revised human health risk assessment, universal oil

SITE: R37933

D R A F T

Revised Human Health Risk Assessment, Universal Oil Products, Operable Unit 2, East Rutherford, New Jersey

Prepared for

Honeywell International Inc.

July 2016

CH2M HILL Engineers, Inc. 1717 Arch Street Suite 4400 Philadelphia, PA 19103

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Executive Summary This revised human health risk assessment (HHRA) for Operable Unit (OU) 2 incorporates new data collected since the 2011 non–time critical removal action (NTCRA) and updates the findings of the 2012 draft baseline HHRA to reflect current site conditions. Analytical data collected from sediment, surface water, and fish tissue were used to estimate potential exposures and risks to current and future receptors at OU2. The HHRA incorporated samples collected by CH2M from 2006 through 2015 and samples collected by the Berrys Creek Study Area (BCSA) potentially responsible party (PRP) group from 2009 to 2013.

Based on the agreement with the BCSA PRP group reached in early 2016, the HHRA addresses chemical concentrations remaining in the channels associated with the Streamlands west of Murray Hill Parkway. Additionally, the offsite marshlands south of OU2, referred to as Ackermans South, were evaluated in the HHRA per agreement with the BCSA PRP group. The Streamlands east of Murray Hill Parkway were not evaluated in this HHRA and will be addressed in the BCSA HHRA.

The Universal Oil Products site is isolated from the surrounding properties by a fence, an active rail line, and various tidal ditches and wetlands. The area near the active rail line is patrolled by New Jersey Transit. The OU2 Streamlands west of Murray Hill Parkway are highly inaccessible due to their physical nature. The wetland vegetation is very dense and cannot be traversed without the use of brush-cutting tools. Similar conditions are also present at Ackermans South. Therefore, trespassing is expected to be infrequent onsite and at Ackermans South, and exposure frequencies used in this HHRA are considered very conservative.

The following receptors and exposure pathways were evaluated quantitatively in the HHRA:

• Current/future onsite trespassers. Older child (6 to 18 years old) and adult trespassers were evaluated for ingestion and dermal contact exposures to site sediment (0 to 6 inches) and dermal contact exposures to site surface water.

• Current/future fish consumers. Younger children (0 to 6 years old), older children, and adults were assumed to consume white perch caught onsite. Ingestion of crab was not evaluated in the HHRA because edible-size blue crabs were not observed at the site during the long-term monitoring sampling events.

• Current/future offsite trespassers. Older child (6 to 18 years old) and adult trespassers were evaluated for ingestion and dermal contact exposures to sediment (0 to 6 inches) in Ackermans South.

Potential excess lifetime cancer risks (ELCRs) and noncarcinogenic hazard indices (HIs) were estimated for the receptor groups using conservative assumptions for exposure factors and exposure point concentrations (Table ES-1). Additionally, potential blood lead levels (BLLs) were estimated for an onsite trespasser scenario using USEPA’s lead models. The estimated ELCRs and HIs for potential current and future trespassers (adult and older child) exposed to site sediment, site surface water, and offsite sediment in Ackermans South were less than or within the U.S. Environmental Protection Agency’s (USEPA) acceptable levels. That is, the potential ELCRs for trespassers were less than or within USEPA’s target ELCR range of 1 × 10-6 to 1 × 10-4, and the estimated target-organ-specific HIs were less than or equal to the threshold of 1. Additionally, the probability of BLLs exceeding 10 micrograms per deciliter (µg/dL) was less than 5 percent for both adult and older child trespassers potentially exposed to lead in site sediment. Therefore, chemicals of concern (COCs) were not identified for onsite and offsite trespassers.

EXECUTIVE SUMMARY

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Risk estimates for fish (white perch) exceeded USEPA-acceptable levels for fish consumers (adult, older child, and younger child) due to polychlorinated biphenyls (PCBs). Therefore, 2,3,7,8-tetrachlorodibenzodioxin toxic equivalent (2,3,7,8-TCDD TEQ) and total PCBs were identified as COCs for fish. However, fishing is not expected to occur at the site. Few edible-size fish of any species have been observed onsite, and the largest white perch caught onsite during the sampling event was 10.2 centimeters. Access is difficult due to the active rail line, fencing, and patrolling by New Jersey Transit. Additionally, the physical characteristics of the wetland (dense vegetation, soft sediments in the side channels at low tide, and strong tidal currents in the main channel of Ackermans Creek at high tide) make the site an unattractive destination for trespassers (including anglers). Therefore, the fish ingestion risk estimates are for a hypothetical exposure scenario that is not expected to occur at OU2.

Table ES-1. Risk Summary OU2, Universal Oil Products (UOP), East Rutherford, NJ

Receptor Age Group Exposure Media ELCR Target Organs with HI >1 a COCs b

Current/future onsite trespasser

Adult Sediment, surface water

8 × 10-6 None None

Older child Sediment, surface water

9 × 10-6 None None

Current/future fish consumer

Adult White perch 7 × 10-5 Reproductive (3), developmental (3), endocrine system (3), immune system (9), dermal (9), and ocular (9)

2,3,7,8-TCDD TEQ and total PCBs

Older child White perch 1 × 10-4 Reproductive (3), developmental (3), endocrine system (3), immune system (10), dermal (10), and ocular (10)


Younger child

White perch 1 × 10-4 Reproductive (5), developmental (5), endocrine system (5), immune system (16), dermal (16), and ocular (16)


Current/future offsite trespasser

Adult Sediment 5 × 10-7 None None

Older child Sediment 7 × 10-7 None None

a Estimated HI is listed in parenthesis following each target organ. b COCs were identified when the estimated ELCR or HI for a receptor group exceeded USEPA threshold values (ELCR of 1 × 10-4 or a target organ-specific HI of 1).

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Contents Section Page

Executive Summary ............................................................................................................................ iii

Acronyms and Abbreviations .............................................................................................................. vii

1 Introduction ......................................................................................................................... 1-1 1.1 Overview .......................................................................................................................... 1-1 1.2 Potential Receptors.......................................................................................................... 1-2

2 Data Evaluation .................................................................................................................... 2-1 2.1 Analytical Data Used in the HHRA ................................................................................... 2-1 2.2 PCB Analysis ..................................................................................................................... 2-2 2.3 Field Duplicates ................................................................................................................ 2-3 2.4 Selection of Chemicals of Potential Concern ................................................................... 2-3

2.4.1 Chemicals of Potential Concern Screening Levels .............................................. 2-4 2.4.2 COPC Screening Results ...................................................................................... 2-5

3 Exposure Assessment ........................................................................................................... 3-1 3.1 Exposure Pathways Quantified ........................................................................................ 3-1 3.2 Quantification of Exposure .............................................................................................. 3-1

3.2.1 Exposure Point Concentrations .......................................................................... 3-2 3.2.2 Exposure Factors ................................................................................................. 3-2 3.2.3 Exposure Factors for Chemicals with Mutagenic Mode of Action ..................... 3-3

4 Toxicity Assessment.............................................................................................................. 4-1 4.1 Noncarcinogenic Toxicity Values ..................................................................................... 4-1 4.2 Carcinogenic Toxicity Values ............................................................................................ 4-1 4.3 Derivation of Dermal Toxicity Values ............................................................................... 4-2 4.4 Lead .................................................................................................................................. 4-2

5 Risk Characterization ............................................................................................................ 5-1 5.1 Approach for Potential Noncarcinogenic Effects ............................................................. 5-1 5.2 Approach for Potential Carcinogenic Effects ................................................................... 5-1 5.3 Summary of Risk Estimates .............................................................................................. 5-2 5.4 Chemicals of Concern ...................................................................................................... 5-3 5.5 Uncertainty Analysis ........................................................................................................ 5-3

5.5.1 Data Evaluation ................................................................................................... 5-4 5.5.2 Exposure Assessment ......................................................................................... 5-5 5.5.3 Toxicity Assessment ............................................................................................ 5-6 5.5.4 Risk Characterization .......................................................................................... 5-6

6 Summary .............................................................................................................................. 6-1

7 References ............................................................................................................................ 7-1

Attachments

A RAGS Part D Tables B Sample Groups

CONTENTS

vi EN0602161110PHL

C Analytical Dataset (on CD) D Fish Screening Levels E ProUCL Output F Lead Modeling

Figures

1-1 Conceptual Exposure Model 2-1 Sediment and Surface Water Sampling Locations 2-2 Fish Sampling Locations

Tables

ES-1 Risk Summary 1-1 2012 Draft Baseline HHRA Conclusions 5-1 Sediment Analytical Data Collected Using Traps and Turf Mats

EN0602161110PHL vii

Acronyms and Abbreviations 2,3,7,8-TCDD 2,3,7,8-tetrachlorodibenzodioxin

µg/dL microgram per deciliter

µg/L microgram per Liter

ABSGI gastrointestinal absorption factor

ADAF age-dependent adjustment factor

ALM Adult Lead Methodology

AVS acid volatile sulfide

BCSA Berrys Creek Study Area

BLL blood lead level

cPAH carcinogenic polycyclic aromatic hydrocarbon

COC chemical of concern

COPC chemical of potential concern

Cr(VI) hexavalent chromium

CSF cancer slope factor

ED exposure duration

ELCR excess lifetime cancer risk

EPC exposure point concentration

HHEM Human Health Evaluation Manual

HHRA human health risk assessment

HI hazard index

HQ hazard quotient

IEUBK Integrated Exposure Uptake Biokinetic

mg/kg milligram per kilogram

mg/kg-day milligram per kilogram per day

MMOA mutagenic mode of action

NTCRA non–time critical removal action

OU operable unit

PCB polychlorinated biphenyl

PPRTV provisional peer-reviewed toxicity value

PRP potentially responsible party

RAGS Risk Assessment Guidance for Superfund

RSL Regional Screening Level

RfD reference dose

ACRONYMS AND ABBREVIATIONS

viii EN0602161110PHL

RME reasonable maximum exposure

SVOC semivolatile organic compound

TCE trichloroethene

TEQ toxic equivalent

UCL upper confidence limit

UOP Universal Oil Products

USEPA U.S. Environmental Protection Agency

VC vinyl chloride

VOC volatile organic compound

SECTION 1

EN0602161110PHL 1-1

Introduction 1.1 Overview This addendum to the draft baseline human health risk assessment (HHRA) for Operable Unit (OU) 2 incorporates new data collected since the 2011 non–time critical removal action (NTCRA) and updates the findings of the baseline HHRA to reflect current site conditions. Therefore, the primary objective of this HHRA is to evaluate potential onsite exposures and risks, including the NTCRA area, using the recently collected analytical data that represent the current conditions at the site.

A draft baseline HHRA for OU2 was submitted to the U.S. Environmental Protection Agency (USEPA) in January 2012 (CH2M, 2012). Data collected during the field sampling events conducted between July 2006 and August 2010 were used in the HHRA. The 2012 HHRA evaluated potential current and future health risks from exposures to sediment, surface water, and blue crab at OU2, in the area from OU1 to Berrys Creek. During preparation of the draft HHRA, a NTCRA was planned for the northwestern area of the site; therefore, this northwestern area was evaluated separately in the draft HHRA. The potential receptors evaluated in the HHRA and results of the HHRA are presented in Table 1-1.

Table 1-1. 2012 Draft Baseline HHRA Conclusions OU2, Universal Oil Products (UOP), East Rutherford, NJ

Receptors Evaluated Media Evaluated Risk Conclusions Chemicals Driving Risk Where Risk >10-4 or Hazard Index >1

Trespassers Sitewide sediment and surface water Acceptable —

Trespassers NTCRA area sediment and surface water

Sediment unacceptable

PCBs

Kayakers Eastern stream channels sediment and surface water

Acceptable —

Crab consumers Blue crab Unacceptable PCBs, methylmercury

PCBs = polychlorinated biphenyls.

In 2012 and 2013, the NTCRA was performed in the northwestern corner of the site, and additional data were collected to monitor the effectiveness of the removal action. This HHRA also incorporates samples collected onsite by the Berrys Creek Study Area (BCSA) potentially responsible party (PRP) group. Based on the agreement with the BCSA PRP Group reached in early 2016, this HHRA addresses concentrations remaining in the channels associated with the Streamlands (that is, OU2) west of Murray Hill Parkway. The Streamlands east of Murray Hill Parkway are not evaluated in this HHRA and will be addressed in the BCSA HHRA. The offsite Ackermans South area is also evaluated in the HHRA because this area is tidally connected to OU2.

In accordance with USEPA guidance documents, this HHRA consists of a four-step evaluation process comprising the following:

1. Data collection and evaluation, including identification of chemicals of potential concern (COPCs) 2. Exposure assessment 3. Toxicity assessment 4. Risk characterization

SECTION 1 – INTRODUCTION

1-2 EN0602161110PHL

The HHRA incorporates the general methodology described in the following guidance documents: Risk Assessment Guidance for Superfund (RAGS), Volume 1: Human Health Evaluation Manual (HHEM), Parts A, D, E, and F (USEPA, 1989, 2001, 2004, 2009), and HHEM, Update of Standard Default Exposure Factors (USEPA, 2014a). In addition, other USEPA guidance documents were used and are cited in the text and tables.

1.2 Potential Receptors The Universal Oil Products (UOP) site is located in an urban area with light industry and commercial/retail operations on adjacent properties. The site is isolated from the surrounding properties by a fence, an active rail line, and various tidal ditches and wetlands. The area near the active rail line is patrolled by New Jersey Transit. The OU2 Streamlands west of Murray Hill Parkway, which are the focus of this HHRA, are highly inaccessible due to their physical nature. The wetland vegetation is very dense and cannot be traversed without the use of brush-cutting tools. Access into the center of the wetlands is also hindered by deep water and strong tidal currents1 in the main channel of Ackermans Creek at high tide, and deep mud (approximately 2.5 to 3 feet) in the side channels at low tide. The water is only deep enough for swimming for a short time during high tide, and the mud is too deep for wading. Therefore, the site conditions are not conducive to swimming or wading. Edible-size fish are occasionally present in the Streamlands west of Murray Hill Parkway; however, fishing has not been observed and is not expected to occur onsite due to the difficulty in accessing the site. Additionally, the Streamlands west of Murray Hill Parkway cannot be accessed by boat from the eastern side of OU2.

The property south of OU2, referred to as Ackermans South, was also evaluated in the HHRA. Access to Ackermans South is difficult due to the adjacent active rail line and the dense vegetation present within the wetlands. As with the UOP site, brush-cutting tools would be needed to enter and move through the wetland. The stream that runs through the Ackermans South area is dry except at high tide; therefore, it does not provide a permanent habitat for fish. Overall, the Ackermans South area is unlikely to be an attractive destination for potential trespassers.

The following potential receptors were evaluated quantitatively in the HHRA:

• Current/future onsite trespassers. Older child (6 to 18 years old) and adult trespassers may occasionally access the site. A young child (0 to 6 years old) is not a realistic receptor because the site is relatively isolated, and access is very difficult.

• Current/future fish consumers. Younger children (0 to 6 years old), older children, and adults may occasionally consume fish (that is, white perch) caught onsite. Based on field observations, the predominant fish species present onsite is mummichog, while the predominant gamefish species present onsite is white perch. No significant percentage of other gamefish are expected to be present onsite based on the fish species observed in Berrys Creek.

• Current/future offsite trespassers. Older child (6 to 18 years old) and adult trespassers may occasionally access Ackermans South. A young child (0 to 6 years old) is not a realistic receptor because the Ackermans South area is relatively isolated and access is very difficult.

Although potential kayakers and crab consumers were quantitatively evaluated in the 2012 Draft Baseline HHRA, these receptors were not evaluated in this revised HHRA because the exposure pathways are incomplete. The 2012 HHRA evaluated potential exposures to surface water and sediment in the eastern stream channels for a kayaker entering from Berrys Creek. Access to the western stream channels by kayak is not possible because Murray Hill Parkway separates the eastern and western stream channels. Potential exposures to blue crab were also determined to be incomplete in the

1 The maximum velocity is approximately 3 feet per second during peak lunar cycle.

ACRONYMS AND ABBREVIATIONS

EN0602161110PHL 1-3

western stream channels because edible-size blue crab were not observed during the long-term monitoring sampling events. Therefore, kayakers and crab consumers were not included as potential receptors in this revised HHRA.

The human health conceptual exposure model presents potential exposure media, exposure points, receptors (current and future), and exposure routes, and is provided in Table 1 of Attachment A and graphically in Figure 1-1.

Primary Sources

Primary Release Mechanisms

Secondary Sources

Onsite: Chemicals Laboratory and Waste

Disposal

Exposure Media

ExposureRoute

Secondary Release Mechanisms

FIGURE 1-1CONCEPTUAL EXPOSURE MODELREVISED HUMAN HEALTH RISK ASSESSMENTUNIVERSAL OIL PRODUCTS (UOP), OU2EAST RUTHERFORD, NJ

Discharge from Storm Drains;

Surface Runoff; Groundwater

Discharge to Surface Water

Potential Receptor Populations

LegendX – Potentially complete exposure pathways identified.1 – Solids transport between high and low energy areas.2 – The site conditions are not conducive for wading or swimming due to heavy vegetation, shallow water depth, and soft sediments. Trespassing is expected to be a very infrequent activity since active rail lines are present along and across the site, the land is patrolled by NJ Transit, and fencing is present.3 – The off-site trespasser scenario is evaluated for the Ackermans South area. 4 – There is heavy vegetation present at the Ackermans South area and trespassers would likely need brush-cutting tools to enter the property. Additionally, active rail lines are adjacent to Ackermans South and the land is patrolled by NJ Transit. Therefore, trespassing is expected to be infrequent at Ackermans South.

Current/Future

Transport (1)

Surface Water and Sediment Dermal Contact

On-site Trespasser

(Adult and Older Child)

X (2)Wetlands Surface Water

Off-site Trespasser

(Adult and Older Child)

(3)

Eastern Stream Channel Sediment (2)

Ingestion/Dermal Contact

Ingestion/Dermal Contact X (2)Wetlands Sediment

(On-site)

X (4)

Bioaccumulation

Offsite: Adjacent Properties and Sources

Downstream and Upstream of Berrys

Creek

Discharge from Storm Drains;

Surface Runoff; Solid Exchange with Berry’s Creek

Partition

Sediment

Ingestion X (2)Fish (White Perch)

FishConsumer

(Adult, Older Child, Younger

Child)

Wetlands Sediment(Ackermans South)

SECTION 2

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Data Evaluation 2.1 Analytical Data Used in the HHRA The sediment, surface water, and fish tissue samples used in the HHRA were collected from 2006 through 2015 by CH2M during the remedial investigation sampling (2006 to 2010), the monitored natural recovery treatability study (2012 to 2015), and long-term monitoring events (2013 and 2015). Additionally, samples collected at the site from 2009 to 2013 by the BCSA PRP Group were included in the HHRA. Details regarding the sampling approaches and field investigation activities are provided in the following reports:

• CH2M. 2011. Remedial Investigation Report, Universal Oil Products, Operable Unit 2, East Rutherford, New Jersey. April.

• CH2M. 2014a. Long-Term Monitoring Plan for Non-Time-Critical Removal Action, Universal Oil Products, Operable Unit 2, East Rutherford, New Jersey, USEPA ID: NJD002005106. May.

• CH2M. 2014b. Non-Critical Time Removal Action – Long-Term Monitoring - Year 1 Biennial Report. May.

• CH2M. 2014c. Monitored Natural Recovery Treatability Study Work Plan Universal Oil Products Operable Unit 2 East Rutherford, New Jersey USEPA ID: NJD002005106. May

• BCSA Group. 2009. Work Plan for Remedial Investigation /Feasibility Study: Berry’s Creek Study Area. Submitted to U.S. Environmental Protection Agency, Submitted by Berry’s Creek Study Area Cooperating PRP Group. C357 - BC787.

• Geosyntec Consultants, Inc., and Integral Consulting Inc. (Geosyntec/Integral). 2009a. Phase 1 Work Plan and QAPP for Remedial Investigation/Feasibility Study. Berry’s Creek Study Area. Prepared for the Berry’s Creek Cooperating PRP Group.

• Geosyntec/Integral. 2009b. Quality Assurance Project Plan. Berry’s Creek Study Area. Prepared for the Berry’s Creek Cooperating PRP Group.

• Geosyntec/Integral. 2010. Phase 2 Work Plan Addendum. Quality Assurance Project Plan/Field Sampling Plan. Prepared for the Berry’s Creek Cooperating PRP Group.

• Geosyntec/Integral. 2011. Baseline Monitoring Work Plan, Berry’s Creek Study Area. Prepared for the Berry’s Creek Cooperating PRP Group.

• Geosyntec/Integral. 2012. Phase 3a Addendum. Quality Assurance Project Plan/Field Sampling Plan. Prepared for the Berry’s Creek Cooperating PRP Group.

• Geosyntec/Integral. 2013. Phase 3b Addendum. Quality Assurance Project Plan/Field Sampling Plan. Prepared for the Berry’s Creek Cooperating PRP Group.

• Geosyntec/Integral. 2014. Phase 3b 2014 Addendum. Quality Assurance Project Plan/Field Sampling Plan. Prepared for the Berry’s Creek Cooperating PRP Group.

• Geosyntec/Integral, 2015. Phase 3b 2015 Addendum. Quality Assurance Project Plan/Field Sampling Plan. Prepared for the Berry’s Creek Cooperating PRP Group.

Sediment data collected from sampling locations within the NTCRA area (prior to the 2012 excavation) and within the area that was remediated when the New Jersey Sports and Exposition Authority rail line was constructed, between 2006 and 2008, were not included in the HHRA because those data represent

SECTION 2 – DATA EVALUATION

2-2 EN0602161110PHL

sediments no longer onsite. Samples collected from each medium were evaluated in the HHRA as follows:

• Sediment. Sediment samples collected west of Murray Hill Parkway at depths between 0 and 6 inches were used to evaluate a potential current and future trespasser scenario in the HHRA. A total of 42 sediment samples, collected from 2006 to 2015, were used in the HHRA. Sediment samples were analyzed for one or more of the following: volatile organic compounds (VOCs), semivolatile organic compounds (SVOCs), PCBs (congeners and Aroclors), pesticides, and inorganics. The sediment sampling locations are depicted on Figure 2-1.

• Surface water. Surface water samples collected west of Murray Hill Parkway were used to evaluate a potential current and future trespasser scenario. Samples collected from high tide and low tide were included in the HHRA. A total of 32 surface water samples, collected from 2009 to 2014, were used in the HHRA. Surface water samples were analyzed for one or more of the following: VOCs, SVOCs, PCBs (Aroclors), pesticides, and inorganics. The surface water sampling locations are depicted on Figure 2-1.

• Fish. Composite tissue samples were collected from white perch caught in the NTCRA area (post-excavation) and in Ackermans Creek west of Murray Hill Parkway. The white perch samples were used to evaluate a hypothetical current and future fish consumer scenario in the HHRA. The fish tissue samples were collected in 2013 and 2015. Tissue samples from smaller fish such as mummichog were not included in the HHRA because they are typically too small for human consumption. The white perch samples were analyzed for PCB congeners, and the analytical data are presented on a wet weight basis. A total of 10 fish samples were included in the HHRA; the largest fish caught onsite was 10.2 centimeters. The white perch sampling locations are shown on Figure 2-2. As discussed in Section 5.5.4 of the Remedial Investigation Report, the fish tissue concentrations are unlikely to be solely attributable to OU2.

• Sediment (Ackermans South). Sediment samples collected from the Ackermans South area at depths from 0 to 6 inches were used to evaluate a potential current and future offsite trespasser scenario in the HHRA. Sediment samples collected from the Ackermans South area were analyzed for one or more of the following: VOCs, SVOCs, PCBs (congeners and Aroclors), pesticides, and inorganics. A total of nine samples were collected in 2006 and 2012. The sediment sampling locations collected from the Ackermans South area and included in the HHRA are shown on Figure 2-1.

Samples used in the HHRA and their associated data groupings are summarized in Table B-1 and Table B-2 of Attachment B. The analytical dataset for the samples used in the HHRA is included in Attachment C.

Although blue crab data were collected historically at the UOP site, they do not represent current site conditions because the samples west of Murray Hill Parkway were collected in the NTCRA area prior to implementing remedial actions. Blue crabs were not observed onsite during the long-term monitoring sampling events. Additionally, crabs are very mobile, moving within the tide onsite and offsite and migrating to deep water during cold weather. Therefore, measured crab concentrations would not be solely attributable to the site, but would reflect other sites and background levels. Crabbing is expected to be infrequent at OU2 due to the difficulty in accessing the site and lack of edible-size crabs.

2.2 PCB Analysis Congener-specific PCB data were available for sediment and fish, and Aroclor data were available for sediment and surface water. Congener-specific, dioxin-like PCB data were converted into 2,3,7,8-tetrachlorodibenzodioxin (2,3,7,8-TCDD) toxic equivalents (TEQs) using the toxicity equivalent factors listed in the USEPA’s Regional Screening Levels (RSLs) for Chemical Contaminants at Superfund Sites


EN0602161110PHL 2-3

(USEPA, 2016a) and as recommended by USEPA (2010). The 2,3,7,8-TCDD TEQs for each dioxin-like PCB congener were summed on a sample-by-sample basis. Non-dioxin-like, congener-specific PCB data were summed on a sample-by-sample basis and evaluated as total PCBs. Additionally, Aroclor data were summed on a sample-by-sample basis and evaluated as total Aroclors.2

The congener-specific PCB data, as well as Aroclor data, were used to evaluate potential risks from PCBs. Both congener-specific PCB data and Aroclor data were not available for all sediment samples. Therefore, the potential exposures and risks for PCBs in sediment were quantified using both congener-specific and Aroclor data. The uncertainties associated with the PCB data are discussed in the uncertainty analysis (Section 5.5).

2.3 Field Duplicates For samples with field duplicate analyses, the field duplicate result was excluded from the HHRA. The purpose of collecting and analyzing field duplicates in site characterization is to evaluate the precision of the sampling process; differences between the parent sample and the field duplicate reflect the heterogeneity of the chemical distribution within the environmental matrix and variation in the laboratory precision and accuracy. Unless specifically stated as a data quality objective in project planning, field duplicates are generally not collected for the purpose of increasing the accuracy or precision of site characterization samples. Therefore, it is not necessary to include the results of the field duplicates in the HHRA.

Common practices for handling duplicates in exposure estimation include (1) selecting the greater of the field duplicate or parent sample value, (2) using the arithmetic average of the field duplicate with the parent sample, or (3) selecting only the parent samples and excluding the duplicate results. In the HHRA, field duplicates cannot be included as separate, independent samples because doing so would bias the results by effectively doubling the statistical weight of the locations where field duplicates were collected. Selecting the greater of the two values results in an overall bias towards greater concentrations, and adds substantial complexity to the data set because the relative magnitude of parent and duplicate results varies among analytes. Taking the average of the duplicate and parent samples might yield a result that is closer to the true chemical concentration at the sample location (although it may only reflect the average of the parent and duplicate sample locations), but without a full understanding of the sources of variation between the duplicate and parent samples, it is not clear that the accuracy of the results is improved by taking the average of the two. In addition, using the average of the results adds complexity to the resulting data set because a new sample is created and the original samples need to be excluded; the added complexity increases the potential for error and complicates third-party replication of the results. For these reasons, the parent samples were retained and the field duplicates excluded in the HHRA.

2.4 Selection of Chemicals of Potential Concern The COPCs are those chemicals that have the greatest potential to cause adverse human health effects if receptors come in contact with site media. The maximum detected concentration of each analyte in each medium was compared to its screening level to select the COPCs for the medium. If the maximum detected concentration exceeded its screening level, the constituent was selected as a COPC. Chemicals considered essential nutrients (calcium, magnesium, potassium, and sodium) were not selected as COPCs since they are toxic only at high doses and high concentrations of essential nutrients were not detected onsite.

2 Nondetected Aroclors in a sample were not included in the “total Aroclor” calculation.


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2.4.1 Chemicals of Potential Concern Screening Levels The maximum detected concentrations in sediment, surface water, and fish were compared to the USEPA’s RSLs for soil, tap water, and fish to identify chemical of potential concern (COPCs) (USEPA, 2016a). The RSLs based on noncarcinogenic health endpoints, with the exception of lead, were reduced by a factor of 10 (that is, adjusted to a hazard quotient [HQ] = 0.1) to account for the potential presence of multiple chemicals affecting the same target organ. No adjustment was made for the RSLs based on carcinogenic health endpoints (that is, the RSLs are based on a target excess lifetime cancer risk [ELCR] of 1 x 10-6). For those chemicals with more than one RSL (for example, carcinogenic-based RSL, non-carcinogenic-based RSL [HQ = 0.1], and soil-saturation-based RSL [sediment only]), the lowest value was selected as the final RSL for that chemical. A detected chemical that has no RSL was compared with an RSL for a surrogate chemical based on structural or functional similarities, if such information and values were available. Chemicals that were 100 percent nondetected in an exposure medium were not selected as COPCs for that medium/data grouping.

USEPA considers lead to be a special case because of the difficulty in identifying the classic “threshold” needed to develop a reference dose (RfD). The screening levels used in the COPC screening for lead were obtained from the USEPA’s RSL table (USEPA, 2016a). The residential soil RSL for lead is 400 milligrams per kilogram (mg/kg) and is based on the Integrated Exposure Uptake Biokinetic (IEUBK) Model (USEPA, 1994) for blood lead levels (BLLs) in children. The tap water RSL for lead is the USEPA’s Action Level of 15 micrograms per liter (µg/L).

The detected concentrations in sediment were compared to the residential soil RSLs and the detected concentrations in surface water were compared to the tap water RSLs. These RSLs are very conservative comparison levels for site sediment and surface water exposure scenarios since the RSLs are based on daily exposure by child and adult residents, which is not a realistic exposure scenario for the site. Concentrations detected in fish samples were compared to RSLs for fish (calculated using the RSL calculator for fish and site-specific exposure assumptions). The input parameters and RSL calculator output for the fish screening levels are provided in Attachment D.

2.4.1.1 Chromium Screening Levels The surface water and sediment samples that were collected west of Murray Hill Parkway and the sediment samples collected from the Ackermans South area were analyzed for total chromium but not for hexavalent chromium [Cr(VI)]. However, Cr(VI) was analyzed in surface and subsurface sediment samples from six locations (five stream channel and one marsh location) in 2007. It was detected in seven of 20 samples at concentrations ranging from 1.5 to 45.1 mg/kg, with six of the results below 8 mg/kg. These detections are inconsistent with the results of other analyses performed for the baseline ecological risk assessment (that is, acid volatile sulfide (AVS) in sediment and Cr(VI) in pore water). Cr(VI) is thermodynamically unstable in anoxic sediments. AVS is formed only in anoxic sediments; therefore, sediments with measurable AVS concentrations should not contain Cr(VI) (USEPA, 2005a; Berry et al., 2004). Additionally, If Cr(VI) is present in sediment and biologically available, it will be detected in pore water (USEPA, 2005a; Berry et al., 2004). AVS was detected in five of seven stream channel samples collected for the baseline ecological risk assessment, and Cr(VI) was not detected in any of the pore water samples collected from the same locations. Based on these results, Cr(VI) is not expected to be stable in stream channel sediments, and reduction to the more-stable, less-toxic trivalent chromium is favored. The maximum Cr(VI) concentration, 45.1 mg/kg, was detected in a surface sample from the marsh location, where organic material is abundant and conditions are likely to be even more anoxic than in the stream channels, suggesting this detection is an analytical outlier.

Laboratory methods for analyzing Cr(VI) in sediment are subject to false positives due to analytical artifacts, including potential interferences from humic substances (Pettine and Capri, 2005). Therefore, the Cr(VI) detections in the UOP samples may be an artifact of the laboratory analysis.


EN0602161110PHL 2-5

Based on the rationale provided above, the RSL for trivalent chromium was used to screen the detected concentrations of total chromium in the HHRA.

2.4.2 COPC Screening Results Results of the COPC screening process for each environmental medium and receptor group are presented in Tables 2.1 through 2.4 of Attachment A and are summarized below:

• Sediment (onsite). Sixteen inorganics (aluminum, antimony, arsenic, barium, cadmium, chromium, cobalt, copper, iron, lead, manganese, mercury, nickel, thallium, vanadium, and zinc), three pesticides (Aldrin, BHC [beta], and heptachlor epoxide), six SVOCs (benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, bis(2-ethylhexyl)phthalate, dibenz(a,h)anthracene, and indeno(1,2,3-cd)pyrene), 2,3,7,8-TCDD TEQ, total Aroclors, and total PCBs were identified as COPCs in sediment (Table 2.1 of Attachment A).

• Surface water. Ten inorganics (aluminum, antimony, arsenic, cobalt, cyanide, iron, lead, manganese, mercury, and silver), four pesticides (Aldrin, chlordane [beta], heptachlor, and heptachlor epoxide), six SVOCs (benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, and indeno(1,2,3-cd)pyrene), three VOCs (benzene, trichloroethene [TCE], and vinyl chloride [VC]), and total Aroclors were identified as COPCs in surface water (Table 2.2 of Attachment A).

• Fish. Total PCBs and 2,3,7,8-TCDD TEQ were identified as COPCs for white perch (Table 2.3 of Attachment A).

• Sediment (Ackermans South). Ten inorganics (aluminum, antimony, arsenic, barium, cobalt, iron, manganese, mercury, nickel, and vanadium), five SVOCs (benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, dibenz(a,h)anthracene, and indeno(1,2,3-cd)pyrene), 2,3,7,8-TCDD TEQ, total Aroclors, and total PCBs were identified as COPCs in sediment in the Ackermans South area (Table 2.4 of Attachment A).

The COPCs identified in each medium were carried forward in the HHRA and were included in the exposure and risk estimates.

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FIGURE 2-1SEDIMENT AND SURFACE WATER SAMPLING LOCATIONSREVISED HUMAN HEALTH RISK ASSESSMENTUNIVERSAL OIL PRODUCTS (UOP),EAST RUTHERFORD, NJ

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BCSAOU2 STREAMLANDS AREA WEST OF MURRAY HILL PARKWAY ACKERMANS AREA SOUTH OU1 UPLANDS

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FIGURE 2-2FISH SAMPLING LOCATIONSREVISED HUMAN HEALTH RISK ASSESSMENTUNIVERSAL OIL PRODUCTS (UOP),EAST RUTHERFORD, NJ

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SECTION 3

EN0602161110PHL 3-1

Exposure Assessment The exposure assessment consists of three main steps:

1. Evaluation of exposure pathways and identification of receptors 2. Estimation of exposure point concentrations (EPCs) 3. Estimation of chemical intake and exposure concentrations

Each step is discussed below.

3.1 Exposure Pathways Quantified An exposure pathway can be described as the physical course that a COPC takes from the point of release (or source) to a receptor. To be complete, an exposure pathway must have all of the following components:

• A source (such as constituent residues in an environmental medium) • A mechanism for chemical release and migration (such as surface runoff) • An environmental transport medium (such as surface water) • A point of potential human contact (exposure point, such as sediment) • A route of intake (such as ingestion or dermal contact)

In the absence of any one of these components, an exposure pathway is considered incomplete, and, by definition, there is no risk or hazard. In some cases, a receptor may contact a source directly, eliminating the release and transport pathways.

The potential exposure pathways for the site were identified in Table 1 in Attachment A and graphically on Figure 1-1. The potential exposure pathways that were quantified for each receptor group are presented below.

• Onsite trespassers:

– Sediment: ingestion and dermal contact exposures to COPCs; EPCs are presented in Table 3.1.RME of Attachment A.

– Surface water: dermal contact exposures to COPCs; EPCs are presented in Table 3.2.RME of Attachment A.

• Fish consumers:

– White perch: ingestion exposures to COPCs; EPCs for fish are presented in Table 3.3.RME of Attachment A.

• Offsite trespassers:

– Sediment (Ackermans South area): ingestion and dermal contact exposures to COPCs; EPCs are presented in Table 3.4.RME of Attachment A.

3.2 Quantification of Exposure To evaluate the potentially complete exposure pathways further, the magnitude, frequency, and duration of exposures were estimated and quantified. EPCs were identified and pathway-specific intakes were estimated. USEPA (1989) guidance recommends selecting intake variable values for a given pathway so that the combination of all intake variable values results in an estimate of the reasonable maximum exposure (RME) for that pathway. USEPA recommends using upper-bound parameter values

SECTION 3 – EXPOSURE ASSESSMENT

3-2 EN0602161110PHL

(as opposed to average values) for exposure frequency and exposure duration. USEPA guidance also recommends that the contact rate be a value representing the 95th percentile.

3.2.1 Exposure Point Concentrations The EPCs were estimated based on measured COPC concentrations in sediment, surface water, and fish. The upper confidence limit (UCL) of the mean concentration was calculated for each COPC where at least eight samples and four detected concentrations were available. The maximum detected concentration was used in place of the UCL as the EPC if (1) the calculated UCL was greater than the maximum detected concentration, or (2) the number of samples or detected concentrations was less than the levels needed to estimate a UCL. The arithmetic mean was used as the EPC for lead, consistent with USEPA guidance (USEPA, 2003a).

EPCs were estimated following the most recent parametric (distributional) and nonparametric USEPA recommendations in ProUCL software Version 5.0.00 (USEPA, 2013). ProUCL provides approaches for calculating UCLs of the mean, particularly when nondetected concentrations are present. These approaches consider a large variety of input, including the perceived distribution of the detected results (if no perceived distribution is acceptable, nonparametric alternatives are provided), sample size, variability, and skewness. The estimated EPCs are summarized in Tables 3.1 through 3.4 of Attachment A, and the ProUCL output is provided in Attachment E.

The PCB concentrations detected in the white perch caught at OU2 are unlikely to be solely attributable to exposures within the OU2 boundary. White perch have been shown to exhibit partial migration, suggesting that fish caught at OU2 may not be resident fish but instead may have migrated from surrounding areas (Kerr and Secor, 2012). It is expected that white perch enter Berrys Creek in the spring and leave in the fall. White perch are expected to stay in the main channel of Berrys Creek for the summer, entering the UOP site only at high tide to feed and not stay. OU2 is also affected by watershed-level contamination as a result of the strong mixing between OU2 and Berrys Creek during each tidal cycle.

3.2.2 Exposure Factors A RME scenario was quantified for potential receptors under current and future land use scenarios (USEPA, 1989). The exposure factors used in the intake calculations are presented in Tables 4.1 through 4.4 of Attachment A. The primary references for exposure factors are the standard default exposure factors presented in USEPA (1989, 2004, 2011, 2014a) guidance. Additionally, some of the exposure factors used in the HHRA are based on site-specific or area-specific assumptions.

The exposure factors used for quantifying potential exposures are conservative and reflect upper-bound assumptions on the exposure. The reliability of the values chosen for the exposure factors contributes substantially to the uncertainty of the resulting risk estimates.

3.2.2.1 Trespassers Due to access limitations and dense vegetation at the UOP site and Ackermans South, the exposure frequency used for a trespasser was assumed to be 13 days per year, representing once a week over a 13-week period during the summer months (June through August). Although older children (6 to 18 years old) were assumed to trespass onsite, they are not expected to be realistic receptors because the UOP site is isolated from the surrounding properties by a fence, an active rail line, and various tidal ditches and wetlands.

Professional judgment was used for the sediment incidental ingestion rate, which was assumed to be 10 percent of the adult soil ingestion rate due to the inaccessibility of the site sediment (under the vegetative mat) and the lack of swimming or wading (due to strong tidal currents and soft sediments). Considering the size of the UOP site and the unattractive swimming and wading conditions, 1 hour per


EN0602161110PHL 3-3

day was identified as a conservative exposure time for surface water. However, actual contact with surface water and sediment is unlikely to occur during each site visit because the environmental conditions at the site are not conducive for swimming or wading. The sediments are soft and would likely deter people from swimming or wading due to safety concerns. Additionally, a thick vegetation mat overlays the sediment in the wetland, thereby making it difficult for trespassers to have direct contact with the sediment. The site is also isolated, and access is very difficult due to large tidal variations and heavy vegetation. Overall, the exposure intensity assumptions used in this HHRA are expected to be conservative.

Because the site is heavily vegetated and wet, inhalation of dust particulates from sediment is an insignificant exposure pathway and was not quantified in the HHRA. The sediment is below a thick detrital layer and root system of the vegetation, and therefore generation of dust from sediment is not likely to occur onsite. Additionally, VOCs were not identified as COPCs in sediment, and elemental mercury has not been observed at the site; therefore, inhalation of vapors from sediment is also an insignificant exposure pathway and was not quantified in the HHRA.

In accordance with the methodology used to establish the USEPA RSLs for soil (USEPA, 2016a), the dermal exposure route for sediment was quantified only for constituents with a dermal absorption fraction from soil values, as presented in Exhibit 3-4 of USEPA’s Risk Assessment Guidance for Superfund Volume I: HHEM (Part E, Supplemental Guidance for Dermal Risk Assessment) (USEPA, 2004). The dermal absorption fraction from soil values used in the HHRA is presented in Table 4.1 Supplement of Attachment A.

3.2.2.2 Fish Consumers Fishing is not expected to occur at OU2 because few edible-size fish are present and access to the site is difficult due to the active rail line, fencing, and patrolling by New Jersey Transit. The area west of Murray Hill Parkway cannot be accessed by boat from the eastern stream channels. Additionally, the physical characteristics of the wetland (for example, dense vegetation, soft sediments, shallow narrow channels, and poor game fish habitat), make the site an unattractive destination for potential anglers. However, hypothetical fish ingestion exposures were estimated in the HHRA.

The fish ingestion rates were derived from USEPA guidance (USEPA, 2014b). The fish ingestion rate of 22 grams per day for an adult is based on uncooked finfish and shellfish consumption rates, and is the 90th percentile for adults consuming freshwater and estuarine organisms. It was assumed the fish ingestion rates for an older child and younger child are two-thirds and one-third of the adult ingestion rate, respectively.

The frequency of ingesting fish from OU2 was conservatively assumed to be 27 days per year (twice a week over a 13-week period). This ingestion frequency was obtained from a survey conducted by Connolly et al. (1992), who reported that the average number of fishing days per year across all New York anglers surveyed was 27 days. The uncertainties associated with the exposure frequency for fish consumption are discussed in the uncertainty analysis.

PCB concentrations have been shown to decrease in fish as a result of trimming and cooking; however, no adjustment for cooking or trimming loss was included in the exposure estimates for fish consumers. The extent to which PCB loss occurs cannot be determined without uncertainty and can largely depend on the cooking method (frying, grilling, etc.). Therefore, it was conservatively assumed that fish consumers were potentially exposed to 100 percent of the EPCs estimated for 2,3,7,8-TCDD and total PCBs.

3.2.3 Exposure Factors for Chemicals with Mutagenic Mode of Action According to cancer guidelines and supplemental guidance (USEPA, 2005b, 2005c), for COPCs that act via a mutagenic mode of action (MMOA), potential exposures were estimated using age-dependent


3-4 EN0602161110PHL

adjustment factors (ADAFs). Carcinogenic polycyclic aromatic hydrocarbons (cPAHs), TCE, and VC were identified as COPCs at OU2 and/or the Ackermans South area and are categorized as having an MMOA. Age-specific toxicity factors (exposure from birth and exposure through adulthood) are available for VC. Therefore, the oral cancer slope factor (CSF) for exposure from adulthood was used to quantify exposures and risks for older child and adult trespassers. TCE is carcinogenic by a MMOA for induction of kidney tumors (USEPA, 2016b). Therefore, ADAFs were used to estimate carcinogenic risks only for the kidney cancer component of TCE. Modes of action have not been established for TCE-induced non-Hodgkin lymphoma and liver cancer; therefore, ADAFs were not used to estimate risks for these types of cancers.

When estimating chemical intakes for the cPAHs and the kidney component of TCE, the exposure duration was adjusted for older child trespassers, as follows:

]1[]3[ 1817166 ADAFEDADAFEDEDadj ×+×= −−

Where:

EDadj = Adjusted exposure duration (days/year) ADAF = Age-dependent adjustment factor of 3 for older child trespassers and 1 for adult trespassers ED6-16 = Adjusted exposure duration, ages 6 to 16 (days/year)

ED17-18 = Adjusted exposure duration, ages 17 to 18 (days/year)

SECTION 4

EN0602161110PHL 4-1

Toxicity Assessment The oral toxicity values (CSFs and RfDs) used in the HHRA were obtained from the USEPA standard hierarchy of toxicity value sources (USEPA, 2003b), as follows:

• Tier 1 Source: Integrated Risk Information System (USEPA, 2016b) • Tier 2 Source: USEPA Provisional Peer-reviewed Toxicity Values (PPRTV) • Tier 3 Sources: other peer-reviewed federal and state toxicity values

− California EPA’s (2016) toxicity database − USEPA’s (1997) Health Effects Assessment Summary Tables

For thallium, the provisional peer-reviewed toxicity value (PPRTV; appendix value) was used for screening level purposes only and was not used for calculation of risk estimates. Guidance for PPRTV for thallium and compounds (USEPA, 2012) states:

It is inappropriate to derive a subchronic or chronic p-PrD for thallium. However, information is available which, although insufficient to support derivation of a provisional toxicity value, under current guidelines, may be of limited use to risk assessors…. Users of screening toxicity values in an appendix to a PPRTV assessment should understand that there is considerably more uncertainty associated with the derivation of a supplemental screening toxicity value than for a value presented in the body of the assessment.

The uncertainty factor associated with the thallium screening toxicity value is 3,000. Uncertainty factors are applied to extrapolate dose points from animal studies to humans. There is a degree of uncertainty in the noncarcinogenic toxicity criteria based on the available scientific data for each constituent. The noncarcinogenic toxicity factors are most likely an overestimate of actual toxicity.

Noncancer toxicity values used in the HHRA are presented in Table 5.1 of Attachment A. Cancer toxicity values for COPCs are provided in Table 6.1 of Attachment A.

4.1 Noncarcinogenic Toxicity Values Noncarcinogenic toxicity values (that is, oral RfDs) were used in estimating potential adverse health effects associated with exposure to COPCs. In general, the RfD is an estimate (with uncertainty spanning perhaps an order of magnitude) of daily exposure to the human population (including sensitive subgroups) that are likely to be without an appreciable risk of deleterious effects during a lifetime of exposure (USEPA, 1989). The oral RfD is used to estimate adverse effects from the oral route of exposure.

The oral RfD for mercuric chloride and other mercury salts was used to evaluate mercury in sediment and surface water. Mercury is expected to be in the form of mercuric chloride and other mercury salts in sediment and surface water. Elemental mercury has not been observed at the site. Additionally, the oral RfD for Aroclor-1254 was used to represent total Aroclors and total PCBs, and the oral RfD for 2,3,7,8-TCDD was used to represent 2,3,7,8-TCDD TEQ. Chronic toxicity data for potential noncarcinogenic effects of COPCs are presented in Table 5.1 of Attachment A.

4.2 Carcinogenic Toxicity Values Carcinogenic toxicity values (that is, oral CSFs) were used in evaluating potential carcinogenic effects associated with exposure to known, probable, or possible carcinogens having a USEPA weight-of-evidence classification of A, B, or C, respectively. CSFs were used to estimate upper-bound lifetime

SECTION 4 – TOXICITY ASSESSMENT

4-2 EN0602161110PHL

statistical probabilities of a hypothetical individual developing cancer as a result of exposure to a potential carcinogen.

Potential exposures to cPAHs were evaluated using the relative potency approach for oral exposures (USEPA, 1993). The toxicity of benzo(a)pyrene was used as a surrogate for other cPAHs, and the CSF of benzo(a)pyrene was scaled using factors of 1, 0.1, 0.01, and 0.001 to estimate CSFs for other cPAHs. The oral CSF for high-risk PCBs was used to represent total Aroclors and total PCBs, and the oral CSF for 2,3,7,8-TCDD was used to represent 2,3,7,8-TCDD TEQ. Toxicity data for potential carcinogenic effects for COPCs are presented in Table 6.1 of Attachment A.

4.3 Derivation of Dermal Toxicity Values Dermal RfDs and CSFs were estimated from oral RfDs and CSFs, respectively, using chemical-specific gastrointestinal absorption factors (ABSGI) to calculate total absorbed dose, as described in USEPA dermal risk assessment guidance (USEPA, 2004). Following USEPA’s recommendation, such a conversion was performed only when a chemical had a gastrointestinal absorption factor of less than 50 percent.

The dermal RfD is derived by multiplying the oral RfD by the ABSGI:

GIod ABS x RfD RfD =

Where:

RfDd = Dermal reference dose (milligram per kilogram per day [mg/kg-day]) RfDo = Oral reference dose (mg/kg-day)

ABSGI = Fraction of constituent absorbed in the gastrointestinal tract (unitless)

The dermal CSF is derived by dividing the oral CSF by the ABSGI:

GI

od

ABSCSFCSF =

Where:

CSFd = Dermal cancer slope factor (mg/kg-day)-1 CSFo = Oral cancer slope factor (mg/kg-day)-1

ABSGI = Fraction of constituent absorbed in the gastrointestinal tract (unitless)

The ABSGI values were obtained from USEPA’s RAGS, Volume I: Human Health Evaluation Manual, Part E (USEPA, 2004). If a chemical-specific gastrointestinal absorption factor was not available, gastrointestinal absorption of the chemical was assumed to be 100 percent, and the oral RfD (or oral CSF) was used as the dermal RfD (or dermal CSF) without adjustment. The dermal RfDs are included in Table 5.1 of Attachment A and the dermal CSFs are presented in Table 6.1 of Attachment A.

4.4 Lead Lead was identified as a COPC in site sediment and surface water for a trespasser scenario; however, quantitative oral toxicity values are not available for lead. An approach to assessing risks associated with adult exposures to lead was developed by USEPA’s Technical Review Workgroup for Lead (USEPA, 2003a) and updated in 2009. This methodology is a variation of the IEUBK model used to evaluate lead exposures to children. The Adult Lead Methodology (ALM) is used to evaluate risks associated with nonresidential adult exposures to lead. The model focuses on estimating fetal BLLs in women exposed to lead in soil (USEPA, 2003c), although it can also be used for evaluating sediment exposures. Therefore, the ALM was used to estimate potential BLLs for older child and adult trespassers potentially exposed to site sediment. The calculation worksheets for lead and the results of the ALM are presented in

SECTION 4 – TOXICITY ASSESSMENT

EN0602161110PHL 4-3

Attachment F. A lead model is not available for surface water; the uncertainty associated with not predicting BLLs for exposures to surface water is discussed in the uncertainty analysis (Section 5.5).

SECTION 5

EN0602161110PHL 5-1

Risk Characterization Potential human health risks are discussed separately for carcinogenic and non-carcinogenic COPCs due to the different toxicological endpoints, relevant exposure durations, and methods used to estimate risk. USEPA Superfund guidance considers an acceptable site ELCR range to be within 1 to 100 in a million (1 × 10-6 to 1 × 10-4). Generally, remedial actions are not warranted for site media with an ELCR of 1 × 10-4 or below, or a hazard index (HI) of 1 or less, although it may be warranted if other site-specific information suggests to risk managers that action is appropriate.

5.1 Approach for Potential Noncarcinogenic Effects The HHRA evaluated the potential for noncarcinogenic effects by comparing chemical intakes for each COPC with oral and dermal RfDs. In USEPA methodology, this ratio of exposure to toxicity is referred to as an HQ. The HQ assumes that there is a level of exposure below which it is unlikely for even sensitive populations to experience adverse health effects. If the exposure level exceeds this threshold, there is the potential for noncancer health effects to occur. The HQ is calculated as follows:

RfDIHQ =

Where:

HQ = Hazard quotient I = Intake level (milligram per kilogram per day [mg/kg-day])

RfD = Reference dose (mg/kg-day)

Intake and RfD are expressed in the same units (mg/kg-day) and represent the same exposure period. An HQ that exceeds 1 (that is, intake exceeds the RfD) indicates that there is a potential for adverse health effects associated with exposure to that COPC.

To assess the potential for noncarcinogenic health effects posed by exposure to multiple COPCs and exposure routes, an HI approach was used (USEPA, 1989). This approach assumes that noncarcinogenic hazards associated with exposure to more than one COPC and exposure route are additive. Synergistic or antagonistic interactions between COPCs are not quantified. The HI may exceed 1 even if all of the individual HQs are less than 1. The HI is equal to the sum of the HQs and is calculated as follows:

i

i

RfDI

RfDI

RfDIHI ++=

2

2

1

1

Where:

HI = Hazard index I = Intake level (mg/kg-day)

RfD = Reference dose (mg/kg-day) Ii = Intake level for the ith constituent

RfDi = Reference dose for the ith constituent

5.2 Approach for Potential Carcinogenic Effects The potential for carcinogenic effects due to exposure to site media was evaluated by estimating the ELCR. The ELCR is the incremental increase in the probability of developing cancer during one’s lifetime

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5-2 EN0602161110PHL

(as a result of exposure to site media) above the probability of developing cancer from nonsite exposures.

Potential ELCRs associated with exposure to individual carcinogens were calculated using CSFs and chemical intakes for oral and dermal contact exposures. The linear low-dose equation was used to estimate the incremental probability of an individual developing cancer over a lifetime as a result of exposure to potential carcinogens. Estimated ELCRs are calculated by multiplying the chemical intake by the CSF:

CSFIELCR ×=

Where:

ELCR = excess lifetime cancer risk I = intake level (mg/kg-day)

CSF = cancer slope factor (mg/kg-day)-1

The theoretical probability of developing cancer as a consequence of exposure to two or more COPCs and by two or more exposure pathways was calculated by summing the risk estimates for each COPC in the appropriate scenarios using the following equation:

( ) ( ) ( )ii CSFICSFICSFIELCRTotal ×+×+×= 2211

Where:

ELCR = excess lifetime cancer risk I = intake level (mg/kg-day)

CSF = cancer slope factor (mg/kg-day)-1 Ii = intake level for the ith constituent

CSFi = cancer slope factor for the ith constituent

5.3 Summary of Risk Estimates Potential risks associated with exposures to COPCs were quantified for the RME scenarios identified below. The risks were estimated using the analytical results for PCB congeners (that is, used to calculate total PCBs and 2,3,7,8-TCDD TEQ) and total Aroclors. The risk estimates discussed in this section incorporate the results for total PCBs and 2,3,7,8-TCDD TEQ. The estimated risks for total Aroclors are discussed separately in the uncertainty analysis (Section 5.5). The calculated ELCRs and HIs are summarized below for the indicated exposure scenarios:

• Onsite Trespassers (Adult and Older Child)—Current/Future Scenario

− Sediment (0 to 6 inches) (ingestion and dermal contact); surface water (dermal contact)

Adult: 8 × 10-6 cumulative ELCR and all target organ-specific HIs equal to or less than 1 (Table 7.1 RME, summarized in Table 9.1 RME of Attachment A)

Older Child: 9 × 10-6 cumulative ELCR and all target organ-specific HIs equal to or less than 1 (Table 7.2 RME, summarized in Table 9.2 RME of Attachment A)

For potential exposure to lead in sediment, the probability of BLLs exceeding 10 micrograms per deciliter (µg/dL) is less than 5 percent for both adult and older child trespassers (Tables 11.1 and 11.2 of Attachment F)

• Fish Consumers (Adult, Older Child, and Younger Child)—Current/Future Scenario

− Consumption of fish (white perch)


EN0602161110PHL 5-3

Adult: 7 × 10-5 cumulative ELCR and six target organ-specific HIs greater than 1: reproductive (3), developmental (3), and endocrine system (3) due to 2,3,7,8-TCDD TEQ and immune system (9), dermal (9), and ocular (9) due to total PCBs (Table 7.3 RME, summarized in Table 9.3 RME of Attachment A)

Older child: 1 × 10-4 cumulative ELCR and six target organ-specific HIs greater than 1: reproductive (3), developmental (3), and endocrine system (3) due to 2,3,7,8-TCDD TEQ and immune system (10), dermal (10), and ocular (10) due to total PCBs (Table 7.4 RME, summarized in Table 9.4 RME of Attachment A)

Younger child: 1 × 10-4 cumulative ELCR and six target organ-specific HIs greater than 1: reproductive (5), developmental (5), and endocrine system (5) due to 2,3,7,8-TCDD TEQ and immune system (16), dermal (16), and ocular (16) due to total PCBs (Table 7.5 RME, summarized in Table 9.5 RME of Attachment A)

• Offsite Trespassers (Adult and Older Child)—Current/Future Scenario

− Sediment in the Ackermans South area (0 to 6 inches) (ingestion and dermal contact)

Adult: 5 × 10-7 cumulative ELCR and all target organ-specific HIs less than 1 (Table 7.6 RME, summarized in Table 9.6 RME of Attachment A)

Older child: 7 × 10-7 cumulative ELCR and all target organ-specific HIs less than 1 (Table 7.7 RME, summarized in Table 9.7 RME of Attachment A)

5.4 Chemicals of Concern In general, chemicals of concern (COCs) are identified when the potential ELCR or HI for a receptor group exceeds USEPA threshold values (a total ELCR of 1 × 10-4 or a target organ-specific HI of 1). When a potential ELCR of 1 × 10-4 is exceeded for an exposure medium for a receptor group, the COPCs posing an individual ELCR greater than 1 × 10-6 in the environmental medium responsible for the unacceptable risks are identified as COCs. When a potential target organ-specific HI exceeds 1 for an exposure medium for a receptor group, the COPCs posing a HQ greater than 0.1 for that target organ in the environmental medium responsible for the unacceptable HI are identified as COCs. Factors such as nature of the chemical source, laboratory contamination, and common pesticide use (unrelated to spills, improper storage disposal or use) are typically considered when identifying COCs.

Risk estimates for site sediment, site surface water, and offsite sediment in the Ackermans South area were less than or within the USEPA acceptable risk range and the estimated target organ-specific HIs were less than or equal to the non-cancer threshold for current and future trespassers (adult and older child). Additionally, the probability of BLLs exceeding 10 µg/dL was less than 5 percent for both adult and older child trespassers potentially exposed to lead in site sediment.

Risk estimates for fish (white perch) exceeded the USEPA non-cancer threshold for fish consumers (adult, older child, and younger child) due to PCBs. Therefore, 2,3,7,8-TCDD TEQ and total PCBs were identified as COCs for fish. The estimated HIs for the COCs are presented in Tables 10.1 through 10.3 of Attachment A.

5.5 Uncertainty Analysis The assumptions used in the HHRA have inherent uncertainty. While it is theoretically possible that this leads to underestimates of potential risk, the use of numerous upper-bound assumptions most likely results in conservative estimates of potential risk. A receptor group’s potential exposure and subsequent potential risk are influenced by the exposure scenario and dose/response and vary on a case-by-case


5-4 EN0602161110PHL

basis. The key assumptions in the HHRA and their influence on the numerical risk estimates and specific uncertainties associated with the HHRA are discussed below.

5.5.1 Data Evaluation The purpose of data evaluation is to determine which constituents, if any, are present at the site at concentrations requiring evaluation in the HHRA. Uncertainty with respect to data evaluation can arise from many sources, such as the quality of data used to characterize the site and the process used to select data and COPCs in the HHRA.

The primary sources of contamination to OU2 include historical industrial activities at the UOP Uplands and the surrounding properties. Historical discharges from the storm drains are likely to have been the most significant transport pathways to OU2. The storm drains were impacted by releases from the surrounding properties, including, but not limited to, the Becton Dickinson and Matheson Gas properties. OU2 is also affected by watershed-level contamination (as a result of the strong mixing between OU2 and Berrys Creek during each tidal cycle) and surrounding anthropogenic sources3 unrelated to former UOP operations. Therefore, the surface water, sediment, and fish tissue data collected at OU2 are likely to have been influenced by potential contamination from surrounding properties and likely overestimate the site-related exposures and risks in the HHRA.

Inorganic constituents and PCBs detected in site media were not compared to background concentrations in the COPC screening step; however, some inorganic chemicals are naturally occurring in site sediment and surface water. Retaining COPCs in the HHRA that are partially or wholly attributable to background conditions overestimates site-related exposures and risks in the HHRA.

Fish RSLs were calculated for chemicals analyzed in fish samples (PCBs). Site-specific exposure factors, a target ELCR of 1 × 10-6, and a target HI of 1 were used in the calculation. PCBs were identified as COPCs in fish tissue. Therefore, using alternate exposure factors or target risk levels would not have resulted in different COPCs being identified for fish tissue.

The four filtered surface water samples collected from location MSW-24 were analyzed for PCBs, and PCBs were not detected in the samples. However, both filtered and unfiltered surface water samples were used in the HHRA. The unfiltered surface water data likely represent concentrations in both surface water and suspended sediment. Using unfiltered samples for estimating exposures to PCBs in surface water results in an overestimation of potential surface water dermal exposures and risks at OU2.

Sediment samples collected using traps and turf mats represent sediment that is moving around the system and measure what is being deposited on the marsh surface. The sediment data associated with the trap and turf mat samples are summarized in Table 5-1. The samples were analyzed for chromium, mercury, and PCBs. The detected concentrations of chromium were less than the residential soil RSL; however, mercury and PCBs were detected at concentrations greater than residential soil RSLs. The concentrations of mercury and PCBs detected in the turf mat and trap samples were less than the concentrations detected in the sediment grab samples used in the HHRA. As presented in Table 2.1 in Attachment A, the maximum detected concentrations in the sediment grab samples were as follows: mercury, 143 mg/kg; 2,3,7,8-TCDD TEQ, 0.00271 mg/kg; total Aroclors, 550 mg/kg; and total PCBs, 354 mg/kg. If trespassers were to access the site, they may contact sediments on the marsh surface and at depths below the surface. Because concentrations detected in the turf mat and trap samples were less than the sediment grab samples, there is minimal uncertainty associated with excluding the trap and turf mat samples from the HHRA.

3 Potential anthropogenic sources in the area include car exhaust, industrial emissions, and surface runoff from highways and parking areas, which may have contributed concentrations of inorganics, PAHs, and PCBs to site media.


EN0602161110PHL 5-5

Table 5-1. Sediment Analytical Data Collected Using Traps and Turf Mats OU2, Universal Oil Products (UOP), East Rutherford, NJ

Analyte Minimum

Conc./Qualifier Maximum

Conc./Qualifier Detection Frequency Residential Soil RSLa

Chromium 84 1,610 75/75 12,000 NC

Mercury 2 J 34.6 74/74 2.3 NC

2,3,7,8-TCDD TEQ 0.00000673 0.000545 40/40 0.0000048 C

Total Aroclors 0.62 346 37/37 0.12 NC

Total PCBs 0.415 15.8 40/40 0.12 NC

Concentrations are in milligram per kilogram (mg/kg). a Regional screening levels (RSLs) for Residential Soil (May 2016). Concentrations based on noncarcinogenic health effects are adjusted using HQ=0.1.

C = carcinogenic

NC = noncarcinogenic

J = compound was detected below the reporting limit in the sample

5.5.2 Exposure Assessment The HHRA assumed that the EPCs for site media remain constant throughout the exposure period within the exposure area. This assumption results in an overestimation of risk—because of the lack of a continuous release source, concentrations of COPCs will decrease over the exposure durations used in the HHRA as unimpacted sediment enters the site with tidal flow and is deposited at the surface.

The 95 percent UCL of the mean concentrations or maximum detected concentrations were selected as EPCs. Using the 95 percent UCLs of the mean or maximum detected concentrations as EPCs will likely lead to an overestimation of actual exposure because receptors are assumed to be exposed to the 95 percent UCL of the mean or maximum detected concentrations for the entire exposure duration. As the data indicate, many COPCs were not detected in all samples. Thus, the assumption that all potential exposures are to the 95 percent UCL of the mean or maximum detected concentrations likely results in an overestimation of actual exposures and estimates of potential risk.

Although it was assumed that fish consumers ingest fish caught onsite, fishing is not expected to occur at the site. Few edible-size fish of any species have been observed onsite, and the largest white perch caught onsite during the sampling event was 10.2 centimeters. Site access is difficult due to the active rail line, fencing, and patrolling by New Jersey Transit. Additionally, the physical characteristics of the wetland (dense vegetation, soft sediments in the side channels at low tide, and strong tidal currents in the main channel of Ackermans Creek at high tide) make the site an unattractive destination for trespassers (including anglers). Therefore, the fish ingestion exposure pathway is not expected to occur, but rather is a hypothetical scenario onsite.

The exposure factors used for quantifying potential exposures were conservative and reflect upper-bound assumptions on the exposure. The reliability of the values chosen for the exposure factors also contributes substantially to the uncertainty of the resulting risk estimates. Because most of the exposure factors are upper-bound assumptions, the resulting risks likely overestimate the actual risks. For example, older children (6 to 18 years old) were assumed to trespass onsite for 13 days per year; however, older children are not expected to be realistic receptors because the site is relatively isolated and access is very difficult. In addition, trespassers are assumed to have dermal contact with surface water and sediment for 1 hour each time they are present onsite. Actual contact with surface water and sediment is unlikely to occur during each site visit because the environmental conditions at the site are


5-6 EN0602161110PHL

not conducive for swimming or wading. The sediments are soft and would likely deter people from swimming or wading due to safety concerns. Additionally, a thick vegetation mat overlays the sediment in the wetland, thereby making it difficult for trespassers to have direct contact with the sediment. The site is also isolated, and access is very difficult due to large tidal variations and heavy vegetation. Overall, the exposure intensity assumptions used in this HHRA are expected to be conservative. Any actual risks are likely to be less than the potential risks presented in this HHRA.

PCB concentrations have been shown to decrease in fish as a result of trimming and cooking; however, no adjustment for cooking or trimming loss was included in the exposure estimates for fish consumers. The extent to which PCB loss occurs largely depends on the cooking method (frying, grilling, etc.). It was conservatively assumed that there was no reduction in PCB concentrations as a result of trimming or cooking.

Three volatile COPCs were identified as surface water COPCs. Inhalation exposures were not quantified for these COPCs. However, due to the low EPCs for these COPCs (benzene = 0.57 µg/L, TCE = 2.2 µg/L, and VC = 0.29 µg/L) and the low frequency of exposure assumed for onsite trespassers, potential underestimates of risk are minimal.

5.5.3 Toxicity Assessment Uncertainty associated with the noncarcinogenic toxicity values for COPCs is included in Table 5.1 of Attachment A. Several uncertainty factors were applied by USEPA to extrapolate doses from animal studies to humans. These uncertainty factors range between 1 and 3,000 for the COPCs identified in the HHRA. Therefore, a high degree of uncertainty exists in the noncarcinogenic toxicity values and varies based on the available scientific data for each COPC. The noncarcinogenic toxicity values are expected to overestimate actual toxicity.

Noncancer toxicity values were not available for one pesticide (beta BHC) and six cPAHs [benzo(a)anthracene, benzo(a)pyrene, benzo(b)fluoranthene, benzo(k)fluoranthene, dibenz(a,h)anthracene, and indeno(1,2,3-c,d)pyrene]. This leads to an underestimation of noncancer hazards, although the extent cannot be determined.

Potential exposures to cPAHs through dermal contact with surface water were not quantified in the HHRA due to the uncertainties associated with using the oral CSF for benzo(a)pyrene to quantify dermal exposures. Carcinogenic PAHs are believed to cause skin cancer through local rather than systemic action (USEPA, 1989). In an aqueous medium such as surface water, it is unlikely for a receptor to have prolonged contact with cPAHs at a single contact point on the skin. Therefore, not quantifying the dermal exposure route for cPAHs in surface water is unlikely to significantly underestimate the potential carcinogenic risks for trespassers.

5.5.4 Risk Characterization The potential risk of adverse health effects is characterized based on potential exposures and potential dose-response relationships. An important additional source of uncertainty is introduced in this phase of the HHRA—the combination of upper-bound intake estimates with upper-bound toxicity estimates. Generally, the goal of a baseline risk assessment is to estimate an upper-bound, but reasonable, potential risk. Such an upper-bound estimate can be derived in several ways, depending on how conservative one wants the final estimate to be. HHRAs combine several upper-bound assumptions to estimate potential risk. Most of the assumptions about exposure and toxicity used in this HHRA are representative of statistical upper bounds for each parameter. The result of combining several such upper-bound assumptions is that the final estimate of potential exposure or potential risk is conservative.

Potential exposures and BLLs for lead in surface water were not quantified because there are no lead models that evaluate surface water as an exposure medium. Lead was detected in all eight surface


EN0602161110PHL 5-7

water samples at concentrations ranging from 3.1 µg/L to 32.6 µg/L. The arithmetic mean concentration of 8.2 µg/L was less than the federal action Level of 15 µg/L for drinking water. Additionally, lead was detected only in one filtered surface water sample, suggesting the lead concentrations in the unfiltered samples are primarily due to sediment particulates. Since site surface water is not a drinking water source, and because the expected low frequency of trespassing onsite, potential underestimates of lead risk from not quantifying surface water exposures are minimal.

Some sediment samples were analyzed for both PCB congeners (that is, used to calculate PCB TEQ and total PCBs) and Aroclors; therefore, in order to avoid overestimating risks for PCBs by including both congener-specific and Aroclor data in the cumulative risk estimates, the risks were summed separately for congener-specific and Aroclor data. The estimated risks associated with potential exposures to PCB congeners are discussed in Section 5.3. The estimated ELCRs and HIs for Aroclors were less than the ELCRs and HIs estimated for PCB congeners in onsite sediment, as presented in Tables 9.1 RME and 9.2 RME of Attachment A. The ELCRs and HIs estimated for Aroclors were greater than those estimated for PCB congeners in sediment at Ackermans South; however, they were still within USEPA-acceptable levels, as presented in Tables 9.6 RME and 9.7 RME of Attachment A. Therefore, the overall conclusions for the HHRA are the same based on the congener-specific PCB data and Aroclor data.

The estimated risks for consumption of white perch from OU2 exceeded USEPA-acceptable levels; however, the actual current and future site-related risks are expected to be lower than those estimated in the HHRA, based on the following rationales:

• Fishing is not expected to occur at OU2 because few edible-size fish are present and access to the site is difficult due to the active rail line, fencing, and patrolling by New Jersey Transit. The area west of Murray Hill Parkway cannot be accessed by boat from the eastern stream channels. Additionally, the physical characteristics of the wetland (dense vegetation, soft sediments, shallow narrow channels, and poor game fish habitat) make the site an unattractive destination for potential anglers. Therefore, the exposure frequency of 27 days per year that was used in the HHRA for fish consumers is overly conservative for OU2.

• The PCB concentrations detected in the white perch caught at OU2 are unlikely to be solely attributable to exposures within the OU2 boundary. White perch have been shown to exhibit partial migration, suggesting that fish caught at OU2 may not be resident fish but instead may have migrated from surrounding areas (Kerr and Secor, 2012). It is expected that the white perch enter Berrys Creek in the spring and leave in the fall. White perch are expected to stay in the main channel of Berrys Creek for the summer, entering the UOP site only at high tide to feed and not staying in UOP. OU2 is also affected by watershed-level contamination as a result of the strong mixing between OU2 and Berrys Creek during each tidal cycle.

• PCB concentrations in fish are expected to be lower in the future due to the reduction in PCB sediment sources, deposition of sediments not impacted by PCBs, and interaction of fish with non-impacted sediment.

Overall, due to there being very few edible-size fish onsite, access limitations at OU2, the migratory behavior of white perch, and the influence of offsite contamination from tidal fluctuations, the estimated risks in this HHRA are likely overestimated in relation to the actual current and future site-related risks associated with consumption of fish from OU2.

SECTION 6

EN0602161110PHL 6-1

Summary An HHRA was conducted for OU2 using analytical data collected from sediment, surface water, and fish tissue. The objective of the HHRA was to evaluate potential exposures and risks using analytical data representing the site conditions following the NTCRA. Based on the agreement with the BCSA PRP Group reached in early 2016, the HHRA addresses chemical concentrations remaining in the channels associated with the Streamlands west of Murray Hill Parkway. Additionally, the offsite marshlands south of OU2, referred to as Ackermans South, were evaluated in the HHRA per agreement with the BCSA PRP Group. The HHRA incorporated samples collected by CH2M from 2006 through 2015 and samples collected by the BCSA PRP Group from 2009 to 2013.

The UOP site is isolated from the surrounding properties by a fence, an active rail line, and various tidal ditches and wetlands. The area near the active rail line is patrolled by New Jersey Transit. The OU2 Streamlands west of Murray Hill Parkway, which are the focus of this HHRA, are highly inaccessible due to their physical nature. The wetland vegetation is very dense, and cannot be traversed without the use of brush-cutting tools. Similar conditions are also present in Ackermans South. Therefore, trespassing is expected to be infrequent onsite and at Ackermans South, and exposure frequencies used in this HHRA are considered very conservative.

The following receptors and exposure pathways were evaluated quantitatively in the HHRA:

• Current/future onsite trespassers. Older child (6 to 18 years old) and adult trespassers were evaluated for ingestion and dermal contact exposures to site sediment (0 to 6 inches) and dermal contact exposures to site surface water.

• Current/future fish consumers. Younger children (0 to 6 years old), older children, and adults were assumed to consume white perch caught onsite. Ingestion of crab was not evaluated in the HHRA because edible-size blue crabs were not observed at the site during the long-term monitoring sampling events.

• Current/future offsite trespassers. Older child (6 to 18 years old) and adult trespassers were evaluated for ingestion and dermal contact exposures to sediment (0 to 6 inches) in Ackermans South.

Risk estimates for site sediment, site surface water, and offsite sediment in Ackermans South were less than or within USEPA acceptable levels for current and future trespassers (adult and older child). That is, the potential ELCRs for trespassers were within the target ELCR range of 1 × 10-6 to 1 × 10-4, and the estimated target-organ-specific HIs were less than or equal to the threshold of 1. Additionally, the probability of BLLs exceeding 10 µg/dL was less than 5 percent for both adult and older child trespassers potentially exposed to lead in site sediment.

Risk estimates for fish (white perch) exceeded USEPA-acceptable levels for fish consumers (adult, older child, and younger child) due to PCBs. Therefore, 2,3,7,8-TCDD TEQ and total PCBs were identified as COCs for fish. However, fishing is not expected to occur at OU2. There are very few edible-size fish onsite and access to the site is difficult due to the active rail line, fencing, and patrolling by New Jersey Transit. Additionally, the physical characteristics of the wetland (dense vegetation, soft sediments in the side channels at low tide, and strong tidal currents in the main channel of Ackermans Creek at high tide) make the site an unattractive destination for trespassers (including anglers). Therefore, the fish ingestion risk estimates are for a hypothetical exposure scenario that is not expected to occur.

SECTION 7

EN0602161110PHL 7-1

References BCSA Group. 2009. Work Plan for Remedial Investigation /Feasibility Study: Berry’s Creek Study Area. Submitted to U.S. Environmental Protection Agency, Submitted by Berry’s Creek Study Area Cooperating PRP Group. C357 - BC787, Geosyntec Consultants, Inc., Oak Brook, IL, and Integral Consulting Inc.

Berry, W.J., W.S. Boothman, J.R. Serbest, and P.A. Edwards. 2004. Predicting the Toxicity of Chromium in Sediments. Environ. Toxicol. Chem. Vol. 23, no. 12. pp. 2981–92.

California EPA. 2016. Toxicity Criteria Database. Office of Environmental Health Hazard Assessment. http://www.oehha.ca.gov/risk/ChemicalDB/index.asp.

CH2M. 2011. Remedial Investigation Report, Universal Oil Products, Operable Unit 2, East Rutherford, New Jersey. April.

CH2M. 2012. Human Health Risk Assessment, Universal Oil Products, Operable Unit 2, East Rutherford, New Jersey. February.

CH2M. 2013. Non-Time-Critical Removal Action Project (NTCRA) Construction Completion Report, Universal Oil Products, Inc., East Rutherford, New Jersey. Draft. March.

CH2M. 2014a. Long-Term Monitoring Plan for Non-Time-Critical Removal Action, Universal Oil Products, Operable Unit 2, East Rutherford, New Jersey, USEPA ID: NJD002005106. May.

CH2M. 2014b. Non-Critical Time Removal Action – Long-Term Monitoring - Year 1 Biennial Report. May.

CH2M. 2014c. Monitored Natural Recovery Treatability Study Work Plan Universal Oil Products Operable Unit 2 East Rutherford, New Jersey USEPA ID: NJD002005106. May.

Connolly, N.A., B.A. Knuth, and C.A. Bisogni. 1992. Effects of the health advisory and advisory changes on fishing habits and fish consumption in New York sport fisheries. Report for New York Sea Grant Institute Project No. R/FHD-2-PD. September. Human Dimension Research Unit, Department of Natural Resources, New York State College of Agriculture and Life Sciences, Cornell University, Ithaca, NY.

Geosyntec Consultants, Inc., and Integral Consulting Inc. (Geosyntec/Integral). 2009a. Phase 1 Work Plan and QAPP for Remedial Investigation/Feasibility Study. Berry’s Creek Study Area. Prepared for the Berry’s Creek Cooperating PRP Group.

Geosyntec/Integral. 2009b. Quality Assurance Project Plan. Berry’s Creek Study Area. Prepared for the Berry’s Creek Cooperating PRP Group.

Geosyntec/Integral. 2010. Phase 2 Work Plan Addendum. Quality Assurance Project Plan/Field Sampling Plan. Prepared for the Berry’s Creek Cooperating PRP Group.

Geosyntec/Integral. 2011. Baseline Monitoring Work Plan, Berry’s Creek Study Area. Prepared for the Berry’s Creek Cooperating PRP Group.

Geosyntec/Integral. 2012. Phase 3a Addendum. Quality Assurance Project Plan/Field Sampling Plan. Prepared for the Berry’s Creek Cooperating PRP Group.

Geosyntec/Integral. 2013. Phase 3b Addendum. Quality Assurance Project Plan/Field Sampling Plan. Prepared for the Berry’s Creek Cooperating PRP Group.

Geosyntec/Integral. 2014. Phase 3b 2014 Addendum. Quality Assurance Project Plan/Field Sampling Plan. Prepared for the Berry’s Creek Cooperating PRP Group.

SECTION 7 – REFERENCES

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Geosyntec/Integral, 2015. Phase 3b 2015 Addendum. Quality Assurance Project Plan/Field Sampling Plan. Phase Prepared for the Berry’s Creek Cooperating PRP Group.

Kerr, L.A., and D.H. Secor. 2012. Partial Migration Across Populations of White Perch (Morone americana): A Flexible Life History Strategy in a Variable Estuarine Environment. Estuaries and Coasts. Vol. 35, no. 1. pp 227-236.

Pettine, M., and S. Capri. 2005. Digestion Treatments and Risks of Cr(III)-Cr(VI) Interconversions During Cr(VI) Determination in Soils and Sediments: A Review. Analytica Chimica Acta. Vol. 540. pp. 231-238.

U.S. Environmental Protection Agency (USEPA). 1989. Risk Assessment Guidance for Superfund, Volume I: Human Health Evaluation Manual (Part A). Office of Emergency and Remedial Response. EPA/540/1-89/002. December

USEPA. 1993. Provisional Guidance for Quantitative Risk Assessment of Polycyclic Aromatic Hydrocarbons. Office of Research and Development.

USEPA. 1994. Revised Interim Soil Lead Guidance for CERCLA Sites and RCRA Corrective Action Facilities. OSWER Directive 9355.4-12.

USEPA. 1997. Health Effects Assessment Summary Tables, Annual Update (HEAST). USEPA, Environmental Criterion Assessment Office, Office of Research and Development, Cincinnati, OH.

USEPA. 2001. Risk Assessment Guidance for Superfund (RAGS); Volume I—Human Health Evaluation Manual (Part D, Standardized Planning, Reporting and Review of Superfund Risk Assessments). Final. December.

USEPA. 2003a. Recommendations of the Technical Review Workgroup for Lead for an Approach to Assessing Risks Associated with Adult Exposure to Lead in Soil. Office of Solid Waste and Emergency Response. OSWER 9285.7-54. January.

USEPA. 2003b. Human Health Toxicity Values in Superfund Risk Assessments. OSWER Directive 9285.7-53. December 5.

USEPA. 2003c. Adult Lead Methodology (ALM) Spreadsheets. Office of Solid Waste and Emergency Response. http://www.epa.gov/superfund/programs/lead/products/alm05_03.xls. Last update on 19 May.

USEPA. 2004. Risk Assessment Guidance for Superfund, Volume I: HHEM (Part E, Supplemental Guidance for Dermal Risk Assessment). Final. USEPA/540/R-99/005.

USEPA. 2005a. Procedures for the Derivation of Equilibrium Partitioning Sediment Benchmarks (ESBs) for the Protection of Benthic Organisms: Metal Mixtures (Cadmium, Copper, Lead, Nickel, Silver, and Zinc). Attachment D: Chromium. EPA-600-R-02-011. Office of Research and Development. Washington, DC.

USEPA. 2005b. Supplemental Guidance for Assessing Susceptibility from Early-Life Exposure to Carcinogens. Risk Assessment Forum. USEPA/630/R-03/003F. March.

USEPA. 2005c. Guidelines for Carcinogen Risk Assessment. Risk Assessment Forum. EPA/630/P-03/001F. March.

USEPA.2008. Provisional Peer Reviewed Toxicity Values for Carbazole (CASRN 86-74-8). Superfund Health Risk Technical Support Center. July.

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USEPA. 2010. Recommended Toxicity Equivalence Factors (TEFs) for Human Health Risk Assessments of 2,3,7,8-Tetrachlorodibenzo-p-dioxin and Dioxin-Like Compounds. EPA/100/R 10/005. December.

SECTION 7 – REFERENCES

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USEPA. 2011. Exposure Factors Handbook: 2011 Edition. EPA/600/R-090/052F. September.

USEPA. 2012. Final Provisional Peer-Reviewed Toxicological Values for Thallium and Compounds. Prepared for U.S. EPA Office of Research and Development’s National Center for Environmental Assessment, Superfund Health Risk Technical Support Center by ICF International. October.

USEPA. 2013. ProUCL, Version 5.0.00. Prepared by Lockheed Martin Environmental Services. September.

USEPA. 2014a. Human Health Evaluation Manual, Supplemental Guidance: Update of Standard Default Exposure Factors, OSWER Directive 9200.1-120. February.

USEPA. 2014b. Estimated fish consumption rates for the U.S. population and selected subpopulations (NHANES 2003-2010). Final Report. EPA-820-R-14-002. April.

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USEPA. 2016b. Integrated Risk Information System (IRIS) Database. http://www.epa.gov/iris/index.html.

Attachment A RAGS Part D Tables

TABLE 1SELECTION OF EXPOSURE PATHWAYS

OU2, Universal Oil Products (UOP), East Rutherford, New Jersey

Scenario Medium Exposure Exposure Receptor Receptor Exposure On-Site/ Type of Rationale for Selection or Exclusion

Timeframe Medium Point Population Age Route Off-Site Analysis of Exposure Pathway(1)

Current/Future Sediment SedimentWetland Sediment

(0 to 6 inches)(On-site)

On-Site Trespasser(2) Adult & Older Child Dermal,

Ingestion On-site QuantTrespassers may contact sediment if they access the site. The site conditions are not conducive for wading or swimming due to heavy vegetation, strong tidal currents at high tide, and soft sediments at low tide. A thick vegetation mat is present above the sediments, hindering access to sediments. Elemental mercury has not been observed on-site.

Surface Water Surface Water Wetland Surface Water On-Site Trespasser(2) Adult & Older Child Dermal On-site Quant

Trespassers may contact surface water if they access the site. The site conditions are not conducive for wading or swimming due to heavy vegetation, shallow water depth, and deep sediments. Elemental mercury has not been observed on-site.

Sediment/Surface Water Fish Fish

(white perch) Fish Consumer (3) Adult, Older Child & Younger Child Ingestion On-site Quant It is highly unlikely that trespassers will access the site for fishing. However, if fishing occurs, fish

consumers could be exposed to site contaminants in fish caught on-site.

Sediment(Ackermans South) Sediment

Wetland Sediment(0 to 6 inches)

(Ackermans South)Off-Site Trespasser

(2) Adult & Older Child Dermal, Ingestion Off-site Quant

Trespassers may contact sediment if they access the Ackermans South area. There is heavy vegetation present at Ackermans South and trespassers would likely need brush-cutting tools to enter the area. The stream that runs through the area is dry except for at high tide and therefore, does not provide a habitat for fish. Due to the physical characteristics of the Ackermans South area, it is unlikely to be an attractive destination for trespassers.

Notes:(1) The age groups include: younger child (0-6 years old); older child (6-18 years old); and adult (18-30 years old).(2) Trespassing is expected to be a very infrequent activity since active rail lines are present along and across the site, the land is patrolled by NJ Transit, fencing is present, and very dense vegetation is present onsite.(3) Fish consumers are assumed to be adult or older child trespassers on-site, or a younger child who eats fish caught on-site.Quant: Quantitative

Page 1 of 1

Scenario Timeframe: Current/Future Medium: Sediment Exposure Medium: Sediment

Exposure CAS Chemical Units Location Detection Range of Concentration Background Screening Potential Potential COPC Rationale forPoint Number of Maximum Frequency Detection Used for Value Toxicity Value ARAR/TBC ARAR/TBC Flag Selection or

Concentration Limits Screening Value Source Deletion(1) (2) (3)

Wetland Sediment 7429-90-5 Aluminum 1.02E+03 2.71E+04 mg/kg SC-B.4 40 / 40 1.20E+01 - 1.60E+02 2.71E+04 NA 7.70E+03 nc NA NA Yes ASL(0 to 6 inches) 7440-36-0 Antimony 2.20E+00 J 1.44E+02 mg/kg WC-B.6 5 / 40 4.90E-01 - 3.50E+01 1.44E+02 NA 3.10E+00 nc NA NA Yes ASL

(On-site) 7440-38-2 Arsenic 2.10E+00 1.46E+02 mg/kg SC-B.1 32 / 40 3.80E-01 - 1.60E+01 1.46E+02 NA 6.80E-01 ca NA NA Yes ASL7440-39-3 Barium 2.92E+01 2.12E+03 J mg/kg MRH-238 31 / 40 9.00E-02 - 1.60E+02 2.12E+03 NA 1.50E+03 nc NA NA Yes ASL7440-41-7 Beryllium 2.00E-01 1.40E+00 mg/kg SC-A.2 16 / 40 5.40E-02 - 1.60E+00 1.40E+00 NA 1.60E+01 nc NA NA No BSL7440-43-9 Cadmium 8.00E-01 3.16E+01 mg/kg SC-B.1 22 / 40 4.50E-02 - 3.90E+00 3.16E+01 NA 7.10E+00 nc NA NA Yes ASL7440-70-2 Calcium 4.91E+02 5.10E+04 J mg/kg DWC-214 37 / 40 2.00E+01 - 3.90E+03 5.10E+04 NA NUT NA NA No NUT7440-47-3 Chromium 8.20E+00 1.26E+04 mg/Kg LTM04 40 / 40 2.50E-01 - 1.70E+01 1.26E+04 NA 1.20E+04 nc NA NA Yes ASL7440-48-4 Cobalt 5.80E+00 J 7.70E+01 mg/kg WC-B.6 25 / 40 2.00E-01 - 3.90E+01 7.70E+01 NA 2.30E+00 nc NA NA Yes ASL7440-50-8 Copper 3.00E+00 1.35E+03 mg/kg WC-B.6 40 / 40 9.30E-01 - 2.00E+01 1.35E+03 NA 3.10E+02 nc NA NA Yes ASL7439-89-6 Iron 2.63E+03 9.42E+04 mg/kg WC-B.6 40 / 40 6.20E+00 - 8.70E+01 9.42E+04 NA 5.50E+03 nc NA NA Yes ASL7439-92-1 Lead 4.00E+00 9.36E+02 mg/kg WC-B.6 40 / 40 2.40E-01 - 1.60E+01 9.36E+02 NA 4.00E+02 nc NA NA Yes ASL7439-95-4 Magnesium 4.85E+02 1.06E+04 mg/kg SC-B.4 37 / 40 6.40E+00 - 3.90E+03 1.06E+04 NA NUT NA NA No NUT7439-96-5 Manganese 1.56E+01 5.21E+04 J mg/kg MRH-237 40 / 40 9.30E-02 - 1.20E+01 5.21E+04 NA 1.80E+02 nc NA NA Yes ASL7439-97-6 Mercury 6.80E-02 1.43E+02 mg/kg LTM04 39 / 40 3.20E-02 - 7.30E+00 1.43E+02 NA 2.30E+00 nc NA NA Yes ASL22967-92-6 Methyl Mercury 9.00E-06 J 1.60E-01 J mg/kg BAZ-2028 30 / 31 9.00E-06 - 1.80E-03 1.60E-01 NA 7.80E-01 nc NA NA No BSL7440-02-0 Nickel 2.80E+00 4.03E+02 J mg/kg MRH-237 35 / 40 3.40E-01 - 3.10E+01 4.03E+02 NA 1.50E+02 nc NA NA Yes ASL7440-09-7 Potassium 7.20E+02 B 4.47E+03 mg/kg WC-G.4 21 / 40 7.80E+00 - 7.80E+03 4.47E+03 NA NUT NA NA No NUT7782-49-2 Selenium 1.40E+00 J 7.90E+00 mg/kg WC-B.6 3 / 40 5.70E-01 - 1.60E+01 7.90E+00 NA 3.90E+01 nc NA NA No BSL7440-22-4 Silver 3.30E-01 J 8.30E+00 J mg/kg MRH-236 17 / 40 1.30E-01 - 3.90E+00 8.30E+00 NA 3.90E+01 nc NA NA No BSL7440-23-5 Sodium 3.60E+02 J 1.42E+04 J mg/kg MRH-237 31 / 40 8.30E+01 - 7.80E+03 1.42E+04 NA NUT NA NA No NUT7440-28-0 Thallium 1.20E+00 J 2.18E+02 J mg/kg MRH-237 8 / 40 6.70E-01 - 1.27E+01 2.18E+02 NA 7.80E-02 nc NA NA Yes ASL7440-62-2 Vanadium 4.20E+00 1.31E+02 mg/kg WC-B.7 36 / 40 1.50E-01 - 8.70E+01 1.31E+02 NA 3.90E+01 nc NA NA Yes ASL7440-66-6 Zinc 1.31E+01 4.33E+03 mg/kg WC-B.6 40 / 40 1.30E+00 - 8.70E+01 4.33E+03 NA 2.30E+03 nc NA NA Yes ASL

TCDD_TEQ 2,3,7,8-TCDD TEQ 2.19E-06 2.71E-03 mg/kg LTM04 15 / 15 - 2.71E-03 NA 4.80E-06 ca NA NA Yes ASLAroclorTotal Total Aroclors 4.83E-02 5.50E+02 mg/kg DWC-214 38 / 41 7.60E-04 - 1.40E+00 5.50E+02 NA 1.20E-01 nc NA NA Yes ASL

PCBTotal Total PCBs 1.61E-01 3.54E+02 mg/kg LTM04 15 / 15 - 3.54E+02 NA 1.20E-01 nc NA NA Yes ASL72-55-9 4-4’-DDE 1.10E+00 J 1.10E+00 J mg/kg BAZ-2028 1 / 2 2.60E-03 - 3.00E-02 1.10E+00 NA 2.00E+00 ca NA NA No BSL309-00-2 Aldrin 3.00E+00 J 3.00E+00 J mg/kg BAZ-2028 1 / 1 3.50E-02 - 3.50E-02 3.00E+00 NA 3.90E-02 ca NA NA Yes ASL319-85-7 BHC (beta) 6.70E+00 J 6.70E+00 J mg/kg BAZ-2028 1 / 2 4.50E-03 - 5.10E-02 6.70E+00 NA 3.00E-01 ca NA NA Yes ASL959-98-8 Endosulfan I 7.50E-02 J 3.90E-01 J mg/kg BAZ-2028 2 / 2 3.30E-03 - 3.70E-02 3.90E-01 NA 4.70E+01 nc NA NA No BSL

TABLE 2.1.RMEOCCURRENCE, DISTRIBUTION AND SELECTION OF CHEMICALS OF POTENTIAL CONCERN


Qualifier Qualifier

Minimum MaximumConcentration Concentration






Qualifier Qualifier


1031-07-8 Endosulfan sulfate 8.60E-02 J 8.60E-02 J mg/kg BAZ-2028 1 / 2 1.80E-03 - 2.10E-02 8.60E-02 NA 4.70E+01 nc NA NA No BSL72-20-8 Endrin 1.80E-01 N,J 1.80E-01 N,J mg/kg BAZ-1077 1 / 2 3.40E-03 - 3.80E-02 1.80E-01 NA 1.90E+00 nc NA NA No BSL

1024-57-3 Heptachlor epoxide 3.90E-01 N,J 1.60E+00 N,J mg/kg BAZ-2028 2 / 2 3.40E-03 - 3.80E-02 1.60E+00 NA 7.00E-02 ca NA NA Yes ASL92-52-4 1,1'-Biphenyl 3.10E-02 J 6.05E-02 J mg/kg LTM04 2 / 29 4.00E-03 - 7.30E-02 6.05E-02 NA 4.70E+00 nc NA NA No BSL91-57-6 2-Methylnaphthalene 3.50E-02 J 1.77E-01 J mg/kg LTM04 3 / 29 8.10E-03 - 1.20E-01 1.77E-01 NA 2.40E+01 nc NA NA No BSL106-44-5 4-Methylphenol 7.10E-02 J 8.60E-02 J mg/kg BAZ-2028 2 / 2 1.50E-02 - 7.70E-02 8.60E-02 NA 6.30E+02 nc NA NA No BSL83-32-9 Acenaphthene 1.65E-02 J 2.57E-01 mg/kg LTM04 4 / 29 1.00E-02 - 1.10E-01 2.57E-01 NA 3.60E+02 nc NA NA No BSL208-96-8 Acenaphthylene 1.69E-02 J 4.30E-01 J mg/kg BAZ-2028 10 / 29 4.50E-03 - 7.00E-02 4.30E-01 NA 3.60E+02 nc NA NA No BSL120-12-7 Anthracene 1.91E-02 J 2.12E+00 mg/kg LTM04 16 / 29 3.70E-03 - 7.60E-02 2.12E+00 NA 1.80E+03 nc NA NA No BSL100-52-7 Benzaldehyde 3.18E-02 J 1.40E+00 J mg/kg BAZ-2028 7 / 29 8.00E-03 - 1.20E-01 1.40E+00 NA 1.70E+02 ca NA NA No BSL56-55-3 Benzo(a)anthracene 1.95E-02 J 1.50E+00 J mg/kg BAZ-1077 25 / 29 8.30E-03 - 7.10E-02 1.50E+00 NA 1.60E-01 ca NA NA Yes ASL50-32-8 Benzo(a)pyrene 1.40E-02 J 1.30E+00 J mg/kg BAZ-1077 24 / 29 9.20E-03 - 6.70E-02 1.30E+00 NA 1.60E-02 ca NA NA Yes ASL205-99-2 Benzo(b)fluoranthene 4.84E-02 J 2.10E+00 J mg/kg BAZ-1077 23 / 29 8.90E-03 - 7.30E-02 2.10E+00 NA 1.60E-01 ca NA NA Yes ASL191-24-2 Benzo(g,h,i)perylene 5.37E-02 8.70E-01 J mg/kg BAZ-1077 23 / 29 5.20E-03 - 8.10E-02 8.70E-01 NA 1.80E+02 nc NA NA No BSL207-08-9 Benzo(k)fluoranthene 2.48E-02 J 4.62E-01 mg/kg LTM04 21 / 29 9.60E-03 - 8.20E-02 4.62E-01 NA 1.60E+00 ca NA NA No BSL117-81-7 Bis(2-ethylhexyl)phthalate 7.92E-02 J 4.47E+01 mg/kg LTM04 24 / 29 1.50E-02 - 2.00E-01 4.47E+01 NA 3.90E+01 ca NA NA Yes ASL86-74-8 Carbazole 2.05E-02 J 1.96E-01 J mg/kg LTM04 4 / 29 4.80E-03 - 1.00E-01 1.96E-01 NA NA NA NA No NTX218-01-9 Chrysene 2.01E-02 J 1.88E+00 mg/kg LTM04 25 / 29 7.00E-03 - 7.40E-02 1.88E+00 NA 1.60E+01 ca NA NA No BSL53-70-3 Dibenz(a,h)anthracene 2.51E-02 J 2.27E-01 mg/kg LTM04 13 / 29 1.20E-02 - 7.50E-02 2.27E-01 NA 1.60E-02 ca NA NA Yes ASL132-64-9 Dibenzofuran 3.85E-01 3.85E-01 mg/kg LTM04 1 / 29 6.00E-03 - 7.80E-02 3.85E-01 NA 7.30E+00 nc NA NA No BSL131-11-3 Dimethyl phthalate 1.12E-01 J 4.41E-01 mg/kg SC-B.1 4 / 29 6.20E-03 - 8.60E-02 4.41E-01 NA 6.30E+01 nc NA NA No BSL84-74-2 Di-n-butyl phthalate 9.48E-01 9.48E-01 mg/kg WC-B.6 1 / 29 5.10E-03 - 9.90E-02 9.48E-01 NA 6.30E+02 nc NA NA No BSL117-84-0 Di-n-octyl phthalate 1.90E-01 J 2.50E-01 J mg/kg BAZ-1077 2 / 29 5.80E-03 - 1.10E-01 2.50E-01 NA 6.30E+01 nc NA NA No BSL206-44-0 Fluoranthene 4.32E-02 3.79E+00 mg/kg LTM04 25 / 29 5.30E-03 - 9.60E-02 3.79E+00 NA 2.40E+02 nc NA NA No BSL86-73-7 Fluorene 1.89E-02 J 2.80E-01 mg/kg LTM04 5 / 29 5.10E-03 - 7.20E-02 2.80E-01 NA 2.40E+02 nc NA NA No BSL193-39-5 Indeno(1,2,3-cd)pyrene 3.76E-02 J 8.90E-01 J mg/kg BAZ-1077 22 / 29 3.90E-03 - 7.60E-02 8.90E-01 NA 1.60E-01 ca NA NA Yes ASL78-59-1 Isophorone 6.13E-02 J 6.13E-02 J mg/kg WC-B.8 1 / 29 8.10E-03 - 5.90E-02 6.13E-02 NA 5.70E+02 ca NA NA No BSL91-20-3 Naphthalene 1.20E-01 J 1.20E-01 J mg/kg BAZ-2028 1 / 29 6.90E-03 - 6.00E-02 1.20E-01 NA 3.80E+00 ca NA NA No BSL86-30-6 N-Nitrosodiphenylamine 1.00E-01 J 1.00E-01 J mg/kg BAZ-1077 1 / 29 1.40E-02 - 1.30E-01 1.00E-01 NA 1.10E+02 ca NA NA No BSL85-01-8 Phenanthrene 3.21E-02 J 1.67E+00 mg/kg LTM04 23 / 29 4.80E-03 - 9.90E-02 1.67E+00 NA 1.80E+03 nc NA NA No BSL108-95-2 Phenol 3.20E-02 J 3.20E-02 J mg/kg BAZ-1077 1 / 29 1.40E-02 - 2.30E-01 3.20E-02 NA 1.90E+03 nc NA NA No BSL129-00-0 Pyrene 3.56E-02 3.84E+00 mg/kg LTM04 26 / 29 5.40E-03 - 8.40E-02 3.84E+00 NA 1.80E+02 nc NA NA No BSL95-50-1 1,2-Dichlorobenzene 2.40E-03 J 2.21E-02 J mg/kg SC-B.1 4 / 17 2.50E-04 - 5.80E-02 2.21E-02 NA 1.80E+02 nc NA NA No BSL






Qualifier Qualifier


541-73-1 1,3-Dichlorobenzene 1.65E-02 J 1.65E-02 J mg/kg SC-B.1 1 / 17 2.60E-04 - 5.90E-02 1.65E-02 NA 1.80E+02 nc NA NA No BSL106-46-7 1,4-Dichlorobenzene 1.78E-02 J 2.94E-01 J mg/kg SC-G.4 2 / 17 3.10E-04 - 7.20E-02 2.94E-01 NA 2.60E+00 ca NA NA No BSL67-64-1 Acetone 8.70E-03 J 1.34E+00 J mg/kg SC-G.4 10 / 17 2.10E-03 - 4.80E-01 1.34E+00 NA 6.10E+03 nc NA NA No BSL71-43-2 Benzene 4.60E-04 J 1.09E-01 J mg/kg SC-G.4 2 / 17 3.20E-04 - 7.30E-02 1.09E-01 NA 1.20E+00 ca NA NA No BSL75-15-0 Carbon Disulfide 1.00E-03 J 1.94E-01 J mg/kg SC-G.4 7 / 17 2.80E-04 - 6.50E-02 1.94E-01 NA 7.70E+01 nc NA NA No BSL108-90-7 Chlorobenzene 5.40E-03 8.19E-01 J mg/kg SC-G.4 4 / 17 3.20E-04 - 7.30E-02 8.19E-01 NA 2.80E+01 nc NA NA No BSL79-20-9 Methyl Acetate 3.00E+00 3.00E+00 mg/kg SC-G.4 1 / 17 7.70E-04 - 1.80E-01 3.00E+00 NA 7.80E+03 nc NA NA No BSL108-87-2 Methylcyclohexane 1.86E-01 J 1.86E-01 J mg/kg SC-G.4 1 / 17 6.10E-04 - 1.40E-01 1.86E-01 NA 1.17E+02 csat NA NA No BSL108-88-3 Toluene 5.80E-04 J 7.73E-02 J mg/kg SC-G.4 4 / 17 2.70E-04 - 6.30E-02 7.73E-02 NA 4.90E+02 nc NA NA No BSL

Notes:(1) Maximum concentration is used for screening.

COPC = Chemical of Potential Concern(2) Regional Screening Levels for Residential Soil (May 2016). Concentrations based on non-carcinogenic health effects are ARAR/TBC = Applicable or Relevant and Appropriate Requirement/

adjusted using HQ=0.1. To Be ConsideredThe SL for Antimony (metallic) was used as the SL for Antimony. ca = CarcinogenicThe SL for Beryllium and compounds was used as the SL for Beryllium. csat = Saturation ConcentrationThe SL for Cadmium (diet) was used as the SL for Cadmium. nc = NoncarcinogenicThe SL for Chromium (III) Insoluble Salts was used as the SL for Chromium. NA = Not availableThe SL for Manganese (non-diet) was used as the SL for Manganese. B = compound also detected in associated blankThe SL for Mercuric Chloride (and other Mercury salts) was used as the SL for Mercury. J = compound was detected below the reporting limit in the sampleThe SL for Nickel Soluble Salts was used as the SL for Nickel. N = presumptive evidence of compoundThe SL for Vanadium and compounds was used as the SL for Vanadium. SL = Screening LevelThe SL for Zinc (metallic) was used as the SL for Zinc. mg/kg = milligram per kilogramThe SL for 2,3,7,8-TCDD was used as the SL for PCB TEQ. PCB = Polychlorinated BiphenylThe SL for Aroclor-1254 was used as the SL for Total Aroclors. 2,3,7,8-TCDD TEQ = Tetrachlorodibenzo-p-dioxin Toxicity EquivalentThe SL for Aroclor-1254 was used as the SL for Total PCBs.The SL for Endosulfan was used as the SL for Endosulfan I.The SL for Endosulfan was used as the SL for Endosulfan I.The SL for Acenaphthene was used as the SL for Acenaphthylene.The SL for Pyrene was used as the SL for Benzo(g,h,i)peryleneNo screening level is available for carbazole. The HEAST cancer slope factor has been withdrawn.The SL for Di-n-octylphthalate was used as the SL for Dimethyl phthalate.The SL for Anthracene was used as the SL for Phenanthrene.The SL for 1,2-Dichlorobenzene was used as the SL for 1,3-Dichlorobenzene.The SL for Cyclohexane was used as the SL for methylcyclohexane

(3) Rationale Codes:Selection Reason: Above Screening Levels (ASL)Deletion Reason: Below Screening Level (BSL)

Essential Nutrient (NUT)No Toxicity Information (NTX)

Scenario Timeframe: Current/Future Medium: Surface Water Exposure Medium: Surface Water



Wetland 7429-90-5-D Aluminum, Dissolved 2.05E+01 J 2.05E+01 J ug/L MSW-24 1 / 8 1.90E+01 - 2.00E+02 2.05E+01 NA 2.00E+03 nc NA NA No BSLSurface Water 7440-36-0-D Antimony, Dissolved 4.90E-01 J 8.80E-01 J ug/L MSW-24 2 / 8 1.30E-01 - 6.00E+00 8.80E-01 NA 7.80E-01 nc NA NA Yes ASL

7440-38-2-D Arsenic, Dissolved 1.90E+00 J 3.80E+00 ug/L SL07 5 / 8 4.00E-01 - 3.00E+00 3.80E+00 NA 5.20E-02 ca NA NA Yes ASL (4)7440-39-3-D Barium, Dissolved 5.20E+01 J 9.28E+01 ug/L MSW-24 4 / 8 1.90E-01 - 2.00E+02 9.28E+01 NA 3.80E+02 nc NA NA No BSL7440-70-2-D Calcium, Dissolved 4.43E+04 J 1.29E+05 ug/L SL07 8 / 8 2.20E+01 - 5.00E+03 1.29E+05 NA NUT NA NA No NUT7440-47-3-D Chromium, Dissolved 1.10E+00 J 1.10E+00 J ug/L MSW-24 1 / 12 7.10E-01 - 1.00E+01 1.10E+00 NA 2.20E+03 nc NA NA No BSL7440-48-4-D Cobalt, Dissolved 2.50E+00 5.20E+00 ug/L MSW-24 2 / 8 5.80E-02 - 5.00E+01 5.20E+00 NA 6.00E-01 nc NA NA Yes ASL7439-89-6-D Iron, Dissolved 9.55E+01 J 5.94E+02 ug/L SW06 5 / 8 2.60E+01 - 1.30E+02 5.94E+02 NA 1.40E+03 nc NA NA No BSL7439-92-1-D Lead, Dissolved 3.70E-01 J 3.70E-01 J ug/L MSW-24 1 / 8 1.80E-01 - 3.00E+00 3.70E-01 NA 1.50E+01 nc NA NA No BSL7439-95-4-D Magnesium, Dissolved 2.67E+04 J 2.88E+05 ug/L SL07 8 / 8 1.70E+01 - 5.00E+03 2.88E+05 NA NUT NA NA No NUT7439-96-5-D Manganese, Dissolved 3.21E+02 6.50E+03 ug/L SW06 8 / 8 8.30E-01 - 1.50E+01 6.50E+03 NA 4.30E+01 nc NA NA Yes ASL (4)7439-97-6-D Mercury, Dissolved 4.40E-03 1.96E-02 J ug/L MSW-24 4 / 12 1.20E-04 - 2.00E-01 1.96E-02 NA 6.30E-02 nc NA NA No BSL7440-02-0-D Nickel, Dissolved 2.20E+00 3.10E+00 ug/L MSW-24 4 / 8 2.00E-01 - 1.00E+01 3.10E+00 NA 3.90E+01 nc NA NA No BSL7440-09-7-D Potassium, Dissolved 1.16E+04 1.10E+05 ug/L SL07 8 / 8 8.30E+00 - 1.00E+04 1.10E+05 NA NUT NA NA No NUT7440-23-5-D Sodium, Dissolved 2.31E+05 J 2.34E+06 ug/L SL07 8 / 8 6.90E+00 - 5.00E+04 2.34E+06 NA NUT NA NA No NUT7440-62-2-D Vanadium, Dissolved 1.10E+00 J 1.70E+00 J ug/L MSW-24 3 / 8 4.40E-01 - 5.00E+01 1.70E+00 NA 8.60E+00 nc NA NA No BSL7440-66-6-D Zinc, Dissolved 8.38E+01 J 8.38E+01 J ug/L MSW-24 1 / 7 2.30E+00 - 2.00E+01 8.38E+01 NA 6.00E+02 nc NA NA No BSL

57-12-5 Cyanide 1.60E+00 J 3.30E+00 J ug/L MSW-24 2 / 4 1.50E+00 - 1.60E+00 3.30E+00 NA 1.50E-01 nc NA NA Yes ASL7429-90-5 Aluminum 2.11E+02 2.64E+03 ug/L SW06 8 / 8 1.90E+01 - 2.00E+02 2.64E+03 NA 2.00E+03 nc NA NA Yes ASL7440-36-0 Antimony 3.40E-01 J 4.20E-01 J ug/L MSW-24 2 / 8 1.30E-01 - 6.00E+00 4.20E-01 NA 7.80E-01 nc NA NA No BSL7440-38-2 Arsenic 1.60E+00 J 1.13E+01 ug/L SW06 7 / 8 4.00E-01 - 3.00E+00 1.13E+01 NA 5.20E-02 ca NA NA Yes ASL7440-39-3 Barium 4.95E+01 J 9.71E+01 ug/L MSW-24 4 / 8 1.90E-01 - 2.00E+02 9.71E+01 NA 3.80E+02 nc NA NA No BSL7440-70-2 Calcium 4.42E+04 J 1.13E+05 J ug/L MSW-24 8 / 8 2.20E+01 - 5.00E+03 1.13E+05 NA NUT NA NA No NUT7440-47-3 Chromium 3.30E+00 J 1.14E+02 ug/L SW06 18 / 28 7.10E-01 - 1.00E+01 1.14E+02 NA 2.20E+03 nc NA NA No BSL7440-48-4 Cobalt 3.80E-01 J 3.80E-01 J ug/L MSW-24 1 / 8 5.80E-02 - 5.00E+01 3.80E-01 NA 6.00E-01 nc NA NA No BSL7440-50-8 Copper 3.30E+00 J 7.19E+01 ug/L SW06 8 / 8 2.90E-01 - 1.00E+01 7.19E+01 NA 8.00E+01 nc NA NA No BSL7439-89-6 Iron 5.54E+02 1.65E+04 ug/L SW06 8 / 8 2.60E+01 - 1.00E+02 1.65E+04 NA 1.40E+03 nc NA NA Yes ASL7439-92-1 Lead 3.10E+00 3.26E+01 ug/L SW06 8 / 8 1.80E-01 - 3.00E+00 3.26E+01 NA 1.50E+01 nc NA NA Yes ASL7439-95-4 Magnesium 2.78E+04 J 2.39E+05 ug/L SL07, SL08 8 / 8 1.70E+01 - 5.00E+03 2.39E+05 NA NUT NA NA No NUT7439-96-5 Manganese 3.16E+02 7.04E+03 ug/L SW06 8 / 8 8.30E-01 - 1.50E+01 7.04E+03 NA 4.30E+01 nc NA NA Yes ASL7439-97-6 Mercury 8.10E-02 J 5.60E+00 ug/L SW06 19 / 28 4.80E-03 - 4.00E-01 5.60E+00 NA 5.70E-01 nc NA NA Yes ASL22967-92-6 Methyl Mercury 5.10E-04 J 1.70E-03 ug/L MSW-24 4 / 4 5.00E-05 - 1.00E-04 1.70E-03 NA 2.00E-01 nc NA NA No BSL

22967-92-6-D Methyl Mercury, Dissolved 3.70E-04 1.20E-03 ug/L MSW-24 4 / 4 1.00E-05 - 2.00E-05 1.20E-03 NA 2.00E-01 nc NA NA No BSL7440-02-0 Nickel 2.60E+00 1.10E+01 ug/L SW06 5 / 8 2.00E-01 - 1.00E+01 1.10E+01 NA 3.90E+01 nc NA NA No BSL7440-09-7 Potassium 1.20E+04 9.55E+04 ug/L SL07 8 / 8 8.30E+00 - 1.00E+04 9.55E+04 NA NUT NA NA No NUT7440-22-4 Silver 4.70E+01 J 4.70E+01 J ug/L SL08 1 / 8 8.00E-02 - 1.00E+01 4.70E+01 NA 9.40E+00 nc NA NA Yes ASL7440-23-5 Sodium 2.42E+05 J 1.96E+06 ug/L SL08 8 / 8 6.90E+00 - 5.00E+04 1.96E+06 NA NUT NA NA No NUT



Qualifier Qualifier


Page 1 of 3






Qualifier Qualifier


7440-62-2 Vanadium 1.80E+00 J 2.40E+00 J ug/L MSW-24 4 / 8 4.40E-01 - 5.00E+01 2.40E+00 NA 8.60E+00 nc NA NA No BSL7440-66-6 Zinc 2.20E+01 J 1.27E+02 ug/L SW06 6 / 8 2.30E+00 - 2.00E+01 1.27E+02 NA 6.00E+02 nc NA NA No BSL_

6 Total Aroclors 6.10E-02 2.67E-01 ug/L MSW-24 2 / 12 2.40E-03 - 3.30E-01 2.67E-01 NA 7.80E-03 ca NA NA Yes ASL72-55-9 4-4’-DDE 1.30E-03 J 1.30E-03 J ug/L MSW-24 1 / 4 7.50E-04 - 7.90E-03 1.30E-03 NA 4.60E-02 ca NA NA No BSL50-29-3 4-4’-DDT 1.00E-03 J 3.60E-02 ug/L MSW-24 3 / 4 7.00E-04 - 7.40E-03 3.60E-02 NA 2.30E-01 ca NA NA No BSL309-00-2 Aldrin 4.20E-03 J 4.30E-03 N,J ug/L MSW-24 2 / 3 7.90E-04 - 8.30E-03 4.30E-03 NA 9.20E-04 ca NA NA Yes ASL319-85-7 BHC (beta) 2.60E-03 N,J 2.60E-03 N,J ug/L MSW-24 1 / 4 9.50E-04 - 1.00E-02 2.60E-03 NA 2.50E-02 ca NA NA No BSL58-89-9 BHC (gamma) 3.60E-03 J 5.60E-03 N,J ug/L MSW-24 3 / 4 7.60E-04 - 8.00E-03 5.60E-03 NA 4.20E-02 ca NA NA No BSL

5103-74-2 Chlordane (beta) 5.70E-03 3.40E-02 ug/L MSW-24 2 / 4 9.10E-04 - 9.60E-03 3.40E-02 NA 2.00E-02 ca NA NA No ASL33213-65-9 Endosulfan II 5.20E-03 N,J 5.20E-03 N,J ug/L MSW-24 2 / 4 9.30E-04 - 9.80E-03 5.20E-03 NA 1.00E+01 nc NA NA No BSL

72-20-8 Endrin 3.90E-03 J 3.90E-03 J ug/L MSW-24 1 / 4 9.10E-04 - 9.60E-03 3.90E-03 NA 2.30E-01 nc NA NA No BSL76-44-8 Heptachlor 9.00E-03 9.00E-03 ug/L MSW-24 1 / 2 2.00E-03 - 9.90E-03 9.00E-03 NA 1.40E-03 ca NA NA Yes ASL

1024-57-3 Heptachlor epoxide 3.40E-03 3.40E-03 J ug/L MSW-24 2 / 4 9.20E-04 - 9.70E-03 3.40E-03 NA 1.40E-03 ca NA NA Yes ASL51-28-5 2,4-Dinitrophenol 1.00E+00 J 1.00E+00 J ug/L MSW-24 1 / 12 5.80E-01 - 8.10E-01 1.00E+00 NA 3.90E+00 nc NA NA No BSL91-57-6 2-Methylnaphthalene 1.80E-02 J 1.80E-02 J ug/L MSW-24 1 / 12 1.20E-02 - 7.20E-01 1.80E-02 NA 3.60E+00 nc NA NA No BSL95-48-7 2-Methylphenol 1.90E-02 J 1.90E-02 J ug/L MSW-24 1 / 12 1.30E-02 - 1.20E+00 1.90E-02 NA 9.30E+01 nc NA NA No BSL83-32-9 Acenaphthene 1.60E-02 J 1.90E-02 J ug/L MSW-24 2 / 12 1.40E-02 - 4.00E-01 1.90E-02 NA 5.30E+01 nc NA NA No BSL98-86-2 Acetophenone 3.40E-02 J 7.90E-02 J ug/L MSW-24 3 / 12 2.10E-02 - 4.40E-01 7.90E-02 NA 1.90E+02 nc NA NA No BSL120-12-7 Anthracene 1.50E-02 J 2.90E-01 ug/L MSW-24 3 / 12 8.10E-03 - 1.80E-01 2.90E-01 NA 1.80E+02 nc NA NA No BSL100-52-7 Benzaldehyde 7.90E-01 J 1.40E+00 J ug/L MSW-24 7 / 12 4.70E-02 - 4.40E-01 1.40E+00 NA 1.90E+01 ca NA NA No BSL56-55-3 Benzo(a)anthracene 3.20E+00 3.20E+00 ug/L MSW-24 1 / 12 1.40E-02 - 1.30E-01 3.20E+00 NA 1.20E-02 ca NA NA Yes ASL50-32-8 Benzo(a)pyrene 2.40E+00 2.40E+00 ug/L MSW-24 1 / 12 1.10E-02 - 1.00E-01 2.40E+00 NA 3.40E-03 ca NA NA Yes ASL205-99-2 Benzo(b)fluoranthene 3.00E+00 3.00E+00 ug/L MSW-24 1 / 12 1.50E-02 - 2.70E-01 3.00E+00 NA 3.40E-02 ca NA NA Yes ASL191-24-2 Benzo(g,h,i)perylene 3.60E+00 3.60E+00 ug/L MSW-24 1 / 12 8.10E-03 - 1.30E-01 3.60E+00 NA 1.20E+01 nc NA NA No BSL207-08-9 Benzo(k)fluoranthene 3.70E+00 3.70E+00 ug/L MSW-24 1 / 12 1.50E-02 - 4.20E-01 3.70E+00 NA 3.40E-01 ca NA NA Yes ASL117-81-7 Bis(2-ethylhexyl)phthalate 9.10E-01 J 1.50E+00 B ug/L MSW-24 3 / 12 4.30E-02 - 8.70E-01 1.50E+00 NA 5.60E+00 ca NA NA No BSL85-68-7 Butyl benzyl phthalate 3.30E-01 J 1.20E+00 B ug/L MSW-24 2 / 12 1.40E-01 - 3.20E-01 1.20E+00 NA 1.60E+01 ca NA NA No BSL105-60-2 Caprolactam 1.50E+00 J 3.00E+00 J ug/L MSW-24 2 / 12 2.10E-01 - 1.30E+00 3.00E+00 NA 9.90E+02 nc NA NA No BSL86-74-8 Carbazole 1.40E-02 J 3.40E-02 J ug/L MSW-24 3 / 12 1.30E-02 - 1.80E-01 3.40E-02 NA NA NA NA No NTX218-01-9 Chrysene 3.10E+00 3.10E+00 ug/L MSW-24 1 / 12 1.00E-02 - 1.20E-01 3.10E+00 NA 3.40E+00 ca NA NA No BSL53-70-3 Dibenz(a,h)anthracene 3.80E+00 3.80E+00 ug/L MSW-24 1 / 12 1.20E-02 - 1.70E-01 3.80E+00 NA 3.40E-03 ca NA NA Yes ASL132-64-9 Dibenzofuran 2.10E-02 J 2.70E-02 J ug/L MSW-24 3 / 12 1.70E-02 - 3.30E-01 2.70E-02 NA 7.90E-01 nc NA NA No BSL84-66-2 Diethyl phthalate 1.60E-01 J 3.90E-01 J ug/L MSW-24 2 / 12 4.20E-02 - 1.80E-01 3.90E-01 NA 1.50E+03 nc NA NA No BSL84-74-2 Di-n-butyl phthalate 1.40E-01 J 2.90E-01 J ug/L MSW-24 3 / 12 2.80E-02 - 2.10E-01 2.90E-01 NA 9.00E+01 nc NA NA No BSL117-84-0 Di-n-octyl phthalate 1.40E+00 1.40E+00 ug/L MSW-24 1 / 12 1.50E-02 - 4.40E-01 1.40E+00 NA 2.00E+01 nc NA NA No BSL206-44-0 Fluoranthene 2.10E-02 J 7.70E-01 ug/L MSW-24 4 / 12 9.40E-03 - 1.90E-01 7.70E-01 NA 8.00E+01 nc NA NA No BSL86-73-7 Fluorene 1.90E-02 J 2.70E-02 J ug/L MSW-24 3 / 12 9.30E-03 - 2.90E-01 2.70E-02 NA 2.90E+01 nc NA NA No BSL193-39-5 Indeno(1,2,3-cd)pyrene 3.70E+00 3.70E+00 ug/L MSW-24 1 / 12 1.50E-02 - 1.40E-01 3.70E+00 NA 3.40E-02 ca NA NA Yes ASL

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Qualifier Qualifier


91-20-3 Naphthalene 3.30E-02 J 7.10E-02 J ug/L MSW-24 2 / 12 1.40E-02 - 4.70E-01 7.10E-02 NA 1.70E-01 ca NA NA No BSL85-01-8 Phenanthrene 6.80E-02 J 1.50E-01 J ug/L MSW-24 3 / 12 2.70E-02 - 2.30E-01 1.50E-01 NA 1.80E+02 nc NA NA No BSL108-95-2 Phenol 1.20E-01 J 1.20E-01 J ug/L MSW-24 1 / 12 2.20E-02 - 6.40E-01 1.20E-01 NA 5.80E+02 nc NA NA No BSL129-00-0 Pyrene 1.80E-02 J 7.70E-01 ug/L MSW-24 4 / 12 1.00E-02 - 1.70E-01 7.70E-01 NA 1.20E+01 nc NA NA No BSL95-50-1 1,2-Dichlorobenzene 2.90E-01 J 4.70E+00 ug/L MSW-24 4 / 8 1.50E-01 - 2.60E-01 4.70E+00 NA 3.00E+01 nc NA NA No BSL106-46-7 1,4-Dichlorobenzene 2.50E-01 J 2.50E-01 J ug/L MSW-24 1 / 8 2.10E-01 - 2.80E-01 2.50E-01 NA 4.80E-01 ca NA NA No BSL67-64-1 Acetone 3.40E+00 J 3.90E+00 J ug/L MSW-24 2 / 8 2.50E+00 - 2.90E+00 3.90E+00 NA 1.40E+03 nc NA NA No BSL71-43-2 Benzene 1.40E-01 J 5.70E-01 J ug/L MSW-24 3 / 8 1.10E-01 - 2.30E-01 5.70E-01 NA 4.60E-01 ca NA NA Yes ASL108-90-7 Chlorobenzene 1.70E+00 3.70E+00 ug/L MSW-24 3 / 8 1.40E-01 - 3.90E-01 3.70E+00 NA 7.80E+00 nc NA NA No BSL67-66-3 Chloroform 2.00E-01 J 2.00E-01 J ug/L MSW-24 1 / 8 1.70E-01 - 2.30E-01 2.00E-01 NA 2.20E-01 ca NA NA No BSL156-59-2 cis-1,2-Dichloroethene 2.60E-01 J 1.60E+00 ug/L MSW-24 5 / 8 2.20E-01 - 2.40E-01 1.60E+00 NA 3.60E+00 nc NA NA No BSL127-18-4 Tetrachloroethene 1.60E-01 J 6.60E-01 J ug/L MSW-24 4 / 8 1.50E-01 - 2.70E-01 6.60E-01 NA 4.10E+00 nc NA NA No BSL108-88-3 Toluene 1.80E-01 J 2.00E-01 J ug/L MSW-24 2 / 8 1.50E-01 - 3.00E-01 2.00E-01 NA 1.10E+02 nc NA NA No BSL79-01-6 Trichloroethene 1.90E-01 J 5.00E+00 ug/L MSW-24 4 / 8 1.40E-01 - 2.40E-01 5.00E+00 NA 2.80E-01 nc NA NA Yes ASL75-01-4 Vinyl Chloride 2.90E-01 J 2.90E-01 J ug/L MSW-24 1 / 8 2.30E-01 - 4.40E-01 2.90E-01 NA 1.90E-02 ca NA NA Yes ASL


COPC = Chemical of Potential Concern(2) Regional Screening Levels for Tapwater (May 2016). Concentrations based on non-carcinogenic health effects are ARAR/TBC = Applicable or Relevant and Appropriate Requirement/

adjusted using HQ=0.1. To Be ConsideredThe SL for Chromium (III) Insoluble Salts was used as the SL for Chromium. ca = CarcinogenicThe Federal Action Level for Lead was used as the SL. nc = NoncarcinogenicThe SL for Manganese (non-diet) was used as the SL for Manganese. NA = Not availableThe SL for Mercuric Chloride (and other Mercury salts) was used as the SL for Mercury. B = compound also detected in associated blankThe SL for Nickel Soluble Salts was used as the SL for Nickel. J = compound was detected below the reporting limit in the sampleThe SL for Zinc (metallic) was used as the SL for Zinc. N = presumptive evidence of compoundThe SL for Aroclor-1254 was used as the SL for Total Aroclors. SL = Screening LevelThe SL for Chlordane was used as the SL for Chlordane (beta). ug/L = microgram per literThe SL for Endosulfan was used as the SL for Endosulfan II.The SL for Pyrene was used as the SL for Benzo(g,h,i)peryleneNo screening level is available for carbazole. The HEAST cancer slope factor has been withdrawn.The SL for Anthracene was used as the SL for Phenanthrene.

(3) Rationale CodesSelection Reason: Above Screening Levels (ASL)Deletion Reason: Below Screening Level (BSL)


(4) The concentrations of arsenic and manganese were higher in the unfiltered samples; therefore, the filtered results are not further evaluated in the HHRA.

Page 3 of 3



Scenario Timeframe: Current/Future Medium: Sediment/Surface Water Exposure Medium: Fish



Fish TCDD_TEQ 2,3,7,8-TCDD TEQ 4.58E-05 1.19E-04 mg/kg WP04 10 / 10 - 1.19E-04 NA 1.90E-06 nc NA NA Yes ASL(white perch) PCBTotal Total PCBs 4.89E+00 9.03E+00 mg/kg WP04 7 / 7 - 9.03E+00 NA 5.60E-02 nc NA NA Yes ASL


COPC = Chemical of Potential Concern(2) Regional Screening Levels (RSLs) for Fish (calculated using the RSL calculator, May 2016). ARAR/TBC = Applicable or Relevant and Appropriate Requirement/

Concentrations based on non-carcinogenic health effects are adjusted using HQ=0.1. To Be ConsideredThe SL for 2,3,7,8-TCDD was used as the SL for PCB TEQ. nc = NoncarcinogenicThe SL for Aroclor-1254 was used as the SL for Total PCBs. NA = Not available

SL = Screening Level(3) Rationale Codes: mg/kg = milligram per kilogram

Selection Reason: Above Screening Levels (ASL) PCB = Polychlorinated Biphenyl2,3,7,8-TCDD TEQ = Tetrachlorodibenzo-p-dioxin Toxicity Equivalent


Qualifier Qualifier

Page 1 of 1

Scenario Timeframe: Current/Future Medium: Sediment (Ackermans South) Exposure Medium: Sediment



Wetland Sediment 7429-90-5 Aluminum 9.50E+03 J 1.70E+04 J mg/kg MRH-323 3 / 3 2.80E+01 - 1.30E+02 1.70E+04 NA 7.70E+03 nc NA NA Yes ASL(0 to 6 inches) 7440-36-0 Antimony 3.30E+00 J 3.70E+00 J mg/kg MRH-323 2 / 3 1.20E+00 - 1.30E+01 3.70E+00 NA 3.10E+00 nc NA NA Yes ASL

(Ackermans South) 7440-38-2 Arsenic 4.90E+01 J 6.80E+01 J mg/kg MRH-323 2 / 3 8.90E-01 - 1.30E+01 6.80E+01 NA 6.80E-01 ca NA NA Yes ASL7440-39-3 Barium 5.20E+02 J 2.80E+03 J mg/kg MRH-323 2 / 3 2.10E-01 - 1.30E+02 2.80E+03 NA 1.50E+03 nc NA NA Yes ASL7440-41-7 Beryllium 1.90E-01 J 7.20E-01 J mg/kg MRH-323 2 / 3 1.30E-01 - 3.20E+00 7.20E-01 NA 1.60E+01 nc NA NA No BSL7440-43-9 Cadmium 5.10E+00 J 5.10E+00 J mg/kg MRH-323 2 / 3 1.10E-01 - 3.20E+00 5.10E+00 NA 7.10E+00 nc NA NA No BSL7440-70-2 Calcium 4.00E+03 J 9.30E+03 J mg/kg MRH-323 3 / 3 4.70E+01 - 3.20E+03 9.30E+03 NA NUT NA NA No NUT7440-47-3 Chromium 3.00E+02 J 1.10E+03 J mg/kg MRH-323 3 / 3 5.90E-01 - 6.40E+00 1.10E+03 NA 1.20E+04 nc NA NA No BSL7440-48-4 Cobalt 2.30E+01 J 8.70E+01 J mg/kg MRH-323 2 / 3 4.70E-01 - 3.20E+01 8.70E+01 NA 2.30E+00 nc NA NA Yes ASL7440-50-8 Copper 9.00E+01 J 1.70E+02 J mg/kg MRH-323 3 / 3 2.20E+00 - 1.60E+01 1.70E+02 NA 3.10E+02 nc NA NA No BSL7439-89-6 Iron 1.32E+04 9.90E+04 J mg/kg MRH-323 3 / 3 1.40E+01 - 6.40E+01 9.90E+04 NA 5.50E+03 nc NA NA Yes ASL7439-92-1 Lead 1.10E+02 J 2.20E+02 J mg/kg MRH-323 3 / 3 5.60E-01 - 1.30E+01 2.20E+02 NA 4.00E+02 nc NA NA No BSL7439-95-4 Magnesium 5.18E+03 7.50E+03 J mg/kg MRH-323 3 / 3 1.50E+01 - 3.20E+03 7.50E+03 NA NUT NA NA No NUT7439-96-5 Manganese 3.57E+02 9.30E+04 J mg/kg MRH-323 3 / 3 2.20E-01 - 9.50E+00 9.30E+04 NA 1.80E+02 nc NA NA Yes ASL7439-97-6 Mercury 5.40E+00 J 6.20E+01 J mg/kg MRH-321 8 / 9 6.00E-02 - 7.30E-01 6.20E+01 NA 2.30E+00 nc NA NA Yes ASL22967-92-6 Methyl Mercury 3.70E-04 J 9.70E-02 J mg/kg BAZ-3038 8 / 8 1.20E-04 - 1.50E-03 9.70E-02 NA 7.80E-01 nc NA NA No BSL7440-02-0 Nickel 6.12E+01 1.60E+02 J mg/kg MRH-323 3 / 3 8.00E-01 - 2.50E+01 1.60E+02 NA 1.50E+02 nc NA NA Yes ASL7440-09-7 Potassium 2.30E+03 J 2.70E+03 J mg/kg MRH-323 2 / 3 1.80E+01 - 3.20E+03 2.70E+03 NA NUT NA NA No NUT7782-49-2 Selenium 3.40E+00 J 3.40E+00 J mg/kg MRH-323 1 / 3 1.30E+00 - 1.60E+01 3.40E+00 NA 3.90E+01 nc NA NA No BSL7440-22-4 Silver 3.20E+00 J 3.20E+00 J mg/kg MRH-323 1 / 3 3.00E-01 - 6.40E+00 3.20E+00 NA 3.90E+01 nc NA NA No BSL7440-23-5 Sodium 5.70E+03 J 1.00E+04 J mg/kg MRH-323 3 / 3 1.90E+02 - 6.40E+03 1.00E+04 NA NUT NA NA No NUT7440-62-2 Vanadium 5.40E+01 1.00E+02 J mg/kg MRH-323 3 / 3 3.50E-01 - 3.20E+01 1.00E+02 NA 3.90E+01 nc NA NA Yes ASL7440-66-6 Zinc 1.72E+02 1.40E+03 J mg/kg MRH-323 3 / 3 3.00E+00 - 1.30E+01 1.40E+03 NA 2.30E+03 nc NA NA No BSL

TCDD_TEQ 2,3,7,8-TCDD TEQ 5.47E-05 5.47E-05 mg/kg SC-G.3 1 / 1 - 5.47E-05 NA 4.80E-06 ca NA NA Yes ASLAroclorTotal Total Aroclors 2.15E-01 6.36E+01 mg/kg BAZ-3038 8 / 8 1.20E-03 - 1.20E-01 6.36E+01 NA 1.20E-01 nc NA NA Yes ASL

PCBTotal Total PCBs 2.41E+00 2.41E+00 mg/kg SC-G.3 1 / 1 - 2.41E+00 NA 1.20E-01 nc NA NA Yes ASL72-54-8 4,4'-DDD 6.10E-03 J 6.10E-03 J mg/kg MRH-323 1 / 1 1.00E-04 - 1.00E-04 6.10E-03 NA 2.30E+00 ca NA NA No BSL72-55-9 4-4’-DDE 6.30E-03 N,J 2.80E-02 J mg/kg MRH-323 2 / 2 9.20E-05 - 1.20E-04 2.80E-02 NA 2.00E+00 ca NA NA No BSL

5103-71-9 Alpha Chlordane 7.50E-03 J 7.50E-03 J mg/kg MRH-323 1 / 2 1.20E-04 - 1.60E-04 7.50E-03 NA 1.70E+00 ca NA NA No BSL319-84-6 BHC (alpha) 4.10E-03 J 4.10E-03 J mg/kg MRH-323 1 / 2 1.00E-04 - 1.30E-04 4.10E-03 NA 8.60E-02 ca NA NA No BSL319-85-7 BHC (beta) 4.40E-03 N,J 5.40E-03 N,J mg/kg MRH-323 2 / 2 1.60E-04 - 2.10E-04 5.40E-03 NA 3.00E-01 ca NA NA No BSL319-86-8 BHC (delta) 5.40E-03 J 5.40E-03 J mg/kg MRH-323 1 / 2 9.40E-05 - 1.20E-04 5.40E-03 NA 8.60E-02 ca NA NA No BSL58-89-9 BHC (gamma) 5.00E-03 J 5.00E-03 J mg/kg MRH-323 1 / 1 1.40E-04 - 1.40E-04 5.00E-03 NA 5.70E-01 ca NA NA No BSL60-57-1 Dieldrin 2.90E-03 N,J 9.30E-03 J mg/kg MRH-323 2 / 2 1.00E-04 - 1.30E-04 9.30E-03 NA 3.40E-02 ca NA NA No BSL

Qualifier Qualifier




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Qualifier Qualifier




959-98-8 Endosulfan I 3.80E-03 J 4.20E-03 J mg/kg MRH-323 2 / 2 1.20E-04 - 1.50E-04 4.20E-03 NA 4.70E+01 nc NA NA No BSL33213-65-9 Endosulfan II 3.30E-03 N,J 3.30E-03 N,J mg/kg MRH-323 1 / 1 1.40E-04 - 1.40E-04 3.30E-03 NA 4.70E+01 nc NA NA No BSL1031-07-8 Endosulfan sulfate 7.10E-03 J 7.10E-03 J mg/kg MRH-323 1 / 1 8.30E-05 - 8.30E-05 7.10E-03 NA 4.70E+01 nc NA NA No BSL

72-20-8 Endrin 1.20E-02 J 2.30E-02 N,J mg/kg MRH-323 2 / 2 1.20E-04 - 1.50E-04 2.30E-02 NA 1.90E+00 nc NA NA No BSL7421-93-4 Endrin aldehyde 9.70E-04 J 1.30E-03 J mg/kg MRH-323 2 / 2 1.20E-04 - 1.50E-04 1.30E-03 NA 1.90E+00 nc NA NA No BSL53494-70-5 Endrin ketone 3.60E-03 J 1.10E-02 J mg/kg MRH-323 2 / 2 9.50E-05 - 1.20E-04 1.10E-02 NA 1.90E+00 nc NA NA No BSL5566-34-7 gamma-Chlordane 2.20E-02 J 6.60E-02 J mg/kg MRH-323 2 / 2 1.20E-04 - 1.60E-04 6.60E-02 NA 1.70E+00 ca NA NA No BSL1024-57-3 Heptachlor epoxide 1.20E-02 N,J 2.90E-02 N,J mg/kg MRH-323 2 / 2 1.20E-04 - 1.50E-04 2.90E-02 NA 7.00E-02 ca NA NA No BSL

72-43-5 Methoxychlor 2.00E-02 J 4.00E-02 J mg/kg MRH-323 2 / 2 1.30E-04 - 1.70E-04 4.00E-02 NA 3.20E+01 nc NA NA No BSL92-52-4 1,1'-Biphenyl 2.20E-02 J 2.20E-02 J mg/kg MRH-323 1 / 2 1.80E-02 - 2.20E-02 2.20E-02 NA 4.70E+00 nc NA NA No BSL91-57-6 2-Methylnaphthalene 3.90E-02 J 4.50E-02 J mg/kg MRH-323 2 / 2 3.60E-03 - 4.50E-03 4.50E-02 NA 2.40E+01 nc NA NA No BSL95-48-7 2-Methylphenol 1.90E-02 J 1.90E-02 J mg/kg MRH-323 1 / 2 1.40E-02 - 1.70E-02 1.90E-02 NA 3.20E+02 nc NA NA No BSL106-47-8 4-Chloroaniline 6.60E-02 J 6.60E-02 J mg/kg MRH-323 1 / 2 1.60E-02 - 2.00E-02 6.60E-02 NA 2.70E+00 ca NA NA No BSL83-32-9 Acenaphthene 2.60E-02 J 3.00E-02 J mg/kg MRH-323 2 / 2 3.80E-03 - 4.80E-03 3.00E-02 NA 3.60E+02 nc NA NA No BSL208-96-8 Acenaphthylene 5.80E-02 J 1.70E-01 J mg/kg MRH-323 2 / 2 4.50E-03 - 5.70E-03 1.70E-01 NA 3.60E+02 nc NA NA No BSL98-86-2 Acetophenone 4.00E-02 J 4.00E-02 J mg/kg MRH-323 1 / 2 1.60E-02 - 2.10E-02 4.00E-02 NA 7.80E+02 nc NA NA No BSL120-12-7 Anthracene 7.20E-02 J 1.30E-01 J mg/kg MRH-323 2 / 2 3.90E-03 - 4.90E-03 1.30E-01 NA 1.80E+03 nc NA NA No BSL100-52-7 Benzaldehyde 1.20E-01 J 4.40E-01 J mg/kg MRH-323 2 / 2 3.00E-02 - 3.80E-02 4.40E-01 NA 1.70E+02 ca NA NA No BSL56-55-3 Benzo(a)anthracene 5.90E-01 J 6.40E-01 J mg/kg MRH-323 2 / 2 5.00E-03 - 6.30E-03 6.40E-01 NA 1.60E-01 ca NA NA Yes ASL50-32-8 Benzo(a)pyrene 6.20E-01 J 7.80E-01 J mg/kg MRH-323 2 / 2 4.00E-03 - 5.00E-03 7.80E-01 NA 1.60E-02 ca NA NA Yes ASL205-99-2 Benzo(b)fluoranthene 8.50E-01 J 1.00E+00 J mg/kg MRH-323 2 / 2 6.20E-03 - 7.90E-03 1.00E+00 NA 1.60E-01 ca NA NA Yes ASL191-24-2 Benzo(g,h,i)perylene 5.20E-01 J 6.20E-01 J mg/kg MRH-323 2 / 2 3.90E-03 - 5.00E-03 6.20E-01 NA 1.80E+02 nc NA NA No BSL207-08-9 Benzo(k)fluoranthene 2.50E-01 J 5.30E-01 J mg/kg MRH-323 2 / 2 8.00E-03 - 1.00E-02 5.30E-01 NA 1.60E+00 ca NA NA No BSL117-81-7 Bis(2-ethylhexyl)phthalate 3.50E-01 J 9.60E-01 J mg/kg MRH-323 2 / 2 3.20E-02 - 4.00E-02 9.60E-01 NA 3.90E+01 ca NA NA No BSL85-68-7 Butyl benzyl phthalate 1.30E-01 J 1.30E-01 J mg/kg MRH-323 1 / 2 2.70E-02 - 3.40E-02 1.30E-01 NA 2.90E+02 ca NA NA No BSL86-74-8 Carbazole 3.80E-02 J 7.10E-02 J mg/kg MRH-323 2 / 2 3.70E-03 - 4.60E-03 7.10E-02 NA NA NA NA No NTX218-01-9 Chrysene 6.70E-01 J 8.30E-01 J mg/kg MRH-323 2 / 2 4.70E-03 - 6.00E-03 8.30E-01 NA 1.60E+01 ca NA NA No BSL53-70-3 Dibenz(a,h)anthracene 1.20E-01 J 2.70E-01 J mg/kg MRH-323 2 / 2 4.40E-03 - 5.60E-03 2.70E-01 NA 1.60E-02 ca NA NA Yes ASL132-64-9 Dibenzofuran 2.80E-02 J 3.40E-02 J mg/kg MRH-323 2 / 2 2.00E-02 - 2.50E-02 3.40E-02 NA 7.30E+00 nc NA NA No BSL84-74-2 Di-n-butyl phthalate 5.10E-02 J 5.10E-02 J mg/kg MRH-323 1 / 2 2.50E-02 - 3.10E-02 5.10E-02 NA 6.30E+02 nc NA NA No BSL117-84-0 Di-n-octyl phthalate 5.10E-02 J 5.10E-02 J mg/kg MRH-323 1 / 2 2.10E-02 - 2.60E-02 5.10E-02 NA 6.30E+01 nc NA NA No BSL206-44-0 Fluoranthene 6.60E-01 J 1.10E+00 J mg/kg MRH-323 2 / 2 4.20E-03 - 5.40E-03 1.10E+00 NA 2.40E+02 nc NA NA No BSL

Page 2 of 3




Qualifier Qualifier




86-73-7 Fluorene 3.60E-02 J 4.60E-02 J mg/kg MRH-323 2 / 2 5.20E-03 - 6.60E-03 4.60E-02 NA 2.40E+02 nc NA NA No BSL193-39-5 Indeno(1,2,3-cd)pyrene 4.80E-01 J 6.50E-01 J mg/kg MRH-323 2 / 2 4.10E-03 - 5.20E-03 6.50E-01 NA 1.60E-01 ca NA NA Yes ASL91-20-3 Naphthalene 7.50E-02 J 8.70E-02 J mg/kg MRH-323 2 / 2 3.40E-03 - 4.30E-03 8.70E-02 NA 3.80E+00 ca NA NA No BSL86-30-6 N-Nitrosodiphenylamine 2.60E-02 J 1.10E-01 J mg/kg MRH-323 2 / 2 1.80E-02 - 2.30E-02 1.10E-01 NA 1.10E+02 ca NA NA No BSL85-01-8 Phenanthrene 2.70E-01 J 3.90E-01 J mg/kg MRH-323 2 / 2 6.30E-03 - 8.00E-03 3.90E-01 NA 1.80E+03 nc NA NA No BSL108-95-2 Phenol 1.00E-02 J 1.00E-02 J mg/kg MRH-323 1 / 2 4.70E-03 - 5.90E-03 1.00E-02 NA 1.90E+03 nc NA NA No BSL129-00-0 Pyrene 7.80E-01 J 9.10E-01 J mg/kg MRH-323 2 / 2 4.00E-03 - 5.10E-03 9.10E-01 NA 1.80E+02 nc NA NA No BSL


COPC = Chemical of Potential Concern(2) Regional Screening Levels for Residential Soil (May 2016). Concentrations based on non-carcinogenic health effects are ARAR/TBC = Applicable or Relevant and Appropriate Requirement/

adjusted using HQ=0.1. To Be ConsideredThe SL for Antimony (metallic) was used as the SL for Antimony. ca = CarcinogenicThe SL for Beryllium and compounds was used as the SL for Beryllium. csat = Saturation ConcentrationThe SL for Cadmium (diet) was used as the SL for Cadmium. nc = NoncarcinogenicThe SL for Chromium (III) Insoluble Salts was used as the SL for Chromium. NA = Not availableThe SL for Manganese (non-diet) was used as the SL for Manganese. J = compound was detected below the reporting limit in the sampleThe SL for Mercuric Chloride (and other Mercury salts) was used as the SL for Mercury. N = presumptive evidence of compoundThe SL for Nickel Soluble Salts was used as the SL for Nickel. SL = Screening LevelThe SL for Vanadium and compounds was used as the SL for Vanadium. mg/kg = milligram per kilogramThe SL for Zinc (metallic) was used as the SL for Zinc. PCB = Polychlorinated BiphenylThe SL for 2,3,7,8-TCDD was used as the SL for PCB TEQ. 2,3,7,8-TCDD TEQ = Tetrachlorodibenzo-p-dioxin Toxicity EquivalentThe SL for Aroclor-1254 was used as the SL for Total Aroclors.The SL for Aroclor-1254 was used as the SL for Total PCBs.Used Chlordane (12789-03-6) as a surrogateUsed BHC (alpha) (319-84-6) as a surrogateUsed Endosulfan (115-29-7) as a surrogateUsed Endosulfan (115-29-7) as a surrogateUsed Endosulfan (115-29-7) as a surrogateUsed Endrin (72-20-8) as a surrogateUsed Endrin (72-20-8) as a surrogateUsed Chlordane (12789-03-6) as a surrogateThe SL for Acenaphthene was used as the SL for Acenaphthylene.The SL for Pyrene was used as the SL for Benzo(g,h,i)peryleneNo screening level is available for carbazole. The HEAST cancer slope factor has been withdrawn.The SL for Anthracene was used as the SL for Phenanthrene.

(3) Rationale Codes:Selection Reason: Above Screening Levels (ASL)Deletion Reason: Below Screening Level (BSL)


Page 3 of 3


Exposure Point Chemical Units Arithmeticof Mean

PotentialConcern Value Units Statistic Rationale

Wetland Sediment Aluminum mg/kg 1.14E+04 1.32E+04 N 2.71E+04 1.32E+04 mg/kg 95% Student's-t UCL 2(0 to 6 inches) Antimony mg/kg 3.11E+01 2.24E+01 1.44E+02 2.24E+01 mg/kg 95% KM (Chebyshev) UCL 4

(On-site) Arsenic mg/kg 2.47E+01 3.24E+01 G 1.46E+02 3.24E+01 mg/kg 95% GROS Adjusted Gamma UCL 3Barium mg/kg 3.95E+02 6.46E+02 2.12E+03 J 6.46E+02 mg/kg 95% KM (Chebyshev) UCL 4

Cadmium mg/kg 6.96E+00 7.10E+00 G 3.16E+01 7.10E+00 mg/kg 95% GROS Adjusted Gamma UCL 3Chromium mg/kg 1.08E+03 2.69E+03 1.26E+04 2.69E+03 mg/kg 95% Chebyshev (Mean, Sd) UCL 4

Cobalt mg/kg 2.08E+01 1.97E+01 7.70E+01 1.97E+01 mg/kg 95% KM (BCA) UCL 4Copper mg/kg 1.47E+02 2.10E+02 G 1.35E+03 2.10E+02 mg/kg 95% Adjusted Gamma UCL 3

Iron mg/kg 2.57E+04 3.05E+04 N 9.42E+04 3.05E+04 mg/kg 95% Student's-t UCL 2Lead mg/kg 1.63E+02 2.34E+02 G 9.36E+02 1.63E+02 mg/kg Arithmetic Mean 7

Manganese mg/kg 2.94E+03 8.81E+03 5.21E+04 J 8.81E+03 mg/kg 95% Chebyshev (Mean, Sd) UCL 4Mercury mg/kg 2.06E+01 4.20E+01 1.43E+02 4.20E+01 mg/kg 95% KM (Chebyshev) UCL 4Nickel mg/kg 6.43E+01 8.89E+01 G 4.03E+02 J 8.89E+01 mg/kg 95% GROS Adjusted Gamma UCL 3

Thallium mg/kg 3.93E+01 3.45E+01 2.18E+02 J 3.45E+01 mg/kg 95% KM (Chebyshev) UCL 4Vanadium mg/kg 4.92E+01 5.35E+01 1.31E+02 5.35E+01 mg/kg 95% KM (t) UCL 4

Zinc mg/kg 5.66E+02 8.29E+02 G 4.33E+03 8.29E+02 mg/kg 95% Adjusted Gamma UCL 32,3,7,8-TCDD TEQ mg/kg 2.60E-04 2.04E-03 2.71E-03 2.04E-03 mg/kg 99% Chebyshev (Mean, Sd) UCL 4

Total Aroclors mg/kg 3.36E+01 1.78E+02 5.50E+02 1.78E+02 mg/kg 99% KM (Chebyshev) UCL 4Total PCBs mg/kg 2.83E+01 2.61E+02 3.54E+02 2.61E+02 mg/kg 99% Chebyshev (Mean, Sd) UCL 4

Aldrin mg/kg 3.00E+00 NA 3.00E+00 J 3.00E+00 mg/kg Max 5BHC (beta) mg/kg 6.70E+00 NA 6.70E+00 J 6.70E+00 mg/kg Max 5

Heptachlor epoxide mg/kg 9.95E-01 NA 1.60E+00 N,J 1.60E+00 mg/kg Max 5Benzo(a)anthracene mg/kg 2.74E-01 6.67E-01 1.50E+00 J 6.67E-01 mg/kg 97.5% KM (Chebyshev) UCL 4

Benzo(a)pyrene mg/kg 3.08E-01 6.75E-01 1.30E+00 J 6.75E-01 mg/kg 97.5% KM (Chebyshev) UCL 4Benzo(b)fluoranthene mg/kg 4.29E-01 9.70E-01 2.10E+00 J 9.70E-01 mg/kg 97.5% KM (Chebyshev) UCL 4

Bis(2-ethylhexyl)phthalate mg/kg 4.62E+00 2.09E+01 4.47E+01 2.09E+01 mg/kg 99% KM (Chebyshev) UCL 4Dibenz(a,h)anthracene mg/kg 1.03E-01 8.63E-02 2.27E-01 8.63E-02 mg/kg 95% KM (t) UCL 4Indeno(1,2,3-cd)pyrene mg/kg 2.37E-01 2.66E-01 8.90E-01 J 2.66E-01 mg/kg 95% KM (BCA) UCL 4

Notes:ProUCL, Version 5.0.00 used to determine distribution of data using the Shapiro-Wilk W Test. ProUCL used to calculate RME EPC, following recommendationsbased on distribution and standard deviation in users guide (EPA. September 2013. ProUCL, Version 5.0.00 Prepared by Lockheed Martin Environmental Services).Statistics: KM (BCA) - nonparametric UCL based upon Kaplan-Meier estimates using the Bias Corrected Accelerated method.

KM (Chebyshev) - nonparametric UCL based upon Kaplan-Meier estimates using the Chebyshev inequality.KM (t) - nonparametric UCL based upon Kaplan-Meier estimates using the Student’s t-distribution critical valueChebyshev (mean, SD) - nonparametric UCL based on Chebyshev inequality.Student's-t - parametric UCL based on Student's t statistic assuming normal distribution.Adjusted Gamma - parametric UCL adjusted for level significance assuming gamma distribution.GROS Adjusted Gamma - parametric UCL based on the regression on order statistics (ROS) method for a gamma distribution.Max - Maximum Detected Concentration

(1) Shapiro-Wilk W/Lilliefors Test indicates data are log-normally distributed.(2) Shapiro-Wilk W/Lilliefors Test indicates data are normally distributed.(3) Anderson-Darling and/or Kolmogorov-Smirnov Tests indicate data are gamma distributed.(4) Distribution tests are inconclusive (data are not normal, log-normal, or gamma-distributed).(5) The maximum detected concentration was used as the EPC because there are less than 4 detects or 8 samples.(6) The maximum detected concentration was used as the EPC because the UCL was greater than the Max.(7) The arithmetic mean is used as the EPC for lead.mg/kg = milligram per kilogramNA = Not available or not applicableUCL = Upper confidence limitDistributions:G = Gamma distributionN = Normal distributionQualifiers:J = compound was detected below the reporting limit in the sampleN = presumptive evidence of a compound

TABLE 3.1.RMEMEDIUM-SPECIFIC EXPOSURE POINT CONCENTRATION SUMMARY


Concentration(Qualifier)

95% UCL(Distribution)

Exposure Point ConcentrationMaximum




Wetland Aluminum µg/L 6.03E+02 1.88E+03 2.64E+03 1.88E+03 µg/L 95% Chebyshev (Mean, Sd) UCL 4Surface Water Antimony, Dissolved µg/L 6.85E-01 NA 8.80E-01 J 8.80E-01 µg/L Max 5

Arsenic µg/L 4.10E+00 7.27E+00 G 1.13E+01 7.27E+00 µg/L 95% Adjusted Gamma KM-UCL 3Cobalt, Dissolved µg/L 3.85E+00 NA 5.20E+00 5.20E+00 µg/L Max 5

Cyanide µg/L 2.45E+00 NA 3.30E+00 J 3.30E+00 µg/L Max 5Iron µg/L 3.10E+03 2.83E+04 1.65E+04 1.65E+04 µg/L Max 6Lead µg/L 8.16E+00 2.36E+01 3.26E+01 8.16E+00 µg/L Arithmetic Mean 7

Manganese µg/L 1.27E+03 1.95E+04 7.04E+03 7.04E+03 µg/L Max 6Mercury µg/L 7.16E-01 9.74E-01 5.60E+00 9.74E-01 µg/L 95% KM (BCA) UCL 4Silver µg/L 4.70E+01 NA 4.70E+01 J 4.70E+01 µg/L Max 5

Total Aroclors µg/L 1.64E-01 NA 2.67E-01 2.67E-01 µg/L Max 5Aldrin µg/L 4.25E-03 NA 4.30E-03 N,J 4.30E-03 µg/L Max 5

Chlordane (beta) µg/L 1.99E-02 NA 3.40E-02 3.40E-02 µg/L Max 5Heptachlor µg/L 9.00E-03 NA 9.00E-03 9.00E-03 µg/L Max 5

Heptachlor epoxide µg/L 3.40E-03 NA 3.40E-03 J 3.40E-03 µg/L Max 5Benzo(a)anthracene µg/L 3.20E+00 NA 3.20E+00 3.20E+00 µg/L Max 5

Benzo(a)pyrene µg/L 2.40E+00 NA 2.40E+00 2.40E+00 µg/L Max 5Benzo(b)fluoranthene µg/L 3.00E+00 NA 3.00E+00 3.00E+00 µg/L Max 5Benzo(k)fluoranthene µg/L 3.70E+00 NA 3.70E+00 3.70E+00 µg/L Max 5

Dibenz(a,h)anthracene µg/L 3.80E+00 NA 3.80E+00 3.80E+00 µg/L Max 5Indeno(1,2,3-cd)pyrene µg/L 3.70E+00 NA 3.70E+00 3.70E+00 µg/L Max 5

Benzene µg/L 2.83E-01 NA 5.70E-01 J 5.70E-01 µg/L Max 5Trichloroethene µg/L 1.77E+00 2.29E+00 5.00E+00 2.29E+00 µg/L 95% KM (t) UCL 4Vinyl Chloride µg/L 2.90E-01 NA 2.90E-01 J 2.90E-01 µg/L Max 5

Notes:ProUCL, Version 5.0.00 used to determine distribution of data using the Shapiro-Wilk W Test. ProUCL used to calculate RME EPC, following recommendationsbased on distribution and standard deviation in users guide (EPA. September 2013. ProUCL, Version 5.0.00 Prepared by Lockheed Martin Environmental Services).Statistics: KM (BCA) - nonparametric UCL based upon Kaplan-Meier estimates using the Bias Corrected Accelerated method.

KM (t) - nonparametric UCL based upon Kaplan-Meier estimates using the Student’s t-distribution critical valueChebyshev (mean, SD) - nonparametric UCL based on Chebyshev inequality.Adjusted Gamma - parametric UCL adjusted for level significance assuming gamma distribution.Max - Maximum Detected Concentration

(1) Shapiro-Wilk W/Lilliefors Test indicates data are log-normally distributed.(2) Shapiro-Wilk W/Lilliefors Test indicates data are normally distributed.(3) Anderson-Darling and/or Kolmogorov-Smirnov Tests indicate data are gamma distributed.(4) Distribution tests are inconclusive (data are not normal, log-normal, or gamma-distributed).(5) The maximum detected concentration was used as the EPC because there are less than 4 detects or 8 samples.(6) The maximum detected concentration was used as the EPC because the UCL was greater than the Max.(7) The arithmetic mean is used as the EPC for lead.G = Gamma distributionJ = compound was detected below the reporting limit in the sampleN = presumptive evidence of a compoundNA = Not available or not applicableUCL = Upper confidence limitµg/L = microgram per liter



Concentration(Qualifier)


Exposure Point ConcentrationMaximum

Scenario Timeframe: Current/Future Medium: Sediment/Surface Water Exposure Medium: Fish



Fish 2,3,7,8-TCDD TEQ mg/kg 8.27E-05 9.93E-05 N 1.19E-04 9.93E-05 mg/kg 95% Student's-t UCL 2(white perch)* Total PCBs mg/kg 7.13E+00 8.08E+00 N 9.03E+00 9.03E+00 mg/kg Max 5

Notes:ProUCL, Version 5.0.00 used to determine distribution of data using the Shapiro-Wilk W Test. ProUCL used to calculate RME EPC, following recommendationsbased on distribution and standard deviation in users guide (EPA. September 2013. ProUCL, Version 5.0.00 Prepared by Lockheed Martin Environmental Services).Statistics: Student's-t - parametric UCL based on Student's t statistic assuming normal distribution. Max - Maximum Detected Concentration

* Analytical data for white perch are presented on a wet weight basis.(1) Shapiro-Wilk W/Lilliefors Test indicates data are log-normally distributed.(2) Shapiro-Wilk W/Lilliefors Test indicates data are normally distributed.(3) Anderson-Darling and/or Kolmogorov-Smirnov Tests indicate data are gamma distributed.(4) Distribution tests are inconclusive (data are not normal, log-normal, or gamma-distributed).(5) The maximum detected concentration was used as the EPC because there are less than 4 detects or 8 samples.

N = Normal distributionmg/kg = Milligram per kilogramUCL = Upper confidence limit

(Qualifier)




ConcentrationExposure Point ConcentrationMaximum




Wetland Sediment Aluminum mg/kg 1.23E+04 NA 1.70E+04 J 1.70E+04 mg/kg Max 5(0 to 6 inches) Antimony mg/kg 3.50E+00 NA 3.70E+00 J 3.70E+00 mg/kg Max 5

(Ackermans South) Arsenic mg/kg 5.85E+01 NA 6.80E+01 J 6.80E+01 mg/kg Max 5Barium mg/kg 1.66E+03 NA 2.80E+03 J 2.80E+03 mg/kg Max 5Cobalt mg/kg 5.50E+01 NA 8.70E+01 J 8.70E+01 mg/kg Max 5

Iron mg/kg 4.64E+04 NA 9.90E+04 J 9.90E+04 mg/kg Max 5Manganese mg/kg 3.14E+04 NA 9.30E+04 J 9.30E+04 mg/kg Max 5

Mercury mg/kg 2.52E+01 3.55E+01 6.20E+01 J 3.55E+01 mg/kg 95% KM (t) UCL 4Nickel mg/kg 1.01E+02 NA 1.60E+02 J 1.60E+02 mg/kg Max 5

Vanadium mg/kg 8.13E+01 NA 1.00E+02 J 1.00E+02 mg/kg Max 52,3,7,8-TCDD TEQ mg/kg 5.47E-05 NA 5.47E-05 5.47E-05 mg/kg Max 5

Total Aroclors mg/kg 8.77E+00 8.68E+01 6.36E+01 6.36E+01 mg/kg Max 6Total PCBs mg/kg 2.41E+00 NA 2.41E+00 2.41E+00 mg/kg Max 5

Benzo(a)anthracene mg/kg 6.15E-01 NA 6.40E-01 J 6.40E-01 mg/kg Max 5Benzo(a)pyrene mg/kg 7.00E-01 NA 7.80E-01 J 7.80E-01 mg/kg Max 5

Benzo(b)fluoranthene mg/kg 9.25E-01 NA 1.00E+00 J 1.00E+00 mg/kg Max 5Dibenz(a,h)anthracene mg/kg 1.95E-01 NA 2.70E-01 J 2.70E-01 mg/kg Max 5Indeno(1,2,3-cd)pyrene mg/kg 5.65E-01 NA 6.50E-01 J 6.50E-01 mg/kg Max 5

Notes:ProUCL, Version 5.0.00 used to determine distribution of data using the Shapiro-Wilk W Test. ProUCL used to calculate RME EPC, following recommendationsbased on distribution and standard deviation in users guide (EPA. September 2013. ProUCL, Version 5.0.00 Prepared by Lockheed Martin Environmental Services).Statistics: KM (t) - nonparametric UCL based upon Kaplan-Meier estimates using the Student’s t-distribution critical value

Max - Maximum Detected Concentration(1) Shapiro-Wilk W/Lilliefors Test indicates data are log-normally distributed.(2) Shapiro-Wilk W/Lilliefors Test indicates data are normally distributed.(3) Anderson-Darling and/or Kolmogorov-Smirnov Tests indicate data are gamma distributed.(4) Distribution tests are inconclusive (data are not normal, log-normal, or gamma-distributed).(5) The maximum detected concentration was used as the EPC because there are less than 4 detects or 8 samples.(6) The maximum detected concentration was used as the EPC because the UCL was greater than the Max.

J = compound was detected below the reporting limit in the samplemg/kg = milligram per kilogramUCL = Upper confidence limit

(Distribution) Concentration(Qualifier)



95% UCL Maximum Exposure Point Concentration

TABLE 4.1.RMEVALUES USED FOR DAILY INTAKE CALCULATIONS

REASONABLE MAXIMUM EXPOSUREOU2, Universal Oil Products (UOP), East Rutherford, New Jersey

Scenario Timeframe: Current/Future Medium: SedimentExposure Medium: Sediment

Exposure Route Receptor Population Receptor Age Exposure Point Parameter Parameter Definition Value Units Rationale/ Intake Equation/

Code Reference Model Name

Ingestion On-site Adult Wetland Sediment Csed Chemical Concentration in Sediment See Table 3s.RME mg/kg See Table 3s.RME Chronic Daily Intake (CDI) (mg/kg-day) =Trespasser (0 to 6 inches) IR-Sed Ingestion Rate of Sediment 10 mg/day EPA, 1991 (1) Csed x IR-Sed x EF x ED x CF x 1/BW x 1/AT

(On-site) EF Exposure Frequency 13 days/year (2)ED Exposure Duration 8 years EPA, 2014 (3)CF Conversion Factor 0.000001 kg/mg - -BW Body Weight 80 kg EPA, 2014

AT-N Averaging Time (Non-Cancer) 2,920 days (4)AT-C Averaging Time (Cancer) 25,550 days (5)

Older Child Wetland Sediment Csed Chemical Concentration in Sediment See Table 3s.RME mg/kg See Table 3s.RME CDI (mg/kg-day) =(0 to 6 inches) IR-Sed Ingestion Rate of Sediment 10 mg/day EPA, 1991 (1) Csed x IR-Sed x EF x ED x CF x 1/BW x 1/AT

(On-site) EF Exposure Frequency 13 days/year (2)ED Exposure Duration 12 years Professional Judgment CDI - MMOA (mg/kg-day) (9) =CF Conversion Factor 0.000001 kg/mg - - Csed x IR-Sed x EF x EDadj x CF x 1/BW x 1/ATBW Body Weight 50.2 kg EPA 2011 (6)

AT-N Averaging Time (Non-Cancer) 4,380 days (4) EDadj = ED6-16 x ADAF [3] + ED17-18 x ADAF [1]AT-C Averaging Time (Cancer) 25,550 days (5)

Dermal On-site Adult Wetland Sediment Csed Chemical Concentration in Sediment See Table 3s.RME mg/kg See Table 3s.RME CDI (mg/kg-day) =Trespasser (0 to 6 inches) SA Skin Surface Area Available for Contact 5,230 cm2 EPA, 2011 (7) Csed x SA x SSAF x DABS x CF x EF x ED x 1/BW x 1/AT

(On-site) SSAF Soil to Skin Adherence Factor 0.3 mg/cm2-day EPA, 2004DABS Dermal Absorption Factor Solids Chemical specific -- EPA, 2004

CF Conversion Factor 0.000001 kg/mg - -EF Exposure Frequency 13 days/year (2)ED Exposure Duration 8 years EPA, 2014 (3)BW Body Weight 80 kg EPA, 2014


Older Child Wetland Sediment Csed Chemical Concentration in Sediment See Table 3s.RME mg/kg See Table 3s.RME CDI (mg/kg-day) =(0 to 6 inches) SA Skin Surface Area Available for Contact 3,201 cm2 EPA, 2011 (7,8) Csed x SA x SSAF x DABS x CF x EF x ED x 1/BW x 1/AT

(On-site) SSAF Soil to Skin Adherence Factor 0.2 mg/cm2-day EPA, 2004DABS Dermal Absorption Factor Solids chem specific -- EPA, 2004 CDI - MMOA (mg/kg-day) (9) =

CF Conversion Factor 0.000001 kg/mg - - Csed x SA x SSAF x DABS x CF x EF x EDadj x 1/BW x 1/ATEF Exposure Frequency 13 days/year (2)ED Exposure Duration 12 years Professional Judgment EDadj = ED6-16 x ADAF [3] + ED17-18 x ADAF [1]BW Body Weight 50.2 kg EPA 2011 (6)


Notes:(1) Assumed sediment ingestion rate is equal to 1/10 of the incidental soil ingestion rate.(2) Professional judgment assuming 1 days per week over a 13-week period. Areas of the wetland are inaccessible and there are few access points.(3) Exposure duration of adults was calculated by subtracting exposure duration of young child (6 years) and older child (12 years) from default residential exposure duration of 26 years.(4) Calculated as the product of ED (years) x 365 days/year.(5) Calculated as the product of 70 years assumed human lifetime (EPA, 1989) x 365 days/year.(6) Age-weighted body weight for older male children from 6 to 18 years of age. (7) Exposed skin surface area includes hands, forearms and lower legs.(8) Age-weighted exposed skin surface area for older male children from 6 to 18 years of age. (9) For the carcinogenic polycyclic aromatic hydrocarbons that act with mutagenic mode of action (MMOA), intake equations are adjusted with age dependent adjustment factors (ADAFs). Sources: EPA, 1989: Risk Assessment Guidance for Superfund. Vol.1: Human Health Evaluation Manual, Part A. OERR. EPA/540/1-89/002. EPA, 1991: Risk Assessment Guidance for Superfund. Vol.1: Human Health Evaluation Manual - Supplemental Guidance, Standard Default Exposure Factors. Interim Final. OSWER Directive 9285.6-03. EPA, 2004: Risk Assessment Guidance for Superfund Volume I: Human Health Evaluation Manual (Part E, Supplemental Guidance for Dermal Risk Assessment (Final). EPA/540/R/99/005. July 2004. EPA, 2011. Exposure Factors Handbook: 2011 Edition. EPA/600/R-090/052F. September 2011. EPA, 2014: Human Health Evaluation Manual, Supplemental Guidance: Update of Standard Default Exposure Factors, OSWER Directive 9200.1-120, February 6, 2014.

TABLE 4.1 SupplementDERMAL ABSORPTION FRACTION FROM SOIL


Chemical CAS Chemical Dermal NoteGroup Number Absorption

Fraction

Inorganic 7429-90-5 Aluminum NA (1)Inorganic 7440-36-0 Antimony NA (1)Inorganic 7440-38-2 Arsenic 0.03 EPA, 2004Inorganic 7440-39-3 Barium NA (1)Inorganic 7440-43-9 Cadmium 0.001 EPA, 2004Inorganic 7440-47-3 Chromium NA (1)Inorganic 7440-48-4 Cobalt NA (1)Inorganic 7440-50-8 Copper NA (1)Inorganic 7439-89-6 Iron NA (1)Inorganic 7439-92-1 Lead NA (1)Inorganic 7439-96-5 Manganese NA (1)Inorganic 7439-97-6 Mercury NA (1)Inorganic 7440-02-0 Nickel NA (1)Inorganic 7440-28-0 Thallium NA EPA, 2004Inorganic 7440-62-2 Vanadium NA (1)Inorganic 7440-66-6 Zinc NA (1)

PCB TCDD_TEQ 2,3,7,8-TCDD TEQ 0.03 EPA, 2004PCB AroclorTotal Total Aroclors 0.14 EPA, 2004PCB PCBTotal Total PCBs 0.14 EPA, 2004

Pesticide 309-00-2 Aldrin NA (1)Pesticide 319-85-7 BHC (beta) 0.1 EPA, 2004Pesticide 1024-57-3 Heptachlor epoxide NA (1)

SVOC 56-55-3 Benzo(a)anthracene 0.13 EPA, 2004SVOC 50-32-8 Benzo(a)pyrene 0.13 EPA, 2004SVOC 205-99-2 Benzo(b)fluoranthene 0.13 EPA, 2004SVOC 117-81-7 Bis(2-ethylhexyl)phthalate 0.1 EPA, 2004SVOC 53-70-3 Dibenz(a,h)anthracene 0.13 EPA, 2004SVOC 193-39-5 Indeno(1,2,3-cd)pyrene 0.13 EPA, 2004

Notes:(1) No default dermal absorption values are currently available for pesticides and inorganics. Therefore, consistent with EPA RAGS Part E (EPA, 2004) and the RSL Table (EPA, 2016), dermal exposure is not assessed for these constituents.

Sources:EPA, 2004: Risk Assessment Guidance for Superfund (RAGS) Volume I: Human Health Evaluation Manual. (Part E, Supplemental Guidance for Dermal Risk Assessment (Final). EPA/540/R/99/005. July 2004.EPA, 2016: Regional Screening Levels for Chemical Contaminants at Superfund Sites. May.

NA = Not Available/Not ApplicablePCB = Polychlorinated BiphenylSVOC = Semi-volatile Organic Compound



Scenario Timeframe: Current/Future Medium: Surface WaterExposure Medium: Surface Water



Dermal On-site Adult Wetland Surface Water Csw Chemical Concentration in Surface Water See Table 3s.RME µg/l See Table 3s.RME CDI (mg/kg-day) =Trespasser DAevent Dermally Absorbed Dose per Event calculated mg/cm2-event calculated DAevent x SA x EV x EF x ED x 1/BW x 1/AT

FA Fraction absorbed water chemical specific dimensionless EPA, 2004Kp Permeability Coefficient chemical specific cm/hr EPA, 2004 Inorganics: DAevent (mg/cm2-event) = Lag Time chemical specific hr/event EPA, 2004 Kp x Csw x tevent x CF1 x CF2t* Time to Reach Steady-state chemical specific hours EPA, 2004B Ratio of Permeability of Stratum Corneum to Epidermis chemical specific dimensionless EPA, 2004

tevent Event Time 1 hr/event (1) Organics: DAevent (mg/cm2-event) = SA Skin Surface Area Available for Contact 5,230 cm2 EPA, 2011 (2) tevent<t*: DAevent (mg/cm2-event) = EV Event Frequency 1 events/day (1) 2 x FA x Kp x Csw x (sqrt((6 x x tevent)/))EF Exposure Frequency 13 days/year (3) x CF1 x CF2ED Exposure Duration 8 years EPA, 2014 (4)BW Body Weight 80 kg EPA, 2014 tevent>t*: DAevent (mg/cm2-event) =

AT-N Averaging Time (Non-Cancer) 2,920 days (5) FA x Kp x Csw x ( tevent/(1+B) + 2 x x AT-C Averaging Time (Cancer) 25,550 days (6) ((1 + 3B + 3B2)/(1+B)2)) x CF1 x CF2CF1 Conversion Factor 1 0.001 mg/µg - -CF2 Conversion Factor 2 0.001 l/cm3 - -

Dermal On-site Older Child Wetland Surface Water Csw Chemical Concentration in Surface Water See Table 3s.RME µg/l See Table 3s.RME CDI (mg/kg-day) =Trespasser DAevent Dermally Absorbed Dose per Event calculated mg/cm2-event calculated DAevent x SA x EV x EF x ED x 1/BW x 1/AT

FA Fraction absorbed water chemical specific dimensionless EPA, 2004Kp Permeability Coefficient chemical specific cm/hr EPA, 2004 Inorganics: DAevent (mg/cm2-event) = Lag Time chemical specific hr/event EPA, 2004 Kp x Csw x tevent x CF1 x CF2t* Time to Reach Steady-state chemical specific hours EPA, 2004B Ratio of Permeability of Stratum Corneum to Epidermis chemical specific dimensionless EPA, 2004 Organics: DAevent (mg/cm2-event) =

tevent Event Time 1 hr/event (1) tevent<t*: DAevent (mg/cm2-event) = SA Skin Surface Area Available for Contact 3,201 cm2 EPA, 2011 (2,7) 2 x FA x Kp x Csw x (sqrt((6 x x tevent)/))EV Event Frequency 1 events/day (1) x CF1 x CF2EF Exposure Frequency 13 days/year (3)ED Exposure Duration 12 years Professional Judgment tevent>t*: DAevent (mg/cm2-event) = BW Body Weight 50.2 kg EPA 2011 (8) FA x Kp x Csw x ( tevent/(1+B) + 2 x x

AT-N Averaging Time (Non-Cancer) 4,380 days (4) ((1 + 3B + 3B2)/(1+B)2)) x CF1 x CF2AT-C Averaging Time (Cancer) 25,550 days (5)CF1 Conversion Factor 1 0.001 mg/µg - - CDI - MMOA (mg/kg-day) (9) =CF2 Conversion Factor 2 0.001 l/cm3 - - DAevent x SA x EV x EF x EDadj x 1/BW x 1/AT

EDadj = ED6-16 x ADAF [3] + ED17-18 x ADAF [1]

Notes:(1) Professional judgment assuming contact for 1 hour per day. The site is not attractive for wading and deep sediments make wading very difficult.(2) Exposed skin surface area includes hands, forearms and lower legs.(3) Professional judgment assuming 1 days per week over a 13-week period. Areas of the wetland are inaccessible and there are few access points.(4) Exposure duration of adults was calculated by subtracting exposure duration of young child (6 years) and older child (12 years) from default residential exposure duration of 26 years.(5) Calculated as the product of ED (years) x 365 days/year.(6) Calculated as the product of 70 years assumed human lifetime (EPA, 1989) x 365 days/year.(7) Age-weighted exposed skin surface area for older male children from 6 to 18 years of age. (8) Age-weighted body weight for older male children from 6 to 18 years of age. (9) For trichloroethene, which acts with mutagenic mode of action (MMOA) through the kidney, intake equations for the kidney component were adjusted with age dependent adjustment factors (ADAFs).

Sources: EPA, 1989: Risk Assessment Guidance for Superfund. Vol.1: Human Health Evaluation Manual, Part A. OERR. EPA/540/1-89/002. EPA, 2004: Risk Assessment Guidance for Superfund Volume I: Human Health Evaluation Manual (Part E, Supplemental Guidance for Dermal Risk Assessment (Final). EPA/540/R/99/005. July 2004. EPA, 2011. Exposure Factors Handbook: 2011 Edition. EPA/600/R-090/052F. September 2011. EPA, 2014: Human Health Evaluation Manual, Supplemental Guidance: Update of Standard Default Exposure Factors, OSWER Directive 9200.1-120, February 6, 2014.



Scenario Timeframe: Current/Future

Exposure Medium: Fish



Ingestion Fish Consumer Adult Fish Cfish Chemical Concentration in Fish See Table 3s.RME mg/kg-fish See Table 3s.RME Chronic Daily Intake (CDI) (mg/kg-day) =(white perch) IR-F Fish Ingestion Rate 22.0 g-fish/day EPA, 2014a Cfish x IR-F x EF x ED x CF1 x 1/BW x 1/AT

EF Exposure Frequency 27 days/year (1)ED Exposure Duration 8 years EPA, 2014 (2)BW Body Weight 80 kg EPA, 2014b

AT-N Averaging Time (Non-Cancer) 2,920 days (3)AT-C Averaging Time (Cancer) 25,550 days (4)CF1 Conversion Factor 1 0.001 kg/g - -

Older Child Fish Cfish Chemical Concentration in Fish See Table 3s.RME mg/kg-fish See Table 3s.RME CDI (mg/kg-day) =(white perch) IR-F Fish Ingestion Rate 14.7 g-fish/day EPA, 2014a (5) Cfish x IR-F x EF x ED x CF1 x 1/BW x 1/AT

EF Exposure Frequency 27 days/year (1)ED Exposure Duration 12 years Professional JudgmentBW Body Weight 50.2 kg EPA 2011 (6)


Younger Child Fish Cfish Chemical Concentration in Fish See Table 3s.RME mg/kg-fish See Table 3s.RME CDI (mg/kg-day) =(white perch) IR-F Fish Ingestion Rate 7.3 g-fish/day EPA, 2014a (5) Cfish x IR-F x EF x ED x CF1 x 1/BW x 1/AT

EF Exposure Frequency 27 days/year (1)ED Exposure Duration 6 years EPA, 2014bBW Body Weight 15 kg EPA, 2014b


Notes:(1) Based on a survey of New York anglers by Connolly et al. (1992).(2) Exposure duration of adults was calculated by subtracting exposure duration of young child (6 years) and older child (12 years) from default residential exposure duration of 26 years.(3) Calculated as the product of 70 years assumed human lifetime (EPA, 1989) x 365 days/year.(4) Calculated as the product of ED (years) x 365 days/year.(5) Fish ingestion rates for an older child and a younger child are two-thirds and one-third, respectively, of the adult fish ingestion rate (22.0 grams/day). (6) Age-weighted body weight for older male children from 6 to 18 years of age.

Sources: EPA, 1989: Risk Assessment Guidance for Superfund. Vol.1: Human Health Evaluation Manual, Part A. OERR. EPA/540/1-89/002. EPA, 2002: Estimated per Capita Fish Consumption in the United States. EPA-821-C-02-003. EPA, 2011. Exposure Factors Handbook: 2011 Edition. EPA/600/R-090/052F. September 2011. EPA, 2014a: Estimated Fish Consumption Rates for the U.S. Population and Selected Populations (NHANES 2003-2010). Final Report. EPA-820-R-14-002. April. EPA, 2014b: Human Health Evaluation Manual, Supplemental Guidance: Update of Standard Default Exposure Factors, OSWER Directive 9200.1-120, February 6, 2014.

Medium: Sediment/Surface Water



Scenario Timeframe: Current/Future Medium: Sediment (Ackermans South)Exposure Medium: Sediment



Ingestion Off-site Trespasser Adult Wetland Sediment Csed Chemical Concentration in Sediment See Table 3s.RME mg/kg See Table 3s.RME Chronic Daily Intake (CDI) (mg/kg-day) =(0 to 6 inches) IR-Sed Ingestion Rate of Sediment 10 mg/day EPA, 1991 (1) Csed x IR-Sed x EF x ED x CF x 1/BW x 1/AT

(Ackermans South) EF Exposure Frequency 13 days/year (2)ED Exposure Duration 8 years EPA, 2014 (3)CF Conversion Factor 0.000001 kg/mg - -BW Body Weight 80 kg EPA, 2014


Older Child Wetland Sediment Csed Chemical Concentration in Sediment See Table 3s.RME mg/kg See Table 3s.RME CDI (mg/kg-day) =(0 to 6 inches) IR-Sed Ingestion Rate of Sediment 10 mg/day EPA, 1991 (1) Csed x IR-Sed x EF x ED x CF x 1/BW x 1/AT

(Ackermans South) EF Exposure Frequency 13 days/year (2)ED Exposure Duration 12 years Professional Judgment CDI - MMOA (mg/kg-day) (9) =CF Conversion Factor 0.000001 kg/mg - - Csed x IR-Sed x EF x EDadj x CF x 1/BW x 1/ATBW Body Weight 50.2 kg EPA 2011 (6)

AT-N Averaging Time (Non-Cancer) 4,380 days (4) EDadj = ED6-16 x ADAF [3] + ED17-18 x ADAF [1]AT-C Averaging Time (Cancer) 25,550 days (5)

Dermal Off-site Trespasser Adult Wetland Sediment Csed Chemical Concentration in Sediment See Table 3s.RME mg/kg See Table 3s.RME CDI (mg/kg-day) =(0 to 6 inches) SA Skin Surface Area Available for Contact 5,230 cm2 EPA, 2011 (7) Csed x SA x SSAF x DABS x CF x EF x ED x 1/BW x 1/AT

(Ackermans South) SSAF Soil to Skin Adherence Factor 0.3 mg/cm2-day EPA, 2004DABS Dermal Absorption Factor Solids Chemical specific -- EPA, 2004

CF Conversion Factor 0.000001 kg/mg - -EF Exposure Frequency 13 days/year (2)ED Exposure Duration 8 years EPA, 2014 (3)BW Body Weight 80 kg EPA, 2014


Older Child Wetland Sediment Csed Chemical Concentration in Sediment See Table 3s.RME mg/kg See Table 3s.RME CDI (mg/kg-day) =(0 to 6 inches) SA Skin Surface Area Available for Contact 3,201 cm2 EPA, 2011 (7,8) Csed x SA x SSAF x DABS x CF x EF x ED x 1/BW x 1/AT

(Ackermans South) SSAF Soil to Skin Adherence Factor 0.2 mg/cm2-day EPA, 2004DABS Dermal Absorption Factor Solids chem specific -- EPA, 2004 CDI - MMOA (mg/kg-day) (9) =

CF Conversion Factor 0.000001 kg/mg - - Csed x SA x SSAF x DABS x CF x EF x EDadj x 1/BW x 1/ATEF Exposure Frequency 13 days/year (2)ED Exposure Duration 12 years Professional Judgment EDadj = ED6-16 x ADAF [3] + ED17-18 x ADAF [1]BW Body Weight 50.2 kg EPA 2011 (6)


Notes:(1) Assumed sediment ingestion rate is equal to 1/10 of the incidental soil ingestion rate.(2) Professional judgment assuming 1 days per week over a 13-week period. Areas of the wetland are inaccessible and there are few access points.(3) Exposure duration of adults was calculated by subtracting exposure duration of young child (6 years) and older child (12 years) from default residential exposure duration of 26 years.(4) Calculated as the product of ED (years) x 365 days/year.(5) Calculated as the product of 70 years assumed human lifetime (EPA, 1989) x 365 days/year.(6) Age-weighted body weight for older male children from 6 to 18 years of age. (7) Exposed skin surface area includes hands, forearms and lower legs.(8) Age-weighted exposed skin surface area for older male children from 6 to 18 years of age. (9) For the carcinogenic polycyclic aromatic hydrocarbons that act with mutagenic mode of action (MMOA), intake equations are adjusted with age dependent adjustment factors (ADAFs).

Sources: EPA, 1989: Risk Assessment Guidance for Superfund. Vol.1: Human Health Evaluation Manual, Part A. OERR. EPA/540/1-89/002. EPA, 1991: Risk Assessment Guidance for Superfund. Vol.1: Human Health Evaluation Manual - Supplemental Guidance, Standard Default Exposure Factors. Interim Final. OSWER Directive 9285.6-03. EPA, 2004: Risk Assessment Guidance for Superfund Volume I: Human Health Evaluation Manual (Part E, Supplemental Guidance for Dermal Risk Assessment (Final). EPA/540/R/99/005. July 2004. EPA, 2011. Exposure Factors Handbook: 2011 Edition. EPA/600/R-090/052F. September 2011. EPA, 2014: Human Health Evaluation Manual, Supplemental Guidance: Update of Standard Default Exposure Factors, OSWER Directive 9200.1-120, February 6, 2014.

TABLE 5.1NON-CANCER TOXICITY DATA -- ORAL/DERMAL


Chemical Chronic/ Oral RfD Oral Absorption Absorbed RfD for Dermal (2) Primary Combined RfD:Target Organ(s)of Potential Subchronic Efficiency for Dermal Target Uncertainty/Modifying

Concern Value Units Value Units Organ(s) Factors Source(s) Date(s)(1) (MM/DD/YYYY)

Aluminum Chronic 1.0E+00 mg/kg/day >50% 1.0E+00 mg/kg/day Nervous System 100 PPRTV 10/23/2006Antimony Chronic 4.0E-04 mg/kg-day 15% 6.0E-05 mg/kg-day Lifetime, Hematologic 1000 / 1 IRIS 3/21/2016Arsenic Chronic 3.0E-04 mg/kg-day 95% 3.0E-04 mg/kg-day Dermal, Cardiovascular System 3 / 1 IRIS 3/21/2016Barium Chronic 2.0E-01 mg/kg-day 7% 1.4E-02 mg/kg-day Urinary System 300 IRIS 3/21/2016Cadmium (3) Chronic 5.0E-04 mg/kg-day 5% 2.5E-05 mg/kg-day Urinary System 10 / 1 IRIS 3/21/2016Chromium (4) Chronic 1.5E+00 mg/kg-day 1.3% 2.0E-02 mg/kg-day NOE 100 / 10 IRIS 3/21/2016Cobalt Chronic 3.0E-04 mg/kg-day > 50% 3.0E-04 mg/kg/day Endocrine System 3000 PPRTV 8/25/2008Copper Chronic 4.0E-02 mg/kg-day > 50% 4.0E-02 mg/kg/day Gastrointestinal NA HEAST 7/31/1997Cyanide Chronic 6.0E-04 mg/kg-day > 50% 6.0E-04 mg/kg/day Reproductive 3000 / 1 IRIS 3/21/2016Iron Chronic 7.0E-01 mg/kg-day > 50% 7.0E-01 mg/kg/day Gastrointestinal 1.5 PPRTV 9/11/2006Lead Chronic NA NA NA NA NA NA NA NA NAManganese (5) Chronic 2.4E-02 mg/kg-day 4% 9.6E-04 mg/kg-day Nervous System 1 / 1 IRIS 3/21/2016Mercury (6) Chronic 3.0E-04 mg/kg-day 7% 2.1E-05 mg/kg-day Immune System, Urinary System 1000 / 1 IRIS 3/21/2016Nickel Chronic 2.0E-02 mg/kg-day 4% 8.0E-04 mg/kg-day Body Weight, Organ Weight 300 / 1 IRIS 3/21/2016Silver Chronic 5.0E-03 mg/kg-day 4% 2.0E-04 mg/kg/day Dermal 3 / 1 IRIS 3/21/2016Thallium Chronic 1.0E-05 mg/kg-day 100% 1.0E-05 mg/kg-day Hair 3000 PPRTV Screen 10/25/2012Vanadium (7) Chronic 5.0E-03 mg/kg-day 2.6% 1.3E-04 mg/kg-day Dermal 100 / 1 IRIS 3/21/2016Zinc Chronic 3.0E-01 mg/kg-day > 50% 3.0E-01 mg/kg-day Immune System, Hematologic 3 / 1 IRIS 3/21/20162,3,7,8-TCDD TEQ (8) Chronic 7.0E-10 mg/kg-day 50-83% 7.0E-10 mg/kg-day Developmental, Endocrine System, Reproductive 30 IRIS 3/21/2016Total Aroclors (9) Chronic 2.0E-05 mg/kg-day 80 - 96% 2.0E-05 mg/kg-day Dermal, Immune System, and Ocular 300 / 1 IRIS 3/21/2016Total PCBs (9) Chronic 2.0E-05 mg/kg-day 80 - 96% 2.0E-05 mg/kg-day Dermal, Immune System, and Ocular 300 / 1 IRIS 3/21/2016Aldrin Chronic 3.0E-05 mg/kg-day > 50% 3.0E-05 mg/kg-day Hepatic 1000 / 1 IRIS 3/21/2016BHC (beta) Chronic NA NA NA NA NA NA NA NA NAChlordane (beta) (10) Chronic 5.0E-04 mg/kg-day > 50% 5.0E-04 mg/kg-day Hepatic 300 / 1 IRIS 3/21/2016Heptachlor Chronic 5.0E-04 mg/kg-day > 50% 5.0E-04 mg/kg-day Hepatic 300 / 1 IRIS 3/21/2016Heptachlor epoxide Chronic 1.3E-05 mg/kg-day > 50% 1.3E-05 mg/kg-day Hepatic 1000 / 1 IRIS 3/21/2016Benzo(a)anthracene Chronic NA NA NA NA NA NA NA NA NABenzo(a)pyrene Chronic NA NA NA NA NA NA NA NA NABenzo(b)fluoranthene Chronic NA NA NA NA NA NA NA NA NABenzo(k)fluoranthene Chronic NA NA NA NA NA NA NA NA NABis(2-ethylhexyl)phthalate Chronic 2.0E-02 mg/kg-day >50% 2.0E-02 mg/kg-day Liver 1000 IRIS 3/21/2016Dibenz(a,h)anthracene Chronic NA NA NA NA NA NA NA NA NAIndeno(1,2,3-cd)pyrene Chronic NA NA NA NA NA NA NA NA NABenzene Chronic 4.0E-03 mg/kg-day >50% 4.0E-03 mg/kg-day Immune System 300 / 1 IRIS 3/21/2016

Page 1 of 2

TABLE 5.1NON-CANCER TOXICITY DATA -- ORAL/DERMAL


Chemical Chronic/ Oral RfD Oral Absorption Absorbed RfD for Dermal (2) Primary Combined RfD:Target Organ(s)of Potential Subchronic Efficiency for Dermal Target Uncertainty/Modifying

Concern Value Units Value Units Organ(s) Factors Source(s) Date(s)(1) (MM/DD/YYYY)

Trichloroethene Chronic 5.0E-04 mg/kg-day > 50% 5.0E-04 mg/kg-day multiple (see below) multiple (see below) IRIS 3/21/2016Trichloroethene Chronic 4.8E-04 mg/kg-day > 50% 4.8E-04 mg/kg-day Immune System 100 IRIS 3/21/2016Trichloroethene Chronic 3.7E-04 mg/kg-day > 50% 3.7E-04 mg/kg-day Developmental, Immune System 1000 IRIS 3/21/2016Trichloroethene Chronic 5.1E-04 mg/kg-day > 50% 5.1E-04 mg/kg-day Developmental, Cardiovascular System 10 IRIS 3/21/2016Vinyl Chloride Chronic 3.0E-03 mg/kg-day > 50% 3.0E-03 mg/kg/day Liver 30 IRIS 3/21/2016Note:(1) Source: Risk Assessment Guidance for Superfund. Volume 1: Human Health Definitions: NA = Not Available Evaluation Manual (Part E, Supplemental Guidance for Dermal Risk Assessment) Final. HEAST = Health Effects Assessment Summary Tables Section 4.2 and Exhibit 4-1. USEPA recommends that the oral RfD should not be adjusted to IRIS = Integrated Risk Information System estimate the absorbed dose for compounds when the absorption efficiency is greater than 50%. NOE = No Observed Effects Constituents that do not have oral absorption efficiencies reported on this table PPRTV = Provisional Peer-Reviewed Toxicity Value were assumed to have an oral absorption efficiency of >50%.(2) Adjusted based on RAGS Part E.(3) The RfD for cadmium is based on exposure to water.(4) Chromium (III) was used to represent total chromium.

(6) Mercuric chloride (and other Mercury salts) was used to represent Mercury.(7) The RfD for vanadium is derived from the IRIS oral RfD for Vanadium Pentoxide by factoring out the molecular weight of the oxide ion.(8) 2,3,7,8-TCDD was used to represent 2,3,7,8-TCDD TEQ.(9) Aroclor-1254 was used to represent Total Aroclors and Total PCBs due to the availability of a non-cancer toxicity value for this Aroclor.(10) Chlordane (technical) was used to represent chlordane (beta).

manganese exposure sources.

(5) The RfD for managanese is based on non-diet sources. The RfD (0.14 mg/kg-day) presented in IRIS includes manganese from all sources, including diet. This RfD was adjusted by subtracting the dietary contribution from the normal U.S. diet (5 mg/day) and applying a modifying factor of 3 to address uncertainties associated with non-food

Page 2 of 2

TABLE 6.1CANCER TOXICITY DATA -- ORAL/DERMAL


Chemical Oral Cancer Slope Factor Oral Absorption Absorbed Cancer Slope Factor Weight of Evidence/ Oral CSFof Potential Efficiency for Dermal for Dermal (2) Cancer Guideline

Concern Value Units (1) Value Units Description Source(s) Date(s)(MM/DD/YYYY)

Aluminum NA NA NA NA NA NA NA NAAntimony NA NA NA NA NA NA NA NAArsenic 1.5E+00 (mg/kg-day)-1 95% 1.5E+00 (mg/kg-day)-1 A IRIS 3/21/2016Barium NA NA NA NA NA D IRIS 3/21/2016Cadmium NA NA NA NA NA NA NA NAChromium NA NA NA NA NA D IRIS 3/21/2016Cobalt NA NA NA NA NA NA NA NACopper NA NA NA NA NA D IRIS 3/21/2016Cyanide NA NA NA NA NA D IRIS 3/21/2016Iron NA NA NA NA NA NA NA NALead NA NA NA NA NA B2 IRIS 3/21/2016Manganese NA NA NA NA NA D IRIS 3/21/2016Mercury NA NA NA NA NA C IRIS 3/21/2016Nickel NA NA NA NA NA NA NA NASilver NA NA NA NA NA D IRIS 3/21/2016Thallium NA NA NA NA NA NA NA NAVanadium NA NA NA NA NA NA NA NAZinc NA NA NA NA NA D IRIS 3/21/20162,3,7,8-TCDD TEQ (4) 1.3E+05 (mg/kg-day)-1 > 50% 1.3E+05 (mg/kg-day)-1 NA Cal/EPA 3/21/2016Total Aroclors (5) 2.0E+00 (mg/kg-day)-1 80 - 96% 2.0E+00 (mg/kg-day)-1 B2 IRIS 3/21/2016Total PCBs (5) 2.0E+00 (mg/kg-day)-1 80 - 96% 2.0E+00 (mg/kg-day)-1 B2 IRIS 3/21/2016Aldrin 1.7E+01 (mg/kg-day)-1 > 50% 1.7E+01 (mg/kg-day)-1 B2 IRIS 3/21/2016BHC (beta) 1.8E+00 (mg/kg-day)-1 > 50% 1.8E+00 (mg/kg-day)-1 C IRIS 3/21/2016Chlordane (beta) (7) 3.5E-01 (mg/kg-day)-1 > 50% 3.5E-01 (mg/kg-day)-1 B2 IRIS 3/21/2016Heptachlor 4.5E+00 (mg/kg-day)-1 > 50% 4.5E+00 (mg/kg-day)-1 B2 IRIS 3/21/2016Heptachlor epoxide 9.1E+00 (mg/kg-day)-1 > 50% 9.1E+00 (mg/kg-day)-1 B2 IRIS 3/21/2016Benzo(a)anthracene (3) 7.3E-01 (mg/kg-day)-1 58-89% 7.3E-01 (mg/kg-day)-1 B2 IRIS (6) 3/21/2016Benzo(a)pyrene (3) 7.3E+00 (mg/kg-day)-1 58-89% 7.3E+00 (mg/kg-day)-1 B2 IRIS 3/21/2016Benzo(b)fluoranthene (3) 7.3E-01 (mg/kg-day)-1 58-89% 7.3E-01 (mg/kg-day)-1 B2 IRIS (6) 3/21/2016Benzo(k)fluoranthene 7.3E-02 (mg/kg-day)-1 58-89% 7.3E-01 (mg/kg-day)-1 B2 IRIS (6) 3/21/2016Bis(2-ethylhexyl)phthalate 1.4E-02 (mg/kg-day)-1 >50% 1.4E-02 (mg/kg-day)-1 B2 IRIS 3/21/2016Dibenz(a,h)anthracene (3) 7.3E+00 (mg/kg-day)-1 58-89% 7.3E+00 (mg/kg-day)-1 B2 IRIS (6) 3/21/2016Indeno(1,2,3-cd)pyrene (3) 7.3E-01 (mg/kg-day)-1 58-89% 7.3E-01 (mg/kg-day)-1 B2 IRIS (6) 3/21/2016Benzene 5.5E-02 (mg/kg-day)-1 >50% 5.5E-02 (mg/kg-day)-1 A IRIS 3/21/2016

Page 1 of 2

TABLE 6.1CANCER TOXICITY DATA -- ORAL/DERMAL


Chemical Oral Cancer Slope Factor Oral Absorption Absorbed Cancer Slope Factor Weight of Evidence/ Oral CSFof Potential Efficiency for Dermal for Dermal (2) Cancer Guideline

Concern Value Units (1) Value Units Description Source(s) Date(s)(MM/DD/YYYY)

Trichloroethylene 4.6E-02 (mg/kg-day)-1 > 50% 4.6E-02 (mg/kg-day)-1 Carcinogenic to humans IRIS 3/21/2016Trichloroethylene (Kidney) (3) 9.3E-03 (mg/kg-day)-1 > 50% 9.3E-03 (mg/kg-day)-1 Carcinogenic to humans IRIS 3/21/2016Trichloroethylene (NHL + Liver) 3.7E-02 (mg/kg-day)-1 > 50% 3.7E-02 (mg/kg-day)-1 Carcinogenic to humans IRIS 3/21/2016Vinyl Chloride (Adulthood) 7.2E-01 (mg/kg-day)-1 > 50% 7.2E-01 (mg/kg-day)-1 A IRIS 3/21/2016

Note:(1) Source: Risk Assessment Guidance for Superfund. Volume 1: Human Health Definitions: NA = Not Available Evaluation Manual (Part E, Supplemental Guidance for Dermal Risk Assessment) Final. Cal/EPA = California Environemental Protection Agency Section 4.2 and Exhibit 4-1. USEPA recommends that the oral slope factor should not be adjusted to IRIS = Integrated Risk Information System estimate the absorbed dose for compounds when the absorption efficiency is greater than 50%. Constituents that do not have oral absorption efficiencies reported on this table were assumed to have an oral absorption efficiency of >50%.(2) Adjusted based on RAGS Part E.(3) This chemical operates with a mutagenic mode of action. With the exception of vinyl chloride, chemical-specific data are not available; therefore, USEPA (2005) default age-dependant adjustment factors (ADAF) will be applied to the slope factor as follows:

AGE AGE ADAF6-<16 316-<26 1

(4) 2,3,7,8-TCDD was used to represent 2,3,7,8-TCDD TEQ.(5) High Risk PCBs were used to represent total Aroclors and total PCBs.(6) Consistent with the RSL table (May 2016), the oral slope factors for benzo(a)anthracene, benzo(b)fluoranthene, dibenz(a,h)anthracene, and indeno(1,2,3-cd)pyrene were derived using the oral slope factor for benzo(a)pyrene and the following toxic equivalency factors (TEFs):

PAH TEFBenz(a)anthracene 0.1Benzo(b)fluoranthene 0.1Dibenz(a,h)anthracene 1Indeno(1,2,3-c,d)pyrene 0.1

(7) Chlordane (technical) was used to represent chlordane (beta).

Weight of Evidence definitions:Group A chemicals (known human carcinogens) are agents for which there is sufficient evidence to support the causal association between exposure to the agents in humans and cancer.Group B1 chemicals (probable human carcinogens) are agents for which there is limited evidence of possible carcinogenicity in humans.Group B2 chemicals (probable human carcinogens) are agents for which there is sufficient evidence of carcinogenicity in animals but inadequate or a lack of evidence in humans.Group C chemicals (possible human carcinogens) are agents for which there is limited evidence of carcinogenicity in animals and inadequate or a lack of human data.Group D chemicals (not classifiable as to human carcinogenicity) are agents with inadequate human and animal evidence of carcinogenicity or for which no data are available.Group E chemicals (evidence of noncarcinogenicity in humans) are agents for which there is no evidence of carcinogenicity from human or animal studies, or both.

Page 2 of 2

TABLE 7.1.RMECALCULATION OF CHEMICAL CANCER RISKS AND NON-CANCER HAZARDS


Scenario Timeframe: Current/FutureReceptor Population: On-Site TrespasserReceptor Age: Adult

Medium Exposure Medium Exposure Point Exposure Route Chemical of EPC Cancer Risk Calculations Non-Cancer Hazard Calculations

Potential Concern Value Units Intake/Exposure Concentration CSF/Unit Risk Cancer

RiskIntake/Exposure Concentration RfD/RfC Hazard

Quotient

Value Units Value Units Value Units Value Units

Surface Water Surface Water Wetland Surface Water Dermal Aluminum 1.9E+03 ug/L 5.0E-07 mg/kg-day NA NA NA 4.4E-06 mg/kg-day 1.0E+00 mg/kg-day 4.4E-06Antimony, Dissolved 8.8E-01 ug/L 2.3E-10 mg/kg-day NA NA NA 2.0E-09 mg/kg-day 6.0E-05 mg/kg-day 3.4E-05

Arsenic 7.3E+00 ug/L 1.9E-09 mg/kg-day 1.5E+00 1/(mg/kg-day) 3E-09 1.7E-08 mg/kg-day 3.0E-04 mg/kg-day 5.6E-05Cobalt, Dissolved 5.2E+00 ug/L 1.4E-10 mg/kg-day NA NA NA 1.2E-09 mg/kg-day 3.0E-04 mg/kg-day 4.0E-06Cyanide 3.3E+00 ug/L 8.8E-10 mg/kg-day NA NA NA 7.7E-09 mg/kg-day 6.0E-04 mg/kg-day 1.3E-05Iron 1.7E+04 ug/L 4.4E-06 mg/kg-day NA NA NA 3.8E-05 mg/kg-day 7.0E-01 mg/kg-day 5.5E-05Lead 8.2E+00 ug/L 1.3E-09 mg/kg-day NA NA NA 1.1E-08 mg/kg-day NA NA NAManganese 7.0E+03 ug/L 1.9E-06 mg/kg-day NA NA NA 1.6E-05 mg/kg-day 9.6E-04 mg/kg-day 1.7E-02Mercury 9.7E-01 ug/L 2.6E-10 mg/kg-day NA NA NA 2.3E-09 mg/kg-day 2.1E-05 mg/kg-day 1.1E-04Silver 4.7E+01 ug/L 7.5E-09 mg/kg-day NA NA NA 6.6E-08 mg/kg-day 2.0E-04 mg/kg-day 3.3E-04Total Aroclors 2.7E-01 ug/L 2.3E-07 mg/kg-day 2.0E+00 1/(mg/kg-day) 5E-07 2.0E-06 mg/kg-day 2.0E-05 mg/kg-day 1.0E-01Aldrin 4.3E-03 ug/L 3.2E-09 mg/kg-day 1.7E+01 1/(mg/kg-day) 5E-08 2.8E-08 mg/kg-day 3.0E-05 mg/kg-day 9.2E-04Chlordane (beta) 3.4E-02 ug/L 2.4E-08 mg/kg-day 3.5E-01 1/(mg/kg-day) 9E-09 2.1E-07 mg/kg-day 5.0E-04 mg/kg-day 4.3E-04Heptachlor 9.0E-03 ug/L 3.4E-09 mg/kg-day 4.5E+00 1/(mg/kg-day) 2E-08 3.0E-08 mg/kg-day 5.0E-04 mg/kg-day 6.0E-05Heptachlor epoxide 3.4E-03 ug/L 2.1E-10 mg/kg-day 9.1E+00 1/(mg/kg-day) 2E-09 1.8E-09 mg/kg-day 1.3E-05 mg/kg-day 1.4E-04Benzo(a)anthracene 3.2E+00 ug/L NA NA NA NA NA NA NA NA NA NABenzo(a)pyrene 2.4E+00 ug/L NA NA NA NA NA NA NA NA NA NABenzo(b)fluoranthene 3.0E+00 ug/L NA NA NA NA NA NA NA NA NA NABenzo(k)fluoranthene 3.7E+00 ug/L NA NA NA NA NA NA NA NA NA NADibenz(a,h)anthracene 3.8E+00 ug/L NA NA NA NA NA NA NA NA NA NAIndeno(1,2,3-cd)pyrene 3.7E+00 ug/L NA NA NA NA NA NA NA NA NA NABenzene 5.7E-01 ug/L 3.5E-09 mg/kg-day 5.5E-02 1/(mg/kg-day) 2E-10 3.1E-08 mg/kg-day 4.0E-03 mg/kg-day 7.7E-06Trichloroethene 2.3E+00 ug/L 1.5E-08 mg/kg-day 4.6E-02 1/(mg/kg-day) 7E-10 1.3E-07 mg/kg-day 5.0E-04 mg/kg-day 2.6E-04Vinyl Chloride 2.9E-01 ug/L 9.4E-10 mg/kg-day 7.2E-01 1/(mg/kg-day) 7E-10 8.3E-09 mg/kg-day 3.0E-03 mg/kg-day 2.8E-06

Exp. Route Total 5E-07 1.2E-01Exposure Point Total 5E-07 1.2E-01

Exposure Medium Total 5E-07 1.2E-01Surface Water Total 5E-07 1.2E-01

Page 1 of 3







Quotient


Sediment Sediment Wetland Sediment Ingestion Aluminum 1.3E+04 mg/kg 6.7E-06 mg/kg-day NA NA NA 5.9E-05 mg/kg-day 1.0E+00 mg/kg-day 5.9E-05(0 to 6 inches) Antimony 2.2E+01 mg/kg 1.1E-08 mg/kg-day NA NA NA 1.0E-07 mg/kg-day 4.0E-04 mg/kg-day 2.5E-04

(On-site) Arsenic 3.2E+01 mg/kg 1.6E-08 mg/kg-day 1.5E+00 1/(mg/kg-day) 2E-08 1.4E-07 mg/kg-day 3.0E-04 mg/kg-day 4.8E-04Barium 6.5E+02 mg/kg 3.3E-07 mg/kg-day NA NA NA 2.9E-06 mg/kg-day 2.0E-01 mg/kg-day 1.4E-05Cadmium 7.1E+00 mg/kg 3.6E-09 mg/kg-day NA NA NA 3.2E-08 mg/kg-day 5.0E-04 mg/kg-day 6.3E-05Chromium 2.7E+03 mg/kg 1.4E-06 mg/kg-day NA NA NA 1.2E-05 mg/kg-day 1.5E+00 mg/kg-day 8.0E-06Cobalt 2.0E+01 mg/kg 1.0E-08 mg/kg-day NA NA NA 8.8E-08 mg/kg-day 3.0E-04 mg/kg-day 2.9E-04Copper 2.1E+02 mg/kg 1.1E-07 mg/kg-day NA NA NA 9.3E-07 mg/kg-day 4.0E-02 mg/kg-day 2.3E-05Iron 3.1E+04 mg/kg 1.6E-05 mg/kg-day NA NA NA 1.4E-04 mg/kg-day 7.0E-01 mg/kg-day 1.9E-04Lead 1.6E+02 mg/kg 8.3E-08 mg/kg-day NA NA NA 7.3E-07 mg/kg-day NA NA NAManganese 8.8E+03 mg/kg 4.5E-06 mg/kg-day NA NA NA 3.9E-05 mg/kg-day 2.4E-02 mg/kg-day 1.6E-03Mercury 4.2E+01 mg/kg 2.1E-08 mg/kg-day NA NA NA 1.9E-07 mg/kg-day 3.0E-04 mg/kg-day 6.2E-04Nickel 8.9E+01 mg/kg 4.5E-08 mg/kg-day NA NA NA 4.0E-07 mg/kg-day 2.0E-02 mg/kg-day 2.0E-05Thallium 3.5E+01 mg/kg 1.8E-08 mg/kg-day NA NA NA 1.5E-07 mg/kg-day NA NA NAVanadium 5.4E+01 mg/kg 2.7E-08 mg/kg-day NA NA NA 2.4E-07 mg/kg-day 5.0E-03 mg/kg-day 4.8E-05Zinc 8.3E+02 mg/kg 4.2E-07 mg/kg-day NA NA NA 3.7E-06 mg/kg-day 3.0E-01 mg/kg-day 1.2E-052,3,7,8-TCDD TEQ 2.0E-03 mg/kg 1.0E-12 mg/kg-day 1.3E+05 1/(mg/kg-day) 1E-07 9.1E-12 mg/kg-day 7.0E-10 mg/kg-day 1.3E-02Total Aroclors 1.8E+02 mg/kg 9.0E-08 mg/kg-day 2.0E+00 1/(mg/kg-day) 2E-07 7.9E-07 mg/kg-day 2.0E-05 mg/kg-day 4.0E-02Total PCBs 2.6E+02 mg/kg 1.3E-07 mg/kg-day 2.0E+00 1/(mg/kg-day) 3E-07 1.2E-06 mg/kg-day 2.0E-05 mg/kg-day 5.8E-02Aldrin 3.0E+00 mg/kg 1.5E-09 mg/kg-day 1.7E+01 1/(mg/kg-day) 3E-08 1.3E-08 mg/kg-day 3.0E-05 mg/kg-day 4.5E-04BHC (beta) 6.7E+00 mg/kg 3.4E-09 mg/kg-day 1.8E+00 1/(mg/kg-day) 6E-09 3.0E-08 mg/kg-day NA NA NAHeptachlor epoxide 1.6E+00 mg/kg 8.1E-10 mg/kg-day 9.1E+00 1/(mg/kg-day) 7E-09 7.1E-09 mg/kg-day 1.3E-05 mg/kg-day 5.5E-04Benzo(a)anthracene 6.7E-01 mg/kg 3.4E-10 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-10 3.0E-09 mg/kg-day NA NA NABenzo(a)pyrene 6.8E-01 mg/kg 3.4E-10 mg/kg-day 7.3E+00 1/(mg/kg-day) 3E-09 3.0E-09 mg/kg-day NA NA NABenzo(b)fluoranthene 9.7E-01 mg/kg 4.9E-10 mg/kg-day 7.3E-01 1/(mg/kg-day) 4E-10 4.3E-09 mg/kg-day NA NA NABis(2-ethylhexyl)phthalate 2.1E+01 mg/kg 1.1E-08 mg/kg-day 1.4E-02 1/(mg/kg-day) 1E-10 9.3E-08 mg/kg-day 2.0E-02 mg/kg-day 4.7E-06Dibenz(a,h)anthracene 8.6E-02 mg/kg 4.4E-11 mg/kg-day 7.3E+00 1/(mg/kg-day) 3E-10 3.8E-10 mg/kg-day NA NA NAIndeno(1,2,3-cd)pyrene 2.7E-01 mg/kg 1.4E-10 mg/kg-day 7.3E-01 1/(mg/kg-day) 1E-10 1.2E-09 mg/kg-day NA NA NA

Exp. Route Total (Total Aroclors)1 2E-07 4.4E-02Exp. Route Total (Total PCBs)2 5E-07 7.6E-02

Page 2 of 3







Quotient


Sediment Sediment Wetland Sediment Dermal Aluminum 1.3E+04 mg/kg NA NA NA NA NA NA NA 1.0E+00 mg/kg-day NA(0 to 6 inches) Antimony 2.2E+01 mg/kg NA NA NA NA NA NA NA 6.0E-05 mg/kg-day NA

(On-site) Arsenic 3.2E+01 mg/kg 7.8E-08 mg/kg-day 1.5E+00 1/(mg/kg-day) 1E-07 6.8E-07 mg/kg-day 3.0E-04 mg/kg-day 2.3E-03Barium 6.5E+02 mg/kg NA NA NA NA NA NA NA 1.4E-02 mg/kg-day NACadmium 7.1E+00 mg/kg 5.7E-10 mg/kg-day NA NA NA 5.0E-09 mg/kg-day 2.5E-05 mg/kg-day 2.0E-04Chromium 2.7E+03 mg/kg NA NA NA NA NA NA NA 2.0E-02 mg/kg-day NACobalt 2.0E+01 mg/kg NA NA NA NA NA NA NA 3.0E-04 mg/kg-day NACopper 2.1E+02 mg/kg NA NA NA NA NA NA NA 4.0E-02 mg/kg-day NAIron 3.1E+04 mg/kg NA NA NA NA NA NA NA 7.0E-01 mg/kg-day NALead 1.6E+02 mg/kg NA NA NA NA NA NA NA NA NA NAManganese 8.8E+03 mg/kg NA NA NA NA NA NA NA 9.6E-04 mg/kg-day NAMercury 4.2E+01 mg/kg NA NA NA NA NA NA NA 2.1E-05 mg/kg-day NANickel 8.9E+01 mg/kg NA NA NA NA NA NA NA 8.0E-04 mg/kg-day NAThallium 3.5E+01 mg/kg NA NA NA NA NA NA NA NA NA NAVanadium 5.4E+01 mg/kg NA NA NA NA NA NA NA 1.3E-04 mg/kg-day NAZinc 8.3E+02 mg/kg NA NA NA NA NA NA NA 3.0E-01 mg/kg-day NA2,3,7,8-TCDD TEQ 2.0E-03 mg/kg 4.9E-12 mg/kg-day 1.3E+05 1/(mg/kg-day) 6E-07 4.3E-11 mg/kg-day 7.0E-10 mg/kg-day 6.1E-02Total Aroclors 1.8E+02 mg/kg 2.0E-06 mg/kg-day 2.0E+00 1/(mg/kg-day) 4E-06 1.7E-05 mg/kg-day 2.0E-05 mg/kg-day 8.7E-01Total PCBs 2.6E+02 mg/kg 2.9E-06 mg/kg-day 2.0E+00 1/(mg/kg-day) 6E-06 2.5E-05 mg/kg-day 2.0E-05 mg/kg-day 1.3E+00Aldrin 3.0E+00 mg/kg NA NA 1.7E+01 1/(mg/kg-day) NA NA NA 3.0E-05 mg/kg-day NABHC (beta) 6.7E+00 mg/kg 5.3E-08 mg/kg-day 1.8E+00 1/(mg/kg-day) 1E-07 4.7E-07 mg/kg-day NA NA NAHeptachlor epoxide 1.6E+00 mg/kg NA NA 9.1E+00 1/(mg/kg-day) NA NA NA 1.3E-05 mg/kg-day NABenzo(a)anthracene 6.7E-01 mg/kg 6.9E-09 mg/kg-day 7.3E-01 1/(mg/kg-day) 5E-09 6.1E-08 mg/kg-day NA NA NABenzo(a)pyrene 6.8E-01 mg/kg 7.0E-09 mg/kg-day 7.3E+00 1/(mg/kg-day) 5E-08 6.1E-08 mg/kg-day NA NA NABenzo(b)fluoranthene 9.7E-01 mg/kg 1.0E-08 mg/kg-day 7.3E-01 1/(mg/kg-day) 7E-09 8.8E-08 mg/kg-day NA NA NABis(2-ethylhexyl)phthalate 2.1E+01 mg/kg 1.7E-07 mg/kg-day 1.4E-02 1/(mg/kg-day) 2E-09 1.5E-06 mg/kg-day 2.0E-02 mg/kg-day 7.3E-05Dibenz(a,h)anthracene 8.6E-02 mg/kg 9.0E-10 mg/kg-day 7.3E+00 1/(mg/kg-day) 7E-09 7.8E-09 mg/kg-day NA NA NAIndeno(1,2,3-cd)pyrene 2.7E-01 mg/kg 2.8E-09 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-09 2.4E-08 mg/kg-day NA NA NA

Exp. Route Total (Total Aroclors)1 4E-06 8.7E-01Exp. Route Total (Total PCBs)2 7E-06 1.3E+00

5E-06 9.2E-017E-06 1.4E+005E-06 9.2E-017E-06 1.4E+00

Sediment Total (Total Aroclors)1 5E-06 9.2E-01Sediment Total (Total PCBs)2 7E-06 1.4E+00Receptor Total (Total Aroclors)1 5E-06 1.0E+00Receptor Total (Total PCBs)2 8E-06 1.5E+00Notes:NA = Not applicable or not available1The total includes estimated risks/HIs for Total Aroclors in sediment but not for 2,3,7,8-TCDD TEQ and Total PCBs in sediment.2The total includes estimated risks/HIs for 2,3,7,8-TCDD TEQ and Total PCBs in sediment but not for Total Aroclors in sediment.

Exposure Point Total (Total Aroclors)1

Exposure Point Total (Total PCBs)2

Exposure Medium Total (Total Aroclors)1

Exposure Medium Total (Total PCBs)2

Page 3 of 3

TABLE 7.1.RME SUPPLEMENT A

CALCULATION OF DAEVENT

REASONABLE MAXIMUM EXPOSURE


Chemical Surface Water Permeability Lag Fraction Durationof Potential Concentration Coefficient Time Absorbed Water of Event

Concern (CW) (Kp) B (event) t* (FA) (tevent) DAevent(ug/L) (cm/hr) (dimensionless) (hr) (hr) (dimensionless) (hr) (mg/cm2-event) Eq

Aluminum 1.9E+03 1.0E-03 NA NA NA NA 1.0 1.9E-06 1

Antimony, Dissolved 8.8E-01 1.0E-03 NA NA NA NA 1.0 8.8E-10 1

Arsenic 7.3E+00 1.0E-03 NA NA NA NA 1.0 7.3E-09 1

Cobalt, Dissolved 5.2E+00 1.0E-04 NA NA NA NA 1.0 5.2E-10 1

Cyanide 3.3E+00 1.0E-03 NA NA NA NA 1.0 3.3E-09 1

Iron 1.7E+04 1.0E-03 NA NA NA NA 1.0 1.7E-05 1

Lead 8.2E+00 6.0E-04 NA NA NA NA 1.0 4.9E-09 1

Manganese 7.0E+03 1.0E-03 NA NA NA NA 1.0 7.0E-06 1

Mercury 9.7E-01 1.0E-03 NA NA NA NA 1.0 9.7E-10 1

Silver 4.7E+01 6.0E-04 NA NA NA NA 1.0 2.8E-08 1

Total Aroclors 2.7E-01 5.5E-01 3.6E+00 4.5E+00 1.9E+01 1.0E+00 1.0 8.6E-07 2

Aldrin 4.3E-03 2.9E-01 2.2E+00 1.2E+01 4.8E+01 1.0E+00 1.0 1.2E-08 2

Chlordane (beta) 3.4E-02 1.1E-01 8.3E-01 2.1E+01 8.0E+01 2.0E+00 1.0 9.2E-08 2

Heptachlor 9.0E-03 1.4E-01 1.1E+00 1.3E+01 5.0E+01 1.0E+00 1.0 1.3E-08 2

Heptachlor epoxide 3.4E-03 2.1E-02 1.6E-01 1.6E+01 3.8E+01 1.0E+00 1.0 7.8E-10 2

Benzo(a)anthracene 3.2E+00 5.5E-01 3.2E+00 2.0E+00 8.5E+00 1.0E+00 1.0 6.9E-06 2

Benzo(a)pyrene 2.4E+00 7.1E-01 4.4E+00 2.7E+00 1.2E+01 1.0E+00 1.0 7.8E-06 2

Benzo(b)fluoranthene 3.0E+00 4.2E-01 2.5E+00 2.7E+00 1.1E+01 1.0E+00 1.0 5.7E-06 2

Benzo(k)fluoranthene 3.7E+00 6.9E-01 4.2E+00 2.7E+00 1.2E+01 1.0E+00 1.0 1.2E-05 2

Dibenz(a,h)anthracene 3.8E+00 9.5E-01 6.1E+00 3.8E+00 1.7E+01 1.0E+00 1.0 2.0E-05 2

Indeno(1,2,3-cd)pyrene 3.7E+00 1.2E+00 7.9E+00 3.7E+00 1.7E+01 1.0E+00 1.0 2.4E-05 2

Benzene 5.7E-01 1.5E-02 5.1E-02 2.9E-01 6.9E-01 1.0E+00 1.0 1.3E-08 3

Trichloroethene 2.3E+00 1.2E-02 5.1E-02 5.7E-01 1.4E+00 1.0E+00 1.0 5.5E-08 2

Vinyl Chloride 2.9E-01 8.4E-03 2.5E-02 2.4E-01 5.7E-01 1.0E+00 1.0 3.5E-09 3

Inorganics: DAevent (mg/cm2-event) = DAevent = Kp x CW x tevent x 0.001 mg/ug x 0.001 l/cm

3 (Eq 1)

Organics: DAevent (mg/cm2-event) = DAevent = tevent ≤ t*: DAevent (mg/cm2-event) =

2 x FA x Kp x Cw x (sqrt((6 x x tevent) / (3.1415))) x CF1 x CF2 (Eq 2)

tevent>t*: DAevent (mg/cm2-event) =

FA x Kp x CW x ( tevent/(1+B) + 2 x x ((1 + 3B + 3B2)/(1+B)2)) xCF1 x CF2 (Eq 3)

Notes:

Values for permeability constants, B, tau, t*, and FA are from EPA 2004, Risk Assessment Guidance for Superfund Volume I: Human Health Evaluation Manual (Part E, Supplemental Guidance for Dermal Risk Assessment - Final). EPA/540/R/99/005.

B - Dimensionless ratio of the permeability coefficient of a compound through the stratum corneum relative to its permeability

coefficient across the viable epidermis (dimensionless).

cm/hr - centimeter per hour

hr - hour

mg/cm2-event - milligram per square centimeter per event

µg/L - microgram per liter

NA - Not applicable

t* - Time to reach steady-state

CF1 - Conversion Factor 1 (0.001 mg/μg), CF2 - Conversion Factor 2 (0.001 L/cm 3)

Page 1 of 1



Scenario Timeframe: Current/FutureReceptor Population: On-Site TrespasserReceptor Age: Older Child

Medium Exposure Medium Exposure Point Exposure Route Chemical of EPC Cancer Risk Calculations3 Non-Cancer Hazard Calculations

Potential Concern Value Units Intake/Exposure Concentration CSF/Unit Risk Cancer Risk Intake/Exposure

Concentration RfD/RfC Hazard Quotient


Surface Water Surface Water Wetland Surface Water Dermal Aluminum 1.9E+03 µg/L 7.3E-07 mg/kg-day NA NA NA 4.3E-06 mg/kg-day 1.0E+00 mg/kg-day 4.3E-06Antimony, Dissolved 8.8E-01 µg/L 3.4E-10 mg/kg-day NA NA NA 2.0E-09 mg/kg-day 6.0E-05 mg/kg-day 3.3E-05Arsenic 7.3E+00 µg/L 2.8E-09 mg/kg-day 1.5E+00 1/(mg/kg-day) 4E-09 1.7E-08 mg/kg-day 3.0E-04 mg/kg-day 5.5E-05Cobalt, Dissolved 5.2E+00 µg/L 2.0E-10 mg/kg-day NA NA NA 1.2E-09 mg/kg-day 3.0E-04 mg/kg-day 3.9E-06Cyanide 3.3E+00 µg/L 1.3E-09 mg/kg-day NA NA NA 7.5E-09 mg/kg-day 6.0E-04 mg/kg-day 1.2E-05Iron 1.7E+04 µg/L 6.4E-06 mg/kg-day NA NA NA 3.7E-05 mg/kg-day 7.0E-01 mg/kg-day 5.4E-05Lead 8.2E+00 µg/L 1.9E-09 mg/kg-day NA NA NA 1.1E-08 mg/kg-day NA NA NAManganese 7.0E+03 µg/L 2.7E-06 mg/kg-day NA NA NA 1.6E-05 mg/kg-day 9.6E-04 mg/kg-day 1.7E-02Mercury 9.7E-01 µg/L 3.8E-10 mg/kg-day NA NA NA 2.2E-09 mg/kg-day 2.1E-05 mg/kg-day 1.1E-04Silver 4.7E+01 µg/L 1.1E-08 mg/kg-day NA NA NA 6.4E-08 mg/kg-day 2.0E-04 mg/kg-day 3.2E-04Total Aroclors 2.7E-01 µg/L 3.3E-07 mg/kg-day 2.0E+00 1/(mg/kg-day) 7E-07 1.9E-06 mg/kg-day 2.0E-05 mg/kg-day 9.7E-02Aldrin 4.3E-03 µg/L 4.6E-09 mg/kg-day 1.7E+01 1/(mg/kg-day) 8E-08 2.7E-08 mg/kg-day 3.0E-05 mg/kg-day 9.0E-04Chlordane (beta) 3.4E-02 ug/L 3.6E-08 mg/kg-day 3.5E-01 1/(mg/kg-day) 1E-08 2.1E-07 mg/kg-day 5.0E-04 mg/kg-day 4.2E-04Heptachlor 9.0E-03 µg/L 5.0E-09 mg/kg-day 4.5E+00 1/(mg/kg-day) 2E-08 2.9E-08 mg/kg-day 5.0E-04 mg/kg-day 5.8E-05Heptachlor epoxide 3.4E-03 µg/L 3.1E-10 mg/kg-day 9.1E+00 1/(mg/kg-day) 3E-09 1.8E-09 mg/kg-day 1.3E-05 mg/kg-day 1.4E-04Benzo(a)anthracene 3.2E+00 µg/L NA NA NA NA NA NA NA NA NA NABenzo(a)pyrene 2.4E+00 µg/L NA NA NA NA NA NA NA NA NA NABenzo(b)fluoranthene 3.0E+00 µg/L NA NA NA NA NA NA NA NA NA NABenzo(k)fluoranthene 3.7E+00 µg/L NA NA NA NA NA NA NA NA NA NADibenz(a,h)anthracene 3.8E+00 µg/L NA NA NA NA NA NA NA NA NA NAIndeno(1,2,3-cd)pyrene 3.7E+00 µg/L NA NA NA NA NA NA NA NA NA NABenzene 5.7E-01 µg/L 5.1E-09 mg/kg-day 5.5E-02 1/(mg/kg-day) 3E-10 3.0E-08 mg/kg-day 4.0E-03 mg/kg-day 7.5E-06Trichloroethene 2.3E+00 µg/L 2.2E-08 mg/kg-day 4.6E-02 1/(mg/kg-day) 1E-09 1.3E-07 mg/kg-day 5.0E-04 mg/kg-day 2.5E-04Vinyl Chloride 2.9E-01 µg/L 1.4E-09 mg/kg-day 7.2E-01 1/(mg/kg-day) 1E-09 8.0E-09 mg/kg-day 3.0E-03 mg/kg-day 2.7E-06

Exp. Route Total 8E-07 1.2E-01Exposure Point Total 8E-07 1.2E-01

Exposure Medium total 8E-07 1.2E-01Surface Water Total 8E-07 1.2E-01

Page 1 of 3








Sediment Sediment Wetland Sediment Ingestion Aluminum 1.3E+04 mg/kg 1.6E-05 mg/kg-day NA NA NA 9.4E-05 mg/kg-day 1.0E+00 mg/kg-day 9.4E-05(0 to 6 inches) Antimony 2.2E+01 mg/kg 2.7E-08 mg/kg-day NA NA NA 1.6E-07 mg/kg-day 4.0E-04 mg/kg-day 4.0E-04

(On-site) Arsenic 3.2E+01 mg/kg 3.9E-08 mg/kg-day 1.5E+00 1/(mg/kg-day) 6E-08 2.3E-07 mg/kg-day 3.0E-04 mg/kg-day 7.7E-04Barium 6.5E+02 mg/kg 7.9E-07 mg/kg-day NA NA NA 4.6E-06 mg/kg-day 2.0E-01 mg/kg-day 2.3E-05Cadmium 7.1E+00 mg/kg 8.6E-09 mg/kg-day NA NA NA 5.0E-08 mg/kg-day 5.0E-04 mg/kg-day 1.0E-04Chromium 2.7E+03 mg/kg 3.3E-06 mg/kg-day NA NA NA 1.9E-05 mg/kg-day 1.5E+00 mg/kg-day 1.3E-05Cobalt 2.0E+01 mg/kg 2.4E-08 mg/kg-day NA NA NA 1.4E-07 mg/kg-day 3.0E-04 mg/kg-day 4.7E-04Copper 2.1E+02 mg/kg 2.6E-07 mg/kg-day NA NA NA 1.5E-06 mg/kg-day 4.0E-02 mg/kg-day 3.7E-05Iron 3.1E+04 mg/kg 3.7E-05 mg/kg-day NA NA NA 2.2E-04 mg/kg-day 7.0E-01 mg/kg-day 3.1E-04Lead 1.6E+02 mg/kg 2.0E-07 mg/kg-day NA NA NA 1.2E-06 mg/kg-day NA NA NAManganese 8.8E+03 mg/kg 1.1E-05 mg/kg-day NA NA NA 6.3E-05 mg/kg-day 2.4E-02 mg/kg-day 2.6E-03Mercury 4.2E+01 mg/kg 5.1E-08 mg/kg-day NA NA NA 3.0E-07 mg/kg-day 3.0E-04 mg/kg-day 9.9E-04Nickel 8.9E+01 mg/kg 1.1E-07 mg/kg-day NA NA NA 6.3E-07 mg/kg-day 2.0E-02 mg/kg-day 3.2E-05Thallium 3.5E+01 mg/kg 4.2E-08 mg/kg-day NA NA NA 2.5E-07 mg/kg-day NA NA NAVanadium 5.4E+01 mg/kg 6.5E-08 mg/kg-day NA NA NA 3.8E-07 mg/kg-day 5.0E-03 mg/kg-day 7.6E-05Zinc 8.3E+02 mg/kg 1.0E-06 mg/kg-day NA NA NA 5.9E-06 mg/kg-day 3.0E-01 mg/kg-day 2.0E-052,3,7,8-TCDD TEQ 2.0E-03 mg/kg 2.5E-12 mg/kg-day 1.3E+05 1/(mg/kg-day) 3E-07 1.4E-11 mg/kg-day 7.0E-10 mg/kg-day 2.1E-02Total Aroclors 1.8E+02 mg/kg 2.2E-07 mg/kg-day 2.0E+00 1/(mg/kg-day) 4E-07 1.3E-06 mg/kg-day 2.0E-05 mg/kg-day 6.3E-02Total PCBs 2.6E+02 mg/kg 3.2E-07 mg/kg-day 2.0E+00 1/(mg/kg-day) 6E-07 1.8E-06 mg/kg-day 2.0E-05 mg/kg-day 9.2E-02Aldrin 3.0E+00 mg/kg 3.6E-09 mg/kg-day 1.7E+01 1/(mg/kg-day) 6E-08 2.1E-08 mg/kg-day 3.0E-05 mg/kg-day 7.1E-04BHC (beta) 6.7E+00 mg/kg 8.1E-09 mg/kg-day 1.8E+00 1/(mg/kg-day) 1E-08 4.8E-08 mg/kg-day NA NA NAHeptachlor epoxide 1.6E+00 mg/kg 1.9E-09 mg/kg-day 9.1E+00 1/(mg/kg-day) 2E-08 1.1E-08 mg/kg-day 1.3E-05 mg/kg-day 8.7E-04Benzo(a)anthracene 6.7E-01 mg/kg 2.2E-09 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-09 4.7E-09 mg/kg-day NA NA NABenzo(a)pyrene 6.8E-01 mg/kg 2.2E-09 mg/kg-day 7.3E+00 1/(mg/kg-day) 2E-08 4.8E-09 mg/kg-day NA NA NABenzo(b)fluoranthene 9.7E-01 mg/kg 3.1E-09 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-09 6.9E-09 mg/kg-day NA NA NABis(2-ethylhexyl)phthalate 2.1E+01 mg/kg 2.5E-08 mg/kg-day 1.4E-02 1/(mg/kg-day) 4E-10 1.5E-07 mg/kg-day 2.0E-02 mg/kg-day 7.4E-06Dibenz(a,h)anthracene 8.6E-02 mg/kg 2.8E-10 mg/kg-day 7.3E+00 1/(mg/kg-day) 2E-09 6.1E-10 mg/kg-day NA NA NAIndeno(1,2,3-cd)pyrene 2.7E-01 mg/kg 8.6E-10 mg/kg-day 7.3E-01 1/(mg/kg-day) 6E-10 1.9E-09 mg/kg-day NA NA NA


Page 2 of 3








Sediment Sediment Wetland Sediment Dermal Aluminum 1.3E+04 mg/kg NA NA NA NA NA NA NA 1.0E+00 mg/kg-day NA(0 to 6 inches) Antimony 2.2E+01 mg/kg NA NA NA NA NA NA NA 6.0E-05 mg/kg-day NA

(On-site) Arsenic 3.2E+01 mg/kg 7.6E-08 mg/kg-day 1.5E+00 1/(mg/kg-day) 1E-07 4.4E-07 mg/kg-day 3.0E-04 mg/kg-day 1.5E-03Barium 6.5E+02 mg/kg NA NA NA NA NA NA NA 1.4E-02 mg/kg-day NACadmium 7.1E+00 mg/kg 5.5E-10 mg/kg-day NA NA NA 3.2E-09 mg/kg-day 2.5E-05 mg/kg-day 1.3E-04Chromium 2.7E+03 mg/kg NA NA NA NA NA NA NA 2.0E-02 mg/kg-day NACobalt 2.0E+01 mg/kg NA NA NA NA NA NA NA 3.0E-04 mg/kg-day NACopper 2.1E+02 mg/kg NA NA NA NA NA NA NA 4.0E-02 mg/kg-day NAIron 3.1E+04 mg/kg NA NA NA NA NA NA NA 7.0E-01 mg/kg-day NALead 1.6E+02 mg/kg NA NA NA NA NA NA NA NA NA NAManganese 8.8E+03 mg/kg NA NA NA NA NA NA NA 9.6E-04 mg/kg-day NAMercury 4.2E+01 mg/kg NA NA NA NA NA NA NA 2.1E-05 mg/kg-day NANickel 8.9E+01 mg/kg NA NA NA NA NA NA NA 8.0E-04 mg/kg-day NAThallium 3.5E+01 mg/kg NA NA NA NA NA NA NA NA NA NAVanadium 5.4E+01 mg/kg NA NA NA NA NA NA NA 1.3E-04 mg/kg-day NAZinc 8.3E+02 mg/kg NA NA NA NA NA NA NA 3.0E-01 mg/kg-day NA2,3,7,8-TCDD TEQ 2.0E-03 mg/kg 4.8E-12 mg/kg-day 1.3E+05 1/(mg/kg-day) 6E-07 2.8E-11 mg/kg-day 7.0E-10 mg/kg-day 4.0E-02Total Aroclors 1.8E+02 mg/kg 1.9E-06 mg/kg-day 2.0E+00 1/(mg/kg-day) 4E-06 1.1E-05 mg/kg-day 2.0E-05 mg/kg-day 5.6E-01Total PCBs 2.6E+02 mg/kg 2.8E-06 mg/kg-day 2.0E+00 1/(mg/kg-day) 6E-06 1.7E-05 mg/kg-day 2.0E-05 mg/kg-day 8.3E-01Aldrin 3.0E+00 mg/kg NA NA 1.7E+01 1/(mg/kg-day) NA NA NA 3.0E-05 mg/kg-day NABHC (beta) 6.7E+00 mg/kg 5.2E-08 mg/kg-day 1.8E+00 1/(mg/kg-day) 9E-08 3.0E-07 mg/kg-day NA NA NAHeptachlor epoxide 1.6E+00 mg/kg NA NA 9.1E+00 1/(mg/kg-day) NA NA NA 1.3E-05 mg/kg-day NABenzo(a)anthracene 6.7E-01 mg/kg 1.8E-08 mg/kg-day 7.3E-01 1/(mg/kg-day) 1E-08 3.9E-08 mg/kg-day NA NA NABenzo(a)pyrene 6.8E-01 mg/kg 1.8E-08 mg/kg-day 7.3E+00 1/(mg/kg-day) 1E-07 4.0E-08 mg/kg-day NA NA NABenzo(b)fluoranthene 9.7E-01 mg/kg 2.6E-08 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-08 5.7E-08 mg/kg-day NA NA NABis(2-ethylhexyl)phthalate 2.1E+01 mg/kg 1.6E-07 mg/kg-day 1.4E-02 1/(mg/kg-day) 2E-09 9.5E-07 mg/kg-day 2.0E-02 mg/kg-day 4.8E-05Dibenz(a,h)anthracene 8.6E-02 mg/kg 2.3E-09 mg/kg-day 7.3E+00 1/(mg/kg-day) 2E-08 5.1E-09 mg/kg-day NA NA NAIndeno(1,2,3-cd)pyrene 2.7E-01 mg/kg 7.2E-09 mg/kg-day 7.3E-01 1/(mg/kg-day) 5E-09 1.6E-08 mg/kg-day NA NA NA


5E-06 6.4E-018E-06 9.9E-015E-06 6.4E-018E-06 9.9E-01

Sediment Total (Total Aroclors)1 5E-06 6.4E-01Sediment Total (Total PCBs)2 8E-06 9.9E-01Receptor Total (Total Aroclors)1 6E-06 7.5E-01Receptor Total (Total PCBs)2 9E-06 1.1E+00Notes:NA = Not applicable or not available1The total includes estimated risks/HIs for Total Aroclors in sediment but not for 2,3,7,8-TCDD TEQ and Total PCBs in sediment.2The total includes estimated risks/HIs for 2,3,7,8-TCDD TEQ and Total PCBs in sediment but not for Total Aroclors in sediment.3COPCs acting with a mutagenic mode of action (refer to Table 6.1 of Attachment A) were evaluated using an age dependent adjustment factor of 3.





Page 3 of 3

TABLE 7.2.RME SUPPLEMENT A

CALCULATION OF DAEVENT

REASONABLE MAXIMUM EXPOSURE


Chemical Surface Water Permeability Lag Fraction Durationof Potential Concentration Coefficient Time Absorbed Water of Event

Concern (CW) (Kp) B (event) t* (FA) (tevent) DAevent(ug/L) (cm/hr) (dimensionless) (hr) (hr) (dimensionless) (hr) (mg/cm2-event) Eq

Aluminum 1.9E+03 1.0E-03 NA NA NA NA 1.0 1.9E-06 1

Antimony, Dissolved 8.8E-01 1.0E-03 NA NA NA NA 1.0 8.8E-10 1

Arsenic 7.3E+00 1.0E-03 NA NA NA NA 1.0 7.3E-09 1

Cobalt, Dissolved 5.2E+00 1.0E-04 NA NA NA NA 1.0 5.2E-10 1

Cyanide 3.3E+00 1.0E-03 NA NA NA NA 1.0 3.3E-09 1

Iron 1.7E+04 1.0E-03 NA NA NA NA 1.0 1.7E-05 1

Lead 8.2E+00 6.0E-04 NA NA NA NA 1.0 4.9E-09 1

Manganese 7.0E+03 1.0E-03 NA NA NA NA 1.0 7.0E-06 1

Mercury 9.7E-01 1.0E-03 NA NA NA NA 1.0 9.7E-10 1

Silver 4.7E+01 6.0E-04 NA NA NA NA 1.0 2.8E-08 1

Total Aroclors 2.7E-01 5.5E-01 3.6E+00 4.5E+00 1.9E+01 1.0E+00 1.0 8.6E-07 2

Aldrin 4.3E-03 2.9E-01 2.2E+00 1.2E+01 4.8E+01 1.0E+00 1.0 1.2E-08 2

Chlordane (beta) 3.4E-02 1.1E-01 8.3E-01 2.1E+01 8.0E+01 2.0E+00 1.0 9.2E-08 2

Heptachlor 9.0E-03 1.4E-01 1.1E+00 1.3E+01 5.0E+01 1.0E+00 1.0 1.3E-08 2

Heptachlor epoxide 3.4E-03 2.1E-02 1.6E-01 1.6E+01 3.8E+01 1.0E+00 1.0 7.8E-10 2

Benzo(a)anthracene 3.2E+00 5.5E-01 3.2E+00 2.0E+00 8.5E+00 1.0E+00 1.0 6.9E-06 2

Benzo(a)pyrene 2.4E+00 7.1E-01 4.4E+00 2.7E+00 1.2E+01 1.0E+00 1.0 7.8E-06 2

Benzo(b)fluoranthene 3.0E+00 4.2E-01 2.5E+00 2.7E+00 1.1E+01 1.0E+00 1.0 5.7E-06 2

Benzo(k)fluoranthene 3.7E+00 6.9E-01 4.2E+00 2.7E+00 1.2E+01 1.0E+00 1.0 1.2E-05 2

Dibenz(a,h)anthracene 3.8E+00 9.5E-01 6.1E+00 3.8E+00 1.7E+01 1.0E+00 1.0 2.0E-05 2

Indeno(1,2,3-cd)pyrene 3.7E+00 1.2E+00 7.9E+00 3.7E+00 1.7E+01 1.0E+00 1.0 2.4E-05 2

Benzene 5.7E-01 1.5E-02 5.1E-02 2.9E-01 6.9E-01 1.0E+00 1.0 1.3E-08 3

Trichloroethene 2.3E+00 1.2E-02 5.1E-02 5.7E-01 1.4E+00 1.0E+00 1.0 5.5E-08 2

Vinyl Chloride 2.9E-01 8.4E-03 2.5E-02 2.4E-01 5.7E-01 1.0E+00 1.0 3.5E-09 3

Inorganics: DAevent (mg/cm2-event) = DAevent = Kp x CW x tevent x 0.001 mg/ug x 0.001 l/cm

3 (Eq 1)

Organics: DAevent (mg/cm2-event) = DAevent = tevent ≤ t*: DAevent (mg/cm2-event) =

2 x FA x Kp x Cw x (sqrt((6 x x tevent) / (3.1415))) x CF1 x CF2 (Eq 2)

tevent>t*: DAevent (mg/cm2-event) =

FA x Kp x CW x ( tevent/(1+B) + 2 x x ((1 + 3B + 3B2)/(1+B)2)) xCF1 x CF2 (Eq 3)

Notes:

Values for permeability constants, B, tau, t*, and FA are from EPA 2004, Risk Assessment Guidance for Superfund Volume I: Human Health Evaluation Manual (Part E, Supplemental Guidance for Dermal Risk Assessment - Final). EPA/540/R/99/005.

B - Dimensionless ratio of the permeability coefficient of a compound through the stratum corneum relative to its permeability

coefficient across the viable epidermis (dimensionless).

cm/hr - centimeter per hour

hr - hour

mg/cm2-event - milligram per square centimeter per event

µg/L - microgram per liter

NA - Not applicable

t* - Time to reach steady-state

CF1 - Conversion Factor 1 (0.001 mg/μg), CF2 - Conversion Factor 2 (0.001 L/cm 3)

Page 1 of 1




Receptor Age: Adult


Potential Concern Value Units Intake/Exposure Concentration CSF Cancer

Risk

Intake/Exposure

ConcentrationRfD Hazard

Quotient


Fish Fish Ingestion 2,3,7,8-TCDD TEQ 9.9E-05 mg/kg-fish 2.3E-10 mg/kg/day 1.3E+05 1/(mg/kg/day) 3E-05 2.0E-09 mg/kg/day 7.0E-10 mg/kg/day 2.9E+00(white perch) Total PCBs 9.0E+00 mg/kg-fish 2.1E-05 mg/kg/day 2.0E+00 1/(mg/kg/day) 4E-05 1.8E-04 mg/kg/day 2.0E-05 mg/kg/day 9.2E+00

Exp. Route Total 7E-05 1.2E+017E-05 1.2E+017E-05 1.2E+01

Sediment/Surface Water Total 7E-05 1.2E+01Receptor Total 7E-05 1.2E+01

Receptor Population: Fish Consumer

Exposure Point TotalExposure Medium Total

Sediment/Surface Water

Page 1 of 1




Receptor Age: Older Child



RiskIntake/Exposure Concentration RfD Hazard

Quotient








Page 1 of 1




Receptor Age: Younger Child



RiskIntake/Exposure Concentration RfD Hazard

Quotient








Page 1 of 1



Scenario Timeframe: Current/FutureReceptor Population: Off-Site TrespasserReceptor Age: Adult




Quotient


Sediment Sediment Sediment Ingestion Aluminum 1.7E+04 mg/kg 8.6E-06 mg/kg-day NA NA NA 7.6E-05 mg/kg-day 1.0E+00 mg/kg-day 7.6E-05(Ackermans South) (0 to 6 inches) Antimony 3.7E+00 mg/kg 1.9E-09 mg/kg-day NA NA NA 1.6E-08 mg/kg-day 4.0E-04 mg/kg-day 4.1E-05

(Ackermans South) Arsenic 6.8E+01 mg/kg 3.5E-08 mg/kg-day 1.5E+00 1/(mg/kg-day) 5E-08 3.0E-07 mg/kg-day 3.0E-04 mg/kg-day 1.0E-03Barium 2.8E+03 mg/kg 1.4E-06 mg/kg-day NA NA NA 1.2E-05 mg/kg-day 2.0E-01 mg/kg-day 6.2E-05Cobalt 8.7E+01 mg/kg 4.4E-08 mg/kg-day NA NA NA 3.9E-07 mg/kg-day 3.0E-04 mg/kg-day 1.3E-03Iron 9.9E+04 mg/kg 5.0E-05 mg/kg-day NA NA NA 4.4E-04 mg/kg-day 7.0E-01 mg/kg-day 6.3E-04Manganese 9.3E+04 mg/kg 4.7E-05 mg/kg-day NA NA NA 4.1E-04 mg/kg-day 2.4E-02 mg/kg-day 1.7E-02Mercury 3.5E+01 mg/kg 1.8E-08 mg/kg-day NA NA NA 1.6E-07 mg/kg-day 3.0E-04 mg/kg-day 5.3E-04Nickel 1.6E+02 mg/kg 8.1E-08 mg/kg-day NA NA NA 7.1E-07 mg/kg-day 2.0E-02 mg/kg-day 3.6E-05Vanadium 1.0E+02 mg/kg 5.1E-08 mg/kg-day NA NA NA 4.5E-07 mg/kg-day 5.0E-03 mg/kg-day 8.9E-05Benzo(a)anthracene 6.4E-01 mg/kg 3.3E-10 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-10 2.8E-09 mg/kg-day NA NA NABenzo(a)pyrene 7.8E-01 mg/kg 4.0E-10 mg/kg-day 7.3E+00 1/(mg/kg-day) 3E-09 3.5E-09 mg/kg-day NA NA NABenzo(b)fluoranthene 1.0E+00 mg/kg 5.1E-10 mg/kg-day 7.3E-01 1/(mg/kg-day) 4E-10 4.5E-09 mg/kg-day NA NA NADibenz(a,h)anthracene 2.7E-01 mg/kg 1.4E-10 mg/kg-day 7.3E+00 1/(mg/kg-day) 1E-09 1.2E-09 mg/kg-day NA NA NAIndeno(1,2,3-cd)pyrene 6.5E-01 mg/kg 3.3E-10 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-10 2.9E-09 mg/kg-day NA NA NA2,3,7,8-TCDD TEQ 5.5E-05 mg/kg 2.8E-14 mg/kg-day 1.3E+05 1/(mg/kg-day) 4E-09 2.4E-13 mg/kg-day 7.0E-10 mg/kg-day 3.5E-04Total Aroclors 6.4E+01 mg/kg 3.2E-08 mg/kg-day 2.0E+00 1/(mg/kg-day) 6E-08 2.8E-07 mg/kg-day 2.0E-05 mg/kg-day 1.4E-02Total PCBs 2.4E+00 mg/kg 1.2E-09 mg/kg-day 2.0E+00 1/(mg/kg-day) 2E-09 1.1E-08 mg/kg-day 2.0E-05 mg/kg-day 5.4E-04


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Quotient


Sediment Sediment Sediment Dermal Aluminum 1.7E+04 mg/kg NA NA NA NA NA NA NA 1.0E+00 mg/kg-day NA(Ackermans South) (0 to 6 inches) Antimony 3.7E+00 mg/kg NA NA NA NA NA NA NA 6.0E-05 mg/kg-day NA

(Ackermans South) Arsenic 6.8E+01 mg/kg 1.6E-07 mg/kg-day 1.5E+00 1/(mg/kg-day) 2E-07 1.4E-06 mg/kg-day 3.0E-04 mg/kg-day 4.7E-03Barium 2.8E+03 mg/kg NA NA NA NA NA NA NA 1.4E-02 mg/kg-day NACobalt 8.7E+01 mg/kg NA NA NA NA NA NA NA 3.0E-04 mg/kg-day NAIron 9.9E+04 mg/kg NA NA NA NA NA NA NA 7.0E-01 mg/kg-day NAManganese 9.3E+04 mg/kg NA NA NA NA NA NA NA 9.6E-04 mg/kg-day NAMercury 3.5E+01 mg/kg NA NA NA NA NA NA NA 2.1E-05 mg/kg-day NANickel 1.6E+02 mg/kg NA NA NA NA NA NA NA 8.0E-04 mg/kg-day NAVanadium 1.0E+02 mg/kg NA NA NA NA NA NA NA 1.3E-04 mg/kg-day NABenzo(a)anthracene 6.4E-01 mg/kg 6.6E-09 mg/kg-day 7.3E-01 1/(mg/kg-day) 5E-09 5.8E-08 mg/kg-day NA NA NABenzo(a)pyrene 7.8E-01 mg/kg 8.1E-09 mg/kg-day 7.3E+00 1/(mg/kg-day) 6E-08 7.1E-08 mg/kg-day NA NA NABenzo(b)fluoranthene 1.0E+00 mg/kg 1.0E-08 mg/kg-day 7.3E-01 1/(mg/kg-day) 8E-09 9.1E-08 mg/kg-day NA NA NADibenz(a,h)anthracene 2.7E-01 mg/kg 2.8E-09 mg/kg-day 7.3E+00 1/(mg/kg-day) 2E-08 2.5E-08 mg/kg-day NA NA NAIndeno(1,2,3-cd)pyrene 6.5E-01 mg/kg 6.7E-09 mg/kg-day 7.3E-01 1/(mg/kg-day) 5E-09 5.9E-08 mg/kg-day NA NA NA2,3,7,8-TCDD TEQ 5.5E-05 mg/kg 1.3E-13 mg/kg-day 1.3E+05 1/(mg/kg-day) 2E-08 1.1E-12 mg/kg-day 7.0E-10 mg/kg-day 1.6E-03Total Aroclors 6.4E+01 mg/kg 7.1E-07 mg/kg-day 2.0E+00 1/(mg/kg-day) 1E-06 6.2E-06 mg/kg-day 2.0E-05 mg/kg-day 3.1E-01Total PCBs 2.4E+00 mg/kg 2.7E-08 mg/kg-day 2.0E+00 1/(mg/kg-day) 5E-08 2.4E-07 mg/kg-day 2.0E-05 mg/kg-day 1.2E-02


2E-06 3.5E-015E-07 4.0E-022E-06 3.5E-015E-07 4.0E-02

Sediment Total (Total Aroclors)1 2E-06 3.5E-01Sediment Total (Total PCBs)2 5E-07 4.0E-02Receptor Total (Total Aroclors)1 2E-06 3.5E-01Receptor Total (Total PCBs)2 5E-07 4.0E-02Notes:NA = Not applicable or not available1The total includes estimated risks/HIs for Total Aroclors in sediment but not for 2,3,7,8-TCDD TEQ and Total PCBs in sediment.2The total includes estimated risks/HIs for 2,3,7,8-TCDD TEQ and Total PCBs in sediment but not for Total Aroclors in sediment.





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Scenario Timeframe: Current/FutureReceptor Population: Off-Site TrespasserReceptor Age: Older Child





Sediment Sediment Sediment Ingestion Aluminum 1.7E+04 mg/kg 2.1E-05 mg/kg-day NA NA NA 1.2E-04 mg/kg-day 1.0E+00 mg/kg-day 1.2E-04(Ackermans South) (0 to 6 inches) Antimony 3.7E+00 mg/kg 4.5E-09 mg/kg-day NA NA NA 2.6E-08 mg/kg-day 4.0E-04 mg/kg-day 6.6E-05

(Ackermans South) Arsenic 6.8E+01 mg/kg 8.3E-08 mg/kg-day 1.5E+00 1/(mg/kg-day) 1E-07 4.8E-07 mg/kg-day 3.0E-04 mg/kg-day 1.6E-03Barium 2.8E+03 mg/kg 3.4E-06 mg/kg-day NA NA NA 2.0E-05 mg/kg-day 2.0E-01 mg/kg-day 9.9E-05Cobalt 8.7E+01 mg/kg 1.1E-07 mg/kg-day NA NA NA 6.2E-07 mg/kg-day 3.0E-04 mg/kg-day 2.1E-03Iron 9.9E+04 mg/kg 1.2E-04 mg/kg-day NA NA NA 7.0E-04 mg/kg-day 7.0E-01 mg/kg-day 1.0E-03Manganese 9.3E+04 mg/kg 1.1E-04 mg/kg-day NA NA NA 6.6E-04 mg/kg-day 2.4E-02 mg/kg-day 2.7E-02Mercury 3.5E+01 mg/kg 4.3E-08 mg/kg-day NA NA NA 2.5E-07 mg/kg-day 3.0E-04 mg/kg-day 8.4E-04Nickel 1.6E+02 mg/kg 1.9E-07 mg/kg-day NA NA NA 1.1E-06 mg/kg-day 2.0E-02 mg/kg-day 5.7E-05Vanadium 1.0E+02 mg/kg 1.2E-07 mg/kg-day NA NA NA 7.1E-07 mg/kg-day 5.0E-03 mg/kg-day 1.4E-04Benzo(a)anthracene 6.4E-01 mg/kg 2.1E-09 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-09 4.5E-09 mg/kg-day NA NA NABenzo(a)pyrene 7.8E-01 mg/kg 2.5E-09 mg/kg-day 7.3E+00 1/(mg/kg-day) 2E-08 5.5E-09 mg/kg-day NA NA NABenzo(b)fluoranthene 1.0E+00 mg/kg 3.2E-09 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-09 7.1E-09 mg/kg-day NA NA NADibenz(a,h)anthracene 2.7E-01 mg/kg 8.8E-10 mg/kg-day 7.3E+00 1/(mg/kg-day) 6E-09 1.9E-09 mg/kg-day NA NA NAIndeno(1,2,3-cd)pyrene 6.5E-01 mg/kg 2.1E-09 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-09 4.6E-09 mg/kg-day NA NA NA2,3,7,8-TCDD TEQ 5.5E-05 mg/kg 6.7E-14 mg/kg-day 1.3E+05 1/(mg/kg-day) 9E-09 3.9E-13 mg/kg-day 7.0E-10 mg/kg-day 5.5E-04Total Aroclors 6.4E+01 mg/kg 7.7E-08 mg/kg-day 2.0E+00 1/(mg/kg-day) 2E-07 4.5E-07 mg/kg-day 2.0E-05 mg/kg-day 2.3E-02Total PCBs 2.4E+00 mg/kg 2.9E-09 mg/kg-day 2.0E+00 1/(mg/kg-day) 6E-09 1.7E-08 mg/kg-day 2.0E-05 mg/kg-day 8.5E-04


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Sediment Sediment Sediment Dermal Aluminum 1.7E+04 mg/kg NA NA NA NA NA NA NA 1.0E+00 mg/kg-day NA(Ackermans South) (0 to 6 inches) Antimony 3.7E+00 mg/kg NA NA NA NA NA NA NA 6.0E-05 mg/kg-day NA

(Ackermans South) Arsenic 6.8E+01 mg/kg 1.6E-07 mg/kg-day 1.5E+00 1/(mg/kg-day) 2E-07 9.3E-07 mg/kg-day 3.0E-04 mg/kg-day 3.1E-03Barium 2.8E+03 mg/kg NA NA NA NA NA NA NA 1.4E-02 mg/kg-day NACobalt 8.7E+01 mg/kg NA NA NA NA NA NA NA 3.0E-04 mg/kg-day NAIron 9.9E+04 mg/kg NA NA NA NA NA NA NA 7.0E-01 mg/kg-day NAManganese 9.3E+04 mg/kg NA NA NA NA NA NA NA 9.6E-04 mg/kg-day NAMercury 3.5E+01 mg/kg NA NA NA NA NA NA NA 2.1E-05 mg/kg-day NANickel 1.6E+02 mg/kg NA NA NA NA NA NA NA 8.0E-04 mg/kg-day NAVanadium 1.0E+02 mg/kg NA NA NA NA NA NA NA 1.3E-04 mg/kg-day NABenzo(a)anthracene 6.4E-01 mg/kg 1.7E-08 mg/kg-day 7.3E-01 1/(mg/kg-day) 1E-08 3.8E-08 mg/kg-day NA NA NABenzo(a)pyrene 7.8E-01 mg/kg 2.1E-08 mg/kg-day 7.3E+00 1/(mg/kg-day) 2E-07 4.6E-08 mg/kg-day NA NA NABenzo(b)fluoranthene 1.0E+00 mg/kg 2.7E-08 mg/kg-day 7.3E-01 1/(mg/kg-day) 2E-08 5.9E-08 mg/kg-day NA NA NADibenz(a,h)anthracene 2.7E-01 mg/kg 7.3E-09 mg/kg-day 7.3E+00 1/(mg/kg-day) 5E-08 1.6E-08 mg/kg-day NA NA NAIndeno(1,2,3-cd)pyrene 6.5E-01 mg/kg 1.8E-08 mg/kg-day 7.3E-01 1/(mg/kg-day) 1E-08 3.8E-08 mg/kg-day NA NA NA2,3,7,8-TCDD TEQ 5.5E-05 mg/kg 1.3E-13 mg/kg-day 1.3E+05 1/(mg/kg-day) 2E-08 7.5E-13 mg/kg-day 7.0E-10 mg/kg-day 1.1E-03Total Aroclors 6.4E+01 mg/kg 6.9E-07 mg/kg-day 2.0E+00 1/(mg/kg-day) 1E-06 4.0E-06 mg/kg-day 2.0E-05 mg/kg-day 2.0E-01Total PCBs 2.4E+00 mg/kg 2.6E-08 mg/kg-day 2.0E+00 1/(mg/kg-day) 5E-08 1.5E-07 mg/kg-day 2.0E-05 mg/kg-day 7.7E-03


2E-06 2.6E-017E-07 4.7E-022E-06 2.6E-017E-07 4.7E-02

Sediment Total (Total Aroclors)1 2E-06 2.6E-01Sediment Total (Total PCBs)2 7E-07 4.7E-02Receptor Total (Total Aroclors)1 2E-06 2.6E-01Receptor Total (Total PCBs)2 7E-07 4.7E-02Notes:NA = Not applicable or not available1The total includes estimated risks/HIs for Total Aroclors in sediment but not for 2,3,7,8-TCDD TEQ and Total PCBs in sediment.2The total includes estimated risks/HIs for 2,3,7,8-TCDD TEQ and Total PCBs in sediment but not for Total Aroclors in sediment.





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TABLE 9.1.RMESUMMARY OF RECEPTOR RISKS AND HAZARDS FOR COPCs



Medium Exposure Exposure Chemical Carcinogenic Risk Non-Carcinogenic Hazard Quotient

Medium Point of Potential

Concern Ingestion Inhalation Dermal Exposure Primary Ingestion Inhalation Dermal Exposure

Routes Total Target Organ(s) Routes Total

Surface Water Surface Water Wetland Surface Water Aluminum NA NA NA NA Nervous System NA NA 4E-06 4E-06 Antimony, Dissolved NA NA NA NA Lifetime, Hematologic NA NA 3E-05 3E-05

Arsenic NA NA 3E-09 3E-09 Dermal, Cardiovascular System NA NA 6E-05 6E-05Cobalt, Dissolved NA NA NA NA Endocrine System NA NA 4E-06 4E-06Cyanide NA NA NA NA Reproductive NA NA 1E-05 1E-05Iron NA NA NA NA Gastrointestinal NA NA 5E-05 5E-05Lead NA NA NA NA NA NA NA NA NAManganese NA NA NA NA Nervous System NA NA 2E-02 2E-02Mercury NA NA NA NA Immune System, Urinary System NA NA 1E-04 1E-04Silver NA NA NA NA Dermal NA NA 3E-04 3E-04Total Aroclors NA NA 5E-07 5E-07 Dermal, Immune System, and Ocular NA NA 1E-01 1E-01Aldrin NA NA 5E-08 5E-08 Liver NA NA 9E-04 9E-04Chlordane (beta) NA NA 9E-09 9E-09 Liver NA NA 4E-04 4E-04Heptachlor NA NA 2E-08 2E-08 Liver NA NA 6E-05 6E-05Heptachlor epoxide NA NA 2E-09 2E-09 Liver NA NA 1E-04 1E-04Benzo(a)anthracene NA NA NA NA NA NA NA NA NABenzo(a)pyrene NA NA NA NA NA NA NA NA NABenzo(b)fluoranthene NA NA NA NA NA NA NA NA NABenzo(k)fluoranthene NA NA NA NA NA NA NA NA NADibenz(a,h)anthracene NA NA NA NA NA NA NA NA NAIndeno(1,2,3-cd)pyrene NA NA NA NA NA NA NA NA NABenzene NA NA 2E-10 2E-10 Immune System NA NA 8E-06 8E-06Trichloroethene NA NA 7E-10 7E-10 Developmental, Cardiovascular System, Immune System NA NA 3E-04 3E-04Vinyl Chloride NA NA 7E-10 7E-10 Liver NA NA 3E-06 3E-06

Exposure Point Total NA NA 5E-07 5E-07 NA NA 1E-01 1E-01Exposure Medium Total NA NA 5E-07 5E-07 NA NA 1E-01 1E-01

Medium Total NA NA 5E-07 5E-07 NA NA 1E-01 1E-01

Sediment Sediment Wetland Sediment Aluminum NA NA NA NA Nervous System 6E-05 NA NA 6E-05(0 to 6 inches) Antimony NA NA NA NA Lifetime, Hematologic 2E-04 NA NA 2E-04

(On-site) Arsenic 2E-08 NA 1E-07 1E-07 Dermal, Cardiovascular System 5E-04 NA 2E-03 3E-03Barium NA NA NA NA Urinary System 1E-05 NA NA 1E-05Cadmium NA NA NA NA Urinary System 6E-05 NA 2E-04 3E-04Chromium NA NA NA NA NOE 8E-06 NA NA 8E-06Cobalt NA NA NA NA Endocrine System 3E-04 NA NA 3E-04Copper NA NA NA NA Gastrointestinal 2E-05 NA NA 2E-05Iron NA NA NA NA Gastrointestinal 2E-04 NA NA 2E-04Lead NA NA NA NA NA NA NA NA NAManganese NA NA NA NA Nervous System 2E-03 NA NA 2E-03Mercury NA NA NA NA Immune System, Urinary System 6E-04 NA NA 6E-04Nickel NA NA NA NA Body Weight, Organ Weight 2E-05 NA NA 2E-05Thallium NA NA NA NA NA NA NA NA NAVanadium NA NA NA NA Dermal 5E-05 NA NA 5E-05Zinc NA NA NA NA Immune System, Hematologic 1E-05 NA NA 1E-052,3,7,8-TCDD TEQ 1E-07 NA 6E-07 8E-07 Developmental, Endocrine System, Reproductive 1E-02 NA 6E-02 7E-02Total Aroclors 2E-07 NA 4E-06 4E-06 Dermal, Immune System, and Ocular 4E-02 NA 9E-01 9E-01

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Total PCBs 3E-07 NA 6E-06 6E-06 Dermal, Immune System, and Ocular 6E-02 NA 1E+00 1E+00Aldrin 3E-08 NA NA 3E-08 Liver 4E-04 NA NA 4E-04BHC (beta) 6E-09 NA 1E-07 1E-07 NA NA NA NA NAHeptachlor epoxide 7E-09 NA NA 7E-09 Liver 5E-04 NA NA 5E-04Benzo(a)anthracene 2E-10 NA 5E-09 5E-09 NA NA NA NA NABenzo(a)pyrene 3E-09 NA 5E-08 5E-08 NA NA NA NA NABenzo(b)fluoranthene 4E-10 NA 7E-09 8E-09 NA NA NA NA NABis(2-ethylhexyl)phthalate 1E-10 NA 2E-09 2E-09 Liver 5E-06 NA 7E-05 8E-05Dibenz(a,h)anthracene 3E-10 NA 7E-09 7E-09 NA NA NA NA NAIndeno(1,2,3-cd)pyrene 1E-10 NA 2E-09 2E-09 NA NA NA NA NA

2E-07 NA 4E-06 5E-06 4E-02 NA 9E-01 9E-015E-07 NA 7E-06 7E-06 8E-02 NA 1E+00 1E+002E-07 NA 4E-06 5E-06 4E-02 NA 9E-01 9E-015E-07 NA 7E-06 7E-06 8E-02 NA 1E+00 1E+00

Medium Total (Total Aroclors)1 2E-07 NA 4E-06 5E-06 4E-02 NA 9E-01 9E-01Medium Total (Total PCBs)2 5E-07 NA 7E-06 7E-06 8E-02 NA 1E+00 1E+00Receptor Total (Total Aroclors)1 2E-07 NA 5E-06 5E-06 4E-02 NA 1E+00 1E+00Receptor Total (Total PCBs)2 5E-07 NA 7E-06 8E-06 8E-02 NA 1E+00 2E+00

NA = Not applicable or not availableNOE = No Observed Effects Total Hematologic HI Across Media = 0.00031The total includes estimated risks/HIs for Total Aroclors in sediment but not for PCB TEQ and Total PCBs in sediment. Total Reproductive HI Across Media = 0.072The total includes estimated risks/HIs for PCB TEQ and Total PCBs in sediment but not for Total Aroclors in sediment. Total Gastrointestinal HI Across Media = 0.00033The total includes estimated HIs for Total Aroclors in sediment but not for Total PCBs in sediment. Total Immune System HI Across Media 3 = 14The total includes estimated HIs for Total PCBs in sediment but not for Total Aroclors in sediment. Total Immune System HI Across Media 4 = 1

Total Urinary System HI Across Media = 0.001Total Liver HI Across Media = 0.003

Total Nervous System HI Across Media = 0.02Total Body Weight HI Across Media = 0.00002

Total Dermal HI Across Media3 = 1Total Dermal HI Across Media4 = 1

Total Developmental HI Across Media = 0.07Total Cardiovascular System HI Across Media = 0.003

Total Endocrine System HI Across Media = 0.07Total Organ Weight HI Across Media = 0.00002

Total NOE HI Across Media = 0.000008Total Ocular HI Across Media3 = 1Total Ocular HI Across Media4 = 1

Total Lifetime HI Across Media = 0.0003


Exposure Medium Total (Total Aroclors)1Exposure Point Total (Total PCBs)2


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Surface Water Surface Water Wetland Surface Water Aluminum NA NA NA NA Nervous System NA NA 4E-06 4E-06Antimony, Dissolved NA NA NA NA Lifetime, Hematologic NA NA 3E-05 3E-05Arsenic NA NA 4E-09 4E-09 Dermal, Cardiovascular System NA NA 6E-05 6E-05Cobalt, Dissolved NA NA NA NA Endocrine System NA NA 4E-06 4E-06Cyanide NA NA NA NA Reproductive NA NA 1E-05 1E-05Iron NA NA NA NA Gastrointestinal NA NA 5E-05 5E-05Lead NA NA NA NA NA NA NA NA NAManganese NA NA NA NA Nervous System NA NA 2E-02 2E-02Mercury NA NA NA NA Immune System, Urinary System NA NA 1E-04 1E-04Silver NA NA NA NA Dermal NA NA 3E-04 3E-04Total Aroclors NA NA 7E-07 7E-07 Dermal, Immune System, and Ocular NA NA 1E-01 1E-01Aldrin NA NA 8E-08 8E-08 Liver NA NA 9E-04 9E-04Chlordane (beta) NA NA 1E-08 1E-08 Liver NA NA 4E-04 4E-04Heptachlor NA NA 2E-08 2E-08 Liver NA NA 6E-05 6E-05Heptachlor epoxide NA NA 3E-09 3E-09 Liver NA NA 1E-04 1E-04Benzo(a)anthracene NA NA NA NA NA NA NA NA NABenzo(a)pyrene NA NA NA NA NA NA NA NA NABenzo(b)fluoranthene NA NA NA NA NA NA NA NA NABenzo(k)fluoranthene NA NA NA NA NA NA NA NA NADibenz(a,h)anthracene NA NA NA NA NA NA NA NA NAIndeno(1,2,3-cd)pyrene NA NA NA NA NA NA NA NA NABenzene NA NA 3E-10 3E-10 Immune System NA NA 8E-06 8E-06Trichloroethene NA NA 1E-09 1E-09 Developmental, Cardiovascular System, Immune System NA NA 3E-04 3E-04Vinyl Chloride NA NA 1E-09 1E-09 Liver NA NA 3E-06 3E-06

Exposure Point Total NA NA 8E-07 8E-07 NA NA 1E-01 1E-01Exposure Medium Total NA NA 8E-07 8E-07 NA NA 1E-01 1E-01

Medium Total NA NA 8E-07 8E-07 NA NA 1E-01 1E-01

Sediment Sediment Wetland Sediment Aluminum NA NA NA NA Nervous System 9E-05 NA NA 9E-05(0 to 6 inches) Antimony NA NA NA NA Lifetime, Hematologic 4E-04 NA NA 4E-04

(On-site) Arsenic 6E-08 NA 1E-07 2E-07 Dermal, Cardiovascular System 8E-04 NA 1E-03 2E-03Barium NA NA NA NA Urinary System 2E-05 NA NA 2E-05Cadmium NA NA NA NA Urinary System 1E-04 NA 1E-04 2E-04Chromium NA NA NA NA NOE 1E-05 NA NA 1E-05Cobalt NA NA NA NA Endocrine System 5E-04 NA NA 5E-04Copper NA NA NA NA Gastrointestinal 4E-05 NA NA 4E-05Iron NA NA NA NA Gastrointestinal 3E-04 NA NA 3E-04Lead NA NA NA NA NA NA NA NA NAManganese NA NA NA NA Nervous System 3E-03 NA NA 3E-03Mercury NA NA NA NA Immune System, Urinary System 1E-03 NA NA 1E-03Nickel NA NA NA NA Body Weight, Organ Weight 3E-05 NA NA 3E-05Thallium NA NA NA NA NA NA NA NA NAVanadium NA NA NA NA Dermal 8E-05 NA NA 8E-05Zinc NA NA NA NA Immune System, Hematologic 2E-05 NA NA 2E-052,3,7,8-TCDD TEQ 3E-07 NA 6E-07 9E-07 Developmental, Endocrine System, Reproductive 2E-02 NA 4E-02 6E-02

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Total Aroclors 4E-07 NA 4E-06 4E-06 Dermal, Immune System, and Ocular 6E-02 NA 6E-01 6E-01Total PCBs 6E-07 NA 6E-06 6E-06 Dermal, Immune System, and Ocular 9E-02 NA 8E-01 9E-01Aldrin 6E-08 NA NA 6E-08 Liver 7E-04 NA NA 7E-04BHC (beta) 1E-08 NA 9E-08 1E-07 NA NA NA NA NAHeptachlor epoxide 2E-08 NA NA 2E-08 Liver 9E-04 NA NA 9E-04Benzo(a)anthracene 2E-09 NA 1E-08 1E-08 NA NA NA NA NABenzo(a)pyrene 2E-08 NA 1E-07 1E-07 NA NA NA NA NABenzo(b)fluoranthene 2E-09 NA 2E-08 2E-08 NA NA NA NA NABis(2-ethylhexyl)phthalate 4E-10 NA 2E-09 3E-09 Liver 7E-06 NA 5E-05 5E-05Dibenz(a,h)anthracene 2E-09 NA 2E-08 2E-08 NA NA NA NA NAIndeno(1,2,3-cd)pyrene 6E-10 NA 5E-09 6E-09 NA NA NA NA NA

6E-07 NA 4E-06 5E-06 7E-02 NA 6E-01 6E-011E-06 NA 7E-06 8E-06 1E-01 NA 9E-01 1E+006E-07 NA 4E-06 5E-06 7E-02 NA 6E-01 6E-011E-06 NA 7E-06 8E-06 1E-01 NA 9E-01 1E+00

Medium Total (Total Aroclors)1 6E-07 NA 4E-06 5E-06 7E-02 NA 6E-01 6E-01Medium Total (Total PCBs)2 1E-06 NA 7E-06 8E-06 1E-01 NA 9E-01 1E+00Receptor Total (Total Aroclors)1 6E-07 NA 5E-06 6E-06 7E-02 NA 7E-01 8E-01Receptor Total (Total PCBs)2 1E-06 NA 7E-06 9E-06 1E-01 NA 1E+00 1E+00

NA = Not applicable or not availableNOE = No Observed Effects Total Hematologic HI Across Media = 0.00041The total includes estimated risks/HIs for Total Aroclors in sediment but not for PCB TEQ and Total PCBs in sediment. Total Reproductive HI Across Media = 0.062The total includes estimated risks/HIs for PCB TEQ and Total PCBs in sediment but not for Total Aroclors in sediment. Total Gastrointestinal HI Across Media = 0.00043The total includes estimated HIs for Total Aroclors in sediment but not for Total PCBs in sediment. Total Immune System HI Across Media 3 = 0.74The total includes estimated HIs for Total PCBs in sediment but not for Total Aroclors in sediment. Total Immune System HI Across Media 4 = 1

Total Urinary System HI Across Media = 0.001Total Liver HI Across Media = 0.003

Total Nervous System HI Across Media = 0.02Total Body Weight HI Across Media = 0.00003

Total Dermal HI Across Media3 = 0.7Total Dermal HI Across Media4 = 1



Total NOE HI Across Media = 0.00001Total Ocular HI Across Media3 = 0.7Total Ocular HI Across Media4 = 1






Page 2 of 2



Scenario Timeframe: Current/Future Receptor Population: Fish ConsumerReceptor Age: Adult





Sediment/Surface Water Fish Fish 2,3,7,8-TCDD TEQ 3E-05 NA NA 3E-05 Developmental, Endocrine System, Reproductive 3E+00 NA NA 3E+00(white perch) Total PCBs 4E-05 NA NA 4E-05 Dermal, Immune System, and Ocular 9E+00 NA NA 9E+00

7E-05 NA NA 7E-05 1E+01 NA NA 1E+017E-05 NA NA 7E-05 1E+01 NA NA 1E+01

Medium Total 7E-05 NA NA 7E-05 1E+01 NA NA 1E+01Receptor Total 7E-05 NA NA 7E-05 1E+01 NA NA 1E+01

NA = Not available or not applicable Total Reproductive HI Across Media = 3

Total Immune System HI Across Media = 9

Total Dermal HI Across Media = 9

Total Developmental HI Across Media = 3

Total Endocrine System HI Across Media = 3

Total Ocular HI Across Media = 9


Page 1 of 1



Scenario Timeframe: Current/Future Receptor Population: Fish ConsumerReceptor Age: Older Child















Page 1 of 1



Scenario Timeframe: Current/Future Receptor Population: Fish ConsumerReceptor Age: Younger Child















Page 1 of 1








Sediment Sediment Sediment Aluminum NA NA NA NA Nervous System 8E-05 NA NA 8E-05(Ackermans South) (0 to 6 inches) Antimony NA NA NA NA Lifetime, Hematologic 4E-05 NA NA 4E-05

(Ackermans South) Arsenic 5E-08 NA 2E-07 3E-07 Dermal, Cardiovascular System 1E-03 NA 5E-03 6E-03Barium NA NA NA NA Urinary System 6E-05 NA NA 6E-05Cobalt NA NA NA NA Endocrine System 1E-03 NA NA 1E-03Iron NA NA NA NA Gastrointestinal 6E-04 NA NA 6E-04Manganese NA NA NA NA Nervous System 2E-02 NA NA 2E-02Mercury NA NA NA NA Immune System, Urinary System 5E-04 NA NA 5E-04Nickel NA NA NA NA Body Weight, Organ Weight 4E-05 NA NA 4E-05Vanadium NA NA NA NA Dermal 9E-05 NA NA 9E-05Benzo(a)anthracene 2E-10 NA 5E-09 5E-09 NA NA NA NA NABenzo(a)pyrene 3E-09 NA 6E-08 6E-08 NA NA NA NA NABenzo(b)fluoranthene 4E-10 NA 8E-09 8E-09 NA NA NA NA NADibenz(a,h)anthracene 1E-09 NA 2E-08 2E-08 NA NA NA NA NAIndeno(1,2,3-cd)pyrene 2E-10 NA 5E-09 5E-09 NA NA NA NA NA2,3,7,8-TCDD TEQ 4E-09 NA 2E-08 2E-08 Developmental, Endocrine System, Reproductive 3E-04 NA 2E-03 2E-03Total Aroclors 6E-08 NA 1E-06 1E-06 Dermal, Immune System, and Ocular 1E-02 NA 3E-01 3E-01Total PCBs 2E-09 NA 5E-08 6E-08 Dermal, Immune System, and Ocular 5E-04 NA 1E-02 1E-02

1E-07 NA 2E-06 2E-06 4E-02 NA 3E-01 4E-016E-08 NA 4E-07 5E-07 2E-02 NA 2E-02 4E-021E-07 NA 2E-06 2E-06 4E-02 NA 3E-01 4E-016E-08 NA 4E-07 5E-07 2E-02 NA 2E-02 4E-02

Medium Total (Total Aroclors)1 1E-07 NA 2E-06 2E-06 4E-02 NA 3E-01 4E-01Medium Total (Total PCBs)2 6E-08 NA 4E-07 5E-07 2E-02 NA 2E-02 4E-02Receptor Total (Total Aroclors)1 1E-07 NA 2E-06 2E-06 4E-02 NA 3E-01 4E-01Receptor Total (Total PCBs)2 6E-08 NA 4E-07 5E-07 2E-02 NA 2E-02 4E-02

NA = Not applicable or not availableNOE = No Observed Effects Total Hematologic HI Across Media = 0.000041The total includes estimated risks/HIs for Total Aroclors in sediment but not for PCB TEQ and Total PCBs in sediment. Total Reproductive HI Across Media = 0.0022The total includes estimated risks/HIs for PCB TEQ and Total PCBs in sediment but not for Total Aroclors in sediment. Total Gastrointestinal HI Across Media = 0.00063The total includes estimated HIs for Total Aroclors in sediment but not for Total PCBs in sediment. Total Immune System HI Across Media 3 = 0.34The total includes estimated HIs for Total PCBs in sediment but not for Total Aroclors in sediment. Total Immune System HI Across Media 4 = 0.01

Total Urinary System HI Across Media = 0.0006Total Nervous System HI Across Media = 0.02

Total Body Weight HI Across Media = 0.00004Total Dermal HI Across Media3 = 0.3Total Dermal HI Across Media4 = 0.02



Total Ocular HI Across Media3 = 0.3Total Ocular HI Across Media4 = 0.01






Page 1 of 1








Sediment Sediment Sediment Aluminum NA NA NA NA Nervous System 1E-04 NA NA 1E-04(Ackermans South) (0 to 6 inches) Antimony NA NA NA NA Lifetime, Hematologic 7E-05 NA NA 7E-05

(Ackermans South) Arsenic 1E-07 NA 2E-07 4E-07 Dermal, Cardiovascular System 2E-03 NA 3E-03 5E-03Barium NA NA NA NA Urinary System 1E-04 NA NA 1E-04Cobalt NA NA NA NA Endocrine System 2E-03 NA NA 2E-03Iron NA NA NA NA Gastrointestinal 1E-03 NA NA 1E-03Manganese NA NA NA NA Nervous System 3E-02 NA NA 3E-02Mercury NA NA NA NA Immune System, Urinary System 8E-04 NA NA 8E-04Nickel NA NA NA NA Body Weight, Organ Weight 6E-05 NA NA 6E-05Vanadium NA NA NA NA Dermal 1E-04 NA NA 1E-04Benzo(a)anthracene 2E-09 NA 1E-08 1E-08 NA NA NA NA NABenzo(a)pyrene 2E-08 NA 2E-07 2E-07 NA NA NA NA NABenzo(b)fluoranthene 2E-09 NA 2E-08 2E-08 NA NA NA NA NADibenz(a,h)anthracene 6E-09 NA 5E-08 6E-08 NA NA NA NA NAIndeno(1,2,3-cd)pyrene 2E-09 NA 1E-08 1E-08 NA NA NA NA NA2,3,7,8-TCDD TEQ 9E-09 NA 2E-08 3E-08 Developmental, Endocrine System, Reproductive 6E-04 NA 1E-03 2E-03Total Aroclors 2E-07 NA 1E-06 2E-06 Dermal, Immune System, and Ocular 2E-02 NA 2E-01 2E-01Total PCBs 6E-09 NA 5E-08 6E-08 Dermal, Immune System, and Ocular 9E-04 NA 8E-03 9E-03

3E-07 NA 2E-06 2E-06 6E-02 NA 2E-01 3E-012E-07 NA 6E-07 7E-07 3E-02 NA 1E-02 5E-023E-07 NA 2E-06 2E-06 6E-02 NA 2E-01 3E-012E-07 NA 6E-07 7E-07 3E-02 NA 1E-02 5E-02

Medium Total (Total Aroclors)1 3E-07 NA 2E-06 2E-06 6E-02 NA 2E-01 3E-01Medium Total (Total PCBs)2 2E-07 NA 6E-07 7E-07 3E-02 NA 1E-02 5E-02Receptor Total (Total Aroclors)1 3E-07 NA 2E-06 2E-06 6E-02 NA 2E-01 3E-01Receptor Total (Total PCBs)2 2E-07 NA 6E-07 7E-07 3E-02 NA 1E-02 5E-02

NA = Not applicable or not availableNOE = No Observed Effects Total Hematologic HI Across Media = 0.000071The total includes estimated risks/HIs for Total Aroclors in sediment but not for PCB TEQ and Total PCBs in sediment. Total Reproductive HI Across Media = 0.0022The total includes estimated risks/HIs for PCB TEQ and Total PCBs in sediment but not for Total Aroclors in sediment. Total Gastrointestinal HI Across Media = 0.0013The total includes estimated HIs for Total Aroclors in sediment but not for Total PCBs in sediment. Total Immune System HI Across Media 3 = 0.24The total includes estimated HIs for Total PCBs in sediment but not for Total Aroclors in sediment. Total Immune System HI Across Media 4 = 0.009

Total Urinary System HI Across Media = 0.0009Total Nervous System HI Across Media = 0.03

Total Body Weight HI Across Media = 0.00006Total Dermal HI Across Media3 = 0.2Total Dermal HI Across Media4 = 0.01



Total Ocular HI Across Media3 = 0.2Total Ocular HI Across Media4 = 0.009






Page 1 of 1

TABLE 10.1.RMERISK SUMMARY


Scenario Timeframe: Current/Future Receptor Population: Fish ConsumerReceptor Age: Adult



Concern Ingestion Inhalation Dermal Exposure Primary Ingestion Inhalation Dermal Exposure Routes Total Target Organ(s) Routes Total

Sediment/Surface Water Fish Fish 2,3,7,8-TCDD TEQ Developmental, Endocrine System, Reproductive 3E+00 NA NA 3E+00(white perch) Total PCBs Dermal, Immune System, and Ocular 9E+00 NA NA 9E+00

1E+01 NA NA 1E+011E+01 NA NA 1E+01

Medium Total 1E+01 NA NA 1E+01Receptor Total 1E+01 NA NA 1E+01










Scenario Timeframe: Current/Future Receptor Population: Fish ConsumerReceptor Age: Older Child





1E+01 NA NA 1E+011E+01 NA NA 1E+01











Scenario Timeframe: Current/Future Receptor Population: Fish ConsumerReceptor Age: Younger Child





2E+01 NA NA 2E+012E+01 NA NA 2E+01









Attachment B Sample Groups

Table B‐1. Data Groupings for Revised HHRA


Data Grouping Data Description Sample Counts

SW Surface water samples collected onsite at high and low tide 32

SD_Grab Sediment samples collected on‐site (0 to 6 inches) 42

Fish_WP White perch tissue samples collected on‐site 10

SD_South Sediment samples collected at Ackermans South (0 to 6 inches) 9

Table B‐2. Samples Used in Revised HHRA

OU2, Universal Oil Products (UOP), East Rutherford, New JerseyData

Grouping1 Matrix Station ID Sample ID

Collection

Date Upper Depth Lower Depth Depth Units

SW SW MNR‐1 042612‐SW‐WW‐MNR1‐ebb 4/26/12 NA NA NA

SW SW MNR‐1 042712‐SW‐WW‐MNR1‐FLOOD 4/27/12 NA NA NA


SW SW MNR‐1 070112‐SW‐WW‐MNR1‐flood 7/1/12 NA NA NA









SW SW MNR‐5 040214‐SW‐WW‐MNR5‐HIGH 4/2/14 NA NA NA








SW SW MSW‐24 MQW‐24F‐09166 6/15/09 NA NA NA




SW SW MSW‐24 MQW‐24U‐09166 6/15/09 NA NA NA




SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/10 NA NA NA



SW SW SW06 100410‐SW‐SL06‐EBB 10/4/10 NA NA NA

Fish_WP Tissue WP02 092315‐FT‐WP02 9/23/15 NA NA NA



Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/13 NA NA NA







SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/09 0 10 cm



SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/12 0 10 cm

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/11 0 10 cm

SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/11 10 30 cm

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/13 0 0.5 ft












Page 1 of 2

Table B‐2. Samples Used in Revised HHRA

OU2, Universal Oil Products (UOP), East Rutherford, New JerseyData

Grouping1 Matrix Station ID Sample ID

Collection

Date Upper Depth Lower Depth Depth Units

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/10 0 5 cm






SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/06 0 0.5 ft

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/10 0 0.5 ft





SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/10 0 0.5 ft

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/10 0 0.8 ft

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/10 0 0.5 ft

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/10 0 0.5 ft

SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/06 0 0.5 ft

SD_Grab SD WC‐B.2 071906‐WC‐MAR‐0B2‐0001 7/19/06 0 0.5 ft

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/10 0 0.5 ft




SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/10 0 0.5 ft

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/10 0 0.5 ft

SD_South SD BAZ‐3038 BAZ‐3038‐13239 8/27/13 0 10 cm

SD_South SD MMDB‐314 MMDB‐314‐0‐5‐12250 9/6/12 0 5 cm

SD_South SD MRH‐321 MRH‐321‐0‐5‐12250 9/6/12 0 5 cm






SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/06 0 0.5 ft

Notes:1 Data groupings are defined on Table 1 of Attachment B.

cm = centimeter

ft = feet

SD = Sediment

SW = Surface Water

Page 2 of 2

Attachment C Analytical Dataset

(on CD)

Attachment C

Analytical Data Used in Revised HHRA


AOC_ID1Matrix StationID SampleID

Collection

Date

Sample

Type

Chemical

Group Analyte Result

Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

Fish_WP Tissue WP02 092315‐FT‐WP02 9/23/2015 N PCB Congener 2,3,7,8‐TCDD TEQ 4.8E‐05 = mg/kg Y

Fish_WP Tissue WP02 092315‐FT‐WP02 9/23/2015 N PCB Congener PCB‐105 0.0646 J mg/kg Y 1.63E‐07 9.98E‐06

Fish_WP Tissue WP02 092315‐FT‐WP02 9/23/2015 N PCB Congener PCB‐106/118 0.179 J mg/kg Y 4.09E‐07 0.00002

Fish_WP Tissue WP02 092315‐FT‐WP02 9/23/2015 N PCB Congener PCB‐114 0.0051 = mg/kg Y 2.42E‐07 9.98E‐06






Fish_WP Tissue WP02 092315‐FT‐WP02 9/23/2015 N PCB Congener PCB‐169 5.98E‐06 = mg/kg Y 2.19E‐07 4.99E‐07






























Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener 2,3,7,8‐TCDD TEQ 9.9E‐05 = mg/kg Y

Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐1 0.000341 = mg/kg Y 1.18E‐07





Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐106/118 0.236 = mg/kg Y 1.21E‐07



Page 1 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit









Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐121 5.23E‐06 U mg/kg N 1.19E‐07 5.23E-06Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐122 0.00383 = mg/kg Y 6.53E‐08




Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐127 5.22E‐05 U mg/kg N 9.25E‐08 0.0000522Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐128/162 0.0162 = mg/kg Y 2.02E‐07



Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐131 6.46E‐05 = mg/kg Y 8.96E‐08







Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐138/163/164 0.0932 = mg/kg Y 2.42E‐07


Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐14 6.01E‐05 U mg/kg N 9.45E‐08 0.0000601Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐140 0.000751 = mg/kg Y 1.19E‐07




















Page 2 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit





































Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐204 1.25E‐05 J mg/kg Y 1.07E‐07









Page 3 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit










Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐36 0.000114 U mg/kg N 2.46E‐07 0.000114Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐37 0.00968 = mg/kg Y 1.57E‐07





Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐41/64/71/72 0.377 = mg/kg Y 5.55E‐07









Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐50 0.00226 = mg/kg Y 0.0000001





















Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐80 0.000202 U mg/kg N 8.34E‐08 0.000202

Page 4 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit















Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB Congener PCB‐99 0.18 = mg/kg Y 1.41E-07Fish_WP Tissue WP02 082213‐FT‐WP02‐01 8/22/2013 N PCB_TOT Total PCBs 7.305415 = mg/kg Y

Fish_WP Tissue WP02 082213‐FT‐WP02‐02 8/22/2013 N PCB Congener 2,3,7,8‐TCDD TEQ 0.00011 = mg/kg Y





















Fish_WP Tissue WP02 082213‐FT‐WP02‐02 8/22/2013 N PCB Congener PCB‐127 5.89E‐05 U mg/kg N 9.25E‐08 0.0000589









Page 5 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit






















Fish_WP Tissue WP02 082213‐FT‐WP02‐02 8/22/2013 N PCB Congener PCB‐159 0.00007 U mg/kg N 8.49E‐08 0.00007Fish_WP Tissue WP02 082213‐FT‐WP02‐02 8/22/2013 N PCB Congener PCB‐16/32 0.12 = mg/kg Y 1.53E‐07






















Fish_WP Tissue WP02 082213‐FT‐WP02‐02 8/22/2013 N PCB Congener PCB‐186 7.69E‐06 U mg/kg N 7.92E‐08 7.69E-06Fish_WP Tissue WP02 082213‐FT‐WP02‐02 8/22/2013 N PCB Congener PCB‐188 9.89E‐05 = mg/kg Y 6.73E‐08

Page 6 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit















































Page 7 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




























Fish_WP Tissue WP02 082213‐FT‐WP02‐02 8/22/2013 N PCB Congener PCB‐84/92 0.135 = mg/kg Y 1.66E-07Fish_WP Tissue WP02 082213‐FT‐WP02‐02 8/22/2013 N PCB Congener PCB‐85/116 0.0685 = mg/kg Y 2.15E-07Fish_WP Tissue WP02 082213‐FT‐WP02‐02 8/22/2013 N PCB Congener PCB‐86 0.00314 = mg/kg Y 1.06E‐07










Fish_WP Tissue WP02 082213‐FT‐WP02‐02 8/22/2013 N PCB_TOT Total PCBs 7.490679 = mg/kg Y






Page 8 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit














































Page 9 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit














































Page 10 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit






























Fish_WP Tissue WP02 082213‐FT‐WP02‐03 8/22/2013 N PCB Congener PCB‐52/69 0.437 J mg/kg Y 1.97E‐07












Fish_WP Tissue WP02 082213‐FT‐WP02‐03 8/22/2013 N PCB Congener PCB‐67 0.009 = mg/kg Y 1.1E-07Fish_WP Tissue WP02 082213‐FT‐WP02‐03 8/22/2013 N PCB Congener PCB‐68 0.003 = mg/kg Y 1.34E-07Fish_WP Tissue WP02 082213‐FT‐WP02‐03 8/22/2013 N PCB Congener PCB‐7/9 0.00155 = mg/kg Y 1.68E‐07



Page 11 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit












































Page 12 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit














































Page 13 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit















































Page 14 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit










Fish_WP Tissue WP03 082213‐FT‐WP03‐01 8/22/2013 N PCB Congener PCB‐53 0.095 = mg/kg Y 1.53E-07Fish_WP Tissue WP03 082213‐FT‐WP03‐01 8/22/2013 N PCB Congener PCB‐54 0.00154 = mg/kg Y 8.52E-08Fish_WP Tissue WP03 082213‐FT‐WP03‐01 8/22/2013 N PCB Congener PCB‐55 0.00717 = mg/kg Y 1.15E‐07


































Page 15 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit














































Page 16 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit












































Fish_WP Tissue WP04 082113‐FT‐WP04‐01 8/21/2013 N PCB Congener PCB‐204 0.000012 J mg/kg Y 1.07E‐07

Page 17 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit






















Fish_WP Tissue WP04 082113‐FT‐WP04‐01 8/21/2013 N PCB Congener PCB‐40 0.0561 = mg/kg Y 1.19E-07Fish_WP Tissue WP04 082113‐FT‐WP04‐01 8/21/2013 N PCB Congener PCB‐41/64/71/72 0.482 J mg/kg Y 5.55E-07Fish_WP Tissue WP04 082113‐FT‐WP04‐01 8/21/2013 N PCB Congener PCB‐42/59 0.165 = mg/kg Y 2.35E‐07


Fish_WP Tissue WP04 082113‐FT‐WP04‐01 8/21/2013 N PCB Congener PCB‐44 0.492 J mg/kg Y 1.42E‐07


















Fish_WP Tissue WP04 082113‐FT‐WP04‐01 8/21/2013 N PCB Congener PCB‐66/76 0.508 J mg/kg Y 2.05E‐07



Page 18 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit













































Page 19 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit















































Page 20 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit






Fish_WP Tissue WP04 082113‐FT‐WP04‐02 8/21/2013 N PCB Congener PCB‐186 0.000012 U mg/kg N 7.92E‐08 0.000012Fish_WP Tissue WP04 082113‐FT‐WP04‐02 8/21/2013 N PCB Congener PCB‐188 8.61E‐05 = mg/kg Y 6.73E‐08





























Fish_WP Tissue WP04 082113‐FT‐WP04‐02 8/21/2013 N PCB Congener PCB‐29 0.000256 = mg/kg Y 1.82E-07Fish_WP Tissue WP04 082113‐FT‐WP04‐02 8/21/2013 N PCB Congener PCB‐3 0.000201 = mg/kg Y 1.38E-07Fish_WP Tissue WP04 082113‐FT‐WP04‐02 8/21/2013 N PCB Congener PCB‐30 0.00007 = mg/kg Y 1.23E‐07









Page 21 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit













































Page 22 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit














































Page 23 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit






























Fish_WP Tissue WP04 082113‐FT‐WP04‐03 8/21/2013 N PCB Congener PCB‐186 9.53E‐06 U mg/kg N 7.92E‐08 9.53E‐06
















Page 24 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



Fish_WP Tissue WP04 082113‐FT‐WP04‐03 8/21/2013 N PCB Congener PCB‐204 1.09E‐05 J mg/kg Y 1.07E-07Fish_WP Tissue WP04 082113‐FT‐WP04‐03 8/21/2013 N PCB Congener PCB‐205 0.000166 = mg/kg Y 6.99E‐08

































Fish_WP Tissue WP04 082113‐FT‐WP04‐03 8/21/2013 N PCB Congener PCB‐51 0.0308 = mg/kg Y 8.21E-08Fish_WP Tissue WP04 082113‐FT‐WP04‐03 8/21/2013 N PCB Congener PCB‐52/69 0.536 J mg/kg Y 1.97E‐07










Page 25 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

Fish_WP Tissue WP04 082113‐FT‐WP04‐03 8/21/2013 N PCB Congener PCB‐65 2.89E‐05 U mg/kg N 1.54E‐07


























SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N GenChem Cyanide 0.37 J mg/kg Y 0.18 1.1SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Aluminum 7740 J mg/kg Y 20.2 42.1SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Antimony 12.6 UJ mg/kg N 0.82 12.6SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Arsenic 10.2 J mg/kg Y 0.63 2.1SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Barium 99.6 J mg/kg Y 0.15 42.1SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Beryllium 1.1 UJ mg/kg N 0.09 1.1SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Cadmium 3.4 J mg/kg Y 0.076 1.1SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Calcium 5290 J mg/kg Y 33.6 1050SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Chromium 818 J mg/kg Y 0.42 2.1SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Cobalt 11.8 J mg/kg Y 0.34 10.5SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Copper 143 J mg/kg Y 1.6 5.3SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Iron 15300 J mg/kg Y 10.3 21

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Lead 83.4 J mg/kg Y 0.4 0.63SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Magnesium 2690 J mg/kg Y 10.7 1050

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Manganese 1080 J mg/kg Y 0.16 3.2

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Mercury 3.4 J mg/kg Y 0.032 0.21SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Methyl Mercury 0.002 J mg/kg Y 0.000078 0.00021SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Nickel 40.4 J mg/kg Y 0.57 8.4SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Potassium 956 B J mg/kg Y 13 1050SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Selenium 1.1 UJ mg/kg N 0.95 1.1

Page 26 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Silver 0.33 J mg/kg Y 0.21 2.1SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Sodium 1440 = mg/kg Y 139 1050SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Thallium 1.5 J mg/kg Y 1.2 2.1SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Vanadium 23.2 J mg/kg Y 0.25 10.5SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N Metal Zinc 639 J mg/kg Y 2.1 4.2

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PCB Aroclor‐1016 0.44 UJ mg/kg N 0.065 0.44SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PCB Aroclor‐1221 0.44 UJ mg/kg N 0.084 0.44SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PCB Aroclor‐1232 0.44 UJ mg/kg N 0.075 0.44SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PCB Aroclor‐1242 0.44 UJ mg/kg N 0.071 0.44SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PCB Aroclor‐1248 28 J mg/kg Y 0.041 0.44SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PCB Aroclor‐1254 8.3 J mg/kg Y 0.062 0.44SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PCB Aroclor‐1260 0.95 J mg/kg Y 0.062 0.44SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PCB Aroclor‐1262 0.44 UJ mg/kg N 0.096 0.44

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PCB Aroclor‐1268 0.44 UJ mg/kg N 0.056 0.44SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PCB_TOT Total Aroclors 37.25 = mg/kg Y 0.065 0.44SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST 4,4'‐DDD 0.018 UJ mg/kg N 0.0023 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST 4‐4’‐DDE 0.018 UJ mg/kg N 0.0026 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST 4‐4’‐DDT 0.018 UJ mg/kg N 0.0026 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Alpha Chlordane 0.018 UJ mg/kg N 0.0035 0.018

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST BHC (alpha) 0.018 UJ mg/kg N 0.0029 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST BHC (beta) 0.018 UJ mg/kg N 0.0045 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST BHC (gamma) 0.018 UJ mg/kg N 0.0031 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Chlordane (beta) 0.018 UJ mg/kg N 0.0034 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Endosulfan I 0.075 J mg/kg Y 0.0033 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Endosulfan II 0.018 UJ mg/kg N 0.0031 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Endosulfan sulfate 0.018 UJ mg/kg N 0.0018 0.018

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Endrin 0.18 NJ mg/kg Y 0.0034 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Endrin aldehyde 0.018 UJ mg/kg N 0.0034 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Endrin ketone 0.018 UJ mg/kg N 0.0027 0.018SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Heptachlor epoxide 0.39 NJ mg/kg Y 0.0034 0.018

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Methoxychlor 0.035 UJ mg/kg N 0.0037 0.035SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N PEST Toxaphene 0.7 UJ mg/kg N 0.12 0.7SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 1,1'‐Biphenyl 0.031 J mg/kg Y 0.016 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2,4,5‐Trichlorophenol 0.35 UJ mg/kg N 0.0087 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2,4,6‐Trichlorophenol 0.35 UJ mg/kg N 0.017 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2,4‐Dichlorophenol 0.07 UJ mg/kg N 0.014 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2,4‐Dimethylphenol 0.35 UJ mg/kg N 0.015 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2,4‐Dinitrophenol 1.8 UJ mg/kg N 0.11 1.8SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2,4‐Dinitrotoluene 0.35 UJ mg/kg N 0.016 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2,6‐Dinitrotoluene 0.35 UJ mg/kg N 0.018 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2‐3‐4‐6‐Tetrachlorophenol 0.35 UJ mg/kg N 0.01 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2‐Chloronaphthalene 0.07 UJ mg/kg N 0.0095 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2‐Chlorophenol 0.35 UJ mg/kg N 0.011 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2‐Methylnaphthalene 0.035 J mg/kg Y 0.014 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2‐Methylphenol 0.35 UJ mg/kg N 0.013 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2‐Nitroaniline 1.8 UJ mg/kg N 0.021 1.8SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 2‐Nitrophenol 0.35 UJ mg/kg N 0.013 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 3,3‐Dichlorobenzidine 0.35 UJ mg/kg N 0.066 0.35

Page 27 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 3‐Nitroaniline 1.8 UJ mg/kg N 0.011 1.8SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 4,6‐Dinitro‐2‐methylphenol 1.8 UJ mg/kg N 0.34 1.8SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 4‐Bromophenyl phenyl ether 0.35 UJ mg/kg N 0.015 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 4‐Chloro‐3‐methylphenol 0.35 UJ mg/kg N 0.01 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 4‐Chloroaniline 0.35 UJ mg/kg N 0.011 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 4‐Chlorophenyl phenyl ether 0.35 UJ mg/kg N 0.016 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 4‐Methylphenol 0.071 J mg/kg Y 0.015 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 4‐Nitroaniline 1.8 UJ mg/kg N 0.017 1.8

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC 4‐Nitrophenol 1.8 UJ mg/kg N 0.21 1.8SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Acenaphthene 0.099 J mg/kg Y 0.011 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Acenaphthylene 0.15 J mg/kg Y 0.014 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Acetophenone 0.35 UJ mg/kg N 0.016 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Anthracene 0.38 J mg/kg Y 0.012 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Atrazine 0.35 UJ mg/kg N 0.017 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Benzaldehyde 0.39 J mg/kg Y 0.0092 0.35

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Benzo(a)anthracene 1.5 J mg/kg Y 0.011 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Benzo(a)pyrene 1.3 J mg/kg Y 0.02 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Benzo(b)fluoranthene 2.1 J mg/kg Y 0.014 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Benzo(g,h,i)perylene 0.87 J mg/kg Y 0.0052 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Benzo(k)fluoranthene 0.07 UJ mg/kg N 0.015 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Bis(2‐chloroethoxy)methane 0.35 UJ mg/kg N 0.014 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Bis(2‐chloroethyl)ether 0.07 UJ mg/kg N 0.0062 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC bis(2‐Chloroisopropyl)ether 0.07 UJ mg/kg N 0.015 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Bis(2‐ethylhexyl)phthalate 8.6 J mg/kg Y 0.03 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Butyl benzyl phthalate 0.35 UJ mg/kg N 0.025 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Caprolactam 1.8 UJ mg/kg N 0.046 1.8SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Carbazole 0.13 J mg/kg Y 0.0092 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Chrysene 1.4 J mg/kg Y 0.012 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Dibenz(a,h)anthracene 0.2 J mg/kg Y 0.015 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Dibenzofuran 0.35 UJ mg/kg N 0.012 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Diethyl phthalate 0.35 UJ mg/kg N 0.02 0.35

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Dimethyl phthalate 0.35 UJ mg/kg N 0.012 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Di‐n‐butyl phthalate 0.35 UJ mg/kg N 0.02 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Di‐n‐octyl phthalate 0.25 J mg/kg Y 0.009 0.35SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Fluoranthene 3.3 J mg/kg Y 0.0059 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Fluorene 0.037 J mg/kg Y 0.011 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Hexachlorobenzene 0.07 UJ mg/kg N 0.013 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Hexachlorobutadiene 0.07 UJ mg/kg N 0.015 0.07SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Hexachlorocyclopentadiene 0.35 UJ mg/kg N 0.013 0.35

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Hexachloroethane 0.35 UJ mg/kg N 0.012 0.35

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Indeno(1,2,3‐cd)pyrene 0.89 J mg/kg Y 0.0039 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Isophorone 0.35 UJ mg/kg N 0.014 0.35

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Naphthalene 0.07 UJ mg/kg N 0.01 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Nitrobenzene 0.07 UJ mg/kg N 0.018 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC N‐Nitroso‐di‐n‐propylamine 0.07 UJ mg/kg N 0.019 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC N‐Nitrosodiphenylamine 0.1 J mg/kg Y 0.014 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Pentachlorophenol 0.35 UJ mg/kg N 0.061 0.35

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Phenanthrene 0.94 J mg/kg Y 0.0084 0.07

Page 28 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Phenol 0.032 J mg/kg Y 0.014 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N SVOC Pyrene 2 J mg/kg Y 0.019 0.07

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1,1,1‐Trichloroethane 0.013 UJ mg/kg N 0.0012 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1,1,2,2‐Tetrachloroethane 0.013 UJ mg/kg N 0.0018 0.013


SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1,1,2‐Trichlorotrifluoroethane 0.013 UJ mg/kg N 0.0027 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1,1‐Dichloroethane 0.013 UJ mg/kg N 0.0015 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1,1‐Dichloroethene 0.013 UJ mg/kg N 0.0022 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1,2,4‐Trichlorobenzene 0.013 UJ mg/kg N 0.0023 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1,2‐Dibromo‐3‐chloropropane 0.013 UJ mg/kg N 0.0019 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1,2‐Dibromoethane 0.013 UJ mg/kg N 0.0022 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1,2‐Dichlorobenzene 0.013 UJ mg/kg N 0.002 0.013


SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1,2‐Dichloropropane 0.013 UJ mg/kg N 0.0014 0.013



SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1‐2‐3‐Trichlorobenzene 0.013 UJ mg/kg N 0.0022 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 1‐2‐4‐5‐Tetrachlorobenzene 0.35 UJ mg/kg N 0.026 0.35

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC 2‐Hexanone 0.013 UJ mg/kg N 0.0018 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Acetone 0.059 J mg/kg Y 0.013 0.051

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Benzene 0.013 UJ mg/kg N 0.0017 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Bromochloromethane 0.013 UJ mg/kg N 0.0018 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Bromodichloromethane 0.013 UJ mg/kg N 0.0014 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Bromoform 0.013 UJ mg/kg N 0.0011 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Bromomethane 0.013 UJ mg/kg N 0.0019 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Carbon Disulfide 0.013 UJ mg/kg N 0.0013 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Carbon Tetrachloride 0.013 UJ mg/kg N 0.0011 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Chlorobenzene 0.013 UJ mg/kg N 0.0019 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Chloroethane 0.013 UJ mg/kg N 0.004 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Chloroform 0.013 UJ mg/kg N 0.0015 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Chloromethane 0.013 UJ mg/kg N 0.0022 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC cis‐1,2‐Dichloroethene 0.013 UJ mg/kg N 0.0018 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC cis‐1,3‐Dichloropropene 0.013 UJ mg/kg N 0.0017 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Cyclohexane 0.013 UJ mg/kg N 0.00095 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Dibromochloromethane 0.013 UJ mg/kg N 0.0018 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Dichlorodifluoromethane 0.013 UJ mg/kg N 0.0017 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Ethylbenzene 0.013 UJ mg/kg N 0.0016 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Isopropylbenzene 0.013 UJ mg/kg N 0.0017 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC m,p‐Xylenes 0.026 UJ mg/kg N 0.0038 0.026

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Methyl Acetate 0.013 UJ mg/kg N 0.0023 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Methyl ethyl ketone 0.013 UJ mg/kg N 0.0023 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Methyl isobutyl ketone 0.013 UJ mg/kg N 0.0017 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Methyl tert‐butyl ether 0.013 UJ mg/kg N 0.0019 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Methylcyclohexane 0.013 UJ mg/kg N 0.0019 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Methylene Chloride 0.013 UJ mg/kg N 0.0017 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC o‐Xylene 0.013 UJ mg/kg N 0.002 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Styrene 0.013 UJ mg/kg N 0.0018 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Tetrachloroethene 0.013 UJ mg/kg N 0.0017 0.013

Page 29 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Toluene 0.013 UJ mg/kg N 0.0019 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC trans‐1,2‐Dichloroethene 0.013 UJ mg/kg N 0.0015 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC trans‐1,3‐Dichloropropene 0.013 UJ mg/kg N 0.0015 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Trichloroethene 0.013 UJ mg/kg N 0.0017 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Trichlorofluoromethane 0.013 UJ mg/kg N 0.0024 0.013

SD_Grab SD BAZ‐1077 BAZ‐1077‐09162 6/11/2009 N VOC Vinyl Chloride 0.013 UJ mg/kg N 0.0012 0.013

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Aluminum 14000 J mg/kg Y 23.1 48.1

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Antimony 14.4 UJ mg/kg N 0.94 14.4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Arsenic 46.3 J mg/kg Y 0.72 2.4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Barium 534 J mg/kg Y 0.17 48.1

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Beryllium 1.2 UJ mg/kg N 0.1 1.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Cadmium 2.7 J mg/kg Y 0.087 1.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Calcium 3490 J mg/kg Y 38.5 1200

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Chromium 6390 J mg/kg Y 0.48 2.4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Cobalt 11.6 J mg/kg Y 0.38 12

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Copper 220 J mg/kg Y 1.8 6

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Iron 37400 J mg/kg Y 11.8 24.1

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Lead 297 J mg/kg Y 0.46 0.72

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Magnesium 5760 J mg/kg Y 12.3 1200

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Manganese 575 J mg/kg Y 0.18 3.6

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Mercury 129 J mg/kg Y 1.8 12

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Methyl Mercury 0.16 J mg/kg Y 0.0018 0.0048

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Nickel 32.8 J mg/kg Y 0.65 9.6

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Potassium 2220 J mg/kg Y 14.9 1200SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Selenium 1.4 J mg/kg Y 1.1 1.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Silver 3.3 J mg/kg Y 0.24 2.4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Sodium 5200 J mg/kg Y 159 1200

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Thallium 1.5 J mg/kg Y 1.3 2.4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Vanadium 58.5 J mg/kg Y 0.29 12

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N Metal Zinc 371 J mg/kg Y 2.4 4.8

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PCB Aroclor‐1016 1 UJ mg/kg N 0.15 1




SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PCB Aroclor‐1248 90 J mg/kg Y 0.094 1

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PCB Aroclor‐1254 32 J mg/kg Y 0.14 1




SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PCB_TOT Total Aroclors 122 = mg/kg Y 0.15 1

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST 4,4'‐DDD 0.2 UJ mg/kg N 0.026 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST 4‐4’‐DDE 1.1 J mg/kg Y 0.03 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST 4‐4’‐DDT 0.2 UJ mg/kg N 0.03 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Aldrin 3 J mg/kg Y 0.035 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Alpha Chlordane 0.2 U mg/kg N 0.039 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST BHC (alpha) 0.2 UJ mg/kg N 0.032 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST BHC (beta) 6.7 J mg/kg Y 0.051 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST BHC (delta) 0.2 UJ mg/kg N 0.03 0.2

Page 30 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST BHC (gamma) 0.2 UJ mg/kg N 0.035 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Chlordane (beta) 0.2 UJ mg/kg N 0.039 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Endosulfan I 0.39 J mg/kg Y 0.037 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Endosulfan II 0.2 UJ mg/kg N 0.035 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Endosulfan sulfate 0.086 J mg/kg Y 0.021 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Endrin 0.2 UJ mg/kg N 0.038 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Endrin aldehyde 0.2 UJ mg/kg N 0.038 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Endrin ketone 0.2 UJ mg/kg N 0.031 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Heptachlor epoxide 1.6 NJ mg/kg Y 0.038 0.2

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Methoxychlor 0.4 UJ mg/kg N 0.041 0.4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N PEST Toxaphene 7.9 UJ mg/kg N 0.014 7.9

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 1,1'‐Biphenyl 0.78 UJ mg/kg N 0.073 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2,4,5‐Trichlorophenol 0.78 UJ mg/kg N 0.084 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2,4,6‐Trichlorophenol 0.78 UJ mg/kg N 0.12 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2,4‐Dichlorophenol 0.16 UJ mg/kg N 0.016 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2,4‐Dimethylphenol 0.78 UJ mg/kg N 0.12 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2,4‐Dinitrophenol 4 UJ mg/kg N 0.94 4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2,4‐Dinitrotoluene 0.78 UJ mg/kg N 0.064 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2,6‐Dinitrotoluene 0.78 UJ mg/kg N 0.081 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2‐3‐4‐6‐Tetrachlorophenol 0.78 UJ mg/kg N 0.051 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2‐Chloronaphthalene 0.16 UJ mg/kg N 0.016 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2‐Chlorophenol 0.78 UJ mg/kg N 0.064 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2‐Methylnaphthalene 0.071 J mg/kg Y 0.014 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2‐Methylphenol 0.78 UJ mg/kg N 0.055 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2‐Nitroaniline 4 UJ mg/kg N 0.35 4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 2‐Nitrophenol 0.78 UJ mg/kg N 0.087 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 3,3‐Dichlorobenzidine 0.78 UJ mg/kg N 0.083 0.78


SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 4 UJ mg/kg N 0.32 4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 4‐Bromophenyl phenyl ether 0.78 UJ mg/kg N 0.069 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 4‐Chloro‐3‐methylphenol 0.78 UJ mg/kg N 0.073 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 4‐Chloroaniline 0.78 UJ mg/kg N 0.063 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 4‐Chlorophenyl phenyl ether 0.78 UJ mg/kg N 0.088 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 4‐Methylphenol 0.086 J mg/kg Y 0.077 0.78


SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC 4‐Nitrophenol 4 UJ mg/kg N 0.27 4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Acenaphthene 0.16 UJ mg/kg N 0.015 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Acenaphthylene 0.43 J mg/kg Y 0.018 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Acetophenone 0.78 U mg/kg N 0.065 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Anthracene 0.38 J mg/kg Y 0.015 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Atrazine 0.78 UJ mg/kg N 0.077 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Benzaldehyde 1.4 J mg/kg Y 0.12 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Benzo(a)anthracene 0.75 J mg/kg Y 0.02 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Benzo(a)pyrene 0.84 J mg/kg Y 0.016 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Benzo(b)fluoranthene 1.5 J mg/kg Y 0.025 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Benzo(g,h,i)perylene 0.84 J mg/kg Y 0.016 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Benzo(k)fluoranthene 0.16 UJ mg/kg N 0.032 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Bis(2‐chloroethoxy)methane 0.78 UJ mg/kg N 0.052 0.78

Page 31 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Bis(2‐chloroethyl)ether 0.16 UJ mg/kg N 0.021 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC bis(2‐Chloroisopropyl)ether 0.16 UJ mg/kg N 0.017 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Bis(2‐ethylhexyl)phthalate 15 J mg/kg Y 0.13 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Butyl benzyl phthalate 0.78 UJ mg/kg N 0.11 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Caprolactam 4 UJ mg/kg N 0.6 4

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Carbazole 0.16 UJ mg/kg N 0.015 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Chrysene 1.2 J mg/kg Y 0.019 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Dibenz(a,h)anthracene 0.19 J mg/kg Y 0.018 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Dibenzofuran 0.78 UJ mg/kg N 0.078 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Diethyl phthalate 0.78 UJ mg/kg N 0.086 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Dimethyl phthalate 0.78 UJ mg/kg N 0.086 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Di‐n‐butyl phthalate 0.78 UJ mg/kg N 0.099 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Di‐n‐octyl phthalate 0.19 J mg/kg Y 0.083 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Fluoranthene 1.2 J mg/kg Y 0.017 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Fluorene 0.16 UJ mg/kg N 0.021 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Hexachlorobenzene 0.16 UJ mg/kg N 0.017 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Hexachlorobutadiene 0.16 UJ mg/kg N 0.018 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Hexachlorocyclopentadiene 0.78 UJ mg/kg N 0.085 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Hexachloroethane 0.78 UJ mg/kg N 0.057 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.62 J mg/kg Y 0.016 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Isophorone 0.78 UJ mg/kg N 0.059 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Naphthalene 0.12 J mg/kg Y 0.014 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Nitrobenzene 0.16 UJ mg/kg N 0.066 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 0.16 UJ mg/kg N 0.018 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC N‐Nitrosodiphenylamine 0.16 UJ mg/kg N 0.073 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Pentachlorophenol 0.78 UJ mg/kg N 0.071 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Phenanthrene 0.44 J mg/kg Y 0.025 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Phenol 0.16 UJ mg/kg N 0.019 0.16

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N SVOC Pyrene 1.4 J mg/kg Y 0.016 0.16


SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC 1,1,2,2‐Tetrachloroethane 0.012 UJ mg/kg N 0.0017 0.012


SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 0.012 UJ mg/kg N 0.0026 0.012


SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC 1,1‐Dichloroethene 0.012 UJ mg/kg N 0.0021 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC 1,2,4‐Trichlorobenzene 0.012 UJ mg/kg N 0.0021 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 0.012 UJ mg/kg N 0.0018 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC 1,2‐Dibromoethane 0.012 UJ mg/kg N 0.0021 0.012



SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC 1,2‐Dichloropropane 0.012 UJ mg/kg N 0.0013 0.012



SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC 1‐2‐3‐Trichlorobenzene 0.012 UJ mg/kg N 0.0021 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC 1‐2‐4‐5‐Tetrachlorobenzene 0.78 UJ mg/kg N 0.06 0.78

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC 2‐Hexanone 0.012 UJ mg/kg N 0.0017 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Acetone 0.013 J mg/kg Y 0.012 0.049

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Benzene 0.012 UJ mg/kg N 0.0016 0.012

Page 32 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Bromochloromethane 0.012 UJ mg/kg N 0.0017 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Bromodichloromethane 0.012 UJ mg/kg N 0.0014 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Bromoform 0.012 UJ mg/kg N 0.0011 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Bromomethane 0.012 UJ mg/kg N 0.0018 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Carbon Disulfide 0.012 UJ mg/kg N 0.0012 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Carbon Tetrachloride 0.012 UJ mg/kg N 0.0011 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Chlorobenzene 0.012 UJ mg/kg N 0.0018 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Chloroethane 0.012 UJ mg/kg N 0.0038 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Chloroform 0.012 UJ mg/kg N 0.0014 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Chloromethane 0.012 UJ mg/kg N 0.0021 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC cis‐1,2‐Dichloroethene 0.012 UJ mg/kg N 0.0017 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC cis‐1,3‐Dichloropropene 0.012 UJ mg/kg N 0.0016 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Cyclohexane 0.012 UJ mg/kg N 0.0009 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Dibromochloromethane 0.012 UJ mg/kg N 0.0017 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Dichlorodifluoromethane 0.012 UJ mg/kg N 0.0016 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Ethylbenzene 0.012 UJ mg/kg N 0.0016 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Isopropylbenzene 0.012 UJ mg/kg N 0.0016 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC m,p‐Xylenes 0.024 UJ mg/kg N 0.0036 0.024

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Methyl Acetate 0.012 UJ mg/kg N 0.0022 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Methyl ethyl ketone 0.012 UJ mg/kg N 0.0021 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Methyl isobutyl ketone 0.012 UJ mg/kg N 0.0016 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Methyl tert‐butyl ether 0.012 UJ mg/kg N 0.0018 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Methylcyclohexane 0.012 UJ mg/kg N 0.0018 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Methylene Chloride 0.012 UJ mg/kg N 0.0016 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC o‐Xylene 0.012 UJ mg/kg N 0.0019 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Styrene 0.012 UJ mg/kg N 0.0017 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Tetrachloroethene 0.012 UJ mg/kg N 0.0017 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Toluene 0.012 UJ mg/kg N 0.0018 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC trans‐1,2‐Dichloroethene 0.012 UJ mg/kg N 0.0014 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC trans‐1,3‐Dichloropropene 0.012 UJ mg/kg N 0.0015 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Trichloroethene 0.012 UJ mg/kg N 0.0016 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Trichlorofluoromethane 0.012 UJ mg/kg N 0.0022 0.012

SD_Grab SD BAZ‐2028 BAZ‐2028‐10225 8/13/2010 N VOC Vinyl Chloride 0.012 UJ mg/kg N 0.0011 0.012

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Aluminum 4900 = mg/kg Y 12 25

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Antimony 1.3 U mg/kg N 0.49 1.3

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Arsenic 6.4 = mg/kg Y 0.38 1.3

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Barium 78 B mg/kg Y 0.09 25

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Beryllium 0.28 J mg/kg Y 0.054 0.63SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Cadmium 0.8 = mg/kg Y 0.045 0.25

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Calcium 13000 B mg/kg Y 20 630

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Chromium 270 = mg/kg Y 0.25 0.63

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Cobalt 5.8 J mg/kg Y 0.2 6.3

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Copper 40 = mg/kg Y 0.93 3.2

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Iron 14000 = mg/kg Y 6.2 13

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Lead 79 = mg/kg Y 0.24 0.38

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Magnesium 2100 = mg/kg Y 6.4 630

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Manganese 1100 B mg/kg Y 0.093 1.9

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Mercury 3.9 = mg/kg Y 0.19 1.3

Page 33 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Methyl Mercury 0.0013 J mg/kg Y 0.00046 0.0012

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Nickel 14 = mg/kg Y 0.34 5.1

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Potassium 720 B mg/kg Y 7.8 630

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Selenium 0.63 U mg/kg N 0.57 0.63

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Silver 0.63 U mg/kg N 0.13 0.63

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Sodium 360 J mg/kg Y 83 630

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Thallium 1.3 U mg/kg N 0.69 1.3

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Vanadium 15 = mg/kg Y 0.15 6.3

SD_Grab SD BAZ‐2049 BAZ‐2049‐11294 10/21/2011 N Metal Zinc 160 = mg/kg Y 1.3 2.5

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Aluminum 9500 J mg/kg Y 33 70

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Antimony 3.5 UJ mg/kg N 1.4 3.5

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Arsenic 12 J mg/kg Y 1 3.5

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Barium 140 J mg/kg Y 0.25 70

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Beryllium 1.7 U mg/kg N 0.15 1.7

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Cadmium 1 J mg/kg Y 0.13 0.7

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Calcium 5000 J mg/kg Y 56 1700

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Chromium 240 J mg/kg Y 0.7 1.7

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Cobalt 10 J mg/kg Y 0.56 17

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Copper 61 J mg/kg Y 2.6 8.7

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Iron 26000 J mg/kg Y 17 35

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Lead 50 J mg/kg Y 0.66 1

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Magnesium 4300 J mg/kg Y 18 1700

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Manganese 810 J mg/kg Y 0.26 5.2

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Mercury 6 J mg/kg Y 0.063 0.42

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Nickel 28 J mg/kg Y 0.94 14

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Potassium 1700 U mg/kg N 22 1700

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Selenium 1.7 UJ mg/kg N 1.6 1.7

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Silver 0.44 J mg/kg Y 0.35 1.7

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Sodium 4300 J mg/kg Y 230 1700

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Thallium 3.5 UJ mg/kg N 1.9 3.5

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Vanadium 29 J mg/kg Y 0.42 17

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N Metal Zinc 210 J mg/kg Y 3.5 7

SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N PCB Aroclor‐1016 0.0083 UJ mg/kg N 0.0012 0.0083




SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N PCB Aroclor‐1248 0.95 J mg/kg Y 0.00079 0.0083


SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N PCB Aroclor‐1260 0.081 J mg/kg Y 0.0012 0.0083



SD_Grab SD BAZ‐3027 TOX‐319‐12268 9/24/2012 N PCB_TOT Total Aroclors 1.031 = mg/kg Y 0.0012 0.0083

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Aluminum 6300 J mg/kg Y 20 43

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Antimony 2.2 J mg/kg Y 0.83 2.1

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Arsenic 14 J mg/kg Y 0.64 2.1

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Barium 140 J mg/kg Y 0.15 43

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Beryllium 1.1 UJ mg/kg N 0.092 1.1

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Cadmium 2.1 J mg/kg Y 0.077 0.43

Page 34 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Calcium 51000 J mg/kg Y 34 1100

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Chromium 710 J mg/kg Y 0.43 1.1

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Cobalt 12 J mg/kg Y 0.34 11

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Copper 70 J mg/kg Y 1.6 5.3

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Iron 27000 J mg/kg Y 10 21

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Lead 75 J mg/kg Y 0.41 0.64

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Magnesium 3500 J mg/kg Y 11 1100

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Manganese 1700 J mg/kg Y 0.16 3.2

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Mercury 9.9 J mg/kg Y 0.56 3.7

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Methyl Mercury 0.017 J mg/kg Y 0.00039 0.0011

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Nickel 37 J mg/kg Y 0.58 8.5

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Potassium 1100 UJ mg/kg N 13 1100

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Selenium 1.1 UJ mg/kg N 0.96 1.1

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Silver 0.93 J mg/kg Y 0.21 1.1

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Sodium 1700 J mg/kg Y 140 1100

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Thallium 2.1 UJ mg/kg N 1.2 2.1

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Vanadium 29 J mg/kg Y 0.26 11

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N Metal Zinc 320 J mg/kg Y 2.1 4.3

SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N PCB Aroclor‐1016 9.2 UJ mg/kg N 1.4 9.2




SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N PCB Aroclor‐1248 550 J mg/kg Y 0.87 9.2



SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N PCB Aroclor‐1262 9.2 UJ mg/kg N 2 9.2


SD_Grab SD DWC‐214 DWC‐214‐0‐10‐11179 6/28/2011 N PCB_TOT Total Aroclors 550 = mg/kg Y 1.4 9.2

SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Aluminum 15000 J mg/kg Y 24 49SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Antimony 2.5 UJ mg/kg N 0.96 2.5SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Arsenic 13 J mg/kg Y 0.74 2.5SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Barium 72 J mg/kg Y 0.17 49SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Beryllium 1.2 J mg/kg Y 0.11 1.2SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Cadmium 0.86 J mg/kg Y 0.089 0.49SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Calcium 2800 J mg/kg Y 39 1200SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Chromium 35 J mg/kg Y 0.49 1.2SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Cobalt 16 J mg/kg Y 0.39 12SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Copper 18 J mg/kg Y 1.8 6.2SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Iron 40000 J mg/kg Y 12 25SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Lead 12 J mg/kg Y 0.47 0.74SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Magnesium 6700 J mg/kg Y 13 1200

SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Manganese 320 J mg/kg Y 0.18 3.7SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Mercury 0.38 J mg/kg Y 0.037 0.25SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Methyl Mercury 0.00065 J mg/kg Y 0.00009 0.00024SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Nickel 25 J mg/kg Y 0.66 9.8SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Potassium 2200 J mg/kg Y 15 1200

SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Selenium 1.2 UJ mg/kg N 1.1 1.2SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Silver 1.2 UJ mg/kg N 0.25 1.2

Page 35 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Sodium 2700 J mg/kg Y 160 1200SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Thallium 2.5 UJ mg/kg N 1.4 2.5SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Vanadium 48 J mg/kg Y 0.3 12

SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N Metal Zinc 85 J mg/kg Y 2.5 4.9SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N PCB Aroclor‐1016 0.0051 UJ mg/kg N 0.00076 0.0051SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N PCB Aroclor‐1221 0.0051 UJ mg/kg N 0.00097 0.0051SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N PCB Aroclor‐1232 0.0051 UJ mg/kg N 0.00087 0.0051

SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N PCB Aroclor‐1242 0.0051 UJ mg/kg N 0.00083 0.0051SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N PCB Aroclor‐1248 0.14 NJ mg/kg Y 0.00048 0.0051SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N PCB Aroclor‐1254 0.0051 UJ mg/kg N 0.00072 0.0051SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N PCB Aroclor‐1260 0.0051 UJ mg/kg N 0.00072 0.0051SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N PCB Aroclor‐1262 0.0051 UJ mg/kg N 0.0011 0.0051SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N PCB Aroclor‐1268 0.0051 UJ mg/kg N 0.00065 0.0051SD_Grab SD DWC‐214 DWC‐214‐10‐30‐11179 6/28/2011 N PCB_TOT Total Aroclors 0.14 = mg/kg Y 0.00076 0.0051SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Aluminum 1590 = mg/kg Y 52 52SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Antimony 2.1 U mg/kg N 2.1 2.1SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Arsenic 2.1 U mg/kg N 2.1 2.1SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Barium 21 U mg/kg N 21 21

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Beryllium 0.21 U mg/kg N 0.21 0.21SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Cadmium 0.52 U mg/kg N 0.52 0.52SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Calcium 520 U mg/kg N 520 520SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Chromium 8.2 = mg/kg Y 1 1

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Cobalt 5.2 U mg/kg N 5.2 5.2SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Copper 3 = mg/kg Y 2.6 2.6SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Iron 3680 = mg/kg Y 52 52SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Lead 4 = mg/kg Y 2.1 2.1

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Magnesium 520 U mg/kg N 520 520

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Manganese 15.6 = mg/kg Y 1.6 1.6SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Mercury 0.23 = mg/kg Y 0.042 0.042SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Methyl Mercury 0.000882 = mg/kg Y 0.000013 0.000031SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Nickel 4.2 U mg/kg N 4.2 4.2SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Potassium 1000 U mg/kg N 1000 1000SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Selenium 2.1 U mg/kg N 2.1 2.1SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Silver 0.52 U mg/kg N 0.52 0.52SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Sodium 1000 U mg/kg N 1000 1000SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Thallium 1 U mg/kg N 1 1SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Vanadium 5.2 U mg/kg N 5.2 5.2SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N Metal Zinc 13.1 = mg/kg Y 2.1 2.1SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Aroclor‐1016 0.042 U mg/kg N 0.011 0.042SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Aroclor‐1221 0.042 U mg/kg N 0.025 0.042SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Aroclor‐1232 0.042 U mg/kg N 0.021 0.042

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Aroclor‐1242 0.042 U mg/kg N 0.013 0.042SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Aroclor‐1248 0.042 U mg/kg N 0.013 0.042SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Aroclor‐1254 0.042 U mg/kg N 0.02 0.042

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Aroclor‐1260 0.042 U mg/kg N 0.014 0.042SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Aroclor‐1262 0.042 U mg/kg N 0.013 0.042

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Aroclor‐1268 0.042 U mg/kg N 0.012 0.042

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener 2,3,7,8‐TCDD TEQ 2.56E‐06 = mg/kg Y

Page 36 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐1 3.78E‐05 = mg/kg Y 8.3E‐07



SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐104 4.93E‐06 J mg/kg Y 4.69E‐07

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐105 0.00186 = mg/kg Y 3.74E‐07

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐106/118 0.00403 = mg/kg Y 7.91E‐07










SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐120 1.02E‐05 U mg/kg N 1.09E‐06 0.0000102SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐121 9.89E‐06 U mg/kg N 8.36E‐07 9.89E‐06




SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐126 0.000023 J mg/kg Y 7.57E‐07

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐127 1.12E‐05 U mg/kg N 4.89E‐07 0.0000112SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐128/162 0.000292 = mg/kg Y 1.28E‐06


SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐130 0.000114 = mg/kg Y 0.000001

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐131 9.29E‐06 U mg/kg N 5.08E‐07 9.29E-06SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐132/161 0.000548 = mg/kg Y 1.18E‐06

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐133/142 6.96E‐05 = mg/kg Y 0.0000012





SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐138/163/164 0.00142 = mg/kg Y 1.63E‐06


SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐14 6.49E‐05 U mg/kg N 1.87E‐06 0.0000649






SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐148 1.14E‐05 U mg/kg N 8.31E‐07 0.0000114SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐15 0.00101 = mg/kg Y 1.34E‐06

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐150 8.74E‐06 U mg/kg N 1.04E‐06 8.74E-06SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐151 0.000253 = mg/kg Y 5.04E‐07



Page 37 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐158/160 6.03E‐06 U mg/kg N 1.45E‐06 6.03E-06SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐159 7.41E‐06 U mg/kg N 4.8E‐07 7.41E-06SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐16/32 0.00295 = mg/kg Y 5.93E‐07

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐166 7.4E‐06 U mg/kg N 9.75E‐07 0.0000074SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐167 7.72E‐05 = mg/kg Y 3.92E‐07

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐168 6.11E‐06 U mg/kg N 8.88E‐07 6.11E-06SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐169 5.94E‐06 U mg/kg N 7.62E‐07 5.94E-06SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐17 0.00216 = mg/kg Y 6.29E‐07




SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐173 6.83E‐06 U mg/kg N 8.36E‐07 6.83E‐06













SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐186 3.46E‐06 U mg/kg N 1.12E‐06 3.46E-06SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐188 3.66E‐06 U mg/kg N 7.7E‐07 3.66E-06SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐189 1.48E‐05 J mg/kg Y 5.99E‐07




SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐192 4.67E‐06 U mg/kg N 7.32E‐07 4.67E-06SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐193 2.58E‐05 = mg/kg Y 8.79E‐07




SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐197 6.79E‐06 U mg/kg N 6.29E‐07 6.79E-06SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐198 7.61E‐06 J mg/kg Y 9.55E‐07


SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐2 1.91E‐05 J mg/kg Y 7.74E-07SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐20/21/33 0.002 = mg/kg Y 2.61E‐06

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐200 1.63E‐05 J mg/kg Y 0.0000009




Page 38 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit
























SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐41/64/71/72 0.00847 = mg/kg Y 1.54E‐06

























Page 39 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐7/9 0.000059 J mg/kg Y 3.16E‐06














SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB Congener PCB‐88/91 0.0015 = mg/kg Y 0.0000013









SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB_TOT Total Aroclors 0 U mg/kg N 0.011 0.042

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N PCB_TOT Total PCBs 0.160504 = mg/kg Y

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 1,1'‐Biphenyl 0.076 U mg/kg N 0.0044 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2,4,5‐Trichlorophenol 0.19 U mg/kg N 0.044 0.19


SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2,4‐Dichlorophenol 0.19 U mg/kg N 0.061 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2,4‐Dimethylphenol 0.19 U mg/kg N 0.064 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2,4‐Dinitrophenol 0.76 UJ mg/kg N 0.046 0.76

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2,4‐Dinitrotoluene 0.076 U mg/kg N 0.017 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2,6‐Dinitrotoluene 0.076 U mg/kg N 0.014 0.076SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2‐Chloronaphthalene 0.076 U mg/kg N 0.012 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2‐Chlorophenol 0.19 U mg/kg N 0.038 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2‐Methylnaphthalene 0.076 U mg/kg N 0.021 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2‐Methylphenol 0.076 U mg/kg N 0.043 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2‐Nitroaniline 0.19 U mg/kg N 0.017 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 2‐Nitrophenol 0.19 U mg/kg N 0.04 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 3&4‐Methylphenol 0.076 U mg/kg N 0.048 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 3,3‐Dichlorobenzidine 0.19 U mg/kg N 0.0096 0.19


SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 4,6‐Dinitro‐2‐methylphenol 0.76 U mg/kg N 0.046 0.76

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 4‐Bromophenyl phenyl ether 0.076 U mg/kg N 0.014 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 4‐Chloro‐3‐methylphenol 0.19 U mg/kg N 0.038 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 4‐Chloroaniline 0.19 U mg/kg N 0.012 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC 4‐Chlorophenyl phenyl ether 0.076 U mg/kg N 0.011 0.076

Page 40 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Acenaphthene 0.038 U mg/kg N 0.011 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Acenaphthylene 0.038 U mg/kg N 0.012 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Anthracene 0.038 U mg/kg N 0.013 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Atrazine 0.19 U mg/kg N 0.0075 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Benzaldehyde 0.19 U mg/kg N 0.0087 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Benzo(a)anthracene 0.0543 = mg/kg Y 0.012 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Benzo(a)pyrene 0.0601 = mg/kg Y 0.012 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Benzo(b)fluoranthene 0.1 = mg/kg Y 0.013 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Benzo(g,h,i)perylene 0.0668 = mg/kg Y 0.014 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Benzo(k)fluoranthene 0.0391 = mg/kg Y 0.014 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Bis(2‐chloroethoxy)methane 0.076 U mg/kg N 0.015 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Bis(2‐chloroethyl)ether 0.076 U mg/kg N 0.011 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC bis(2‐Chloroisopropyl)ether 0.076 U mg/kg N 0.011 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Bis(2‐ethylhexyl)phthalate 0.184 = mg/kg Y 0.033 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Butyl benzyl phthalate 0.076 U mg/kg N 0.022 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Caprolactam 0.076 U mg/kg N 0.012 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Carbazole 0.076 U mg/kg N 0.018 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Chrysene 0.0833 = mg/kg Y 0.013 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Dibenz(a,h)anthracene 0.038 U mg/kg N 0.013 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Dibenzofuran 0.076 U mg/kg N 0.011 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Diethyl phthalate 0.076 U mg/kg N 0.013 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Dimethyl phthalate 0.076 U mg/kg N 0.013 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Di‐n‐butyl phthalate 0.076 U mg/kg N 0.0084 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Di‐n‐octyl phthalate 0.076 U mg/kg N 0.018 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Fluoranthene 0.114 = mg/kg Y 0.017 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Fluorene 0.038 U mg/kg N 0.012 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Hexachlorobenzene 0.076 U mg/kg N 0.012 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Hexachlorobutadiene 0.038 U mg/kg N 0.011 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Hexachlorocyclopentadiene 0.38 U mg/kg N 0.039 0.38

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Hexachloroethane 0.19 U mg/kg N 0.011 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Indeno(1,2,3‐cd)pyrene 0.0483 = mg/kg Y 0.013 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Isophorone 0.076 U mg/kg N 0.01 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Naphthalene 0.038 U mg/kg N 0.01 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Nitrobenzene 0.076 U mg/kg N 0.011 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC N‐Nitroso‐di‐n‐propylamine 0.076 U mg/kg N 0.0092 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC N‐Nitrosodiphenylamine 0.19 U mg/kg N 0.023 0.19

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Pentachlorophenol 0.38 U mg/kg N 0.065 0.38

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Phenanthrene 0.0383 = mg/kg Y 0.017 0.038

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Phenol 0.076 U mg/kg N 0.04 0.076

SD_Grab SD LTM01 081313‐SD‐LTM01‐01 8/13/2013 N SVOC Pyrene 0.117 = mg/kg Y 0.015 0.038

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Aluminum 14100 J mg/kg Y 75 75

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Antimony 3 UJ mg/kg N 3 3

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Arsenic 9.5 = mg/kg Y 3 3

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Barium 120 = mg/kg Y 30 30

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Beryllium 0.69 = mg/kg Y 0.3 0.3

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Cadmium 2.6 = mg/kg Y 0.75 0.75

Page 41 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Calcium 4110 = mg/kg Y 750 750

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Chromium 223 = mg/kg Y 1.5 1.5

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Cobalt 9.6 = mg/kg Y 7.5 7.5

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Copper 110 = mg/kg Y 3.7 3.7

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Iron 25100 = mg/kg Y 75 75

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Lead 108 = mg/kg Y 3 3

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Magnesium 6220 = mg/kg Y 750 750

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Manganese 369 = mg/kg Y 2.2 2.2

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Mercury 7.6 = mg/kg Y 0.67 0.67

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Methyl Mercury 0.00157 = mg/kg Y 0.000021 0.000066

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Nickel 29 = mg/kg Y 6 6

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Potassium 2820 J mg/kg Y 1500 1500

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Selenium 3 U mg/kg N 3 3

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Silver 1.5 = mg/kg Y 0.75 0.75

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Sodium 6860 = mg/kg Y 1500 1500

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Thallium 1.5 U mg/kg N 1.5 1.5

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Vanadium 38.1 = mg/kg Y 7.5 7.5

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N Metal Zinc 385 = mg/kg Y 7.5 7.5





SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Aroclor‐1248 0.621 J mg/kg Y 0.031 0.1






SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐1 0.000867 = mg/kg Y 5.64E‐07 0.000166



SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐104 0.000166 U mg/kg N 8.38E‐07 0.000166


SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐106/118 0.102 = mg/kg Y 1.45E‐06 0.000331















Page 42 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit













SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐138/163/164 0.0444 = mg/kg Y 1.32E‐06 0.000497




























SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐171 0.00187 = mg/kg Y 0.0000012 0.000166








Page 43 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐179 0.00336 = mg/kg Y 4.3E-07 0.000166SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐18 0.136 = mg/kg Y 1.38E‐06 0.000166

















SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐196/203 0.00534 = mg/kg Y 0.0000025 0.000331






























Page 44 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐41/64/71/72 0.235 = mg/kg Y 3.07E‐06 0.000662













































Page 45 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐97 0.05 = mg/kg Y 1.06E-06 0.000166SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB Congener PCB‐99 0.0747 = mg/kg Y 1.34E‐06 0.000166SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB_TOT Total Aroclors 0.821 = mg/kg Y 0.032 0.1SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N PCB_TOT Total PCBs 4.174566 = mg/kg Y

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 1,1'‐Biphenyl 0.2 U mg/kg N 0.018 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2,4,5‐Trichlorophenol 0.49 U mg/kg N 0.088 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2,4,6‐Trichlorophenol 0.49 U mg/kg N 0.079 0.49

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2,4‐Dichlorophenol 0.49 U mg/kg N 0.078 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2,4‐Dimethylphenol 0.49 U mg/kg N 0.18 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2,4‐Dinitrophenol 0.49 U mg/kg N 0.43 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2,4‐Dinitrotoluene 0.098 U mg/kg N 0.018 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2,6‐Dinitrotoluene 0.098 U mg/kg N 0.025 0.098

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2‐Chloronaphthalene 0.2 U mg/kg N 0.014 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2‐Chlorophenol 0.2 U mg/kg N 0.072 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2‐Methylnaphthalene 0.2 U mg/kg N 0.018 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2‐Methylphenol 0.2 U mg/kg N 0.14 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2‐Nitroaniline 0.49 U mg/kg N 0.022 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 2‐Nitrophenol 0.49 U mg/kg N 0.09 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 3&4‐Methylphenol 0.2 U mg/kg N 0.093 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 3,3‐Dichlorobenzidine 0.2 U mg/kg N 0.064 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 3‐Nitroaniline 0.49 U mg/kg N 0.028 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 4,6‐Dinitro‐2‐methylphenol 0.49 U mg/kg N 0.19 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 4‐Bromophenyl phenyl ether 0.2 U mg/kg N 0.022 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 4‐Chloro‐3‐methylphenol 0.49 U mg/kg N 0.088 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 4‐Chloroaniline 0.49 U mg/kg N 0.026 0.49

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 4‐Chlorophenyl phenyl ether 0.2 U mg/kg N 0.018 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 4‐Nitroaniline 0.49 U mg/kg N 0.033 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC 4‐Nitrophenol 0.98 U mg/kg N 0.17 0.98SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Acenaphthene 0.098 U mg/kg N 0.092 0.098

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Acenaphthylene 0.066 J mg/kg Y 0.01 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Anthracene 0.122 = mg/kg Y 0.0084 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Atrazine 0.2 U mg/kg N 0.04 0.2

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Benzaldehyde 0.49 U mg/kg N 0.024 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Benzo(a)anthracene 0.612 = mg/kg Y 0.019 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Benzo(a)pyrene 0.821 = mg/kg Y 0.021 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Benzo(b)fluoranthene 1.21 = mg/kg Y 0.02 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Benzo(g,h,i)perylene 0.717 = mg/kg Y 0.029 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Benzo(k)fluoranthene 0.413 = mg/kg Y 0.022 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Bis(2‐chloroethoxy)methane 0.2 U mg/kg N 0.022 0.2

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Bis(2‐chloroethyl)ether 0.2 U mg/kg N 0.041 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC bis(2‐Chloroisopropyl)ether 0.2 U mg/kg N 0.022 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Bis(2‐ethylhexyl)phthalate 5.9 J mg/kg Y 0.034 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Butyl benzyl phthalate 0.2 U mg/kg N 0.053 0.2

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Caprolactam 0.2 U mg/kg N 0.063 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Carbazole 0.0835 J mg/kg Y 0.011 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Chrysene 0.987 = mg/kg Y 0.016 0.098

Page 46 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Dibenz(a,h)anthracene 0.153 = mg/kg Y 0.035 0.098


SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Diethyl phthalate 0.2 U mg/kg N 0.012 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Dimethyl phthalate 0.2 U mg/kg N 0.014 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Di‐n‐butyl phthalate 0.2 U mg/kg N 0.012 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Di‐n‐octyl phthalate 0.2 U mg/kg N 0.013 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Fluoranthene 1.56 = mg/kg Y 0.012 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Fluorene 0.0509 J mg/kg Y 0.012 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Hexachlorobenzene 0.2 U mg/kg N 0.019 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Hexachlorobutadiene 0.098 U mg/kg N 0.026 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Hexachlorocyclopentadiene 0.98 U mg/kg N 0.16 0.98SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Hexachloroethane 0.49 U mg/kg N 0.032 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Indeno(1,2,3‐cd)pyrene 0.657 = mg/kg Y 0.051 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Isophorone 0.2 U mg/kg N 0.018 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Naphthalene 0.098 U mg/kg N 0.016 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Nitrobenzene 0.2 U mg/kg N 0.031 0.2

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC N‐Nitroso‐di‐n‐propylamine 0.2 U mg/kg N 0.029 0.2SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC N‐Nitrosodiphenylamine 0.49 U mg/kg N 0.051 0.49SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Pentachlorophenol 0.49 U mg/kg N 0.24 0.49

SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Phenanthrene 0.423 = mg/kg Y 0.011 0.098SD_Grab SD LTM01 091715‐SD‐LTM01‐01 9/17/2015 N SVOC Phenol 0.2 U mg/kg N 0.073 0.2


SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Aluminum 1020 = mg/kg Y 48 48SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Antimony 1.9 U mg/kg N 1.9 1.9SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Arsenic 1.9 U mg/kg N 1.9 1.9SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Barium 19 U mg/kg N 19 19SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Beryllium 0.19 U mg/kg N 0.19 0.19SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Cadmium 0.48 U mg/kg N 0.48 0.48SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Calcium 491 = mg/kg Y 480 480

SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Chromium 11 = mg/kg Y 0.96 0.96SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Cobalt 4.8 U mg/kg N 4.8 4.8SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Copper 7.6 = mg/kg Y 2.4 2.4SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Iron 3060 = mg/kg Y 48 48SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Lead 9.7 = mg/kg Y 1.9 1.9SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Magnesium 480 U mg/kg N 480 480SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Manganese 36.7 = mg/kg Y 1.4 1.4SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Mercury 0.16 = mg/kg Y 0.04 0.04SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Methyl Mercury 0.000932 J mg/kg Y 0.000012 0.000029SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Nickel 3.8 U mg/kg N 3.8 3.8SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Potassium 960 U mg/kg N 960 960SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Selenium 1.9 U mg/kg N 1.9 1.9SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Silver 0.48 U mg/kg N 0.48 0.48SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Sodium 960 U mg/kg N 960 960

SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Thallium 0.96 U mg/kg N 0.96 0.96SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Vanadium 4.8 U mg/kg N 4.8 4.8SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N Metal Zinc 26.2 = mg/kg Y 1.9 1.9SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Aroclor‐1016 0.042 U mg/kg N 0.011 0.042


Page 47 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Aroclor‐1232 0.042 U mg/kg N 0.021 0.042SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Aroclor‐1242 0.042 U mg/kg N 0.013 0.042SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Aroclor‐1248 0.042 U mg/kg N 0.013 0.042SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Aroclor‐1254 0.042 U mg/kg N 0.02 0.042SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Aroclor‐1260 0.042 U mg/kg N 0.014 0.042SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Aroclor‐1262 0.042 U mg/kg N 0.013 0.042SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Aroclor‐1268 0.042 U mg/kg N 0.012 0.042SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Congener 2,3,7,8‐TCDD TEQ 2.19E‐06 = mg/kg Y

























SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Congener PCB‐133/142 6.47E‐05 = mg/kg Y 0.0000012







SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Congener PCB‐14 5.05E‐05 U mg/kg N 1.87E‐06 0.0000505SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Congener PCB‐140 1.04E‐05 J mg/kg Y 4.64E‐07




Page 48 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit





SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Congener PCB‐153 0.00108 = mg/kg Y 7.7E-07SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Congener PCB‐154 1.93E‐05 J mg/kg Y 4.65E‐07









































Page 49 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit





SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Congener PCB‐200 4.55E‐06 U mg/kg N 0.0000009 4.55E‐06












































Page 50 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit









SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Congener PCB‐68 9.24E‐05 = mg/kg Y 1.08E-06SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB Congener PCB‐7/9 0.000147 = mg/kg Y 3.16E‐06























SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N PCB_TOT Total Aroclors 0 U mg/kg N 0.011 0.042










SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N SVOC 2‐Chloronaphthalene 0.08 U mg/kg N 0.012 0.08






Page 51 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit













SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N SVOC Anthracene 0.0241 J mg/kg Y 0.014 0.04
















SD_Grab SD LTM02 081313‐SD‐LTM02‐01 8/13/2013 N SVOC Dibenz(a,h)anthracene 0.0251 J mg/kg Y 0.014 0.04




















Page 52 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Aluminum 4200 = mg/kg Y 35 35

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Antimony 1.4 U mg/kg N 1.4 1.4

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Arsenic 2.1 = mg/kg Y 1.4 1.4

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Barium 29.2 = mg/kg Y 14 14


SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Cadmium 0.35 U mg/kg N 0.35 0.35


SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Chromium 49.2 = mg/kg Y 0.7 0.7

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Cobalt 3.5 U mg/kg N 3.5 3.5

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Copper 9.2 = mg/kg Y 1.7 1.7


SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Lead 9.9 = mg/kg Y 1.4 1.4


SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Manganese 131 = mg/kg Y 1 1



SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Nickel 5.3 = mg/kg Y 2.8 2.8

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Potassium 700 U mg/kg N 700 700

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Selenium 1.4 U mg/kg N 1.4 1.4

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Silver 0.35 U mg/kg N 0.35 0.35




SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N Metal Zinc 31.8 = mg/kg Y 3.5 3.5





SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Aroclor‐1248 1.32 = mg/kg Y 0.014 0.046


















Page 53 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐120 9.55E‐05 = mg/kg Y 9.32E‐07 0.0000812









SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐130 0.00154 = mg/kg Y 9.41E-07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐131 8.12E‐05 U mg/kg N 1.26E‐06 0.0000812



































Page 54 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



















SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐189 7.72E‐05 J mg/kg Y 7.04E‐07 0.0000812






























Page 55 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit















SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐44 0.169 = mg/kg Y 1.18E-06 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐45 0.024 = mg/kg Y 6.03E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐46 0.0119 = mg/kg Y 5.44E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐47 0.0408 = mg/kg Y 0.0000015 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐48/75 0.0315 = mg/kg Y 7.12E‐07 0.000162SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐5/8 0.014 = mg/kg Y 1.08E‐06 0.000162SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐50 0.000585 = mg/kg Y 7.69E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐51 0.00823 = mg/kg Y 8.04E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐52/69 0.153 = mg/kg Y 1.46E‐06 0.000162SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐53 0.0265 = mg/kg Y 1.08E‐06 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐54 0.000469 = mg/kg Y 6.39E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐55 0.00145 = mg/kg Y 5.16E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐56/60 0.0817 = mg/kg Y 1.18E‐06 0.000162SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐57 0.000621 = mg/kg Y 8.59E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐58 0.000421 = mg/kg Y 8.3E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐6 0.00769 = mg/kg Y 1.24E‐06 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐61/70 0.153 = mg/kg Y 1.49E‐06 0.000162SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐62 8.12E‐05 U mg/kg N 1.23E‐06 0.0000812

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐63 0.00566 = mg/kg Y 5.32E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐65 8.12E‐05 U mg/kg N 9.82E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐66/76 0.121 = mg/kg Y 5.66E‐07 0.000162SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐67 0.00325 = mg/kg Y 1.13E‐06 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐68 0.000744 = mg/kg Y 7.73E‐07 0.0000812

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐7/9 0.0012 = mg/kg Y 7.5E‐07 0.000162SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐73 0.000195 = mg/kg Y 5.81E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐74 0.064 = mg/kg Y 9.03E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐77 0.00828 = mg/kg Y 7.99E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐78 8.12E‐05 U mg/kg N 6.28E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐79 0.00109 = mg/kg Y 1.16E‐06 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐80 8.12E‐05 U mg/kg N 1.07E‐06 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐81 0.000427 = mg/kg Y 6.59E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐82 0.0157 = mg/kg Y 1.24E‐06 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐83 8.12E‐05 U mg/kg N 4.5E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐84/92 0.0393 = mg/kg Y 8.76E‐07 0.000162

Page 56 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐85/116 0.0174 = mg/kg Y 1.99E‐06 0.000162SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐86 0.000963 = mg/kg Y 1.27E‐06 0.0000812

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐87/117/125 0.0256 = mg/kg Y 1.47E‐06 0.000244SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐88/91 0.0181 = mg/kg Y 2.27E‐06 0.000162SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐89 0.00338 = mg/kg Y 7.86E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐90/101 0.0627 = mg/kg Y 4.49E‐07 0.000162SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐93 8.12E‐05 U mg/kg N 1.35E‐06 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐94 0.00106 = mg/kg Y 8.44E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐95/98/102 0.0586 = mg/kg Y 2.28E‐06 0.000244SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐96 0.00176 = mg/kg Y 7.96E‐07 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐97 0.0276 = mg/kg Y 1.06E‐06 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB Congener PCB‐99 0.037 = mg/kg Y 1.34E‐06 0.0000812SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB_TOT Total Aroclors 1.54 = mg/kg Y 0.015 0.046SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N PCB_TOT Total PCBs 2.236273 = mg/kg Y

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 1,1'‐Biphenyl 0.086 U mg/kg N 0.008 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2,4,5‐Trichlorophenol 0.22 U mg/kg N 0.039 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2,4,6‐Trichlorophenol 0.22 U mg/kg N 0.035 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2,4‐Dichlorophenol 0.22 U mg/kg N 0.035 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2,4‐Dimethylphenol 0.22 U mg/kg N 0.079 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2,4‐Dinitrophenol 0.22 U mg/kg N 0.19 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2,4‐Dinitrotoluene 0.043 U mg/kg N 0.0081 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2,6‐Dinitrotoluene 0.043 U mg/kg N 0.011 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2‐Chloronaphthalene 0.086 U mg/kg N 0.0062 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2‐Chlorophenol 0.086 U mg/kg N 0.032 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2‐Methylnaphthalene 0.086 U mg/kg N 0.0081 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2‐Methylphenol 0.086 U mg/kg N 0.063 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2‐Nitroaniline 0.22 U mg/kg N 0.0098 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 2‐Nitrophenol 0.22 U mg/kg N 0.04 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 3&4‐Methylphenol 0.086 U mg/kg N 0.041 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 3,3‐Dichlorobenzidine 0.086 U mg/kg N 0.028 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 3‐Nitroaniline 0.22 U mg/kg N 0.012 0.22

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 4,6‐Dinitro‐2‐methylphenol 0.22 U mg/kg N 0.082 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 4‐Bromophenyl phenyl ether 0.086 U mg/kg N 0.0098 0.086


SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 4‐Chloroaniline 0.22 U mg/kg N 0.011 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 4‐Chlorophenyl phenyl ether 0.086 U mg/kg N 0.0081 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 4‐Nitroaniline 0.22 U mg/kg N 0.014 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC 4‐Nitrophenol 0.43 U mg/kg N 0.073 0.43SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Acenaphthene 0.043 U mg/kg N 0.041 0.043

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Acenaphthylene 0.043 U mg/kg N 0.0045 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Anthracene 0.043 U mg/kg N 0.0037 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Atrazine 0.086 U mg/kg N 0.018 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Benzaldehyde 0.22 U mg/kg N 0.011 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Benzo(a)anthracene 0.0535 = mg/kg Y 0.0083 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Benzo(a)pyrene 0.0691 = mg/kg Y 0.0092 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Benzo(b)fluoranthene 0.0966 = mg/kg Y 0.0089 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Benzo(g,h,i)perylene 0.0618 = mg/kg Y 0.013 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Benzo(k)fluoranthene 0.0357 J mg/kg Y 0.0096 0.043

Page 57 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Bis(2‐chloroethoxy)methane 0.086 U mg/kg N 0.0098 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Bis(2‐chloroethyl)ether 0.086 U mg/kg N 0.018 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC bis(2‐Chloroisopropyl)ether 0.086 U mg/kg N 0.0099 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Bis(2‐ethylhexyl)phthalate 0.176 = mg/kg Y 0.015 0.086

SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Butyl benzyl phthalate 0.086 U mg/kg N 0.023 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Caprolactam 0.086 U mg/kg N 0.028 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Carbazole 0.086 U mg/kg N 0.0048 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Chrysene 0.0889 = mg/kg Y 0.007 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Dibenz(a,h)anthracene 0.043 U mg/kg N 0.015 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Dibenzofuran 0.086 U mg/kg N 0.006 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Diethyl phthalate 0.086 U mg/kg N 0.0055 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Dimethyl phthalate 0.086 U mg/kg N 0.0062 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Di‐n‐butyl phthalate 0.086 U mg/kg N 0.0051 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Di‐n‐octyl phthalate 0.086 U mg/kg N 0.0058 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Fluoranthene 0.14 = mg/kg Y 0.0053 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Fluorene 0.043 U mg/kg N 0.0051 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Hexachlorobenzene 0.086 U mg/kg N 0.0085 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Hexachlorobutadiene 0.043 U mg/kg N 0.011 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Hexachlorocyclopentadiene 0.43 U mg/kg N 0.069 0.43SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Hexachloroethane 0.22 U mg/kg N 0.014 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Indeno(1,2,3‐cd)pyrene 0.0584 = mg/kg Y 0.022 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Isophorone 0.086 U mg/kg N 0.0081 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Naphthalene 0.043 U mg/kg N 0.0069 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Nitrobenzene 0.086 U mg/kg N 0.014 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC N‐Nitroso‐di‐n‐propylamine 0.086 U mg/kg N 0.013 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC N‐Nitrosodiphenylamine 0.22 U mg/kg N 0.023 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Pentachlorophenol 0.22 U mg/kg N 0.11 0.22SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Phenanthrene 0.0491 = mg/kg Y 0.0048 0.043SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Phenol 0.086 U mg/kg N 0.032 0.086SD_Grab SD LTM02 091615‐SD‐LTM02‐01 9/16/2015 N SVOC Pyrene 0.145 = mg/kg Y 0.0054 0.043SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Aluminum 4340 = mg/kg Y 68 68SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Antimony 2.7 U mg/kg N 2.7 2.7SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Arsenic 2.7 U mg/kg N 2.7 2.7SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Barium 27 U mg/kg N 27 27SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Beryllium 0.27 U mg/kg N 0.27 0.27SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Cadmium 0.68 U mg/kg N 0.68 0.68SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Calcium 991 = mg/kg Y 680 680

SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Chromium 74.9 = mg/kg Y 1.4 1.4SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Cobalt 6.8 U mg/kg N 6.8 6.8

SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Copper 16.2 = mg/kg Y 3.4 3.4SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Iron 9070 = mg/kg Y 68 68SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Lead 17.6 = mg/kg Y 2.7 2.7SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Magnesium 1260 = mg/kg Y 680 680SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Manganese 90.9 = mg/kg Y 2 2

SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Mercury 0.96 = mg/kg Y 0.042 0.042SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Methyl Mercury 0.00113 = mg/kg Y 0.000013 0.000033SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Nickel 6.4 = mg/kg Y 5.4 5.4


Page 58 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Silver 0.68 U mg/kg N 0.68 0.68SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Sodium 1400 U mg/kg N 1400 1400SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Thallium 1.4 U mg/kg N 1.4 1.4SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Vanadium 12 = mg/kg Y 6.8 6.8SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N Metal Zinc 67.9 = mg/kg Y 2.7 2.7SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Aroclor‐1016 0.044 U mg/kg N 0.011 0.044SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Aroclor‐1221 0.044 U mg/kg N 0.026 0.044SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Aroclor‐1232 0.044 U mg/kg N 0.022 0.044SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Aroclor‐1242 0.044 U mg/kg N 0.014 0.044SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Aroclor‐1248 0.419 = mg/kg Y 0.013 0.044SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Aroclor‐1254 0.13 = mg/kg Y 0.021 0.044

SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Aroclor‐1260 0.044 U mg/kg N 0.014 0.044SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Aroclor‐1262 0.044 U mg/kg N 0.014 0.044SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Aroclor‐1268 0.044 U mg/kg N 0.013 0.044SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Congener 2,3,7,8‐TCDD TEQ 1.24E‐05 = mg/kg Y



SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Congener PCB‐103 0.000206 = mg/kg Y 8.22E-07SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Congener PCB‐104 9.58E‐06 J mg/kg Y 4.69E‐07





























Page 59 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 60 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit













SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Congener PCB‐200 5.23E‐05 = mg/kg Y 0.0000009








SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Congener PCB‐209 0.000231 = mg/kg Y 3.79E-07SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB Congener PCB‐22 0.00464 = mg/kg Y 1.08E‐06



























Page 61 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit









































SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N PCB_TOT Total Aroclors 0.549 = mg/kg Y 0.011 0.044







SD_Grab SD LTM03 081413‐SD‐LTM03‐01 8/14/2013 N SVOC 2,4‐Dinitrophenol 0.88 U mg/kg N 0.054 0.88

Page 62 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 63 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit
















SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N Metal Cadmium 3 = mg/kg Y 0.79 0.79


SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N Metal Chromium 311 = mg/kg Y 1.6 1.6


SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N Metal Copper 109 = mg/kg Y 4 4





SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N Metal Mercury 11.2 = mg/kg Y 0.67 0.67SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N Metal Methyl Mercury 0.00338 J mg/kg Y 0.000194 0.000606


SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N Metal Potassium 3110 = mg/kg Y 1600 1600


SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N Metal Silver 2 = mg/kg Y 0.79 0.79



















Page 64 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 65 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



























SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐189 0.000383 = mg/kg Y 7.04E-07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐19 0.0146 = mg/kg Y 1.11E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐190 0.00171 = mg/kg Y 8.9E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐191 0.000344 = mg/kg Y 6.81E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐192 0.000165 U mg/kg N 6.32E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐193 0.000957 = mg/kg Y 6.69E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐194 0.00416 = mg/kg Y 6.66E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐195 0.00177 = mg/kg Y 3.97E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐196/203 0.00734 = mg/kg Y 0.0000025 0.00033SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐197 0.00023 = mg/kg Y 7.3E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐198 0.000347 = mg/kg Y 2.52E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐199 0.00781 = mg/kg Y 1.25E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐2 0.000726 = mg/kg Y 7.19E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐20/21/33 0.0609 = mg/kg Y 2.51E‐06 0.000495SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐200 0.000805 = mg/kg Y 1.06E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐201 0.000165 UJ mg/kg N 1.21E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐202 0.00232 = mg/kg Y 1.09E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐204 0.000165 U mg/kg N 1.54E‐06 0.000165

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐205 0.000191 = mg/kg Y 8.26E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐206 0.00488 = mg/kg Y 1.21E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐207 0.00052 = mg/kg Y 8.87E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐208 0.00188 = mg/kg Y 6.3E‐07 0.000165

Page 66 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐22 0.0396 = mg/kg Y 8.45E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐23 0.000165 U mg/kg N 1.08E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐24/27 0.0125 = mg/kg Y 0.0000012 0.00033SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐25 0.0851 = mg/kg Y 8.9E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐26 0.0979 = mg/kg Y 6.55E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐28 0.167 = mg/kg Y 3.05E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐29 0.000241 = mg/kg Y 9.82E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐3 0.00125 = mg/kg Y 4.73E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐30 0.000165 U mg/kg N 6.38E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐31 0.185 = mg/kg Y 1.99E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐34 0.00222 = mg/kg Y 1.28E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐35 0.00199 = mg/kg Y 1.15E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐36 0.000165 U mg/kg N 1.08E‐06 0.000165

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐37 0.0251 = mg/kg Y 4.64E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐38 0.00391 = mg/kg Y 8.23E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐39 0.000505 = mg/kg Y 1.34E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐4/10 0.00711 = mg/kg Y 8.45E‐07 0.00033SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐40 0.0526 = mg/kg Y 1.11E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐41/64/71/72 0.297 = mg/kg Y 3.07E‐06 0.00066SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐42/59 0.108 = mg/kg Y 8.25E‐07 0.00033

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐43/49 0.364 = mg/kg Y 1.94E‐06 0.00033SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐44 0.306 = mg/kg Y 1.18E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐45 0.0469 = mg/kg Y 6.03E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐46 0.0299 = mg/kg Y 5.44E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐47 0.128 = mg/kg Y 0.0000015 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐48/75 0.0478 = mg/kg Y 7.12E‐07 0.00033SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐5/8 0.0224 = mg/kg Y 1.08E‐06 0.00033

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐50 0.00133 = mg/kg Y 7.69E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐51 0.024 = mg/kg Y 8.04E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐52/69 0.392 = mg/kg Y 1.46E‐06 0.00033SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐53 0.0743 = mg/kg Y 1.08E‐06 0.000165



SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐6 0.0277 = mg/kg Y 1.24E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐61/70 0.297 = mg/kg Y 1.49E‐06 0.00033SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐62 0.000165 U mg/kg N 1.23E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐63 0.0148 = mg/kg Y 5.32E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐65 0.000165 U mg/kg N 9.82E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐66/76 0.281 = mg/kg Y 5.66E‐07 0.00033SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐67 0.0108 = mg/kg Y 1.13E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐68 0.0024 = mg/kg Y 7.73E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐7/9 0.00185 = mg/kg Y 7.5E‐07 0.00033SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐73 0.000639 = mg/kg Y 5.81E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐74 0.139 = mg/kg Y 9.03E‐07 0.000165

Page 67 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐77 0.0239 = mg/kg Y 7.99E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐78 0.000165 U mg/kg N 6.28E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐79 0.00329 = mg/kg Y 1.16E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐80 0.000165 U mg/kg N 1.07E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐81 0.000873 = mg/kg Y 6.59E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐82 0.0365 = mg/kg Y 1.24E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐83 0.000229 = mg/kg Y 4.5E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐84/92 0.103 = mg/kg Y 8.76E‐07 0.00033


SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐86 0.00182 = mg/kg Y 1.27E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐87/117/125 0.0641 = mg/kg Y 1.47E‐06 0.000495SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐88/91 0.0503 = mg/kg Y 2.27E‐06 0.00033SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐89 0.0075 = mg/kg Y 7.86E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐90/101 0.169 = mg/kg Y 4.49E‐07 0.00033

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐93 0.000165 U mg/kg N 1.35E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐94 0.00281 = mg/kg Y 8.44E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐95/98/102 0.152 = mg/kg Y 2.28E‐06 0.000495SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐96 0.00444 = mg/kg Y 7.96E‐07 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐97 0.073 = mg/kg Y 1.06E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB Congener PCB‐99 0.109 = mg/kg Y 1.34E‐06 0.000165SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB_TOT Total Aroclors 2.339 = mg/kg Y 0.034 0.11SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N PCB_TOT Total PCBs 5.388899 = mg/kg Y

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 1,1'‐Biphenyl 0.2 U mg/kg N 0.019 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2,4,5‐Trichlorophenol 0.51 U mg/kg N 0.092 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2,4,6‐Trichlorophenol 0.51 U mg/kg N 0.082 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2,4‐Dichlorophenol 0.51 U mg/kg N 0.082 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2,4‐Dimethylphenol 0.51 U mg/kg N 0.19 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2,4‐Dinitrophenol 0.51 U mg/kg N 0.45 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2,4‐Dinitrotoluene 0.1 U mg/kg N 0.019 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2,6‐Dinitrotoluene 0.1 U mg/kg N 0.026 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2‐Chloronaphthalene 0.2 U mg/kg N 0.015 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2‐Chlorophenol 0.2 U mg/kg N 0.075 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2‐Methylnaphthalene 0.2 U mg/kg N 0.019 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2‐Methylphenol 0.2 U mg/kg N 0.15 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2‐Nitroaniline 0.51 U mg/kg N 0.023 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 2‐Nitrophenol 0.51 U mg/kg N 0.094 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 3&4‐Methylphenol 0.2 U mg/kg N 0.098 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 3,3‐Dichlorobenzidine 0.2 U mg/kg N 0.067 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 3‐Nitroaniline 0.51 U mg/kg N 0.029 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 4,6‐Dinitro‐2‐methylphenol 0.51 U mg/kg N 0.19 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 4‐Bromophenyl phenyl ether 0.2 U mg/kg N 0.023 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 4‐Chloro‐3‐methylphenol 0.51 U mg/kg N 0.093 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 4‐Chloroaniline 0.51 U mg/kg N 0.027 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 4‐Chlorophenyl phenyl ether 0.2 U mg/kg N 0.019 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 4‐Nitroaniline 0.51 U mg/kg N 0.034 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC 4‐Nitrophenol 1 U mg/kg N 0.17 1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Acenaphthene 0.1 U mg/kg N 0.096 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Acenaphthylene 0.0558 J mg/kg Y 0.011 0.1

Page 68 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Anthracene 0.0733 J mg/kg Y 0.0088 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Atrazine 0.2 U mg/kg N 0.042 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Benzaldehyde 0.51 U mg/kg N 0.026 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Benzo(a)anthracene 0.268 = mg/kg Y 0.02 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Benzo(a)pyrene 0.37 = mg/kg Y 0.022 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Benzo(b)fluoranthene 0.521 = mg/kg Y 0.021 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Benzo(g,h,i)perylene 0.287 = mg/kg Y 0.031 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Benzo(k)fluoranthene 0.198 = mg/kg Y 0.023 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Bis(2‐chloroethoxy)methane 0.2 U mg/kg N 0.023 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Bis(2‐chloroethyl)ether 0.2 U mg/kg N 0.043 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC bis(2‐Chloroisopropyl)ether 0.2 U mg/kg N 0.023 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Bis(2‐ethylhexyl)phthalate 0.924 = mg/kg Y 0.036 0.2

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Butyl benzyl phthalate 0.2 U mg/kg N 0.055 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Caprolactam 0.2 U mg/kg N 0.066 0.2

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Carbazole 0.2 U mg/kg N 0.011 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Chrysene 0.416 = mg/kg Y 0.016 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Dibenz(a,h)anthracene 0.0711 J mg/kg Y 0.037 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Dibenzofuran 0.2 U mg/kg N 0.014 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Diethyl phthalate 0.2 U mg/kg N 0.013 0.2

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Dimethyl phthalate 0.2 U mg/kg N 0.015 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Di‐n‐butyl phthalate 0.2 U mg/kg N 0.012 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Di‐n‐octyl phthalate 0.2 U mg/kg N 0.014 0.2

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Fluoranthene 0.628 = mg/kg Y 0.012 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Fluorene 0.1 U mg/kg N 0.012 0.1

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Hexachlorobenzene 0.2 U mg/kg N 0.02 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Hexachlorobutadiene 0.1 U mg/kg N 0.027 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Hexachlorocyclopentadiene 1 U mg/kg N 0.16 1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Hexachloroethane 0.51 U mg/kg N 0.033 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Indeno(1,2,3‐cd)pyrene 0.296 = mg/kg Y 0.053 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Isophorone 0.2 U mg/kg N 0.019 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Naphthalene 0.1 U mg/kg N 0.016 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Nitrobenzene 0.2 U mg/kg N 0.032 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC N‐Nitroso‐di‐n‐propylamine 0.2 U mg/kg N 0.03 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC N‐Nitrosodiphenylamine 0.51 U mg/kg N 0.054 0.51SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Pentachlorophenol 0.51 U mg/kg N 0.25 0.51

SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Phenanthrene 0.189 = mg/kg Y 0.011 0.1SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Phenol 0.2 U mg/kg N 0.077 0.2SD_Grab SD LTM03 091715‐SD‐LTM03‐01 9/17/2015 N SVOC Pyrene 0.683 = mg/kg Y 0.013 0.1SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N Metal Aluminum 3450 = mg/kg Y 64 64


SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N Metal Arsenic 2.6 U mg/kg N 2.6 2.6

SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N Metal Barium 26 U mg/kg N 26 26



SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N Metal Calcium 640 U mg/kg N 640 640




Page 69 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N Metal Manganese 61.9 = mg/kg Y 1.9 1.9



SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N Metal Nickel 5.1 U mg/kg N 5.1 5.1




SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N Metal Sodium 1300 U mg/kg N 1300 1300



SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N Metal Zinc 52.7 = mg/kg Y 2.6 2.6



































Page 70 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

































SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N PCB Congener PCB‐168 1.26E‐05 J mg/kg Y 8.88E-07SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N PCB Congener PCB‐169 8.1E‐06 U mg/kg N 7.62E‐07 0.0000081















Page 71 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 72 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 73 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




























SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N SVOC Acenaphthylene 0.0169 J mg/kg Y 0.013 0.042





















Page 74 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SD_Grab SD LTM04 081513‐SD‐LTM04‐01 8/15/2013 N SVOC Fluoranthene 0.042 U mg/kg N 0.018 0.042

















SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N Metal Antimony 35 U mg/kg N 35 35






SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N Metal Chromium 12600 = mg/kg Y 17 17


SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N Metal Copper 565 = mg/kg Y 4.4 4.4


SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N Metal Lead 430 = mg/kg Y 10 10



SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N Metal Mercury 143 = mg/kg Y 7 7


SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N Metal Nickel 98.9 = mg/kg Y 7 7






SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N Metal Vanadium 106 = mg/kg Y 87 87

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N Metal Zinc 1550 = mg/kg Y 87 87





SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Aroclor‐1248 238 J mg/kg Y 2.1 6.9


Page 75 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener 2,3,7,8‐TCDD TEQ 0.002713 = mg/kg Y





SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐105 2.14 J mg/kg Y 4.97E‐07 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐106/118 5.76 J mg/kg Y 1.45E‐06 0.00102




SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐110 8.38 J mg/kg Y 8.76E‐07 0.000509

























SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐14 0.00144 = mg/kg Y 4.17E-07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐140 0.0132 = mg/kg Y 8.28E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐141 0.298 = mg/kg Y 6.32E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐144 0.0786 = mg/kg Y 9.42E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐145 0.00234 = mg/kg Y 1.29E‐06 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐146/165 0.207 = mg/kg Y 8.75E‐07 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐147 0.0905 = mg/kg Y 1.22E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐148 0.000509 U mg/kg N 9.37E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐15 0.381 = mg/kg Y 6.24E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐150 0.00505 = mg/kg Y 5.61E‐07 0.000509

Page 76 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐151 0.356 = mg/kg Y 6.92E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐152 0.0101 = mg/kg Y 8.66E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐153 1.13 = mg/kg Y 2.25E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐154 0.0279 = mg/kg Y 1.74E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐155 0.000509 U mg/kg N 6.65E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐156 0.189 = mg/kg Y 3.78E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐157 0.049 = mg/kg Y 6.04E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐158/160 0.199 = mg/kg Y 8.82E‐07 0.00102

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐159 0.000509 U mg/kg N 3.78E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐16/32 10.9 J mg/kg Y 1.43E‐06 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐166 0.0114 = mg/kg Y 8.23E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐167 0.0726 = mg/kg Y 5.95E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐168 0.00332 = mg/kg Y 5.94E‐07 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐169 0.000484 U mg/kg N 7.31E‐07 0.000484SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐17 7.43 J mg/kg Y 6.69E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐170 0.227 = mg/kg Y 5.75E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐171 0.0657 = mg/kg Y 0.0000012 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐172 0.0412 = mg/kg Y 1.09E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐173 0.00767 = mg/kg Y 1.37E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐174 0.272 = mg/kg Y 0.0000011 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐175 0.0122 = mg/kg Y 1.14E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐176 0.0363 = mg/kg Y 6.48E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐177 0.147 = mg/kg Y 1.13E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐178 0.056 = mg/kg Y 5.21E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐179 0.128 = mg/kg Y 4.3E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐18 22 J mg/kg Y 1.38E‐06 0.000509


SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐184 0.000509 U mg/kg N 7.64E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐185 0.0326 = mg/kg Y 5.67E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐186 0.000509 U mg/kg N 5.92E‐07 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐188 0.000509 U mg/kg N 7.05E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐189 0.0102 = mg/kg Y 7.04E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐19 3.23 J mg/kg Y 1.11E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐190 0.046 = mg/kg Y 8.9E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐191 0.00982 = mg/kg Y 6.81E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐192 0.000509 U mg/kg N 6.32E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐193 0.0251 = mg/kg Y 6.69E‐07 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐194 0.126 = mg/kg Y 6.66E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐195 0.0513 = mg/kg Y 3.97E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐196/203 0.202 = mg/kg Y 0.0000025 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐197 0.00598 = mg/kg Y 7.3E‐07 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐198 0.00834 = mg/kg Y 2.52E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐199 0.196 = mg/kg Y 1.25E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐2 0.0605 = mg/kg Y 7.19E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐20/21/33 5.13 = mg/kg Y 2.51E‐06 0.00153

Page 77 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐201 0.0255 = mg/kg Y 1.21E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐202 0.0486 = mg/kg Y 1.09E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐204 0.000509 U mg/kg N 1.54E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐205 0.00652 = mg/kg Y 8.26E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐206 0.0937 = mg/kg Y 1.21E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐207 0.0111 = mg/kg Y 8.87E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐208 0.0272 = mg/kg Y 6.3E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐209 0.0353 = mg/kg Y 1.83E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐22 4.85 J mg/kg Y 8.45E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐23 0.000509 U mg/kg N 1.08E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐24/27 1.34 = mg/kg Y 0.0000012 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐25 12.5 J mg/kg Y 8.9E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐26 13.3 J mg/kg Y 6.55E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐28 17.5 J mg/kg Y 3.05E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐29 0.00665 = mg/kg Y 9.82E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐3 0.072 = mg/kg Y 4.73E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐30 0.00276 = mg/kg Y 6.38E‐07 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐31 21.2 J mg/kg Y 1.99E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐34 0.226 = mg/kg Y 1.28E‐06 0.000509


SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐36 0.00835 = mg/kg Y 1.08E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐37 1.23 = mg/kg Y 4.64E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐38 0.0837 = mg/kg Y 8.23E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐39 0.0594 = mg/kg Y 1.34E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐4/10 1.6 = mg/kg Y 8.45E‐07 0.00102

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐40 2.96 J mg/kg Y 1.11E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐41/64/71/72 20 J mg/kg Y 3.07E‐06 0.00203SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐42/59 7.71 J mg/kg Y 8.25E‐07 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐43/49 22.9 J mg/kg Y 1.94E‐06 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐44 19.4 J mg/kg Y 1.18E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐45 2.19 J mg/kg Y 6.03E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐46 2.29 J mg/kg Y 5.44E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐47 8.56 J mg/kg Y 0.0000015 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐48/75 2.87 = mg/kg Y 7.12E‐07 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐5/8 1.77 = mg/kg Y 1.08E‐06 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐50 0.121 = mg/kg Y 7.69E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐51 2.19 J mg/kg Y 8.04E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐52/69 24.7 J mg/kg Y 1.46E‐06 0.00102

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐53 6.43 J mg/kg Y 1.08E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐54 0.19 = mg/kg Y 6.39E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐55 0.287 = mg/kg Y 5.16E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐56/60 7.62 J mg/kg Y 1.18E‐06 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐57 0.202 = mg/kg Y 8.59E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐58 0.0613 = mg/kg Y 8.3E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐6 7.29 J mg/kg Y 1.24E‐06 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐61/70 12.2 J mg/kg Y 1.49E‐06 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐62 0.000509 U mg/kg N 1.23E‐06 0.000509

Page 78 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐63 0.965 = mg/kg Y 5.32E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐65 0.000509 U mg/kg N 9.82E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐66/76 11.5 J mg/kg Y 5.66E‐07 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐67 0.708 = mg/kg Y 1.13E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐68 0.151 = mg/kg Y 7.73E‐07 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐7/9 0.114 = mg/kg Y 7.5E‐07 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐73 0.058 = mg/kg Y 5.81E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐74 7.24 J mg/kg Y 9.03E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐77 1.05 = mg/kg Y 7.99E‐07 0.000509

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐78 0.000509 U mg/kg N 6.28E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐79 0.0796 = mg/kg Y 1.16E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐80 0.000509 U mg/kg N 1.07E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐81 0.0316 = mg/kg Y 6.59E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐82 1.83 = mg/kg Y 1.24E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐83 0.011 = mg/kg Y 4.5E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐84/92 4.61 J mg/kg Y 8.76E‐07 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐85/116 2.18 = mg/kg Y 1.99E‐06 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐86 0.109 = mg/kg Y 1.27E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐87/117/125 3.1 = mg/kg Y 1.47E‐06 0.00153SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐88/91 2.43 = mg/kg Y 2.27E‐06 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐89 0.325 = mg/kg Y 7.86E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐90/101 6.61 J mg/kg Y 4.49E‐07 0.00102SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐93 0.000509 U mg/kg N 1.35E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐94 0.181 = mg/kg Y 8.44E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐95/98/102 6.11 J mg/kg Y 2.28E‐06 0.00153SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐96 0.256 = mg/kg Y 7.96E‐07 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐97 2.92 J mg/kg Y 1.06E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB Congener PCB‐99 4.44 J mg/kg Y 1.34E‐06 0.000509SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB_TOT Total Aroclors 238 = mg/kg Y 0.11 0.34SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N PCB_TOT Total PCBs 353.9138 = mg/kg Y

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 1,1'‐Biphenyl 0.0605 J mg/kg Y 0.021 0.23

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2,4,5‐Trichlorophenol 0.57 U mg/kg N 0.1 0.57SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2,4,6‐Trichlorophenol 0.57 U mg/kg N 0.092 0.57SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2,4‐Dichlorophenol 0.57 U mg/kg N 0.091 0.57

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2,4‐Dimethylphenol 0.57 U mg/kg N 0.21 0.57SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2,4‐Dinitrophenol 0.57 U mg/kg N 0.5 0.57

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2,4‐Dinitrotoluene 0.11 U mg/kg N 0.021 0.11SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2,6‐Dinitrotoluene 0.11 U mg/kg N 0.029 0.11SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2‐Chloronaphthalene 0.23 U mg/kg N 0.016 0.23SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2‐Chlorophenol 0.23 U mg/kg N 0.084 0.23SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2‐Methylnaphthalene 0.177 J mg/kg Y 0.021 0.23SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2‐Methylphenol 0.23 U mg/kg N 0.17 0.23SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2‐Nitroaniline 0.57 U mg/kg N 0.026 0.57SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 2‐Nitrophenol 0.57 U mg/kg N 0.11 0.57SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 3&4‐Methylphenol 0.23 U mg/kg N 0.11 0.23SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 3,3‐Dichlorobenzidine 0.23 U mg/kg N 0.074 0.23SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 3‐Nitroaniline 0.57 U mg/kg N 0.032 0.57


Page 79 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 4‐Bromophenyl phenyl ether 0.23 U mg/kg N 0.026 0.23SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 4‐Chloro‐3‐methylphenol 0.57 U mg/kg N 0.1 0.57SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 4‐Chloroaniline 0.57 U mg/kg N 0.03 0.57SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 4‐Chlorophenyl phenyl ether 0.23 U mg/kg N 0.021 0.23SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 4‐Nitroaniline 0.57 U mg/kg N 0.038 0.57

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC 4‐Nitrophenol 1.1 U mg/kg N 0.19 1.1SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC Acenaphthene 0.257 = mg/kg Y 0.11 0.11

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC Acenaphthylene 0.358 = mg/kg Y 0.012 0.11

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC Anthracene 2.12 = mg/kg Y 0.0098 0.11


SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC Benzaldehyde 1.24 = mg/kg Y 0.028 0.57












SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC Carbazole 0.196 J mg/kg Y 0.013 0.23


SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC Dibenz(a,h)anthracene 0.227 = mg/kg Y 0.041 0.11

SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC Dibenzofuran 0.385 = mg/kg Y 0.016 0.23






SD_Grab SD LTM04 091615‐SD‐LTM04‐01 9/16/2015 N SVOC Fluorene 0.28 = mg/kg Y 0.014 0.11

















Page 80 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N Metal Beryllium 0.24 U mg/kg N 0.24 0.24


SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N Metal Calcium 1210 J mg/kg Y 590 590

SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N Metal Chromium 47.4 J mg/kg Y 1.2 1.2


SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N Metal Copper 6 = mg/kg Y 3 3



SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N Metal Magnesium 590 U mg/kg N 590 590



SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N Metal Methyl Mercury 0.000799 J mg/kg Y 0.000013 0.000032







SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N Metal Vanadium 5.9 U mg/kg N 5.9 5.9

SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N Metal Zinc 25.2 J mg/kg Y 2.4 2.4























SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N PCB Congener PCB‐114 0.002 = mg/kg Y 6.69E-07SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N PCB Congener PCB‐119 0.00214 = mg/kg Y 6.28E‐07



Page 81 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 82 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit















































SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N PCB Congener PCB‐31 0.0893 J mg/kg Y 0.0000012


Page 83 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit








SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N PCB Congener PCB‐41/64/71/72 0.116 J mg/kg Y 1.54E‐06









































Page 84 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit












SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N SVOC 2,4,5‐Trichlorophenol 0.2 U mg/kg N 0.046 0.2SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N SVOC 2,4,6‐Trichlorophenol 0.2 U mg/kg N 0.037 0.2






















SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N SVOC Acenaphthene 0.0165 J mg/kg Y 0.012 0.04

SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N SVOC Acenaphthylene 0.0253 J mg/kg Y 0.013 0.04













Page 85 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N SVOC Carbazole 0.0205 J mg/kg Y 0.018 0.079









SD_Grab SD LTM05 081413‐SD‐LTM05‐01 8/14/2013 N SVOC Fluorene 0.0189 J mg/kg Y 0.013 0.04





















SD_Grab SD LTM05 091715‐SD‐LTM05‐01 9/17/2015 N Metal Calcium 330 U mg/kg N 330 330







SD_Grab SD LTM05 091715‐SD‐LTM05‐01 9/17/2015 N Metal Manganese 50.3 = mg/kg Y 1 1









Page 86 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 87 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 88 of 215

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Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit
























SD_Grab SD LTM05 091715‐SD‐LTM05‐01 9/17/2015 N PCB Congener PCB‐29 8.15E‐05 UJ mg/kg N 9.82E‐07 0.0000815

























Page 89 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


























SD_Grab SD LTM05 091715‐SD‐LTM05‐01 9/17/2015 N PCB Congener PCB‐86 0.000855 = mg/kg Y 1.27E-06 0.0000815SD_Grab SD LTM05 091715‐SD‐LTM05‐01 9/17/2015 N PCB Congener PCB‐87/117/125 0.0259 = mg/kg Y 1.47E‐06 0.000245






















Page 90 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 91 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SD_Grab SD LTM05 091715‐SD‐LTM05‐01 9/17/2015 N SVOC Phenanthrene 0.0321 J mg/kg Y 0.0048 0.044




SD_Grab SD LTM06 081313‐SD‐LTM06‐01 8/13/2013 N Metal Antimony 2 U mg/kg N 2 2

SD_Grab SD LTM06 081313‐SD‐LTM06‐01 8/13/2013 N Metal Arsenic 2 U mg/kg N 2 2









SD_Grab SD LTM06 081313‐SD‐LTM06‐01 8/13/2013 N Metal Lead 5.6 = mg/kg Y 2 2


SD_Grab SD LTM06 081313‐SD‐LTM06‐01 8/13/2013 N Metal Manganese 44.8 = mg/kg Y 1.5 1.5









SD_Grab SD LTM06 081313‐SD‐LTM06‐01 8/13/2013 N Metal Vanadium 4.9 U mg/kg N 4.9 4.9

SD_Grab SD LTM06 081313‐SD‐LTM06‐01 8/13/2013 N Metal Zinc 23 = mg/kg Y 2 2



















Page 92 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 93 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 94 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit










































SD_Grab SD LTM06 081313‐SD‐LTM06‐01 8/13/2013 N PCB Congener PCB‐7/9 7.16E‐05 J mg/kg Y 3.16E‐06







Page 95 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 96 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SD_Grab SD LTM06 081313‐SD‐LTM06‐01 8/13/2013 N SVOC Benzo(k)fluoranthene 0.0248 J mg/kg Y 0.015 0.039





















SD_Grab SD LTM06 081313‐SD‐LTM06‐01 8/13/2013 N SVOC Indeno(1,2,3‐cd)pyrene 0.0376 J mg/kg Y 0.014 0.039







SD_Grab SD LTM06 081313‐SD‐LTM06‐01 8/13/2013 N SVOC Phenanthrene 0.0339 J mg/kg Y 0.018 0.039






SD_Grab SD LTM06 091515‐SD‐LTM06‐01 9/15/2015 N Metal Barium 39.1 = mg/kg Y 17 17











Page 97 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD LTM06 091515‐SD‐LTM06‐01 9/15/2015 N Metal Methyl Mercury 0.0013 J mg/kg Y 0.000143 0.000446















































Page 98 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 99 of 215

Attachment C




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Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 100 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 101 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 102 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit















SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Aluminum 11300 J mg/kg Y 42 87.4

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Antimony 26.2 UJ mg/kg N 1.7 26.2

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Arsenic 14.4 J mg/kg Y 1.3 4.4

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Barium 106 J mg/kg Y 0.31 87.4

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Beryllium 2.2 UJ mg/kg N 0.19 2.2

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Cadmium 2.2 U mg/kg N 0.16 2.2

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Calcium 4110 J mg/kg Y 69.9 2190

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Chromium 205 J mg/kg Y 0.87 4.4

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Cobalt 18.4 J mg/kg Y 0.7 21.9

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Copper 102 J mg/kg Y 3.2 10.9

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Iron 21500 J mg/kg Y 21.4 43.7

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Lead 121 J mg/kg Y 0.83 1.3

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Magnesium 7610 J mg/kg Y 22.3 2190

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Manganese 2460 J mg/kg Y 0.32 6.6

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Mercury 11.5 J mg/kg Y 0.33 2.2

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Methyl Mercury 0.0027 J mg/kg Y 0.00081 0.0022

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Nickel 57.2 J mg/kg Y 1.2 17.5

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Potassium 2310 J mg/kg Y 27.1 2190

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Selenium 2.2 UJ mg/kg N 2 2.2

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Silver 4.4 U mg/kg N 0.44 4.4

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Sodium 13400 J mg/kg Y 288 2190

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Thallium 7.1 J mg/kg Y 2.4 4.4

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Vanadium 37.6 J mg/kg Y 0.52 21.9

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N Metal Zinc 272 J mg/kg Y 4.4 8.7

SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N PCB Aroclor‐1016 0.018 UJ mg/kg N 0.0027 0.018




SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N PCB Aroclor‐1248 0.3 J mg/kg Y 0.0017 0.018





SD_Grab SD MRH‐236 MRH‐236‐0‐5‐10225 8/13/2010 N PCB_TOT Total Aroclors 0.57 = mg/kg Y 0.0027 0.018

Page 103 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD MRH‐236 MRH‐236‐10‐15‐10225 8/13/2010 N Metal Aluminum 15900 J mg/kg Y 43.1 89.9

SD_Grab SD MRH‐236 MRH‐236‐10‐15‐10225 8/13/2010 N Metal Antimony 27 UJ mg/kg N 1.8 27




SD_Grab SD MRH‐236 MRH‐236‐10‐15‐10225 8/13/2010 N Metal Cadmium 2.2 U mg/kg N 0.16 2.2





SD_Grab SD MRH‐236 MRH‐236‐10‐15‐10225 8/13/2010 N Metal Iron 28000 J mg/kg Y 22 44.9






SD_Grab SD MRH‐236 MRH‐236‐10‐15‐10225 8/13/2010 N Metal Nickel 53.3 J mg/kg Y 1.2 18


SD_Grab SD MRH‐236 MRH‐236‐10‐15‐10225 8/13/2010 N Metal Selenium 3.8 J mg/kg Y 2 2.2

SD_Grab SD MRH‐236 MRH‐236‐10‐15‐10225 8/13/2010 N Metal Silver 8.3 J mg/kg Y 0.45 4.5




SD_Grab SD MRH‐236 MRH‐236‐10‐15‐10225 8/13/2010 N Metal Zinc 234 J mg/kg Y 4.5 9












SD_Grab SD MRH‐237 MRH‐237‐0‐5‐10225 8/13/2010 N Metal Antimony 27.7 UJ mg/kg N 1.8 27.7




SD_Grab SD MRH‐237 MRH‐237‐0‐5‐10225 8/13/2010 N Metal Cadmium 2.4 J mg/kg Y 0.17 2.3









Page 104 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit





SD_Grab SD MRH‐237 MRH‐237‐0‐5‐10225 8/13/2010 N Metal Selenium 11.5 UJ mg/kg N 10.4 11.5

SD_Grab SD MRH‐237 MRH‐237‐0‐5‐10225 8/13/2010 N Metal Silver 23.1 UJ mg/kg N 2.3 23.1















SD_Grab SD MRH‐237 MRH‐237‐10‐15‐10225 8/13/2010 N Metal Aluminum 11200 J mg/kg Y 40.3 84

SD_Grab SD MRH‐237 MRH‐237‐10‐15‐10225 8/13/2010 N Metal Antimony 3.2 J mg/kg Y 1.6 25.2


SD_Grab SD MRH‐237 MRH‐237‐10‐15‐10225 8/13/2010 N Metal Barium 1110 J mg/kg Y 0.3 84





SD_Grab SD MRH‐237 MRH‐237‐10‐15‐10225 8/13/2010 N Metal Cobalt 71.3 J mg/kg Y 0.67 21


SD_Grab SD MRH‐237 MRH‐237‐10‐15‐10225 8/13/2010 N Metal Iron 39300 J mg/kg Y 20.6 42






SD_Grab SD MRH‐237 MRH‐237‐10‐15‐10225 8/13/2010 N Metal Nickel 403 J mg/kg Y 1.1 16.8



SD_Grab SD MRH‐237 MRH‐237‐10‐15‐10225 8/13/2010 N Metal Silver 21 U mg/kg N 2.1 21


SD_Grab SD MRH‐237 MRH‐237‐10‐15‐10225 8/13/2010 N Metal Thallium 218 J mg/kg Y 11.6 21

SD_Grab SD MRH‐237 MRH‐237‐10‐15‐10225 8/13/2010 N Metal Vanadium 109 J mg/kg Y 0.5 21






Page 105 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit









SD_Grab SD MRH‐238 MRH‐238‐0‐5‐10225 8/13/2010 N Metal Arsenic 9.1 J mg/kg Y 1 3.5









SD_Grab SD MRH‐238 MRH‐238‐0‐5‐10225 8/13/2010 N Metal Lead 561 J mg/kg Y 0.66 1






SD_Grab SD MRH‐238 MRH‐238‐0‐5‐10225 8/13/2010 N Metal Potassium 1730 U mg/kg N 21.4 1730
















SD_Grab SD MRH‐238 MRH‐238‐0‐5‐10225 8/13/2010 N PCB_TOT Total Aroclors 3 = mg/kg Y 0.0021 0.014







SD_Grab SD MRH‐238 MRH‐238‐10‐15‐10225 8/13/2010 N Metal Calcium 2540 J mg/kg Y 34 1060


Page 106 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD MRH‐238 MRH‐238‐10‐15‐10225 8/13/2010 N Metal Cobalt 14 J mg/kg Y 0.34 10.6








SD_Grab SD MRH‐238 MRH‐238‐10‐15‐10225 8/13/2010 N Metal Nickel 95 J mg/kg Y 0.57 8.5












SD_Grab SD MRH‐238 MRH‐238‐10‐15‐10225 8/13/2010 N PCB Aroclor‐1248 51 J mg/kg Y 0.083 0.88

SD_Grab SD MRH‐238 MRH‐238‐10‐15‐10225 8/13/2010 N PCB Aroclor‐1254 33 J mg/kg Y 0.12 0.88




SD_Grab SD MRH‐238 MRH‐238‐10‐15‐10225 8/13/2010 N PCB_TOT Total Aroclors 84 = mg/kg Y 0.13 0.88

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Aluminum 11700 = mg/kg Y 44 44

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Antimony 4.4 U mg/kg N 4.4 4.4

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Arsenic 11.8 = mg/kg Y 4.4 4.4

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Barium 216 = mg/kg Y 44 44

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Beryllium 1.4 = mg/kg Y 1.1 1.1

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Cadmium 5 = mg/kg Y 1.1 1.1

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Calcium 4730 = mg/kg Y 1100 1100

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Chromium 885 = mg/kg Y 2.2 2.2

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Cobalt 11.6 = mg/kg Y 11 11

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Copper 132 = mg/kg Y 5.5 5.5

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Iron 24400 = mg/kg Y 22 22

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Lead 180 = mg/kg Y 4.4 4.4

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Magnesium 4980 = mg/kg Y 1100 1100

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Manganese 736 = mg/kg Y 3.3 3.3

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Mercury 15.5 = mg/kg Y 6.6 6.6

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Nickel 41.5 = mg/kg Y 8.8 8.8

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Potassium 2120 = mg/kg Y 1100 1100

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Selenium 4.4 U mg/kg N 4.4 4.4

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Silver 2.3 = mg/kg Y 2.2 2.2

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Sodium 2460 = mg/kg Y 2200 2200

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Thallium 2.2 U mg/kg N 2.2 2.2

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Vanadium 36.5 = mg/kg Y 11 11

Page 107 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N Metal Zinc 472 = mg/kg Y 4.4 4.4

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Aroclor‐1016 1.5 U mg/kg N 0.28 1.5




SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Aroclor‐1248 58.1 = mg/kg Y 0.51 1.5



SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Congener 2,3,7,8‐TCDD TEQ 0.00048 = mg/kg Y

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Congener PCB‐1 0.00521 = mg/kg Y 0 0.0000157





SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Congener PCB‐106/118 0.897 = mg/kg Y 0 0.0000157











SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Congener PCB‐121 1.57E‐05 U mg/kg N 0 0.0000157
















SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Congener PCB‐138/163/164 0.295 = mg/kg Y 0 0.0000157







Page 108 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit










SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Congener PCB‐155 5.51E‐05 = mg/kg Y 0 0.0000157





















SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Congener PCB‐18 0.466 J mg/kg Y 0 0.0000157


















Page 109 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit
















SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Congener PCB‐23 0.000848 J mg/kg Y 0 0.0000157

















SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB Congener PCB‐41/64/71/72 1.24 J mg/kg Y 0 0.0000157
















Page 110 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


































SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB_TOT Total Aroclors 58.1 = mg/kg Y 0.28 1.5

SD_Grab SD SC‐A.2 072106‐SD‐ONC‐0A2‐0001 7/21/2006 N PCB_TOT Total PCBs 31.24462 = mg/kg Y

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Aluminum 17800 = mg/kg Y 160 160

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Antimony 16 U mg/kg N 16 16

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Arsenic 146 = mg/kg Y 16 16

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Barium 388 = mg/kg Y 160 160

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Beryllium 1.6 U mg/kg N 1.6 1.6

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Cadmium 31.6 = mg/kg Y 3.9 3.9

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Calcium 41600 = mg/kg Y 3900 3900

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Chromium 5610 = mg/Kg Y 7.8 7.8

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Cobalt 49.1 = mg/kg Y 39 39

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Copper 451 = mg/kg Y 20 20

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Iron 61600 = mg/kg Y 78 78

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Lead 193 = mg/kg Y 16 16

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Magnesium 6510 = mg/kg Y 3900 3900

Page 111 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Manganese 1930 = mg/kg Y 12 12

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Mercury 53.1 = mg/kg Y 4.7 4.7

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Methyl Mercury 0.00371 = mg/kg Y 0.000196 0.000613

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Nickel 234 = mg/kg Y 31 31

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Potassium 7800 U mg/kg N 7800 7800

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Selenium 16 U mg/kg N 16 16

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Silver 3.9 U mg/kg N 3.9 3.9

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Sodium 11500 = mg/kg Y 7800 7800

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Thallium 7.8 U mg/kg N 7.8 7.8

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Vanadium 110 = mg/kg Y 39 39

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N Metal Zinc 3390 = mg/kg Y 16 16

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N PCB Aroclor‐1016 0.22 U mg/kg N 0.08 0.22




SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N PCB Aroclor‐1248 37.5 = mg/kg Y 0.44 2.2





SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N PCB_TOT Total Aroclors 37.5 = mg/kg Y 0.08 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 1,1'‐Biphenyl 0.44 U mg/kg N 0.025 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2,4,5‐Trichlorophenol 1.1 U mg/kg N 0.25 1.1


SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2,4‐Dichlorophenol 1.1 U mg/kg N 0.35 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2,4‐Dimethylphenol 1.1 U mg/kg N 0.37 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2,4‐Dinitrophenol 4.4 U mg/kg N 0.27 4.4

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2,4‐Dinitrotoluene 0.44 U mg/kg N 0.095 0.44


SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2‐Chloronaphthalene 0.44 U mg/kg N 0.068 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2‐Chlorophenol 1.1 U mg/kg N 0.22 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2‐Methylnaphthalene 0.44 U mg/kg N 0.12 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2‐Methylphenol 0.44 U mg/kg N 0.25 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2‐Nitroaniline 1.1 U mg/kg N 0.096 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 2‐Nitrophenol 1.1 U mg/kg N 0.23 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 3&4‐Methylphenol 0.44 U mg/kg N 0.28 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 3,3‐Dichlorobenzidine 1.1 U mg/kg N 0.056 1.1


SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 4.4 U mg/kg N 0.27 4.4

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 4‐Bromophenyl phenyl ether 0.44 U mg/kg N 0.079 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 4‐Chloro‐3‐methylphenol 1.1 U mg/kg N 0.22 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 4‐Chloroaniline 1.1 U mg/kg N 0.07 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC 4‐Chlorophenyl phenyl ether 0.44 U mg/kg N 0.066 0.44



SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Acenaphthene 0.22 U mg/kg N 0.063 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Acenaphthylene 0.22 U mg/kg N 0.07 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Acetophenone 1.1 U mg/kg N 0.038 1.1

Page 112 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Anthracene 0.22 U mg/kg N 0.076 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Atrazine 1.1 U mg/kg N 0.043 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Benzaldehyde 1.1 U mg/kg N 0.05 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Benzo(a)anthracene 0.22 U mg/kg N 0.071 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Benzo(a)pyrene 0.22 U mg/kg N 0.067 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Benzo(b)fluoranthene 0.22 U mg/kg N 0.073 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Benzo(g,h,i)perylene 0.22 U mg/kg N 0.081 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Benzo(k)fluoranthene 0.22 U mg/kg N 0.082 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Bis(2‐chloroethoxy)methane 0.44 U mg/kg N 0.088 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Bis(2‐chloroethyl)ether 0.44 U mg/kg N 0.066 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC bis(2‐Chloroisopropyl)ether 0.44 U mg/kg N 0.065 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Bis(2‐ethylhexyl)phthalate 19.1 = mg/kg Y 0.19 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Butyl benzyl phthalate 0.44 U mg/kg N 0.13 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Caprolactam 0.44 U mg/kg N 0.069 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Carbazole 0.44 U mg/kg N 0.1 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Chrysene 0.22 U mg/kg N 0.074 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Dibenz(a,h)anthracene 0.22 U mg/kg N 0.075 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Dibenzofuran 0.44 U mg/kg N 0.065 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Diethyl phthalate 0.44 U mg/kg N 0.075 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Dimethyl phthalate 0.441 = mg/kg Y 0.077 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Di‐n‐butyl phthalate 0.44 U mg/kg N 0.049 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Di‐n‐octyl phthalate 0.44 U mg/kg N 0.11 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Fluoranthene 0.131 J mg/kg Y 0.096 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Fluorene 0.22 U mg/kg N 0.072 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Hexachlorobenzene 0.44 U mg/kg N 0.071 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Hexachlorobutadiene 0.22 U mg/kg N 0.061 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Hexachlorocyclopentadiene 4.4 U mg/kg N 0.22 4.4

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Hexachloroethane 1.1 U mg/kg N 0.061 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.22 U mg/kg N 0.076 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Isophorone 0.44 U mg/kg N 0.059 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Naphthalene 0.22 U mg/kg N 0.06 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Nitrobenzene 0.44 U mg/kg N 0.063 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 0.44 U mg/kg N 0.053 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC N‐Nitrosodiphenylamine 1.1 U mg/kg N 0.13 1.1

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Pentachlorophenol 2.2 U mg/kg N 0.37 2.2

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Phenanthrene 0.22 U mg/kg N 0.099 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Phenol 0.44 U mg/kg N 0.23 0.44

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N SVOC Pyrene 0.109 J mg/kg Y 0.084 0.22

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 1,1,1‐Trichloroethane 0.069 U mg/kg N 0.0018 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 1,1,2,2‐Tetrachloroethane 0.069 U mg/kg N 0.004 0.069


SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 0.069 U mg/kg N 0.0077 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 1,1‐Dichloroethane 0.069 U mg/kg N 0.0019 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 1,1‐Dichloroethene 0.069 U mg/kg N 0.0091 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 1,2,4‐Trichlorobenzene 0.069 U mg/kg N 0.0047 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 0.14 U mg/kg N 0.0074 0.14

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 1,2‐Dibromoethane 0.014 U mg/kg N 0.0019 0.014

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 1,2‐Dichlorobenzene 0.0221 J mg/kg Y 0.0037 0.069

Page 113 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 1,2‐Dichloropropane 0.069 U mg/kg N 0.0018 0.069



SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC 2‐Hexanone 0.069 U mg/kg N 0.013 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Acetone 0.73 J mg/kg Y 0.031 0.14

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Benzene 0.014 U mg/kg N 0.0047 0.014

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Bromodichloromethane 0.069 U mg/kg N 0.0035 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Bromoform 0.069 U mg/kg N 0.0021 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Bromomethane 0.069 U mg/kg N 0.0055 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Carbon Disulfide 0.063 J mg/kg Y 0.0042 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Carbon Tetrachloride 0.069 U mg/kg N 0.0076 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Chlorobenzene 0.188 = mg/kg Y 0.0047 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Chloroethane 0.069 U mg/kg N 0.014 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Chloroform 0.069 U mg/kg N 0.0044 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Chloromethane 0.069 U mg/kg N 0.0023 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC cis‐1,2‐Dichloroethene 0.069 U mg/kg N 0.0033 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC cis‐1,3‐Dichloropropene 0.069 U mg/kg N 0.0018 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Cyclohexane 0.069 U mg/kg N 0.0021 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Dibromochloromethane 0.069 U mg/kg N 0.0015 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Dichlorodifluoromethane 0.069 U mg/kg N 0.013 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Ethylbenzene 0.014 U mg/kg N 0.0051 0.014

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Isopropylbenzene 0.069 U mg/kg N 0.0071 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Methyl Acetate 0.069 U mg/kg N 0.011 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Methyl ethyl ketone 0.14 U mg/kg N 0.027 0.14

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Methyl isobutyl ketone 0.069 U mg/kg N 0.011 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Methyl tert‐butyl ether 0.014 U mg/kg N 0.0039 0.014

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Methylcyclohexane 0.069 U mg/kg N 0.009 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Methylene Chloride 0.069 U mg/kg N 0.0031 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Styrene 0.069 U mg/kg N 0.0015 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Tetrachloroethene 0.069 U mg/kg N 0.002 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Toluene 0.0085 J mg/kg Y 0.004 0.014

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC trans‐1,2‐Dichloroethene 0.069 U mg/kg N 0.0062 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC trans‐1,3‐Dichloropropene 0.069 U mg/kg N 0.0013 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Trichloroethene 0.069 U mg/kg N 0.0072 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Trichlorofluoromethane 0.069 U mg/kg N 0.0031 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Vinyl Chloride 0.069 U mg/kg N 0.0024 0.069

SD_Grab SD SC‐B.1 063010‐SD‐SC‐B1‐001 6/30/2010 N VOC Xylenes, Total 0.027 U mg/kg N 0.0064 0.027


SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Antimony 7.1 U mg/kg N 7.1 7.1

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Arsenic 31.5 = mg/kg Y 7.1 7.1


SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Beryllium 1 = mg/kg Y 0.71 0.71

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Cadmium 17.2 = mg/kg Y 1.8 1.8



SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Cobalt 22.1 = mg/kg Y 18 18

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Copper 318 = mg/kg Y 8.9 8.9

Page 114 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Lead 221 = mg/kg Y 7.1 7.1


SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Manganese 878 = mg/kg Y 5.3 5.3



SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Nickel 84.6 = mg/kg Y 14 14

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Potassium 4020 = mg/kg Y 3600 3600

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Selenium 7.1 U mg/kg N 7.1 7.1

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Silver 4.4 = mg/kg Y 1.8 1.8



SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Vanadium 68.8 = mg/kg Y 18 18

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N Metal Zinc 1010 = mg/kg Y 7.1 7.1

































SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC 4‐Nitroaniline 0.48 U mg/kg N 0.037 0.48SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC 4‐Nitrophenol 0.96 U mg/kg N 0.16 0.96

Page 115 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Acenaphthylene 0.0398 J mg/kg Y 0.031 0.096


SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Anthracene 0.044 J mg/kg Y 0.033 0.096


SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Benzaldehyde 0.0378 J mg/kg Y 0.022 0.48

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Benzo(a)anthracene 0.157 = mg/kg Y 0.031 0.096

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Benzo(a)pyrene 0.203 = mg/kg Y 0.029 0.096

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Benzo(b)fluoranthene 0.21 = mg/kg Y 0.032 0.096

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Benzo(g,h,i)perylene 0.158 = mg/kg Y 0.036 0.096

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Benzo(k)fluoranthene 0.158 = mg/kg Y 0.036 0.096








SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Chrysene 0.184 = mg/kg Y 0.032 0.096

SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Dibenz(a,h)anthracene 0.0702 J mg/kg Y 0.033 0.096



SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Dimethyl phthalate 0.192 = mg/kg Y 0.034 0.19



SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Fluoranthene 0.324 = mg/kg Y 0.042 0.096






SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.139 = mg/kg Y 0.033 0.096







SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Phenanthrene 0.0908 J mg/kg Y 0.044 0.096


SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N SVOC Pyrene 0.279 = mg/kg Y 0.037 0.096








Page 116 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit






SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N VOC 1,3‐Dichlorobenzene 0.026 U mg/kg N 0.0014 0.026










SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N VOC Chlorobenzene 0.026 U mg/kg N 0.0017 0.026



















SD_Grab SD SC‐B.2 063010‐SD‐SC‐B2‐001 6/30/2010 N VOC Toluene 0.0051 U mg/kg N 0.0015 0.0051











SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N Metal Beryllium 0.54 = mg/kg Y 0.24 0.24

SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N Metal Cadmium 0.61 U mg/kg N 0.61 0.61


Page 117 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N Metal Chromium 33.7 = mg/Kg Y 1.2 1.2

SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N Metal Cobalt 9.9 = mg/kg Y 6.1 6.1

SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N Metal Copper 21.2 = mg/kg Y 3 3


SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N Metal Lead 9 = mg/kg Y 2.4 2.4





SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N Metal Nickel 18.9 = mg/kg Y 4.9 4.9




SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N Metal Sodium 1200 U mg/kg N 1200 1200


SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N Metal Vanadium 30 = mg/kg Y 6.1 6.1

SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N Metal Zinc 50.8 = mg/kg Y 2.4 2.4
































Page 118 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit







SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Anthracene 0.0254 J mg/kg Y 0.012 0.035


SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Benzaldehyde 0.0318 J mg/kg Y 0.0081 0.18

SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Benzo(a)anthracene 0.0195 J mg/kg Y 0.012 0.035

SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Benzo(a)pyrene 0.014 J mg/kg Y 0.011 0.035









SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Caprolactam 0.071 U mg/kg N 0.011 0.071SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Carbazole 0.071 U mg/kg N 0.016 0.071

SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Chrysene 0.0201 J mg/kg Y 0.012 0.035




SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Dimethyl phthalate 0.071 U mg/kg N 0.012 0.071


SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Di‐n‐octyl phthalate 0.071 U mg/kg N 0.017 0.071SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Fluoranthene 0.0432 = mg/kg Y 0.016 0.035













SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Phenanthrene 0.037 = mg/kg Y 0.016 0.035


SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N SVOC Pyrene 0.0356 = mg/kg Y 0.014 0.035





Page 119 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit












SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N VOC Acetone 0.63 U mg/kg N 0.14 0.63





SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N VOC Carbon Disulfide 0.31 U mg/kg N 0.019 0.31


SD_Grab SD SC‐B.3 062910‐SD‐SC‐B3‐001 6/29/2010 N VOC Chlorobenzene 0.159 J mg/kg Y 0.021 0.31






























Page 120 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Beryllium 1.2 = mg/kg Y 0.25 0.25



SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Chromium 40.4 = mg/Kg Y 1.2 1.2

SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Cobalt 20.4 = mg/kg Y 6.2 6.2

SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Copper 39.2 = mg/kg Y 3.1 3.1


SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Lead 22.1 = mg/kg Y 2.5 2.5



SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Mercury 0.042 U mg/kg N 0.042 0.042

SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Methyl Mercury 0.00001 U mg/kg N 0.00001 0.000031

SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Nickel 43.5 = mg/kg Y 4.9 4.9




SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Sodium 1200 U mg/kg N 1200 1200


SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Vanadium 40.9 = mg/kg Y 6.2 6.2

SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N Metal Zinc 119 = mg/kg Y 2.5 2.5





























Page 121 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit





















SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.073 U mg/kg N 0.032 0.073








SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N SVOC Dimethyl phthalate 0.073 U mg/kg N 0.013 0.073



SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N SVOC Fluoranthene 0.036 U mg/kg N 0.016 0.036















SD_Grab SD SC‐B.4 062910‐SD‐SC‐B4‐001 6/29/2010 N SVOC Pyrene 0.036 U mg/kg N 0.014 0.036


Page 122 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 123 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Antimony 13 U mg/kg N 13 13

SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Arsenic 22.5 = mg/kg Y 13 13

SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Barium 130 U mg/kg N 130 130

SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Beryllium 1.3 U mg/kg N 1.3 1.3




SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Cobalt 33 U mg/kg N 33 33

SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Copper 71.2 = mg/kg Y 16 16


SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Lead 38.3 = mg/kg Y 13 13





SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Nickel 29.9 = mg/kg Y 26 26

SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Potassium 6600 U mg/kg N 6600 6600

SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Selenium 13 U mg/kg N 13 13




SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Vanadium 37.1 = mg/kg Y 33 33

SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N Metal Zinc 248 = mg/kg Y 13 13


























Page 124 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit









SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N SVOC 4‐Nitrophenol 2 U mg/kg N 0.33 2















SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.39 U mg/kg N 0.17 0.39








SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N SVOC Dimethyl phthalate 0.333 J mg/kg Y 0.069 0.39



SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N SVOC Fluoranthene 0.2 U mg/kg N 0.087 0.2












SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N SVOC Pentachlorophenol 2 U mg/kg N 0.34 2


Page 125 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD SC‐B.5 063019‐SD‐SC‐B5‐001 6/30/2010 N SVOC Pyrene 0.2 U mg/kg N 0.075 0.2















































Page 126 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Aluminum 13500 = mg/kg Y 20 20

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Antimony 9.9 U mg/kg N 9.9 9.9

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Arsenic 27.4 = mg/kg Y 2 2

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Barium 260 = mg/kg Y 20 20

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Beryllium 0.38 = mg/kg Y 0.2 0.2

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Cadmium 4.4 = mg/kg Y 0.5 0.5

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Calcium 4100 = mg/kg Y 500 500

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Chromium 2920 = mg/Kg Y 0.99 0.99

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Cobalt 9.6 = mg/kg Y 5 5

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Copper 125 = mg/kg Y 2.5 2.5

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Iron 17600 = mg/kg Y 50 50

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Lead 104 = mg/kg Y 2 2

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Magnesium 3780 = mg/kg Y 500 500

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Manganese 2900 = mg/kg Y 7.4 7.4

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Mercury 47.3 = mg/kg Y 7.3 7.3

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Methyl Mercury 0.00414 J mg/kg Y 0.000093 0.000291

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Nickel 45 = mg/kg Y 4 4

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Potassium 1820 = mg/kg Y 990 990

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Selenium 2 U mg/kg N 2 2

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Silver 1.1 = mg/kg Y 0.5 0.5

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Sodium 2560 = mg/kg Y 990 990

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Thallium 5 U mg/kg N 5 5

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Vanadium 47.4 = mg/kg Y 5 5

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N Metal Zinc 542 = mg/kg Y 9.9 9.9

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N PCB Aroclor‐1016 0.068 U mg/kg N 0.024 0.068



SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N PCB Aroclor‐1242 83.5 J mg/kg Y 1.2 3.4






SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N PCB_TOT Total Aroclors 83.5 = mg/kg Y 0.024 0.068

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 1,1'‐Biphenyl 0.13 U mg/kg N 0.0076 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2,4,5‐Trichlorophenol 0.33 U mg/kg N 0.076 0.33


SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2,4‐Dichlorophenol 0.33 U mg/kg N 0.11 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2,4‐Dimethylphenol 0.33 U mg/kg N 0.11 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2,4‐Dinitrophenol 1.3 UJ mg/kg N 0.08 1.3

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2,4‐Dinitrotoluene 0.13 U mg/kg N 0.029 0.13


SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2‐Chloronaphthalene 0.13 U mg/kg N 0.02 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2‐Chlorophenol 0.33 U mg/kg N 0.066 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2‐Methylnaphthalene 0.13 U mg/kg N 0.037 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2‐Methylphenol 0.13 U mg/kg N 0.075 0.13

Page 127 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2‐Nitroaniline 0.33 U mg/kg N 0.029 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 2‐Nitrophenol 0.33 U mg/kg N 0.07 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 3&4‐Methylphenol 0.13 U mg/kg N 0.083 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 3,3‐Dichlorobenzidine 0.33 U mg/kg N 0.017 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 3‐Nitroaniline 0.33 UJ mg/kg N 0.026 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 1.3 U mg/kg N 0.08 1.3

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 4‐Bromophenyl phenyl ether 0.13 U mg/kg N 0.024 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 4‐Chloro‐3‐methylphenol 0.33 U mg/kg N 0.066 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 4‐Chloroaniline 0.33 U mg/kg N 0.021 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 4‐Chlorophenyl phenyl ether 0.13 U mg/kg N 0.02 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC 4‐Nitroaniline 0.33 UJ mg/kg N 0.026 0.33


SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Acenaphthene 0.187 = mg/kg Y 0.019 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Acenaphthylene 0.129 = mg/kg Y 0.021 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Acetophenone 0.33 U mg/kg N 0.012 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Anthracene 0.422 = mg/kg Y 0.023 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Atrazine 0.33 U mg/kg N 0.013 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Benzaldehyde 0.33 U mg/kg N 0.015 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Benzo(a)anthracene 0.49 = mg/kg Y 0.021 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Benzo(a)pyrene 0.49 = mg/kg Y 0.02 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Benzo(b)fluoranthene 0.454 = mg/kg Y 0.022 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Benzo(g,h,i)perylene 0.351 = mg/kg Y 0.024 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Benzo(k)fluoranthene 0.416 = mg/kg Y 0.025 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Bis(2‐chloroethoxy)methane 0.13 U mg/kg N 0.027 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Bis(2‐chloroethyl)ether 0.13 U mg/kg N 0.02 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC bis(2‐Chloroisopropyl)ether 0.13 U mg/kg N 0.02 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Bis(2‐ethylhexyl)phthalate 10.1 = mg/kg Y 0.12 0.26

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Butyl benzyl phthalate 0.13 U mg/kg N 0.038 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Caprolactam 0.13 U mg/kg N 0.021 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Carbazole 0.13 U mg/kg N 0.03 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Chrysene 0.732 = mg/kg Y 0.022 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Dibenz(a,h)anthracene 0.102 = mg/kg Y 0.022 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Dibenzofuran 0.13 U mg/kg N 0.02 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Diethyl phthalate 0.13 U mg/kg N 0.022 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Dimethyl phthalate 0.13 U mg/kg N 0.023 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Di‐n‐butyl phthalate 0.13 U mg/kg N 0.015 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Di‐n‐octyl phthalate 0.13 U mg/kg N 0.032 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Fluoranthene 1.02 = mg/kg Y 0.029 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Fluorene 0.132 = mg/kg Y 0.022 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Hexachlorobenzene 0.13 U mg/kg N 0.021 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Hexachlorobutadiene 0.066 U mg/kg N 0.018 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Hexachlorocyclopentadiene 1.3 UJ mg/kg N 0.067 1.3

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Hexachloroethane 0.33 U mg/kg N 0.018 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.311 = mg/kg Y 0.023 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Isophorone 0.13 U mg/kg N 0.018 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Naphthalene 0.066 U mg/kg N 0.018 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Nitrobenzene 0.13 U mg/kg N 0.019 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 0.13 U mg/kg N 0.016 0.13

Page 128 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC N‐Nitrosodiphenylamine 0.33 U mg/kg N 0.039 0.33

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Pentachlorophenol 0.66 U mg/kg N 0.11 0.66

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Phenanthrene 0.63 = mg/kg Y 0.03 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Phenol 0.13 U mg/kg N 0.069 0.13

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N SVOC Pyrene 1.05 = mg/kg Y 0.025 0.066

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,1,1‐Trichloroethane 1.1 U mg/kg N 0.027 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,1,2,2‐Tetrachloroethane 1.1 U mg/kg N 0.063 1.1


SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 1.1 U mg/kg N 0.12 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,1‐Dichloroethane 1.1 U mg/kg N 0.03 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,1‐Dichloroethene 1.1 U mg/kg N 0.14 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,2,4‐Trichlorobenzene 1.1 U mg/kg N 0.074 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 2.1 U mg/kg N 0.12 2.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,2‐Dibromoethane 0.21 U mg/kg N 0.029 0.21

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,2‐Dichlorobenzene 1.1 U mg/kg N 0.058 1.1


SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,2‐Dichloropropane 1.1 U mg/kg N 0.028 1.1


SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 1,4‐Dichlorobenzene 0.294 J mg/kg Y 0.072 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC 2‐Hexanone 1.1 U mg/kg N 0.21 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Acetone 1.34 J mg/kg Y 0.48 2.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Benzene 0.109 J mg/kg Y 0.073 0.21

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Bromodichloromethane 1.1 U mg/kg N 0.055 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Bromoform 1.1 U mg/kg N 0.032 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Bromomethane 1.1 U mg/kg N 0.087 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Carbon Disulfide 0.194 J mg/kg Y 0.065 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Carbon Tetrachloride 1.1 U mg/kg N 0.12 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Chlorobenzene 0.819 J mg/kg Y 0.073 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Chloroethane 1.1 U mg/kg N 0.21 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Chloroform 1.1 U mg/kg N 0.068 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Chloromethane 1.1 U mg/kg N 0.035 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC cis‐1,2‐Dichloroethene 1.1 U mg/kg N 0.051 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC cis‐1,3‐Dichloropropene 1.1 U mg/kg N 0.029 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Cyclohexane 1.1 U mg/kg N 0.032 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Dibromochloromethane 1.1 U mg/kg N 0.024 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Dichlorodifluoromethane 1.1 U mg/kg N 0.2 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Ethylbenzene 0.21 U mg/kg N 0.08 0.21

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Isopropylbenzene 1.1 U mg/kg N 0.11 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Methyl Acetate 3 = mg/kg Y 0.18 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Methyl ethyl ketone 2.1 U mg/kg N 0.42 2.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Methyl isobutyl ketone 1.1 U mg/kg N 0.17 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Methyl tert‐butyl ether 0.21 U mg/kg N 0.061 0.21

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Methylcyclohexane 0.186 J mg/kg Y 0.14 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Methylene Chloride 1.1 U mg/kg N 0.048 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Styrene 1.1 U mg/kg N 0.023 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Tetrachloroethene 1.1 U mg/kg N 0.031 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Toluene 0.0773 J mg/kg Y 0.063 0.21

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC trans‐1,2‐Dichloroethene 1.1 U mg/kg N 0.096 1.1

Page 129 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC trans‐1,3‐Dichloropropene 1.1 U mg/kg N 0.021 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Trichloroethene 1.1 U mg/kg N 0.11 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Trichlorofluoromethane 1.1 U mg/kg N 0.049 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Vinyl Chloride 1.1 U mg/kg N 0.038 1.1

SD_Grab SD SC‐G.4 062810‐SD‐SC‐G4‐001 6/28/2010 N VOC Xylenes, Total 0.43 U mg/kg N 0.1 0.43

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Aluminum 13000 = mg/kg Y 20 20

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Antimony 2 UJ mg/kg N 2 2

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Arsenic 2 U mg/kg N 2 2

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Barium 87.1 = mg/kg Y 20 20

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Beryllium 0.32 = mg/kg Y 0.2 0.2

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Cadmium 0.51 U mg/kg N 0.51 0.51

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Calcium 1730 J mg/kg Y 510 510

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Chromium 30.2 J mg/Kg Y 1 1

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Cobalt 8.5 = mg/kg Y 5.1 5.1

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Copper 8.4 = mg/kg Y 2.6 2.6

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Iron 11900 J mg/kg Y 10 10

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Lead 5.6 = mg/kg Y 2 2

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Magnesium 2950 J mg/kg Y 510 510

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Manganese 168 J mg/kg Y 1.5 1.5

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Mercury 0.068 = mg/kg Y 0.039 0.039

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Methyl Mercury 0.000009 J mg/kg Y 0.000009 0.00003

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Nickel 17.2 = mg/kg Y 4.1 4.1

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Potassium 1000 U mg/kg N 1000 1000

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Selenium 2 U mg/kg N 2 2

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Silver 0.51 U mg/kg N 0.51 0.51

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Sodium 1000 U mg/kg N 1000 1000

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Thallium 1 U mg/kg N 1 1

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Vanadium 23.1 = mg/kg Y 5.1 5.1

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N Metal Zinc 38.8 J mg/kg Y 2 2










SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N PCB_TOT Total Aroclors 0 U mg/kg N 0.013 0.036

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 1,1'‐Biphenyl 0.07 U mg/kg N 0.004 0.07



SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 2,4‐Dichlorophenol 0.17 U mg/kg N 0.056 0.17

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 2,4‐Dimethylphenol 0.17 U mg/kg N 0.058 0.17

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 2,4‐Dinitrophenol 0.7 U mg/kg N 0.042 0.7



SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 2‐Chloronaphthalene 0.07 U mg/kg N 0.011 0.07

Page 130 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 2‐Chlorophenol 0.17 U mg/kg N 0.035 0.17

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 2‐Methylnaphthalene 0.07 U mg/kg N 0.019 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 2‐Methylphenol 0.07 U mg/kg N 0.04 0.07



SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 3&4‐Methylphenol 0.07 U mg/kg N 0.044 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 3,3‐Dichlorobenzidine 0.17 U mg/kg N 0.0088 0.17


SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 0.7 U mg/kg N 0.042 0.7

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 4‐Bromophenyl phenyl ether 0.07 U mg/kg N 0.013 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 4‐Chloro‐3‐methylphenol 0.17 U mg/kg N 0.035 0.17

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 4‐Chloroaniline 0.17 U mg/kg N 0.011 0.17

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC 4‐Chlorophenyl phenyl ether 0.07 U mg/kg N 0.01 0.07



SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Acenaphthene 0.035 U mg/kg N 0.01 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Acenaphthylene 0.035 U mg/kg N 0.011 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Acetophenone 0.17 U mg/kg N 0.0061 0.17

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Anthracene 0.035 U mg/kg N 0.012 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Atrazine 0.17 U mg/kg N 0.0069 0.17

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Benzaldehyde 0.17 U mg/kg N 0.008 0.17

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Benzo(a)anthracene 0.035 U mg/kg N 0.011 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Benzo(a)pyrene 0.035 U mg/kg N 0.011 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Benzo(b)fluoranthene 0.035 U mg/kg N 0.012 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Benzo(g,h,i)perylene 0.035 U mg/kg N 0.013 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Benzo(k)fluoranthene 0.035 U mg/kg N 0.013 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Bis(2‐chloroethoxy)methane 0.07 U mg/kg N 0.014 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Bis(2‐chloroethyl)ether 0.07 U mg/kg N 0.01 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC bis(2‐Chloroisopropyl)ether 0.07 U mg/kg N 0.01 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.07 U mg/kg N 0.031 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Butyl benzyl phthalate 0.07 U mg/kg N 0.02 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Caprolactam 0.07 U mg/kg N 0.011 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Carbazole 0.07 U mg/kg N 0.016 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Chrysene 0.035 U mg/kg N 0.012 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Dibenz(a,h)anthracene 0.035 U mg/kg N 0.012 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Dibenzofuran 0.07 U mg/kg N 0.01 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Diethyl phthalate 0.07 U mg/kg N 0.012 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Dimethyl phthalate 0.07 U mg/kg N 0.012 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Di‐n‐butyl phthalate 0.07 U mg/kg N 0.0077 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Di‐n‐octyl phthalate 0.07 U mg/kg N 0.017 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Fluoranthene 0.035 U mg/kg N 0.015 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Fluorene 0.035 U mg/kg N 0.011 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Hexachlorobenzene 0.07 U mg/kg N 0.011 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Hexachlorobutadiene 0.035 U mg/kg N 0.0097 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Hexachlorocyclopentadiene 0.7 UJ mg/kg N 0.035 0.7

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Hexachloroethane 0.17 U mg/kg N 0.0097 0.17

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.035 U mg/kg N 0.012 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Isophorone 0.07 U mg/kg N 0.0094 0.07

Page 131 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Naphthalene 0.035 U mg/kg N 0.0095 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Nitrobenzene 0.07 U mg/kg N 0.01 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 0.07 U mg/kg N 0.0085 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC N‐Nitrosodiphenylamine 0.17 U mg/kg N 0.021 0.17

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Pentachlorophenol 0.35 U mg/kg N 0.06 0.35

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Phenanthrene 0.035 U mg/kg N 0.016 0.035

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Phenol 0.07 U mg/kg N 0.037 0.07

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N SVOC Pyrene 0.035 U mg/kg N 0.013 0.035


SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC 1,1,2,2‐Tetrachloroethane 0.0047 U mg/kg N 0.00027 0.0047


SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 0.0047 U mg/kg N 0.00052 0.0047


SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC 1,1‐Dichloroethene 0.0047 U mg/kg N 0.00062 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC 1,2,4‐Trichlorobenzene 0.0047 U mg/kg N 0.00032 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 0.0093 U mg/kg N 0.0005 0.0093

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC 1,2‐Dibromoethane 0.00093 U mg/kg N 0.00013 0.00093

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC 1,2‐Dichlorobenzene 0.0046 J mg/kg Y 0.00025 0.0047


SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC 1,2‐Dichloropropane 0.0047 U mg/kg N 0.00012 0.0047



SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC 2‐Hexanone 0.0047 U mg/kg N 0.0009 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Acetone 0.009 J mg/kg Y 0.0021 0.0093

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Benzene 0.00046 J mg/kg Y 0.00032 0.00093

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Bromodichloromethane 0.0047 U mg/kg N 0.00024 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Bromoform 0.0047 U mg/kg N 0.00014 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Bromomethane 0.0047 U mg/kg N 0.00038 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Carbon Disulfide 0.0076 U mg/kg N 0.00028 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Carbon Tetrachloride 0.0047 U mg/kg N 0.00052 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Chlorobenzene 0.0054 = mg/kg Y 0.00032 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Chloroethane 0.0047 U mg/kg N 0.00093 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Chloroform 0.0047 U mg/kg N 0.0003 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Chloromethane 0.0047 U mg/kg N 0.00015 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC cis‐1,2‐Dichloroethene 0.0047 U mg/kg N 0.00022 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC cis‐1,3‐Dichloropropene 0.0047 U mg/kg N 0.00012 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Cyclohexane 0.0047 U mg/kg N 0.00014 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Dibromochloromethane 0.0047 U mg/kg N 0.0001 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Dichlorodifluoromethane 0.0047 U mg/kg N 0.00088 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Ethylbenzene 0.00093 U mg/kg N 0.00035 0.00093

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Isopropylbenzene 0.0047 U mg/kg N 0.00048 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Methyl Acetate 0.0047 U mg/kg N 0.00077 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Methyl ethyl ketone 0.0093 U mg/kg N 0.0018 0.0093

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Methyl isobutyl ketone 0.0047 U mg/kg N 0.00075 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Methyl tert‐butyl ether 0.00093 U mg/kg N 0.00026 0.00093

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Methylcyclohexane 0.0047 U mg/kg N 0.00061 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Methylene Chloride 0.0047 U mg/kg N 0.00021 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Styrene 0.0047 U mg/kg N 0.0001 0.0047

Page 132 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Tetrachloroethene 0.0047 U mg/kg N 0.00013 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Toluene 0.00058 J mg/kg Y 0.00027 0.00093

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC trans‐1,2‐Dichloroethene 0.0047 U mg/kg N 0.00042 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC trans‐1,3‐Dichloropropene 0.0047 U mg/kg N 0.000089 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Trichloroethene 0.0047 U mg/kg N 0.00049 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Trichlorofluoromethane 0.0047 U mg/kg N 0.00021 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Vinyl Chloride 0.0047 U mg/kg N 0.00017 0.0047

SD_Grab SD SC‐G.5 062810‐SD‐SC‐G5‐001 6/28/2010 N VOC Xylenes, Total 0.0019 U mg/kg N 0.00044 0.0019

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Aluminum 16300 = mg/kg Y 42 42

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Antimony 4.2 U mg/kg N 4.2 4.2

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Arsenic 25 = mg/kg Y 4.2 4.2

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Barium 143 = mg/kg Y 42 42

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Beryllium 0.42 U mg/kg N 0.42 0.42

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Cadmium 1.1 U mg/kg N 1.1 1.1

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Calcium 3390 = mg/kg Y 1100 1100

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Chromium 787 = mg/Kg Y 2.1 2.1

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Cobalt 11 U mg/kg N 11 11

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Copper 59.3 = mg/kg Y 5.3 5.3

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Iron 24200 = mg/kg Y 21 21

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Lead 130 = mg/kg Y 4.2 4.2

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Magnesium 5460 = mg/kg Y 1100 1100

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Manganese 793 = mg/kg Y 3.2 3.2

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Mercury 29 = mg/kg Y 3.3 3.3

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Nickel 23.1 = mg/kg Y 8.4 8.4

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Potassium 3890 = mg/kg Y 2100 2100

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Selenium 4.2 U mg/kg N 4.2 4.2

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Silver 1.1 U mg/kg N 1.1 1.1

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Sodium 3250 = mg/kg Y 2100 2100

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Thallium 2.1 U mg/kg N 2.1 2.1

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Vanadium 61.6 = mg/kg Y 11 11

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N Metal Zinc 103 = mg/kg Y 4.2 4.2

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N PCB Aroclor‐1016 0.063 U mg/kg N 0.023 0.063




SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N PCB Aroclor‐1248 1.26 = mg/kg Y 0.013 0.063





SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N PCB_TOT Total Aroclors 1.895 = mg/kg Y 0.023 0.063

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 1,1'‐Biphenyl 0.12 U mg/kg N 0.0071 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2,4,5‐Trichlorophenol 0.31 U mg/kg N 0.071 0.31


SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2,4‐Dichlorophenol 0.31 U mg/kg N 0.099 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2,4‐Dimethylphenol 0.31 U mg/kg N 0.1 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2,4‐Dinitrophenol 1.2 U mg/kg N 0.075 1.2

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2,4‐Dinitrotoluene 0.12 U mg/kg N 0.027 0.12

Page 133 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2‐Chloronaphthalene 0.12 U mg/kg N 0.019 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2‐Chlorophenol 0.31 U mg/kg N 0.062 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2‐Methylnaphthalene 0.12 U mg/kg N 0.034 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2‐Methylphenol 0.12 U mg/kg N 0.07 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2‐Nitroaniline 0.31 U mg/kg N 0.027 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 2‐Nitrophenol 0.31 U mg/kg N 0.065 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 3&4‐Methylphenol 0.12 U mg/kg N 0.078 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 3,3‐Dichlorobenzidine 0.31 U mg/kg N 0.016 0.31


SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 1.2 U mg/kg N 0.075 1.2

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 4‐Bromophenyl phenyl ether 0.12 U mg/kg N 0.022 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 4‐Chloro‐3‐methylphenol 0.31 U mg/kg N 0.061 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 4‐Chloroaniline 0.31 U mg/kg N 0.02 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC 4‐Chlorophenyl phenyl ether 0.12 U mg/kg N 0.018 0.12



SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Acenaphthene 0.061 U mg/kg N 0.018 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Acenaphthylene 0.061 U mg/kg N 0.02 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Acetophenone 0.31 U mg/kg N 0.011 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Anthracene 0.0223 J mg/kg Y 0.022 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Atrazine 0.31 U mg/kg N 0.012 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Benzaldehyde 0.31 U mg/kg N 0.014 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Benzo(a)anthracene 0.072 = mg/kg Y 0.02 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Benzo(a)pyrene 0.0833 = mg/kg Y 0.019 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Benzo(b)fluoranthene 0.0484 J mg/kg Y 0.021 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Benzo(g,h,i)perylene 0.0656 = mg/kg Y 0.023 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Benzo(k)fluoranthene 0.0532 J mg/kg Y 0.023 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Bis(2‐chloroethoxy)methane 0.12 U mg/kg N 0.025 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Bis(2‐chloroethyl)ether 0.12 U mg/kg N 0.018 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC bis(2‐Chloroisopropyl)ether 0.12 U mg/kg N 0.018 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.0792 J mg/kg Y 0.054 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Butyl benzyl phthalate 0.12 U mg/kg N 0.036 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Caprolactam 0.12 U mg/kg N 0.019 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Carbazole 0.12 U mg/kg N 0.028 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Chrysene 0.0966 = mg/kg Y 0.021 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Dibenz(a,h)anthracene 0.061 U mg/kg N 0.021 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Dibenzofuran 0.12 U mg/kg N 0.018 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Diethyl phthalate 0.12 U mg/kg N 0.021 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Dimethyl phthalate 0.12 U mg/kg N 0.022 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Di‐n‐butyl phthalate 0.12 U mg/kg N 0.014 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Di‐n‐octyl phthalate 0.12 U mg/kg N 0.03 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Fluoranthene 0.134 = mg/kg Y 0.027 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Fluorene 0.061 U mg/kg N 0.02 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Hexachlorobenzene 0.12 U mg/kg N 0.02 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Hexachlorobutadiene 0.061 U mg/kg N 0.017 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Hexachlorocyclopentadiene 1.2 UJ mg/kg N 0.063 1.2

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Hexachloroethane 0.31 U mg/kg N 0.017 0.31

Page 134 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.0495 J mg/kg Y 0.021 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Isophorone 0.12 U mg/kg N 0.017 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Naphthalene 0.061 U mg/kg N 0.017 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Nitrobenzene 0.12 U mg/kg N 0.018 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 0.12 U mg/kg N 0.015 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC N‐Nitrosodiphenylamine 0.31 U mg/kg N 0.037 0.31

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Pentachlorophenol 0.61 U mg/kg N 0.11 0.61

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Phenanthrene 0.0813 = mg/kg Y 0.028 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Phenol 0.12 U mg/kg N 0.065 0.12

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N SVOC Pyrene 0.153 = mg/kg Y 0.024 0.061

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 1,1,1‐Trichloroethane 0.014 U mg/kg N 0.00036 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 1,1,2,2‐Tetrachloroethane 0.014 U mg/kg N 0.00083 0.014


SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 0.014 U mg/kg N 0.0016 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 1,1‐Dichloroethane 0.014 U mg/kg N 0.00039 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 1,1‐Dichloroethene 0.014 U mg/kg N 0.0019 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 1,2,4‐Trichlorobenzene 0.014 U mg/kg N 0.00098 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 0.028 U mg/kg N 0.0015 0.028

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 1,2‐Dibromoethane 0.0028 U mg/kg N 0.00039 0.0028

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 1,2‐Dichlorobenzene 0.014 U mg/kg N 0.00076 0.014


SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 1,2‐Dichloropropane 0.014 U mg/kg N 0.00037 0.014



SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC 2‐Hexanone 0.014 U mg/kg N 0.0027 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Acetone 0.028 U mg/kg N 0.0063 0.028

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Benzene 0.0028 U mg/kg N 0.00096 0.0028

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Bromodichloromethane 0.014 U mg/kg N 0.00073 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Bromoform 0.014 U mg/kg N 0.00043 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Bromomethane 0.014 U mg/kg N 0.0011 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Carbon Disulfide 0.014 UJ mg/kg N 0.00086 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Carbon Tetrachloride 0.014 U mg/kg N 0.0016 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Chlorobenzene 0.014 U mg/kg N 0.00096 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Chloroethane 0.014 U mg/kg N 0.0028 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Chloroform 0.014 U mg/kg N 0.0009 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Chloromethane 0.014 U mg/kg N 0.00047 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC cis‐1,2‐Dichloroethene 0.014 U mg/kg N 0.00068 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC cis‐1,3‐Dichloropropene 0.014 U mg/kg N 0.00038 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Cyclohexane 0.014 UJ mg/kg N 0.00043 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Dibromochloromethane 0.014 U mg/kg N 0.00031 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Dichlorodifluoromethane 0.014 U mg/kg N 0.0027 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Ethylbenzene 0.0028 U mg/kg N 0.001 0.0028

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Isopropylbenzene 0.014 U mg/kg N 0.0015 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Methyl Acetate 0.014 U mg/kg N 0.0023 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Methyl ethyl ketone 0.028 U mg/kg N 0.0056 0.028

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Methyl isobutyl ketone 0.014 U mg/kg N 0.0023 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Methyl tert‐butyl ether 0.0028 U mg/kg N 0.0008 0.0028

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Methylcyclohexane 0.014 U mg/kg N 0.0019 0.014

Page 135 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Methylene Chloride 0.014 U mg/kg N 0.00063 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Styrene 0.014 U mg/kg N 0.0003 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Tetrachloroethene 0.014 U mg/kg N 0.00041 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Toluene 0.0028 U mg/kg N 0.00083 0.0028

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC trans‐1,2‐Dichloroethene 0.014 U mg/kg N 0.0013 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC trans‐1,3‐Dichloropropene 0.014 U mg/kg N 0.00027 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Trichloroethene 0.014 U mg/kg N 0.0015 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Trichlorofluoromethane 0.014 U mg/kg N 0.00065 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Vinyl Chloride 0.014 U mg/kg N 0.0005 0.014

SD_Grab SD WC‐A.3 062210‐SD‐WC‐A3‐001 6/22/2010 N VOC Xylenes, Total 0.0057 U mg/kg N 0.0013 0.0057

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Aluminum 15300 = mg/kg Y 89 89

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Antimony 8.9 U mg/kg N 8.9 8.9

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Arsenic 26.4 = mg/kg Y 8.9 8.9

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Barium 284 = mg/kg Y 89 89

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Beryllium 0.89 U mg/kg N 0.89 0.89

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Cadmium 2.2 U mg/kg N 2.2 2.2

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Calcium 4120 = mg/kg Y 2200 2200

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Chromium 1740 = mg/Kg Y 4.4 4.4

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Cobalt 22 U mg/kg N 22 22

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Copper 149 = mg/kg Y 11 11

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Iron 22900 = mg/kg Y 44 44

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Lead 195 = mg/kg Y 8.9 8.9

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Magnesium 6180 = mg/kg Y 2200 2200

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Manganese 2010 = mg/kg Y 6.7 6.7

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Mercury 30.3 = mg/kg Y 3 3

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Nickel 83.3 = mg/kg Y 18 18

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Potassium 4400 U mg/kg N 4400 4400

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Selenium 8.9 U mg/kg N 8.9 8.9

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Silver 2.8 = mg/kg Y 2.2 2.2

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Sodium 5860 = mg/kg Y 4400 4400

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Thallium 4.4 U mg/kg N 4.4 4.4

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Vanadium 62.2 = mg/kg Y 22 22

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N Metal Zinc 318 = mg/kg Y 8.9 8.9










SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N PCB_TOT Total Aroclors 5.57 = mg/kg Y 0.047 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 1,1'‐Biphenyl 0.26 U mg/kg N 0.015 0.26



SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 2,4‐Dichlorophenol 0.65 U mg/kg N 0.21 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 2,4‐Dimethylphenol 0.65 U mg/kg N 0.22 0.65

Page 136 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 2,4‐Dinitrophenol 2.6 U mg/kg N 0.16 2.6



SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 2‐Chloronaphthalene 0.26 U mg/kg N 0.04 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 2‐Chlorophenol 0.65 U mg/kg N 0.13 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 2‐Methylnaphthalene 0.26 U mg/kg N 0.072 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 2‐Methylphenol 0.26 U mg/kg N 0.15 0.26



SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 3&4‐Methylphenol 0.26 U mg/kg N 0.16 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 3,3‐Dichlorobenzidine 0.65 U mg/kg N 0.033 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 3‐Nitroaniline 0.65 UJ mg/kg N 0.052 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 2.6 U mg/kg N 0.16 2.6

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 4‐Bromophenyl phenyl ether 0.26 U mg/kg N 0.047 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 4‐Chloro‐3‐methylphenol 0.65 U mg/kg N 0.13 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 4‐Chloroaniline 0.65 U mg/kg N 0.041 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC 4‐Chlorophenyl phenyl ether 0.26 U mg/kg N 0.039 0.26



SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Acenaphthene 0.13 U mg/kg N 0.037 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Acenaphthylene 0.13 U mg/kg N 0.041 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Acetophenone 0.65 U mg/kg N 0.023 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Anthracene 0.13 U mg/kg N 0.045 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Atrazine 0.65 U mg/kg N 0.025 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Benzaldehyde 0.65 U mg/kg N 0.03 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Benzo(a)anthracene 0.107 J mg/kg Y 0.042 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Benzo(a)pyrene 0.158 = mg/kg Y 0.039 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Benzo(b)fluoranthene 0.138 = mg/kg Y 0.043 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Benzo(g,h,i)perylene 0.137 = mg/kg Y 0.048 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Benzo(k)fluoranthene 0.128 J mg/kg Y 0.049 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Bis(2‐chloroethoxy)methane 0.26 U mg/kg N 0.052 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Bis(2‐chloroethyl)ether 0.26 U mg/kg N 0.039 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC bis(2‐Chloroisopropyl)ether 0.26 U mg/kg N 0.038 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.309 = mg/kg Y 0.11 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Butyl benzyl phthalate 0.26 U mg/kg N 0.075 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Caprolactam 0.26 U mg/kg N 0.041 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Carbazole 0.26 U mg/kg N 0.06 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Chrysene 0.153 = mg/kg Y 0.044 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Dibenz(a,h)anthracene 0.13 U mg/kg N 0.044 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Dibenzofuran 0.26 U mg/kg N 0.038 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Diethyl phthalate 0.26 U mg/kg N 0.044 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Dimethyl phthalate 0.26 U mg/kg N 0.046 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Di‐n‐butyl phthalate 0.26 U mg/kg N 0.029 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Di‐n‐octyl phthalate 0.26 U mg/kg N 0.063 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Fluoranthene 0.192 = mg/kg Y 0.057 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Fluorene 0.13 U mg/kg N 0.042 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Hexachlorobenzene 0.26 U mg/kg N 0.042 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Hexachlorobutadiene 0.13 U mg/kg N 0.036 0.13

Page 137 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Hexachlorocyclopentadiene 2.6 UJ mg/kg N 0.13 2.6

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Hexachloroethane 0.65 U mg/kg N 0.036 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.0959 J mg/kg Y 0.045 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Isophorone 0.26 U mg/kg N 0.035 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Naphthalene 0.13 U mg/kg N 0.035 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Nitrobenzene 0.26 U mg/kg N 0.037 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 0.26 U mg/kg N 0.032 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC N‐Nitrosodiphenylamine 0.65 U mg/kg N 0.077 0.65

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Pentachlorophenol 1.3 U mg/kg N 0.22 1.3

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Phenanthrene 0.0826 J mg/kg Y 0.059 0.13

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Phenol 0.26 U mg/kg N 0.14 0.26

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N SVOC Pyrene 0.192 = mg/kg Y 0.05 0.13


SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC 1,1,2,2‐Tetrachloroethane 0.034 U mg/kg N 0.002 0.034


SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 0.034 U mg/kg N 0.0039 0.034


SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC 1,1‐Dichloroethene 0.034 U mg/kg N 0.0045 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC 1,2,4‐Trichlorobenzene 0.034 U mg/kg N 0.0024 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 0.069 U mg/kg N 0.0037 0.069

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC 1,2‐Dibromoethane 0.0069 U mg/kg N 0.00094 0.0069

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC 1,2‐Dichlorobenzene 0.0048 J mg/kg Y 0.0019 0.034


SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC 1,2‐Dichloropropane 0.034 U mg/kg N 0.00089 0.034



SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC 2‐Hexanone 0.034 U mg/kg N 0.0066 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Acetone 0.159 = mg/kg Y 0.015 0.069

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Benzene 0.0069 U mg/kg N 0.0023 0.0069

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Bromodichloromethane 0.034 U mg/kg N 0.0018 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Bromoform 0.034 U mg/kg N 0.001 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Bromomethane 0.034 U mg/kg N 0.0028 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Carbon Disulfide 0.0113 J mg/kg Y 0.0021 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Carbon Tetrachloride 0.034 U mg/kg N 0.0038 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Chlorobenzene 0.034 U mg/kg N 0.0023 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Chloroethane 0.034 U mg/kg N 0.0069 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Chloroform 0.034 U mg/kg N 0.0022 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Chloromethane 0.034 U mg/kg N 0.0011 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC cis‐1,2‐Dichloroethene 0.034 U mg/kg N 0.0016 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC cis‐1,3‐Dichloropropene 0.034 U mg/kg N 0.00091 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Cyclohexane 0.034 UJ mg/kg N 0.001 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Dibromochloromethane 0.034 U mg/kg N 0.00075 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Dichlorodifluoromethane 0.034 U mg/kg N 0.0065 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Ethylbenzene 0.0069 U mg/kg N 0.0025 0.0069

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Isopropylbenzene 0.034 U mg/kg N 0.0036 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Methyl Acetate 0.034 U mg/kg N 0.0056 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Methyl ethyl ketone 0.069 U mg/kg N 0.014 0.069

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Methyl isobutyl ketone 0.034 U mg/kg N 0.0056 0.034

Page 138 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Methyl tert‐butyl ether 0.0069 U mg/kg N 0.0019 0.0069

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Methylcyclohexane 0.034 U mg/kg N 0.0045 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Methylene Chloride 0.034 U mg/kg N 0.0015 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Styrene 0.034 U mg/kg N 0.00073 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Tetrachloroethene 0.034 U mg/kg N 0.00099 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Toluene 0.0069 U mg/kg N 0.002 0.0069

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC trans‐1,2‐Dichloroethene 0.034 U mg/kg N 0.0031 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC trans‐1,3‐Dichloropropene 0.034 U mg/kg N 0.00066 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Trichloroethene 0.034 U mg/kg N 0.0036 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Trichlorofluoromethane 0.034 U mg/kg N 0.0016 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Vinyl Chloride 0.034 U mg/kg N 0.0012 0.034

SD_Grab SD WC‐A.4 062210‐SD‐WC‐A4‐001 6/22/2010 N VOC Xylenes, Total 0.014 U mg/kg N 0.0032 0.014

SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB Aroclor‐1016 0.34 U mg/kg N 0.065 0.34




SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB Aroclor‐1248 1.34 = mg/kg Y 0.12 0.34



SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB Congener 2,3,7,8‐TCDD TEQ 5.35E‐05 = mg/kg Y

SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB Congener PCB‐1 0.000308 = mg/kg Y 0 0.0000156



SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB Congener PCB‐104 3.31E‐05 = mg/kg Y 0 0.0000156


SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB Congener PCB‐106/118 0.0917 = mg/kg Y 0 0.0000156











SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB Congener PCB‐121 1.56E‐05 U mg/kg N 0 0.0000156












Page 139 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit





SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB Congener PCB‐138/163/164 0.041 = mg/kg Y 0 0.0000156

























SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB Congener PCB‐169 7.06E‐06 J mg/kg Y 0 0.0000156



















Page 140 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit












































SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB Congener PCB‐41/64/71/72 0.103 = mg/kg Y 0 0.0000156





Page 141 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit













































SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB_TOT Total Aroclors 1.34 = mg/kg Y 0.065 0.34

SD_Grab SD WC‐B.1 071806‐WC‐MAR‐0B1‐0001 7/18/2006 N PCB_TOT Total PCBs 2.677517 = mg/kg Y



Page 142 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SD_Grab SD WC‐B.2 071906‐WC‐MAR‐0B2‐0001 7/19/2006 N PCB Aroclor‐1248 3.16 = mg/kg Y 0.068 0.2



SD_Grab SD WC‐B.2 071906‐WC‐MAR‐0B2‐0001 7/19/2006 N PCB Congener 2,3,7,8‐TCDD TEQ 0.000397 = mg/kg Y











































Page 143 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















































Page 144 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐B.2 071906‐WC‐MAR‐0B2‐0001 7/19/2006 N PCB Congener PCB‐2 0.000208 = mg/kg Y 0 0.0000156SD_Grab SD WC‐B.2 071906‐WC‐MAR‐0B2‐0001 7/19/2006 N PCB Congener PCB‐20/21/33 0.0596 = mg/kg Y 0 0.0000156




























SD_Grab SD WC‐B.2 071906‐WC‐MAR‐0B2‐0001 7/19/2006 N PCB Congener PCB‐41/64/71/72 0.51 = mg/kg Y 0 0.0000156



















Page 145 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit































SD_Grab SD WC‐B.2 071906‐WC‐MAR‐0B2‐0001 7/19/2006 N PCB_TOT Total Aroclors 3.16 = mg/kg Y 0.037 0.2

SD_Grab SD WC‐B.2 071906‐WC‐MAR‐0B2‐0001 7/19/2006 N PCB_TOT Total PCBs 16.43355 = mg/kg Y

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Aluminum 12800 = mg/kg Y 130 130

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Antimony 13 U mg/kg N 13 13

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Arsenic 21.7 = mg/kg Y 13 13

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Barium 130 U mg/kg N 130 130

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Beryllium 1.3 U mg/kg N 1.3 1.3

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Cadmium 5.1 = mg/kg Y 3.2 3.2

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Calcium 5730 = mg/kg Y 3200 3200

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Chromium 577 = mg/Kg Y 6.5 6.5

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Cobalt 32 U mg/kg N 32 32

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Copper 192 = mg/kg Y 16 16

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Iron 10300 = mg/kg Y 65 65

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Lead 385 = mg/kg Y 13 13

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Magnesium 5690 = mg/kg Y 3200 3200

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Manganese 149 = mg/kg Y 9.7 9.7

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Mercury 24.3 = mg/kg Y 4.2 4.2

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Nickel 59.5 = mg/kg Y 26 26

Page 146 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Potassium 6500 U mg/kg N 6500 6500

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Selenium 13 U mg/kg N 13 13

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Silver 3.2 U mg/kg N 3.2 3.2

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Sodium 10000 = mg/kg Y 6500 6500

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Thallium 6.5 U mg/kg N 6.5 6.5

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Vanadium 71.7 = mg/kg Y 32 32

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N Metal Zinc 386 = mg/kg Y 13 13

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N PCB Aroclor‐1016 0.18 U mg/kg N 0.066 0.18




SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N PCB Aroclor‐1248 0.937 = mg/kg Y 0.036 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N PCB Aroclor‐1254 0.395 J mg/kg Y 0.046 0.18




SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N PCB_TOT Total Aroclors 1.332 = mg/kg Y 0.066 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 1,1'‐Biphenyl 0.36 U mg/kg N 0.021 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2,4,5‐Trichlorophenol 0.89 U mg/kg N 0.21 0.89


SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2,4‐Dichlorophenol 0.89 U mg/kg N 0.29 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2,4‐Dimethylphenol 0.89 U mg/kg N 0.3 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2,4‐Dinitrophenol 3.6 U mg/kg N 0.22 3.6

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2,4‐Dinitrotoluene 0.36 U mg/kg N 0.078 0.36


SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2‐Chloronaphthalene 0.36 U mg/kg N 0.055 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2‐Chlorophenol 0.89 U mg/kg N 0.18 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2‐Methylnaphthalene 0.36 U mg/kg N 0.1 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2‐Methylphenol 0.36 U mg/kg N 0.2 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2‐Nitroaniline 0.89 U mg/kg N 0.079 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 2‐Nitrophenol 0.89 U mg/kg N 0.19 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 3&4‐Methylphenol 0.36 U mg/kg N 0.23 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 3,3‐Dichlorobenzidine 0.89 U mg/kg N 0.045 0.89


SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 3.6 U mg/kg N 0.22 3.6

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 4‐Bromophenyl phenyl ether 0.36 U mg/kg N 0.065 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 4‐Chloro‐3‐methylphenol 0.89 U mg/kg N 0.18 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 4‐Chloroaniline 0.89 U mg/kg N 0.057 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC 4‐Chlorophenyl phenyl ether 0.36 U mg/kg N 0.054 0.36



SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Acenaphthene 0.18 U mg/kg N 0.052 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Acenaphthylene 0.18 U mg/kg N 0.057 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Acetophenone 0.89 U mg/kg N 0.031 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Anthracene 0.18 U mg/kg N 0.063 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Atrazine 0.89 U mg/kg N 0.035 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Benzaldehyde 0.89 U mg/kg N 0.041 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Benzo(a)anthracene 0.0886 J mg/kg Y 0.058 0.18

Page 147 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Benzo(a)pyrene 0.103 J mg/kg Y 0.054 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Benzo(b)fluoranthene 0.0663 J mg/kg Y 0.06 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Benzo(g,h,i)perylene 0.0807 J mg/kg Y 0.066 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Benzo(k)fluoranthene 0.096 J mg/kg Y 0.067 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Bis(2‐chloroethoxy)methane 0.36 U mg/kg N 0.072 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Bis(2‐chloroethyl)ether 0.36 U mg/kg N 0.054 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC bis(2‐Chloroisopropyl)ether 0.36 U mg/kg N 0.053 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.36 U mg/kg N 0.16 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Butyl benzyl phthalate 0.36 U mg/kg N 0.1 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Caprolactam 0.36 U mg/kg N 0.056 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Carbazole 0.36 U mg/kg N 0.083 0.36SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Chrysene 0.119 J mg/kg Y 0.06 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Dibenz(a,h)anthracene 0.18 U mg/kg N 0.061 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Dibenzofuran 0.36 U mg/kg N 0.053 0.36SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Diethyl phthalate 0.36 U mg/kg N 0.061 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Dimethyl phthalate 0.36 U mg/kg N 0.063 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Di‐n‐butyl phthalate 0.36 U mg/kg N 0.04 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Di‐n‐octyl phthalate 0.36 U mg/kg N 0.087 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Fluoranthene 0.17 J mg/kg Y 0.079 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Fluorene 0.18 U mg/kg N 0.059 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Hexachlorobenzene 0.36 U mg/kg N 0.058 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Hexachlorobutadiene 0.18 U mg/kg N 0.05 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Hexachlorocyclopentadiene 3.6 UJ mg/kg N 0.18 3.6

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Hexachloroethane 0.89 U mg/kg N 0.05 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.0779 J mg/kg Y 0.062 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Isophorone 0.36 U mg/kg N 0.048 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Naphthalene 0.18 U mg/kg N 0.049 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Nitrobenzene 0.36 U mg/kg N 0.052 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 0.36 U mg/kg N 0.044 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC N‐Nitrosodiphenylamine 0.89 U mg/kg N 0.11 0.89

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Pentachlorophenol 1.8 U mg/kg N 0.31 1.8

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Phenanthrene 0.095 J mg/kg Y 0.081 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Phenol 0.36 U mg/kg N 0.19 0.36

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N SVOC Pyrene 0.163 J mg/kg Y 0.069 0.18

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 1,1,1‐Trichloroethane 0.046 U mg/kg N 0.0012 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 1,1,2,2‐Tetrachloroethane 0.046 U mg/kg N 0.0027 0.046


SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 0.046 U mg/kg N 0.0052 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 1,1‐Dichloroethane 0.046 U mg/kg N 0.0013 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 1,1‐Dichloroethene 0.046 U mg/kg N 0.0061 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 1,2,4‐Trichlorobenzene 0.046 U mg/kg N 0.0032 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 0.092 U mg/kg N 0.005 0.092

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 1,2‐Dibromoethane 0.0092 U mg/kg N 0.0013 0.0092

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 1,2‐Dichlorobenzene 0.046 U mg/kg N 0.0025 0.046


SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 1,2‐Dichloropropane 0.046 U mg/kg N 0.0012 0.046



Page 148 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC 2‐Hexanone 0.046 U mg/kg N 0.0089 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Acetone 0.24 = mg/kg Y 0.021 0.092

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Benzene 0.0092 U mg/kg N 0.0032 0.0092

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Bromodichloromethane 0.046 U mg/kg N 0.0024 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Bromoform 0.046 U mg/kg N 0.0014 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Bromomethane 0.046 U mg/kg N 0.0037 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Carbon Disulfide 0.017 J mg/kg Y 0.0028 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Carbon Tetrachloride 0.046 U mg/kg N 0.0051 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Chlorobenzene 0.046 U mg/kg N 0.0031 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Chloroethane 0.046 U mg/kg N 0.0092 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Chloroform 0.046 U mg/kg N 0.0029 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Chloromethane 0.046 U mg/kg N 0.0015 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC cis‐1,2‐Dichloroethene 0.046 U mg/kg N 0.0022 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC cis‐1,3‐Dichloropropene 0.046 U mg/kg N 0.0012 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Cyclohexane 0.046 U mg/kg N 0.0014 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Dibromochloromethane 0.046 U mg/kg N 0.001 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Dichlorodifluoromethane 0.046 U mg/kg N 0.0087 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Ethylbenzene 0.0092 U mg/kg N 0.0034 0.0092

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Isopropylbenzene 0.046 U mg/kg N 0.0048 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Methyl Acetate 0.046 U mg/kg N 0.0076 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Methyl ethyl ketone 0.092 U mg/kg N 0.018 0.092

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Methyl isobutyl ketone 0.046 U mg/kg N 0.0075 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Methyl tert‐butyl ether 0.0092 U mg/kg N 0.0026 0.0092

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Methylcyclohexane 0.046 U mg/kg N 0.006 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Methylene Chloride 0.046 U mg/kg N 0.0021 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Styrene 0.046 U mg/kg N 0.00099 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Tetrachloroethene 0.046 U mg/kg N 0.0013 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Toluene 0.0187 = mg/kg Y 0.0027 0.0092

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC trans‐1,2‐Dichloroethene 0.046 U mg/kg N 0.0042 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC trans‐1,3‐Dichloropropene 0.046 U mg/kg N 0.00089 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Trichloroethene 0.046 U mg/kg N 0.0049 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Trichlorofluoromethane 0.046 U mg/kg N 0.0021 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Vinyl Chloride 0.046 U mg/kg N 0.0016 0.046

SD_Grab SD WC‐B.5 062210‐SD‐WC‐B5‐001 6/22/2010 N VOC Xylenes, Total 0.018 U mg/kg N 0.0043 0.018


SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N Metal Antimony 144 = mg/kg Y 6.4 6.4

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N Metal Arsenic 36.8 = mg/kg Y 6.4 6.4

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N Metal Barium 711 = mg/kg Y 64 64





SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N Metal Cobalt 77 = mg/kg Y 16 16






Page 149 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N Metal Nickel 208 = mg/kg Y 13 13


SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N Metal Selenium 7.9 = mg/kg Y 6.4 6.4

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N Metal Silver 4.7 = mg/kg Y 1.6 1.6










































SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Anthracene 0.0455 J mg/kg Y 0.032 0.091


Page 150 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Benzaldehyde 0.225 J mg/kg Y 0.021 0.46

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Benzo(a)anthracene 0.197 = mg/kg Y 0.03 0.091

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Benzo(a)pyrene 0.185 = mg/kg Y 0.028 0.091

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Benzo(b)fluoranthene 0.121 = mg/kg Y 0.03 0.091

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Benzo(g,h,i)perylene 0.171 = mg/kg Y 0.034 0.091

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Benzo(k)fluoranthene 0.175 = mg/kg Y 0.034 0.091




SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.699 = mg/kg Y 0.081 0.18



SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Carbazole 0.18 U mg/kg N 0.042 0.18

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Chrysene 0.234 = mg/kg Y 0.031 0.091

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Dibenz(a,h)anthracene 0.0664 J mg/kg Y 0.031 0.091

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Dibenzofuran 0.18 U mg/kg N 0.027 0.18

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Diethyl phthalate 0.18 U mg/kg N 0.031 0.18


SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Di‐n‐butyl phthalate 0.948 = mg/kg Y 0.02 0.18


SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Fluoranthene 0.302 = mg/kg Y 0.04 0.091




SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Hexachlorocyclopentadiene 1.8 U mg/kg N 0.093 1.8


SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.142 = mg/kg Y 0.032 0.091







SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Phenanthrene 0.15 = mg/kg Y 0.042 0.091

SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Phenol 0.18 U mg/kg N 0.096 0.18SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N SVOC Pyrene 0.369 = mg/kg Y 0.035 0.091







SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N VOC 1,2,4‐Trichlorobenzene 0.029 U mg/kg N 0.002 0.029SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 0.057 U mg/kg N 0.0031 0.057





Page 151 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N VOC Acetone 0.057 U mg/kg N 0.013 0.057





SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N VOC Carbon Disulfide 0.029 U mg/kg N 0.0017 0.029





















SD_Grab SD WC‐B.6 062110‐SD‐WC‐B6‐001 6/21/2010 N VOC Toluene 0.0057 U mg/kg N 0.0017 0.0057








SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Antimony 8.6 U mg/kg N 8.6 8.6

SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Arsenic 60.1 = mg/kg Y 8.6 8.6

SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Barium 808 = mg/kg Y 86 86

SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Beryllium 1.2 = mg/kg Y 0.86 0.86




SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Cobalt 30.6 = mg/kg Y 22 22



SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Lead 317 = mg/kg Y 8.6 8.6

Page 152 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Nickel 92.5 = mg/kg Y 17 17

SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Potassium 4330 = mg/kg Y 4300 4300

SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Selenium 8.6 U mg/kg N 8.6 8.6




SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Vanadium 131 = mg/kg Y 22 22

SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N Metal Zinc 615 = mg/kg Y 8.6 8.6






































Page 153 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit












SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.174 J mg/kg Y 0.11 0.25




SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N SVOC Chrysene 0.083 J mg/kg Y 0.042 0.12











SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N SVOC Hexachlorocyclopentadiene 2.5 UJ mg/kg N 0.13 2.5


SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.12 U mg/kg N 0.043 0.12







SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N SVOC Phenanthrene 0.12 U mg/kg N 0.057 0.12


SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N SVOC Pyrene 0.127 = mg/kg Y 0.048 0.12











Page 154 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit











SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N VOC Carbon Disulfide 0.031 UJ mg/kg N 0.0019 0.031





SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N VOC Chloromethane 0.031 U mg/kg N 0.001 0.031SD_Grab SD WC‐B.7 062210‐SD‐WC‐B7‐001 6/22/2010 N VOC cis‐1,2‐Dichloroethene 0.031 U mg/kg N 0.0015 0.031























SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N Metal Antimony 11 U mg/kg N 11 11

SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N Metal Arsenic 22.5 = mg/kg Y 11 11SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N Metal Barium 148 = mg/kg Y 110 110


SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N Metal Cadmium 2.7 U mg/kg N 2.7 2.7



SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N Metal Cobalt 27 U mg/kg N 27 27


Page 155 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N Metal Manganese 580 = mg/kg Y 8 8


SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N Metal Nickel 41 = mg/kg Y 21 21


SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N Metal Selenium 11 U mg/kg N 11 11





















SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N SVOC 2,4‐Dinitrophenol 3 U mg/kg N 0.18 3












SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 3 U mg/kg N 0.18 3








Page 156 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit














SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.21 J mg/kg Y 0.13 0.3




SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N SVOC Chrysene 0.139 J mg/kg Y 0.051 0.15











SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N SVOC Hexachlorocyclopentadiene 3 UJ mg/kg N 0.15 3


SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.0898 J mg/kg Y 0.052 0.15

SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N SVOC Isophorone 0.0613 J mg/kg Y 0.04 0.3






SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N SVOC Phenanthrene 0.0824 J mg/kg Y 0.068 0.15


SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N SVOC Pyrene 0.165 = mg/kg Y 0.058 0.15









Page 157 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit













SD_Grab SD WC‐B.8 062210‐SD‐WC‐B8‐001 6/22/2010 N VOC Carbon Disulfide 0.051 UJ mg/kg N 0.0031 0.051




























SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Aluminum 18000 = mg/kg Y 76 76

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Antimony 7.6 U mg/kg N 7.6 7.6

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Arsenic 19 = mg/kg Y 7.6 7.6

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Barium 235 = mg/kg Y 76 76

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Beryllium 0.83 = mg/kg Y 0.76 0.76

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Cadmium 3.2 = mg/kg Y 1.9 1.9

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Calcium 4740 = mg/kg Y 1900 1900

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Chromium 803 = mg/Kg Y 3.8 3.8

Page 158 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Cobalt 25.7 = mg/kg Y 19 19

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Copper 181 = mg/kg Y 9.6 9.6

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Iron 29800 = mg/kg Y 38 38

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Lead 218 = mg/kg Y 7.6 7.6

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Magnesium 7270 = mg/kg Y 1900 1900

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Manganese 4340 = mg/kg Y 5.7 5.7

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Mercury 16.4 = mg/kg Y 1.2 1.2

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Methyl Mercury 0.000934 = mg/kg Y 0.000159 0.000496

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Nickel 94 = mg/kg Y 15 15

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Potassium 3800 U mg/kg N 3800 3800

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Selenium 7.6 U mg/kg N 7.6 7.6

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Silver 4.3 = mg/kg Y 1.9 1.9

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Sodium 7280 = mg/kg Y 3800 3800SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Thallium 3.8 U mg/kg N 3.8 3.8

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Vanadium 62.9 = mg/kg Y 19 19

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N Metal Zinc 565 = mg/kg Y 7.6 7.6SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N PCB Aroclor‐1016 0.11 U mg/kg N 0.038 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N PCB Aroclor‐1221 0.11 U mg/kg N 0.071 0.11



SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N PCB Aroclor‐1248 3.51 = mg/kg Y 0.021 0.11





SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N PCB_TOT Total Aroclors 3.51 = mg/kg Y 0.038 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 1,1'‐Biphenyl 0.22 U mg/kg N 0.013 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2,4,5‐Trichlorophenol 0.55 U mg/kg N 0.13 0.55


SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2,4‐Dichlorophenol 0.55 U mg/kg N 0.18 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2,4‐Dimethylphenol 0.55 U mg/kg N 0.18 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2,4‐Dinitrophenol 2.2 U mg/kg N 0.13 2.2

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2,4‐Dinitrotoluene 0.22 U mg/kg N 0.048 0.22


SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2‐Chloronaphthalene 0.22 U mg/kg N 0.034 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2‐Chlorophenol 0.55 U mg/kg N 0.11 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2‐Methylnaphthalene 0.22 U mg/kg N 0.061 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2‐Methylphenol 0.22 U mg/kg N 0.12 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2‐Nitroaniline 0.55 U mg/kg N 0.048 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 2‐Nitrophenol 0.55 U mg/kg N 0.12 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 3&4‐Methylphenol 0.22 U mg/kg N 0.14 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 3,3‐Dichlorobenzidine 0.55 U mg/kg N 0.028 0.55


SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 2.2 U mg/kg N 0.13 2.2

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 4‐Bromophenyl phenyl ether 0.22 U mg/kg N 0.04 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 4‐Chloro‐3‐methylphenol 0.55 U mg/kg N 0.11 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 4‐Chloroaniline 0.55 U mg/kg N 0.035 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC 4‐Chlorophenyl phenyl ether 0.22 U mg/kg N 0.033 0.22

Page 159 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Acenaphthene 0.11 U mg/kg N 0.032 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Acenaphthylene 0.0761 J mg/kg Y 0.035 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Acetophenone 0.55 U mg/kg N 0.019 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Anthracene 0.0874 J mg/kg Y 0.038 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Atrazine 0.55 U mg/kg N 0.022 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Benzaldehyde 0.0542 J mg/kg Y 0.025 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Benzo(a)anthracene 0.361 = mg/kg Y 0.036 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Benzo(a)pyrene 0.444 = mg/kg Y 0.033 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Benzo(b)fluoranthene 0.52 = mg/kg Y 0.037 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Benzo(g,h,i)perylene 0.34 = mg/kg Y 0.041 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Benzo(k)fluoranthene 0.282 = mg/kg Y 0.041 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Bis(2‐chloroethoxy)methane 0.22 U mg/kg N 0.044 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Bis(2‐chloroethyl)ether 0.22 U mg/kg N 0.033 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC bis(2‐Chloroisopropyl)ether 0.22 U mg/kg N 0.032 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.594 = mg/kg Y 0.097 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Butyl benzyl phthalate 0.22 U mg/kg N 0.063 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Caprolactam 0.22 U mg/kg N 0.034 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Carbazole 0.22 U mg/kg N 0.051 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Chrysene 0.438 = mg/kg Y 0.037 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Dibenz(a,h)anthracene 0.146 = mg/kg Y 0.037 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Dibenzofuran 0.22 U mg/kg N 0.032 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Diethyl phthalate 0.22 U mg/kg N 0.037 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Dimethyl phthalate 0.112 J mg/kg Y 0.039 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Di‐n‐butyl phthalate 0.22 U mg/kg N 0.024 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Di‐n‐octyl phthalate 0.22 U mg/kg N 0.053 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Fluoranthene 0.739 = mg/kg Y 0.048 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Fluorene 0.11 U mg/kg N 0.036 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Hexachlorobenzene 0.22 U mg/kg N 0.036 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Hexachlorobutadiene 0.11 U mg/kg N 0.03 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Hexachlorocyclopentadiene 2.2 U mg/kg N 0.11 2.2

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Hexachloroethane 0.55 U mg/kg N 0.03 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.306 = mg/kg Y 0.038 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Isophorone 0.22 U mg/kg N 0.029 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Naphthalene 0.11 U mg/kg N 0.03 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Nitrobenzene 0.22 U mg/kg N 0.032 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 0.22 U mg/kg N 0.027 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC N‐Nitrosodiphenylamine 0.55 U mg/kg N 0.065 0.55

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Pentachlorophenol 1.1 U mg/kg N 0.19 1.1

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Phenanthrene 0.304 = mg/kg Y 0.05 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Phenol 0.22 U mg/kg N 0.11 0.22

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N SVOC Pyrene 0.643 = mg/kg Y 0.042 0.11

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 1,1,1‐Trichloroethane 0.036 U mg/kg N 0.00092 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 1,1,2,2‐Tetrachloroethane 0.036 U mg/kg N 0.0021 0.036


SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 0.036 U mg/kg N 0.004 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 1,1‐Dichloroethane 0.036 U mg/kg N 0.00099 0.036

Page 160 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 1,1‐Dichloroethene 0.036 U mg/kg N 0.0047 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 1,2,4‐Trichlorobenzene 0.036 U mg/kg N 0.0025 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 0.072 U mg/kg N 0.0039 0.072

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 1,2‐Dibromoethane 0.0072 U mg/kg N 0.00098 0.0072

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 1,2‐Dichlorobenzene 0.036 U mg/kg N 0.0019 0.036


SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 1,2‐Dichloropropane 0.036 U mg/kg N 0.00093 0.036



SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC 2‐Hexanone 0.036 U mg/kg N 0.0069 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Acetone 0.072 UJ mg/kg N 0.016 0.072

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Benzene 0.0072 U mg/kg N 0.0024 0.0072

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Bromodichloromethane 0.036 U mg/kg N 0.0018 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Bromoform 0.036 U mg/kg N 0.0011 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Bromomethane 0.036 U mg/kg N 0.0029 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Carbon Disulfide 0.036 U mg/kg N 0.0022 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Carbon Tetrachloride 0.036 U mg/kg N 0.004 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Chlorobenzene 0.036 U mg/kg N 0.0024 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Chloroethane 0.036 U mg/kg N 0.0072 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Chloroform 0.036 U mg/kg N 0.0023 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Chloromethane 0.036 U mg/kg N 0.0012 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC cis‐1,2‐Dichloroethene 0.036 U mg/kg N 0.0017 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC cis‐1,3‐Dichloropropene 0.036 U mg/kg N 0.00095 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Cyclohexane 0.036 U mg/kg N 0.0011 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Dibromochloromethane 0.036 U mg/kg N 0.00079 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Dichlorodifluoromethane 0.036 U mg/kg N 0.0068 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Ethylbenzene 0.0072 U mg/kg N 0.0027 0.0072

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Isopropylbenzene 0.036 U mg/kg N 0.0037 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Methyl Acetate 0.036 U mg/kg N 0.0059 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Methyl ethyl ketone 0.072 U mg/kg N 0.014 0.072

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Methyl isobutyl ketone 0.036 U mg/kg N 0.0058 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Methyl tert‐butyl ether 0.0072 U mg/kg N 0.002 0.0072

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Methylcyclohexane 0.036 U mg/kg N 0.0047 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Methylene Chloride 0.036 U mg/kg N 0.0016 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Styrene 0.036 U mg/kg N 0.00077 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Tetrachloroethene 0.036 U mg/kg N 0.001 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Toluene 0.0072 U mg/kg N 0.0021 0.0072

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC trans‐1,2‐Dichloroethene 0.036 U mg/kg N 0.0032 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC trans‐1,3‐Dichloropropene 0.036 U mg/kg N 0.00069 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Trichloroethene 0.036 U mg/kg N 0.0038 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Trichlorofluoromethane 0.036 U mg/kg N 0.0016 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Vinyl Chloride 0.036 U mg/kg N 0.0013 0.036

SD_Grab SD WC‐G.3 062910‐SD‐WC‐G3‐001 6/29/2010 N VOC Xylenes, Total 0.014 U mg/kg N 0.0034 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Aluminum 16500 = mg/kg Y 48 48

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Antimony 4.8 U mg/kg N 4.8 4.8

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Arsenic 18.6 = mg/kg Y 4.8 4.8

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Barium 121 = mg/kg Y 48 48

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Beryllium 0.48 U mg/kg N 0.48 0.48

Page 161 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Cadmium 1.2 U mg/kg N 1.2 1.2

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Calcium 3540 = mg/kg Y 1200 1200

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Chromium 285 = mg/Kg Y 2.4 2.4

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Cobalt 12 U mg/kg N 12 12

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Copper 43.6 = mg/kg Y 6 6

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Iron 26800 = mg/kg Y 24 24

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Lead 93.7 = mg/kg Y 4.8 4.8

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Magnesium 5730 = mg/kg Y 1200 1200

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Manganese 546 = mg/kg Y 3.6 3.6

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Mercury 11.2 = mg/kg Y 1.5 1.5

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Nickel 20.4 = mg/kg Y 9.7 9.7

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Potassium 4470 = mg/kg Y 2400 2400

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Selenium 4.8 U mg/kg N 4.8 4.8

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Silver 1.2 U mg/kg N 1.2 1.2

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Sodium 3900 = mg/kg Y 2400 2400

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Thallium 2.4 U mg/kg N 2.4 2.4

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Vanadium 55.3 = mg/kg Y 12 12

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N Metal Zinc 84.5 = mg/kg Y 4.8 4.8






SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N PCB Aroclor‐1254 0.163 = mg/kg Y 0.017 0.067




SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N PCB_TOT Total Aroclors 0.163 = mg/kg Y 0.024 0.067

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 1,1'‐Biphenyl 0.13 U mg/kg N 0.0076 0.13



SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 2,4‐Dichlorophenol 0.33 U mg/kg N 0.11 0.33

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 2,4‐Dimethylphenol 0.33 U mg/kg N 0.11 0.33

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 2,4‐Dinitrophenol 1.3 U mg/kg N 0.08 1.3


SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 2,6‐Dinitrotoluene 0.13 U mg/kg N 0.025 0.13SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 2‐Chloronaphthalene 0.13 U mg/kg N 0.02 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 2‐Chlorophenol 0.33 U mg/kg N 0.066 0.33

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 2‐Methylnaphthalene 0.13 U mg/kg N 0.036 0.13SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 2‐Methylphenol 0.13 U mg/kg N 0.074 0.13



SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 3&4‐Methylphenol 0.13 U mg/kg N 0.083 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 3,3‐Dichlorobenzidine 0.33 U mg/kg N 0.017 0.33


SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 1.3 U mg/kg N 0.08 1.3

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 4‐Bromophenyl phenyl ether 0.13 U mg/kg N 0.024 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 4‐Chloro‐3‐methylphenol 0.33 U mg/kg N 0.065 0.33

Page 162 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 4‐Chloroaniline 0.33 U mg/kg N 0.021 0.33

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC 4‐Chlorophenyl phenyl ether 0.13 U mg/kg N 0.02 0.13



SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Acenaphthene 0.065 U mg/kg N 0.019 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Acenaphthylene 0.065 U mg/kg N 0.021 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Acetophenone 0.33 U mg/kg N 0.011 0.33

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Anthracene 0.065 U mg/kg N 0.023 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Atrazine 0.33 U mg/kg N 0.013 0.33

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Benzaldehyde 0.33 U mg/kg N 0.015 0.33

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Benzo(a)anthracene 0.0308 J mg/kg Y 0.021 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Benzo(a)pyrene 0.065 U mg/kg N 0.02 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Benzo(b)fluoranthene 0.065 U mg/kg N 0.022 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Benzo(g,h,i)perylene 0.065 U mg/kg N 0.024 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Benzo(k)fluoranthene 0.065 U mg/kg N 0.025 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Bis(2‐chloroethoxy)methane 0.13 U mg/kg N 0.026 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Bis(2‐chloroethyl)ether 0.13 U mg/kg N 0.02 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC bis(2‐Chloroisopropyl)ether 0.13 U mg/kg N 0.019 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.13 U mg/kg N 0.058 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Butyl benzyl phthalate 0.13 U mg/kg N 0.038 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Caprolactam 0.13 U mg/kg N 0.021 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Carbazole 0.13 U mg/kg N 0.03 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Chrysene 0.0387 J mg/kg Y 0.022 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Dibenz(a,h)anthracene 0.065 U mg/kg N 0.022 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Dibenzofuran 0.13 U mg/kg N 0.019 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Diethyl phthalate 0.13 U mg/kg N 0.022 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Dimethyl phthalate 0.13 U mg/kg N 0.023 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Di‐n‐butyl phthalate 0.13 U mg/kg N 0.014 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Di‐n‐octyl phthalate 0.13 U mg/kg N 0.032 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Fluoranthene 0.0506 J mg/kg Y 0.029 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Fluorene 0.065 U mg/kg N 0.021 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Hexachlorobenzene 0.13 U mg/kg N 0.021 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Hexachlorobutadiene 0.065 U mg/kg N 0.018 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Hexachlorocyclopentadiene 1.3 UJ mg/kg N 0.067 1.3

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Hexachloroethane 0.33 U mg/kg N 0.018 0.33

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Indeno(1,2,3‐cd)pyrene 0.065 U mg/kg N 0.023 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Isophorone 0.13 U mg/kg N 0.018 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Naphthalene 0.065 U mg/kg N 0.018 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Nitrobenzene 0.13 U mg/kg N 0.019 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 0.13 U mg/kg N 0.016 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC N‐Nitrosodiphenylamine 0.33 U mg/kg N 0.039 0.33

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Pentachlorophenol 0.65 U mg/kg N 0.11 0.65

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Phenanthrene 0.065 U mg/kg N 0.03 0.065

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Phenol 0.13 U mg/kg N 0.069 0.13

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N SVOC Pyrene 0.0499 J mg/kg Y 0.025 0.065


SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC 1,1,2,2‐Tetrachloroethane 0.014 U mg/kg N 0.0008 0.014


Page 163 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 0.014 U mg/kg N 0.0015 0.014


SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC 1,1‐Dichloroethene 0.014 U mg/kg N 0.0018 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC 1,2,4‐Trichlorobenzene 0.014 U mg/kg N 0.00094 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 0.027 U mg/kg N 0.0015 0.027

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC 1,2‐Dibromoethane 0.0027 U mg/kg N 0.00037 0.0027



SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC 1,2‐Dichloropropane 0.014 U mg/kg N 0.00036 0.014



SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC 2‐Hexanone 0.014 U mg/kg N 0.0026 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Acetone 0.027 U mg/kg N 0.0061 0.027

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Benzene 0.0027 U mg/kg N 0.00093 0.0027

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Bromodichloromethane 0.014 U mg/kg N 0.0007 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Bromoform 0.014 U mg/kg N 0.00041 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Bromomethane 0.014 U mg/kg N 0.0011 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Carbon Disulfide 0.014 UJ mg/kg N 0.00083 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Carbon Tetrachloride 0.014 U mg/kg N 0.0015 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Chlorobenzene 0.014 U mg/kg N 0.00093 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Chloroethane 0.014 U mg/kg N 0.0027 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Chloroform 0.014 U mg/kg N 0.00087 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Chloromethane 0.014 U mg/kg N 0.00045 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC cis‐1,2‐Dichloroethene 0.014 U mg/kg N 0.00065 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC cis‐1,3‐Dichloropropene 0.014 U mg/kg N 0.00036 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Cyclohexane 0.014 UJ mg/kg N 0.00041 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Dibromochloromethane 0.014 U mg/kg N 0.0003 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Dichlorodifluoromethane 0.014 U mg/kg N 0.0026 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Ethylbenzene 0.0027 U mg/kg N 0.001 0.0027

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Isopropylbenzene 0.014 U mg/kg N 0.0014 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Methyl Acetate 0.014 U mg/kg N 0.0023 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Methyl ethyl ketone 0.027 U mg/kg N 0.0054 0.027

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Methyl isobutyl ketone 0.014 U mg/kg N 0.0022 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Methyl tert‐butyl ether 0.0027 U mg/kg N 0.00077 0.0027

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Methylcyclohexane 0.014 U mg/kg N 0.0018 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Methylene Chloride 0.014 U mg/kg N 0.00061 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Styrene 0.014 U mg/kg N 0.00029 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Tetrachloroethene 0.014 U mg/kg N 0.0004 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Toluene 0.0027 U mg/kg N 0.0008 0.0027

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC trans‐1,2‐Dichloroethene 0.014 U mg/kg N 0.0012 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC trans‐1,3‐Dichloropropene 0.014 U mg/kg N 0.00026 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Trichloroethene 0.014 U mg/kg N 0.0014 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Trichlorofluoromethane 0.014 U mg/kg N 0.00063 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Vinyl Chloride 0.014 U mg/kg N 0.00049 0.014

SD_Grab SD WC‐G.4 062210‐SD‐WC‐G4‐001 6/22/2010 N VOC Xylenes, Total 0.0055 U mg/kg N 0.0013 0.0055

SD_South SD BAZ‐3038 BAZ‐3038‐13239 8/27/2013 N Metal Mercury 48 J mg/kg Y 0.45 3

SD_South SD BAZ‐3038 BAZ‐3038‐13239 8/27/2013 N Metal Methyl Mercury 0.097 J mg/kg Y 0.00094 0.0026

SD_South SD BAZ‐3038 BAZ‐3038‐13239 8/27/2013 N PCB Aroclor‐1016 0.094 U mg/kg N 0.094 0.63

Page 164 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SD_South SD BAZ‐3038 BAZ‐3038‐13239 8/27/2013 N PCB Aroclor‐1248 57 = mg/kg Y 0.06 0.63


SD_South SD BAZ‐3038 BAZ‐3038‐13239 8/27/2013 N PCB Aroclor‐1260 6.6 = mg/kg Y 0.089 0.63



SD_South SD BAZ‐3038 BAZ‐3038‐13239 8/27/2013 N PCB_TOT Total Aroclors 63.6 = mg/kg Y 0.12 0.63

SD_South SD MMDB‐314 MMDB‐314‐0‐5‐12250 9/6/2012 N Metal Mercury 11.5 = mg/kg Y 0.0879 0.8

SD_South SD MMDB‐314 MMDB‐314‐0‐5‐12250 9/6/2012 N Metal Methyl Mercury 0.00535 = mg/kg Y 0.000346 0.00223

SD_South SD MRH‐321 MRH‐321‐0‐5‐12250 9/6/2012 N Metal Mercury 13 J mg/kg Y 0.36 2.4

SD_South SD MRH‐321 MRH‐321‐0‐5‐12250 9/6/2012 N Metal Methyl Mercury 0.0037 J mg/kg Y 0.0013 0.0035

SD_South SD MRH‐321 MRH‐321‐0‐5‐12250 9/6/2012 N PCB Aroclor‐1016 0.0013 UJ mg/kg N 0.0013 0.0086




SD_South SD MRH‐321 MRH‐321‐0‐5‐12250 9/6/2012 N PCB Aroclor‐1248 0.39 J mg/kg Y 0.00082 0.0086





SD_South SD MRH‐321 MRH‐321‐0‐5‐12250 9/6/2012 N PCB_TOT Total Aroclors 0.443 = mg/kg Y 0.0016 0.0086













SD_South SD MRH‐322 MRH‐322‐0‐5‐12250 9/6/2012 N Metal Mercury 5.4 J mg/kg Y 0.06 0.4SD_South SD MRH‐322 MRH‐322‐0‐5‐12250 9/6/2012 N Metal Methyl Mercury 0.0027 J mg/kg Y 0.00012 0.00033


SD_South SD MRH‐322 MRH‐322‐0‐5‐12250 9/6/2012 N PCB Aroclor‐1221 0.0015 UJ mg/kg N 0.0015 0.008SD_South SD MRH‐322 MRH‐322‐0‐5‐12250 9/6/2012 N PCB Aroclor‐1232 0.0014 UJ mg/kg N 0.0014 0.008









Page 165 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit












SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Aluminum 9500 J mg/kg Y 35 73

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Antimony 3.7 J mg/kg Y 1.4 3.6

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Arsenic 68 J mg/kg Y 1.1 3.6

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Barium 2800 J mg/kg Y 0.26 73

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Beryllium 0.19 J mg/kg Y 0.16 1.8

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Cadmium 5.1 J mg/kg Y 0.13 0.73

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Calcium 9300 J mg/kg Y 58 1800

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Chromium 300 J mg/kg Y 0.73 1.8

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Cobalt 87 J mg/kg Y 0.58 18

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Copper 90 J mg/kg Y 2.7 9.1

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Iron 99000 J mg/kg Y 18 36

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Lead 110 J mg/kg Y 0.69 1.1

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Magnesium 7500 J mg/kg Y 19 1800

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Manganese 93000 J mg/kg Y 2.7 55



SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Nickel 160 J mg/kg Y 0.98 15

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Potassium 2700 J mg/kg Y 23 1800

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Selenium 16 UJ mg/kg N 16 18

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Silver 3.6 UJ mg/kg N 3.6 18

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Sodium 10000 J mg/kg Y 240 1800

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Thallium 20 UJ mg/kg N 20 36

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Vanadium 90 J mg/kg Y 0.44 18

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N Metal Zinc 1400 J mg/kg Y 3.6 7.3











SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST 4,4'‐DDD 0.0061 J mg/kg Y 0.0001 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST 4‐4’‐DDE 0.0063 NJ mg/kg Y 0.00012 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Alpha Chlordane 0.0075 J mg/kg Y 0.00016 0.0008

Page 166 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST BHC (alpha) 0.0041 J mg/kg Y 0.00013 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST BHC (beta) 0.0044 NJ mg/kg Y 0.00021 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST BHC (delta) 0.0054 J mg/kg Y 0.00012 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST BHC (gamma) 0.005 J mg/kg Y 0.00014 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Dieldrin 0.0093 J mg/kg Y 0.00013 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Endosulfan I 0.0038 J mg/kg Y 0.00015 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Endosulfan II 0.0033 NJ mg/kg Y 0.00014 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Endosulfan sulfate 0.0071 J mg/kg Y 0.000083 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Endrin 0.012 J mg/kg Y 0.00015 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Endrin aldehyde 0.0013 J mg/kg Y 0.00015 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Endrin ketone 0.0036 J mg/kg Y 0.00012 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST gamma‐Chlordane 0.022 J mg/kg Y 0.00016 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Heptachlor epoxide 0.012 NJ mg/kg Y 0.00015 0.0008

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Methoxychlor 0.02 J mg/kg Y 0.00017 0.0016

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N PEST Toxaphene 0.0053 UJ mg/kg N 0.0053 0.032

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 1,1'‐Biphenyl 0.022 UJ mg/kg N 0.022 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2,4,5‐Trichlorophenol 0.027 UJ mg/kg N 0.027 0.25


SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2,4‐Dichlorophenol 0.005 UJ mg/kg N 0.005 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2,4‐Dimethylphenol 0.039 UJ mg/kg N 0.039 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2,4‐Dinitrophenol 0.3 UJ mg/kg N 0.3 1.3

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2,4‐Dinitrotoluene 0.02 UJ mg/kg N 0.02 0.25


SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2‐3‐4‐6‐Tetrachlorophenol 0.016 UJ mg/kg N 0.016 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2‐Chloronaphthalene 0.0052 UJ mg/kg N 0.0052 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2‐Chlorophenol 0.02 UJ mg/kg N 0.02 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2‐Methylnaphthalene 0.039 J mg/kg Y 0.0045 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2‐Methylphenol 0.019 J mg/kg Y 0.017 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2‐Nitroaniline 0.11 UJ mg/kg N 0.11 1.3

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 2‐Nitrophenol 0.028 UJ mg/kg N 0.028 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 3,3‐Dichlorobenzidine 0.026 UJ mg/kg N 0.026 0.25


SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 4,6‐Dinitro‐2‐methylphenol 0.1 UJ mg/kg N 0.1 1.3

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 4‐Bromophenyl phenyl ether 0.022 UJ mg/kg N 0.022 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 4‐Chloro‐3‐methylphenol 0.023 UJ mg/kg N 0.023 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 4‐Chloroaniline 0.02 UJ mg/kg N 0.02 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 4‐Chlorophenyl phenyl ether 0.028 UJ mg/kg N 0.028 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC 4‐Methylphenol 0.024 UJ mg/kg N 0.024 0.25



SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Acenaphthene 0.026 J mg/kg Y 0.0048 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Acenaphthylene 0.058 J mg/kg Y 0.0057 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Acetophenone 0.04 J mg/kg Y 0.021 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Anthracene 0.072 J mg/kg Y 0.0049 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Atrazine 0.024 UJ mg/kg N 0.024 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Benzaldehyde 0.44 J mg/kg Y 0.038 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Benzo(a)anthracene 0.64 J mg/kg Y 0.0063 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Benzo(a)pyrene 0.62 J mg/kg Y 0.005 0.05

Page 167 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Benzo(b)fluoranthene 1 J mg/kg Y 0.0079 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Benzo(g,h,i)perylene 0.52 J mg/kg Y 0.005 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Benzo(k)fluoranthene 0.25 J mg/kg Y 0.01 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Bis(2‐chloroethoxy)methane 0.016 UJ mg/kg N 0.016 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Bis(2‐chloroethyl)ether 0.0067 UJ mg/kg N 0.0067 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC bis(2‐Chloroisopropyl)ether 0.0054 UJ mg/kg N 0.0054 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Bis(2‐ethylhexyl)phthalate 0.35 J mg/kg Y 0.04 0.5

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Butyl benzyl phthalate 0.034 UJ mg/kg N 0.034 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Caprolactam 0.19 UJ mg/kg N 0.19 1.3

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Carbazole 0.038 J mg/kg Y 0.0046 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Chrysene 0.67 J mg/kg Y 0.006 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Dibenz(a,h)anthracene 0.12 J mg/kg Y 0.0056 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Dibenzofuran 0.028 J mg/kg Y 0.025 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Diethyl phthalate 0.027 UJ mg/kg N 0.027 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Dimethyl phthalate 0.027 UJ mg/kg N 0.027 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Di‐n‐butyl phthalate 0.031 UJ mg/kg N 0.031 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Di‐n‐octyl phthalate 0.026 UJ mg/kg N 0.026 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Fluoranthene 0.66 J mg/kg Y 0.0054 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Fluorene 0.036 J mg/kg Y 0.0066 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Hexachlorobenzene 0.0053 UJ mg/kg N 0.0053 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Hexachlorobutadiene 0.0056 UJ mg/kg N 0.0056 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Hexachlorocyclopentadiene 0.027 UJ mg/kg N 0.027 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Hexachloroethane 0.018 UJ mg/kg N 0.018 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Indeno(1,2,3‐cd)pyrene 0.48 J mg/kg Y 0.0052 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Isophorone 0.019 UJ mg/kg N 0.019 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Naphthalene 0.075 J mg/kg Y 0.0043 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Nitrobenzene 0.021 UJ mg/kg N 0.021 0.5

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC N‐Nitroso‐di‐n‐propylamine 0.0059 UJ mg/kg N 0.0059 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC N‐Nitrosodiphenylamine 0.026 J mg/kg Y 0.023 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Pentachlorophenol 0.022 UJ mg/kg N 0.022 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Phenanthrene 0.27 J mg/kg Y 0.008 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Phenol 0.0059 UJ mg/kg N 0.0059 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N SVOC Pyrene 0.78 J mg/kg Y 0.0051 0.05

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,1,1‐Trichloroethane 0.0037 UJ mg/kg N 0.0037 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,1,2,2‐Tetrachloroethane 0.0055 UJ mg/kg N 0.0055 0.038


SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,1,2‐Trichlorotrifluoroethane 0.0081 UJ mg/kg N 0.0081 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,1‐Dichloroethane 0.0044 UJ mg/kg N 0.0044 0.038SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,1‐Dichloroethene 0.0065 UJ mg/kg N 0.0065 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,2,4‐Trichlorobenzene 0.0067 UJ mg/kg N 0.0067 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,2‐Dibromo‐3‐chloropropane 0.0057 UJ mg/kg N 0.0057 0.038SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,2‐Dibromoethane 0.0066 UJ mg/kg N 0.0066 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,2‐Dichlorobenzene 0.0061 UJ mg/kg N 0.0061 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,2‐Dichloroethane 0.0047 UJ mg/kg N 0.0047 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1,2‐Dichloropropane 0.0041 UJ mg/kg N 0.0041 0.038



SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1‐2‐3‐Trichlorobenzene 0.0064 UJ mg/kg N 0.0064 0.038

Page 168 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 1‐2‐4‐5‐Tetrachlorobenzene 0.019 UJ mg/kg N 0.019 0.25

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC 2‐Hexanone 0.0053 UJ mg/kg N 0.0053 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Acetone 0.038 UJ mg/kg N 0.038 0.15

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Benzene 0.0051 UJ mg/kg N 0.0051 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Bromochloromethane 0.0052 UJ mg/kg N 0.0052 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Bromodichloromethane 0.0043 UJ mg/kg N 0.0043 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Bromoform 0.0034 UJ mg/kg N 0.0034 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Bromomethane 0.0056 UJ mg/kg N 0.0056 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Carbon Disulfide 0.0039 UJ mg/kg N 0.0039 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Carbon Tetrachloride 0.0034 UJ mg/kg N 0.0034 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Chlorobenzene 0.0058 UJ mg/kg N 0.0058 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Chloroethane 0.012 UJ mg/kg N 0.012 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Chloroform 0.0045 UJ mg/kg N 0.0045 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Chloromethane 0.0065 UJ mg/kg N 0.0065 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC cis‐1,2‐Dichloroethene 0.0054 UJ mg/kg N 0.0054 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC cis‐1,3‐Dichloropropene 0.0052 UJ mg/kg N 0.0052 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Cyclohexane 0.0028 UJ mg/kg N 0.0028 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Dibromochloromethane 0.0054 UJ mg/kg N 0.0054 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Dichlorodifluoromethane 0.0051 UJ mg/kg N 0.0051 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Ethylbenzene 0.0049 UJ mg/kg N 0.0049 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Isopropylbenzene 0.0052 UJ mg/kg N 0.0052 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC m,p‐Xylenes 0.011 UJ mg/kg N 0.011 0.076

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Methyl Acetate 0.0069 UJ mg/kg N 0.0069 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Methyl ethyl ketone 0.0067 UJ mg/kg N 0.0067 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Methyl isobutyl ketone 0.005 UJ mg/kg N 0.005 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Methyl tert‐butyl ether 0.0057 UJ mg/kg N 0.0057 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Methylcyclohexane 0.0055 UJ mg/kg N 0.0055 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Methylene Chloride 0.0051 UJ mg/kg N 0.0051 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC o‐Xylene 0.0059 UJ mg/kg N 0.0059 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Styrene 0.0054 UJ mg/kg N 0.0054 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Tetrachloroethene 0.0052 UJ mg/kg N 0.0052 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Toluene 0.0056 UJ mg/kg N 0.0056 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC trans‐1,2‐Dichloroethene 0.0045 UJ mg/kg N 0.0045 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC trans‐1,3‐Dichloropropene 0.0045 UJ mg/kg N 0.0045 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Trichloroethene 0.005 UJ mg/kg N 0.005 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Trichlorofluoromethane 0.007 UJ mg/kg N 0.007 0.038

SD_South SD MRH‐323 MRH‐323‐0‐5‐12250 9/6/2012 N VOC Vinyl Chloride 0.0036 UJ mg/kg N 0.0036 0.038

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Aluminum 17000 J mg/kg Y 28 59

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Antimony 3.3 J mg/kg Y 1.2 3

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Arsenic 49 J mg/kg Y 0.89 3

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Barium 520 J mg/kg Y 0.21 59

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Beryllium 0.72 J mg/kg Y 0.13 1.5

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Cadmium 5.1 J mg/kg Y 0.11 0.59

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Calcium 4000 J mg/kg Y 47 1500

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Chromium 1100 J mg/kg Y 0.59 1.5

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Cobalt 23 J mg/kg Y 0.47 15

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Copper 170 J mg/kg Y 2.2 7.4

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Iron 27000 J mg/kg Y 14 30

Page 169 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Lead 220 J mg/kg Y 0.56 0.89

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Magnesium 6500 J mg/kg Y 15 1500

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Manganese 930 J mg/kg Y 0.22 4.4



SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Nickel 81 J mg/kg Y 0.8 12

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Potassium 2300 J mg/kg Y 18 1500

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Selenium 3.4 J mg/kg Y 1.3 1.5

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Silver 3.2 J mg/kg Y 0.3 1.5

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Sodium 5700 J mg/kg Y 190 1500

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Thallium 1.6 UJ mg/kg N 1.6 3

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Vanadium 100 J mg/kg Y 0.35 15

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N Metal Zinc 720 J mg/kg Y 3 5.9











SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST 4‐4’‐DDE 0.028 J mg/kg Y 0.000092 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST 4‐4’‐DDT 0.000092 UJ mg/kg N 0.000092 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST Alpha Chlordane 0.00012 UJ mg/kg N 0.00012 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST BHC (alpha) 0.0001 UJ mg/kg N 0.0001 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST BHC (beta) 0.0054 NJ mg/kg Y 0.00016 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST BHC (delta) 0.000094 UJ mg/kg N 0.000094 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST Dieldrin 0.0029 NJ mg/kg Y 0.0001 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST Endosulfan I 0.0042 J mg/kg Y 0.00012 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST Endrin 0.023 NJ mg/kg Y 0.00012 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST Endrin aldehyde 0.00097 J mg/kg Y 0.00012 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST Endrin ketone 0.011 J mg/kg Y 0.000095 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST gamma‐Chlordane 0.066 J mg/kg Y 0.00012 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST Heptachlor epoxide 0.029 NJ mg/kg Y 0.00012 0.00061

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST Methoxychlor 0.04 J mg/kg Y 0.00013 0.0012

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N PEST Toxaphene 0.0041 UJ mg/kg N 0.0041 0.024

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 1,1'‐Biphenyl 0.022 J mg/kg Y 0.018 0.2



SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 2,4‐Dichlorophenol 0.004 UJ mg/kg N 0.004 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 2,4‐Dimethylphenol 0.031 UJ mg/kg N 0.031 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 2,4‐Dinitrophenol 0.24 UJ mg/kg N 0.24 1



SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 2‐3‐4‐6‐Tetrachlorophenol 0.013 UJ mg/kg N 0.013 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 2‐Chloronaphthalene 0.0041 UJ mg/kg N 0.0041 0.04

Page 170 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 2‐Chlorophenol 0.016 UJ mg/kg N 0.016 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 2‐Methylnaphthalene 0.045 J mg/kg Y 0.0036 0.04


SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 2‐Nitroaniline 0.089 UJ mg/kg N 0.089 1


SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 3,3‐Dichlorobenzidine 0.021 UJ mg/kg N 0.021 0.2


SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 4,6‐Dinitro‐2‐methylphenol 0.08 UJ mg/kg N 0.08 1

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 4‐Bromophenyl phenyl ether 0.017 UJ mg/kg N 0.017 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 4‐Chloro‐3‐methylphenol 0.018 UJ mg/kg N 0.018 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 4‐Chloroaniline 0.066 J mg/kg Y 0.016 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 4‐Chlorophenyl phenyl ether 0.022 UJ mg/kg N 0.022 0.2



SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC 4‐Nitrophenol 0.072 UJ mg/kg N 0.072 1

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Acenaphthene 0.03 J mg/kg Y 0.0038 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Acenaphthylene 0.17 J mg/kg Y 0.0045 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Acetophenone 0.016 UJ mg/kg N 0.016 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Anthracene 0.13 J mg/kg Y 0.0039 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Atrazine 0.019 UJ mg/kg N 0.019 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Benzaldehyde 0.12 J mg/kg Y 0.03 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Benzo(a)anthracene 0.59 J mg/kg Y 0.005 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Benzo(a)pyrene 0.78 J mg/kg Y 0.004 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Benzo(b)fluoranthene 0.85 J mg/kg Y 0.0062 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Benzo(g,h,i)perylene 0.62 J mg/kg Y 0.0039 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Benzo(k)fluoranthene 0.53 J mg/kg Y 0.008 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Bis(2‐chloroethoxy)methane 0.013 UJ mg/kg N 0.013 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Bis(2‐chloroethyl)ether 0.0053 UJ mg/kg N 0.0053 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC bis(2‐Chloroisopropyl)ether 0.0043 UJ mg/kg N 0.0043 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Bis(2‐ethylhexyl)phthalate 0.96 J mg/kg Y 0.032 0.4

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Butyl benzyl phthalate 0.13 J mg/kg Y 0.027 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Caprolactam 0.15 UJ mg/kg N 0.15 1

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Carbazole 0.071 J mg/kg Y 0.0037 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Chrysene 0.83 J mg/kg Y 0.0047 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Dibenz(a,h)anthracene 0.27 J mg/kg Y 0.0044 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Dibenzofuran 0.034 J mg/kg Y 0.02 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Diethyl phthalate 0.022 UJ mg/kg N 0.022 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Dimethyl phthalate 0.022 UJ mg/kg N 0.022 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Di‐n‐butyl phthalate 0.051 J mg/kg Y 0.025 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Di‐n‐octyl phthalate 0.051 J mg/kg Y 0.021 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Fluoranthene 1.1 J mg/kg Y 0.0042 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Fluorene 0.046 J mg/kg Y 0.0052 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Hexachlorobenzene 0.0042 UJ mg/kg N 0.0042 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Hexachlorobutadiene 0.0044 UJ mg/kg N 0.0044 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Hexachlorocyclopentadiene 0.021 UJ mg/kg N 0.021 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Hexachloroethane 0.014 UJ mg/kg N 0.014 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Indeno(1,2,3‐cd)pyrene 0.65 J mg/kg Y 0.0041 0.04SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Isophorone 0.015 UJ mg/kg N 0.015 0.2

Page 171 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Naphthalene 0.087 J mg/kg Y 0.0034 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Nitrobenzene 0.017 UJ mg/kg N 0.017 0.4

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC N‐Nitroso‐di‐n‐propylamine 0.0047 UJ mg/kg N 0.0047 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC N‐Nitrosodiphenylamine 0.11 J mg/kg Y 0.018 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Pentachlorophenol 0.018 UJ mg/kg N 0.018 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Phenanthrene 0.39 J mg/kg Y 0.0063 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Phenol 0.01 J mg/kg Y 0.0047 0.04

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N SVOC Pyrene 0.91 J mg/kg Y 0.004 0.04


SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1,1,2,2‐Tetrachloroethane 0.0029 UJ mg/kg N 0.0029 0.02


SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1,1,2‐Trichlorotrifluoroethane 0.0044 UJ mg/kg N 0.0044 0.02


SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1,1‐Dichloroethene 0.0035 UJ mg/kg N 0.0035 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1,2,4‐Trichlorobenzene 0.0036 UJ mg/kg N 0.0036 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1,2‐Dibromo‐3‐chloropropane 0.0031 UJ mg/kg N 0.0031 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1,2‐Dibromoethane 0.0035 UJ mg/kg N 0.0035 0.02



SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1,2‐Dichloropropane 0.0022 UJ mg/kg N 0.0022 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1,3‐Dichlorobenzene 0.0027 UJ mg/kg N 0.0027 0.02SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1,4‐Dichlorobenzene 0.0026 UJ mg/kg N 0.0026 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1‐2‐3‐Trichlorobenzene 0.0034 UJ mg/kg N 0.0034 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 1‐2‐4‐5‐Tetrachlorobenzene 0.015 UJ mg/kg N 0.015 0.2

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC 2‐Hexanone 0.0028 UJ mg/kg N 0.0028 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Acetone 0.02 UJ mg/kg N 0.02 0.082

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Benzene 0.0028 UJ mg/kg N 0.0028 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Bromochloromethane 0.0028 UJ mg/kg N 0.0028 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Bromodichloromethane 0.0023 UJ mg/kg N 0.0023 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Bromoform 0.0018 UJ mg/kg N 0.0018 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Bromomethane 0.003 UJ mg/kg N 0.003 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Carbon Disulfide 0.0021 UJ mg/kg N 0.0021 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Carbon Tetrachloride 0.0018 UJ mg/kg N 0.0018 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Chlorobenzene 0.0031 UJ mg/kg N 0.0031 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Chloroethane 0.0063 UJ mg/kg N 0.0063 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Chloroform 0.0024 UJ mg/kg N 0.0024 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Chloromethane 0.0035 UJ mg/kg N 0.0035 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC cis‐1,2‐Dichloroethene 0.0029 UJ mg/kg N 0.0029 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC cis‐1,3‐Dichloropropene 0.0028 UJ mg/kg N 0.0028 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Cyclohexane 0.0015 UJ mg/kg N 0.0015 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Dibromochloromethane 0.0029 UJ mg/kg N 0.0029 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Dichlorodifluoromethane 0.0027 UJ mg/kg N 0.0027 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Ethylbenzene 0.0026 UJ mg/kg N 0.0026 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Isopropylbenzene 0.0028 UJ mg/kg N 0.0028 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC m,p‐Xylenes 0.006 UJ mg/kg N 0.006 0.041

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Methyl Acetate 0.0037 UJ mg/kg N 0.0037 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Methyl ethyl ketone 0.0036 UJ mg/kg N 0.0036 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Methyl isobutyl ketone 0.0027 UJ mg/kg N 0.0027 0.02

Page 172 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Methyl tert‐butyl ether 0.003 UJ mg/kg N 0.003 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Methylcyclohexane 0.003 UJ mg/kg N 0.003 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Methylene Chloride 0.0027 UJ mg/kg N 0.0027 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC o‐Xylene 0.0032 UJ mg/kg N 0.0032 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Styrene 0.0029 UJ mg/kg N 0.0029 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Tetrachloroethene 0.0028 UJ mg/kg N 0.0028 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Toluene 0.003 UJ mg/kg N 0.003 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC trans‐1,2‐Dichloroethene 0.0024 UJ mg/kg N 0.0024 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC trans‐1,3‐Dichloropropene 0.0024 UJ mg/kg N 0.0024 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Trichloroethene 0.0027 UJ mg/kg N 0.0027 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Trichlorofluoromethane 0.0037 UJ mg/kg N 0.0037 0.02

SD_South SD MRH‐323 MRH‐323‐10‐15‐12250 9/6/2012 N VOC Vinyl Chloride 0.0019 UJ mg/kg N 0.0019 0.02

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Aluminum 10500 = mg/kg Y 130 130

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Antimony 13 U mg/kg N 13 13

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Arsenic 13 U mg/kg N 13 13

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Barium 130 U mg/kg N 130 130

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Beryllium 3.2 U mg/kg N 3.2 3.2

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Cadmium 3.2 U mg/kg N 3.2 3.2

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Calcium 5200 = mg/kg Y 3200 3200

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Chromium 360 = mg/kg Y 6.4 6.4

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Cobalt 32 U mg/kg N 32 32

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Copper 148 = mg/kg Y 16 16

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Iron 13200 = mg/kg Y 64 64

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Lead 203 = mg/kg Y 13 13

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Magnesium 5180 = mg/kg Y 3200 3200

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Manganese 357 = mg/kg Y 9.5 9.5

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Mercury 0.2 U mg/kg N 0.2 0.2

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Nickel 61.2 = mg/kg Y 25 25

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Potassium 3200 U mg/kg N 3200 3200

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Selenium 13 U mg/kg N 13 13

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Silver 6.4 U mg/kg N 6.4 6.4

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Sodium 8580 = mg/kg Y 6400 6400

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Thallium 6.4 U mg/kg N 6.4 6.4

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Vanadium 54 = mg/kg Y 32 32

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N Metal Zinc 172 = mg/kg Y 13 13

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Aroclor‐1016 0.21 U mg/kg N 0.039 0.21




SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Aroclor‐1248 1.75 = mg/kg Y 0.071 0.21



SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener 2,3,7,8‐TCDD TEQ 5.47E‐05 = mg/kg Y

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener PCB‐1 0.000333 = mg/kg Y 0 0.0000156



SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener PCB‐104 2.19E‐05 = mg/kg Y 0 0.0000156


Page 173 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener PCB‐106/118 0.0982 = mg/kg Y 0 0.0000156











SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener PCB‐121 1.56E‐05 U mg/kg N 0 0.0000156
















SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener PCB‐138/163/164 0.0354 = mg/kg Y 0 0.0000156





















Page 174 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit














































SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener PCB‐207 0.000231 = mg/kg Y 0 0.0000156SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener PCB‐208 0.000743 = mg/kg Y 0 0.0000156


Page 175 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit










SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener PCB‐31 0.0617 = mg/kg Y 0 0.0000156SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener PCB‐34 0.00045 = mg/kg Y 0 0.0000156








SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB Congener PCB‐41/64/71/72 0.0876 = mg/kg Y 0 0.0000156






























Page 176 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




















SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB_TOT Total Aroclors 1.75 = mg/kg Y 0.12 0.21

SD_South SD SC‐G.3 072106‐SD‐OFC‐0G3‐0001 7/21/2006 N PCB_TOT Total PCBs 2.4135 = mg/kg Y

SW SW MNR‐1 042612‐SW‐WW‐MNR1‐ebb 4/26/2012 N Metal Chromium 10 U µg/l N 10 10

SW SW MNR‐1 042612‐SW‐WW‐MNR1‐ebb 4/26/2012 N Metal Mercury 0.43 = µg/l Y 0.2 0.2

SW SW MNR‐1 042712‐SW‐WW‐MNR1‐FLOOD 4/27/2012 N Metal Chromium 10 U µg/l N 10 10

SW SW MNR‐1 042712‐SW‐WW‐MNR1‐FLOOD 4/27/2012 N Metal Mercury 0.59 = µg/l Y 0.2 0.2



SW SW MNR‐1 070112‐SW‐WW‐MNR1‐flood 7/1/2012 N Metal Chromium 10.4 = µg/l Y 10 10

SW SW MNR‐1 070112‐SW‐WW‐MNR1‐flood 7/1/2012 N Metal Mercury 0.23 = µg/l Y 0.2 0.2

SW SW MNR‐2 042612‐SW‐WW‐MNR2‐ebb 4/26/2012 N Metal Chromium 12.2 = µg/l Y 10 10




SW SW MNR‐2 062812‐SW‐WW‐MNR2‐ebb 6/28/2012 N Metal Chromium 11.9 = µg/l Y 10 10

SW SW MNR‐2 062812‐SW‐WW‐MNR2‐ebb 6/28/2012 N Metal Mercury 0.2 U µg/l N 0.2 0.2


SW SW MNR‐2 070112‐SW‐WW‐MNR2‐flood 7/1/2012 N Metal Mercury 0.2 U µg/l N 0.2 0.2









SW SW MNR‐5 040214‐SW‐WW‐MNR5‐HIGH 4/2/2014 N DissMetal Chromium, Dissolved 10 U µg/l N 0.89 10

SW SW MNR‐5 040214‐SW‐WW‐MNR5‐HIGH 4/2/2014 N DissMetal Mercury, Dissolved 0.098 U µg/l N 0.048 0.2

SW SW MNR‐5 040214‐SW‐WW‐MNR5‐HIGH 4/2/2014 N Metal Chromium 6.4 J µg/l Y 0.89 10

Page 177 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MNR‐5 040214‐SW‐WW‐MNR5‐HIGH 4/2/2014 N Metal Mercury 0.23 U µg/l N 0.048 0.2





SW SW MNR‐5 062613‐SW‐WW‐MNR5‐HIGH 6/26/2013 N DissMetal Chromium, Dissolved 10 U µg/l N 10 10


SW SW MNR‐5 062613‐SW‐WW‐MNR5‐HIGH 6/26/2013 N Metal Chromium 10 U µg/l N 10 10

SW SW MNR‐5 062613‐SW‐WW‐MNR5‐HIGH 6/26/2013 N Metal Mercury 0.34 = µg/l Y 0.2 0.2

SW SW MNR‐5 062812‐SW‐WW‐MNR5‐ebb 6/28/2012 N Metal Chromium 16 = µg/l Y 10 10

SW SW MNR‐5 062812‐SW‐WW‐MNR5‐ebb 6/28/2012 N Metal Mercury 0.2 U µg/l N 0.2 0.2






SW SW MNR‐5 092513‐SW‐WW‐MNR5‐HIGH 9/25/2013 N Metal Mercury 0.32 = µg/l Y 0.089 0.2




SW SW MNR‐5 102214‐SW‐WW‐MNR5‐HIGH 10/22/2014 N Metal Mercury 0.081 J µg/l Y 0.064 0.2

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Aluminum, Dissolved 20.5 J µg/l Y 19 50

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Antimony, Dissolved 2 U µg/l N 0.13 2

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Arsenic, Dissolved 2.6 J µg/l Y 0.4 5

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Barium, Dissolved 52 J µg/l Y 0.19 1

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Beryllium, Dissolved 1 U µg/l N 0.2 1

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Cadmium, Dissolved 1 U µg/l N 0.13 1

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Calcium, Dissolved 44300 J µg/l Y 22 1000

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Chromium, Dissolved 2 U µg/l N 0.71 2

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Cobalt, Dissolved 1 U µg/l N 0.058 1

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Copper, Dissolved 2 U µg/l N 0.29 2

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Iron, Dissolved 95.5 J µg/l Y 26 50SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Lead, Dissolved 1 U µg/l N 0.18 1

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Magnesium, Dissolved 44200 J µg/l Y 17 1000

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Manganese, Dissolved 328 = µg/l Y 0.83 1

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Mercury, Dissolved 0.0177 = µg/l Y 0.00048 0.002

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Nickel, Dissolved 2.2 = µg/l Y 0.2 2

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Potassium, Dissolved 19100 = µg/l Y 8.3 1000

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Selenium, Dissolved 5 U µg/l N 1.2 5

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Silver, Dissolved 1 U µg/l N 0.08 1

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Sodium, Dissolved 449000 J µg/l Y 6.9 1000

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Thallium, Dissolved 1 U µg/l N 0.14 1

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Vanadium, Dissolved 1.7 J µg/l Y 0.44 20

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N DissMetal Zinc, Dissolved 20 U µg/l N 2.3 20

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N Metal Methyl Mercury, Dissolved 0.00069 = µg/l Y 0.00001 0.00005

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N PCB Aroclor‐1016 0.0095 U µg/l N 0.0024 0.0095



Page 178 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit







SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N PCB_TOT Total Aroclors 0 U µg/l N 0.0024 0.0095

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 1,1'‐Biphenyl 0.94 U µg/l N 0.014 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2,4,5‐Trichlorophenol 0.94 U µg/l N 0.014 0.94


SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2,4‐Dichlorophenol 0.19 U µg/l N 0.013 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2,4‐Dimethylphenol 0.94 U µg/l N 0.0075 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2,4‐Dinitrophenol 4.7 U µg/l N 0.58 4.7

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2,4‐Dinitrotoluene 0.94 U µg/l N 0.016 0.94


SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2‐3‐4‐6‐Tetrachlorophenol 0.94 U µg/l N 0.096 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2‐Chloronaphthalene 0.19 U µg/l N 0.014 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2‐Chlorophenol 0.94 U µg/l N 0.02 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2‐Methylnaphthalene 0.19 U µg/l N 0.015 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2‐Methylphenol 0.94 U µg/l N 0.013 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2‐Nitroaniline 4.7 U µg/l N 0.016 4.7

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 2‐Nitrophenol 0.94 U µg/l N 0.013 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 3,3‐Dichlorobenzidine 0.94 U µg/l N 0.034 0.94


SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 4,6‐Dinitro‐2‐methylphenol 4.7 U µg/l N 0.73 4.7

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 4‐Bromophenyl phenyl ether 0.94 U µg/l N 0.018 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 4‐Chloro‐3‐methylphenol 0.94 U µg/l N 0.024 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 4‐Chloroaniline 0.94 U µg/l N 0.1 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC 4‐Chlorophenyl phenyl ether 0.94 U µg/l N 0.0098 0.94




SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Acenaphthene 0.19 U µg/l N 0.014 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Acenaphthylene 0.19 U µg/l N 0.008 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Acetophenone 0.079 J µg/l Y 0.021 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Anthracene 0.19 U µg/l N 0.0081 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Atrazine 0.94 U µg/l N 0.019 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Benzaldehyde 1 = µg/l Y 0.047 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Benzo(a)anthracene 0.19 U µg/l N 0.017 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Benzo(a)pyrene 0.19 U µg/l N 0.011 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Benzo(b)fluoranthene 0.19 U µg/l N 0.015 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Benzo(g,h,i)perylene 0.19 U µg/l N 0.0081 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Benzo(k)fluoranthene 0.19 U µg/l N 0.015 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Bis(2‐chloroethoxy)methane 0.94 U µg/l N 0.013 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Bis(2‐chloroethyl)ether 0.19 U µg/l N 0.025 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC bis(2‐Chloroisopropyl)ether 0.19 U µg/l N 0.033 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Bis(2‐ethylhexyl)phthalate 0.91 J µg/l Y 0.043 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Butyl benzyl phthalate 0.94 U µg/l N 0.29 0.94

Page 179 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Caprolactam 1.5 J µg/l Y 0.68 4.7

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Carbazole 0.19 U µg/l N 0.013 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Chrysene 0.19 U µg/l N 0.01 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Dibenz(a,h)anthracene 0.19 U µg/l N 0.012 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Dibenzofuran 0.021 J µg/l Y 0.017 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Diethyl phthalate 0.39 J µg/l Y 0.042 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Dimethyl phthalate 0.94 U µg/l N 0.013 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Di‐n‐butyl phthalate 0.94 U µg/l N 0.028 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Di‐n‐octyl phthalate 0.94 U µg/l N 0.015 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Fluoranthene 0.19 U µg/l N 0.0094 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Fluorene 0.023 J µg/l Y 0.0093 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Hexachlorobenzene 0.19 U µg/l N 0.017 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Hexachlorobutadiene 0.19 U µg/l N 0.011 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Hexachlorocyclopentadiene 0.94 UJ µg/l N 0.011 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Hexachloroethane 0.94 U µg/l N 0.0072 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Indeno(1,2,3‐cd)pyrene 0.19 U µg/l N 0.015 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Isophorone 0.94 U µg/l N 0.027 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Naphthalene 0.19 U µg/l N 0.026 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Nitrobenzene 0.19 U µg/l N 0.017 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC N‐Nitroso‐di‐n‐propylamine 0.19 U µg/l N 0.036 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC N‐Nitrosodiphenylamine 0.19 U µg/l N 0.046 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Pentachlorophenol 0.94 U µg/l N 0.18 0.94

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Phenanthrene 0.19 U µg/l N 0.027 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Phenol 0.19 U µg/l N 0.022 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N SVOC Pyrene 0.19 U µg/l N 0.01 0.19

SW SW MSW‐24 MQW‐24F‐09166 6/15/2009 N VOC 1‐2‐4‐5‐Tetrachlorobenzene 0.94 U µg/l N 0.093 0.94

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Aluminum, Dissolved 50 UJ µg/l N 19 50

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Antimony, Dissolved 2 U µg/l N 0.13 2

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Arsenic, Dissolved 2 J µg/l Y 0.4 5

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Barium, Dissolved 92.8 = µg/l Y 0.19 1




SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Chromium, Dissolved 1.1 J µg/l Y 0.71 2

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Cobalt, Dissolved 5.2 = µg/l Y 0.058 1


SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Iron, Dissolved 50 U µg/l N 26 50

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Lead, Dissolved 0.37 J µg/l Y 0.18 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Magnesium, Dissolved 219000 = µg/l Y 17 1000







SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Sodium, Dissolved 1840000 = µg/l Y 138 20000



Page 180 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N DissMetal Zinc, Dissolved 83.8 J µg/l Y 2.3 20












SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 1,1'‐Biphenyl 1 U µg/l N 0.016 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 2,4,5‐Trichlorophenol 1 U µg/l N 0.016 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 2,4,6‐Trichlorophenol 1 U µg/l N 0.0094 1


SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 2,4‐Dimethylphenol 1 U µg/l N 0.0082 1


SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 2,4‐Dinitrotoluene 1 U µg/l N 0.017 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 2,6‐Dinitrotoluene 1 U µg/l N 0.02 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 2‐3‐4‐6‐Tetrachlorophenol 1 U µg/l N 0.1 1


SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 2‐Chlorophenol 1 U µg/l N 0.022 1


SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 2‐Methylphenol 1 U µg/l N 0.014 1


SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 2‐Nitrophenol 1 U µg/l N 0.014 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 3,3‐Dichlorobenzidine 1 U µg/l N 0.037 1



SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 4‐Bromophenyl phenyl ether 1 U µg/l N 0.019 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 4‐Chloro‐3‐methylphenol 1 U µg/l N 0.026 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 4‐Chloroaniline 1 U µg/l N 0.11 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 4‐Chlorophenyl phenyl ether 1 U µg/l N 0.011 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC 4‐Methylphenol 1 U µg/l N 0.018 1





SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Acetophenone 1 U µg/l N 0.023 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Anthracene 0.015 J µg/l Y 0.0089 0.21

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Atrazine 1 U µg/l N 0.021 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Benzaldehyde 1.3 = µg/l Y 0.052 1






Page 181 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Bis(2‐chloroethoxy)methane 1 U µg/l N 0.014 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Bis(2‐chloroethyl)ether 0.21 U µg/l N 0.027 0.21SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC bis(2‐Chloroisopropyl)ether 0.21 U µg/l N 0.036 0.21

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Bis(2‐ethylhexyl)phthalate 1 U µg/l N 0.048 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Butyl benzyl phthalate 1 U µg/l N 0.32 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Caprolactam 5.2 U µg/l N 0.74 5.2

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Carbazole 0.02 J µg/l Y 0.014 0.21



SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Dibenzofuran 1 U µg/l N 0.019 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Diethyl phthalate 1 U µg/l N 0.046 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Dimethyl phthalate 1 U µg/l N 0.014 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Di‐n‐butyl phthalate 1 U µg/l N 0.031 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Di‐n‐octyl phthalate 1 U µg/l N 0.016 1SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Fluoranthene 0.21 U µg/l N 0.01 0.21

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Fluorene 0.21 U µg/l N 0.01 0.21



SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Hexachlorocyclopentadiene 1 UJ µg/l N 0.012 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Hexachloroethane 1 U µg/l N 0.0079 1


SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Isophorone 1 U µg/l N 0.03 1





SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Pentachlorophenol 1 U µg/l N 0.19 1

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Phenanthrene 0.095 J µg/l Y 0.029 0.21

SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N SVOC Phenol 0.12 J µg/l Y 0.024 0.21


SW SW MSW‐24 MQW‐24F‐09264 9/21/2009 N VOC 1‐2‐4‐5‐Tetrachlorobenzene 1 U µg/l N 0.1 1

SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N DissMetal Aluminum, Dissolved 50 U µg/l N 19 50

SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N DissMetal Antimony, Dissolved 0.88 J µg/l Y 0.13 2

SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N DissMetal Arsenic, Dissolved 5 U µg/l N 0.4 5

SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N DissMetal Barium, Dissolved 66.3 J µg/l Y 0.19 1





SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N DissMetal Cobalt, Dissolved 2.5 = µg/l Y 0.058 1


SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N DissMetal Iron, Dissolved 114 = µg/l Y 26 50

SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N DissMetal Lead, Dissolved 1 U µg/l N 0.18 1





SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N DissMetal Potassium, Dissolved 38800 J µg/l Y 8.3 1000

Page 182 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit






















SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC 2,4‐Dinitrophenol 4.8 UJ µg/l N 0.59 4.8



SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC 2‐3‐4‐6‐Tetrachlorophenol 0.96 U µg/l N 0.098 0.96



SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC 2‐Methylnaphthalene 0.018 J µg/l Y 0.015 0.19

SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC 2‐Methylphenol 0.019 J µg/l Y 0.013 0.96





SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC 4,6‐Dinitro‐2‐methylphenol 4.8 UJ µg/l N 0.75 4.8



SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC 4‐Chloroaniline 0.96 U µg/l N 0.1 0.96

SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC 4‐Chlorophenyl phenyl ether 0.96 U µg/l N 0.01 0.96




SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC Acenaphthene 0.016 J µg/l Y 0.014 0.19


SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC Acetophenone 0.075 J µg/l Y 0.021 0.96


SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC Atrazine 0.96 UJ µg/l N 0.019 0.96

SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC Benzaldehyde 1.4 J µg/l Y 0.048 0.96


Page 183 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit








SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC Bis(2‐ethylhexyl)phthalate 0.96 U µg/l N 0.044 0.96






SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC Dibenzofuran 0.027 J µg/l Y 0.018 0.96

SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC Diethyl phthalate 0.96 U µg/l N 0.043 0.96




SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC Fluoranthene 0.021 J µg/l Y 0.0096 0.19




SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC Hexachlorocyclopentadiene 0.96 UJ µg/l N 0.011 0.96




SW SW MSW‐24 MQW‐24F‐09341 12/7/2009 N SVOC Naphthalene 0.071 J µg/l Y 0.027 0.19









SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Aluminum, Dissolved 250 U µg/l N 95 250

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Antimony, Dissolved 0.49 J µg/l Y 0.13 2

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Arsenic, Dissolved 1.9 J µg/l Y 0.4 5

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Barium, Dissolved 53.9 J µg/l Y 0.19 1





SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Cobalt, Dissolved 5 U µg/l N 0.29 5


SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Iron, Dissolved 250 U µg/l N 130 250

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Lead, Dissolved 1 U µg/l N 0.18 1


Page 184 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Manganese, Dissolved 452 J µg/l Y 0.83 1

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Mercury, Dissolved 0.0196 J µg/l Y 0.0024 0.01

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Nickel, Dissolved 2.3 J µg/l Y 1 10






SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Vanadium, Dissolved 100 U µg/l N 2.2 100

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N DissMetal Zinc, Dissolved 100 U µg/l N 11.5 100




















SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC 2‐3‐4‐6‐Tetrachlorophenol 0.98 U µg/l N 0.13 0.98SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC 2‐Chloronaphthalene 0.2 U µg/l N 0.015 0.2











SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC 4‐Chloroaniline 0.98 U µg/l N 0.087 0.98SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC 4‐Chlorophenyl phenyl ether 0.98 U µg/l N 0.049 0.98



SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC 4‐Nitrophenol 4.9 UJ µg/l N 0.59 4.9



Page 185 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC Acetophenone 0.98 U µg/l N 0.078 0.98


SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC Atrazine 0.98 U µg/l N 0.087 0.98

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC Benzaldehyde 0.83 J µg/l Y 0.15 0.98









SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC Bis(2‐ethylhexyl)phthalate 0.98 U µg/l N 0.78 0.98






SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC Dibenzofuran 0.98 U µg/l N 0.06 0.98

SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC Diethyl phthalate 0.98 U µg/l N 0.14 0.98




SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC Fluoranthene 0.032 J µg/l Y 0.016 0.2




SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC Hexachlorocyclopentadiene 0.98 U µg/l N 0.051 0.98











SW SW MSW‐24 MQW‐24F‐10125 5/5/2010 N SVOC Pyrene 0.018 J µg/l Y 0.015 0.2


SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N GenChem Cyanide 10 U µg/l N 1.5 10

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Aluminum 265 = µg/l Y 19 50

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Antimony 2 U µg/l N 0.13 2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Arsenic 3 J µg/l Y 0.4 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Barium 49.5 J µg/l Y 0.19 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Beryllium 1 U µg/l N 0.2 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Cadmium 1 U µg/l N 0.13 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Calcium 44200 J µg/l Y 22 1000

Page 186 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Chromium 4.5 = µg/l Y 0.71 2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Cobalt 1 U µg/l N 0.058 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Copper 4.5 J µg/l Y 0.29 2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Iron 878 J µg/l Y 26 50

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Lead 4.2 = µg/l Y 0.18 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Magnesium 56300 J µg/l Y 85 5000

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Manganese 316 = µg/l Y 0.83 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Mercury 0.318 = µg/l Y 0.012 0.05

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Methyl Mercury 0.0013 J µg/l Y 0.0001 0.0005

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Nickel 2.8 = µg/l Y 0.2 2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Potassium 22700 = µg/l Y 8.3 1000

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Selenium 5 U µg/l N 1.2 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Silver 1 U µg/l N 0.08 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Sodium 523000 J µg/l Y 34.5 5000

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Thallium 1 U µg/l N 0.14 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Vanadium 2.4 J µg/l Y 0.44 20

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N Metal Zinc 20 U µg/l N 2.3 20

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PCB Aroclor‐1016 0.0095 U µg/l N 0.0024 0.0095









SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PCB_TOT Total Aroclors 0 U µg/l N 0.0024 0.0095

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST 4,4'‐DDD 0.0012 U µg/l N 0.00064 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST 4‐4’‐DDE 0.0012 U µg/l N 0.00075 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST 4‐4’‐DDT 0.001 J µg/l Y 0.0007 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Aldrin 0.0043 NJ µg/l Y 0.00079 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Alpha Chlordane 0.0012 U µg/l N 0.00093 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST BHC (alpha) 0.0012 U µg/l N 0.00063 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST BHC (beta) 0.0012 U µg/l N 0.00095 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST BHC (gamma) 0.0056 NJ µg/l Y 0.00076 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Chlordane (beta) 0.034 = µg/l Y 0.00091 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Dieldrin 0.0012 U µg/l N 0.00078 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Endosulfan I 0.0012 U µg/l N 0.00089 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Endosulfan II 0.0052 NJ µg/l Y 0.00093 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Endosulfan sulfate 0.0012 U µg/l N 0.00054 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Endrin 0.0012 U µg/l N 0.00091 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Endrin aldehyde 0.0012 U µg/l N 0.00086 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Endrin ketone 0.0012 U µg/l N 0.00087 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Heptachlor epoxide 0.0012 U µg/l N 0.00092 0.0012

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Methoxychlor 0.0024 U µg/l N 0.00086 0.0024

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N PEST Toxaphene 0.048 U µg/l N 0.00066 0.048

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 1,1'‐Biphenyl 1 U µg/l N 0.015 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2,4,5‐Trichlorophenol 1 U µg/l N 0.015 1

Page 187 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2,4,6‐Trichlorophenol 1 U µg/l N 0.0091 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2,4‐Dichlorophenol 0.2 U µg/l N 0.014 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2,4‐Dimethylphenol 1 U µg/l N 0.008 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2,4‐Dinitrophenol 1 J µg/l Y 0.61 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2,4‐Dinitrotoluene 1 U µg/l N 0.016 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2,6‐Dinitrotoluene 1 U µg/l N 0.019 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2‐3‐4‐6‐Tetrachlorophenol 1 U µg/l N 0.1 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2‐Chloronaphthalene 0.2 U µg/l N 0.015 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2‐Chlorophenol 1 U µg/l N 0.021 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2‐Methylnaphthalene 0.2 U µg/l N 0.016 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2‐Methylphenol 1 U µg/l N 0.014 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2‐Nitroaniline 5 U µg/l N 0.017 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 2‐Nitrophenol 1 U µg/l N 0.014 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 3,3‐Dichlorobenzidine 1 U µg/l N 0.036 1


SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 4,6‐Dinitro‐2‐methylphenol 5 U µg/l N 0.78 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 4‐Bromophenyl phenyl ether 1 U µg/l N 0.019 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 4‐Chloro‐3‐methylphenol 1 U µg/l N 0.025 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 4‐Chloroaniline 1 U µg/l N 0.11 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 4‐Chlorophenyl phenyl ether 1 U µg/l N 0.01 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 4‐Methylphenol 1 U µg/l N 0.018 1


SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC 4‐Nitrophenol 5 U µg/l N 0.7 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Acenaphthene 0.019 J µg/l Y 0.014 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Acenaphthylene 0.2 U µg/l N 0.0085 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Acetophenone 0.034 J µg/l Y 0.022 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Anthracene 0.2 U µg/l N 0.0086 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Atrazine 1 U µg/l N 0.02 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Benzaldehyde 1 = µg/l Y 0.05 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Benzo(a)anthracene 0.2 U µg/l N 0.018 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Benzo(a)pyrene 0.2 U µg/l N 0.012 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Benzo(b)fluoranthene 0.2 U µg/l N 0.016 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Benzo(g,h,i)perylene 0.2 U µg/l N 0.0087 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Benzo(k)fluoranthene 0.2 U µg/l N 0.016 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Bis(2‐chloroethoxy)methane 1 U µg/l N 0.014 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Bis(2‐chloroethyl)ether 0.2 U µg/l N 0.026 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC bis(2‐Chloroisopropyl)ether 0.2 U µg/l N 0.035 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Bis(2‐ethylhexyl)phthalate 1.5 B µg/l Y 0.046 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Butyl benzyl phthalate 1.2 B µg/l Y 0.31 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Caprolactam 3 J µg/l Y 0.72 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Carbazole 0.2 U µg/l N 0.014 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Chrysene 0.2 U µg/l N 0.011 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Dibenz(a,h)anthracene 0.2 U µg/l N 0.013 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Dibenzofuran 0.024 J µg/l Y 0.018 1SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Diethyl phthalate 0.16 J µg/l Y 0.045 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Dimethyl phthalate 1 U µg/l N 0.014 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Di‐n‐butyl phthalate 0.29 J µg/l Y 0.03 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Di‐n‐octyl phthalate 1 U µg/l N 0.016 1

Page 188 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Fluoranthene 0.052 J µg/l Y 0.01 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Fluorene 0.019 J µg/l Y 0.0099 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Hexachlorobenzene 0.2 U µg/l N 0.018 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Hexachlorobutadiene 0.2 U µg/l N 0.012 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Hexachlorocyclopentadiene 1 U µg/l N 0.012 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Hexachloroethane 1 U µg/l N 0.0077 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Indeno(1,2,3‐cd)pyrene 0.2 U µg/l N 0.016 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Isophorone 1 U µg/l N 0.029 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Naphthalene 0.2 U µg/l N 0.028 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Nitrobenzene 0.2 U µg/l N 0.018 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC N‐Nitroso‐di‐n‐propylamine 0.2 U µg/l N 0.039 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC N‐Nitrosodiphenylamine 0.2 U µg/l N 0.049 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Pentachlorophenol 1 U µg/l N 0.19 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Phenanthrene 0.068 J µg/l Y 0.028 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Phenol 0.2 U µg/l N 0.024 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N SVOC Pyrene 0.033 J µg/l Y 0.011 0.2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,1,1‐Trichloroethane 1 U µg/l N 0.29 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,1,2,2‐Tetrachloroethane 1 U µg/l N 0.2 1


SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,1,2‐Trichlorotrifluoroethane 1 U µg/l N 0.32 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,1‐Dichloroethane 1 U µg/l N 0.12 1SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,1‐Dichloroethene 1 U µg/l N 0.3 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,2,4‐Trichlorobenzene 1 U µg/l N 0.27 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,2‐Dibromo‐3‐chloropropane 1 U µg/l N 0.14 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,2‐Dibromoethane 1 U µg/l N 0.18 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,2‐Dichlorobenzene 1 U µg/l N 0.15 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,2‐Dichloroethane 1 U µg/l N 0.21 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1,2‐Dichloropropane 1 U µg/l N 0.095 1



SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1‐2‐3‐Trichlorobenzene 1 U µg/l N 0.15 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 1‐2‐4‐5‐Tetrachlorobenzene 1 U µg/l N 0.099 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC 2‐Hexanone 5 U µg/l N 0.16 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Acetone 5 U µg/l N 2.5 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Benzene 1 U µg/l N 0.11 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Bromochloromethane 1 U µg/l N 0.18 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Bromodichloromethane 1 U µg/l N 0.13 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Bromoform 1 U µg/l N 0.19 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Bromomethane 1 U µg/l N 0.31 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Carbon Disulfide 1 U µg/l N 0.21 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Carbon Tetrachloride 1 U µg/l N 0.14 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Chlorobenzene 1 U µg/l N 0.14 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Chloroethane 1 U µg/l N 0.21 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Chloroform 1 U µg/l N 0.17 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Chloromethane 1 U µg/l N 0.28 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC cis‐1,2‐Dichloroethene 0.33 J µg/l Y 0.24 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC cis‐1,3‐Dichloropropene 1 U µg/l N 0.19 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Cyclohexane 1 U µg/l N 0.25 1

Page 189 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Dibromochloromethane 1 U µg/l N 0.14 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Dichlorodifluoromethane 1 U µg/l N 0.19 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Ethylbenzene 1 U µg/l N 0.23 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Isopropylbenzene 1 U µg/l N 0.16 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC m,p‐Xylenes 2 U µg/l N 0.41 2

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Methyl Acetate 1 U µg/l N 0.14 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Methyl ethyl ketone 5 U µg/l N 0.55 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Methyl isobutyl ketone 5 U µg/l N 0.53 5

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Methyl tert‐butyl ether 1 U µg/l N 0.18 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Methylcyclohexane 1 U µg/l N 0.26 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Methylene Chloride 1 U µg/l N 0.15 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC o‐Xylene 1 U µg/l N 0.11 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Styrene 1 U µg/l N 0.097 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Tetrachloroethene 0.16 J µg/l Y 0.15 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Toluene 1 U µg/l N 0.15 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC trans‐1,2‐Dichloroethene 1 U µg/l N 0.17 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC trans‐1,3‐Dichloropropene 1 U µg/l N 0.15 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Trichloroethene 0.19 J µg/l Y 0.14 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Trichlorofluoromethane 1 U µg/l N 0.2 1

SW SW MSW‐24 MQW‐24U‐09166 6/15/2009 N VOC Vinyl Chloride 1 U µg/l N 0.23 1

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N GenChem Cyanide 10 U µg/l N 1.6 10


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N Metal Antimony 2 U µg/l N 0.13 2

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N Metal Arsenic 2.7 J µg/l Y 0.4 5

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N Metal Barium 97.1 = µg/l Y 0.19 1





SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N Metal Cobalt 0.38 J µg/l Y 0.058 1


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N Metal Iron 554 = µg/l Y 26 50


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N Metal Magnesium 220000 = µg/l Y 17 1000



SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N Metal Methyl Mercury 0.00051 J µg/l Y 0.0001 0.0005

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N Metal Nickel 3 = µg/l Y 0.2 2




SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N Metal Sodium 1860000 = µg/l Y 138 20000



SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N Metal Zinc 20 U µg/l N 2.3 20




Page 190 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PCB Aroclor‐1248 0.21 J µg/l Y 0.0023 0.0099





SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PCB_TOT Total Aroclors 0.267 = µg/l Y 0.0025 0.0099



SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PEST 4‐4’‐DDT 0.036 = µg/l Y 0.0074 0.013

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PEST Aldrin 0.013 U µg/l N 0.0083 0.013




SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PEST BHC (delta) 0.013 U µg/l N 0.0044 0.013

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PEST BHC (gamma) 0.013 U µg/l N 0.008 0.013

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PEST Chlordane (beta) 0.013 U µg/l N 0.0096 0.013



SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PEST Endosulfan II 0.013 U µg/l N 0.0098 0.013





SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PEST Heptachlor 0.013 U µg/l N 0.0099 0.013

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PEST Heptachlor epoxide 0.013 U µg/l N 0.0097 0.013

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N PEST Methoxychlor 0.025 UJ µg/l N 0.0091 0.025


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 1,1'‐Biphenyl 0.98 U µg/l N 0.015 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 2,4,5‐Trichlorophenol 0.98 U µg/l N 0.015 0.98



SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 2,4‐Dimethylphenol 0.98 U µg/l N 0.0078 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 2,4‐Dinitrophenol 4.9 U µg/l N 0.6 4.9

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 2,4‐Dinitrotoluene 0.98 U µg/l N 0.016 0.98


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 2‐3‐4‐6‐Tetrachlorophenol 0.98 U µg/l N 0.1 0.98


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 2‐Chlorophenol 0.98 U µg/l N 0.021 0.98


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 2‐Methylphenol 0.98 U µg/l N 0.014 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 2‐Nitroaniline 4.9 U µg/l N 0.016 4.9

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 2‐Nitrophenol 0.98 U µg/l N 0.014 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 3,3‐Dichlorobenzidine 0.98 U µg/l N 0.035 0.98


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 4,6‐Dinitro‐2‐methylphenol 4.9 U µg/l N 0.76 4.9

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 4‐Bromophenyl phenyl ether 0.98 U µg/l N 0.018 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 4‐Chloro‐3‐methylphenol 0.98 U µg/l N 0.025 0.98

Page 191 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 4‐Chloroaniline 0.98 U µg/l N 0.11 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC 4‐Chlorophenyl phenyl ether 0.98 U µg/l N 0.01 0.98




SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Acenaphthene 0.2 U µg/l N 0.014 0.2


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Acetophenone 0.98 U µg/l N 0.022 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Anthracene 0.02 J µg/l Y 0.0084 0.2

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Atrazine 0.98 U µg/l N 0.02 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Benzaldehyde 0.79 J µg/l Y 0.049 0.98






SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Bis(2‐chloroethoxy)methane 0.98 U µg/l N 0.013 0.98



SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Bis(2‐ethylhexyl)phthalate 0.98 U µg/l N 0.045 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Butyl benzyl phthalate 0.98 U µg/l N 0.3 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Caprolactam 4.9 U µg/l N 0.71 4.9SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Carbazole 0.014 J µg/l Y 0.013 0.2


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Dibenz(a,h)anthracene 0.2 U µg/l N 0.013 0.2SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Dibenzofuran 0.98 U µg/l N 0.018 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Diethyl phthalate 0.98 U µg/l N 0.044 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Dimethyl phthalate 0.98 U µg/l N 0.014 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Di‐n‐butyl phthalate 0.98 U µg/l N 0.029 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Di‐n‐octyl phthalate 0.98 U µg/l N 0.015 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Fluoranthene 0.2 U µg/l N 0.0098 0.2

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Fluorene 0.027 J µg/l Y 0.0097 0.2


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Hexachlorobutadiene 0.2 UJ µg/l N 0.012 0.2

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Hexachlorocyclopentadiene 0.98 UJ µg/l N 0.011 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Hexachloroethane 0.98 U µg/l N 0.0075 0.98


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Isophorone 0.98 U µg/l N 0.028 0.98





SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Pentachlorophenol 0.98 U µg/l N 0.18 0.98

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Phenanthrene 0.2 U µg/l N 0.028 0.2


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N SVOC Pyrene 0.2 U µg/l N 0.011 0.2



Page 192 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit




SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N VOC 1,1‐Dichloroethene 1 U µg/l N 0.3 1




SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N VOC 1,2‐Dichlorobenzene 0.82 J µg/l Y 0.15 1






SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N VOC 1‐2‐4‐5‐Tetrachlorobenzene 0.98 U µg/l N 0.097 0.98


SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N VOC Acetone 5 U µg/l N 2.5 5

SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N VOC Benzene 0.14 J µg/l Y 0.11 1







SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N VOC Chlorobenzene 1.9 = µg/l Y 0.14 1




SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N VOC cis‐1,2‐Dichloroethene 0.38 J µg/l Y 0.24 1

















SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N VOC Toluene 1 U µg/l N 0.15 1



SW SW MSW‐24 MQW‐24U‐09264 9/21/2009 N VOC Trichloroethene 0.67 J µg/l Y 0.14 1

Page 193 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N GenChem Cyanide 1.6 J µg/l Y 1.6 10


SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N Metal Antimony 0.42 J µg/l Y 0.13 2








SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N Metal Copper 5 J µg/l Y 0.29 2






SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N Metal Methyl Mercury 0.0015 = µg/l Y 0.00005 0.00025


SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N Metal Potassium 36700 J µg/l Y 8.3 1000






SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N Metal Zinc 29.3 J µg/l Y 2.3 20










SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PCB_TOT Total Aroclors 0.061 = µg/l Y 0.0025 0.0099



SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PEST 4‐4’‐DDT 0.0037 J µg/l Y 0.0015 0.0026

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PEST Aldrin 0.0042 J µg/l Y 0.0016 0.0026




SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PEST BHC (delta) 0.0026 U µg/l N 0.00075 0.0026

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PEST BHC (gamma) 0.0036 J µg/l Y 0.0016 0.0026

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PEST Chlordane (beta) 0.0057 = µg/l Y 0.0019 0.0026


Page 194 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PEST Endosulfan II 0.0052 J µg/l Y 0.0019 0.0026


SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PEST Endrin 0.0039 J µg/l Y 0.0019 0.0026



SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PEST Heptachlor 0.009 = µg/l Y 0.002 0.0026

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PEST Heptachlor epoxide 0.0034 J µg/l Y 0.0019 0.0026

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N PEST Methoxychlor 0.005 U µg/l N 0.0018 0.005














SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC 2‐Methylphenol 0.98 U µg/l N 0.014 0.98SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC 2‐Nitroaniline 4.9 U µg/l N 0.016 4.9


SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC 3,3‐Dichlorobenzidine 0.98 U µg/l N 0.035 0.98SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC 3‐Nitroaniline 4.9 U µg/l N 0.025 4.9












SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Anthracene 0.2 U µg/l N 0.0084 0.2

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Atrazine 0.98 UJ µg/l N 0.02 0.98

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Benzaldehyde 0.98 U µg/l N 0.049 0.98








Page 195 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Bis(2‐ethylhexyl)phthalate 0.98 U µg/l N 0.045 0.98

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Butyl benzyl phthalate 0.98 U µg/l N 0.3 0.98

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Caprolactam 4.9 U µg/l N 0.71 4.9

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Carbazole 0.2 U µg/l N 0.013 0.2


SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Dibenz(a,h)anthracene 0.2 U µg/l N 0.013 0.2

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Dibenzofuran 0.98 U µg/l N 0.018 0.98



SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Di‐n‐butyl phthalate 0.18 J µg/l Y 0.029 0.98

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Di‐n‐octyl phthalate 0.98 U µg/l N 0.015 0.98

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Fluoranthene 0.2 U µg/l N 0.0098 0.2

SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Fluorene 0.2 U µg/l N 0.0097 0.2












SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Phenanthrene 0.2 U µg/l N 0.028 0.2


SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N SVOC Pyrene 0.035 J µg/l Y 0.011 0.2







SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N VOC 1,2,4‐Trichlorobenzene 1 UJ µg/l N 0.27 1



SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N VOC 1,2‐Dichlorobenzene 1.1 = µg/l Y 0.15 1





SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N VOC 1‐2‐3‐Trichlorobenzene 1 UJ µg/l N 0.15 1



SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N VOC Acetone 3.9 J µg/l Y 2.5 5



Page 196 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit










SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N VOC cis‐1,2‐Dichloroethene 1.2 = µg/l Y 0.24 1












SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N VOC Methylcyclohexane 1 UJ µg/l N 0.26 1





SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N VOC Toluene 0.18 J µg/l Y 0.15 1



SW SW MSW‐24 MQW‐24U‐09341 12/7/2009 N VOC Trichloroethene 1.2 = µg/l Y 0.14 1



SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N GenChem Cyanide 3.3 J µg/l Y 1.5 10


SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N Metal Antimony 0.34 J µg/l Y 0.13 2












SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N Metal Manganese 476 J µg/l Y 0.83 1

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N Metal Mercury 0.263 J µg/l Y 0.0048 0.02

Page 197 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N Metal Methyl Mercury 0.0017 = µg/l Y 0.0001 0.0005








SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N Metal Zinc 22 J µg/l Y 2.3 20










SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PCB_TOT Total Aroclors 0 U µg/l N 0.0024 0.0096


SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST 4‐4’‐DDE 0.0013 J µg/l Y 0.00076 0.0012

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST 4‐4’‐DDT 0.0012 UJ µg/l N 0.00071 0.0012



SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST BHC (beta) 0.0026 NJ µg/l Y 0.00096 0.0012

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST BHC (gamma) 0.0053 J µg/l Y 0.00077 0.0012SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST Chlordane (beta) 0.0012 U µg/l N 0.00092 0.0012


SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST Endosulfan I 0.0012 U µg/l N 0.0009 0.0012SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST Endosulfan II 0.0012 U µg/l N 0.00094 0.0012

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST Endosulfan sulfate 0.0012 UJ µg/l N 0.00055 0.0012


SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST Endrin aldehyde 0.0012 UJ µg/l N 0.00086 0.0012

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST Endrin ketone 0.0012 UJ µg/l N 0.00088 0.0012

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST Heptachlor epoxide 0.0034 = µg/l Y 0.00093 0.0012

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N PEST Methoxychlor 0.0024 UJ µg/l N 0.00087 0.0024













Page 198 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit





SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC 3,3‐Dichlorobenzidine 1.1 U µg/l N 0.12 1.1









SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC 4‐Nitrophenol 5.4 UJ µg/l N 0.66 5.4




SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Anthracene 0.29 = µg/l Y 0.017 0.22

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Atrazine 1.1 U µg/l N 0.097 1.1

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Benzaldehyde 0.91 J µg/l Y 0.16 1.1

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Benzo(a)anthracene 3.2 = µg/l Y 0.016 0.22

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Benzo(a)pyrene 2.4 = µg/l Y 0.015 0.22

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Benzo(b)fluoranthene 3 = µg/l Y 0.017 0.22

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Benzo(g,h,i)perylene 3.6 = µg/l Y 0.016 0.22

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Benzo(k)fluoranthene 3.7 = µg/l Y 0.06 0.22




SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Bis(2‐ethylhexyl)phthalate 1.5 = µg/l Y 0.87 1.1

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Butyl benzyl phthalate 0.33 J µg/l Y 0.16 1.1

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Caprolactam 5.4 U µg/l N 1.3 5.4

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Carbazole 0.034 J µg/l Y 0.017 0.22

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Chrysene 3.1 = µg/l Y 0.015 0.22

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Dibenz(a,h)anthracene 3.8 = µg/l Y 0.017 0.22

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Dibenzofuran 1.1 U µg/l N 0.067 1.1



SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Di‐n‐butyl phthalate 0.14 J µg/l Y 0.14 1.1

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Di‐n‐octyl phthalate 1.4 = µg/l Y 0.23 1.1

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Fluoranthene 0.77 = µg/l Y 0.018 0.22

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Fluorene 0.22 U µg/l N 0.024 0.22





SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Indeno(1,2,3‐cd)pyrene 3.7 = µg/l Y 0.022 0.22


SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Naphthalene 0.033 J µg/l Y 0.015 0.22

Page 199 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit





SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Phenanthrene 0.15 J µg/l Y 0.047 0.22


SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N SVOC Pyrene 0.77 = µg/l Y 0.017 0.22










SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC 1,2‐Dichlorobenzene 4.7 = µg/l Y 0.15 1




SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC 1,4‐Dichlorobenzene 0.25 J µg/l Y 0.21 1




SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC Acetone 3.4 J µg/l Y 2.5 5





SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC Bromomethane 1 UJ µg/l N 0.31 1




SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC Chloroethane 1 UJ µg/l N 0.21 1

SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC Chloroform 0.2 J µg/l Y 0.17 1


SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC cis‐1,2‐Dichloroethene 1.6 = µg/l Y 0.24 1












Page 200 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC Methylene Chloride 1 UJ µg/l N 0.15 1




SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC Toluene 0.2 J µg/l Y 0.15 1



SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC Trichloroethene 5 = µg/l Y 0.14 1


SW SW MSW‐24 MQW‐24U‐10125 5/5/2010 N VOC Vinyl Chloride 0.29 J µg/l Y 0.23 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Aluminum, Dissolved 200 U µg/l N 200 200

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Antimony, Dissolved 6 U µg/l N 6 6

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Arsenic, Dissolved 3.8 U µg/l N 3 3

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Barium, Dissolved 200 U µg/l N 200 200

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Beryllium, Dissolved 1 U µg/l N 1 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Cadmium, Dissolved 3 U µg/l N 3 3

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Calcium, Dissolved 119000 = µg/l Y 5000 5000

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Chromium, Dissolved 10 U µg/l N 10 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Cobalt, Dissolved 50 U µg/l N 50 50

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Copper, Dissolved 10 U µg/l N 10 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Iron, Dissolved 100 U µg/l N 100 100

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Lead, Dissolved 3 U µg/l N 3 3

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Magnesium, Dissolved 244000 = µg/l Y 5000 5000

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Manganese, Dissolved 549 = µg/l Y 15 15

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Mercury, Dissolved 0.52 U µg/l N 0.2 0.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Nickel, Dissolved 10 U µg/l N 10 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Potassium, Dissolved 87100 = µg/l Y 10000 10000

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Selenium, Dissolved 10 U µg/l N 10 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Silver, Dissolved 10 U µg/l N 10 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Sodium, Dissolved 1900000 = µg/l Y 50000 50000

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Thallium, Dissolved 2 U µg/l N 2 2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Vanadium, Dissolved 50 U µg/l N 50 50

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N DissMetal Zinc, Dissolved 20 U µg/l N 20 20

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Aluminum 412 = µg/l Y 200 200

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Antimony 6 U µg/l N 6 6

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Arsenic 3.5 U µg/l N 3 3

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Barium 200 U µg/l N 200 200

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Beryllium 1 U µg/l N 1 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Cadmium 3 U µg/l N 3 3

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Calcium 106000 = µg/l Y 5000 5000

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Chromium 15.5 = µg/l Y 10 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Cobalt 50 U µg/l N 50 50

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Copper 40.4 = µg/l Y 10 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Iron 1520 = µg/l Y 100 100

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Lead 5.5 = µg/l Y 3 3

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Magnesium 214000 = µg/l Y 5000 5000

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Manganese 550 = µg/l Y 15 15

Page 201 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Mercury 1.7 U µg/l N 0.2 0.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Nickel 10 U µg/l N 10 10SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Potassium 76400 = µg/l Y 10000 10000

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Selenium 10 U µg/l N 10 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Silver 10 U µg/l N 10 10SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Sodium 1700000 = µg/l Y 50000 50000

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Thallium 2 U µg/l N 2 2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Vanadium 50 U µg/l N 50 50

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N Metal Zinc 35.8 = µg/l Y 20 20

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N PCB Aroclor‐1016 0.54 U µg/L N 0.32 0.54







SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N PCB Aroclor‐1262 0.54 U µg/l N 0.11 0.54


SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N PCB_TOT Total Aroclors 0 U µg/L N 0.32 0.54

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 1,1'‐Biphenyl 1.1 U µg/l N 0.46 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2,4,5‐Trichlorophenol 5.5 U µg/l N 1.5 5.5


SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2,4‐Dichlorophenol 5.5 U µg/l N 1.3 5.5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2,4‐Dimethylphenol 5.5 U µg/l N 1.8 5.5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2,4‐Dinitrophenol 22 U µg/l N 0.81 22

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2,4‐Dinitrotoluene 2.2 U µg/l N 0.24 2.2


SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2‐Chloronaphthalene 2.2 U µg/l N 0.46 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2‐Chlorophenol 5.5 U µg/l N 1.2 5.5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2‐Methylnaphthalene 1.1 U µg/l N 0.72 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2‐Methylphenol 2.2 U µg/l N 1.2 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2‐Nitroaniline 5.5 U µg/l N 0.26 5.5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 2‐Nitrophenol 5.5 U µg/l N 1.4 5.5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 3&4‐Methylphenol 2.2 U µg/l N 1.1 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 3,3‐Dichlorobenzidine 5.5 U µg/l N 0.32 5.5


SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 22 U µg/l N 0.56 22

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 4‐Bromophenyl phenyl ether 2.2 U µg/l N 0.38 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 4‐Chloro‐3‐methylphenol 5.5 U µg/l N 1.2 5.5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 4‐Chloroaniline 5.5 U µg/l N 0.28 5.5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 4‐Chlorophenyl phenyl ether 2.2 U µg/l N 0.39 2.2


SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC 4‐Nitrophenol 11 U µg/l N 0.91 11

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Acenaphthene 1.1 U µg/l N 0.4 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Acenaphthylene 1.1 U µg/l N 0.3 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Acetophenone 2.2 U µg/l N 0.44 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Anthracene 1.1 U µg/l N 0.18 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Atrazine 5.5 U µg/l N 0.43 5.5

Page 202 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Benzaldehyde 5.5 U µg/l N 0.44 5.5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Benzo(a)anthracene 1.1 U µg/l N 0.13 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Benzo(a)pyrene 1.1 U µg/l N 0.1 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Benzo(b)fluoranthene 1.1 U µg/l N 0.27 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Benzo(g,h,i)perylene 1.1 U µg/l N 0.13 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Benzo(k)fluoranthene 1.1 U µg/l N 0.41 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Bis(2‐chloroethoxy)methane 2.2 U µg/l N 0.27 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Bis(2‐chloroethyl)ether 2.2 U µg/l N 0.34 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC bis(2‐Chloroisopropyl)ether 2.2 U µg/l N 0.43 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Bis(2‐ethylhexyl)phthalate 2.2 U µg/l N 0.36 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Butyl benzyl phthalate 2.2 U µg/l N 0.28 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Caprolactam 2.2 U µg/l N 0.21 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Carbazole 1.1 U µg/l N 0.18 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Chrysene 1.1 U µg/l N 0.12 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Dibenz(a,h)anthracene 1.1 U µg/l N 0.17 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Dibenzofuran 5.5 U µg/l N 0.33 5.5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Diethyl phthalate 2.2 U µg/l N 0.18 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Dimethyl phthalate 2.2 U µg/l N 0.25 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Di‐n‐butyl phthalate 2.2 U µg/l N 0.21 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Di‐n‐octyl phthalate 2.2 U µg/l N 0.43 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Fluoranthene 1.1 U µg/l N 0.19 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Fluorene 1.1 U µg/l N 0.29 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Hexachlorobenzene 1.1 U µg/l N 0.29 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Hexachlorobutadiene 1.1 U µg/l N 0.14 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Hexachlorocyclopentadiene 22 U µg/l N 0.27 22

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Hexachloroethane 2.2 U µg/l N 0.23 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Indeno(1,2,3‐cd)pyrene 1.1 U µg/l N 0.14 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Isophorone 2.2 U µg/l N 0.27 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Naphthalene 1.1 U µg/l N 0.47 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Nitrobenzene 2.2 U µg/l N 0.28 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 2.2 U µg/l N 0.48 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC N‐Nitrosodiphenylamine 5.5 U µg/l N 0.24 5.5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Pentachlorophenol 11 U µg/l N 0.88 11

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Phenanthrene 1.1 U µg/l N 0.23 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Phenol 2.2 U µg/l N 0.63 2.2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N SVOC Pyrene 1.1 U µg/l N 0.17 1.1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 1,1,1‐Trichloroethane 1 U µg/l N 0.26 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 1,1,2,2‐Tetrachloroethane 1 U µg/l N 0.24 1


SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 5 U µg/l N 0.38 5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 1,1‐Dichloroethane 1 U µg/l N 0.29 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 1,1‐Dichloroethene 1 U µg/l N 0.4 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 1,2,4‐Trichlorobenzene 5 U µg/l N 0.56 5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 10 U µg/l N 1.1 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 1,2‐Dibromoethane 2 U µg/l N 0.39 2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 1,2‐Dichlorobenzene 1 U µg/l N 0.26 1


SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 1,2‐Dichloropropane 1 U µg/l N 0.27 1

Page 203 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC 2‐Hexanone 5 U µg/l N 1.4 5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Acetone 10 U µg/l N 2.9 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Benzene 1 U µg/l N 0.23 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Bromodichloromethane 1 U µg/l N 0.22 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Bromoform 4 U µg/l N 0.23 4

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Bromomethane 2 U µg/l N 0.3 2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Carbon Disulfide 2 U µg/l N 0.74 2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Carbon Tetrachloride 1 U µg/l N 0.26 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Chlorobenzene 1 U µg/l N 0.39 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Chloroethane 1 U µg/l N 0.37 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Chloroform 1 U µg/l N 0.23 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Chloromethane 1 U µg/l N 0.29 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC cis‐1,2‐Dichloroethene 0.26 J µg/l Y 0.22 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC cis‐1,3‐Dichloropropene 1 U µg/l N 0.25 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Cyclohexane 5 U µg/l N 1.9 5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Dibromochloromethane 1 U µg/l N 0.22 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Dichlorodifluoromethane 5 U µg/l N 0.92 5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Ethylbenzene 1 U µg/l N 0.27 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Isopropylbenzene 2 U µg/l N 0.57 2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Methyl Acetate 5 U µg/l N 1.5 5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Methyl ethyl ketone 10 U µg/l N 1.6 10

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Methyl isobutyl ketone 5 U µg/l N 0.86 5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Methyl tert‐butyl ether 1 U µg/l N 0.23 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Methylcyclohexane 5 U µg/l N 0.35 5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Methylene Chloride 2 U µg/l N 0.3 2

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Styrene 5 U µg/l N 0.58 5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Tetrachloroethene 1 U µg/l N 0.27 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Toluene 1 U µg/l N 0.3 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC trans‐1,2‐Dichloroethene 1 U µg/l N 0.25 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC trans‐1,3‐Dichloropropene 1 U µg/l N 0.21 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Trichloroethene 1 U µg/l N 0.24 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Trichlorofluoromethane 5 U µg/l N 0.54 5

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Vinyl Chloride 1 U µg/l N 0.44 1

SW SW SL03 062910‐SW‐SL03‐FLOOD 6/29/2010 N VOC Xylenes, Total 1 U µg/l N 0.25 1



SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N DissMetal Arsenic, Dissolved 3.8 = µg/l Y 3 3








SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N DissMetal Iron, Dissolved 231 = µg/l Y 100 100


Page 204 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit














SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N Metal Arsenic 3.9 = µg/l Y 3 3












SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N Metal Mercury 1.4 U µg/l N 0.2 0.2SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N Metal Nickel 10 U µg/l N 10 10

SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N Metal Potassium 95500 = µg/l Y 10000 10000


SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N Metal Silver 10 U µg/l N 10 10

SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N Metal Sodium 1920000 = µg/l Y 50000 50000


















Page 205 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit


SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N SVOC 2,4‐Dinitrophenol 21 U µg/l N 0.78 21



SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N SVOC 2‐Chloronaphthalene 2.1 U µg/l N 0.44 2.1

SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N SVOC 2‐Chlorophenol 5.3 U µg/l N 1.1 5.3SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N SVOC 2‐Methylnaphthalene 1.1 U µg/l N 0.69 1.1



















SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N SVOC Benzaldehyde 5.3 UJ µg/l N 0.43 5.3























Page 206 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit








































SW SW SL07 063010‐SW‐SL07‐FLOOD 6/30/2010 N VOC cis‐1,2‐Dichloroethene 1 U µg/l N 0.22 1









Page 207 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit
















SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N DissMetal Arsenic, Dissolved 3.5 = µg/l Y 3 3








SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N DissMetal Iron, Dissolved 224 = µg/l Y 100 100















SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N Metal Arsenic 3.7 = µg/l Y 3 3










Page 208 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N Metal Mercury 1.7 U µg/l N 0.2 0.2

SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N Metal Nickel 10 U µg/l N 10 10

SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N Metal Potassium 94400 = µg/l Y 10000 10000


SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N Metal Silver 47 J µg/l Y 10 10

SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N Metal Sodium 1960000 = µg/l Y 50000 50000



















SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N SVOC 2,4‐Dinitrophenol 22 U µg/l N 0.79 22SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N SVOC 2,4‐Dinitrotoluene 2.2 U µg/l N 0.24 2.2


SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N SVOC 2‐Chloronaphthalene 2.2 U µg/l N 0.45 2.2SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N SVOC 2‐Chlorophenol 5.4 U µg/l N 1.2 5.4

SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N SVOC 2‐Methylnaphthalene 1.1 U µg/l N 0.71 1.1

















Page 209 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit



SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N SVOC Benzaldehyde 5.4 UJ µg/l N 0.43 5.4














































Page 210 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

















SW SW SL08 063010‐SW‐SL08‐FLOOD 6/30/2010 N VOC cis‐1,2‐Dichloroethene 1 U µg/l N 0.22 1






















SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Aluminum, Dissolved 200 U µg/l N 200 200

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Antimony, Dissolved 6 U µg/l N 6 6

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Arsenic, Dissolved 3 U µg/l N 3 3

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Barium, Dissolved 200 U µg/l N 200 200

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Beryllium, Dissolved 1 U µg/l N 1 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Cadmium, Dissolved 3 U µg/l N 3 3

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Calcium, Dissolved 109000 J µg/l Y 5000 5000

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Chromium, Dissolved 10 U µg/l N 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Cobalt, Dissolved 50 U µg/l N 50 50

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Copper, Dissolved 10 U µg/l N 10 10

Page 211 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Iron, Dissolved 594 = µg/l Y 100 100

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Lead, Dissolved 3 U µg/l N 3 3

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Magnesium, Dissolved 211000 J µg/l Y 5000 5000

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Manganese, Dissolved 6500 = µg/l Y 15 15

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Mercury, Dissolved 0.2 U µg/l N 0.2 0.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Nickel, Dissolved 10 U µg/l N 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Potassium, Dissolved 73700 J µg/l Y 10000 10000

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Selenium, Dissolved 10 U µg/l N 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Silver, Dissolved 10 U µg/l N 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Sodium, Dissolved 1410000 J µg/l Y 20000 20000

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Thallium, Dissolved 10 U µg/l N 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Vanadium, Dissolved 50 U µg/l N 50 50

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N DissMetal Zinc, Dissolved 20 U µg/l N 20 20

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Aluminum 2640 = µg/l Y 200 200

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Antimony 6 U µg/l N 6 6

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Arsenic 11.3 = µg/l Y 3 3

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Barium 200 U µg/l N 200 200

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Beryllium 1 U µg/l N 1 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Cadmium 3 U µg/l N 3 3

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Calcium 98500 J µg/l Y 5000 5000

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Chromium 114 = µg/l Y 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Cobalt 50 U µg/l N 50 50

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Copper 71.9 = µg/l Y 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Iron 16500 = µg/l Y 100 100

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Lead 32.6 = µg/l Y 3 3

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Magnesium 184000 J µg/l Y 5000 5000

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Manganese 7040 = µg/l Y 15 15

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Mercury 5.6 = µg/l Y 0.4 0.4

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Nickel 11 = µg/l Y 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Potassium 63200 J µg/l Y 10000 10000

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Selenium 10 U µg/l N 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Silver 10 U µg/l N 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Sodium 867000 J µg/l Y 10000 10000

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Thallium 10 U µg/l N 10 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Vanadium 50 U µg/l N 50 50

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N Metal Zinc 127 = µg/l Y 20 20

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N PCB Aroclor‐1016 0.5 U µg/L N 0.3 0.5







SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N PCB_TOT Total Aroclors 0 U µg/L N 0.3 0.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 1,1'‐Biphenyl 1.1 U µg/l N 0.46 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2,4,5‐Trichlorophenol 5.5 U µg/l N 1.5 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2,4,6‐Trichlorophenol 5.5 U µg/l N 1.3 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2,4‐Dichlorophenol 5.5 U µg/l N 1.3 5.5

Page 212 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2,4‐Dimethylphenol 5.5 U µg/l N 1.8 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2,4‐Dinitrophenol 22 U µg/l N 0.81 22

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2,4‐Dinitrotoluene 2.2 U µg/l N 0.24 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2,6‐Dinitrotoluene 2.2 U µg/l N 0.36 2.2SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2‐Chloronaphthalene 2.2 U µg/l N 0.46 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2‐Chlorophenol 5.5 U µg/l N 1.2 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2‐Methylnaphthalene 1.1 U µg/l N 0.72 1.1SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2‐Methylphenol 2.2 U µg/l N 1.2 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2‐Nitroaniline 5.5 U µg/l N 0.26 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 2‐Nitrophenol 5.5 U µg/l N 1.4 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 3&4‐Methylphenol 2.2 U µg/l N 1.1 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 3,3‐Dichlorobenzidine 5.5 U µg/l N 0.32 5.5


SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 4,6‐Dinitro‐2‐methylphenol 22 U µg/l N 0.56 22

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 4‐Bromophenyl phenyl ether 2.2 U µg/l N 0.38 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 4‐Chloro‐3‐methylphenol 5.5 U µg/l N 1.2 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 4‐Chloroaniline 5.5 U µg/l N 0.28 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 4‐Chlorophenyl phenyl ether 2.2 U µg/l N 0.39 2.2


SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC 4‐Nitrophenol 11 UJ µg/l N 0.91 11

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Acenaphthene 1.1 U µg/l N 0.4 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Acenaphthylene 1.1 U µg/l N 0.3 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Acetophenone 2.2 U µg/l N 0.44 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Anthracene 1.1 U µg/l N 0.18 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Atrazine 5.5 U µg/l N 0.43 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Benzaldehyde 5.5 U µg/l N 0.44 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Benzo(a)anthracene 1.1 U µg/l N 0.13 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Benzo(a)pyrene 1.1 U µg/l N 0.1 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Benzo(b)fluoranthene 1.1 U µg/l N 0.27 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Benzo(g,h,i)perylene 1.1 U µg/l N 0.13 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Benzo(k)fluoranthene 1.1 U µg/l N 0.42 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Bis(2‐chloroethoxy)methane 2.2 U µg/l N 0.27 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Bis(2‐chloroethyl)ether 2.2 U µg/l N 0.34 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC bis(2‐Chloroisopropyl)ether 2.2 U µg/l N 0.43 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Bis(2‐ethylhexyl)phthalate 2.2 U µg/l N 0.36 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Butyl benzyl phthalate 2.2 U µg/l N 0.28 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Caprolactam 2.2 U µg/l N 0.21 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Carbazole 1.1 U µg/l N 0.18 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Chrysene 1.1 U µg/l N 0.12 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Dibenz(a,h)anthracene 1.1 U µg/l N 0.17 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Dibenzofuran 5.5 U µg/l N 0.33 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Diethyl phthalate 2.2 U µg/l N 0.18 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Dimethyl phthalate 2.2 U µg/l N 0.25 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Di‐n‐butyl phthalate 2.2 U µg/l N 0.21 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Di‐n‐octyl phthalate 2.2 U µg/l N 0.44 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Fluoranthene 1.1 U µg/l N 0.19 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Fluorene 1.1 U µg/l N 0.29 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Hexachlorobenzene 1.1 U µg/l N 0.29 1.1

Page 213 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Hexachlorobutadiene 1.1 U µg/l N 0.14 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Hexachlorocyclopentadiene 22 U µg/l N 0.27 22

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Hexachloroethane 2.2 U µg/l N 0.23 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Indeno(1,2,3‐cd)pyrene 1.1 U µg/l N 0.14 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Isophorone 2.2 U µg/l N 0.27 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Naphthalene 1.1 U µg/l N 0.47 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Nitrobenzene 2.2 U µg/l N 0.28 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC N‐Nitroso‐di‐n‐propylamine 2.2 U µg/l N 0.48 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC N‐Nitrosodiphenylamine 5.5 U µg/l N 0.24 5.5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Pentachlorophenol 11 U µg/l N 0.88 11

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Phenanthrene 1.1 U µg/l N 0.23 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Phenol 2.2 U µg/l N 0.64 2.2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N SVOC Pyrene 1.1 U µg/l N 0.17 1.1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,1,1‐Trichloroethane 1 U µg/l N 0.26 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,1,2,2‐Tetrachloroethane 1 U µg/l N 0.24 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,1,2‐Trichloroethane 1 U µg/l N 0.23 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,1,2‐Trichlorotrifluoroethane 5 U µg/l N 0.38 5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,1‐Dichloroethane 1 U µg/l N 0.29 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,1‐Dichloroethene 1 U µg/l N 0.4 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,2,4‐Trichlorobenzene 5 U µg/l N 0.56 5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,2‐Dibromo‐3‐chloropropane 10 U µg/l N 1.1 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,2‐Dibromoethane 2 U µg/l N 0.39 2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,2‐Dichlorobenzene 0.29 J µg/l Y 0.26 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,2‐Dichloroethane 1 U µg/l N 0.33 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,2‐Dichloropropane 1 U µg/l N 0.27 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,3‐Dichlorobenzene 1 U µg/l N 0.25 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 1,4‐Dichlorobenzene 1 U µg/l N 0.28 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC 2‐Hexanone 5 U µg/l N 1.4 5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Acetone 10 U µg/l N 2.9 10

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Benzene 1 U µg/l N 0.23 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Bromodichloromethane 1 U µg/l N 0.22 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Bromoform 4 U µg/l N 0.23 4

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Bromomethane 2 U µg/l N 0.3 2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Carbon Disulfide 2 U µg/l N 0.74 2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Carbon Tetrachloride 1 U µg/l N 0.26 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Chlorobenzene 1 U µg/l N 0.39 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Chloroethane 1 U µg/l N 0.37 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Chloroform 1 U µg/l N 0.23 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Chloromethane 1 U µg/l N 0.29 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC cis‐1,2‐Dichloroethene 1 U µg/l N 0.22 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC cis‐1,3‐Dichloropropene 1 U µg/l N 0.25 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Cyclohexane 5 U µg/l N 1.9 5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Dibromochloromethane 1 U µg/l N 0.22 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Dichlorodifluoromethane 5 U µg/l N 0.92 5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Ethylbenzene 1 U µg/l N 0.27 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Isopropylbenzene 2 U µg/l N 0.57 2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Methyl Acetate 5 U µg/l N 1.5 5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Methyl ethyl ketone 10 UJ µg/l N 1.6 10

Page 214 of 215

Attachment C




Collection

Date

Sample

Type

Chemical


Proj

Qual Units Detect

Detection

Limit

Reporting

Limit

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Methyl isobutyl ketone 5 U µg/l N 0.86 5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Methyl tert‐butyl ether 1 U µg/l N 0.23 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Methylcyclohexane 5 U µg/l N 0.35 5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Methylene Chloride 2 U µg/l N 0.3 2

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Styrene 5 U µg/l N 0.58 5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Tetrachloroethene 1 U µg/l N 0.27 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Toluene 1 U µg/l N 0.3 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC trans‐1,2‐Dichloroethene 1 U µg/l N 0.25 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC trans‐1,3‐Dichloropropene 1 U µg/l N 0.21 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Trichloroethene 1 U µg/l N 0.24 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Trichlorofluoromethane 5 U µg/l N 0.54 5

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Vinyl Chloride 1 U µg/l N 0.44 1

SW SW SW06 100410‐SW‐SL06‐EBB 10/4/2010 N VOC Xylenes, Total 1 U µg/l N 0.25 1

Notes:1 Data groupings are defined on Table 1 of Attachment B.

PCB = Polychlorinated Biphenyl

Pest = Pesticide

SD = Sediment

SVOC = Semi‐volatile Organic Compound

SW = Surface Water

VOC = Volatile Organic Compound

Qualifiers:

B = compound also detected in associated blank

N = presumptive evidence of a compound

J = compound was detected below the reporting limit in the sample

U = compound not detected

Page 215 of 215

Attachment D Fish Screening Levels

Attachment DFish Screening Levels - Adult Input


Site-specific adult

RSL Equation Inputs for Fish

Variable ValueTR (target cancer risk) unitless 0.000001THQ (target hazard quotient) unitless 0.1AT (averaging time) 365EFres-a (exposure frequency) days/yr 27EDres (exposure duration) yr 8LT (lifetime) yr 70BWres-a (body weight) kg 80IRFres-a (fish consumption rate) mg/day 22000

Attachment DFish Screening Levels - Adult Output


Site-specific adult

Fish Screening Levels (RSL)

ca=Cancer, nc=Noncancer, ca* (Where nc SL < 100 x ca SL),ca** (Where nc SL < 10 x ca SL), max=SL exceeds ceiling limit (see User's Guide), sat=SL exceeds csat,Smax=Soil SL exceeds ceiling limit and has been substituted with the max value (see User's Guide),Ssat=Soil inhalation SL exceeds csat and has been substituted with the csat

Chemical CAS Number Mutagen?VOC

?

IngestionSF

(mg/kg-day)-1SFORef

ChronicRfD

(mg/kg-day)

ChronicRfDRef

IngestionSL

TR=1.0E-6(mg/kg)

IngestionSL

THQ=0.1(mg/kg)

ScreeningLevel

(mg/kg)TCDD, 2,3,7,8- 1746-01-6 No Yes 1.30E+05 C 7.00E-10 I 3.31E-06 3.44E-06 3.31E-06 ca**Aroclor 1254 11097-69-1 No Yes 2.00E+00 S 2.00E-05 I 2.15E-01 9.83E-02 9.83E-02 nc

Attachment DFish Screening Levels - Older Child Input


Site-specific youth


Variable ValueTR (target cancer risk) unitless 0.000001THQ (target hazard quotient) unitless 0.1AT (averaging time) 365EFres-a (exposure frequency) days/yr 27EDres (exposure duration) yr 12LT (lifetime) yr 70BWres-a (body weight) kg 50.2IRFres-a (fish consumption rate) mg/day 14700

Attachment DFish Screening Levels - Older Child Output


Site-specific youth




?

IngestionSF

(mg/kg-day)-1SFORef

ChronicRfD

(mg/kg-day)

ChronicRfDRef

IngestionSL

TR=1.0E-6(mg/kg)

IngestionSL

THQ=0.1(mg/kg)

ScreeningLevel

(mg/kg)TCDD, 2,3,7,8- 1746-01-6 No Yes 1.30E+05 C 7.00E-10 I 2.07E-06 3.23E-06 2.07E-06 ca**Aroclor 1254 11097-69-1 No Yes 2.00E+00 S 2.00E-05 I 1.35E-01 9.23E-02 9.23E-02 nc

Attachment DFish Screening Levels - Younger Child Input


Site-specific child


Variable ValueTR (target cancer risk) unitless 0.000001THQ (target hazard quotient) unitless 0.1AT (averaging time) 365EFres-a (exposure frequency) days/yr 27EDres (exposure duration) yr 6LT (lifetime) yr 70BWres-a (body weight) kg 15IRFres-a (fish consumption rate) mg/day 7300

Attachment DFish Screening Levels - Younger Child Output


Site-specific child




?

IngestionSF

(mg/kg-day)-1SFORef

ChronicRfD

(mg/kg-day)

ChronicRfDRef

IngestionSL

TR=1.0E-6(mg/kg)

IngestionSL

THQ=0.1(mg/kg)

ScreeningLevel

(mg/kg)TCDD, 2,3,7,8- 1746-01-6 No Yes 1.30E+05 C 7.00E-10 I 2.49E-06 1.94E-06 1.94E-06 ncAroclor 1254 11097-69-1 No Yes 2.00E+00 S 2.00E-05 I 1.62E-01 5.56E-02 5.56E-02 nc

Attachment E ProUCL Output

Attachment E

ProUCL Output, Version 5.0 ‐ Wetland Sediment (On‐site)


15 15

0

2.1946E-6 2.5991E-4

0.00271 2.6237E-5

6.9430E-4 1.7927E-4

2.671 3.6

0.414

0.881

0.408

0.229

5.7565E-4 7.3284E-4

6.0343E-4

1.425

0.827

0.314

0.239

0.339 0.316

7.6666E-4 8.2339E-4

10.17 9.47

2.5991E-4 4.6261E-4

3.613

0.0324 3.18

6.8120E-4 7.7386E-4

0.945

0.881

0.163

0.2295% Lilliefors Critical Value Data appear Lognormal at 5% Significance Level

Data appear Lognormal at 5% Significance Level

5% Shapiro Wilk Critical Value Data appear Lognormal at 5% Significance Level

Lilliefors Test Statistic Lilliefors Lognormal GOF Test

Lognormal GOF Test

Shapiro Wilk Test Statistic Shapiro Wilk Lognormal GOF Test

Assuming Gamma Distribution

95% Approximate Gamma UCL (use when n>=50)) 95% Adjusted Gamma UCL (use when n<50)

Adjusted Level of Significance Adjusted Chi Square Value

MLE Mean (bias corrected) MLE Sd (bias corrected)

Approximate Chi Square Value (0.05)

Theta hat (MLE) Theta star (bias corrected MLE)

nu hat (MLE) nu star (bias corrected)

Gamma Statistics

k hat (MLE) k star (bias corrected MLE)

5% K-S Critical Value Data Not Gamma Distributed at 5% Significance Level

Data Not Gamma Distributed at 5% Significance Level

5% A-D Critical Value Data Not Gamma Distributed at 5% Significance Level

K-S Test Statistic Kolmogrov-Smirnoff Gamma GOF Test

Gamma GOF Test

A-D Test Statistic Anderson-Darling Gamma GOF Test

95% Student's-t UCL 95% Adjusted-CLT UCL (Chen-1995)

95% Modified-t UCL (Johnson-1978)

Data Not Normal at 5% Significance Level

Assuming Normal Distribution

95% Normal UCL 95% UCLs (Adjusted for Skewness)

Lilliefors Test Statistic Lilliefors GOF Test

5% Lilliefors Critical Value Data Not Normal at 5% Significance Level

Normal GOF Test

Shapiro Wilk Test Statistic Shapiro Wilk GOF Test

5% Shapiro Wilk Critical Value Data Not Normal at 5% Significance Level

UCL Statistics for Data Sets with Non-Detects

General Statistics

Total Number of Observations Number of Distinct Observations

2,3,7,8-TCDD TEQ (mg/kg)

Coefficient of Variation Skewness

Maximum Median

SD Std. Error of Mean

Number of Missing Observations

Minimum Mean

Page 1 of 68

Attachment E



-13.03 -10.25

-5.91 1.948

0.00241 4.8632E-4

6.2611E-4 8.2015E-4

0.0012

5.5478E-4 5.7565E-4

5.4540E-4 0.00175

0.00177 5.9095E-4

8.0349E-4

7.9771E-4 0.00104

0.00138 0.00204

0.00204

40 39

0

1020 11425

27100 11850

6728 1064

0.589 0.297

0.954

0.94

0.0839

0.14

13217 13228

13226




5% Lilliefors Critical Value

Normal GOF Test

Lilliefors Test Statistic


5% Shapiro Wilk Critical Value Data appear Normal at 5% Significance Level

Lilliefors GOF Test

Data appear Normal at 5% Significance Level



Coefficient of Variation

Maximum

SD



Minimum Mean

Median

Std. Error of Mean

Skewness

Aluminum (mg/kg)

General Statistics

Note: Suggestions regarding the selection of a 95% UCL are provided to help the user to select the most appropriate 95% UCL.

These recommendations are based upon the results of the simulation studies summarized in Singh, Singh, and Iaci (2002)

and Singh and Singh (2003). However, simulations results will not cover all Real World data sets.

For additional insight the user may want to consult a statistician.

Suggested UCL to Use

99% Chebyshev (Mean, Sd) UCL

90% Chebyshev(Mean, Sd) UCL 95% Chebyshev(Mean, Sd) UCL

97.5% Chebyshev(Mean, Sd) UCL 99% Chebyshev(Mean, Sd) UCL

95% Hall's Bootstrap UCL 95% Percentile Bootstrap UCL

95% BCA Bootstrap UCL

95% CLT UCL 95% Jackknife UCL

95% Standard Bootstrap UCL 95% Bootstrap-t UCL

Nonparametric Distribution Free UCL Statistics

Data appear to follow a Discernible Distribution at 5% Significance Level

Nonparametric Distribution Free UCLs

95% Chebyshev (MVUE) UCL 97.5% Chebyshev (MVUE) UCL

99% Chebyshev (MVUE) UCL

Assuming Lognormal Distribution

95% H-UCL 90% Chebyshev (MVUE) UCL

Maximum of Logged Data SD of logged Data

Lognormal Statistics

Minimum of Logged Data Mean of logged Data

Page 2 of 68

Attachment E



1.16

0.759

0.167

0.141

2.037 1.901

5609 6011

162.9 152.1

11425 8287

124.6

0.044 123.6

13948 14053

0.864

0.94

0.2

0.14

6.928 9.078

10.21 0.862

17348 18346

20971 24614

31770

13175 13217

13142 13300

13367 13187

13312

14616 16062

18068 22009

13217








95% Student's-t UCL












Data Not Lognormal at 5% Significance Level






Lognormal GOF Test




5% Shapiro Wilk Critical Value Data Not Lognormal at 5% Significance Level

Lilliefors Lognormal GOF Test





Gamma Statistics







Gamma GOF Test



Page 3 of 68

Attachment E



40 33

5 35

5 30

2.2 1.3

144 35

3981 87.5%

31.14 63.09

3.2 2.026

2.236 4.999

1.839 1.76

0.56

0.762

0.469

0.396

5.227 3.932

22.23 12.49

11.85 12.42

11.69 90.4

17.02 22.37

29.78 44.35

1.143

0.724

0.481

0.375

0.41 0.297

75.98 104.8

4.098 2.973

31.14 57.11

0.0553 4.421

0.895 0.839

25.82 27.55

Gamma Kaplan-Meier (KM) Statistics

Gamma (KM) may not be used when k hat (KM) is < 0.1

k hat (KM) nu hat (KM)

Approximate Chi Square Value (4.42, α) Adjusted Chi Square Value (4.42, β)

95% Gamma Approximate KM-UCL (use when n>=50) 95% Gamma Adjusted KM-UCL (use when n<50)



Gamma Statistics on Detected Data Only



5% K-S Critical Value

Gamma GOF Tests on Detected Observations Only

A-D Test Statistic Anderson-Darling GOF Test

5% A-D Critical Value Detected Data Not Gamma Distributed at 5% Significance Level

K-S Test Statistic Kolmogrov-Smirnoff GOF

Detected Data Not Gamma Distributed at 5% Significance Level


90% KM Chebyshev UCL

97.5% KM Chebyshev UCL

SD 95% KM (BCA) UCL

Mean Standard Error of Mean

Kaplan-Meier (KM) Statistics using Normal Critical Values and other Nonparametric UCLs

95% KM (t) UCL 95% KM (Percentile Bootstrap) UCL

95% KM (z) UCL 95% KM Bootstrap t UCL




Normal GOF Test on Detects Only


5% Shapiro Wilk Critical Value Detected Data Not Normal at 5% Significance Level


Detected Data Not Normal at 5% Significance Level


Mean of Logged Detects

Skewness Detects

Maximum Detect Maximum Non-Detect

Variance Detects Percent Non-Detects

Mean Detects SD Detects

Median Detects CV Detects

Kurtosis Detects

SD of Logged Detects

Number of Distinct Detects Number of Distinct Non-Detects

Minimum Detect Minimum Non-Detect


Number of Detects Number of Non-Detects

General Statistics

Antimony (mg/kg)

Page 4 of 68

Attachment E



0.01 3.901

144 0.01

22.74 5.828

0.149 0.155

26.17 25.24

11.92 12.36

3.901 9.924

0.044

5.468 5.296

8.822 9.108

0.655

0.762

0.424

0.396

3.994 -1.805

22.72 1.619

10.05 11.15

18.25 137.9

1.403

7.516 1.055

22.51 1.116

13.51 8.442

22.37

Recommendations are based upon data size, data distribution, and skewness.

These recommendations are based upon the results of the simulation studies summarized in Singh, Maichle, and Lee (2006).

However, simulations results will not cover all Real World data sets; for additional insight the user may want to consult a statistician.



95% KM (Chebyshev) UCL

DL/2 is not a recommended method, provided for comparisons and historical reasons


Data do not follow a Discernible Distribution at 5% Significance Level

SD in Original Scale SD in Log Scale

95% t UCL (Assumes normality) 95% H-Stat UCL

DL/2 Statistics

DL/2 Normal DL/2 Log-Transformed

Mean in Original Scale Mean in Log Scale

95% BCA Bootstrap UCL 95% Bootstrap t UCL

95% H-UCL (Log ROS)

95% t UCL (assumes normality of ROS data) 95% Percentile Bootstrap UCL




Lognormal GOF Test on Detected Observations Only



5% Shapiro Wilk Critical Value Detected Data Not Lognormal at 5% Significance Level

Lilliefors GOF Test

Detected Data Not Lognormal at 5% Significance Level


Lognormal ROS Statistics Using Imputed Non-Detects

95% Gamma Approximate UCL (use when n>=50)

Approximate Chi Square Value (12.36, α)




Adjusted Level of Significance (β)

Adjusted Chi Square Value (12.36, β)

95% Gamma Adjusted UCL (use when n<50)

SD CV


Minimum Mean

Maximum Median

For such situations, GROS method tends to yield inflated values of UCLs and BTVs

For gamma distributed detected data, BTVs and UCLs may be computed using gamma distribution on KM estimates

Gamma ROS Statistics using Imputed Non-Detects

GROS may not be used when data set has > 50% NDs with many tied observations at multiple DLs

GROS may not be used when kstar of detected data is small such as < 0.1

Page 5 of 68

Attachment E



40 36

32 8

30 7

2.1 1.3

146 2.7

712.2 20%

24.69 26.69

18.45 1.081

3.296 13.75

2.825 0.894

0.667

0.93

0.241

0.157

20.03 4.061

25.28 26.94

26.87 27.19

26.71 31.31

32.21 37.73

45.39 60.44

0.463

0.765

0.124

0.158

1.455 1.34

16.97 18.43

93.15 85.75

24.69 21.33

0.627 50.19

34.92 34.44

28.78 29.1895% Gamma Approximate KM-UCL (use when n>=50) 95% Gamma Adjusted KM-UCL (use when n<50)








5% K-S Critical Value Detected data appear Gamma Distributed at 5% Significance Level

Detected data appear Gamma Distributed at 5% Significance Level


5% A-D Critical Value Detected data appear Gamma Distributed at 5% Significance Level



90% KM Chebyshev UCL 95% KM Chebyshev UCL

97.5% KM Chebyshev UCL 99% KM Chebyshev UCL





SD 95% KM (BCA) UCL

5% Lilliefors Critical Value Detected Data Not Normal at 5% Significance Level






Skewness Detects Kurtosis Detects

Mean of Logged Detects SD of Logged Detects








General Statistics


Arsenic (mg/kg)


Page 6 of 68

Attachment E



0.01 19.76

146 12.5

25.81 1.306

0.4 0.387

49.37 51.08

32.01 30.94

19.76 31.77

0.044

19.24 18.89

31.78 32.36

0.983

0.93

0.0889

0.157

20.24 2.435

25.45 1.124

27.02 27.37

29.48 31.47

34.01

2.319 40.87

1.284 2.759

0.207

19.97 2.268

25.65 1.385

26.8 47.91


Detected Data appear Gamma Distributed at 5% Significance Level



DL/2 Statistics


KM Standard Error of Mean (logged)

UCLs using Lognormal Distribution and KM Estimates when Detected data are Lognormally Distributed

KM SD (logged) 95% Critical H Value (KM-Log)

KM Mean (logged) 95% H-UCL (KM -Log)



95% H-UCL (Log ROS)






5% Lilliefors Critical Value Detected Data appear Lognormal at 5% Significance Level

5% Shapiro Wilk Critical Value Detected Data appear Lognormal at 5% Significance Level




Detected Data appear Lognormal at 5% Significance Level


95% Gamma Approximate UCL (use when n>=50) 95% Gamma Adjusted UCL (use when n<50)





SD CV


Maximum Median






Minimum Mean

Page 7 of 68

Attachment E



26.94 32.36

29.18

40 38

31 9

30 8

29.2 13

2120 130

272959 22.5%

394.7 522.5

148 1.324

2.293 4.895

5.383 1.054

0.653

0.929

0.294

0.159

310.8 76.95

478.7 456.4

440.5 437.8

437.4 525.1

541.7 646.3

791.4 1076

1.673

0.777

0.198

0.163

0.973 0.901

405.6 438.3

60.34 55.83

394.7 416MLE Mean (bias corrected) MLE Sd (bias corrected)







5% K-S Critical Value Detected Data Not Gamma Distributed at 5% Significance Level







SD 95% KM (BCA) UCL



















Barium (mg/kg)

General Statistics






95% Adjusted Gamma KM-UCL


95% KM (BCA) UCL 95% GROS Adjusted Gamma UCL

Page 8 of 68

Attachment E



0.422 33.74

21.45 21.09

488.8 497.3

0.01 305.9

2120 136

487.7 1.594

0.271 0.267

1129 1145

21.68 21.38

305.9 591.7

0.044

11.88 11.61

550.8 563.4

0.948

0.929

0.159

0.159

311.8 4.889

484 1.321

440.8 445.7

475.2 510.9

575.6

4.799 688.8

1.447 2.976

0.235

311.1 4.791

484.6 1.495

440.1 763




DL/2 Statistics








95% H-UCL (Log ROS)


















Maximum Median

SD CV


Minimum Mean









Page 9 of 68

Attachment E



646.3

29 29

25 4

25 4

0.0195 0.035

1.5 0.22

0.148 13.79%

0.274 0.384

0.105 1.405

2.281 4.784

-1.975 1.127

0.645

0.918

0.299

0.177

0.243 0.0679

0.358 0.364

0.359 0.356

0.355 0.429

0.447 0.539

0.667 0.919

1.463

0.779

0.234

0.18










SD 95% KM (BCA) UCL



















Benzo(a)anthracene (mg/kg)

General Statistics









Detected Data appear Lognormal Distributed at 5% Significance Level

Page 10 of 68

Attachment E



0.866 0.789

0.316 0.347

43.29 39.43

0.274 0.308

0.461 26.74

15.95 15.45

0.408 0.421

0.01 0.239

1.5 0.0886

0.367 1.535

0.732 0.68

0.326 0.351

42.48 39.42

0.239 0.29

0.0407

26.04 25.39

0.362 0.371

0.945

0.918

0.163

0.177

0.243 -2.151

0.365 1.166

0.358 0.359

0.39 0.444

0.414

-2.143 0.396

1.138 2.643

0.219KM Standard Error of Mean (logged)





95% H-UCL (Log ROS)


















Maximum Median

SD CV


Minimum Mean














Page 11 of 68

Attachment E



0.244 -2.136

0.364 1.17

0.359 0.424

0.667

29 28

24 5

23 5

0.014 0.035

1.3 0.22

0.139 17.24%

0.308 0.373

0.132 1.21

1.811 2.339

-1.76 1.097

0.698

0.916

0.319

0.181

0.263 0.0658

0.347 0.369

0.375 0.374

0.372 0.415

0.461 0.55

0.675 0.91997.5% KM Chebyshev UCL 99% KM Chebyshev UCL

95% KM (z) UCL




SD 95% KM (BCA) UCL


95% KM Bootstrap t UCL








Lilliefors GOF Test



Median Detects

Skewness Detects






CV Detects

Kurtosis Detects



Benzo(a)pyrene (mg/kg)

General Statistics








97.5% KM (Chebyshev) UCL


DL/2 Statistics





Page 12 of 68

Attachment E



1.288

0.772

0.225

0.183

0.992 0.895

0.311 0.344

47.59 42.98

0.308 0.326

0.577 33.49

21.26 20.67

0.415 0.427

0.01 0.26

1.3 0.123

0.355 1.367

0.758 0.702

0.343 0.37

43.95 40.74

0.26 0.31

0.0407

27.11 26.45

0.39 0.4

0.944

0.916

0.156

0.181

0.263 -2.02

0.353 1.185

0.375 0.378

0.402 0.424

0.491 95% H-UCL (Log ROS)










Lilliefors GOF Test




95% Gamma Approximate UCL (use when n>=50)







95% Gamma Adjusted UCL (use when n<50)

SD CV


Minimum Mean

Maximum Median

















K-S Test Statistic



Kolmogrov-Smirnoff GOF



Page 13 of 68

Attachment E



-2.061 0.532

1.245 2.786

0.242

0.265 -2.008

0.352 1.187

0.376 0.499

0.675

29 27

23 6

22 5

0.0484 0.035

2.1 0.22

0.327 20.69%

0.429 0.572

0.169 1.331

1.902 2.668

-1.49 1.083

0.66

0.914

0.345

0.185

DL/2 Statistics









Benzo(b)fluoranthene (mg/kg)








Shapiro Wilk Test Statistic

5% Shapiro Wilk Critical Value

Shapiro Wilk GOF Test


Lilliefors GOF Test



Maximum Detect

Variance Detects

Maximum Non-Detect

Percent Non-Detects





Number of Distinct Detects

Minimum Detect

General Statistics



Number of Distinct Non-Detects

Minimum Non-Detect





Page 14 of 68

Attachment E



0.353 0.0988

0.52 0.538

0.521 0.524

0.515 0.586

0.649 0.784

0.97 1.336

1.86

0.774

0.29

0.187

0.906 0.817

0.474 0.525

41.7 37.59

0.429 0.475

0.46 26.69

15.91 15.41

0.592 0.611

0.01 0.343

2.1 0.121

0.535 1.56

0.595 0.556

0.577 0.617

34.48 32.25

0.343 0.46

0.0407

20.27 19.7

0.546 0.561

0.892

0.914

0.222

0.185



5% Lilliefors Critical Value Detected Data Not Lognormal at 5% Significance Level










Theta hat (MLE)

nu hat (MLE)

SD

k hat (MLE)


Minimum Mean

Maximum Median

CV

k star (bias corrected MLE)

Theta star (bias corrected MLE)

nu star (bias corrected)





















Mean

SD

Standard Error of Mean

95% KM (BCA) UCL






Page 15 of 68

Attachment E



0.35 -1.872

0.531 1.271

0.518 0.522

0.552 0.599

0.679

0.351 -1.873

0.531 1.281

0.518 0.693

0.97

29 29

24 5

24 5

0.0792 0.07

44.7 0.39

99.66 17.24%

4.615 9.983

0.417 2.163

3.215 11.6

-0.199 1.802

0.518

0.916

0.379

0.181











Lilliefors GOF Test








Minimum Detect

Maximum Detect

Number of Distinct Detects

General Statistics



Number of Distinct Non-Detects

Minimum Non-Detect

Maximum Non-Detect

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










DL/2 Statistics

95% H-UCL (Log ROS)




Page 16 of 68

Attachment E



3.84 1.717

9.051 6.831

6.761 6.899

6.664 10.52

8.991 11.32

14.56 20.92

2.503

0.833

0.296

0.191

0.383 0.363

12.04 12.71

18.4 17.43

4.615 7.659

0.18 10.44

4.218 3.984

9.503 10.06

0.01 3.821

44.7 0.331

9.219 2.413

0.3 0.292

12.74 13.09

17.39 16.93

3.821 7.073

0.0407

8.621 8.267

7.504 7.825

0.867

0.916

0.202

0.181






Lilliefors GOF Test













Minimum Mean

Maximum Median

SD CV



nu hat (MLE)














5% A-D Critical Value


A-D Test Statistic


95% KM (t) UCL

95% KM (z) UCL

95% KM (Percentile Bootstrap) UCL




Anderson-Darling GOF Test




SD


95% KM (BCA) UCL

Page 17 of 68

Attachment E



3.83 -0.729

9.216 2.061

6.742 6.8

7.985 10.59

19.23

3.837 -0.604

9.213 1.893

6.747 12.5

20.92

40 36

22 18

22 16

0.8 0.33

31.6 3.3

66.54 45%

6.958 8.157

3.35 1.172

2.024 3.712

1.405 1.052

0.721

0.911

0.272

0.189


SD in Log Scale

95% Percentile Bootstrap UCL

SD in Original Scale

95% t UCL (assumes normality of ROS data)




Lilliefors GOF Test
















General Statistics







Cadmium (mg/kg)








DL/2 Statistics



95% H-UCL (Log ROS)

95% Bootstrap t UCL


Page 18 of 68

Attachment E



4.027 1.092

6.745 6.021

5.868 5.962

5.824 6.948

7.304 8.789

10.85 14.9

0.695

0.769

0.172

0.19

1.072 0.956

6.493 7.279

47.15 42.06

6.958 7.117

0.357 28.52

17.33 17.01

6.626 6.754

0.01 3.831

31.6 0.885

6.934 1.81

0.266 0.263

14.4 14.58

21.29 21.02

3.831 7.473

0.044

11.61 11.35

6.938 7.099

0.959

0.911

0.114

0.189






Lilliefors GOF Test















Minimum Mean





Maximum Median

SD CV



MLE Mean (bias corrected)



MLE Sd (bias corrected)









SD 95% KM (BCA) UCL








Page 19 of 68

Attachment E



3.999 0.307

6.842 1.473

5.822 5.877

6.315 6.97

8.186

0.343 7.707

1.43 2.953

0.236

4.086 0.4

6.802 1.45

5.898 8.532

6.021 7.099

6.754

40 40

0

8.2 1082

12600 259.5

2338 369.7

2.162 3.729

0.495

0.94

0.359

0.14

DL/2 Log-Transformed



95% H-Stat UCL







Normal GOF Test



Lilliefors GOF Test



Minimum

Total Number of Observations

Chromium (mg/Kg)

General Statistics

Number of Distinct Observations


Mean

Maximum Median











95% t UCL (Assumes normality)

95% H-UCL (Log ROS)




95% Bootstrap t UCL





DL/2 Statistics

DL/2 Normal

Page 20 of 68

Attachment E



1704 1923

1741

1.544

0.824

0.18

0.148

0.453 0.436

2387 2482

36.24 34.86

1082 1639

22.35

0.044 21.97

1687 1716

0.978

0.94

0.0802

0.14

2.104 5.562

9.441 1.763

3236 2409

2990 3797

5383

1690 1704

1663 2345

2277 1684

2020

2191 2693

3390 4760

95% H-UCL



97.5% Chebyshev (MVUE) UCL

























Lognormal GOF Test

Shapiro Wilk Lognormal GOF Test



K-S Test Statistic


Kolmogrov-Smirnoff Gamma GOF Test


Gamma Statistics






A-D Test Statistic






Gamma GOF Test

Anderson-Darling Gamma GOF Test


Page 21 of 68

Attachment E



2693

40 36

25 15

22 15

5.8 3.3

77 33

340.2 37.5%

20.8 18.44

12.7 0.887

2.262 4.593

2.792 0.648

0.669

0.918

0.272

0.177

15.15 2.66

16.31 19.7

19.63 19.58

19.52 21.57

23.13 26.74

31.76 41.61

1.642

0.755

0.192

0.1775% K-S Critical Value


K-S Test Statistic







95% KM (z) UCL




SD 95% KM (BCA) UCL











Lilliefors GOF Test












General Statistics

Cobalt (mg/kg)








Page 22 of 68

Attachment E



2.211 1.972

9.409 10.55

110.6 98.62

20.8 14.81

0.863 69.02

50.9 50.31

20.54 20.78

0.01 13.67

77 9.95

17.31 1.266

0.363 0.353

37.61 38.74

29.07 28.22

13.67 23.01

0.044

17.1 16.78

22.55 22.99

0.896

0.918

0.171

0.177

15.15 2.372

16.31 0.783

19.49 19.54

20.66 22.21

19.11

2.319 20.24

0.866 2.259

0.147




Lilliefors GOF Test


Detected Data appear Approximate Lognormal at 5% Significance Level



95% H-UCL (Log ROS)







KM Mean (logged)

KM SD (logged)





95% H-UCL (KM -Log)

95% Critical H Value (KM-Log)

SD CV

Maximum Median
















Minimum Mean






Page 23 of 68

Attachment E



15.28 2.298

16.49 0.957

19.67 22.56

19.7

40 39

0

3 146.6

1350 101.5

229.6 36.3

1.566 4.049

0.572

0.94

0.266

0.14

207.8 231.1

211.6

0.527

0.792

0.1

0.1455% K-S Critical Value Detected data appear Gamma Distributed at 5% Significance Level



Gamma GOF Test











Normal GOF Test

Maximum Median





Lilliefors GOF Test



Minimum Mean

General Statistics


Copper (mg/kg)




95% KM (BCA) UCL


Detected Data appear Approximate Lognormal Distributed at 5% Significance Level







DL/2 Statistics


Page 24 of 68

Attachment E



0.723 0.686

202.7 213.8

57.86 54.86

146.6 177

38.84

0.044 38.33

207.1 209.8

0.956

0.94

0.151

0.14

1.099 4.156

7.208 1.433

351.6 318.1

385.2 478.4

661.5

206.3 207.8

205.3 273.5

468.6 210.8

231.2

255.5 304.8

373.3 507.8

209.8












95% Adjusted Gamma UCL







Data appear Approximate Lognormal at 5% Significance Level








95% Approximate Gamma UCL (use when n>=50) 95% Adjusted Gamma UCL (use when n<50)

Lognormal GOF Test









Gamma Statistics



Page 25 of 68

Attachment E



29 27

13 16

13 15

0.0251 0.035

0.227 0.22

0.0052 55.17%

0.103 0.0721

0.0711 0.7

0.496 -1.271

-2.547 0.816

0.891

0.866

0.21

0.246

0.0655 0.0122

0.0605 0.0843

0.0863 0.0862

0.0856 0.0891

0.102 0.119

0.142 0.187

0.463

0.744

0.158

0.239

1.968 1.565

0.0524 0.0658

51.18 40.7

0.103 0.0824

1.172 67.98

50.01 49.08

0.089 0.0907





















Detected Data appear Normal at 5% Significance Level



SD 95% KM (BCA) UCL





Skewness Detects

Mean of Logged Detects

Kurtosis Detects

SD of Logged Detects



Lilliefors GOF Test


Mean Detects

Median Detects






SD Detects

CV Detects

General Statistics

Dibenz(a,h)anthracene (mg/kg)


Page 26 of 68

Attachment E



0.01 0.0633

0.227 0.0373

0.0601 0.949

1.664 1.515

0.0381 0.0418

96.52 87.87

0.0633 0.0514

0.0407

67.26 66.18

0.0827 0.0841

0.901

0.866

0.162

0.246

0.0651 -3.013

0.0588 0.698

0.0837 0.0833

0.0883 0.0911

0.083

-3.058 0.0858

0.76 2.19

0.159

0.0712 -2.978

0.0605 0.836

0.0903 0.103

Mean in Log Scale







DL/2 Statistics



SD in Log Scale

95% H-Stat UCL



95% H-UCL (Log ROS)


95% Bootstrap t UCL






SD CV






Lilliefors GOF Test




Mean in Original Scale


Minimum Mean

Maximum Median









Page 27 of 68

Attachment E



0.0863 0.0862

29 28

22 7

22 6

0.0376 0.035

0.89 0.22

0.0672 24.14%

0.237 0.259

0.114 1.096

1.576 1.254

-1.918 0.957

0.722

0.911

0.324

0.189

0.192 0.0447

0.235 0.266

0.268 0.272

0.266 0.298

0.326 0.387

0.471 0.636

1.355

0.766

0.258

0.195% K-S Critical Value Detected Data Not Gamma Distributed at 5% Significance Level









SD 95% KM (BCA) UCL



















Indeno(1,2,3-cd)pyrene (mg/kg)

General Statistics









Detected Data appear Normal Distributed at 5% Significance Level


Page 28 of 68

Attachment E



1.189 1.057

0.199 0.224

52.32 46.52

0.237 0.23

0.671 38.91

25.62 24.98

0.292 0.299

0.01 0.184

0.89 0.0898

0.244 1.323

0.78 0.722

0.236 0.255

45.23 41.89

0.184 0.217

0.0407

28.05 27.38

0.275 0.282

0.913

0.911

0.196

0.189

0.189 -2.278

0.241 1.101

0.265 0.266

0.287 0.293

0.322

-2.191 0.28

0.972 2.432

0.187






95% H-UCL (Log ROS)






Detected Data appear Approximate Lognormal at 5% Significance Level










SD CV

k star (bias corrected MLE)k hat (MLE)





Minimum Mean

Maximum Median







95% Gamma Approximate KM-UCL (use when n>=50)






95% Gamma Adjusted KM-UCL (use when n<50)

Page 29 of 68

Attachment E



0.192 -2.243

0.239 1.085

0.267 0.324

0.266

40 40

0

2630 25731

94200 24750

18050 2854

0.702 1.49

0.893

0.94

0.137

0.14

30539 31144

30651

0.569

0.76

0.134

0.141





Gamma GOF Test




Data appear Approximate Normal at 5% Significance Level



5% Lilliefors Critical Value Data appear Normal at 5% Significance Level





Minimum Mean

Maximum Median


Normal GOF Test



Iron (mg/kg)

General Statistics








Detected Data appear Approximate Lognormal Distributed at 5% Significance Level

95% KM (BCA) UCL




DL/2 Statistics


Page 30 of 68

Attachment E



1.926 1.799

13357 14306

154.1 143.9

25731 19186

117.2

0.044 116.3

31599 31844

0.928

0.94

0.177

0.14

7.875 9.874

11.45 0.844

37505 39732

45319 53072

68303

30425 30539

30219 31547

32430 30474

31429

34293 38171

43554 54128

30539





95% Student's-t UCL





95% Standard Bootstrap UCL

95% Hall's Bootstrap UCL

95% CLT UCL




95% Jackknife UCL

95% Bootstrap-t UCL












5% Lilliefors Critical Value Data Not Lognormal at 5% Significance Level





Lognormal GOF Test



Gamma Statistics




Page 31 of 68

Attachment E



40 39

0

4 162.9

936 101.7

192.4 30.42

1.181 2.088

0.784

0.94

0.204

0.14

214.2 223.7

215.9

0.51

0.792

0.108

0.145

0.718 0.681

226.8 239.2

57.47 54.49

162.9 197.4

38.53

0.044 38.03

230.4 233.5

0.928

0.94

0.141

0.14

General Statistics

Maximum Median





Lilliefors GOF Test



Normal GOF Test


Minimum Mean

Lead (mg/kg)





Lognormal GOF Test


95% Approximate Gamma UCL (use when n>=50)


95% Adjusted Gamma UCL (use when n<50)





Adjusted Level of Significance






Adjusted Chi Square Value



K-S Test Statistic





Gamma Statistics

Gamma GOF Test

A-D Test Statistic








Page 32 of 68

Attachment E



1.386 4.255

6.842 1.519

472.1 409.3

499.2 624

869.1

213 214.2

212 230.1

232.4 216

223.5

254.2 295.5

352.9 465.6

233.5

40 40

0

15.6 2940

52100 613.5

8520 1347

2.898 5.284

0.355

0.94

0.366

0.14

5210 6359

5397










Coefficient of Variation

Minimum Mean

Maximum Median


Skewness

Normal GOF Test



Manganese (mg/kg)

General Statistics














95% H-UCL



97.5% Chebyshev (MVUE) UCL








Page 33 of 68

Attachment E



2.07

0.83

0.206

0.149

0.423 0.408

6949 7206

33.85 32.64

2940 4603

20.58

0.044 20.22

4663 4746

0.988

0.94

0.0737

0.14

2.747 6.445

10.86 1.731

7177 5465

6770 8581

12138

5156 5210

5172 11654

13052 5253

6542

6981 8812

11353 16344

8812




Gamma Statistics













95% CLT UCL

95% Standard Bootstrap UCL




95% Jackknife UCL

95% Bootstrap-t UCL









Lognormal GOF Test





5% Lilliefors Critical Value Data appear Lognormal at 5% Significance Level






A-D Test Statistic


Gamma GOF Test



K-S Test Statistic

Page 34 of 68

Attachment E



40 37

39 1

36 1

0.068 0.042

143 0.042

1024 2.5%

20.57 32

9.5 1.556

2.658 7.637

1.731 1.978

0.651

0.939

0.261

0.142

20.06 5.023

31.36 29.44

28.52 28.72

28.32 34.94

35.13 41.95

51.42 70.03

0.286

0.815

0.0932

0.15

0.493 0.472

41.76 43.6

38.42 36.8

20.57 29.95

0.409 32.74

20.66 20.3

31.79 32.35



















Minimum Detect

95% Gamma Approximate KM-UCL (use when n>=50)


95% Gamma Adjusted KM-UCL (use when n<50)















SD 95% KM (BCA) UCL

95% KM (t) UCL

Minimum Non-Detect

General Statistics




Mercury (mg/kg)

Page 35 of 68

Attachment E



0.01 20.06

143 8.55

31.76 1.583

0.453 0.435

44.32 46.08

36.21 34.82

20.06 30.4

0.044

22.32 21.95

31.29 31.82

0.953

0.939

0.116

0.142

20.06 1.606

31.76 2.107

28.52 29.03

30.8 33.7

173.3

1.609 156.3

2.074 3.887

0.332

20.06 1.592

31.76 2.144

28.52 192.4 95% t UCL (Assumes normality) 95% H-Stat UCL


Mean in Log Scale


KM Mean (logged)


95% H-UCL (KM -Log)



DL/2 Statistics


Mean in Original Scale

95% H-UCL (Log ROS)
















Lilliefors GOF Test

MLE Mean (bias corrected)

nu hat (MLE)

Maximum Median

SD CV




MLE Sd (bias corrected)







Minimum Mean

Page 36 of 68

Attachment E



41.95 31.82

32.35

40 40

35 5

35 5

2.8 3.8

403 5.1

5997 12.5%

64.31 77.44

41 1.204

3.038 10.86

3.672 1.039

0.656

0.934

0.242

0.15

56.63 11.91

74.24 77.55

76.69 77.99

76.21 89.61

92.35 108.5

131 175.1

0.627

0.773

0.126

0.153

95% KM (Chebyshev) UCL 95% GROS Adjusted Gamma UCL





General Statistics









K-S Test Statistic


A-D Test Statistic

95% KM (z) UCL





Anderson-Darling GOF Test



SD

95% KM (t) UCL





95% KM (BCA) UCL









Lilliefors GOF Test


Nickel (mg/kg)








Page 37 of 68

Attachment E



1.154 1.074

55.72 59.87

80.79 75.2

64.31 62.05

0.582 46.54

31.89 31.43

82.65 83.84

0.01 56.28

403 34.9

75.44 1.341

0.462 0.444

121.9 126.8

36.93 35.49

56.28 84.49

0.044

22.86 22.48

87.37 88.85

0.978

0.934

0.102

0.15

56.88 3.409

75 1.199

76.86 77.51

82.37 93.57

103.1

3.341 116.5

1.297 2.775

0.208KM Standard Error of Mean (logged)





95% H-UCL (Log ROS)


95% t UCL (assumes normality of ROS data)



SD in Log Scale


95% Bootstrap t UCL








Lilliefors GOF Test





SD CV






Minimum Mean

Maximum Median











Theta hat (MLE)

nu hat (MLE)



Theta star (bias corrected MLE)


Page 38 of 68

Attachment E



56.55 3.309

75.24 1.374

76.59 132.5

77.55 88.85

83.84

40 31

8 32

6 27

1.2 0.67

218 7.8

5782 80%

39.31 76.04

6.65 1.934

2.371 5.664

2.05 1.891

0.59

0.818

0.414

0.313

8.492 5.976

35.35 18.92

18.56 19.37

18.32 152.8

26.42 34.54

45.81 67.95


Mean










Standard Error of Mean

SD 95% KM (BCA) UCL











General Statistics







Thallium (mg/kg)











DL/2 Statistics


Page 39 of 68

Attachment E



0.866

0.779

0.367

0.313

0.405 0.336

97.08 116.9

6.479 5.383

39.31 67.78

0.0577 4.616

0.979 0.92

40.03 42.62

0.01 7.871

218 0.01

35.93 4.566

0.145 0.151

54.37 52.28

11.58 12.04

7.871 20.28

0.044

5.256 5.088

18.03 18.63

0.864

0.818

0.269

0.313

7.891 -2.471

35.93 2.537

17.46 18.47

25.77 171.6

13.68










95% H-UCL (Log ROS)
















Minimum Mean

Maximum Median

SD CV





Gamma (KM) may not be used when k hat (KM) is < 0.1












Page 40 of 68

Attachment E



0.168 4.494

1.255 2.721

0.22

8.995 0.475

35.7 1.312

18.5 6.843

34.54

41 39

38 3

38 1

0.0483 0

550 0

9506 7.317%

33.55 97.5

1.964 2.906

4.504 22.42

0.394

0.938

0.393

0.144

31.1 14.72

93.03 59.65

55.89 56.2

55.32 105.2

75.27 95.28

123 177.6









SD 95% KM (BCA) UCL



















Total Aroclors (mg/kg)

General Statistics



DL/2 Statistics











Page 41 of 68

Attachment E



3.56

0.861

0.289

0.156

0.293 0.287

114.5 116.7

22.27 21.85

33.55 62.58

0.112 9.162

0.0441

3.425 3.298

83.18 86.4

31.1 94.19

55.86

177.6

15 15

0

0.161 28.25

353.9 2.142

90.48 23.36

3.203 3.819

0.342

0.881

0.42

0.229


Normal GOF Test








Total PCBs (mg/kg)

General Statistics



Minimum Mean

Maximum Median


DL/2 Statistics

Mean in Original Scale SD in Original Scale

























Page 42 of 68

Attachment E



69.39 91.28

73.23

1.824

0.844

0.319

0.241

0.283 0.271

99.9 104.4

8.483 8.12

28.25 54.3

2.805

0.0324 2.434

81.78 94.23

0.933

0.881

0.147

0.229

-1.829 0.879

5.869 2.045

247.8 39.63

51.21 67.29

98.87







Lognormal GOF Test



















Gamma GOF Test






Gamma Statistics



Page 43 of 68

Attachment E



66.67 69.39

65.2 599.5

500.2 74.32

100.4

98.33 130.1

174.1 260.7

260.7

40 39

36 4

35 4

4.2 4.8

131 5.9

1005 10%

49.23 31.7

41.55 0.644

0.848 0.247

3.649 0.79

0.927

0.935

0.122

0.148

44.73 5.226

32.59 53.69

53.53 53.53

53.32 54.52

60.4 67.51

77.36 96.72

0.279

0.759

0.0885

0.149





SD 95% KM (BCA) UCL














5% Lilliefors Critical Value Detected Data appear Normal at 5% Significance Level

Detected Data appear Approximate Normal at 5% Significance Level


General Statistics


















Vanadium (mg/kg)





Page 44 of 68

Attachment E



2.174 2.012

22.64 24.47

156.6 144.8

49.23 34.71

1.884 150.7

123.3 122.4

54.66 55.07

4.2 44.75

131 37.85

32.97 0.737

1.507 1.411

29.7 31.72

120.6 112.9

44.75 37.68

0.044

89.34 88.55

56.54 57.04

0.941

0.935

0.133

0.148

45.1 3.491

32.55 0.889

53.77 53.66

53.89 54.97

67.46

3.428 73.97

0.994 2.4

0.159

95% H-UCL (Log ROS)































Minimum Mean

Maximum Median

SD CV







Page 45 of 68

Attachment E



44.57 3.38

33.21 1.11

53.41 85.38

53.53 53.53

40 40

0

13.1 566.4

4330 260

897.4 141.9

1.584 2.913

0.619

0.94

0.293

0.14

805.5 869.6

816.4

0.791

0.799

0.128

0.146

Gamma GOF Test















Zinc (mg/kg)

General Statistics



Minimum Mean

Maximum Median



Normal GOF Test




Detected Data appear Approximate Normal Distributed at 5% Significance Level







DL/2 Statistics




Page 46 of 68

Attachment E



0.648 0.616

874.2 919.6

51.83 49.28

566.4 721.7

34.16

0.044 33.69

817.1 828.5

0.974

0.94

0.0739

0.14

2.573 5.396

8.373 1.46

1289 1152

1398 1740

2411

799.8 805.5

796.1 1006

1113 815.9

884.9

992.1 1185

1453 1978

828.5































95% Approximate Gamma UCL (use when n>=50) 95% Adjusted Gamma UCL (use when n<50)

Lognormal GOF Test



Gamma Statistics



Page 47 of 68

Attachment E

ProUCL Output, Version 5.0 ‐ Wetland Surface Water


8 8

0

211 602.5

2640 302.5

827.4 292.5

1.373 2.774

0.51

0.818

0.45

0.313

1157 1390

1205

1.415

0.731

0.386

0.3

1.326 0.912

454.2 660.4

21.22 14.6

602.5 630.8

6.983

0.0195 5.705

1260 1542







Gamma Statistics




Gamma GOF Test














guidance provided in ITRC Tech Reg Guide on ISM (ITRC, 2012) to compute statistics of interest.

For example, you may want to use Chebyshev UCL to estimate EPC (ITRC, 2012).

Chebyshev UCL can be computed using the Nonparametric and All UCL Options of ProUCL 5.0

Normal GOF Test

Minimum Mean

Maximum Median



Note: Sample size is small (e.g., <10), if data are collected using ISM approach, you should use

Aluminum (µg/l)

General Statistics




Page 1 of 68

Attachment E



0.716

0.818

0.314

0.313

5.352 5.979

7.879 0.809

1361 978

1185 1472

2035

1084 1157

1064 4736

3573 1179

1466

1480 1878

2429 3513

1878

8 8

7 1

7 1

1.6 3.5

11.3 3.5

10.67 12.5%

4.1 3.266

3 0.797

2.339 5.824

1.225 0.606














Arsenic (µg/l)

General Statistics



















Data do not follow a Discernible Distribution (0.05)






Lognormal GOF Test





Page 2 of 68

Attachment E



0.683

0.803

0.382

0.335

3.894 1.105

2.887 6.025

5.988 5.913

5.712 9.764

7.21 8.712

10.8 14.89

0.668

0.713

0.311

0.314

2.838 1.717

1.444 2.388

39.74 24.04

4.1 3.129

1.819 29.11

17.79 15.6

6.37 7.267

1.6 3.855

11.3 2.85

3.103 0.805

2.891 1.89

1.333 2.039

46.26 30.24

3.855 2.804

0.0195

18.68 16.43

6.239 7.097




SD CV










Minimum Mean

Maximum Median
















SD 95% KM (BCA) UCL













Page 3 of 68

Attachment E



0.888

0.803

0.268

0.335

3.884 1.18

3.085 0.575

5.951 5.909

6.388 10.15

6.588

1.18 6.221

0.544 2.431

0.211

3.806 1.141

3.136 0.608

5.907 6.766

6.025 7.097

7.267

Iron (µg/l)











DL/2 Statistics













95% H-UCL (Log ROS)








Page 4 of 68

Attachment E



8 8

0

554 3095

16500 1300

5430 1920

1.754 2.799

0.488

0.818

0.476

0.313

6733 8284

7049

1.42

0.741

0.425

0.303

0.854 0.617

3626 5018

13.66 9.869

3095 3941

3.86

0.0195 2.97

7914 10285

0.763

0.818

0.34

0.313






Lognormal GOF Test









Gamma Statistics




Gamma GOF Test











Normal GOF Test




Maximum Median





General Statistics



Minimum Mean

Page 5 of 68

Attachment E



6.317 7.348

9.711 1.024

10098 5072

6280 7957

11250

6253 6733

6031 36246

28305 6920

8792

8855 11464

15085 22198

28305

8 7

0

3.1 8.163

32.6 4.85

9.983 3.529

1.223 2.708

0.552

0.818

0.429

0.313









Normal GOF Test



Minimum Mean

Maximum Median






Lead (µg/l)

General Statistics




Recommended UCL exceeds the maximum observation

In Case Bootstrap t and/or Hall's Bootstrap yields an unreasonably large UCL value, use 97.5% or 99% Chebyshev (Mean, Sd) UCL


















Page 6 of 68

Attachment E



14.85 17.58

15.41

1.121

0.728

0.353

0.299

1.54 1.046

5.3 7.804

24.64 16.74

8.163 7.981

8.483

0.0195 7.049

16.1 19.38

0.774

0.818

0.285

0.313

1.131 1.741

3.484 0.771

17.82 13.46

16.24 20.08

27.64

13.97 14.85

13.66 39.48

39.88 14.76

16.11

18.75 23.55

30.2 43.28
























Lognormal GOF Test











Gamma Statistics




Gamma GOF Test



Page 7 of 68

Attachment E



23.55

8 7

0

316 1269

7040 501

2334 825.2

1.84 2.819

0.457

0.818

0.496

0.313

2832 3505

2969

1.842

0.743

0.482

0.303

0.815 0.593

1556 2140

13.05 9.487

1269 1648

3.624

0.0195 2.768









Gamma Statistics




Gamma GOF Test












Normal GOF Test



Minimum Mean

Maximum Median



Manganese (µg/l)

General Statistics









Page 8 of 68

Attachment E



3321 4348

0.626

0.818

0.418

0.313

5.756 6.42

8.859 1.012

3839 1973

2440 3089

4363

2626 2832

2518 25274

19464 2902

2963

3744 4865

6422 9479

19464







In Case Bootstrap t and/or Hall's Bootstrap yields an unreasonably large UCL value, use 97.5% or 99% Chebyshev (Mean, Sd) UCL























Lognormal GOF Test



Page 9 of 68

Attachment E



28 20

19 9

17 4

0.081 0.2

5.6 1.7

1.433 32.14%

0.716 1.197

0.47 1.671

4.187 17.95

-0.785 0.807

0.384

0.901

0.423

0.203

0.541 0.194

0.998 0.974

0.872 0.922

0.861 1.623

1.125 1.389

1.755 2.476

2.087

0.763

0.304

0.203

1.248 1.086

0.574 0.659

47.43 41.28

0.716 0.687

0.294 16.47

8.294 7.936

1.075 1.123






















SD 95% KM (BCA) UCL
















Mercury (µg/l)

General Statistics


Page 10 of 68

Attachment E



0.01 0.512

5.6 0.33

1.027 2.008

0.561 0.525

0.911 0.974

31.43 29.4

0.512 0.706

0.0404

18.02 17.47

0.834 0.861

0.85

0.901

0.217

0.203

0.542 -1.154

1.013 0.924

0.868 0.912

1.101 1.743

0.735

0.594 -1.045

1.012 0.947

0.92 0.851

0.974









95% KM (BCA) UCL

DL/2 Statistics








95% H-UCL (Log ROS)










5% Shapiro Wilk Critical Value Detected Data Not Lognormal at 5% Significance Level










Minimum Mean

Maximum Median

SD CV


Page 11 of 68

Attachment E



8 5

4 4

4 1

0.19 1

5 1

4.821 50%

1.765 2.196

0.935 1.244

1.792 3.308

-0.0674 1.357

0.797

0.748

0.352

0.443

1.098 0.628

1.511 N/A

2.288 N/A

2.131 N/A

2.982 3.836

5.021 7.349

0.269

0.668

0.245

0.403















SD 95% KM (BCA) UCL





5% Shapiro Wilk Critical Value Detected Data appear Normal at 5% Significance Level












Trichloroethene (µg/l)

General Statistics



Page 12 of 68

Attachment E



0.918 0.396

1.923 4.456

7.342 3.169

1.765 2.804

0.528 8.444

2.995 2.237

3.095 4.143

0.01 1.055

5 0.525

1.653 1.566

0.471 0.378

2.241 2.795

7.533 6.041

1.055 1.717

0.0195

1.661 1.147

3.838 N/A

0.996

0.748

0.177

0.443

1.076 -0.61

1.625 1.175

2.165 2.106

2.655 5.685

6.051

-0.549 4.225

1.059 3.572

0.535









95% H-UCL (Log ROS)











SD CV










Minimum Mean

Maximum Median










Page 13 of 68

Attachment E



1.133 -0.38

1.589 0.949

2.197 3.507

2.288 N/A







Detected Data appear Normal Distributed at 5% Significance Level



Warning: One or more Recommended UCL(s) not available!

DL/2 Statistics





Page 14 of 68

Attachment E

ProUCL Output, Version 5.0 ‐ Fish (White Perch)


10 10

0

4.5849E-5 8.2697E-5

1.1942E-4 9.3802E-5

2.8583E-5 9.0386E-6

N/A -0.324

0.868

0.842

0.216

0.28

9.9266E-5 9.6574E-5

9.9112E-5

0.753

0.727

0.241

0.267

8.19 5.8

1.0097E-5 1.4259E-5

163.8 116

8.2697E-5 3.4339E-5

92.13

0.0267 88.44

1.0412E-4 1.0847E-4

0.833

0.842

0.235

0.285% Lilliefors Critical Value Data appear Lognormal at 5% Significance Level







Lognormal GOF Test




Gamma Statistics






Detected data follow Appr. Gamma Distribution at 5% Significance Level

Gamma GOF Test










Normal GOF Test




2,3,7,8-TCDD TEQ (mg/kg)

Maximum Median



General Statistics



Minimum Mean

Page 1 of 68

Attachment E



-9.99 -9.463

-9.033 0.385

1.0922E-4 1.1375E-4

1.2766E-4 1.4696E-4

1.8488E-4

9.7564E-5 9.9266E-5

9.6950E-5 9.7581E-5

9.4679E-5 9.6507E-5

9.6626E-5

1.0981E-4 1.2210E-4

1.3914E-4 1.7263E-4

9.9266E-5

7 7

0

4.895 7.128

9.032 7.305

1.291 0.488

0.181 -0.491





Maximum Median



General Statistics



Minimum Mean

Note: For highly negatively-skewed data, confidence limits (e.g., Chen, Johnson, Lognormal, and Gamma) may not be

reliable. Chen's and Johnson's methods provide adjustments for positvely skewed data sets.

Total PCBs (mg/kg)







95% Student's-t UCL
















Page 2 of 68

Attachment E



0.963

0.803

0.206

0.335

8.076 7.834

8.061

0.317

0.707

0.229

0.311

32.91 18.9

0.217 0.377

460.7 264.6

7.128 1.64

227.9

0.0158 217.6

8.275 8.668

0.93

0.803

0.238

0.335

1.588 1.949

2.201 0.193

8.363 8.698

9.407 10.39

12.32 99% Chebyshev (MVUE) UCL














Lognormal GOF Test










Gamma Statistics







Gamma GOF Test





Normal GOF Test




Page 3 of 68

Attachment E



7.931 8.076

7.882 7.97

7.928 7.849

7.838

8.592 9.255

10.18 11.98

8.076




Note: For highly negatively-skewed data, confidence limits (e.g., Chen, Johnson, Lognormal, and Gamma) may not be

reliable. Chen's and Johnson's methods provide adjustments for positvely skewed data sets.


95% Student's-t UCL









Page 4 of 68

Attachment E

ProUCL Output, Version 5.0 ‐ Wetland Sediment (Ackermans South)


9 9 8 1 8 1 5.4 0.2 62 0.2 415.3 11.11% 25.24 20.38 16.5 0.807 1.033 -0.199 2.932 0.838

0.868 0.818 0.226 0.313

22.46 6.991 19.62 34.49 35.46 33.78 33.96 42.63 43.43 52.93 66.12 92.02

0.299 0.725 0.209 0.298

1.836 1.231 13.74 20.5 29.38 19.7 25.24 22.75

1.31 23.58 13.53 11.95 39.14 44.29

0.01 22.43 62 13 20.83 0.929 0.607 0.479 36.96 46.86 10.93 8.618 22.43 32.42

0.0231 3.098 2.443 62.41 79.14



MLE Mean (bias corrected) MLE Sd (bias corrected)Adjusted Level of Significance (β)


k hat (MLE) k star (bias corrected MLE)Theta hat (MLE) Theta star (bias corrected MLE)


Minimum MeanMaximum Median

SD CV

Gamma ROS Statistics using Imputed Non-DetectsGROS may not be used when data set has > 50% NDs with many tied observations at multiple DLs

GROS may not be used when kstar of detected data is small such as < 0.1For such situations, GROS method tends to yield inflated values of UCLs and BTVs


k hat (KM) nu hat (KM)Approximate Chi Square Value (23.58, α) Adjusted Chi Square Value (23.58, β)


nu hat (MLE) nu star (bias corrected)MLE Mean (bias corrected) MLE Sd (bias corrected)



Gamma Statistics on Detected Data Onlyk hat (MLE) k star (bias corrected MLE)


5% A-D Critical Value Detected data appear Gamma Distributed at 5% Significance LevelK-S Test Statistic Kolmogrov-Smirnoff GOF



Gamma GOF Tests on Detected Observations OnlyA-D Test Statistic Anderson-Darling GOF Test

95% KM (t) UCL 95% KM (Percentile Bootstrap) UCL 95% KM (z) UCL 95% KM Bootstrap t UCL



Kaplan-Meier (KM) Statistics using Normal Critical Values and other Nonparametric UCLsMean Standard Error of Mean

SD 95% KM (BCA) UCL

5% Shapiro Wilk Critical Value Detected Data appear Normal at 5% Significance LevelLilliefors Test Statistic Lilliefors GOF Test


guidance provided in ITRC Tech Reg Guide on ISM (ITRC, 2012) to compute statistics of interest.For example, you may want to use Chebyshev UCL to estimate EPC (ITRC, 2012).


Normal GOF Test on Detects OnlyShapiro Wilk Test Statistic Shapiro Wilk GOF Test

Skewness Detects Kurtosis DetectsMean of Logged Detects SD of Logged Detects


Variance Detects Percent Non-DetectsMean Detects SD Detects


Number of Distinct Detects Number of Distinct Non-DetectsMinimum Detect Minimum Non-Detect


Mercury (mg/kg)

General StatisticsTotal Number of Observations Number of Distinct Observations


Page 5 of 68

Attachment E



0.962 0.818 0.169 0.313

22.69 2.7 20.54 1.049 35.42 33.83 34.94 43.82 89.33

2.427 599.6 1.607 4.71 0.573

22.44 2.35 20.82 1.913 35.35 2667

35.46 33.78

8 8 0

0.215 8.772 63.6 0.73 22.17 7.837 2.527 2.822

0.447 0.818 0.489 0.313

23.62 30.02 24.92

1.374 0.79 0.39 0.3155% K-S Critical Value Data Not Gamma Distributed at 5% Significance Level


A-D Test Statistic Anderson-Darling Gamma GOF Test5% A-D Critical Value Data Not Gamma Distributed at 5% Significance Level


95% Student's-t UCL 95% Adjusted-CLT UCL (Chen-1995) 95% Modified-t UCL (Johnson-1978)

Gamma GOF Test

5% Lilliefors Critical Value Data Not Normal at 5% Significance LevelData Not Normal at 5% Significance Level

Assuming Normal Distribution 95% Normal UCL 95% UCLs (Adjusted for Skewness)

Normal GOF TestShapiro Wilk Test Statistic Shapiro Wilk GOF Test

5% Shapiro Wilk Critical Value Data Not Normal at 5% Significance LevelLilliefors Test Statistic Lilliefors GOF Test

Note: Sample size is small (e.g., <10), if data are collected using ISM approach, you should useguidance provided in ITRC Tech Reg Guide on ISM (ITRC, 2012) to compute statistics of interest.

For example, you may want to use Chebyshev UCL to estimate EPC (ITRC, 2012).Chebyshev UCL can be computed using the Nonparametric and All UCL Options of ProUCL 5.0

Maximum MedianSD Std. Error of Mean


Total Number of Observations Number of Distinct ObservationsNumber of Missing Observations

Minimum Mean


Total Aroclors (mg/kg)

General Statistics


Note: Suggestions regarding the selection of a 95% UCL are provided to help the user to select the most appropriate 95% UCL.Recommendations are based upon data size, data distribution, and skewness.



Nonparametric Distribution Free UCL StatisticsDetected Data appear Normal Distributed at 5% Significance Level


Mean in Original Scale Mean in Log ScaleSD in Original Scale SD in Log Scale



DL/2 StatisticsDL/2 Normal DL/2 Log-Transformed

UCLs using Lognormal Distribution and KM Estimates when Detected data are Lognormally DistributedKM Mean (logged) 95% H-UCL (KM -Log)


95% t UCL (assumes normality of ROS data) 95% Percentile Bootstrap UCL 95% BCA Bootstrap UCL 95% Bootstrap t UCL

95% H-UCL (Log ROS)


Lognormal ROS Statistics Using Imputed Non-DetectsMean in Original Scale Mean in Log Scale


5% Shapiro Wilk Critical Value Detected Data appear Lognormal at 5% Significance LevelLilliefors Test Statistic Lilliefors GOF Test


Lognormal GOF Test on Detected Observations OnlyShapiro Wilk Test Statistic Shapiro Wilk GOF Test

Page 6 of 68

Attachment E



0.341 0.297 25.72 29.58 5.458 4.744 8.772 16.11

1.036 0.0195 0.668

40.17 62.29

0.826 0.818 0.229 0.313

-1.537 0.192 4.153 1.786

250.6 11.89 15.39 20.26 29.81

21.66 23.62 20.59 368.7 252.9 24.34 32.11 32.28 42.93 57.71 86.75

86.75

Note: Suggestions regarding the selection of a 95% UCL are provided to help the user to select the most appropriate 95% UCL.These recommendations are based upon the results of the simulation studies summarized in Singh, Singh, and Iaci (2002)

and Singh and Singh (2003). However, simulations results will not cover all Real World data sets.For additional insight the user may want to consult a statistician.

Suggested UCL to Use99% Chebyshev (Mean, Sd) UCL


95% BCA Bootstrap UCL 90% Chebyshev(Mean, Sd) UCL 95% Chebyshev(Mean, Sd) UCL


Nonparametric Distribution Free UCLs 95% CLT UCL 95% Jackknife UCL

95% Standard Bootstrap UCL 95% Bootstrap-t UCL 95% Hall's Bootstrap UCL 95% Percentile Bootstrap UCL


Nonparametric Distribution Free UCL StatisticsData appear to follow a Discernible Distribution at 5% Significance Level

Assuming Lognormal Distribution 95% H-UCL 90% Chebyshev (MVUE) UCL



Lognormal StatisticsMinimum of Logged Data Mean of logged Data


5% Shapiro Wilk Critical Value Data appear Lognormal at 5% Significance LevelLilliefors Test Statistic Lilliefors Lognormal GOF Test



Lognormal GOF TestShapiro Wilk Test Statistic Shapiro Wilk Lognormal GOF Test

Approximate Chi Square Value (0.05)Adjusted Level of Significance Adjusted Chi Square Value


Theta hat (MLE) Theta star (bias corrected MLE)nu hat (MLE) nu star (bias corrected)


Gamma Statisticsk hat (MLE) k star (bias corrected MLE)

Page 7 of 68

Attachment F Lead Modeling

TABLE 11.1 (RAGS D ADULT LEAD WORKSHEET)Site Name: OU2, Universal Oil Products (UOP), East Rutherford, New Jersey

Receptor: Current/Future On-Site Trespasser (Adult and Older Child)

1. Lead Screening Questions

Lead Concentration used in Model RunValue Units Value Units

Wetland Sediment (On-site)

162.9 mg/kg 400 mg/kgRecommended Soil Screening

Level

2. Lead Model Questions

MediumOnsite Sediment

Comment/PRG 1NA

If non-default values were used for any of the parameters listed above, where are the rationale for the values located in the risk assessment report?

Attachment A, RAGS Part D Table 4.1.

ResultInput value of 162.9 mg/kg in sediment results in 0.4% of recreational users having a blood lead level of 10 µg/dL. The geometric mean blood lead level = 1.5 µg/dL. This is less than the blood lead goal as described in the 1994 OSWER Directive of no more than 5% of children (fetuses of exposed women) exceeding 10 µg/dL blood lead.

Medium

Basis for Lead Concentration Used For Model Run

Basis for Lead Screening Level

Question Response for Residential Lead Model

Arithmetic Mean

Lead Screening Concentration

Was the default soil ingestion rate (IR; 50 mg/day) used? Yes

What was the point of exposure and location? Wetland Sediment

Where are the output values located in the risk assessment report?

Was the default absorption fraction (AF; 0.12) used? Yes

What statistics were used to represent the exposure concentration terms and where are the data on concentrations in the risk assessment that support use of these statistics?

Arithmetic mean value; data presented in Table 3.1 of Attachment A.

No; the exposure frequency of 13 days/year was used.

Was the default BKSF used (0.4 µg/dL per µg/day) used? Yes

Attachment F.

What GSD value was used? If this is outside the recommended range of 1.8-2.1), provide rationale in Appendix <Y>.

Recommended baseline GSD of 1.8 based on estimates of U.S. women, 17–45 years of age, between NHANES III and 1999–2004 NHANES data was used.

What baseline blood lead concentration (PbB0) value was used? If this is outside the default range of 1.7 to 2.2 provide rationale in Appendix <Y>

Recommended baseline PbB0 of 1.0 (μg/dL) based on estimates of U.S. women, 17–45 years of age, between NHANES III and 1999–2004 NHANES data was used.

Was the default exposure frequency (EF; 219 days/year) used?

EPA Adult Lead Methodology, Version date 06/21/2009

If the EPA Adult Lead Model (ALM) was not used provide rationale for model selected.

NA

Where are the input values located in the risk assessment report? Table 11.2.

What lead model was used? Provide reference and version

Calculations of Preliminary Remediation Goals (PRGs)

TABLE 11.2Adult Lead Methodology Model worksheet - Wetland Sediment - Current/Future On-Site Trespasser (Adult and Older Child)OU2, Universal Oil Products (UOP), East Rutherford, New Jersey

Calculations of Blood Lead Concentrations (PbBs)U.S. EPA Technical Review Workgroup for Lead, Adult Lead CommitteeVersion date 6/21/09

Variable Units

GSDi and PbBo from Analysis of NHANES

1999-2004

GSDi and PbBo from Analysis of NHANES III (Phases 1&2)

PbS µg/g or ppm 162.9 162.9Rfetal/maternal -- 0.9 0.9

BKSF µg/dL per µg/day

0.4 0.4

GSDi -- 1.8 2.1PbB0 µg/dL 1.0 1.5IRS g/day 0.050 0.050

IRS+D g/day -- --WS -- -- --KSD -- -- --

AFS, D -- 0.12 0.12EFS, D days/yr 13 13ATS, D days/yr 365 365

PbBadult PbB of adult worker, geometric mean µg/dL 1.0 1.5

PbBfetal, 0.95 95th percentile PbB among fetuses of adult workers µg/dL 2.4 4.6

PbBt Target PbB level of concern (e.g., 10 µg/dL) µg/dL 10.0 10.0

P(PbBfetal > PbBt) Probability that fetal PbB > PbBt, assuming lognormal distribution % 0.002% 0.4%

Description of Variable

Soil lead concentration

Fetal/maternal PbB ratio Biokinetic Slope Factor

Geometric standard deviation PbB

Baseline PbB

Averaging time (same for soil and dust)

Soil ingestion rate (including soil-derived indoor dust)

Total ingestion rate of outdoor soil and indoor dust

Weighting factor; fraction of IRS+D ingested as outdoor soil

Mass fraction of soil in dust

Absorption fraction (same for soil and dust)

Exposure frequency (same for soil and dust)

Source: U.S. EPA (1996). Recommendations of the Technical Review Workgroup for Lead for an Interim Approach to Assessing Risks Associated with Adult Exposures to Lead in Soil Printed 6/1/2016 2:33 PM

revised human health risk assessment, universal oil

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