 

Beryllium 7/36 2.8E-02 - 2.2E-01 NBA ND --- ND --- 6.80E-02 J --- 

Cadmium 10/36 4.2E-02 - 1.5E+00 6.00E-01 ND --- 4.30E-02 J 7.17E-02 ND --- 

Calcium 25/36 7.6E+01 - 1.5E+04 NBA 3.56E+03 J --- ND --- 7.63E+01 J --- 

Chromium 33/36 3.4E-01 - 2.4E+01 2.60E+01 3.90E+00 J 1.50E-01 4.40E+00 1.69E-01 7.40E+00 2.85E-01 

Cobalt 14/36 1.5E-01 - 2.2E+01 5.00E+01 ND --- 3.10E-01 J 6.20E-03 1.50E-01 J 3.00E-03 Copper 25/36 2.6E+00 - 8.1E+01 1.60E+01 7.40E+00 J 4.63E-01 4.40E+00 2.75E-01 5.80E+00 J 3.63E-01 

Cyanide 3/12 1.3E-01 - 7.2E-01 1.00E-01 ND --- NA --- NA --- 

Iron 36/36 2.4E+02 - 3.5E+05 NBA 2.05E+03 J --- 2.75E+03 --- 3.21E+03 --- Lead 32/36 7.8E-01 - 9.0E+02 3.10E+01 2.49E+01 J 8.03E-01 3.00E+01 J 9.68E-01 1.59E+01 5.13E-01 

Magnesium 28/36 6.9E+00 - 4.0E+03 NBA 3.90E+02 J --- ND --- 2.33E+02 J --- 

Manganese 35/36 2.5E+00 - 8.2E+02 6.30E+02 6.07E+01 J 9.63E-02 7.70E+00 J 1.22E-02 5.10E+00 J 8.10E-03 

Mercury 25/33 2.6E-02 - 1.5E+00 2.00E-01 6.00E-02 J 3.00E-01 4.00E-02 2.00E-01 4.70E-02 2.35E-01 

Nickel 16/36 1.7E-01 - 1.7E+01 1.60E+01 ND --- 1.40E+00 J 8.75E-02 ND --- 

Potassium 10/36 2.5E+01 - 5.8E+02 NBA NA --- NA --- 3.29E+02 J --- 

Selenium 7/36 4.2E-01 - 5.0E+00 NBA ND --- 4.20E-01 J --- ND --- 

Silver 15/36 5.5E-02 - 5.8E-01 5.00E-01 1.30E-01 J 2.60E-01 ND --- ND --- 

Sodium 18/36 7.2E+00 - 4.2E+02 NBA ND --- 7.20E+00 J --- 2.35E+01 J --- 

Thallium 3/36 3.8E-01 - 1.7E+00 NBA 9.30E-01 J --- ND --- ND --- 

Tin 5/36 2.4E+00 - 2.9E+01 NBA ND --- ND --- ND --- 

Vanadium 19/36 9.7E-01 - 2.5E+01 NBA 6.50E+00 J --- 8.20E+00 --- 8.90E+00 J --- 

Zinc 35/36 9.0E-01 - 7.0E+02 1.20E+02 4.50E+01 J 3.75E-01 9.50E+00 7.92E-02 9.80E+00 J 8.17E-02 

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Chemical

Volatiles

2-ButanoneAcetoneBenzeneCarbon disulfideChlorobenzeneChloroformEthylbenzeneMethylene chlorideStyreneTetrachloroetheneTolueneXylenes (total)

Semivolatiles

1,4-DichlorobenzeneBis(2-ethylhexyl)phthalateDibenzofuranDi-n-butyl phthalatePolycyclic Aromatic Hydrocarbons2-MethylnaphthaleneAcenaphtheneAcenaphthyleneAnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneCarbazoleChryseneDibenzo(a,h)anthraceneFluorantheneFluoreneIndeno(1,2,3-cd)pyreneNaphthalenePhenanthrenePyrenePAHs, total

Ratio of Ratio of Ratio of Ratio 

SD-2 May-08 Detected SD-2 Oct-08 Detected SD-2 May-09 Detected SD-2 Sept-09 

Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentra

Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening C

--- ND --- NA --- NA ------ ND --- 1.15E-02 J --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ 6.10E-04 J 3.49E-03 ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ---

4.34E-03 ND --- ND --- ND ---

--- 1.20E-03 J 9.84E-04 ND --- ND ------ 3.30E-03 7.62E-03 ND --- NA ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- ND ------ ND --- ND --- NA ---

SD-2 SD-2 SD-2

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Chemical

Pesticides

4,4'-DDD4,4'-DDE4,4'-DDTDDT and MetabolitesDieldrinEndosulfan-IIgamma-Chlordane

Polychlorinated Biphenyls

Aroclor 1254

Inorganics

AluminumAntimonyArsenicBariumBerylliumCadmiumCalciumChromiumCobaltCopperCyanideIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSilverSodiumThalliumTinVanadiumZinc

Ratio of Ratio of Ratio of Ratio 

SD-2 May-08 Detected SD-2 Oct-08 Detected SD-2 May-09 Detected SD-2 Sept-09 

Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentra

Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening C

SD-2 SD-2 SD-2

1.03E+00 NA --- NA --- NA ---

1.12E+00 NA --- NA --- NA ---

8.00E-01 NA --- NA --- NA ---

2.89E+00 NA --- NA --- NA ---

--- NA --- NA --- NA ---

--- NA --- NA --- NA ---

--- NA --- NA --- NA ---

--- NA --- NA --- NA ---

4.12E-02 1.30E+02 5.10E-03 3.62E+02 1.42E-02 4.36E+02 1.71E-

--- 3.50E-01 J --- ND --- ND ---

--- 3.30E-01 J 5.50E-02 ND --- ND ------ ND --- 6.70E+00 J --- ND ---

--- ND --- 5.40E-02 J --- ND ---

--- ND --- ND --- ND ---

--- ND --- 1.66E+02 J --- ND ---

2.08E-01 9.00E-01 J 3.46E-02 2.00E+00 7.69E-02 1.00E+00 J 3.85E-2.40E-02 ND --- ND --- ND ---

1.81E-01 ND --- 2.70E+00 J 1.69E-01 ND ---

--- NA --- NA --- NA ---

--- 3.64E+02 --- 4.68E+02 --- 3.58E+02 ---

1.81E-01 ND --- 4.20E+00 1.35E-01 1.70E+00 J 5.48E-

--- 1.29E+01 J --- 3.03E+01 J --- 2.23E+01 J ---

1.40E-02 5.10E+00 J 8.10E-03 1.10E+01 J 1.75E-02 1.02E+01 1.62E-

6.00E+00 1.40E-01 7.00E-01 3.40E-02 J 1.70E-01 6.30E-02 3.15E-

--- 2.50E-01 J 1.56E-02 ND --- 2.40E-01 J 1.50E-

--- NA --- 2.54E+01 J --- ND ---

--- ND --- ND --- ND ---

1.10E-01 ND --- ND --- ND ---

--- ND --- 1.90E+01 J --- ND ---

--- ND --- ND --- ND ---

--- ND --- ND --- ND ---

--- 9.70E-01 J --- ND --- ND ---

9.58E-02 ND --- 4.40E+00 J 3.67E-02 2.50E+00 2.08E

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

2-ButanoneAcetoneBenzeneCarbon disulfideChlorobenzeneChloroformEthylbenzeneMethylene chlorideStyreneTetrachloroetheneTolueneXylenes (total)

Semivolatiles

1,4-DichlorobenzeneBis(2-ethylhexyl)phthalateDibenzofuranDi-n-butyl phthalatePolycyclic Aromatic Hydrocarbons2-MethylnaphthaleneAcenaphtheneAcenaphthyleneAnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneCarbazoleChryseneDibenzo(a,h)anthraceneFluorantheneFluoreneIndeno(1,2,3-cd)pyreneNaphthalenePhenanthrenePyrenePAHs, total

Ratio of Ratio of Ratio of 

SD-3 May-08 Detected SD-3 Oct-08 Detected SD-3 May-09 Detected Relocat

May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 C

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Sc

3.70E-02 J --- ND --- NA --- NA 

4.10E-02 J --- ND --- 1.46E-02 J --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

1.20E-02 J 4.72E-02 ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- 9.30E-04 J 7.62E-04 ND 

ND --- ND --- ND --- NA 

6.30E-03 J 1.98E-02 ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

NA --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

5.70E-01 J 1.78E+00 ND --- 4.03E-02 J 1.26E-01 1.43E-02 J 

7.00E-01 J 1.89E+00 ND --- 4.71E-02 J 1.27E-01 ND 

6.60E-01 J 6.35E-02 ND --- 4.31E-02 J 4.14E-03 ND 

7.50E-01 J 3.13E+00 ND --- 3.56E-02 J 1.48E-01 ND 

2.90E-01 J 1.71E+00 ND --- 3.41E-02 J 2.01E-01 ND 

ND --- ND --- ND --- ND 

8.70E-01 J 2.56E+00 ND --- 4.79E-02 J 1.41E-01 1.44E-02 J 

ND --- ND --- ND --- ND 

1.40E+00 J 1.87E+00 ND --- 8.60E-02 1.15E-01 ND 

ND --- ND --- ND --- ND 

3.00E-01 J 1.50E+00 ND --- 2.91E-02 J 1.46E-01 ND 

ND --- ND --- ND --- ND 

4.20E-01 J 7.50E-01 ND --- 2.80E-02 J 5.00E-02 ND 

9.80E-01 J 2.00E+00 ND --- 6.67E-02 1.36E-01 ND 

2.04E+01 5.09E+00 ND --- 6.24E-01 1.56E-01 NA 

SD-3 SD-3 SD-3 SD-3 Relocation

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE4,4'-DDTDDT and MetabolitesDieldrinEndosulfan-IIgamma-Chlordane

Polychlorinated Biphenyls

Aroclor 1254

Inorganics

AluminumAntimonyArsenicBariumBerylliumCadmiumCalciumChromiumCobaltCopperCyanideIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSilverSodiumThalliumTinVanadiumZinc

Ratio of Ratio of Ratio of 

SD-3 May-08 Detected SD-3 Oct-08 Detected SD-3 May-09 Detected Relocat

May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 C

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Sc

SD-3 SD-3 SD-3 SD-3 Relocation

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- NA --- NA 

8.40E+03 J 3.29E-01 5.00E+02 1.96E-02 1.72E+03 6.75E-02 4.33E+02 

ND --- ND --- ND --- ND 

ND --- 5.40E-01 J 9.00E-02 ND --- ND 

1.36E+02 J --- ND --- 2.10E+01 J --- ND 

ND --- ND --- 1.70E-01 J --- ND 

6.10E-01 J 1.02E+00 ND --- 2.00E-01 J 3.33E-01 ND 

5.81E+03 J --- ND --- 3.30E+02 J --- ND 

1.29E+01 J 4.96E-01 2.70E+00 1.04E-01 8.10E+00 3.12E-01 1.80E+00 

2.19E+01 J 4.38E-01 ND --- 1.90E+00 J 3.80E-02 ND 

8.10E+00 J 5.06E-01 ND --- 5.50E+00 J 3.44E-01 ND 

7.20E-01 J 7.20E+00 NA --- NA --- NA 

7.99E+04 J --- 1.25E+03 --- 8.03E+03 --- 1.70E+03 3.85E+01 J 1.24E+00 2.70E+00 J 8.71E-02 7.00E+00 2.26E-01 ND 9.77E+02 J --- 7.58E+01 J --- 2.05E+02 J --- 6.90E+01 J 8.20E+02 J 1.30E+00 7.20E+00 J 1.14E-02 4.51E+01 J 7.16E-02 8.90E+00 

2.20E-01 J 1.10E+00 NA --- NA --- NA 

ND --- 6.60E-01 J 4.13E-02 ND --- 3.80E-01 J 

NA --- NA --- 3.55E+02 J --- 1.61E+02 J 

ND --- ND --- ND --- ND 

2.20E-01 J 4.40E-01 ND --- ND --- 2.30E-01 J 

ND --- 1.08E+01 J --- 3.27E+01 J --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

2.00E+01 J --- 1.40E+00 J --- ND --- ND 

1.72E+02 J 1.43E+00 6.60E+00 5.50E-02 1.86E+01 J 1.55E-01 3.20E+00 

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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

2-ButanoneAcetoneBenzeneCarbon disulfideChlorobenzeneChloroformEthylbenzeneMethylene chlorideStyreneTetrachloroetheneTolueneXylenes (total)

Semivolatiles

1,4-DichlorobenzeneBis(2-ethylhexyl)phthalateDibenzofuranDi-n-butyl phthalatePolycyclic Aromatic Hydrocarbons2-MethylnaphthaleneAcenaphtheneAcenaphthyleneAnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneCarbazoleChryseneDibenzo(a,h)anthraceneFluorantheneFluoreneIndeno(1,2,3-cd)pyreneNaphthalenePhenanthrenePyrenePAHs, total

Ratio of Ratio of Ratio of Ratio of 

SD-4 May-08 Detected SD-4 Oct-08 Detected SD-4-DUP Oct-08 Detected SD-4 May-09 Detected 

May-08 Concentration to Oct-08 Concentration to Oct-08 Concentration to May-09 Concentration to May-

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/k

ND --- ND --- ND --- NA --- NA 

5.10E-02 J --- ND --- ND --- 3.45E-02 J --- 4.66E-01.90E-03 J 1.34E-02 ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- 2.00E-03 J 6.87E-03 1.60E-0ND --- ND --- ND --- ND --- ND ND --- 7.40E-04 J 4.23E-03 ND --- ND --- ND 

1.10E-02 J 6.92E-02 ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND --- ND 

8.40E-03 J 8.48E-03 ND --- ND --- ND --- ND 

ND --- 1.10E-03 J 9.02E-04 1.40E-03 J 1.15E-03 1.30E-03 J 1.07E-03 2.10E-0ND --- 5.20E-03 1.20E-02 1.34E-02 3.09E-02 ND --- 7.80E-0ND --- ND --- ND --- ND --- ND 

1.20E-01 J 6.59E-01 ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- ND --- ND NA --- ND --- ND --- ND --- ND ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- 3.43E-02 J 1.07E-01 ND ND --- ND --- ND --- 3.92E-02 J 1.06E-01 ND ND --- ND --- ND --- 3.93E-02 J 3.78E-03 ND ND --- ND --- ND --- 2.81E-02 J 1.17E-01 ND ND --- ND --- ND --- 3.07E-02 J 1.81E-01 ND ND --- ND --- ND --- ND --- ND ND --- ND --- 3.38E-02 J 9.94E-02 4.00E-02 J 1.18E-01 ND ND --- ND --- ND --- ND --- ND 

1.20E-01 J 1.60E-01 ND --- 5.13E-02 J 6.84E-02 7.44E-02 9.92E-02 4.06E-0

ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- 2.76E-02 J 1.38E-01 ND ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- 5.17E-02 9.23E-02 2.99E-0ND --- ND --- 4.55E-02 J 9.29E-02 5.94E-02 1.21E-01 3.31E-0

1.41E+01 3.53E+00 ND --- 5.76E-01 1.44E-01 5.78E-01 1.45E-01 4.64E-0

SD-4 SD-4 SD-4-DUP SD-4 SD-4-D

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE4,4'-DDTDDT and MetabolitesDieldrinEndosulfan-IIgamma-Chlordane

Polychlorinated Biphenyls

Aroclor 1254

Inorganics

AluminumAntimonyArsenicBariumBerylliumCadmiumCalciumChromiumCobaltCopperCyanideIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSilverSodiumThalliumTinVanadiumZinc

Ratio of Ratio of Ratio of Ratio of 

SD-4 May-08 Detected SD-4 Oct-08 Detected SD-4-DUP Oct-08 Detected SD-4 May-09 Detected 

May-08 Concentration to Oct-08 Concentration to Oct-08 Concentration to May-09 Concentration to May-

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/k

SD-4 SD-4 SD-4-DUP SD-4 SD-4-D

ND --- ND --- 2.90E-03 3.63E-01 3.30E-03 4.13E-01 ND 

1.50E-02 J 3.00E+00 ND --- 1.78E-02 3.56E+00 7.20E-03 1.44E+00 5.90E-0

ND --- ND --- 3.70E-03 4.63E-01 ND --- ND 

2.56E-02 3.66E+00 ND --- 2.44E-02 3.49E+00 1.10E-02 1.57E+00 6.75E-0

ND --- ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND --- ND 

ND --- ND --- ND --- NA --- NA 

2.32E+03 J 9.10E-02 9.95E+02 3.90E-02 1.17E+03 J 4.59E-02 1.29E+03 5.06E-02 1.03E+0

ND --- ND --- ND --- ND --- ND 

ND --- 1.90E+00 J 3.17E-01 1.50E+00 J 2.50E-01 ND --- ND 

2.43E+01 J --- ND --- ND --- 1.23E+01 J --- 1.37E+0

ND --- ND --- ND --- 4.60E-02 J --- 6.90E-0

ND --- ND --- ND --- 1.20E-01 J 2.00E-01 ND 

3.31E+03 J --- 1.04E+03 --- 1.18E+03 J --- 1.29E+03 --- 9.62E+0

6.20E+00 J 2.38E-01 3.60E+00 1.38E-01 4.10E+00 J 1.58E-01 4.20E+00 1.62E-01 3.50E+07.70E+00 J 1.54E-01 ND --- ND --- 3.30E+00 J 6.60E-02 5.10E+0

6.00E+00 J 3.75E-01 6.60E+00 4.13E-01 5.10E+00 J 3.19E-01 7.40E+00 J 4.63E-01 6.10E+0

6.00E-01 J 6.00E+00 NA --- NA --- NA --- NA 

1.02E+04 J --- 3.42E+03 --- 2.93E+03 J --- 2.78E+03 --- 4.01E+0

4.71E+01 J 1.52E+00 2.30E+01 J 7.42E-01 2.13E+01 J 6.87E-01 2.60E+01 8.39E-01 2.10E+01.91E+02 J --- 8.67E+01 J --- ND --- 1.27E+02 J --- 1.04E+0

5.92E+01 J 9.40E-02 4.06E+01 J 6.44E-02 5.37E+01 J 8.52E-02 2.06E+01 J 3.27E-02 2.20E+0

1.70E-01 J 8.50E-01 5.40E-02 2.70E-01 7.50E-02 J 3.75E-01 4.20E-02 J 2.10E-01 5.00E-0

ND --- 1.30E+00 J 8.13E-02 9.50E-01 J 5.94E-02 ND --- ND 

NA --- NA --- NA --- 1.05E+02 J --- 9.95E+0

ND --- ND --- ND --- ND --- ND 

3.30E-01 J 6.60E-01 ND --- ND --- ND --- ND 

ND --- 1.23E+01 J --- 1.58E+01 J --- 2.31E+01 J --- 2.65E+0

ND --- 3.80E-01 J --- ND --- ND --- ND 

2.40E+00 J --- ND --- ND --- ND --- ND 

1.22E+01 J --- 3.90E+00 J --- 4.00E+00 J --- ND --- ND 

2.41E+01 J 2.01E-01 7.60E+00 6.33E-02 1.02E+01 J 8.50E-02 1.05E+01 J 8.75E-02 1.02E+0

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

2-ButanoneAcetoneBenzeneCarbon disulfideChlorobenzeneChloroformEthylbenzeneMethylene chlorideStyreneTetrachloroetheneTolueneXylenes (total)

Semivolatiles

1,4-DichlorobenzeneBis(2-ethylhexyl)phthalateDibenzofuranDi-n-butyl phthalatePolycyclic Aromatic Hydrocarbons2-MethylnaphthaleneAcenaphtheneAcenaphthyleneAnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneCarbazoleChryseneDibenzo(a,h)anthraceneFluorantheneFluoreneIndeno(1,2,3-cd)pyreneNaphthalenePhenanthrenePyrenePAHs, total

Ratio of Ratio of Ratio of Ratio of 

SD-4 Sept-09 Detected SD-5 May-08 Detected SD-5 Oct-08 Detected SD-5 May-09 Detected 

Concentration to May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-0

Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/k

--- ND --- ND --- NA --- NA --- 7.30E-02 --- ND --- 2.18E-02 J --- 6.20E-0--- ND --- ND --- ND --- ND --- ND --- ND --- ND --- 4.20E-0

2.03E-03 ND --- ND --- ND --- ND 

--- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- 1.10E-03 J 9.02E-04 ND --- ND --- ND --- ND --- ND --- ND --- NA --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- NA --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND 

6.06E-02 ND --- ND --- ND --- ND 

--- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND 

4.06E-02 ND --- ND --- ND --- ND 

--- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND 

3.29E-02 ND --- ND --- ND --- ND 

--- ND --- ND --- ND --- NA 

SD-5 SD-5 SD-5 SD-5

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE4,4'-DDTDDT and MetabolitesDieldrinEndosulfan-IIgamma-Chlordane

Polychlorinated Biphenyls

Aroclor 1254

Inorganics

AluminumAntimonyArsenicBariumBerylliumCadmiumCalciumChromiumCobaltCopperCyanideIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSilverSodiumThalliumTinVanadiumZinc

Ratio of Ratio of Ratio of Ratio of 

SD-4 Sept-09 Detected SD-5 May-08 Detected SD-5 Oct-08 Detected SD-5 May-09 Detected 

Concentration to May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-0

Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/k

SD-5 SD-5 SD-5 SD-5

--- 1.10E-02 J 1.38E+00 1.61E-02 2.01E+00 ND --- 5.30E-0--- 4.70E-02 9.40E+00 3.16E-02 6.32E+00 1.83E-02 3.66E+00 4.10E-0--- 2.90E-02 3.63E+00 ND --- 6.50E-03 NJ 8.13E-01 ND 

--- 8.70E-02 1.24E+01 5.02E-02 7.17E+00 2.51E-02 3.59E+00 1.01E-0--- ND --- ND --- ND --- ND 

--- ND --- ND --- ND --- ND 

--- ND --- ND --- ND --- ND 

--- ND --- ND --- NA --- NA 

2.38E-02 7.86E+02 J 3.08E-02 2.92E+03 J 1.15E-01 4.28E+02 1.68E-02 4.06E+0

--- ND --- ND --- ND --- ND 

--- ND --- 5.60E+00 J 9.33E-01 ND --- ND 

--- 2.51E+01 J --- 7.59E+01 J --- 2.01E+01 J --- ND 

--- ND --- ND --- 2.80E-02 J --- ND 

--- ND --- ND --- 4.20E-02 J 7.00E-02 ND 

--- 3.40E+02 J --- 1.27E+04 J --- 1.74E+02 J --- ND 

6.54E-02 1.60E+00 J 6.15E-02 7.70E+00 J 2.96E-01 ND --- ND 

--- ND --- 1.00E+00 J 2.00E-02 ND --- ND 

--- 2.60E+00 J 1.63E-01 1.35E+01 J 8.44E-01 3.60E+00 J 2.25E-01 ND --- ND --- NA --- NA --- NA 

--- 1.39E+03 J --- 1.46E+05 J --- 4.97E+02 --- 1.75E+0

4.06E-01 3.17E+01 J 1.02E+00 4.88E+01 J 1.57E+00 1.84E+01 5.94E-01 8.00E+0

--- ND --- ND --- 2.41E+01 J --- ND 

2.38E-02 3.60E+00 J 5.71E-03 1.92E+02 J 3.05E-01 2.60E+00 J 4.13E-03 6.20E+0

--- 6.30E-02 J 3.15E-01 1.90E-01 J 9.50E-01 ND --- ND 

3.25E-02 ND --- ND --- ND --- 3.10E-0

--- NA --- NA --- 3.61E+01 J --- ND 

--- ND --- 5.00E+00 J --- ND --- ND 

7.80E-01 ND --- ND --- ND --- 4.40E-0

--- ND --- 8.22E+01 J --- 2.00E+01 J --- ND 

--- ND --- ND --- ND --- ND 

--- ND --- ND --- ND --- ND 

--- 4.00E+00 J --- ND --- ND --- ND 

4.42E-02 1.35E+01 J 1.13E-01 4.01E+01 3.34E-01 5.30E+00 J 4.42E-02 6.20E+0

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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

2-ButanoneAcetoneBenzeneCarbon disulfideChlorobenzeneChloroformEthylbenzeneMethylene chlorideStyreneTetrachloroetheneTolueneXylenes (total)

Semivolatiles

1,4-DichlorobenzeneBis(2-ethylhexyl)phthalateDibenzofuranDi-n-butyl phthalatePolycyclic Aromatic Hydrocarbons2-MethylnaphthaleneAcenaphtheneAcenaphthyleneAnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneCarbazoleChryseneDibenzo(a,h)anthraceneFluorantheneFluoreneIndeno(1,2,3-cd)pyreneNaphthalenePhenanthrenePyrenePAHs, total

Ratio of Ratio of Ratio of Ratio of 

SD-6 May-08 Detected SD-6 Oct-08 Detected SD-6 May-09 Detected SD-6 Sept-09 Detected 

May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to S

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (m

ND --- 5.78E-02 J --- 5.72E-02 J --- NA --- N

2.20E+00 D --- 7.95E-01 --- 3.77E-01 J --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- 2.63E-02 J --- 1.32E-02 J --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- NA --- N

5.40E-03 J 1.70E-02 ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- 4.3

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

NA --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- 2.0

ND --- ND --- ND --- ND --- 1.7

ND --- ND --- ND --- ND --- 2.4

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- 1.9

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- 1.8

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- 2.60E-02 J 3.47E-02 2.1

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- 1.7

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- 2.39E-02 J 4.88E-02 2.3

ND --- ND --- ND --- NA --- N

SD-6 SD-6 SD-6 SD-6 SD

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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE4,4'-DDTDDT and MetabolitesDieldrinEndosulfan-IIgamma-Chlordane

Polychlorinated Biphenyls

Aroclor 1254

Inorganics

AluminumAntimonyArsenicBariumBerylliumCadmiumCalciumChromiumCobaltCopperCyanideIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSilverSodiumThalliumTinVanadiumZinc

Ratio of Ratio of Ratio of Ratio of 

SD-6 May-08 Detected SD-6 Oct-08 Detected SD-6 May-09 Detected SD-6 Sept-09 Detected 

May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to S

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (m

SD-6 SD-6 SD-6 SD-6 SD

ND --- 2.39E-02 2.99E+00 ND --- 9.00E-03 1.13E+00 1.15

ND --- 3.13E-02 6.26E+00 1.57E-02 J 3.14E+00 4.07E-02 8.14E+00 4.42

ND --- ND --- 8.10E-03 1.01E+00 2.04E-02 2.55E+00 1.90

ND --- 5.78E-02 8.26E+00 2.45E-02 3.50E+00 7.01E-02 1.00E+01 7.47

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- NA --- NA --- N

4.23E+02 J 1.66E-02 1.11E+03 J 4.35E-02 1.26E+03 J 4.94E-02 1.18E+03 4.63E-02 4.97

ND --- 3.89E+01 J --- ND --- ND --- N

ND --- 2.37E+01 J 3.95E+00 ND --- ND --- N

1.13E+01 J --- 1.26E+02 J --- 3.58E+01 J --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- 2.20E-01 J 3.67E-01 ND --- N

2.00E+03 J --- 3.52E+03 J --- 6.39E+03 J --- 2.50E+03 --- 1.00

ND --- 7.10E+00 J 2.73E-01 4.90E+00 J 1.88E-01 3.40E+00 1.31E-01 1.70

ND --- ND --- 4.40E-01 J 8.80E-03 ND --- N

ND --- ND --- 1.94E+01 J 1.21E+00 8.30E+00 5.19E-01 3.70

ND --- NA --- NA --- NA --- N

1.54E+04 J --- 3.50E+05 J --- 3.04E+04 J --- 2.11E+03 --- 1.04

1.24E+01 J 4.00E-01 2.35E+01 J 7.58E-01 3.58E+01 J 1.15E+00 2.32E+01 7.48E-01 1.149.84E+01 J --- 1.17E+02 J --- 3.34E+02 J --- ND --- N

1.05E+01 J 1.67E-02 1.67E+02 J 2.65E-01 3.05E+01 J 4.84E-02 1.44E+01 2.29E-02 9.20

1.20E-01 J 6.00E-01 1.70E-01 J 8.50E-01 ND --- ND --- N

ND --- ND --- ND --- 4.90E+00 J 3.06E-01 1.40

NA --- NA --- 1.19E+02 J --- ND --- N

ND --- ND --- 1.60E+00 J --- ND --- N

ND --- ND --- ND --- 5.70E-01 J 1.14E+00 3.4

ND --- 2.00E+02 J --- 1.07E+02 J --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- ND --- ND --- ND --- N

ND --- 6.50E+00 J --- ND --- ND --- N

4.02E+01 J 3.35E-01 1.59E+02 J 1.33E+00 5.36E+01 J 4.47E-01 2.75E+01 2.29E-01 1.23

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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

2-ButanoneAcetoneBenzeneCarbon disulfideChlorobenzeneChloroformEthylbenzeneMethylene chlorideStyreneTetrachloroetheneTolueneXylenes (total)

Semivolatiles

1,4-DichlorobenzeneBis(2-ethylhexyl)phthalateDibenzofuranDi-n-butyl phthalatePolycyclic Aromatic Hydrocarbons2-MethylnaphthaleneAcenaphtheneAcenaphthyleneAnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneCarbazoleChryseneDibenzo(a,h)anthraceneFluorantheneFluoreneIndeno(1,2,3-cd)pyreneNaphthalenePhenanthrenePyrenePAHs, total

Ratio of Ratio of Ratio of 

SD-7 May-08 Detected SD-7 Oct-08 Detected SD-7 May-09 Detected SD-7 S

May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Con

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Scre

ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- NA --- NA --- NA ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- 7.61E-02 J --- ND 

4.20E-02 J 3.77E-02 ND --- 1.62E-01 1.45E-01 ND 

NA --- ND --- 2.78E-01 1.38E+01 ND ND --- 2.27E-02 J 3.38E+00 ND --- ND 

4.30E-02 J 7.33E+00 3.64E-02 J 6.20E+00 5.39E-02 9.18E+00 ND 

ND --- 1.30E-01 5.91E-01 6.76E-02 3.07E-01 ND 

7.60E-02 J 2.38E-01 9.42E-01 2.94E+00 1.65E-01 5.16E-01 ND 8.90E-02 J 2.41E-01 1.13E+00 3.05E+00 1.88E-01 5.08E-01 ND 9.60E-02 J 9.23E-03 1.10E+00 1.06E-01 1.87E-01 1.80E-02 ND 8.50E-02 J 3.54E-01 8.98E-01 3.74E+00 1.10E-01 4.58E-01 ND 4.30E-02 J 2.53E-01 9.23E-01 5.43E+00 1.50E-01 8.82E-01 ND 

ND --- 5.33E-02 J --- 2.76E-02 J --- ND 

1.30E-01 J 3.82E-01 1.02E+00 3.00E+00 2.32E-01 6.82E-01 ND 

ND --- 2.92E-01 4.87E+00 5.92E-02 9.87E-01 ND 

1.60E-01 J 2.13E-01 1.46E+00 1.95E+00 2.91E-01 3.88E-01 1.82E-02 J 

ND --- 2.72E-02 J 1.43E-01 ND --- ND 

4.20E-02 J 2.10E-01 7.73E-01 3.87E+00 1.23E-01 6.15E-01 ND 

ND --- ND --- 1.68E-01 9.55E-01 ND 

1.00E-01 J 1.79E-01 5.04E-01 9.00E-01 2.92E-01 5.21E-01 ND 1.20E-01 J 2.45E-01 1.31E+00 2.67E+00 2.70E-01 5.51E-01 ND 

3.18E+00 7.95E-01 8.96E+00 2.24E+00 2.59E+00 6.47E-01 NA 

SD-7 SD-7 SD-7 SD-7

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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE4,4'-DDTDDT and MetabolitesDieldrinEndosulfan-IIgamma-Chlordane

Polychlorinated Biphenyls

Aroclor 1254

Inorganics

AluminumAntimonyArsenicBariumBerylliumCadmiumCalciumChromiumCobaltCopperCyanideIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSilverSodiumThalliumTinVanadiumZinc

Ratio of Ratio of Ratio of 

SD-7 May-08 Detected SD-7 Oct-08 Detected SD-7 May-09 Detected SD-7 S

May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Con

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Scre

SD-7 SD-7 SD-7 SD-7

ND --- 9.70E-03 1.21E+00 3.69E-02 J 4.61E+00 ND 

8.90E-02 1.78E+01 8.59E-02 1.72E+01 7.70E-01 1.54E+02 ND 

7.70E-02 9.63E+00 9.64E-02 1.21E+01 7.56E-01 9.45E+01 ND 2.05E-01 2.93E+01 1.92E-01 2.74E+01 1.56E+00 2.23E+02 ND 

ND --- 8.70E-03 J 4.35E+00 ND --- ND 

ND --- ND --- 4.10E-03 J --- ND 

ND --- 2.30E-03 J 3.29E-01 ND --- ND 

ND --- 1.12E+00 J 1.87E+01 NA --- NA 

2.25E+03 N 8.82E-02 5.18E+03 2.03E-01 4.80E+03 1.88E-01 7.89E+02 

ND --- 8.60E+00 J --- 3.70E+00 --- ND 

ND --- 4.70E+00 7.83E-01 5.80E+00 9.67E-01 ND 

1.47E+01 J --- 1.60E+02 --- 4.44E+01 --- ND 

ND --- ND --- 2.20E-01 J --- ND 

ND --- 1.50E+00 2.50E+00 4.20E-01 J 7.00E-01 ND 

2.55E+02 J --- 3.03E+03 --- 3.14E+03 --- ND 

7.00E+00 J 2.69E-01 2.35E+01 9.04E-01 1.69E+01 6.50E-01 1.70E+00 

7.00E-01 J 1.40E-02 ND --- 1.90E+00 J 3.80E-02 ND 

8.00E+00 J 5.00E-01 8.11E+01 5.07E+00 1.90E+01 J 1.19E+00 1.57E+01 

1.30E-01 J 1.30E+00 NA --- NA --- NA 

4.94E+03 N --- 1.39E+04 --- 1.47E+04 --- 1.40E+03 7.71E+01 J 2.49E+00 9.00E+02 J 2.90E+01 1.09E+02 3.52E+00 4.55E+01 

9.27E+01 J --- 1.03E+03 --- 6.66E+02 J --- ND 

2.60E+01 J 4.13E-02 1.64E+02 J 2.60E-01 9.86E+01 J 1.57E-01 2.50E+00 

1.10E-01 5.50E-01 1.00E-01 5.00E-01 1.50E+00 7.50E+00 ND 

ND --- 1.22E+01 7.63E-01 7.80E+00 4.88E-01 6.50E-01 J 

NA --- NA --- 4.82E+02 J --- ND 

ND --- ND --- 6.80E-01 J --- ND 

1.10E-01 J 2.20E-01 5.80E-01 J 1.16E+00 ND --- 2.30E-01 J 

ND --- 1.22E+02 J --- 3.56E+01 J --- ND 

ND --- ND --- ND --- ND 

6.80E+00 J --- 1.41E+01 --- 2.92E+01 --- ND 

8.90E+00 J --- 1.86E+01 --- 1.79E+01 J --- ND 

3.58E+01 J 2.98E-01 6.95E+02 5.79E+00 1.19E+02 J 9.92E-01 4.20E+00 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

2-ButanoneAcetoneBenzeneCarbon disulfideChlorobenzeneChloroformEthylbenzeneMethylene chlorideStyreneTetrachloroetheneTolueneXylenes (total)

Semivolatiles

1,4-DichlorobenzeneBis(2-ethylhexyl)phthalateDibenzofuranDi-n-butyl phthalatePolycyclic Aromatic Hydrocarbons2-MethylnaphthaleneAcenaphtheneAcenaphthyleneAnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneCarbazoleChryseneDibenzo(a,h)anthraceneFluorantheneFluoreneIndeno(1,2,3-cd)pyreneNaphthalenePhenanthrenePyrenePAHs, total

Ratio of Ratio of Ratio of 

SD-8 May-08 Detected SD-8 Oct-08 Detected SD-8 May-09 Detected SD-8 S

May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Con

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Scre

1.60E-01 J --- 4.26E-02 J --- NA --- NA 5.60E-01 J --- 7.49E-01 --- 3.34E-01 J --- ND 

ND --- ND --- ND --- ND 

9.40E-03 J --- ND --- ND --- 3.50E-04 J 

ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- NA 

1.50E-02 J 4.72E-02 ND --- ND --- ND 

ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND NA --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- ND ND --- ND --- ND --- 1.72E-02 J ND --- ND --- ND --- NA 

SD-8 SD-8 SD-8 SD-8

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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE4,4'-DDTDDT and MetabolitesDieldrinEndosulfan-IIgamma-Chlordane

Polychlorinated Biphenyls

Aroclor 1254

Inorganics

AluminumAntimonyArsenicBariumBerylliumCadmiumCalciumChromiumCobaltCopperCyanideIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSilverSodiumThalliumTinVanadiumZinc

Ratio of Ratio of Ratio of 

SD-8 May-08 Detected SD-8 Oct-08 Detected SD-8 May-09 Detected SD-8 S

May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Con

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Scre

SD-8 SD-8 SD-8 SD-8

ND --- 2.89E-01 3.61E+01 9.80E-03 J 1.23E+00 ND ND --- 1.57E-01 J 3.14E+01 1.96E-02 J 3.92E+00 ND ND --- 2.95E-02 J 3.69E+00 2.03E-02 J 2.54E+00 ND ND --- 4.76E-01 6.79E+01 4.97E-02 7.10E+00 ND ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- NA --- NA 

4.17E+03 J 1.64E-01 6.10E+03 J 2.39E-01 3.17E+03 J 1.24E-01 9.62E+02 

ND --- ND --- ND --- ND 

ND --- 9.80E+00 J 1.63E+00 ND --- ND 

1.06E+02 J --- 1.38E+02 J --- 2.61E+02 J --- ND 

ND --- ND --- ND --- ND 

ND --- ND --- ND --- ND 

3.06E+03 J --- 2.95E+03 J --- 6.99E+03 J --- ND 

9.40E+00 J 3.62E-01 1.56E+01 J 6.00E-01 9.60E+00 J 3.69E-01 3.20E+00 

ND --- 1.24E+01 J 2.48E-01 4.30E+00 J 8.60E-02 ND 

1.03E+01 J 6.44E-01 1.80E+01 J 1.13E+00 2.43E+01 J 1.52E+00 ND 

ND --- ND --- ND --- ND 

1.36E+04 J --- 1.05E+05 J --- 8.06E+04 J --- 4.67E+03 

2.71E+01 J 8.74E-01 3.46E+01 J 1.12E+00 3.09E+01 J 9.97E-01 ND 

2.31E+03 J --- 1.79E+03 J --- 4.04E+03 J --- ND 

8.64E+01 J 1.37E-01 2.05E+02 J 3.25E-01 5.18E+02 J 8.22E-01 1.33E+01 

1.90E-01 J 9.50E-01 2.00E-01 J 1.00E+00 ND --- ND 

ND --- 1.70E+01 J 1.06E+00 ND --- 1.30E+00 J 

NA --- NA --- 5.78E+02 J --- ND 

ND --- 3.70E+00 J --- 4.10E+00 J --- ND 

1.50E-01 J 3.00E-01 ND --- ND --- 4.00E-01 J 

3.43E+02 J --- 2.97E+02 J --- 4.23E+02 J --- ND 

ND --- ND --- 1.70E+00 J --- ND 

ND --- ND --- ND --- ND 

1.40E+01 J --- ND --- ND --- ND 

6.45E+01 J 5.38E-01 1.14E+02 J 9.50E-01 5.24E+01 J 4.37E-01 6.40E+00 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

2-ButanoneAcetoneBenzeneCarbon disulfideChlorobenzeneChloroformEthylbenzeneMethylene chlorideStyreneTetrachloroetheneTolueneXylenes (total)

Semivolatiles

1,4-DichlorobenzeneBis(2-ethylhexyl)phthalateDibenzofuranDi-n-butyl phthalatePolycyclic Aromatic Hydrocarbons2-MethylnaphthaleneAcenaphtheneAcenaphthyleneAnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneCarbazoleChryseneDibenzo(a,h)anthraceneFluorantheneFluoreneIndeno(1,2,3-cd)pyreneNaphthalenePhenanthrenePyrenePAHs, total

Ratio of Ratio of Ratio of Ratio of 

SD-9 May-08 Detected SD-9 Oct-08 Detected SD-9 May-09 Detected SD-9 Sept-09 Detected 

May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to 

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria 

ND --- ND --- NA --- NA --- 

1.20E-01 J --- 1.03E-01 --- 4.63E+00 J --- 7.50E-03 J --- 

ND --- ND --- ND --- ND --- 

ND --- 4.60E-03 J --- ND --- ND --- 

ND --- ND --- ND --- ND --- 

ND --- ND --- 1.00E-02 J 8.26E-02 ND --- 

ND --- ND --- ND --- ND --- 

ND --- ND --- ND --- ND --- 

ND --- ND --- ND --- ND --- 

ND --- ND --- ND --- ND --- 

ND --- ND --- ND --- ND --- 

ND --- ND --- ND --- NA --- 

ND --- NA --- NA --- NA --- 

ND --- NA --- NA --- NA --- 

ND --- NA --- NA --- NA --- 

ND --- NA --- NA --- NA --- 

NA --- NA --- NA --- NA --- 

ND --- NA --- NA --- NA --- 

ND --- NA --- NA --- NA --- 1

ND --- NA --- NA --- NA --- 

ND --- NA --- NA --- NA --- 4

ND --- NA --- NA --- NA --- 3

ND --- NA --- NA --- NA --- 6

ND --- NA --- NA --- NA --- 3

ND --- NA --- NA --- NA --- 3

ND --- NA --- NA --- NA --- 

ND --- NA --- NA --- NA --- 7

ND --- NA --- NA --- NA --- 

1.90E-01 J 2.53E-01 NA --- NA --- NA --- 8

ND --- NA --- NA --- NA --- 

ND --- NA --- NA --- NA --- 3

ND --- NA --- NA --- NA --- 

ND --- NA --- NA --- NA --- 2

ND --- NA --- NA --- NA --- 8

2.54E+01 6.35E+00 NA --- NA --- NA --- 

SD-9 SD-9 SD-9 SD-9 

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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE4,4'-DDTDDT and MetabolitesDieldrinEndosulfan-IIgamma-Chlordane

Polychlorinated Biphenyls

Aroclor 1254

Inorganics

AluminumAntimonyArsenicBariumBerylliumCadmiumCalciumChromiumCobaltCopperCyanideIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSilverSodiumThalliumTinVanadiumZinc

Ratio of Ratio of Ratio of Ratio of 

SD-9 May-08 Detected SD-9 Oct-08 Detected SD-9 May-09 Detected SD-9 Sept-09 Detected 

May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to 

(mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria (mg/kg) Screening Criteria 

SD-9 SD-9 SD-9 SD-9 

1.30E-01 J 1.63E+01 8.70E-03 1.09E+00 2.13E-02 J 2.66E+00 ND --- 

1.50E-01 3.00E+01 6.43E-02 1.29E+01 1.88E-01 3.76E+01 ND --- 

ND --- 1.51E-02 1.89E+00 5.31E-01 6.64E+01 ND --- 

3.72E-01 5.31E+01 8.81E-02 1.26E+01 7.40E-01 1.06E+02 ND --- 

ND --- ND --- ND --- ND --- 

ND --- ND --- ND --- ND --- 

ND --- ND --- ND --- ND --- 

ND --- ND --- NA --- NA --- 

6.35E+03 J 2.49E-01 8.72E+03 J 3.42E-01 2.10E+03 J 8.24E-02 4.75E+01 1.86E-03 1

ND --- 3.10E+00 J --- 1.80E+00 J --- ND --- 

ND --- 9.40E+00 J 1.57E+00 ND --- ND --- 

2.27E+01 J --- 1.03E+02 J --- 1.41E+01 J --- ND --- 

ND --- ND --- 9.80E-02 J --- ND --- 

ND --- 1.10E+00 J 1.83E+00 2.60E-01 J 4.33E-01 ND --- 

5.74E+02 J --- 1.47E+04 J --- 2.55E+02 J --- ND --- 2

5.70E+00 J 2.19E-01 2.36E+01 J 9.08E-01 9.00E+00 J 3.46E-01 3.40E-01 J 1.31E-02 2

ND --- ND --- 9.80E-01 J 1.96E-02 ND --- 

3.23E+01 J 2.02E+00 3.26E+01 J 2.04E+00 1.79E+01 J 1.12E+00 ND --- 3

ND --- NA --- NA --- NA --- 

1.52E+03 J --- 1.44E+04 J --- 6.38E+03 J --- 2.43E+02 --- 6

4.34E+02 J 1.40E+01 1.60E+02 J 5.16E+00 1.01E+02 J 3.26E+00 7.80E-01 J 2.52E-02 9.05E+01 J --- ND --- 1.81E+02 J --- 6.90E+00 J --- 1

1.62E+01 J 2.57E-02 2.66E+02 J 4.22E-01 2.13E+01 J 3.38E-02 ND --- 1

3.20E-01 J 1.60E+00 5.20E-01 J 2.60E+00 1.70E-01 J 8.50E-01 3.70E-01 1.85E+00 

ND --- 1.26E+01 J 7.88E-01 ND --- ND --- 2

NA --- NA --- 3.98E+02 J --- ND --- 

ND --- ND --- 1.30E+00 J --- ND --- 

1.50E-01 J 3.00E-01 5.00E-01 J 1.00E+00 ND --- ND --- 4

ND --- 9.89E+01 J --- 1.22E+02 J --- ND --- 

ND --- ND --- ND --- ND --- 

ND --- ND --- ND --- ND --- 

2.52E+01 J --- 2.52E+01 J --- 1.90E+01 J --- ND --- 2

5.09E+01 J 4.24E-01 3.34E+02 J 2.78E+00 6.14E+01 J 5.12E-01 9.00E-01 J 7.50E-03 1

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Note: Shading indicates the maximum detection exceeds the benchmark.

LEL = Lowest effect level.mg/kg = Milligrams per kilogram.NA = Not analyzed.ND = Not detected.NBA = No benchmark available.

a NJDEP (New Jersey Department of Environmental Protection). Ecological Screening Criteria (ESC): 2009.b Chlordane value used as a surrogate.

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Fresh water (FW2) Ra

Frequency Criteriaa SW-1 Sept

of Chronic Sep-09 Concen

Chemical Detection (μg/L) (μg/L) Screenin

Volatiles

1,1-Dichloroethane 1/15 4.4E-01 - 4.4E-01 NBA NA 

Acetone 2/9 5.8E+00 - 5.8E+00 NBA NA Carbon Disulfide 2/15 1.3E+00 - 1.7E+00 NBA NA Chloromethane 1/15 1.0E-01 - 1.0E-01 NBA NA cis-1,2-Dichloroethene 1/15 3.1E-01 - 3.1E-01 NBA NA trans-1,2-Dichloroethene 1/15 3.1E-01 - 3.1E-01 9.70E+02 NA 1,2-Dichloroethene (total) 1/9 6.2E-01 - 6.2E-01 NBA NA Toluene 1/15 1.0E+00 - 1.0E+00 2.53E+02 NA 

Semivolatiles

3-Methylphenol & 4-Methylphenol 1/13 1.1E+00 - 1.1E+00 NBA NA Bis(2-ethylhexyl)phthalate 2/13 1.2E+00 - 1.4E+00 3.00E-01 NA Butyl Benzyl Phthalate 1/13 1.7E+00 - 1.7E+00 2.30E+01 NA Phenol 1/13 5.2E+00 - 5.2E+00 1.80E+02 NA 

Polycyclic Aromatic Hydrocarbons

Anthracene 1/13 1.8E-01 - 1.8E-01 3.50E-02 NA Benzo(a)anthracene 1/13 5.8E-01 - 5.8E-01 2.50E-02 NA Benzo(a)pyrene 1/13 4.4E-01 - 4.4E-01 1.40E-02 NA Benzo(b)fluoranthene 1/13 7.7E-01 - 7.7E-01 9.07E+00 NA Benzo(k)fluoranthene 2/13 2.3E-01 - 3.9E-01 NBA NA Benzo(g,h,i)perylene 1/13 2.8E-01 - 2.8E-01 7.64E+00 NA Chrysene 1/13 5.9E-01 - 5.9E-01 NBA NA Fluoranthene 2/13 3.0E-01 - 9.9E-01 1.90E+00 NA Fluorene 1/13 2.0E-01 - 2.0E-01 1.90E+01 NA Indeno(1,2,3-cd)pyrene 1/13 3.1E-01 - 3.1E-01 4.31E+00 NA Phenanthrene 3/13 2.7E-01 - 5.1E-01 3.60E+00 NA Pyrene 2/13 1.9E-01 - 9.3E-01 3.00E-01 NA 

(μg/L)

SW-1

Concentrations 

Range of Detected

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Fresh water (FW2) Ra

Frequency Criteriaa SW-1 Sept

of Chronic Sep-09 Concen

Chemical Detection (μg/L) (μg/L) (μg/L) Screenin

SW-1

Concentrations 

Range of Detected

Pesticides

4,4'-DDD 2/10 2.1E-02 - 4.7E-02 NBA NA 4,4'-DDE 1/10 2.2E-02 - 2.2E-02 4.51E-09 NA 

Inorganics

Aluminum 18/27 2.4E+01 - 1.7E+04 NBA 4.26E+02 Antimony 1/27 2.3E+02 - 2.3E+02 8.00E+01 ND Arsenic 3/27 4.0E+00 - 3.6E+02 1.50E+02 ND Barium 18/27 3.4E+01 - 1.8E+03 2.20E+02 5.79E+01 J 2.63Beryllium 1/27 5.3E+00 - 5.3E+00 3.60E+00 ND Calcium 27/27 7.2E+03 - 8.7E+04 NBA 1.09E+04 Chromium 11/27 7.0E-01 - 1.1E+02 3.48E+01 b 9.00E-01 J 2.58

Cobalt 7/27 6.0E-01 - 5.5E+01 2.40E+01 ND Copper 7/27 3.0E+00 - 1.9E+02 4.07E+00 b ND 

Iron 27/27 1.8E+02 - 4.0E+06 NBA 8.60E+02 

Lead 8/27 2.2E+00 - 2.4E+02 9.10E-01 b ND 

Magnesium 24/27 2.4E+03 - 2.5E+04 NBA 3.05E+03 J Manganese 27/27 2.2E+01 - 2.7E+03 NBA 3.85E+01 Mercury 6/19 5.6E-02 - 4.8E-01 7.70E-01 2.30E-01 2.99Nickel 11/27 1.1E+00 - 4.4E+01 2.38E+01 b ND Potassium 19/27 1.3E+03 - 1.0E+04 NBA 1.39E+03 J Selenium 1/27 1.6E+02 - 1.6E+02 5.00E+00 ND Sodium 25/27 6.3E+03 - 3.7E+04 NBA 1.25E+04 

Thallium 3/27 1.6E+00 - 1.9E+00 1.00E+01 ND Tin 1/27 3.3E+01 - 3.3E+01 1.80E+02 ND Vanadium 1/27 1.9E+02 - 1.9E+02 1.20E+01 ND 

Zinc 19/27 3.2E+00 - 8.4E+02 5.41E+01 b 1.95E+01 J 3.60

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-2 May-08 Detected Criteriaa S

Chronic May-08 Concentration to Chronic Oct-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA ND --- NBA NA 

NBA ND --- NBA NA NBA ND --- NBA NA NBA 1.00E-01 J --- NBA NA NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 ND --- 3.00E-01 NA 

2.30E+01 ND --- 2.30E+01 NA 1.80E+02 ND --- 1.80E+02 NA 

3.50E-02 ND --- 3.50E-02 NA 2.50E-02 ND --- 2.50E-02 NA 1.40E-02 ND --- 1.40E-02 NA 

9.07E+00 ND --- 9.07E+00 NA 

NBA ND --- NBA NA 

7.64E+00 ND --- 7.64E+00 NA 

NBA ND --- NBA NA 

1.90E+00 ND --- 1.90E+00 NA 1.90E+01 ND --- 1.90E+01 NA 4.31E+00 ND --- 4.31E+00 NA 3.60E+00 2.70E-01 B 7.50E-02 3.60E+00 NA 

3.00E-01 ND --- 3.00E-01 NA 

SW-2 SW-2

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-2 May-08 Detected Criteriaa S

Chronic May-08 Concentration to Chronic Oct-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-2 SW-2

NBA ND --- NBA NA 

4.51E-09 ND --- 4.51E-09 NA 

NBA ND --- NBA 4.53E+01 J 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 4.91E+01 J 2.23E-01 2.20E+02 6.45E+01 J 3.60E+00 ND --- 3.60E+00 ND 

NBA 1.35E+04 --- NBA 1.87E+04 

4.22E+01 b ND --- 5.49E+01 b 1.20E+00 J 

2.40E+01 ND --- 2.40E+01 6.00E-01 J 4.98E+00 b ND --- 6.55E+00 b ND 

NBA 1.76E+02 --- NBA 2.43E+02 

1.18E+00 b ND --- 1.69E+00 b ND 

NBA 4.03E+03 --- NBA 5.50E+03 NBA 2.97E+01 --- NBA 4.42E+01 

7.70E-01 ND --- 7.70E-01 5.60E-02 J 

2.91E+01 b ND --- 3.82E+01 b 2.40E+00 J 

NBA ND --- NBA ND 

5.00E+00 ND --- 5.00E+00 ND 

NBA 1.09E+04 N --- NBA 1.49E+04 

1.00E+01 ND --- 1.00E+01 ND 1.80E+02 ND --- 1.80E+02 ND 1.20E+01 ND --- 1.20E+01 ND 6.60E+01 b 1.65E+01 J 2.50E-01 8.66E+01 b ND 

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-2 May-09 Detected Criteriaa S

Chronic May-09 Concentration to Chronic Sep-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA NA --- NBA NA 

NBA NA --- NBA NA NBA NA --- NBA NA NBA NA --- NBA NA NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 NA --- 3.00E-01 NA 

2.30E+01 NA --- 2.30E+01 NA 1.80E+02 NA --- 1.80E+02 NA 

3.50E-02 NA --- 3.50E-02 NA 2.50E-02 NA --- 2.50E-02 NA 1.40E-02 NA --- 1.40E-02 NA 

9.07E+00 NA --- 9.07E+00 NA 

NBA NA --- NBA NA 

7.64E+00 NA --- 7.64E+00 NA 

NBA NA --- NBA NA 

1.90E+00 NA --- 1.90E+00 NA 1.90E+01 NA --- 1.90E+01 NA 4.31E+00 NA --- 4.31E+00 NA 3.60E+00 NA --- 3.60E+00 NA 

3.00E-01 NA --- 3.00E-01 NA 

SW-2 SW-2

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-2 May-09 Detected Criteriaa S

Chronic May-09 Concentration to Chronic Sep-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-2 SW-2

NBA NA --- NBA NA 

4.51E-09 NA --- 4.51E-09 NA 

NBA 5.54E+01 J --- NBA 5.59E+02 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 6.33E+01 J 2.88E-01 2.20E+02 5.66E+01 J 3.60E+00 ND --- 3.60E+00 ND 

NBA 1.38E+04 --- NBA 1.05E+04 

4.44E+01 b ND --- 3.33E+01 b 1.50E+00 J 

2.40E+01 7.00E-01 J 2.92E-02 2.40E+01 ND 5.25E+00 b ND --- 3.89E+00 b 2.20E+01 

NBA 2.51E+02 --- NBA 9.61E+02 

1.27E+00 b ND --- 8.57E-01 b 5.40E+00 

NBA 4.64E+03 J --- NBA 2.78E+03 J NBA 3.53E+01 --- NBA 3.62E+01 

7.70E-01 1.40E-01 J 1.82E-01 7.70E-01 3.00E-01 

3.07E+01 b 1.50E+00 J 4.89E-02 2.28E+01 b ND 

NBA 2.03E+03 J --- NBA 1.29E+03 J 

5.00E+00 ND --- 5.00E+00 ND 

NBA 1.46E+04 --- NBA 9.85E+03 J 

1.00E+01 1.60E+00 J 1.60E-01 1.00E+01 ND 

1.80E+02 ND --- 1.80E+02 ND 

1.20E+01 ND --- 1.20E+01 ND 

6.96E+01 b 1.86E+01 J 2.67E-01 5.17E+01 b 2.48E+02 

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-3 May-08 Detected Criteriaa S

Chronic May-08 Concentration to Chronic Oct-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA ND --- NBA NA 

NBA ND --- NBA NA NBA ND --- NBA NA NBA ND --- NBA NA NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 ND --- 3.00E-01 NA 

2.30E+01 ND --- 2.30E+01 NA 1.80E+02 ND --- 1.80E+02 NA 

3.50E-02 ND --- 3.50E-02 NA 2.50E-02 ND --- 2.50E-02 NA 1.40E-02 ND --- 1.40E-02 NA 

9.07E+00 ND --- 9.07E+00 NA 

NBA 2.30E-01 --- NBA NA 

7.64E+00 ND --- 7.64E+00 NA 

NBA ND --- NBA NA 

1.90E+00 ND --- 1.90E+00 NA 1.90E+01 ND --- 1.90E+01 NA 4.31E+00 ND --- 4.31E+00 NA 3.60E+00 ND --- 3.60E+00 NA 

3.00E-01 ND --- 3.00E-01 NA 

SW-3 SW-3

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-3 May-08 Detected Criteriaa S

Chronic May-08 Concentration to Chronic Oct-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-3 SW-3

NBA ND --- NBA NA 

4.51E-09 ND --- 4.51E-09 NA 

NBA ND --- NBA 3.43E+01 J 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 ND --- 2.20E+02 4.33E+01 J 

3.60E+00 ND --- 3.60E+00 ND 

NBA 1.14E+04 --- NBA 1.32E+04 

3.44E+01 b ND --- 3.83E+01 b ND 

2.40E+01 ND --- 2.40E+01 ND 

4.02E+00 b ND --- 4.50E+00 b ND 

NBA 2.01E+02 --- NBA 1.08E+03 

8.96E-01 b ND --- 1.04E+00 b ND 

NBA 2.61E+03 --- NBA ND NBA 3.59E+01 --- NBA 2.16E+01 

7.70E-01 ND --- 7.70E-01 NA 

2.36E+01 b ND --- 2.63E+01 b ND 

NBA 3.33E+03 J --- NBA ND 

5.00E+00 ND --- 5.00E+00 ND 

NBA 1.73E+04 N --- NBA 2.21E+04 

1.00E+01 ND --- 1.00E+01 ND 

1.80E+02 ND --- 1.80E+02 ND 

1.20E+01 ND --- 1.20E+01 ND 

5.34E+01 b ND --- 5.97E+01 b ND 

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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) SW-3 

Criteriaa SW-3 May-09 Detected Criteriaa Rel

Chronic May-09 Concentration to Chronic Sep-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA NA --- NBA NA 

NBA NA --- NBA NA NBA NA --- NBA NA NBA NA --- NBA NA NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 NA --- 3.00E-01 NA 

2.30E+01 NA --- 2.30E+01 NA 1.80E+02 NA --- 1.80E+02 NA 

3.50E-02 NA --- 3.50E-02 NA 2.50E-02 NA --- 2.50E-02 NA 1.40E-02 NA --- 1.40E-02 NA 

9.07E+00 NA --- 9.07E+00 NA 

NBA NA --- NBA NA 

7.64E+00 NA --- 7.64E+00 NA 

NBA NA --- NBA NA 

1.90E+00 NA --- 1.90E+00 NA 1.90E+01 NA --- 1.90E+01 NA 4.31E+00 NA --- 4.31E+00 NA 3.60E+00 NA --- 3.60E+00 NA 

3.00E-01 NA --- 3.00E-01 NA 

SW-3 Relocation

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) SW-3 

Criteriaa SW-3 May-09 Detected Criteriaa Rel

Chronic May-09 Concentration to Chronic Sep-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-3 Relocation

NBA NA --- NBA NA 

4.51E-09 NA --- 4.51E-09 NA 

NBA 3.52E+02 --- NBA ND 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 4.98E+01 J 2.26E-01 2.20E+02 ND 3.60E+00 ND --- 3.60E+00 ND 

NBA 1.34E+04 --- NBA 1.45E+04 

3.91E+01 b 1.10E+00 J 2.81E-02 4.01E+01 b ND 

2.40E+01 1.20E+00 J 5.00E-02 2.40E+01 ND 4.60E+00 b ND --- 4.72E+00 b ND 

NBA 5.95E+03 --- NBA 1.29E+03 

1.07E+00 b ND --- 1.10E+00 b ND 

NBA 3.00E+03 J --- NBA ND NBA 7.08E+01 --- NBA 2.91E+01 

7.70E-01 NA --- 7.70E-01 NA 

2.69E+01 b 2.10E+00 J 7.82E-02 2.76E+01 b ND 

NBA 5.81E+03 J --- NBA 6.42E+03 J 

5.00E+00 ND --- 5.00E+00 ND 

NBA 1.93E+04 --- NBA 2.05E+04 

1.00E+01 ND --- 1.00E+01 ND 

1.80E+02 ND --- 1.80E+02 ND 

1.20E+01 ND --- 1.20E+01 ND 

6.10E+01 b 1.31E+01 J 2.15E-01 6.26E+01 b 4.60E+00 J 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) SW-3 Ratio of SW-3 DUP Fresh water (FW2) 

Criteriaa Relocation Sept-09 Detected Criteriaa 

Chronic Sep-09 Concentration to Chronic May-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA NA --- NBA ND 

NBA NA --- NBA ND 

NBA NA --- NBA ND 

NBA NA --- NBA ND 

NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 NA --- 3.00E-01 ND 

2.30E+01 NA --- 2.30E+01 1.70E+00 1.80E+02 NA --- 1.80E+02 ND 

3.50E-02 NA --- 3.50E-02 1.80E-01 2.50E-02 NA --- 2.50E-02 ND 1.40E-02 NA --- 1.40E-02 ND 

9.07E+00 NA --- 9.07E+00 ND 

NBA NA --- NBA ND 

7.64E+00 NA --- 7.64E+00 ND 

NBA NA --- NBA ND 

1.90E+00 NA --- 1.90E+00 3.00E-01 

1.90E+01 NA --- 1.90E+01 2.00E-01 4.31E+00 NA --- 4.31E+00 ND 3.60E+00 NA --- 3.60E+00 4.50E-01 

3.00E-01 NA --- 3.00E-01 1.90E-01 

Relocation DUP SW-4

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) SW-3 Ratio of SW-3 DUP Fresh water (FW2) 

Criteriaa Relocation Sept-09 Detected Criteriaa 

Chronic Sep-09 Concentration to Chronic May-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

Relocation DUP SW-4

NBA NA --- NBA ND 

4.51E-09 NA --- 4.51E-09 ND 

NBA ND --- NBA ND 

8.00E+01 ND --- 8.00E+01 ND 1.50E+02 ND --- 1.50E+02 ND 2.20E+02 ND --- 2.20E+02 4.10E+01 3.60E+00 ND --- 3.60E+00 ND 

NBA 1.43E+04 --- NBA 1.36E+04 

3.97E+01 b ND --- 3.79E+01 b ND 

2.40E+01 ND --- 2.40E+01 ND 4.67E+00 b ND --- 4.45E+00 b ND 

NBA 1.26E+03 --- NBA 7.91E+02 

1.09E+00 b ND --- 1.02E+00 b ND 

NBA ND --- NBA 2.46E+03 

NBA 2.83E+01 --- NBA 6.25E+01 

7.70E-01 NA --- 7.70E-01 7.40E-02 

2.73E+01 b ND --- 2.60E+01 b ND 

NBA 6.45E+03 J --- NBA 7.18E+03 

5.00E+00 ND --- 5.00E+00 ND 

NBA 2.04E+04 --- NBA 2.05E+04 

1.00E+01 ND --- 1.00E+01 ND 1.80E+02 ND --- 1.80E+02 ND 1.20E+01 ND --- 1.20E+01 ND 6.20E+01 b 6.10E+00 J 9.84E-02 5.90E+01 b ND 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-4 Oct-08 Detected Criteriaa SW

Chronic Oct-08 Concentration to Chronic Oct-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA NA --- NBA NA 

NBA NA --- NBA NA NBA NA --- NBA NA NBA NA --- NBA NA NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA ND --- NBA ND 

3.00E-01 ND --- 3.00E-01 ND 

2.30E+01 ND --- 2.30E+01 ND 1.80E+02 ND --- 1.80E+02 ND 

3.50E-02 ND --- 3.50E-02 ND 2.50E-02 ND --- 2.50E-02 ND 1.40E-02 ND --- 1.40E-02 ND 

9.07E+00 ND --- 9.07E+00 ND 

NBA ND --- NBA ND 

7.64E+00 ND --- 7.64E+00 ND 

NBA ND --- NBA ND 

1.90E+00 ND --- 1.90E+00 ND 1.90E+01 ND --- 1.90E+01 ND 4.31E+00 ND --- 4.31E+00 ND 3.60E+00 ND --- 3.60E+00 ND 

3.00E-01 ND --- 3.00E-01 ND 

SW-4 SW-4-DUP

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-4 Oct-08 Detected Criteriaa SW

Chronic Oct-08 Concentration to Chronic Oct-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-4 SW-4-DUP

NBA NA --- NBA NA 

4.51E-09 NA --- 4.51E-09 NA 

NBA 2.43E+01 J --- NBA 3.06E+01 J 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 ND --- 2.20E+02 4.58E+01 J 

3.60E+00 ND --- 3.60E+00 ND 

NBA 1.44E+04 --- NBA 1.43E+04 

3.99E+01 b ND --- 3.97E+01 b ND 

2.40E+01 ND --- 2.40E+01 ND 

4.70E+00 b ND --- 4.67E+00 b ND 

NBA 2.03E+03 --- NBA 1.84E+03 

1.10E+00 b ND --- 1.09E+00 b ND 

NBA ND --- NBA 2.66E+03 J 

NBA 5.64E+01 --- NBA 5.81E+01 

7.70E-01 ND --- 7.70E-01 ND 

2.75E+01 b ND --- 2.73E+01 b ND 

NBA ND --- NBA ND 

5.00E+00 ND --- 5.00E+00 ND 

NBA 2.35E+04 --- NBA 2.35E+04 

1.00E+01 ND --- 1.00E+01 ND 

1.80E+02 ND --- 1.80E+02 ND 

1.20E+01 ND --- 1.20E+01 ND 

6.23E+01 b ND --- 6.19E+01 b ND 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-4 May-09 Detected Criteriaa SW-

Chronic May-09 Concentration to Chronic May-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA NA --- NBA NA 

NBA NA --- NBA NA NBA NA --- NBA NA NBA NA --- NBA NA NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA ND --- NBA ND 

3.00E-01 ND --- 3.00E-01 1.20E+00 J 

2.30E+01 ND --- 2.30E+01 ND 1.80E+02 ND --- 1.80E+02 ND 

3.50E-02 ND --- 3.50E-02 ND 2.50E-02 ND --- 2.50E-02 ND 1.40E-02 ND --- 1.40E-02 ND 

9.07E+00 ND --- 9.07E+00 ND 

NBA ND --- NBA ND 

7.64E+00 ND --- 7.64E+00 ND 

NBA ND --- NBA ND 

1.90E+00 ND --- 1.90E+00 ND 1.90E+01 ND --- 1.90E+01 ND 4.31E+00 ND --- 4.31E+00 ND 3.60E+00 ND --- 3.60E+00 ND 

3.00E-01 ND --- 3.00E-01 ND 

SW-4 SW-4-DUP

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-4 May-09 Detected Criteriaa SW-

Chronic May-09 Concentration to Chronic May-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-4 SW-4-DUP

NBA NA --- NBA NA 

4.51E-09 NA --- 4.51E-09 NA 

NBA 9.81E+02 --- NBA 4.91E+02 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 3.47E+01 J 1.58E-01 2.20E+02 3.43E+01 J 3.60E+00 ND --- 3.60E+00 ND 

NBA 1.64E+04 --- NBA 1.60E+04 

4.54E+01 b 2.40E+00 J 5.29E-02 4.42E+01 b 1.30E+00 J 

2.40E+01 3.40E+00 J 1.42E-01 2.40E+01 2.60E+00 J 5.37E+00 b 3.00E+00 J 5.59E-01 5.22E+00 b 2.47E+01 

NBA 2.98E+04 --- NBA 2.84E+04 

1.30E+00 b 5.30E+00 4.06E+00 1.26E+00 b 2.20E+00 J 

NBA 3.40E+03 J --- NBA 3.22E+03 J NBA 1.67E+02 --- NBA 1.73E+02 

7.70E-01 ND --- 7.70E-01 ND 

3.13E+01 b 2.20E+00 J 7.02E-02 3.05E+01 b 1.90E+00 J 

NBA 4.13E+03 J --- NBA 4.50E+03 J 

5.00E+00 ND --- 5.00E+00 ND 

NBA ND --- NBA ND 

1.00E+01 1.90E+00 J 1.90E-01 1.00E+01 ND 1.80E+02 ND --- 1.80E+02 ND 

1.20E+01 ND --- 1.20E+01 ND 

7.11E+01 b 2.27E+01 3.19E-01 6.92E+01 b 3.63E+01 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-4 Sept-09 Detected Criteriaa S

Chronic Sep-09 Concentration to Chronic May-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA NA --- NBA ND 

NBA NA --- NBA ND NBA NA --- NBA ND NBA NA --- NBA ND NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 ND --- 3.00E-01 ND 

2.30E+01 ND --- 2.30E+01 ND 

1.80E+02 ND --- 1.80E+02 ND 

3.50E-02 ND --- 3.50E-02 ND 2.50E-02 ND --- 2.50E-02 ND 1.40E-02 ND --- 1.40E-02 ND 

9.07E+00 ND --- 9.07E+00 ND 

NBA ND --- NBA ND 

7.64E+00 ND --- 7.64E+00 ND 

NBA ND --- NBA ND 

1.90E+00 ND --- 1.90E+00 ND 

1.90E+01 ND --- 1.90E+01 ND 

4.31E+00 ND --- 4.31E+00 ND 

3.60E+00 ND --- 3.60E+00 ND 

3.00E-01 ND --- 3.00E-01 ND 

SW-4 SW-5

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-4 Sept-09 Detected Criteriaa S

Chronic Sep-09 Concentration to Chronic May-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-4 SW-5

NBA NA --- NBA ND 

4.51E-09 NA --- 4.51E-09 ND 

NBA 8.25E+02 --- NBA 1.05E+02 J 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 ND --- 2.20E+02 ND 

3.60E+00 ND --- 3.60E+00 ND 

NBA 1.60E+04 --- NBA 1.66E+04 

4.25E+01 b ND --- 4.29E+01 b ND 

2.40E+01 ND --- 2.40E+01 ND 

5.01E+00 b ND --- 5.06E+00 b ND 

NBA 1.12E+04 --- NBA 2.12E+03 J 

1.19E+00 b 5.00E+00 4.19E+00 1.21E+00 b ND 

NBA ND --- NBA 2.39E+03 NBA 1.00E+02 --- NBA 4.87E+01 

7.70E-01 ND --- 7.70E-01 ND 

2.93E+01 b ND --- 2.96E+01 b ND 

NBA 5.88E+03 J --- NBA 4.13E+03 J 

5.00E+00 ND --- 5.00E+00 ND 

NBA 1.66E+04 --- NBA 1.93E+04 N 

1.00E+01 ND --- 1.00E+01 ND 

1.80E+02 ND --- 1.80E+02 ND 

1.20E+01 ND --- 1.20E+01 ND 

6.64E+01 b 1.84E+01 J 2.77E-01 6.71E+01 b 7.00E+00 J 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-5 Oct-08 Detected Criteriaa S

Chronic Oct-08 Concentration to Chronic May-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA ND --- NBA ND 

NBA NA --- NBA 5.80E+00 J 

NBA ND --- NBA ND NBA ND --- NBA ND NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA ND --- NBA 1.10E+00 J 

3.00E-01 ND --- 3.00E-01 1.40E+00 J 

2.30E+01 ND --- 2.30E+01 ND 

1.80E+02 ND --- 1.80E+02 5.20E+00 

3.50E-02 ND --- 3.50E-02 ND 2.50E-02 ND --- 2.50E-02 5.79E-01 1.40E-02 ND --- 1.40E-02 4.35E-01 

9.07E+00 ND --- 9.07E+00 7.69E-01 

NBA ND --- NBA 3.86E-01 

7.64E+00 ND --- 7.64E+00 2.81E-01 

NBA ND --- NBA 5.86E-01 

1.90E+00 ND --- 1.90E+00 9.93E-01 

1.90E+01 ND --- 1.90E+01 ND 

4.31E+00 ND --- 4.31E+00 3.07E-01 

3.60E+00 ND --- 3.60E+00 5.10E-01 

3.00E-01 ND --- 3.00E-01 9.30E-01 

SW-5 SW-5

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-5 Oct-08 Detected Criteriaa S

Chronic Oct-08 Concentration to Chronic May-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-5 SW-5

NBA NA --- NBA NA 

4.51E-09 NA --- 4.51E-09 NA 

NBA 6.68E+01 J --- NBA 1.83E+02 J 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 4.82E+01 J 2.19E-01 2.20E+02 5.55E+01 J 3.60E+00 ND --- 3.60E+00 ND 

NBA 4.03E+04 --- NBA 2.90E+04 

8.33E+01 b 7.00E-01 J 8.41E-03 6.55E+01 b 1.10E+00 J 

2.40E+01 ND --- 2.40E+01 8.00E-01 J 1.01E+01 b ND --- 7.87E+00 b ND 

NBA 9.39E+03 --- NBA 2.64E+04 

2.94E+00 b ND --- 2.13E+00 b ND 

NBA 3.56E+03 J --- NBA 3.30E+03 J 

NBA 2.32E+02 --- NBA 2.05E+02 

7.70E-01 NA --- 7.70E-01 NA 

5.87E+01 b ND --- 4.58E+01 b 1.60E+00 J 

NBA ND --- NBA 5.68E+03 J 

5.00E+00 ND --- 5.00E+00 ND 

NBA 1.87E+04 --- NBA 2.00E+04 

1.00E+01 ND --- 1.00E+01 ND 1.80E+02 ND --- 1.80E+02 ND 1.20E+01 ND --- 1.20E+01 ND 1.33E+02 b ND --- 1.04E+02 b 9.50E+00 J 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-5 Sept-09 Detected Criteriaa S

Chronic Sep-09 Concentration to Chronic May-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA ND --- NBA ND 

NBA NA --- NBA ND NBA ND --- NBA ND NBA ND --- NBA ND NBA ND --- NBA NA 

9.70E+02 ND --- 9.70E+02 NA 

NBA ND --- NBA NA 

2.53E+02 ND --- 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 ND --- 3.00E-01 ND 

2.30E+01 ND --- 2.30E+01 ND 

1.80E+02 ND --- 1.80E+02 ND 

3.50E-02 ND --- 3.50E-02 ND 2.50E-02 ND --- 2.50E-02 ND 1.40E-02 ND --- 1.40E-02 ND 

9.07E+00 ND --- 9.07E+00 ND 

NBA ND --- NBA ND 

7.64E+00 ND --- 7.64E+00 ND 

NBA ND --- NBA ND 

1.90E+00 ND --- 1.90E+00 ND 

1.90E+01 ND --- 1.90E+01 ND 

4.31E+00 ND --- 4.31E+00 ND 

3.60E+00 ND --- 3.60E+00 ND 

3.00E-01 ND --- 3.00E-01 ND 

SW-5 SW-6

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-5 Sept-09 Detected Criteriaa S

Chronic Sep-09 Concentration to Chronic May-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-5 SW-6

NBA NA --- NBA ND 

4.51E-09 NA --- 4.51E-09 ND 

NBA 2.17E+02 --- NBA ND 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 ND --- 2.20E+02 ND 

3.60E+00 ND --- 3.60E+00 ND 

NBA 2.63E+04 --- NBA 2.41E+04 

5.98E+01 b ND --- 5.80E+01 b ND 

2.40E+01 ND --- 2.40E+01 ND 

7.16E+00 b ND --- 6.94E+00 b ND 

NBA 1.23E+04 --- NBA 4.83E+03 

1.89E+00 b 6.10E+00 3.23E+00 1.81E+00 b ND 

NBA 2.75E+03 J --- NBA 3.39E+03 

NBA 1.45E+02 --- NBA 9.27E+01 

7.70E-01 NA --- 7.70E-01 ND 

4.17E+01 b ND --- 4.04E+01 b ND 

NBA 5.58E+03 J --- NBA ND 

5.00E+00 ND --- 5.00E+00 ND 

NBA 1.85E+04 --- NBA 2.00E+04 N 

1.00E+01 ND --- 1.00E+01 ND 

1.80E+02 ND --- 1.80E+02 ND 

1.20E+01 ND --- 1.20E+01 ND 

9.47E+01 b 1.28E+01 J 1.35E-01 9.17E+01 b ND 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-6 Oct-08 Detected Criteriaa S

Chronic Oct-08 Concentration to Chronic May-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA ND --- NBA ND 

NBA NA --- NBA 5.80E+00 J 

NBA 1.70E+00 J --- NBA 1.30E+00 J 

NBA ND --- NBA ND NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 NA --- 3.00E-01 NA 

2.30E+01 NA --- 2.30E+01 NA 

1.80E+02 NA --- 1.80E+02 NA 

3.50E-02 NA --- 3.50E-02 NA 2.50E-02 NA --- 2.50E-02 NA 1.40E-02 NA --- 1.40E-02 NA 

9.07E+00 NA --- 9.07E+00 NA 

NBA NA --- NBA NA 

7.64E+00 NA --- 7.64E+00 NA 

NBA NA --- NBA NA 

1.90E+00 NA --- 1.90E+00 NA 

1.90E+01 NA --- 1.90E+01 NA 

4.31E+00 NA --- 4.31E+00 NA 

3.60E+00 NA --- 3.60E+00 NA 

3.00E-01 NA --- 3.00E-01 NA 

SW-6 SW-6

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-6 Oct-08 Detected Criteriaa S

Chronic Oct-08 Concentration to Chronic May-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-6 SW-6

NBA NA --- NBA NA 

4.51E-09 NA --- 4.51E-09 NA 

NBA 1.68E+04 --- NBA 1.59E+02 J 

8.00E+01 2.32E+02 2.90E+00 8.00E+01 ND 1.50E+02 3.63E+02 2.42E+00 1.50E+02 4.00E+00 2.20E+02 1.75E+03 7.95E+00 2.20E+02 1.41E+02 J 3.60E+00 5.30E+00 1.47E+00 3.60E+00 ND 

NBA 8.66E+04 --- NBA 2.52E+04 

1.48E+02 b 1.08E+02 7.30E-01 5.85E+01 b 1.20E+00 J 

2.40E+01 5.52E+01 J 2.30E+00 2.40E+01 ND 1.84E+01 b 1.88E+02 1.02E+01 7.00E+00 b 3.94E+01 

NBA 3.97E+06 --- NBA 1.74E+05 

6.23E+00 b 2.40E+02 3.85E+01 1.84E+00 b ND 

NBA 4.01E+03 J --- NBA 2.92E+03 J 

NBA 2.69E+03 --- NBA 1.34E+02 

7.70E-01 NA --- 7.70E-01 NA 

1.06E+02 b 4.42E+01 J 4.16E-01 4.07E+01 b 2.70E+00 J 

NBA ND --- NBA 3.66E+03 J 

5.00E+00 1.63E+02 3.26E+01 5.00E+00 ND 

NBA ND --- NBA 1.98E+04 

1.00E+01 ND --- 1.00E+01 ND 1.80E+02 3.26E+01 J 1.81E-01 1.80E+02 ND 1.20E+01 1.88E+02 1.57E+01 1.20E+01 ND 2.42E+02 b 8.44E+02 3.49E+00 9.25E+01 b 2.83E+01 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-6 Sept-09 Detected Criteriaa S

Chronic Sep-09 Concentration to Chronic Sep-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA ND --- NBA NA 

NBA NA --- NBA NA NBA ND --- NBA NA NBA ND --- NBA NA NBA ND --- NBA NA 

9.70E+02 ND --- 9.70E+02 NA 

NBA ND --- NBA NA 

2.53E+02 1.00E+00 3.95E-03 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 NA --- 3.00E-01 ND 

2.30E+01 NA --- 2.30E+01 ND 1.80E+02 NA --- 1.80E+02 ND 

3.50E-02 NA --- 3.50E-02 ND 2.50E-02 NA --- 2.50E-02 ND 1.40E-02 NA --- 1.40E-02 ND 

9.07E+00 NA --- 9.07E+00 ND 

NBA NA --- NBA ND 

7.64E+00 NA --- 7.64E+00 ND 

NBA NA --- NBA ND 

1.90E+00 NA --- 1.90E+00 ND 1.90E+01 NA --- 1.90E+01 ND 4.31E+00 NA --- 4.31E+00 ND 3.60E+00 NA --- 3.60E+00 ND 

3.00E-01 NA --- 3.00E-01 ND 

SW-6 SW-7

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-6 Sept-09 Detected Criteriaa S

Chronic Sep-09 Concentration to Chronic Sep-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-6 SW-7

NBA NA --- NBA ND 

4.51E-09 NA --- 4.51E-09 ND 

NBA 1.18E+03 --- NBA ND 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 ND --- 2.20E+02 ND 

3.60E+00 ND --- 3.60E+00 ND 

NBA 4.76E+04 --- NBA 2.94E+04 

9.66E+01 b ND --- 6.40E+01 b ND 

2.40E+01 ND --- 2.40E+01 ND 

1.18E+01 b 2.98E+01 2.52E+00 7.68E+00 b ND 

NBA 1.13E+04 --- NBA 1.87E+03 

3.57E+00 b 3.20E+01 8.95E+00 2.07E+00 b 2.20E+00 J 

NBA 4.71E+03 J --- NBA 2.47E+03 J NBA 1.58E+02 --- NBA 4.74E+01 

7.70E-01 NA --- 7.70E-01 ND 

6.84E+01 b ND --- 4.47E+01 b 1.10E+00 J 

NBA 5.68E+03 J --- NBA 8.68E+03 J 

5.00E+00 ND --- 5.00E+00 ND 

NBA 1.98E+04 --- NBA 2.35E+04 

1.00E+01 ND --- 1.00E+01 ND 1.80E+02 ND --- 1.80E+02 ND 1.20E+01 ND --- 1.20E+01 ND 1.55E+02 b 1.14E+02 7.33E-01 1.01E+02 b 1.99E+01 J 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-8 May-08 Detected Criteriaa S

Chronic May-08 Concentration to Chronic Oct-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA ND --- NBA ND 

NBA ND --- NBA NA NBA ND --- NBA ND NBA ND --- NBA ND NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 NA --- 3.00E-01 NA 

2.30E+01 NA --- 2.30E+01 NA 

1.80E+02 NA --- 1.80E+02 NA 

3.50E-02 NA --- 3.50E-02 NA 2.50E-02 NA --- 2.50E-02 NA 1.40E-02 NA --- 1.40E-02 NA 

9.07E+00 NA --- 9.07E+00 NA 

NBA NA --- NBA NA 

7.64E+00 NA --- 7.64E+00 NA 

NBA NA --- NBA NA 

1.90E+00 NA --- 1.90E+00 NA 

1.90E+01 NA --- 1.90E+01 NA 

4.31E+00 NA --- 4.31E+00 NA 

3.60E+00 NA --- 3.60E+00 NA 

3.00E-01 NA --- 3.00E-01 NA 

SW-8 SW-8

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-8 May-08 Detected Criteriaa S

Chronic May-08 Concentration to Chronic Oct-08 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-8 SW-8

NBA ND --- NBA 2.10E-02 J 

4.51E-09 ND --- 4.51E-09 ND 

NBA ND --- NBA 7.38E+01 J 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 7.82E+01 3.55E-01 2.20E+02 6.48E+01 J 3.60E+00 ND --- 3.60E+00 ND 

NBA 7.16E+03 --- NBA 1.14E+04 

6.64E+01 b ND --- 9.32E+01 b 1.50E+00 J 

2.40E+01 ND --- 2.40E+01 ND 7.99E+00 b ND --- 1.14E+01 b 9.80E+00 J 

NBA 7.05E+03 --- NBA 1.66E+04 

2.17E+00 b ND --- 3.41E+00 b ND 

NBA 1.69E+04 --- NBA 2.52E+04 

NBA 2.90E+02 --- NBA 4.78E+02 

7.70E-01 ND --- 7.70E-01 ND 

4.64E+01 b ND --- 6.59E+01 b 5.70E+00 J 

NBA 1.01E+04 N --- NBA ND 

5.00E+00 ND --- 5.00E+00 ND 

NBA 3.00E+04 N --- NBA 3.74E+04 

1.00E+01 ND --- 1.00E+01 ND 1.80E+02 ND --- 1.80E+02 ND 1.20E+01 ND --- 1.20E+01 ND 1.05E+02 b 1.10E+01 J 1.04E-01 1.50E+02 b ND 

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-8 May-09 Detected Criteriaa S

Chronic May-09 Concentration to Chronic Sep-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA 4.40E-01 J --- NBA ND 

NBA ND --- NBA NA NBA ND --- NBA ND NBA ND --- NBA ND NBA NA --- NBA 3.10E-01 J 

9.70E+02 NA --- 9.70E+02 3.10E-01 J 

NBA NA --- NBA 6.20E-01 J 

2.53E+02 NA --- 2.53E+02 ND 

NBA NA --- NBA NA 

3.00E-01 NA --- 3.00E-01 NA 

2.30E+01 NA --- 2.30E+01 NA 

1.80E+02 NA --- 1.80E+02 NA 

3.50E-02 NA --- 3.50E-02 NA 2.50E-02 NA --- 2.50E-02 NA 1.40E-02 NA --- 1.40E-02 NA 

9.07E+00 NA --- 9.07E+00 NA 

NBA NA --- NBA NA 

7.64E+00 NA --- 7.64E+00 NA 

NBA NA --- NBA NA 

1.90E+00 NA --- 1.90E+00 NA 

1.90E+01 NA --- 1.90E+01 NA 

4.31E+00 NA --- 4.31E+00 NA 

3.60E+00 NA --- 3.60E+00 NA 

3.00E-01 NA --- 3.00E-01 NA 

SW-8 SW-8

C:\Users\mbrewin\AppData\Local\Microsoft\Windows\Temporary Internet Files\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued (3) 
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'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO

!LMJ&/HD&#.%&%OIQKHBB&)HJC

!LMJ&/HD5&#C^&2CMFCX

Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-8 May-09 Detected Criteriaa S

Chronic May-09 Concentration to Chronic Sep-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-8 SW-8

NBA 4.70E-02 J --- NBA ND 

4.51E-09 2.20E-02 4.88E+06 4.51E-09 ND 

NBA 1.58E+03 --- NBA ND 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 5.30E+00 3.53E-02 1.50E+02 ND 

2.20E+02 3.26E+02 1.48E+00 2.20E+02 ND 3.60E+00 ND --- 3.60E+00 ND 

NBA 1.12E+04 --- NBA 1.24E+04 

8.11E+01 b 5.60E+00 J 6.91E-02 6.84E+01 b ND 

2.40E+01 2.00E+00 J 8.33E-02 2.40E+01 ND 

9.83E+00 b 4.02E+01 4.09E+00 8.24E+00 b ND 

NBA 1.09E+05 --- NBA 6.99E+03 

2.83E+00 b 1.03E+01 3.63E+00 2.26E+00 b ND 

NBA 2.03E+04 --- NBA 1.45E+04 

NBA 4.65E+02 --- NBA 3.16E+02 

7.70E-01 ND --- 7.70E-01 ND 

5.71E+01 b 6.80E+00 J 1.19E-01 4.79E+01 b 1.70E+00 J 

NBA 7.84E+03 J --- NBA 6.58E+03 J 

5.00E+00 ND --- 5.00E+00 ND 

NBA 2.85E+04 --- NBA 6.32E+03 J 

1.00E+01 1.80E+00 J 1.80E-01 1.00E+01 ND 1.80E+02 ND --- 1.80E+02 ND 1.20E+01 ND --- 1.20E+01 ND 1.30E+02 b 4.81E+01 3.71E-01 1.09E+02 b 3.20E+00 J 

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Chemical

Volatiles

1,1-DichloroethaneAcetoneCarbon DisulfideChloromethanecis-1,2-Dichloroethenetrans-1,2-Dichloroethene1,2-Dichloroethene (total)Toluene

Semivolatiles

3-Methylphenol & 4-MethylphenolBis(2-ethylhexyl)phthalateButyl Benzyl PhthalatePhenol

Polycyclic Aromatic Hydrocarbons

AnthraceneBenzo(a)anthraceneBenzo(a)pyreneBenzo(b)fluorantheneBenzo(k)fluorantheneBenzo(g,h,i)peryleneChryseneFluorantheneFluoreneIndeno(1,2,3-cd)pyrenePhenanthrenePyrene

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-9 Sept-09 Detected Criteriaa SW

Chronic Sep-09 Concentration to Chronic Sep-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

NBA NA --- NBA NA 

NBA NA --- NBA NA NBA NA --- NBA NA NBA NA --- NBA NA NBA NA --- NBA NA 

9.70E+02 NA --- 9.70E+02 NA 

NBA NA --- NBA NA 

2.53E+02 NA --- 2.53E+02 NA 

NBA NA --- NBA NA 

3.00E-01 NA --- 3.00E-01 ND 

2.30E+01 NA --- 2.30E+01 ND 1.80E+02 NA --- 1.80E+02 ND 

3.50E-02 NA --- 3.50E-02 ND 2.50E-02 NA --- 2.50E-02 ND 1.40E-02 NA --- 1.40E-02 ND 

9.07E+00 NA --- 9.07E+00 ND 

NBA NA --- NBA ND 

7.64E+00 NA --- 7.64E+00 ND 

NBA NA --- NBA ND 

1.90E+00 NA --- 1.90E+00 ND 1.90E+01 NA --- 1.90E+01 ND 4.31E+00 NA --- 4.31E+00 ND 3.60E+00 NA --- 3.60E+00 ND 

3.00E-01 NA --- 3.00E-01 ND 

SW-9 SW-10

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Chemical

Pesticides

4,4'-DDD4,4'-DDE

Inorganics

AluminumAntimonyArsenicBariumBerylliumCalciumChromiumCobaltCopperIronLeadMagnesiumManganeseMercuryNickelPotassiumSeleniumSodiumThalliumTinVanadiumZinc

Fresh water (FW2) Ratio of Fresh water (FW2) 

Criteriaa SW-9 Sept-09 Detected Criteriaa SW

Chronic Sep-09 Concentration to Chronic Sep-09 

(μg/L) (μg/L) Screening Criteria (μg/L) (μg/L) 

SW-9 SW-10

NBA NA --- NBA NA 

4.51E-09 NA --- 4.51E-09 NA 

NBA ND --- NBA ND 

8.00E+01 ND --- 8.00E+01 ND 

1.50E+02 ND --- 1.50E+02 ND 

2.20E+02 3.54E+01 J 1.61E-01 2.20E+02 ND 

3.60E+00 ND --- 3.60E+00 ND 

NBA 5.01E+04 --- NBA 1.63E+04 

1.09E+02 b ND --- 4.28E+01 b ND 

2.40E+01 ND --- 2.40E+01 ND 

1.33E+01 b ND --- 5.05E+00 b ND 

NBA 5.68E+02 --- NBA 1.66E+03 

4.17E+00 b ND --- 1.20E+00 b ND 

NBA 8.36E+03 --- NBA ND NBA 4.68E+01 --- NBA 2.90E+01 

7.70E-01 4.80E-01 6.23E-01 7.70E-01 ND 

7.72E+01 b ND --- 2.95E+01 b ND 

NBA 2.38E+03 J --- NBA 7.03E+03 J 

5.00E+00 ND --- 5.00E+00 ND 

NBA 1.33E+04 --- NBA 2.35E+04 

1.00E+01 ND --- 1.00E+01 ND 

1.80E+02 ND --- 1.80E+02 ND 

1.20E+01 ND --- 1.20E+01 ND 

1.75E+02 b 3.50E+00 J 1.99E-02 6.70E+01 b 7.90E+00 J 

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Note: Shading indicates the maximum detection exceeds the benchmark.NBA = No benchmark available.μg/L = Micrograms per liter.

a NJDEP (New Jersey Department of Environmental Protection). Ecological Screening Criteria (ESC): 2009.b Criterion is a function of hardness (μg/L as CaCO3), in the water column. Values are based on a sample-specific hardness.

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