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# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey

i 

# TABLE OF CONTENTS

I. Introduction ...................................

................................................... ................................................... 1

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

................................................... ....................................... 1

**A. Background Summary .............................**

**................................................... ...................................... 1** 

**B. Remedial Investigation/Feasibility Study .......**

**................................................... ............................... 3** 

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

**................................................... ...................... 3** 

**D. Institutional Controls .........................**

**................................................... ............................................ 5** 

**E. Final Site Inspection ..........................**

**................................................... ............................................ 5** 

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

................................................... ................................................ 5

**A. Air Monitoring .................................**

**................................................... .............................................. 5** 

**B. Groundwater Monitoring .........................**

**................................................... ...................................... 6** 

**C. Surface Water Monitoring .......................**

**................................................... ...................................... 6** 

**D. Sediment Monitoring ............................**

**................................................... ......................................... 7** 

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

................................................... ........................... 7

V. Clean-up Activity Quality Assurance/Quality Cont rol ............................................... .................... 8

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

................................................... ................................................ 8

**A. Five-year Review Process .......................**

**................................................... ....................................... 8** 

**B. Summary of the Third Five-year Review (Plexus, 2 010) ..............................................**  **................... 9**

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

................................................... ............................................ 9

VIII.Bibliography..................................

................................................... ................................................. 1 0



# ATTACHMENTS

Attachment A – **Tables**

Attachment B – **Figures**

Attachment C – **2009 Ecological Risk Assessment.**

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey

ii 

# ACRONYMS

**ACO Administrative Consent Order**

**ARARs Applicable or Relevant and Appropriate Requ irements** 

**CEA Classification Exemption Area**

**CERCLA Comprehensive Environmental Response, Compe nsation, and Liability Act** 

**COCs contaminants of concern**

**DDE Dichlorodiphenyldichloroethylene**

**DDT Dichlorodiphenyltrichloroethane**

**FFA Federal Facility Agreement**

**FCOR Final Close Out Report**

**FY fiscal year**

**ICs institutional controls**

**JB MDL Joint Base McGuire-Dix-Lakehurst**

**LTM long-term monitoring**

**LTMP long-term monitoring plan**

**LUC land use control**

**NJDEP New Jersey Department of Environmental Prot ection** 

**NJPDES New Jersey Pollutant Discharge Elimination System** 

**NJSA New Jersey Statutes Annotated**

**NPL National Priorities List**

**O&M Operation and Maintenance**

**PDO Property Disposal Office**

**Plexus Plexus Scientific Corporation**

**RCRA Resource Conservation and Recovery Act**

**RI/FS Remedial Investigation/Feasibility Study**

**ROD Record of Decision**

**SVOC Semi-Volatile Organic Compound**

**USACE United States Army Corps of Engineers**

**USAEC United States Army Environmental Command**

**USEPA United States Environmental Protection Agen cy** 

**VOC Volatile Organic Compound**

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



# 1 

# I. Introduction

**Plexus Scientific Corporation (Plexus), under contr act to the United States Army Environmental** 

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

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

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

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

**that allow for unlimited use and unrestricted expos ure. The site was proposed to the National Priorit**  **ies**

**List (NPL) in 1984 and finalized in 1987**

.



# This FCOR documents that JB MDL has completed all r **emedial actions at the Dix Area Sanitary Landfill.**

**The selected remedy at the Dix Area Sanitary Landfi ll includes construction of a landfill cap and vent**  **ing**

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

**and institutional controls (ICs) in the form of Mas ter Plan Amendments and water restrictions. In ord**  **er to**

**ensure the selected remedy continues to provide lon g-term protection, the site will be incorporated in**  **to**

**the New Jersey Classification Exemption Area (CEA).**



# II. Summary of Site Conditions

A. Background Summary

**The Dix Area Sanitary Landfill is located in the so uthwest section of the JB MDL in Pemberton** 

**Township, Burlington County, New Jersey. The landf ill covers approximately 126 acres and is located** 

**about 2,200 feet from the post boundary. Two strea ms flow near the landfill: Cannon Run is located o**  **n**

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

**stream is located northwest of the landfill, and fl ows to the west into the North Branch of Rancocas** 

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

**The area immediately surrounding the Dix Area Sanit ary Landfill consists of a hardwood swamp and** 

**densely vegetated hardwood forest. The town of Bro wns Mills is immediately to the east of the Militar**  **y**

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

**homes, several county buildings, the County Hospita l, and the Burlington County Juvenile Detention** 

**Center and shelter. Pemberton Township municipal b uildings, sewage disposal plant, public water suppl**  **y**

**wells, and several homes are located to the southwe st of the landfill.** 

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

**overlies the fine grained silts and clays of the Ma nasquan, Hornerstown, and Navesink Formations. The** 

**Cohansey and Kirkwood Formations form a single unco nfined aquifer at the site. Groundwater flow in** 

**this aquifer is to the south and southwest. The un derlying Manasquan, Hornerstown, and Navesink** 

**Formations form a confining layer that limits downw ard vertical groundwater flow from the landfill sit**  **e.**

**The Dix Area Sanitary Landfill began operation in 1 950; it was officially closed on July 6, 1984. Pri**  **or to**

**landfill development, the area was used for Army tr aining. Between 1950 and 1984, the landfill was us**  **ed**

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

**1968 until it was closed. Access to the landfill w as not controlled until 1980; therefore, records of** 

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



# 2 **disposal practices, waste types, and quantities are incomplete. Wastes that have been reportedly disp**  **osed**

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

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

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

**landfill in compliance with the landfill closure da te. The landfill was ranked for inclusion on the N**  **PL on**

**September 14, 1984. On September 16, 1985, the Arm y entered into an Administrative Consent Order** 

**(ACO) with the New Jersey Department of Environment al Protection (NJDEP). The ACO required the** 

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

**remedial alternative approved by NJDEP and United S tates Environmental Protection Agency (USEPA).** 

**The Dix Area Sanitary Landfill Site was placed on t he NPL on July 1, 1987.** 

**On July 19, 1991, the Army entered into an interage ncy agreement, under Comprehensive Environmental** 

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

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

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

**Sanitary Landfill Site at JB MDL.**

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

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

**Phase I, a 6-foot security fence was installed arou nd the entire landfill, and erosion control measure**  **s and**

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

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

**installation of drainage facilities, a surface wate r infiltration pond, access roads, and permanent er**  **osion**

**control measures.**

**The site chronology for the Dix Area Sanitary Landf ill site is presented in the table below:** 

Event Date

**Site proposed for placement on the NPL October 1984**

**Final placement on the NPL Ju1y 1,1987**

**RI/FS completed September 1987**

**Army and USEPA sign Federal Facility Agreement Jul y 1991** 

**ROD signed October 1991**

**Phase I Remedial Design completed July 1992**

**Phase I Construction completed 1992**

**Phase II Remedial Design completed February 1994**

**Phase II Construction completed August 1996**

**Construction Completion Report September l997**

**First Five-year Review Report completed September 1 999** 

**Air monitoring termination approved 2000**

**Second Five-year Review Report completed September 2005** 

**Third Five-year Review Report completed September 2 010** 

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



# 3 B. Remedial Investigation/Feasibility Study

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

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

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

**human health and environmental effects that could r esult from exposure to contaminants associated with** 

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

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

**Sanitary Landfill site. These chemicals were selec ted as most representative of site conditions and** 

**expected to contribute the greatest risks to human health and the environment. The indicator chemical**  **s**

**for the site include: 1,2-dichloroethane, benzene, vinyl chloride, trichloroethylene, tetrachloroethy**  **lene,**

**chlorobenzene, 2-butanone, toluene, trans-1,2-dichl oroethylene, bis(2-ethylhexyl)phthalate, 1,4-** 

**dichloroethylene, 1,1,1-trichloroethane, ethylbenze ne, nickel, mercury, cadmium, zinc, chromium, and** 

**manganese.**

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

**objectives:**

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

**local population;**

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

**from restricting State-designated downstream surfac e water uses on the North Branch of** 

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

! **To protect people who perform military-related or u nauthorized recreational activities on the JB** 

**MDL property from potentially harmful effects due t o landfill contaminants;** 

! **To satisfy all appropriate local, State, and Federa l requirements for landfill closure;** 

! **To prevent significant adverse environmental impact s on the surrounding flora and fauna caused** 

**by contaminant release from the Dix Area Sanitary L andfill; and** 

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

**practicable.**

C. Selected Remedy and Implementation

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

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

**low-permeability layers. Maintenance of 2 ft of ex isting final cover on the remaining portion of** 

**the landfill.**

**This action was completed in 1992 and maintenance i s ongoing.** 

! **Installation of a landfill gas venting and air moni toring system to determine if methane gas and** 

**VOC emissions require treatment.**

**This action was completed in August 1996. Air moni toring was discontinued, with approval from** 

**all stake holders, in the year 2000.**

! **Installation of a chain link fence around the perim eter of the landfill to restrict access.** 

**Implementation of landfill closure requirements in accordance with New Jersey Closure** 

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

**Conservation and Recovery Act (RCRA) guidance.**

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



# 4 **This action was completed in August 1996 and mainte nance is ongoing.** 

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

**to the New Jersey State closure requirements. Perf orm a yearly statistical analysis on the** 

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

**This action is ongoing and is reviewed every 5 year s. Groundwater samples are collected from** 

**the network of groundwater monitoring wells, surfac e water and sediment samples are collected** 

**from the existing streams and air monitoring was co nducted at the landfill vents. Termination of** 

**air monitoring was approved in the year 2000.**

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

**This action is ongoing and is reviewed every 5 year s.** 

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

**groundwater in the immediate vicinity of the landfi ll.** 

**This action has been completed under the current Di x Area Master Plan.** 

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

**with the Soil Erosion and Sediment Control Act Regu lations of 1975 - New Jersey Statutes** 

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

**This action was completed in August 1996.**

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

**revise the risk assessment if the trend shows signi ficant changes in water quality. These reviews** 

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

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

**the revised risk assessments. Risk assessments wil l use USEPA guidance and policy effective at** 

**the time of the review.**

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

**Except for monitoring, no groundwater remedy was sp ecified because the contaminant plume could not** 

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

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

**contracts required for completion of the work. Pro fessional engineering services' for both phases wer**  **e**

**provided by Law Engineering and Environmental Servi ces, Inc. (Law Environmental).** 

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

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

**1992. The contractor for Phases I and II was the G eorge Hanus Co.** 

**Phase II included covering of the southernmost 50 a cres with a multilayer impermeable cap. The contra**  **ct**

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

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

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

**Engineer licensed in the State of New Jersey.**

**The remedial design, work plans, performance standa rds, construction quality control measures, O&M,** 

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

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

**design and construction activities, and have determ ined all activities were completed in accordance wi**  **th**

**the approved documents. USEPA made a final inspect ion of the completed work on March 28, 1998.** 

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



# 5 D. Institutional Controls

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

**Dix Area Sanitary Landfill have been implemented si nce the property is under the control and ownership** 

**of the Federal government. The Dix Area Master Pla n restricts Army use of the Dix Area Sanitary** 

**Landfill site including the surrounding impacted ar eas. In the event the landfill property were no lo**  **nger**

**under the control and ownership of the Federal Gove rnment, implementation of appropriate deed** 

**restrictions** or additional remediation to meet non-restricted us e standards **would be required to ensure**

**the remedy remains protective of human health and t he environment. In addition to the Dix Area Maste**  **r**

**Plan, the site is currently enrolled in the NJDEP C lassification Exception Area (CEA) program. The CE**  **A**

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

**groundwater until regulatory standards have been ac hieved.** 

E. Final Site Inspection

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

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

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

**features, cap integrity, site security, and site ma intenance.** 

**In general, the site was found to be in excellent c ondition. Site security was maintained with a 6-fo**  **ot**

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

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

**monitoring wells were in good condition and secure.**

**During 2009 site inspections, an invasive species o f weed was found growing on the cap, and the invasi**  **ve**

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

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

**landfill cap was reseeded.**

**Minor erosion features were noted on the western sl ope of the landfill cap that occurred between the** 

**Fourth Quarter 2009 and First Quarter 2010 inspecti ons. The inspection highlighted small gullies in t**  **he**

**landfill cap and areas where the eroded material ha d deposited silt in the perimeter drainage swale.** 

**During the April 2010 cap reseeding event the gulli es were repaired and drainage swales were cleared o**  **f**

**silt.**

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

**2010, the tree was removed and the fence was rebuil t.** 



# III. Monitoring Results

A. Air Monitoring

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

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

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

**NJDEP and USEPA in 2000.**

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



# 6 B. Groundwater Monitoring

**Nutrient metals are the only analytes exceeding scr eening criteria and exhibiting increasing concentra**  **tion**

**trends according to the Mann-Kendall Analysis. The se exceedances and increasing trends occur both** 

**upgradient and downgradient of the landfill.**

**In reviewing historical analytical data for this si te, it has been noted that nutrient metals have bee**  **n**

**consistently present at concentrations above screen ing criteria. In an effort to understand the geoch**  **emical**

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

**that several naturally-occurring characteristics of the local hydrogeology are contributing to the ele**  **vated**

**concentrations of nutrient metals in groundwater.**

**Fresh, uncontaminated groundwater in the Kirkwood-C ohansey aquifer system has naturally-occurring** 

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

**upgradient and downgradient locations. In the Kirk wood-Cohansey aquifer, calcium and bicarbonate are** 

**usually dominant ions in solution, with smaller amo unts of sodium, potassium, magnesium sulfate,** 

**manganese and chloride. The surficial aquifer unde rlying and adjacent to the Dix Area Sanitary Landfi**  **ll**

**exhibits persistent exceedances of calcium, magnesi um, manganese, sodium, and potassium that are** 

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

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

**pH. Elevated concentrations of manganese and iron are also attributed to reductive dissolution by met**  **al**

**reducing bacteria feeding on petroleum contaminants . The reduced form of both iron and manganese are** 

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

**events, water quality data collected indicated a sp oradic distribution of anaerobic and aerobic** 

**groundwater conditions. The data show both acid le aching and anaerobic degradation of gasoline** 

**contamination that is a waste of concern at the lan dfill, leading to elevated concentrations of mangan**  **ese**

**and iron.**

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

**downgradient of the landfill cap. These groundwate r monitoring locations were sampled for five** 

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

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

**results show no screening criteria exceedances were observed downgradient of the landfill and that COC**  **s**

**are below screening criteria at the landfill unit b oundary. The Addendum to the 2005 CERCLA Five** 

**Year Review (Plexus, 2009) concluded that manganese is naturally occurring and was removed as a COC** 

**from the program. After the evaluation of the prop osed sentinel wells, JBMDL proposed nine alternativ**  **e**

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

**concurred that this site may now be deleted from th e National Priorities List of Superfund and moved t**  **o**

**the site-wide Groundwater Classification Exception Area & Well Restriction Area Program. Wells LTM** 

**9, 10, 12, 13, 14, 17, 18, 34 & 36 are now designat ed as sentinel wells and shall be used for complian**  **ce**

**determination (** Figure 1, Attachment B **).**

C. Surface Water Monitoring

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

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

**presents the COC analytical results for the last th ree years. As part of the five-year review process**  **an**

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



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

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

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

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

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

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

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

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

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

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

**addendum concluded that the mercury exceedances are attributed to a separate site upgradient of the Di**  **x**

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

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

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

D. Sediment Monitoring

**The majority of the sediment location samples that exceed analyte concentrations contain nutrient meta**  **ls**

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

**COC analytical results for the last three years. A s part of the five-year review process an Ecologica**  **l Risk**

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

**including September 2009. With the exception of ch lorobenzene, manganese and mercury, there have** 

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

**chlorobenzene exceeds the screening criteria, it do es not exceed its respective ecological benchmark** 

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

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

**only sample location that exceeds screening criteri a is SD-9. SD-9 is situated northwest of the Dix A**  **rea**

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

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

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

**five year review addendum concluded that the mercur y exceedance is attributed to a separate site** 

**upgradient of the Dix Area Sanitary Landfill.**

**Low-level pesticide exceedances of dichlorodiphenyl dichloroethylene (DDE) and dichlorodiphenyl** 

**trichloroethane (DDT) occur at locations SD-5 and S D-6, but do not occur at the landfill boundary. DD**  **E**

**and DDT are ubiquitous to Fort Dix and are not cons idered COCs for the Dix Area Sanitary Landfill.** 

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

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

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

**location are attributed to a separate site upgradie nt of the Dix Area Sanitary Landfill.** 



# IV. Summary of Operation and Maintenance

**In general, O&M of the Dix Area Sanitary Landfill c onsists of the collection and analysis of groundwat**  **er,**

**sediment, and surface water samples; routine mowing ; limiting erosion; and maintaining site security.** 

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



# 8 **Site inspections are performed by a JB MDL represen tative every 30 days and after large rain events or** 

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

**basis. A compilation of these quarterly inspection reports is submitted to the regulatory agencies fo**  **r**

**review on annual basis.**

**For areas that do not have a landfill cap installed , visual observations are made to ensure run-on and** **run**

**off controls are performing as intended. Any expos ed waste in these areas is covered with compacted** 

**soil.**

**On the landfill cap, tree and brush growth is not a llowed for protection of the cap's liner system. A**  **reas of**

**settlement and damage by burrowing animals are repa ired as needed. The sediment and erosion control** 

**features are maintained by cleaning debris and accu mulated sediment to maintain proper infiltration an**  **d**

**prevent clogging of the outlet control structure an d emergency spillway. Since the last Five-year Rev**  **iew,**

**there has been evidence of minor burrowing activity ; however, the effects of the burrowing activity ha**  **ve**

**not impacted the landfill cap or the protectiveness of the remedy. When located, burrows are routinel**  **y**

**destroyed during the inspection process.**

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

**ensuring that the remedy remains protective into th e future. Site LUCs will continue under the curren**  **t**

**NJDEP CEA program for the site.**



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

**All construction, O&M, remediation and monitoring a ctivities associated with the Dix Area Sanitary** 

**Landfill were completed under direction of a Qualit y Assurance Project Plan, which provided quality** 

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

**performance of the remedial activities. After comp letion of an individual construction segment, the** 

**Quality Control Officer verified that the tasks wer e performed in compliance with the final plans and** 

**specifications and then provided a Compliance Repor t** 

**The Quality Control activities implemented used sta ndardized quality control procedures and provided t**  **he**

**necessary tests and observations for the constructi on, sampling and monitoring process at the Dix Area** 

**Sanitary Landfill.**



# VI. Five-year Review

A. Five-year Review Process

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

**Landfill at levels that will not allow for unrestri cted use. CERCLA Five-year Reviews will continue f**  **or**

**which the USEPA will retain lead regulatory respons ibility. The next Five-year Review for the Dix Are**  **a**

**Sanitary Landfill is required by September 2015. L ong Term Monitoring of groundwater, surface water** 

**and sediment will continue in accordance with Long- Term Monitoring Plan.** 

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



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

**The technical assessment summary from the Third Fiv e-year Review Report concluded that the remedy is** 

**functioning as intended and remains protective of h uman health and the environment. According to the** 

**data reviewed, the site inspection, and the intervi ews, the remedy is functioning as intended in the R**  **OD.**

**There were three issues highlighted in the review:**

**Issue Remedy** 

**Evidence of erosion along the western slope of the**

**landfill. Erosion was stabilized and vegetation cover was** 

**restored.**

**Fallen tree along the northern boundary perimeter**

**fence. Tree was removed and fence was restored.** 

**Lack of sentinel wells to delineate groundwater**

**COCs. Sentinel wells were selected or installed.** 

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

**affect the protectiveness of the remedy. Most ARAR s cited in the ROD have been met. There have been** 

**no changes in the toxicity factors for the COCs, an d there have been no changes to the standardized ri**  **sk**

**assessment methodology that may affect the protecti veness of the remedy.** 



# VII. Site Completion Criteria

**The remedial objectives set forth by the ROD includ e:** 

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

**water supplies of the local population;**

! **To prevent Dix Area Sanitary Landfill contaminant m igration/exposure via Cannon Run and** 

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

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

! **To protect people who perform military-related or u nauthorized recreational activities on the JB** 

**MDL property from potentially harmful effects due t o landfill contaminants;** 

! **To satisfy all appropriate local, State, and Federa l requirements for landfill closure;** 

! **To prevent significant adverse environmental impact s on the surrounding flora and fauna caused** 

**by contaminant release from the Dix Area Sanitary L andfill; and** 

! **To satisfy all site-specific ARARs as practicable.**

**The Dix Area Sanitary Landfill site meets all the s ite completion requirements as specified in the ROD** 

**,**

**and all of the remedial actions at the site have be en implemented. The implemented remedy achieves th**  **e**

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

**removal actions, remedial action objectives, and as sociated clean-up goals are consistent with USEPA** 

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



# 10 **and NJDEP policy and guidance. No further Superfun d response is needed to protect human health and** 

**the environment.**

**Continued implementation of the ICs and LTMP will e nsure the long-term protectiveness of the remedy.** 

**Currently, none of the COCs outlined in the ROD hav e migrated past the landfill unit boundary as** 

**evidenced by groundwater, surface water and sedimen t data collected.** 



# VIII. Bibliography

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

Draft Final **. US Army Corps of Engineers Baltimore District.**

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

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

**Geological Survey, West Trenton, NJ.**

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

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

**District.**

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

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

**Philadelphia District.**

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

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

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

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

**EA Engineering, Science, & Technologies, Inc. (2008 ). 2007 Sampling and Analysis Report for** 

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

**EA Engineering, Science, & Technologies, Inc. (2006 ). Addendum to the Long-Term Monitoring Plan for** 

**the Fort Dix Sanitary Landfill, Fort Dix, NJ. US Ar my Corps of Engineers Baltimore District.** 

**EA Engineering, Science, & Technologies, Inc. (2007 ). Addendum to the Long-Term Monitoring Plan for** 

**the Fort Dix Sanitary Landfill, Fort Dix, NJ. US Ar my Corps of Engineers Baltimore District.** 

**EA Engineering, Science, & Technologies, Inc. (2001 ). Mann-Kendall Statistical Analysis for 12 Rounds** 

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

**District.**

**EA Engineering, Science, & Technologies, Inc. (2001 ). Air Monitoring Report 4**  **th** 

# Quarter 2000, Landfill

**Gas Venting System, US Army Fort Dix, Fort Dix, New Jersey.**  Air Pollution Control Permit

Log# 01-93-4497.

**EA Engineering, Science, & Technologies, Inc. (2002 ). Addendum to the Long-Term Monitoring Plan for** 

**the Fort Dix Sanitary Landfill, Fort Dix, NJ. US Ar my Corps of Engineers Baltimore District.** 

**EA Engineering, Science, & Technologies, Inc. (2005 ). Second five Year Review, Fort Dix Sanitary** 

**(NPL) Landfill. US Army Corps of Engineers Omaha Di strict.** 

**NJDEP. (1985). In the Matter of Fort Dix Sanitary L andfill.**  Administrative Consent Order. **Robert E**

**Hughey, Commissioner.**

# Final Close Out Report Dix Area Sanitary Landfill

JB MDL, New Jersey



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

& Engineering Control.

**Plexus Scientific Corporation. (2009).** Sanitary Landfill 2008 Sampling and Analysis Report for

Groundwater, Surface water, and Sediment.

**Plexus Scientific Corporation. (2009).** Sentinel Well Installation Work Plan Sanitary Landf ill at Fort Dix,

New Jersey.

**Plexus Scientific Corporation. (2009).** Addendum to the 2005 CERCLA Five-Year Review for th e Fort Dix

Sanitary Landfill at Fort Dix, New Jersey.

**Plexus Scientific Corporation. (2009).** Addendum to the Long Term Monitoring Plan for the F ort Dix

Sanitary Landfill.

**Plexus Scientific Corporation. (2009).** General Maintenance Report for Corrective Measures Report

Sanitary Landfill Fort Dix, New Jersey.

**Plexus Scientific Corporation. (2010).** Sentinel Well Installation and Evaluation Report fo r the Fort Dix

Sanitary Landfill at Fort Dix , New Jersey.

**Plexus Scientific Corporation. (2011).** Sanitary Landfill 2009 Sampling and Analysis Report for The Joint

Base McGuire-Dix-Lakehurst Dix Area Sanitary Landfi ll.

**Plexus Scientific Corporation. (2011).** Biennial Certification Monitoring Report Form for a Deed Notice

& Engineering Control.

**Plexus Scientific Corporation. (2011).** Third Five-Year Review Report for The Joint Base Mc Guire-DixLakehurst Dix Area Sanitary Landfill.

**Plexus Scientific Corporation. (2011).** Sanitary Landfill 2010 Sampling and Analysis Report for The Joint

Base McGuire-Dix-Lakehurst Dix Area Sanitary Landfi ll.

**US Army. (1991). Record of Decision, Fort Dix Landf ill, Fort Dix Military Reservation, Pemberton** 

**Township, Burlington County, NJ.**

**US Army. (2007). Document of Environmental Indicato r Determination.**  RCRA Corrective Action,

**RCRIS code CA750, EPA ID# NJ4213720275.**

**US EPA Region II. (1989). In the Matter Of: The US Army Training Center & Fort Dix, Wrightstown,** 

**NJ.** Federal Facility Agreement

**.**

**USGS. (2008). Hydrologic Framework in Three Drainag e Basins in the New Jersey Pinelands, 2004-06.** 

Scientific Investigations Report 2008-5061 **. USGS Reston, VA.**

**USGS. (1998). Radium-226 and Radium-228 in Shallow Ground Water, Southern New Jersey.**  Fact Sheet

FS-062-98

**.**

# ATTACHMENT A

TABLESTable 1 - Sentinel Well Analytical Results2009 - 2011ScreeningAnalyte Value Unit Sep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-11 Sep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-111,1,1-Trichloroethane 30 μg/L 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.24 U 0.26 UJ 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.24 U1,1-Dichloroethane 50 μg/L 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.19 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.19 U1,2-Dichloroethane 2 μg/L 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.18 U 0.33 UJ 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.18 U2-Butanone (MEK) 300 μg/L 43.3 1.6 U 1.6 U 1.6 U 1.6 U 1.6 R 1.6 R 2.9 U 1.6 U 1.6 U 1.6 U 1.6 U 1.6 U 1.6 R 1.6 R 2.9 UBenzene 1 μg/L 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.22 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.22 UChlorobenzene 50 μg/L 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.22 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.22 UEthylbenzene 700 μg/L 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.21 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.21 UTetrachloroethene 1 μg/L 0.27 U 0.27 U 0.27 U 0.27 U 0.27 UJ 0.27 U 0.27 U 0.32 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 UJ 0.27 U 0.27 U 0.32 UToluene 1000 μg/L 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.15 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.15 Utrans-1,2-Dichloroethene 100 μg/L 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.31 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.31 UTrichloroethene 1 μg/L 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.21 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.21 UVinyl chloride 1 μg/L 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.27 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.27 U1,4-Dichlorobenzene 75 μg/L 0.39 U 0.39 U 0.41 U 0.39 U 0.4 U 0.4 U 0.39 U 0.4 U 21.8 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 Ubis(2-Ethylhexyl)phthalate 3 μg/L 0.33 U 0.33 U 0.35 U 0.33 U 1.5 J 1.1 J 0.33 U 0.34 U 0.36 U 0.33 U 0.33 U 0.33 U 1.3 J 0.33 U 1.3 J 0.33 UCadmium 4 μg/L 0.4 U 0.4 U 0.35 U 0.35 U 0.35 U 0.17 U 0.2 U 0.17 U 0.4 U 0.4 U 0.35 U 0.35 U 0.35 U 0.17 U 0.2 U 0.17 UChromium 70 μg/L 0.9 U 0.9 U 0.59 U 10 U 10 U 1.4 J 1.6 U 0.9 U 0.9 U 0.9 U 0.59 U 10 U 10 U 0.9 U 0.9 U 10 UManganese 92.6 μg/L 15 U 11 J 15 U 15 U 15 U 13.3 U 11.5 J 8.8 J 15.3 15 U 15 U 11.2 J 15 U 10.8 U 12 U 15 UMercury 2 μg/L 0.082 U 0.082 U 0.082 U 0.082 U 0.088 UJ 0.088 U 0.088 U 0.088 U 0.082 U 0.082 U 0.082 U 0.082 U 0.1 J 0.088 U 0.088 U 0.088 UNickel 100 μg/L 10 U 1.2 J 0.51 U 10 U 10 U 1.8 U 1.2 J 0.7 J 10 U 0.6 U 0.51 U 10 U 0.51 U 0.41 U 0.6 U 1.4 JZinc 2000 μg/L 11.9 J 20 U 20 U 20 U 20 U 15.9 J 35.3 7.8 J 7.1 J 2.9 U 1.4 U 20 U 20 U 1.9 J 4.4 U 1.7 UIndicates the analyte is not detected or not sampled!g/L - Micrograms per LiterA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriaA cell highlighted and not bold Inidcates a detectedl tthat does not exceed the screening criteriaR - Rejected DataQualifier Key:U - Analyte not detected in the sample. Valuetthe quantitation/detection limit.UJ - Analyte was not detected in the sample, actualquantitation/detection limit may be higher thanreported value.J - Result reported is a quantitative estimateVolatile Organic CompoundsSemivolatile Organic CompoundsMetalsLTM-31LTM-3812/21/2011 7:22 PMPage 1 of 4Table 1 - Sentinel Well Analytical Results2009 - 2011ScreeningAnalyte Value Unit1,1,1-Trichloroethane 30 μg/L1,1-Dichloroethane 50 μg/L1,2-Dichloroethane 2 μg/L2-Butanone (MEK) 300 μg/LBenzene 1 μg/LChlorobenzene 50 μg/LEthylbenzene 700 μg/LTetrachloroethene 1 μg/LToluene 1000 μg/Ltrans-1,2-Dichloroethene 100 μg/LTrichloroethene 1 μg/LVinyl chloride 1 μg/L1,4-Dichlorobenzene 75 μg/Lbis(2-Ethylhexyl)phthalate 3 μg/LCadmium 4 μg/LChromium 70 μg/LManganese 92.6 μg/LMercury 2 μg/LNickel 100 μg/LZinc 2000 μg/LIndicates the analyte is not detected or not sampled!g/L - Micrograms per LiterA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriaA cell highlighted and not bold Inidcates a detectedl tthat does not exceed the screening criteriaR - Rejected DataQualifier Key:U - Analyte not detected in the sample. Valuetthe quantitation/detection limit.UJ - Analyte was not detected in the sample, actualquantitation/detection limit may be higher thanreported value.J - Result reported is a quantitative estimateVolatile Organic CompoundsSemivolatile Organic CompoundsMetalsSep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-11 Sep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-110.26 U 0.26 U 0.51 U 0.26 U 0.51 U 0.26 U 0.26 U 0.24 U 0.26 UJ 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.24 U0.29 U 0.29 U 0.57 U 0.29 U 0.57 U 0.29 U 0.29 U 0.19 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.19 U0.33 U 0.33 U 0.67 U 0.33 U 0.67 U 0.33 U 0.33 U 0.18 U 0.33 UJ 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.18 U1.6 U 1.6 U 3.2 U 1.6 U 3.2 U 1.6 R 1.6 R 2.9 U 1.6 U 1.6 R 1.6 U 1.6 U 1.6 U 1.6 R 1.6 R 2.9 U0.23 U 0.23 U 0.47 U 0.23 U 0.47 U 0.23 U 0.23 U 0.22 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.22 U0.39 U 0.39 U 0.78 U 0.39 U 0.78 U 0.39 U 0.39 U 0.22 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.22 U0.27 U 0.27 U 0.54 U 0.27 U 0.54 U 0.27 U 0.27 U 0.21 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.21 U0.27 U 0.27 U 0.53 U 0.27 U 0.53 U 0.27 U 0.27 U 0.32 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.32 U1.7 0.3 U 0.6 U 0.3 U 0.6 U 0.3 U 0.3 U 0.15 U 0.38 J 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.15 U0.25 U 0.25 U 0.5 U 0.25 U 0.5 U 0.25 U 0.25 U 0.31 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.31 U0.24 U 0.24 U 0.48 U 0.24 U 0.48 U 0.24 U 0.24 U 0.21 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.21 U0.44 U 0.44 U 0.89 U 0.44 U 0.89 U 0.44 U 0.44 U 0.27 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.27 U16.9 U 0.42 U 0.4 U 0.39 U 0.41 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.43 U 0.39 U 0.45 U 0.41 U 0.43 U 0.39 U2 U 0.36 U 0.34 U 0.33 U 0.35 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.36 U 0.33 U 0.38 U 0.34 U 1.3 J 0.33 U0.4 U 0.4 U 0.35 U 0.35 U 0.35 U 0.17 U 0.17 U 0.17 U 0.4 U 0.4 U 0.35 U 0.35 U 0.35 U 0.17 U 3 U 0.17 U35.3 31.5 23.7 25.9 10.4 8.8 J 4.6 U 10 U 1.7 J 0.9 U 10 U 10 U 10 U 2.4 J 3.8 J 0.9 U12876.4 48.9 62.6154 128 123 22929.5 18.7 18.6 17.2 17.4 12.5 U 15 U 19.30.082 U 0.082 U 0.082 U 0.082 U 0.11 J 0.088 U 0.088 U 0.11 J 0.082 U 0.082 U 0.082 U 0.082 U 0.088 U 0.088 U 0.088 U 0.088 U10.1 10 U 1.7 J 10 U 10 U 2.6 U 1.6 J 4 J 10 U 0.9 J 0.51 U 10 U 10 U 2.5 U 10 U 0.6 J52.6 20 U 52.9 20 U 20 U 20.3 13.8 U 32.2 9.9 J 20 U 20 U 20 U 76 34.6 4.9 J 20 ULTM-40LTM-4112/21/2011 7:22 PMPage 2 of 4Table 1 - Sentinel Well Analytical Results2009 - 2011ScreeningAnalyte Value Unit1,1,1-Trichloroethane 30 μg/L1,1-Dichloroethane 50 μg/L1,2-Dichloroethane 2 μg/L2-Butanone (MEK) 300 μg/LBenzene 1 μg/LChlorobenzene 50 μg/LEthylbenzene 700 μg/LTetrachloroethene 1 μg/LToluene 1000 μg/Ltrans-1,2-Dichloroethene 100 μg/LTrichloroethene 1 μg/LVinyl chloride 1 μg/L1,4-Dichlorobenzene 75 μg/Lbis(2-Ethylhexyl)phthalate 3 μg/LCadmium 4 μg/LChromium 70 μg/LManganese 92.6 μg/LMercury 2 μg/LNickel 100 μg/LZinc 2000 μg/LIndicates the analyte is not detected or not sampled!g/L - Micrograms per LiterA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriaA cell highlighted and not bold Inidcates a detectedl tthat does not exceed the screening criteriaR - Rejected DataQualifier Key:U - Analyte not detected in the sample. Valuetthe quantitation/detection limit.UJ - Analyte was not detected in the sample, actualquantitation/detection limit may be higher thanreported value.J - Result reported is a quantitative estimateVolatile Organic CompoundsSemivolatile Organic CompoundsMetalsSep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-11 Sep-09 Nov-09 Apr-10 May-10 Feb-11 May-11 Jul-110.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.24 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.24 U0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.19 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.19 U0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.18 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.18 U1.6 U 1.6 R 1.6 U 1.6 U 1.6 U 1.6 R 1.6 R 2.9 U 1.6 U 1.6 U 1.6 U 1.6 U 1.6 R 1.6 R 2.9 U0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.22 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.22 U0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.22 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.22 U0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.21 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.21 U0.27 U 0.27 U 0.27 U 0.44 J 0.27 U 0.27 U 0.27 U 0.32 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.32 U0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.15 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.15 U0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.31 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.31 U0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.21 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.21 U0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.27 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.27 U0.42 U 0.39 U 0.39 U 0.39 U 0.39 U 0.46 U 0.43 U 0.4 U 0.39 U 0.42 U 0.44 U 0.39 U 0.39 U 0.43 U 0.39 U0.36 U 0.33 U 0.33 U 0.33 U 0.33 U 0.38 U 0.36 U 0.34 U 0.33 U 0.35 U 0.37 U 0.33 U 0.33 U 2 J 0.33 U0.4 U 0.4 U 0.35 U 0.35 U 0.35 U 0.17 U 0.17 U 0.17 U 0.4 U 0.4 U 3 U 3 U 0.17 U 2.6 U 3.510 U 2.2 J 10 U 10 U 10 U 1.4 J 1.1 J 10 U 1 J 2.6 J 0.59 U 10 U 1 J 0.9 U 10 U15.7 17.1 15 U 15 U 15.1 15.8 15 U 15 U 23.5 23.110069.4 29.3604 6270.082 U 0.082 U 0.082 U 0.082 U 0.14 J 0.088 U 0.088 U 0.11 J 0.082 U 0.082 U 0.082 U 0.082 U 0.088 U 0.088 U 0.1 J10 U 2 J 10 U 10 U 2.4 J 1.8 U 10 U 1.3 J 0.6 U 1.4 J 6.2 J 10 U 2.2 U 17.1 31.311.7 J 20 U 20 U 20 U 95.7 28.4 9 J 28.3 7.6 J 20 U 23.6 20 U 65.5 85.3 92.6LTM-42LTM-4312/21/2011 7:22 PMPage 3 of 4Table 1 - Sentinel Well Analytical Results2009 - 2011ScreeningAnalyte Value Unit1,1,1-Trichloroethane 30 μg/L1,1-Dichloroethane 50 μg/L1,2-Dichloroethane 2 μg/L2-Butanone (MEK) 300 μg/LBenzene 1 μg/LChlorobenzene 50 μg/LEthylbenzene 700 μg/LTetrachloroethene 1 μg/LToluene 1000 μg/Ltrans-1,2-Dichloroethene 100 μg/LTrichloroethene 1 μg/LVinyl chloride 1 μg/L1,4-Dichlorobenzene 75 μg/Lbis(2-Ethylhexyl)phthalate 3 μg/LCadmium 4 μg/LChromium 70 μg/LManganese 92.6 μg/LMercury 2 μg/LNickel 100 μg/LZinc 2000 μg/LIndicates the analyte is not detected or not sampled!g/L - Micrograms per LiterA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriaA cell highlighted and not bold Inidcates a detectedl tthat does not exceed the screening criteriaR - Rejected DataQualifier Key:U - Analyte not detected in the sample. Valuetthe quantitation/detection limit.UJ - Analyte was not detected in the sample, actualquantitation/detection limit may be higher thanreported value.J - Result reported is a quantitative estimateVolatile Organic CompoundsSemivolatile Organic CompoundsMetalsSep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-11 Sep-09 Nov-09 Apr-10 May-10 Oct-10 Feb-11 May-11 Jul-110.26 UJ 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.24 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.24 U0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.19 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.19 U0.33 UJ 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.18 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.33 U 0.18 U1.6 U 1.6 U 1.6 U 1.6 U 1.6 U 1.6 R 1.6 R 2.9 U 1.6 U 1.6 R 1.6 U 1.6 U 1.6 U 1.6 R 1.6 R 2.9 U0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.22 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.22 U0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.22 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.22 U0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.21 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.21 U0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.32 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.32 U0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.15 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.15 U0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.31 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.25 U 0.31 U0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.21 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.21 U0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.27 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.27 U0.4 U 0.39 U 0.4 U 0.39 U 0.44 U 0.42 U 0.39 U 0.39 U 0.39 U 0.39 U 0.42 U 0.4 U 0.39 U 0.41 U 0.39 U 0.4 U0.33 U 1.3 J 0.34 U 0.33 U 0.37 U 0.36 U 0.33 U 0.33 U 0.33 U 0.33 U 0.35 U 0.33 U 0.33 U 0.35 U 0.33 U 0.34 U0.4 U 0.4 U 0.35 U 0.35 U 0.35 U 0.2 U 3 U 0.17 U 3 U 3 U 0.52 U 3 U 3 U 0.5 U 3 U 3 U0.9 U 10.8 13.6 10 U 10 U 3.9 J 10 U 5 J 0.9 U 1.2 J 10 U 10 U 10 U 0.9 U 0.9 U 10 U58.7 62.9 86.7 73.7 57.6 66.1 75.1 50 39.4 33.4 49.4 33.1 29.4 28.2 27.4 31.60.082 U 0.082 U 0.082 U 0.082 U 0.19 J 0.088 U 0.088 U 0.088 U 0.082 U 0.082 U 0.082 U 0.082 U 0.1 J 0.088 U 0.088 U 0.088 U10 U 0.6 U 1.1 J 10 U 0.51 U 0.5 U 10 U 2 J 10 U 3.9 J 10 U 10 U 3.9 J 3.9 U 10 U 4.5 J7.4 J 20 U 20 U 20 U 10 U 26.6 20 U 20 U 10.2 J 20 U 20 U 20 U 20 U 25 20 U 42.4LTM-44LTM-4512/21/2011 7:22 PMPage 4 of 4Table 2 - Surface Water Analytical Results2009 - 2011ScreeningAnalyte Value Unit Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-111,1,1-Trichloroethane 120 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NS1,1-Dichloroethane 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NS1,2-Dichloroethane 2 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NS1,2-Dichloroethene (total) μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NS2-Butanone (MEK) 2 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NSBenzene 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NSChlorobenzene 100 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NSEthylbenzene 530 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NSTetrachloroethene 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NSToluene 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NSTrichloroethene 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NSVinyl chloride 1 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NS1,4-Dichlorobenzene 75 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NSbis(2-Ethylhexyl)phthalate 3 μg/L NS NS NS NS NS NS NS NS NS NS NS NS NS NSCadmium 3.4 μg/L 0.4 U 0.35 U 3 U 0.2 U 0.4 U 0.4 U 0.4 J 0.35 U 0.17 U 0.4 U 0.4 U 0.35 U 0.35 U 0.17 UChromium 92 μg/L 0.9 J 1.8 J 10 U 1 U 0.9 U 1.5 J 1.3 J 10 U 0.9 U 1.1 J 0.9 U 0.8 J 10 U 0.9 UManganese 50 μg/L 38.5 38.5 35.5 32 35.3 36.2 29.6 45.7 35.170.829.1 49.5 42.3 J71.7Mercury 0.05 μg/L0.230.082 U0.19 J 0.18 J 0.14 J 0.3 0.15 J 0.12 J 0.14 JNS NS NS NS NSNickel 500 μg/L 10 U 1.8 J 1.9 J 2.1 J 1.5 J 10 U 4.7 J 10 U 1.7 J 2.1 J 10 U 1.4 J 10 U 0.9 JZinc 7,400 μg/L 19.5 J 25.9 20 U 22.9 18.6 J 248 41.2 20 U 17.1 J 13.1 J 4.6 J 30.6 J 20 U 6.4 JpCi/L - Picocuries per LiterR - Rejected DataIndicates the analyte is not detected or not sampledNS - Not Sampled!g/L - Micrograms per LiterA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriaA cell highlighted and not bold Inidcates a detected analytethat does not exceed the screening criteriathe quantitation/detection limit.UJ - Analyte was not detected in the sample, actualquantitation/detection limit may be higher thanreported value.J - Result reported is a quantitative estimateMetalsQualifier Key:U - Analyte not detected in the sample. Value representsVolatile Organic CompoundsSemivolatile Organic CompoundsSW-1SW-2SW-312/21/2011 7:35 PMPage 1 of 3Table 2 - Surface Water Analytical Results2009 - 2011ScreeningAnalyte Value Unit1,1,1-Trichloroethane 120 μg/L1,1-Dichloroethane 1 μg/L1,2-Dichloroethane 2 μg/L1,2-Dichloroethene (total) μg/L2-Butanone (MEK) 2 μg/LBenzene 1 μg/LChlorobenzene 100 μg/LEthylbenzene 530 μg/LTetrachloroethene 1 μg/LToluene 1 μg/LTrichloroethene 1 μg/LVinyl chloride 1 μg/L1,4-Dichlorobenzene 75 μg/Lbis(2-Ethylhexyl)phthalate 3 μg/LCadmium 3.4 μg/LChromium 92 μg/LManganese 50 μg/LMercury 0.05 μg/LNickel 500 μg/LZinc 7,400 μg/LpCi/L - Picocuries per LiterR - Rejected DataIndicates the analyte is not detected or not sampledNS - Not Sampled!g/L - Micrograms per LiterA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriaA cell highlighted and not bold Inidcates a detected analytethat does not exceed the screening criteriathe quantitation/detection limit.UJ - Analyte was not detected in the sample, actualquantitation/detection limit may be higher thanreported value.J - Result reported is a quantitative estimateMetalsQualifier Key:U - Analyte not detected in the sample. Value representsVolatile Organic CompoundsSemivolatile Organic CompoundsMay-09 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11NS NS NS NS NS NS 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U 0.26 UNS NS NS NS NS NS 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 U 0.29 UNS NS NS NS NS NS 0.33 U 0.33 U 0.33 U 0.33 UJ 0.33 U 0.33 U 0.33 U 0.33 U 0.33 UJ 0.33 UNS NS NS NS NS NS 0.22 U 0.22 U 0.22 U 0.22 U 0.22 U 0.22 U 0.22 U 0.22 U 0.22 U 0.22 UNS NS NS NS NS NS NS 1.6 U NS NS NS NS NS NS NS NSNS NS NS NS NS NS 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U 0.23 UNS NS NS NS NS NS 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 UNS NS NS NS NS NS 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 UNS NS NS NS NS NS 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U 0.27 UNS NS NS NS NS NS 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U 1 0.3 U 0.3 U 0.3 UNS NS NS NS NS NS 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U 0.24 UNS NS NS NS NS NS 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U 0.4 U 0.39 U 0.39 U NS NS NS NS NS0.33 U 1.2 J 0.33 U 0.33 U 0.33 U 1.2 J 1.4 J 0.33 U 0.34 U 0.33 U 0.33 U NS NS NS NS NS0.4 U 0.4 U 0.4 U 0.35 U 0.35 U 0.17 U 0.4 U 0.4 U 0.35 U 0.35 U 0.17 U 0.4 U 0.4 U 0.35 U 0.35 U 0.17 U2.4 J 1.3 J 10 U 1 J 10 U 0.9 U 1.1 J 10 U 0.9 J 10 U 0.9 U 1.2 J 10 U 1 J 10 U 0.9 U167 173 10042.2145 63.5 205 145 56.5 50546.9134 15849.6196 1350.049 U 0.049 U 0.082 U 0.082 U NS 0.088 U NS NS NS NS 0.088 U NS NS NS NS NS2.2 J 1.9 J 10 U 0.51 U 10 U 0.9 U 1.6 J 10 U 2 J 10 U 0.9 U 2.7 J 10 U 1.4 J 10 U 1.1 J22.7 36.3 18.4 J 5.4 J 20 U 3.6 U 9.5 J 12.8 J 60.8 20 U 6.7 U 28.3 114 36.7 20 U 5.8 USW-4SW-5SW-612/21/2011 7:35 PMPage 2 of 3Table 2 - Surface Water Analytical Results2009 - 2011ScreeningAnalyte Value Unit1,1,1-Trichloroethane 120 μg/L1,1-Dichloroethane 1 μg/L1,2-Dichloroethane 2 μg/L1,2-Dichloroethene (total) μg/L2-Butanone (MEK) 2 μg/LBenzene 1 μg/LChlorobenzene 100 μg/LEthylbenzene 530 μg/LTetrachloroethene 1 μg/LToluene 1 μg/LTrichloroethene 1 μg/LVinyl chloride 1 μg/L1,4-Dichlorobenzene 75 μg/Lbis(2-Ethylhexyl)phthalate 3 μg/LCadmium 3.4 μg/LChromium 92 μg/LManganese 50 μg/LMercury 0.05 μg/LNickel 500 μg/LZinc 7,400 μg/LpCi/L - Picocuries per LiterR - Rejected DataIndicates the analyte is not detected or not sampledNS - Not Sampled!g/L - Micrograms per LiterA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriaA cell highlighted and not bold Inidcates a detected analytethat does not exceed the screening criteriathe quantitation/detection limit.UJ - Analyte was not detected in the sample, actualquantitation/detection limit may be higher thanreported value.J - Result reported is a quantitative estimateMetalsQualifier Key:U - Analyte not detected in the sample. Value representsVolatile Organic CompoundsSemivolatile Organic CompoundsSep-09 Apr-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 Sep-09 Apr-10 Oct-10 May-11 Sep-09 Apr-10 Oct-10 May-11NS NS NS 0.26 U 0.26 U 0.26 U 0.26 U 0.26 U NS NS NS NS NS NS NS NSNS NS NS 0.44 J 0.29 U 0.29 U 0.29 U 0.29 U NS NS NS NS NS NS NS NSNS NS NS 0.33 U 0.33 U 0.33 U 0.33 UJ 0.33 U NS NS NS NS NS NS NS NSNS NS NS 0.22 U 0.62 J 0.51 J 0.53 J 0.22 U NS NS NS NS NS NS NS NSNS NS NS NS NS NS NS NS NS NS NS NS NS NS NS NSNS NS NS 0.23 U 0.23 U 0.23 U 0.23 U 0.23 U NS NS NS NS NS NS NS NSNS NS NS 0.39 U 0.39 U 0.39 U 0.39 U 0.39 U NS NS NS NS NS NS NS NSNS NS NS 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U NS NS NS NS NS NS NS NSNS NS NS 0.27 U 0.27 U 0.27 U 0.27 U 0.27 U NS NS NS NS NS NS NS NSNS NS NS 0.3 U 0.3 U 0.3 U 0.3 U 0.3 U NS NS NS NS NS NS NS NSNS NS NS 0.24 U 0.24 U 0.24 U 0.24 U 0.24 U NS NS NS NS NS NS NS NSNS NS NS 0.44 U 0.44 U 0.44 U 0.44 U 0.44 U NS NS NS NS NS NS NS NS0.43 U 0.44 U 0.4 U NS NS NS NS NS NS NS NS NS 0.39 U 0.39 U 0.39 U 0.39 U0.36 U 0.37 U 1.1 J NS NS NS NS NS NS NS NS NS 0.33 U 0.33 U 0.33 U 1.3 J0.4 U 0.35 U 1.2 J 0.4 U 0.4 U 0.35 U 0.35 U 0.17 U 0.4 U 0.35 U 0.35 U 0.17 U 0.4 U 0.35 U 0.35 U 0.17 U0.9 U 1.2 J 4.5 J 5.6 J 0.9 U 2 J 10 U 0.9 U 0.9 U 10 U 10 U 1.3 U 0.9 U 0.59 U 10 U 1 J47.4 13.7 J566 465 316 189 479 8846.8 18.2 31 29.6 2955.8 152 59.40.082 U 0.082 U 0.088 U 0.049 U 0.082 U 0.082 U 0.088 U 0.088 U0.48 0.85 0.28 0.370.082 U 0.082 U 0.088 U 0.088 U1.1 J 10 U 4.2 U 6.8 J 1.7 J 10 U 10 U 1.3 U 10 U 10 U 10 U 1.9 U 10 U 10 U 10 U 1 J19.9 J 136 465 48.1 3.2 J 54.8 28.7 3 U 3.5 J 36.6 20 U 13.8 U 7.9 J 4.3 J 28.8 111SW-7SW-8SW-10SW-912/21/2011 7:35 PMPage 3 of 3Table 3 - Sediment Analytical Results2009 - 2011ScreeningAnalyte Value Unit May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-111,1,1-Trichloroethane 4.4 μg/kg 0.15 U 0.14 U 0.13 U 0.17 U 0.12 U 0.17 U 0.14 U 0.14 U 0.098 U 0.12 U 0.2 U 0.081 U 0.15 U 0.14 U 0.14 U1,1-Dichloroethane 2.3 μg/kg 0.17 U 0.15 U 0.14 U 0.18 U 0.13 U 0.18 U 0.16 U 0.15 U 0.11 U 0.13 U 0.21 U 0.088 U 0.17 U 0.15 U 0.15 U1,2-Dichloroethane 1.7 μg/kg 0.41 U 0.38 U 0.35 U 0.46 U 0.33 U 0.45 U 0.39 U 0.37 U 0.26 U 0.33 U 0.54 U 0.22 U 0.42 U 0.38 U 0.39 U1,2-Dichloroethene (total) μg/kg 0.29 U 0.26 U 0.24 U 0.32 U 0.23 U 0.31 U 0.27 U 0.26 U 0.18 U 0.23 U 0.37 U 0.15 U 0.29 U 0.27 U 0.27 U2-Butanone (MEK) 70 μg/kg NS NS 2 U NS 1.9 U NS NS 2.1 U 1.5 U 1.9 U NS NS 2.4 U 2.2 U 2.2 UBenzene 340 μg/kg 0.41 U 0.37 U 0.34 U 0.45 U 0.32 U 0.44 U 0.38 U 0.37 U 0.26 U 0.33 U 0.53 U 0.22 U 0.41 U 0.38 U 0.38 UChlorobenzene 0.86 μg/kg 0.41 U 0.37 U 0.34 U 0.45 U 0.32 U 0.44 U 0.38 U 0.37 U 0.26 U 0.33 U 0.53 U 0.22 U 0.41 U 0.38 U 0.38 UEthylbenzene 1,400 μg/kg 0.44 U 0.4 U 0.37 U 0.49 U 0.35 U 0.48 U 0.42 U 0.4 U 0.28 U 0.36 U 0.58 U 0.24 U 0.45 U 0.41 U 0.42 UTetrachloroethene 450 μg/kg 0.17 U 0.16 U 0.15 U 0.19 U 0.14 U 0.19 U 0.16 U 0.16 U 0.11 U 0.14 U 0.22 U 0.092 U 0.17 U 0.16 U 0.16 UToluene 2,500 μg/kg 0.35 U 0.32 U 0.73 J 0.39 U 0.28 U 0.38 U 0.33 U 1.5 0.22 U 0.28 U 0.93 J 0.19 U 1.5 0.32 U 0.33 UTrichloroethene 1,600 μg/kg 0.63 U 0.57 U 0.53 U 0.7 U 0.5 U 0.68 U 0.59 U 0.57 U 0.4 U 0.51 U 0.82 U 0.33 U 0.63 U 0.58 U 0.59 UVinyl chloride 6.2 μg/kg 0.21 U 0.19 U 0.18 U 0.24 U 0.17 U 0.23 U 0.2 U 0.19 U 0.14 U 0.17 U 0.28 U 0.11 U 0.21 U 0.2 U 0.2 U1,4-Dichlorobenzene 98 μg/kg 15 U 13 U 7.8 U 7.6 U 7.6 U 17 U 14 U 8 U 7.4 U 7.5 U 20 U 7.7 U 7.7 U 8.6 U 7.6 Ubis(2-Ethylhexyl)phthalate 620 μg/kg 21 U 18 U 31 U 30 U 30 U 23 U 19 U 32 U 29 U 30 U 28 U 31 U 30 U 34 U 30 UCadmium 0.6 mg/kg 0.034 U 0.037 U 0.05 U 0.028 U 0.041 U 0.04 U 0.036 U 0.051 U 0.027 U 0.04 U 0.2 J 0.036 U 0.08 J 0.5 U 0.04 UChromium 26 mg/kg 7.4 1.5 1.3 U 1.3 U 0.98 J 2 1 J 1.3 U 1.2 U 3.5 8.1 1.8 2.3 2.6 1.8Manganese 8.04 mg/kg 5.1 J 5.1 1.9 U 4.1 3.511 J 10.23.1 514.5 45.1 J 8.95.111.2 J 9.8Mercury 0.2 mg/kg 0.047 0.026 J 0.014 U 0.03 J 0.024 J 0.034 J 0.063 0.039 0.07 0.091 NS NS 0.013 U NS NSNickel 16 mg/kg 4.6 U 0.17 J 0.2 J 0.28 J 0.21 J 5.4 U 0.24 J 0.12 U 0.11 J 0.33 J 6.7 U 0.38 J 0.42 J 0.75 J 0.47 JZinc 120 mg/kg 9.8 J 3.3 2.9 2.9 2.2 J 4.4 J 2.5 1.6 J 2.5 U 2.8 18.6 J 3.2 3.7 7.3 3.8R - Rejected DataA cell highlighted and not bold Inidcates a detected analytethat does not exceed the screening criteriaIndicates the analyte is not detected or not sampledNS - Not Sampledmg/kg - Milligrams per Kilograms!g/kg - Micrograms per KilogramsA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriathe quantitation/detection limit.UJ - Analyte was not detected in the sample, actualquantitation/detection limit may be higher thanreported value.J - Result reported is a quantitative estimateMetalsQualifier Key:U - Analyte not detected in the sample. Value representsVolatile Organic CompoundsSemivolatile Organic CompoundsSD-1SD-2SD-312/21/2011 7:54 PMPage 1 of 3Table 3 - Sediment Analytical Results2009 - 2011ScreeningAnalyte Value Unit1,1,1-Trichloroethane 4.4 μg/kg1,1-Dichloroethane 2.3 μg/kg1,2-Dichloroethane 1.7 μg/kg1,2-Dichloroethene (total) μg/kg2-Butanone (MEK) 70 μg/kgBenzene 340 μg/kgChlorobenzene 0.86 μg/kgEthylbenzene 1,400 μg/kgTetrachloroethene 450 μg/kgToluene 2,500 μg/kgTrichloroethene 1,600 μg/kgVinyl chloride 6.2 μg/kg1,4-Dichlorobenzene 98 μg/kgbis(2-Ethylhexyl)phthalate 620 μg/kgCadmium 0.6 mg/kgChromium 26 mg/kgManganese 8.04 mg/kgMercury 0.2 mg/kgNickel 16 mg/kgZinc 120 mg/kgR - Rejected DataA cell highlighted and not bold Inidcates a detected analytethat does not exceed the screening criteriaIndicates the analyte is not detected or not sampledNS - Not Sampledmg/kg - Milligrams per Kilograms!g/kg - Micrograms per KilogramsA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriathe quantitation/detection limit.UJ - Analyte was not detected in the sample, actualquantitation/detection limit may be higher thanreported value.J - Result reported is a quantitative estimateMetalsQualifier Key:U - Analyte not detected in the sample. Value representsVolatile Organic CompoundsSemivolatile Organic CompoundsMay-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 May-110.19 U 0.11 U 0.14 U 0.14 U 0.14 U 0.17 U 0.1 U 0.17 U 0.29 UJ 0.17 U 0.39 U 0.099 U 0.12 U 0.12 U 0.16 U NS NS NS NS0.21 U 0.12 U 0.15 U 0.15 U 0.15 U 0.19 U 0.11 U 0.18 U 0.31 UJ 0.18 U 0.42 U 0.11 U 0.13 U 0.13 U 0.17 U NS NS NS NS0.52 U 0.3 U 0.38 U 0.37 U 0.37 U 0.47 U 0.27 U 0.44 U 0.77 UJ 0.45 U 1.1 U 0.27 U 0.34 U 0.33 U 0.43 U NS NS NS NS0.36 U 0.21 U 0.26 U 0.26 U 0.26 U 0.32 U 0.19 U 0.31 U 0.54 UJ 0.31 U 0.73 U 0.19 U 0.23 U 0.23 U 0.3 U NS NS NS NSNS NS 2.2 U 2.1 U 2.1 U NS NS 2.5 U 4.4 UJ 2.6 U 57.2 J NS 1.9 U 1.9 U 2.5 U NS NS NS NS0.51 U 0.29 U 0.38 U 0.37 U 0.37 U 0.46 U 0.27 U 0.44 U 0.76 UJ 0.44 U 1 U 0.26 U 0.33 U 0.32 U 0.43 U NS NS NS NS2 J0.59 J5.8 1 J 7.60.46 U 0.26 U 0.44 U 0.76 UJ 0.44 U 1 U 0.26 U 0.33 U 0.32 U 0.42 U NS NS NS NS0.56 U 0.32 U 0.41 U 0.4 U 0.4 U 0.5 U 0.29 U 0.48 U 0.83 UJ 0.48 U 1.1 U 0.29 U 0.36 U 0.35 U 0.46 U NS NS NS NS0.22 U 0.13 U 0.16 U 0.16 U 0.16 U 0.2 U 0.11 U 0.19 U 0.32 UJ 0.19 U 0.44 U 0.11 U 0.14 U 0.14 U 0.18 U NS NS NS NS1.3 J 0.25 U 1.1 1.4 0.99 J 0.4 U 0.23 U 1.3 0.65 UJ 0.38 U 0.89 U 0.23 U 0.78 J 5 0.37 U NS NS NS NS0.79 U 0.45 U 0.58 U 0.57 U 0.57 U 0.71 U 0.41 U 0.68 U 1.2 UJ 0.68 U 1.6 U 0.41 U 0.51 U 0.5 U 0.66 U NS NS NS NS0.27 U 0.15 U 0.2 U 0.19 U 0.19 U 0.24 U 0.14 U 0.23 U 0.4 UJ 0.23 U 0.54 U 0.14 U 0.17 U 0.17 U 0.22 U NS NS NS NS19 U 8.4 U 7.9 U 9.2 U 8.5 U 18 U 9.7 U 7.9 U98.8 J8.9 U 42 U 19 U 7.8 U 8.6 U 8.6 U 18 U 15 U 9.8 U 7.8 U26 U 33 U 31 U 37 U 34 U 24 U 38 U 31 U 54 UJ 77.6 J 57 U 25 U 31 U 34 U 34 U 95 U 20 U 39 U 31 U7.7 J0.63 U 0.05 U 0.03 J 0.047 U 0.042 J 0.047 U 0.049 U0.64 J0.049 U 0.22 J 0.86 U 0.047 U 0.49 U 0.046 U 0.42 J 0.041 U 0.52 J 0.042 U4.2 1.7 11.4 1.4 0.96 J 1.4 U 1.6 U 2.3 1.5 J 1.1 J 4.9 J 3.4 2.6 12.6 6.1 16.9 1.7 2.6 2.520.6 J 154.39.75.1 2.6 J 6.2 4.151.9 J4.530.5 J 14.42.845.5 26.2 98.6 J2.514.270.042 J 0.015 U0.470.069 0.018 U 0.017 U 0.017 U 0.014 U 0.092 J 0.019 U 0.039 UJ 0.019 U 0.013 U 0.031 J 0.018 U1.50.014 U 0.017 U 0.016 U6.2 U 0.52 J 0.28 J 0.42 J 0.42 J 5.5 U 0.31 J 0.57 J 2.4 J 0.4 J 13 U 4.9 J 0.76 J 3.4 J 2 J 7.8 0.65 J 1.1 J 1 J10.5 J 5.3 3.2 2.6 22.9 5.3 J 6.2 34.4 77 J 2.7 J 53.6 J 27.5 24.3400 192119 J 4.2 66.6 21.8SD-7SD-4SD-5SD-612/21/2011 7:54 PMPage 2 of 3Table 3 - Sediment Analytical Results2009 - 2011ScreeningAnalyte Value Unit1,1,1-Trichloroethane 4.4 μg/kg1,1-Dichloroethane 2.3 μg/kg1,2-Dichloroethane 1.7 μg/kg1,2-Dichloroethene (total) μg/kg2-Butanone (MEK) 70 μg/kgBenzene 340 μg/kgChlorobenzene 0.86 μg/kgEthylbenzene 1,400 μg/kgTetrachloroethene 450 μg/kgToluene 2,500 μg/kgTrichloroethene 1,600 μg/kgVinyl chloride 6.2 μg/kg1,4-Dichlorobenzene 98 μg/kgbis(2-Ethylhexyl)phthalate 620 μg/kgCadmium 0.6 mg/kgChromium 26 mg/kgManganese 8.04 mg/kgMercury 0.2 mg/kgNickel 16 mg/kgZinc 120 mg/kgR - Rejected DataA cell highlighted and not bold Inidcates a detected analytethat does not exceed the screening criteriaIndicates the analyte is not detected or not sampledNS - Not Sampledmg/kg - Milligrams per Kilograms!g/kg - Micrograms per KilogramsA Cell Highlighted and Bold Indicates a detectedanalyte that exceeds the screening criteriathe quantitation/detection limit.UJ - Analyte was not detected in the sample, actualquantitation/detection limit may be higher thanreported value.J - Result reported is a quantitative estimateMetalsQualifier Key:U - Analyte not detected in the sample. Value representsVolatile Organic CompoundsSemivolatile Organic CompoundsMay-09 Sep-09 Apr-10 Oct-10 May-11 May-09 Sep-09 Apr-10 Oct-10 May-11 Sep-09 Apr-10 Oct-10 May-110.88 UJ 0.11 U 0.14 U 0.13 U 0.16 U 0.67 U 0.12 U 0.13 U 0.12 U 0.13 U 0.057 U 0.13 U 0.11 U 0.12 U0.95 UJ 0.12 U 0.15 U 0.14 U 0.18 U 0.72 U 0.13 U 0.14 U 0.12 U 0.14 U 0.061 U 0.14 U 0.11 U 0.13 U2.4 UJ 0.3 U 0.37 U 0.36 U 0.44 U 1.8 U 0.33 U 0.36 U 0.31 U 0.36 U 0.15 U 0.34 U 0.29 U 0.33 U1.6 UJ 0.21 U 0.48 J 0.25 U 0.31 U 1.2 U 0.23 U 0.25 U 0.22 U 0.25 U 0.11 U 0.24 U 0.2 U 0.23 UNS NS 2.1 U 2 U 2.5 U NS NS 2 U 1.8 U 2.1 U NS 2 U 1.6 U 1.9 U2.3 UJ 0.3 U 0.37 U 0.35 U 0.44 U 1.8 U 0.32 U 0.35 U 0.31 U 0.36 U 0.15 U 0.34 U 0.28 U 0.32 U2.3 UJ 0.3 U 0.37 U 0.35 U 0.43 U 1.8 U 0.32 U 0.35 U 0.31 U 0.36 U 0.15 U 0.34 U 0.28 U 0.32 U2.5 UJ 0.33 U 0.4 U 0.38 U 0.48 U 1.9 U 0.35 U 0.39 U 0.34 U 0.39 U 0.16 U 0.37 U 0.31 U 0.35 U0.99 UJ 0.13 U 0.16 U 0.15 U 0.19 U 0.75 U 0.14 U 0.15 U 0.13 U 0.15 U 0.064 U 0.14 U 0.12 U 0.14 U2 UJ 0.26 U 0.83 J 0.3 U 0.37 U 1.5 U 0.28 U 0.92 J 0.26 U 0.31 U 0.13 U 0.84 J 0.24 U 0.28 U3.6 UJ 0.46 U 0.57 U 0.54 U 0.67 U 2.7 U 0.5 U 0.55 U 0.48 U 0.55 U 0.23 U 0.52 U 0.44 U 0.5 U1.2 UJ 0.16 U 0.19 U 0.18 U 0.23 U 0.93 U 0.17 U 0.19 U 0.16 U 0.19 U 0.079 U 0.18 U 0.15 U 0.17 U88 UJ 15 U 9.3 U 8.8 U 8.8 U NS NS 7.5 U NS NS 7.6 U 7.9 U 7.9 U 7.6 U120 UJ 20 U 37 U 35 U 35 U NS NS 30 U NS NS 30 U 31 U 31 U 30 U0.22 UJ 0.66 U 0.058 U 0.5 U 0.049 U 0.26 J 0.035 U 0.044 U 0.027 U 0.038 U 0.59 U 0.057 J 0.026 U 0.04 U9.6 J 3.2 4.2 4.1 5.3 9 J 0.34 J 1.1 U 1.2 U 1.2 2.1 2.2 1.5 1.2518 J 13.3 11 9.9 19.2 21.3 J1.8 U 1.7 1.8 U 4.1122 38.7 22.2 80.10.082 UJ 0.016 U 0.017 J 0.07 0.019 J 0.17 J0.37 0.3 0.39 1.50.013 U 0.013 U 0.018 J 0.016 U29 U 1.3 J 1.2 J 1.2 J 5.7 U 13 U 0.071 U 0.1 U 0.098 J 0.26 J 2 J 1.2 J 0.88 J 2.1 J52.4 J 6.4 7.3 7.3 13.1 61.4 J 0.9 J 0.87 J 2.4 U 1.2 J 13.9 10.9 8.2 15.8SD-8SD-10SD-912/21/2011 7:54 PMPage 3 of 3

# ATTACHMENT B

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# P E M B E R T O N B R O W

N S M I L L R D 

# B u d d ' s R u n



# Legend

@ A Monitoring Wells

& % Sediment/Surface Water Sample Location



# % , D 

# Gas Vents

Water Bodies

Streams

NPL Sanitary Landfill Boundary 

# FIGURE

Sampling Locations Map 

# 1 Created By: AES

Date: February 2012 4501 Ford Ave.

Suite 1200

Alexandria, VA 22302

(P) 703.820.3339

(F) 703.845.8568 

# 0 900 1800 2700

Feet 

# Ü

Final Close Out Report

JB

! MDL, New Jersey

# ATTACHMENT C

2009 ECOLOGICAL RISK ASSESSMENT

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Alexandria, VA 22302

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AVATAR Environmental, LLC

107 South Church Street

West Chester, PA 19382

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**1. INTRODUCTION .................................................................................................................. 1** 

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

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

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

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

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

**ANOMALIES .........................................**

**................................................... ................................... 12** 

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

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

**4.1.2 Surface Water Screening .............................** 

**................................................... ......... 13** 

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

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

**5.1 Sediment Benchmark Uncertainty ......................** 

**................................................... ........ 16** 

**5.1.1 PAHs ..............................................** 

**................................................... ...................... 16** 

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

**5.1.3 PCBs ..............................................** 

**................................................... ...................... 17** 

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

**5.2 Surface Water Benchmark Uncertainty ..................** 

**................................................... ..... 17** 

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

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

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

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

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

**APPENDIX A – SAMPLE BY SAMPLE COMPARISONS TO BENCHM ARKS** 

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**Table 1 – Summary of Detected Concentrations Exceed ing Sediment ESCs** 

**Table 2 – Summary of Detected Concentrations Exceed ing Surface Water ESCs** 

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**Figure 1 – Sediment and Surface Water Locations and Direct ion of Surface Water Flow** 

# 1



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**The following document presents the an update of th e results of the ecological screening** 

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

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

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

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

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

**consultants on 11 June 2009. The screening assessm ent was conducted using the most recent** 

**NJDEP Ecological Screening Criteria (NJDEP, 2009; a s found at** 

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

**screening, EPA requested that the following informat ion be provided where possible:** 

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

**historical records**

! **Discuss any chemical trends in surface water and se diment data based on recently** 

**collected semi-annual surface water and sediment sampling**

! **Present any unique sampling issues (such as data an omalies) associated with any of the** 

**recent sampling events**

! **Discuss the results of comparisons of recent surfac e water and sediment data to** 

**recommended benchmarks**

**The remainder of this ecological screening evaluati on is broken down into the following sections** 

**based on EPA specific information requests. It sho uld be noted that this screening evaluation** 

**should not be construed as a complete screening-lev el or baseline ecological risk assessment.** 

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

**information as requested by Region 2 EPA during an 11 J une 2009 meeting.** 

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

**Section 2 – Surface Water and Sediment Sampling Loc ations** 

**Section 3 – Comparison to Ecological Screening Benchmarks**

**Section 4 – Chemical Trends in Surface Water and Sedi ment, and Any Anomalies** 

**Section 5 – Uncertainty Analysis and Conclusions**

**Section 6 – References**

# 2



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

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

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

**north of the landfill and on Cannon Run, east and s outheast of the landfill. Both water bodies** 

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

**groundwater beneath the landfill runs in south-east erly direction toward Cannon Run (CDM,** 

**1986). Surface water and sediment samples were ini tially collected from two locations along** 

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

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

**initiated in 1994 with quarterly groundwater, surfa ce water, sediment and air sampling through** 

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

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

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

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

**course organic material and iron oxide present in t he sediments. Surface waters at these** 

**locations are typically clear with a slight amber tint.**

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

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

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

**relocated for the Fall 2009 sampling event approxim ately 1100 feet upstream of the original** 

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

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

**the landfill. Sediment and surface water condition s at these locations are similar to those found** 

**at SD/SW1 and SD/SW2.**

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

**eastern portion of the landfill, surface water samp les have only been collected at these locations** 

**during season of heavy precipitation, sediment samp les have been collected at these stations** 

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! 3 J U L I U S T O W N R D



# P E M B E R T O N B R O W

N S M I L L R D 

# B u d d ' s R u n

H B R A N C H R A N C 

# O 

# C 

# A 

# S 

# C R E E K ( G A U N T S 

# NPL Sanitary Landfill EPIC 8 Landfill PDO Landfill



# Legend

& % Sediment/Surface Water Sample Location

Water Bodies

Streams

EPIC 8 Landfill

NPL Sanitary Landfill

PDO Landfill 

# FIGURE

Sediment and Surface Water

Locations and Direction of

Surface Water Flow 

# 1 Created By: MJB

Date: May 2011 4501 Ford Ave.

Suite 1200

Alexandria, VA 22302

(P) 703.820.3339

(F) 703.845.8568 

# 0 900 1800 2700

Feet 

# Ü

Surface Water and Sediment

Ecological Evaluation Surface Water Flow Direction

# 4

**during each sampling round. Sediments at both thes e locations are heavy in organic debris and** 

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

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

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

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

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

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

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

**Canon Run. This location was added to the sampling program in the Fall 2009 to addres s a** 

**potential data gap between Stations 4 and 5.**

**During each sampling event, samples were always tak en, in order, from downstream to upstream** 

**sampling locations so that samples and sample locat ions would remain undisturbed by sampling** 

**events at other locations upstream. At each samplin g location surface water samples were taken** 

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

**sample bottles into the center portion of the strea m. Sample bottles containing preservatives were** 

**not submerged. Sediment samples were collected slig htly upstream of the surface water sampling** 

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

**collected.**



# AS& '(4.$-")(#&,(&*'(%(<"'$%&)'-**#"#<&3*#'>4$-V)&

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

**at the Fort Dix NPL Landfill Site to ecological sed iment and surface water benchmarks,** 

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

**Screening Criteria (ESC) table developed by the New Jersey Department of E nvironmental** 

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

**Assessment (ETRA) Unit was used for both the sedime nt and surface water benchmarks** 

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

**reference for ecological screening criteria. The p rimary source for both sediment and surface** 

**water values in the NJDEP ESC table is the EPA Regi on 5 RCRA Ecological Screening Level** 

# 5

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

**EDQLs) are the initial tool utilized in assessing a dverse risk to the environment through the** 

**RCRA Corrective Action and Permit programs within R egion 5. The ESLs provide protective** 

**benchmarks for 223 contaminants and four environmen tal media, including air, water, sediment,** 

**and soil.**

**For the calculation of several inorganic surface wa ter ESCs including chromium, copper, lead,** 

**nickel, and zinc, site-specific hardness values wer e calculated and used to derive hardness** 

**dependent ESC values. Calcium and magnesium surfac e water concentrations were used in the** 

**following equation to arrive at sample-specific hard ness values (EPA, 1999):** 

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# Once sample-specific hardness values were calculate **d, they were applied to the equations**

**presented in footnotes (f) 3**  

# and (f) **4** 

# in the ESC table in order to arrive at hardness-dependent

**surface water ESCs.**

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

**that exceeded their respective ESC values, as well as the mag nitude of those exceedances.** 

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

**sediment ESCs. In this evaluation, risks were esti mated by comparing individual detected** 

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

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**The results of the screening process indicate that non e of the volatile organic compounds (VOCs)** 

**had concentrations in exceedance of their respectiv e sediment ESC. Note that 2-butanone,** 

**acetone, and carbon disulfide did not have availabl e sediment ESCs for comparison.** 

**The following 12 of 22 detected semivolatile organi c compounds (SVOCs) and polycyclic** 

**aromatic hydrocarbons (PAHs) had concentrations tha t exceeded their respective sediment ESC** 

**(samples exceeding/samples detected; ratio) (see Tabl es 1 and A-1):** 

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Frequency of Number of ESC Number of ESC Number of ESC

Detected Concentrations Exceedances Exceedances Exceedances

Chemica l Exceedin g ESC > 1 < 10 > 10 < 100 > 100

Volatiles

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

**Acetone NBA --- --- ---** 

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

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

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

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

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

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

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

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

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

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

Semivolatiles

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

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

**Dibenzofuran NBA --- --- ---**

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

Polycyclic Aromatic Hydrocarbons

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

**Acenaphthene 1/1 1 --- ---**

**Acenaphthylene 4/4 4 --- ---**

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

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

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

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

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

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

**Carbazole NBA --- --- ---** 

**Chrysene 2/13 2 --- ---** 

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

**Fluoranthene 2/17 2 --- ---**

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

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

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

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

**Pyrene 2/16 2 --- ---** 

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

Pesticides

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

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

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

**DDT and Metabolites 20/21 12 6 2**

**Dieldrin 1/1 1 --- ---** 

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

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

Polychlorinated Biphenyls

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

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Frequency of Number of ESC Number of ESC Number of ESC

Detected Concentrations Exceedances Exceedances Exceedances

Chemica l Exceedin g ESC > 1 < 10 > 10 < 100 > 100

Inorganics

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

**Antimony NBA --- --- ---** 

**Arsenic 3/12 3 --- ---** 

**Barium NBA --- --- ---** 

**Beryllium NBA --- --- ---** 

**Cadmium 3/10 3 --- ---** 

**Calcium NBA --- --- ---** 

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

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

**Copper 9/29 9 --- ---** 

**Cyanide 3/3 3 --- ---** 

**Iron NBA --- --- ---** 

**Lead 13/36 11 2 ---** 

**Magnesium NBA --- --- ---**

**Manganese 1/39 1 --- ---**

**Mercury 6/27 6 --- ---** 

**Nickel 1/19 1 --- ---** 

**Potassium NBA --- --- ---** 

**Selenium NBA --- --- ---** 

**Silver 2/17 2 --- ---** 

**Sodium NBA --- --- ---** 

**Thallium NBA --- --- ---** 

**Tin NBA --- --- ---** 

**Vanadium NBA --- --- ---** 

**Zinc 4/39 4 --- ---** 

**ESC = Ecological Screening Criteria.**

**NBA = No benchmark available.**

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Frequency of Number of ESC Number of ESC Number of ESC

Detected Concentrations Exceedances Exceedances Exceed ances

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

Volatiles

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

**Acetone NBA --- --- ---** 

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

**Chloromethane NBA --- --- ---**

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

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

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

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

Semivolatiles

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

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

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

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

Polycyclic Aromatic Hydrocarbons

**Anthracene 1/1 1 --- ---** 

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

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

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

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

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

**Chrysene NBA --- --- ---** 

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

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

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

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

**Pyrene 1/2 1 --- ---** 

Pesticides

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

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

Inorganics

**Aluminum NBA --- --- ---** 

**Antimony 1/1 1 --- ---** 

**Arsenic 1/3 1 --- ---** 

**Barium 2/19 2 --- ---** 

**Beryllium 1/1 1 --- ---** 

**Calcium NBA --- --- ---** 

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

**Cobalt 1/8 1 --- ---** 

**Copper 6/8 5 1 ---** 

**Iron NBA --- --- ---** 

**Lead 9/9 8 1 ---** 

**Magnesium NBA --- --- ---** 

**Manganese NBA --- --- ---** 

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

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

**Potassium NBA --- --- ---** 

**Selenium 1/1 --- 1 ---** 

**Sodium NBA --- --- ---** 

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

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

**Vanadium 1/1 --- 1 ---** 

**Zinc 2/22 2 --- ---** 

**ESC = Ecological Screening Criteria.**

**NBA = No benchmark available.**

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# 9

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

! **Acenaphthene (1/1; ratio of 3.4)**

! 

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

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

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

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

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

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

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

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

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

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

**Both dibenzofuran and carbazole did not have availa ble sediment ESCs for comparison. In** 

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

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

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

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

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

**exceeded their respective sediment ESC (samples exc eeding/samples detected; ratio) (see Tables** 

**1 and A-1):**

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

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

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

! **Dieldrin (1/1; ratio of 4.4)**

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

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

**compared. Twenty of the 21 detected DDT and metabo lites concentrations exceeded the** 

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

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

**greater than 100. The remaining 12 DDT and metabol ites concentrations exceeded the sediment** 

**ESC by less than a factor of 10. As presented in T able 1, 2 of the 17 detected 4,4’-DDD** 

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

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

# 10

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

**concentrations exceeded the sediment ESC by less th an a factor of 10.** 

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

**Ten of the 25 detected inorganics had detected sedi ment concentrations that exceeded their** 

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

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

**thallium, tin, and vanadium. Calcium, iron, magnesi um, potassium, and sodium are trace** 

**essential nutrients and are not expected to pose an y substantial ecological risk to receptors at the** 

**site. The following 10 inorganics had concentration s that exceeded their respective sediment** 

**ESC (samples exceeding/samples detected; ratio) (se e Tables 1 and A-1):** 

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

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

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

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

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

! **Manganese (1/39; ratio of 1.3)**

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

! **Nickel (1/19; ratio of 1.1)**

! **Silver (2/17; ratio of 1.2)**

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

**With the exception of 2 out of 36 detected lead con centrations, all of the above inorganics** 

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

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

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

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

3"456 % 7848948:;!6<98<4="456<

>?!

# 11

**The results of the screening process indicate that non e of the volatile organic compounds (VOCs)** 

**had concentrations in exceedance of their respectiv e surface water ESC. Note that only trans** 

**1,2-dichloroethene and toluene had available surfac e water ESCs for comparison.** 

**The following 5 of 16 detected SVOCs and PAHs had c oncentrations that exceeded their** 

**respective surface water ESC (samples exceeding/sam ples detected; ratio) (see Tables 2 and A** 

**2):**

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

! **Anthracene (1/1; ratio of 5.1)**

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

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

! **Pyrene (1/2; ratio of 3.1)**

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

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

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

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

**water ESC by less than a factor of 10.**

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

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

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

**surface water due to a lack of an available ESC.**

**Ten of the 22 detected inorganics had detected surface water concentrations that exce eded their** 

**respective surface water ESC (see Table 2). Compoun ds for which no surface water ESC was** 

**available include aluminum, calcium, iron, magnesiu m, manganese, potassium, and sodium.** 

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

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

**inorganics had concentrations that exceeded their r espective surface water ESC (samples** 

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

! **Antimony (1/1; ratio of 2.9)**

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

# 12

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

! **Beryllium (1/1; ratio of 1.5)**

! **Cobalt (1/8; ratio of 2.3)**

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

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

! **Selenium (1/1; ratio of 33)**

! **Vanadium (1/1; ratio of 16)**

! **Zinc (2/22; ratio of 4.8)**

**With the exception of copper, lead, selenium, and v anadium, all of the above inorganics** 

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

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

**selenium concentration, and the only detected vanad ium concentration all exceeded the surface** 

**water ESC with a ratio greater than 10. The remain ing copper and lead concentrations exceeded** 

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



# 9S& '>*4"'$%& ,-*#/)&"#&)+-! $'*& 6$,*-& $#/&)*/"4*#,5&$ #/&

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**Prior to discussing the trends analysis (Plexus, 20 10) as it relates to the aquatic screening results,** 

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

**noted that the trends analysis approach has been us ed and accepted in previous reports for** 

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

Trends Analysis Benchmark Screening

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

**Only primary samples used. Primary and field duplic ate samples considered.** 

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

**reporting limit.**

**All detected samples within a LAP that were less th an** 

**the highest reporting limit were set to zero. All detected concentrations were retained as-was.** 

**Only LAPs with at least four unique non-zero**

**concentrations from the reduced data set were run**

**through the Mann-Kendall analysis. All detected chemicals were screened against** 

**benchmarks.**

**LAP = Location-Analyte Pair. LAPs are a combinatio n of the location and chemical name. For example S**  **D-1**

**Aluminum represents sediment sample location #1 alu minum analyses.** 

# 13

4.1.1 Several detected chemicals had recent concent rations that exceeded

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

number of detects), some of the detected chemicals that exceeded benchma rks

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

**Of detected chemicals with recent concentrations th at exceed benchmarks, only the following** 

**LAPs had trends analysis performed.**

! **Acenaphthylene (SD-7)**

! **Cadmium (SD-4)**

! **Copper (SD-6 through 9)**

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

! **4,4’-DDT (SD-1 and SD-6 through 9)**

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

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

! **Mercury (SD-7 and SD-9)**

! **2-Methylnaphthalene (SD-7)**

**Increasing trends were noted for the following:**

! **Copper (SD-6)**

! **4,4’-DDE (SD-1 and SD-4 through 7)**

! **4,4’-DDT (SD-1, SD-6, and SD-7)**

! **Lead (SD-6)**

! **Manganese (SD-4 and SD-6)**

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

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

**were identified for the pairs called out above.**

4.1.2 Surface Water Screening

**Of detected chemicals with recent concentrations th at exceed benchmarks, only the following** 

**LAPs had trends analysis performed.**

! **Arsenic (SW-6 and SW-8)**

! **Barium (SW-8)**

! **Benzo(a)pyrene (SW-5)**

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

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

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

# 14

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

**pairs.**

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

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

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

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

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

**this evaluation).**

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

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

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

**detected in any of the surface water samples collected.**

**Mercury was frequently detected in most of the surf ace water and sediment sampling location** 

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

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

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

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

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

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

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



# :S& +#'*-,$"#,1&$#$%1)")&$#/&'(#'%+)"(#)&

**Environmental conditions at the time of sampling cou ld have an effect on what concentrations of** 

**contaminants are found in the surface water and sed iment. In areas along the streams where** 

**contaminated groundwater recharge is not in the imm ediate vicinity, taking samples during high** 

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

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

**after rain events could lead to increases in the ob served concentrations as increased groundwater** 

# 15

**volume could force the flow of contaminants from un der the landfill to the seep areas. During** 

**the LTMP program the effect rainfall events does not impac t the protectiveness of the remedy.** 

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

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

**toxic effects on all organisms under all environmental cond itions.** 

**The use of benchmark values for evaluating the pote ntial impacts of reported contaminant** 

**concentrations in sediments and surface water has the fo llowing associated uncertainties:** 

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

**contaminant mixtures. The risk may be over- or unde r-estimated, depending on the** 

**interactions among the various chemicals present at the site.** 

! **The test conditions used in the toxicological studi es used to develop chemical** 

**specific benchmarks may not match the conditions in the stream downgradient from** 

**the landfill; therefore, the benchmarks may over- o r under-estimate risk at the site.** 

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

**- The form in which a chemical was added to the medi um in deriving the** 

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

**the site. This is particularly true where the metal lic salts added for toxicity** 

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

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

**bound forms present).**

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

**carbon [TOC]) in the studies from which the benchma rks were derived may** 

**not mimic those conditions found on-site.**

**- Studies from which chemical-specific benchmarks we re derived reflect the** 

**complex physicochemical processes and mineral complexes of the soil,**

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

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

**conditions in the stream.**

! **Benchmarks and guidelines do not exist for all cont aminants detected at the site. For** 

**contaminants that do not have benchmarks, the poten tial for risk cannot be** 

**ascertained.**

! **The benchmarks used do not consider factors that in fluence chemical bioavailability** 

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

**Particularly for metals, the use of total concentra tion, rather than an estimate of the** 

# 16 **bioavailable fraction, represents a conservative es timate of exposure, and may over** 

**estimate risk.**

! **Different species of plants and animals exhibit var ying degrees of sensitivity to** 

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

**necessarily have the same sensitivities as those fo und at the site. Consequently, the** 

**risk to ecological receptors at the site may be ove r- or under-estimated.** 

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**In general, sediment benchmarks do not address poss ible synergistic, antagonistic, or additive** 

**effects of contaminant mixtures; do not consider un measured chemicals; and are not useful for** 

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

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

**contaminants. These mixtures most likely do not mat ch the conditions in the stream. Sediment** 

**quality guidelines are generally based on overt tox icity to benthic invertebrates and do not** 

**consider other potential effects such as bioaccumul ation and subsequent effects on longer-lived** 

**species. These uncertainties can result in under- o r over-estimation of risks.** 

**The following paragraphs address uncertainty associ ated with the specific sediment guidelines** 

**and benchmarks used in this screening.**

**Sediment benchmarks were not available for 2-butano ne, acetone, carbon disulfide,** 

**dibenzofuran, carbazole, endosulfan II, antimony, b arium, beryllium, calcium, iron, magnesium,** 

**potassium, selenium, sodium, thallium, tin, or vana dium; therefore some potential risks are not** 

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

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

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

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

**iron, magnesium, potassium, and sodium can be consi dered essential nutrients and are generally** 

**not evaluated in ecological risk assessments.**

5.1.1 PAHs

**As noted previously, 12 of the 19 detected PAHs wer e detected in at least one sample at** 

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

**concentrations at which no toxic effects are expected. As sociated severe effect levels (SELs)** 

# 17

**were examined, and of the PAHs, only 2-methylnaphth alene had a concentration exceeding the** 

**levels at which effects are probable. That is, 0.2 8 mg/kg (at SD-7 in May 09) versus the** 

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

**this value is actually for marine organisms as a fres hwater value was not available.** 

5.1.2 Pesticides

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

**exceeded the sediment LEL-based ESCs. As noted pre viously, these values generally represent** 

**concentrations at which no toxic effects are expect ed. Associated SELs were examined, and the** 

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

**assuming a TOC of 1%). DDT and its metabolites had maximum detected concentrations** 

**exceeding the SELs.**

5.1.3 PCBs

**Aroclor 1254 was detected in 1 of 17 samples. The detected concentration, 1.1 mg/kg exceeded** 

**both the LEL (0.06 mg/kg) and SEL (0.34 mg/kg assum ing a TOC of 1%) values. Aroclor 1260** 

**was not positively identified in any sample.**

5.1.4 Inorganics

**All inorganics with upper-bound benchmarks availabl e had concentrations lower than their** 

**respective upper-bound benchmark, with the exceptio n of lead. Two of the 36 samples with** 

**detected concentrations of lead had concentrations higher than the SEL of 250 mg/kg. Cyani de** 

**and silver did not have an upper bound benchmark available.**

**EPA Region 2 asked specifically for a discussion re garding mercury. Mercury was detected in** 

**25 of 33 samples. Detected concentrations in six s amples exceeded the LEL (0.2 mg/kg); with** 

**the maximum detected concentration (1.5 mg/kg) to L EL ratio of 7.5. None of the** 

**concentrations exceeded the SEL (2 mg/kg).**

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**The use of surface water benchmarks for evaluating the potential impacts of reported** 

**contaminant concentrations in surface water has the following general associated uncertainties:** 

# 18

! **The use of the benchmarks as a screening tool canno t be interpreted as a direct** 

**measurement of site-specific bioavailability.**

! **There may be differences between the species with t oxicological data used to develop the** 

**surface water benchmark and those present in the st ream.** 

! **Most benchmarks are based on a threshold for statis tical significance rather than** 

**biological significance.**

! **There is uncertainty surrounding the extrapolation of laboratory data (used to develop** 

**criteria) to field conditions.**

! **Acute and subchronic laboratory toxicity tests freq uently do not measure the most** 

**sensitive ecological endpoints; in particular, fecu ndity is often not measured (Suter,** 

**1996a).**

! **Chronic ambient water quality criteria (AWQC) and b enchmarks derived in like ways are** 

**based on the most statistically sensitive of the me asured response parameters in each** 

**chronic or subchronic test. Therefore, cumulative effects over the life cycle of fish and** 

**invertebrates are not considered (Suter, 1996b). Th is would tend to underestimate risk.** 

**The following paragraphs address uncertainty associ ated with the specific sediment guidelines** 

**and benchmarks used in this screening.**

**Surface water benchmarks were not available for the following detected VOCs (1,1-** 

**dichloroethane, acetone, carbon disulfide, chlorome thane, cis-1,2-dichloroethene, and total 1,2-** 

**dichloroethene), 3&4-methylphenol, benzo(k)fluorant hene, chrysene, 4,4’-DDD, aluminum,** 

**calcium, iron, magnesium, manganese, potassium, and sodium; therefore some potential risks are** 

**not evaluated herein. However, calcium, iron, magn esium, potassium, and sodium can be** 

**considered essential nutrients and are generally not eval uated in ecological risk assessments.** 

5.2.1 Semivolatiles

**Both detected concentrations of bis(2-ethylhexyl)ph thalate exceeded the freshwater chronic** 

**criteria, which was the EPA Region V ESL for phthal ate esters. However, according to USEPA** 

**(2006), “There is a full set of aquatic life toxici ty data that show that DEHP is not toxic to** 

**aquatic organisms at or below its solubility limit.”**

# 19

5.2.2 Pesticides

**As noted above, 4,4’-DDD did not have an N.J.A.C. freshwater criterion. In addition, 4,4’-DDE**

**had a criterion of 4.51E-09 μg/L. This value is th e Region V ESL based on modeled exposures** 

**to a kingfisher and is not appropriate for evaluati ng freshwater aquatic community (e.g., fish)** 

**risks. The chronic national AWQC for DDT and metab olites is 0.001 μg/L. The sum of the** 

**DDD, DDE, and DDT concentrations should not exceed this value. The maximum DDT and** 

**metabolites concentration calculated for samples in which at least one of the compounds is** 

**detected is 0.0728 μg/L (range = 0.0258 to 0.0728 μ g/L). Therefore, it is likely that HQ for the** 

**aquatic community exposed to 4,4’-DDE is highly overestimated.**

5.2.3 Inorganics

**The benchmark values are derived for dissolved concentrations. Comparing tot al recoverable** 

**concentrations with dissolved benchmarks is conserv ative and likely overestimates potential** 

**risks.**

**The values for antimony, barium, beryllium, cobalt, and vanadium are Tier II values that are** 

**derived from data sets that are not robust enough f rom which to derive criteria. It is not known if** 

**the use of these values would under- or over-estimate ri sk.** 

**The only detected beryllium concentration exceeded the surface water benchmark with a ratio of** 

**1.48. However, the benchmark is the EPA Region V ESL, which is a hardness-based value** 

**assuming a hardness of 50 mg/L. Equations to recal culate the ESL using site-specific hardness** 

**values are not provided; but given that the sample- specific hardness associated with the detected** 

**concentration of beryllium is 233 mg/L, it is likel y that the HQ for the aquatic community** 

**exposed to beryllium is overestimated.**

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**The most frequent and substantial exceedances of se diment benchmarks were associated with** 

**4,4’-DDT and its metabolites, which are ubiquitous within the study area. Several PAHs were** 

**detected at concentrations exceeding sediment bench mark values, with most of those** 

**exceedances associated with SD/SW3 (the most downst ream sample in Cannon Run) and** 

**leachate sample SD/SW7. A majority of the metals s ediment benchmark exceedances occurred** 

# 20

**at SD/SW9 (the most upstream location in Budd’s Run ), SD/SW7 and SD/SW8 (the wetland** 

**area located southwest of the landfill).**

**There was a limited number of surface water benchma rk exceedances observed in the 2008 and** 

**2009 samples. Semivolatile exceedances were limite d to SD/SW4 (near a former beaver dam in** 

**Cannon Run at the southern boundary of the landfill ) and SD/SW5 (in Cannon Run south of the** 

**conduit along the mid-eastern boundary of the landf ill). Inorganic exceedances were most** 

**frequent at leachate sample SD/SW6 in Oct. 08 and S D/SW4 and SD/SW8 in May 09.** 

**Sediment and surface water exceedances of benchmark s and screening criteria continue to occur** 

**in Budd’s and Cannon Run. In addition, the most re cent trend analysis indicates that for site** 

**related chemicals exceeding ecological benchmarks, increasing trends of 4,4’-DDE, 4,4’-DDT,** 

**copper, and lead in sediment and of copper and merc ury in surface water were observed.** 



# =S& -*!*-*#'*)&

**Avatar (Avatar Environmental, LLC). 2009a. Techni cal Memorandum: Surface Water and** 

**Sediment Ecological Evaluation: Fort Dix Sanitary Landfill, Fort Dix, New Jersey.** 

**Submitted to Plexus Scientific, Alexandria, VA. Au gust 2009.** 

**Avatar (Avatar Environmental, LLC). 2009b. NPL Sa nitary Landfill Long Term Monitoring** 

**Program Statistical Analyses of Temporal Trends of Chemical Levels in Groundwater,** 

**Surface Water and Sediment: Fort Dix, New Jersey. Submitted to Plexus Scientific,** 

**Alexandria, VA. February 2009.**

**CCME (Canadian Council of Ministers of the Environm ent). 2002. Canadian Sediment Quality** 

**Guidelines for the Protection of Aquatic Life. Sum mary Tables. Update 2002.** 

**Camp Dresser & McGee, Inc. 1987. Remedial Investiga tion Report Study for Fort Dix Sanitary** 

**Landfill, Pemberton Township, New Jersey -Proposed Response Addendum 1. January** 

**Camp Dresser & McGee, Inc. 1986. Remedial Investiga tion Report for Fort Dix Sanitary Landfill,** 

**Pemberton Township, New Jersey -Proposed Response. September.** 

**Camp Dresser & McGee, Inc. 1985.** Remedial Investigation/ Feasibility Study for Fort Dix Sanitary

Landfill, Pemberton Township, New Jersey –Interim R eport **. December.**

**EA (EA Engineering, Science, and Technology, Inc.). 2008.**  2007 Sampling and Analysis Report

for Groundwater, Surface Water, and Sediment for th e Fort Dix Sanitary Landfill. Draft.

**March 2008.**

# 21

**EA Engineering, Science and Technology, Inc. 2007.** 2006 Sampling and Analysis Report for

Groundwater, Surface Water, and Sediment for the Fo rt Dix Sanitary Landfill **. March.**

**EA Engineering, Science and Technology, Inc. 2002.** Addendum to the Long-Term Monitoring

Plan for the Sanitary Landfill, Fort Dix, New Jerse y. **April.**

**EPA (U.S. Environmental Protection Agency). 2006.** National Recommended Water Quality

Criteria **. Office of Water. Office of Science and Technolo gy. (4304T).** 

**EPA (U.S. Environmental Protection Agency) Region V. 2003.** RCRA Ecological Screening

Levels **. 22 August 2003. Available online: http://www.epa.gov/reg5rcra/ca/ESL.pdf** 

**EPA (U.S. Environmental Protection Agency). 1999.** Standard Operating Procedure for the

Analysis of the Hardness of Water by Calculation fr om ICP Metals Data **. 15 December**

**1999.**

**Geisy, J.P. and R.A. Hoke. 1990. Freshwater Sedime nt Quality Criteria: Toxicity Bioassessment.** 

**In: R. Baudo, J. Geisy, and H. Muntau (Eds.)** Sediments: Chemistry and Toxicity of In-place

Pollutants. **Lewis Publ. Inc., Chelsea, MI.**

**NJDEP (New Jersey Department of Environmental Prote ction). 2009. Ecological Screening** 

**Criteria. 10 March 2009. Available online:**

**http://www.state.nj.us/dep/srp/guidance/ecoscreenin g/** 

**Plexus Scientific, Inc. 2009.** 2008 Sampling and Analysis Report for Groundwater, Surface Water,

and Sediment for the Fort Dix Sanitary Landfill **. March.**

**Plexus Scientific, Inc. 2010.** Sanitary Landfill 2009 Sampling and Analysis Repor t at Fort Dix

Sanitary Landfill **. July.**

**Suter, G.W. 1996a. Toxicological benchmarks for sc reening contaminants of potential concern for** 

**effects on freshwater biota.** Enviro. Tox. Chem **. 15:1232-124.**

**Suter, G.W. 1996b. Abuse of hypothesis testing st atistics in ecological risk assessments.**  Human

and Ecological Risk Assessment **. 2:331-347.**

**U.S. Army Corps of Engineers (USACE). 2005.** Second Five-Year Review Report for U.S. Army

Fort Dix (NPL Landfill Site) Fort Dix, New Jersey **. September.**

# $..*#/"0&$&

)$4.%*&31&)$4.%*&'(4.$-")(#)&,(&3*#'>4$-V)&,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXFresh waterRatio ofRatio ofRatio ofRatio ofFrequency CriteriaaSD-1 May-08 Detected SD-1 Oct-08 Detected SD-1 May-09Detected SD-1 Sept-09 DetectedofLEL May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to May-08Chemical Detection(mg/kg) (mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Volatiles**2-Butanone 5/18 3.7E-02 - 1.6E-01 NBA ND --- ND --- NA --- NA -- - ND** **Acetone 22/33 7.5E-03 - 4.6E+00 NBA 1.00E-01 J --- 2.43E-01 J --- 1.31E-02 J --- 4.34E-02 --- ND** **Benzene 1/33 1.9E-03 - 1.9E-03 1.42E-01 ND --- ND --- ND --- ND --- ND** **Carbon disulfide 8/33 3.5E-04 - 2.6E-02 NBA ND --- ND --- ND - -- 8.00E-04 J --- ND** **Chlorobenzene 2/33 5.9E-04 - 2.0E-03 2.91E-01 ND --- ND --- N D --- ND --- ND** **Chloroform 1/33 1.0E-02 - 1.0E-02 1.21E-01 ND --- ND --- ND -- - ND --- ND** **Ethylbenzene 2/33 6.1E-04 - 7.4E-04 1.75E-01 ND --- ND --- ND --- ND --- ND** **Methylene chloride 1/33 1.1E-02 - 1.1E-02 1.59E-01 ND --- N D --- ND --- ND --- ND** **Styrene 2/33 1.1E-02 - 1.2E-02 2.54E-01 1.10E-02 J 4.33E-02 ND --- ND --- ND --- ND** **Tetrachloroethene 3/33 4.3E-03 - 3.9E-02 9.90E-01 3.90E-0 2 J 3.94E-02 ND --- ND --- ND --- 4.30E-03 J** **Toluene 5/33 9.3E-04 - 2.1E-03 1.22E+00 ND --- ND --- ND --- ND --- ND** **Xylenes (total) 3/33 7.8E-04 - 1.3E-02 4.33E-01 ND --- ND -- - ND --- NA --- ND** Semivolatiles**1,4-Dichlorobenzene 3/33 5.4E-03 - 1.5E-02 3.18E-01 ND --- ND --- ND --- ND --- ND** **Bis(2-ethylhexyl)phthalate 1/33 4.3E-02 - 1.2E-01 1.82E- 01 ND --- ND --- ND --- ND --- ND** **Dibenzofuran 1/33 7.6E-02 - 7.6E-02 NBA ND --- ND --- ND --- ND --- ND** **Di-n-butyl phthalate 2/33 4.2E-02 - 1.6E-01 1.11E+00 ND -- - ND --- ND --- ND --- ND** Polycyclic Aromatic Hydrocarbons**2-Methylnaphthalene 1/24 2.8E-01 - 2.8E-01 2.02E-02 NA --- ND --- ND --- ND --- NA** **Acenaphthene 1/33 2.3E-02 - 2.3E-02 6.71E-03 ND --- ND --- ND --- ND --- ND** **Acenaphthylene 4/33 1.1E-02 - 5.4E-02 5.87E-03 ND --- ND --- ND --- ND --- ND** **Anthracene 2/33 6.8E-02 - 1.3E-01 2.20E-01 ND --- ND --- ND -- - ND --- ND** **Benzo(a)anthracene 11/33 1.4E-02 - 9.4E-01 3.20E-01 ND --- 2.89E-02 J 9.03E-02 5.37E-02 1.68E-01 ND --- ND** **Benzo(a)pyrene 9/33 1.8E-02 - 1.1E+00 3.70E-01 ND --- 3.09E -02 J 8.35E-02 4.71E-02 1.27E-01 ND --- ND** **Benzo(b)fluoranthene 9/33 2.5E-02 - 1.1E+00 1.04E+01 ND -- - 3.28E-02 J 3.15E-03 3.98E-02 J 3.83E-03 ND --- ND** **Benzo(k)fluoranthene 9/33 2.2E-02 - 9.0E-01 2.40E-01 ND -- - 2.20E-02 J 9.17E-02 4.11E-02 1.71E-01 ND --- ND** **Benzo(g,h,i)perylene 9/33 1.9E-02 - 9.2E-01 1.70E-01 ND -- - 2.32E-02 J 1.36E-01 3.14E-02 J 1.85E-01 ND --- ND** **Carbazole 2/33 2.8E-02 - 5.3E-02 NBA ND --- ND --- ND --- ND --- ND** **Chrysene 12/33 1.4E-02 - 1.0E+00 3.40E-01 ND --- 3.53E-02 J 1 .04E-01 5.15E-02 1.51E-01 ND --- ND** **Dibenzo(a,h)anthracene 3/33 1.4E-02 - 2.9E-01 6.00E-02 ND --- ND --- ND --- ND --- ND** **Fluoranthene 14/33 1.8E-02 - 1.5E+00 7.50E-01 1.10E-01 J 1. 47E-01 5.70E-02 7.60E-02 8.48E-02 1.13E-01 ND --- ND** **Fluorene 1/33 2.7E-02 - 2.7E-02 1.90E-01 ND --- ND --- ND --- N D --- ND** **Indeno(1,2,3-cd)pyrene 9/33 1.7E-02 - 7.7E-01 2.00E-01 ND --- 1.98E-02 J 9.90E-02 3.26E-02 J 1.63E-01 ND --- ND** **Naphthalene 1/33 1.7E-01 - 1.7E-01 1.76E-01 ND --- ND --- ND - -- ND --- ND** **Phenanthrene 10/33 2.7E-02 - 5.0E-01 5.60E-01 7.80E-02 J 1. 39E-01 3.88E-02 6.93E-02 3.07E-02 J 5.48E-02 ND --- ND** **Pyrene 13/33 1.6E-02 - 1.3E+00 4.90E-01 8.10E-02 J 1.65E-01 5.09E-02 1.04E-01 7.98E-02 1.63E-01 ND --- ND** **PAHs, total 17/33 2.5E-01 - 2.5E+01 4.00E+00 9.27E+00 2.32 E+00 4.36E-01 1.09E-01 6.06E-01 1.51E-01 NA --- ND** Concentrations(mg/kg)SD-1SD-1 SD-1SD-2Range of DetectedSD-1C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXFresh waterRatio ofRatio ofRatio ofRatio ofFrequency CriteriaaSD-1 May-08 Detected SD-1 Oct-08 Detected SD-1 May-09Detected SD-1 Sept-09 DetectedofLEL May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to May-08Chemical Detection(mg/kg) (mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Concentrations(mg/kg)SD-1SD-1 SD-1SD-2Range of DetectedSD-1Pesticides**4,4'-DDD 15/33 2.9E-03 - 2.9E-01 8.00E-03 ND --- ND --- ND --- 4.30E-03 5.38E-01 8.20E-03 J** **4,4'-DDE 21/33 3.0E-03 - 7.7E-01 5.00E-03 ND --- 1.41E-02 2. 82E+00 1.24E-02 2.48E+00 3.00E-03 J 6.00E-01 5.60E-03** **4,4'-DDT 15/33 3.7E-03 - 7.6E-01 8.00E-03 ND --- 2.79E-02 3. 49E+00 1.73E-02 2.16E+00 6.07E-02 J 7.59E+00 6.40E-03 J** **DDT and Metabolites 20/27 6.8E-03 - 1.6E+00 7.00E-03 ND -- - 4.23E-02 6.04E+00 3.00E-02 4.28E+00 6.80E-02 9.71E+00 2.** **02E-02 Dieldrin 1/33 8.7E-03 - 8.7E-03 2.00E-03 ND --- ND --- ND --- N** **D --- ND Endosulfan-II 1/33 4.1E-03 - 4.1E-03 NBA ND --- ND --- ND --- N** **D --- ND gamma-Chlordane 1/32 2.3E-03 - 2.3E-03 7.00E-03** **b ND --- ND --- ND --- ND --- NA** Polychlorinated Biphenyls**Aroclor 1254 1/17 1.1E+00 - 1.1E+00 6.00E-02 ND --- ND --- NA --- NA --- ND** Inorganics**Aluminum 36/36 4.8E+01 - 8.7E+03 2.55E+04 2.11E+03 J 8.27E- 02 1.91E+03 7.49E-02 3.19E+03 1.25E-01 3.58E+02 1.40E-02 1** **.05E+03 N Antimony 7/36 3.5E-01 - 3.9E+01 NBA ND --- 7.00E-01 J --- ND --** **- ND --- ND Arsenic 11/36 3.3E-01 - 2.4E+01 6.00E+00 ND --- 2.10E+00 J 3.** **50E-01 2.70E+00 4.50E-01 ND --- ND Barium 23/36 6.7E+00 - 2.6E+02 NBA 5.31E+01 J --- ND --- 7.00E** **+00 J --- ND --- 2.00E+01 J Beryllium 7/36 2.8E-02 - 2.2E-01 NBA ND --- ND --- 6.80E-02 J -** **-- ND --- ND Cadmium 10/36 4.2E-02 - 1.5E+00 6.00E-01 ND --- 4.30E-02 J 7.** **17E-02 ND --- ND --- ND Calcium 25/36 7.6E+01 - 1.5E+04 NBA 3.56E+03 J --- ND --- 7.63** **E+01 J --- ND --- 3.49E+02 J Chromium 33/36 3.4E-01 - 2.4E+01 2.60E+01 3.90E+00 J 1.50E-** **01 4.40E+00 1.69E-01 7.40E+00 2.85E-01 1.50E+00 5.77E-02 5 .40E+00 J** **Cobalt 14/36 1.5E-01 - 2.2E+01 5.00E+01 ND --- 3.10E-01 J 6.2 0E-03 1.50E-01 J 3.00E-03 ND --- 1.20E+00 J** **Copper 25/36 2.6E+00 - 8.1E+01 1.60E+01 7.40E+00 J 4.63E-01 4.40E+00 2.75E-01 5.80E+00 J 3.63E-01 ND --- 2.90E+00 J** **Cyanide 3/12 1.3E-01 - 7.2E-01 1.00E-01 ND --- NA --- NA --- NA --- ND** **Iron 36/36 2.4E+02 - 3.5E+05 NBA 2.05E+03 J --- 2.75E+03 --- 3.21E** **+03 --- 6.10E+02 --- 9.10E+02 N Lead 32/36 7.8E-01 - 9.0E+02 3.10E+01 2.49E+01 J 8.03E-01 3.** **00E+01 J 9.68E-01 1.59E+01 5.13E-01 3.30E+00 1.06E-01 5.60 E+00 J** **Magnesium 28/36 6.9E+00 - 4.0E+03 NBA 3.90E+02 J --- ND --- 2. 33E+02 J --- 2.78E+01 J --- 3.70E+01 J** **Manganese 35/36 2.5E+00 - 8.2E+02 6.30E+02 6.07E+01 J 9.63E -02 7.70E+00 J 1.22E-02 5.10E+00 J 8.10E-03 5.10E+00 8.10E-** **03 8.80E+00 J Mercury 25/33 2.6E-02 - 1.5E+00 2.00E-01 6.00E-02 J 3.00E-0** **1 4.00E-02 2.00E-01 4.70E-02 2.35E-01 2.60E-02 J 1.30E-01 1 .20E+00** **Nickel 16/36 1.7E-01 - 1.7E+01 1.60E+01 ND --- 1.40E+00 J 8.7 5E-02 ND --- 1.70E-01 J 1.06E-02 ND** **Potassium 10/36 2.5E+01 - 5.8E+02 NBA NA --- NA --- 3.29E+02 J --- ND --- NA** **Selenium 7/36 4.2E-01 - 5.0E+00 NBA ND --- 4.20E-01 J --- ND -- - ND --- ND** **Silver 15/36 5.5E-02 - 5.8E-01 5.00E-01 1.30E-01 J 2.60E-01 ND --- ND --- ND --- 5.50E-02 J** **Sodium 18/36 7.2E+00 - 4.2E+02 NBA ND --- 7.20E+00 J --- 2.35E +01 J --- ND --- ND** **Thallium 3/36 3.8E-01 - 1.7E+00 NBA 9.30E-01 J --- ND --- ND -- - ND --- ND** **Tin 5/36 2.4E+00 - 2.9E+01 NBA ND --- ND --- ND --- ND --- ND** **Vanadium 19/36 9.7E-01 - 2.5E+01 NBA 6.50E+00 J --- 8.20E+00 --- 8.90E+00 J --- ND --- 2.70E+00 J** **Zinc 35/36 9.0E-01 - 7.0E+02 1.20E+02 4.50E+01 J 3.75E-01 9.50E+** **00 7.92E-02 9.80E+00 J 8.17E-02 3.30E+00 2.75E-02 1.15E+01 J** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**2-Butanone Acetone** **Benzene Carbon disulfide** **Chlorobenzene Chloroform** **Ethylbenzene Methylene chloride** **Styrene Tetrachloroethene** **Toluene Xylenes (total)** Semivolatiles**1,4-Dichlorobenzene Bis(2-ethylhexyl)phthalate** **Dibenzofuran Di-n-butyl phthalate** Polycyclic Aromatic Hydrocarbons**2-Methylnaphthalene Acenaphthene** **Acenaphthylene Anthracene** **Benzo(a)anthracene Benzo(a)pyrene** **Benzo(b)fluoranthene Benzo(k)fluoranthene** **Benzo(g,h,i)perylene Carbazole** **Chrysene Dibenzo(a,h)anthracene** **Fluoranthene Fluorene** **Indeno(1,2,3-cd)pyrene Naphthalene** **Phenanthrene Pyrene** **PAHs, total**Ratio ofRatio ofRatio ofRatio ofSD-2 May-08 Detected SD-2 Oct-08 Detected SD-2 May-09Detected SD-2 Sept-09 DetectedConcentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration toScreening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria**--- ND --- NA --- NA --- --- ND --- 1.15E-02 J --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- 6.10E-04 J 3.49E-03 ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- 4.34E-03 ND --- ND --- ND ---** **--- 1.20E-03 J 9.84E-04 ND --- ND --- --- 3.30E-03 7.62E-03 ND --- NA ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- NA ---**SD-2SD-2 SD-2C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** **4,4'-DDT DDT and Metabolites** **Dieldrin Endosulfan-II** **gamma-Chlordane**Polychlorinated Biphenyls**Aroclor 1254**Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Cadmium** **Calcium Chromium** **Cobalt Copper** **Cyanide Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Silver** **Sodium Thallium** **Tin Vanadium** **Zinc**Ratio ofRatio ofRatio ofRatio ofSD-2 May-08 Detected SD-2 Oct-08 Detected SD-2 May-09Detected SD-2 Sept-09 DetectedConcentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration toScreening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening CriteriaSD-2SD-2 SD-2**1.03E+00 NA --- NA --- NA --- 1.12E+00 NA --- NA --- NA ---** **8.00E-01 NA --- NA --- NA --- 2.89E+00 NA --- NA --- NA ---** **--- NA --- NA --- NA --- --- NA --- NA --- NA ---** **--- NA --- NA --- NA --- --- NA --- NA --- NA ---** **4.12E-02 1.30E+02 5.10E-03 3.62E+02 1.42E-02 4.36E+02 1.7 1E-02** **--- 3.50E-01 J --- ND --- ND --- --- 3.30E-01 J 5.50E-02 ND --- ND ---** **--- ND --- 6.70E+00 J --- ND --- --- ND --- 5.40E-02 J --- ND ---** **--- ND --- ND --- ND --- --- ND --- 1.66E+02 J --- ND ---** **2.08E-01 9.00E-01 J 3.46E-02 2.00E+00 7.69E-02 1.00E+00 J 3 .85E-02** **2.40E-02 ND --- ND --- ND --- 1.81E-01 ND --- 2.70E+00 J 1.69E-01 ND ---** **--- NA --- NA --- NA --- --- 3.64E+02 --- 4.68E+02 --- 3.58E+02 ---** **1.81E-01 ND --- 4.20E+00 1.35E-01 1.70E+00 J 5.48E-02 --- 1.29E+01 J --- 3.03E+01 J --- 2.23E+01 J ---** **1.40E-02 5.10E+00 J 8.10E-03 1.10E+01 J 1.75E-02 1.02E+01 1 .62E-02** **6.00E+00 1.40E-01 7.00E-01 3.40E-02 J 1.70E-01 6.30E-02 3. 15E-01** **--- 2.50E-01 J 1.56E-02 ND --- 2.40E-01 J 1.50E-02 --- NA --- 2.54E+01 J --- ND ---** **--- ND --- ND --- ND --- 1.10E-01 ND --- ND --- ND ---** **--- ND --- 1.90E+01 J --- ND --- --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- --- 9.70E-01 J --- ND --- ND ---** **9.58E-02 ND --- 4.40E+00 J 3.67E-02 2.50E+00 2.08E-02**C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**2-Butanone Acetone** **Benzene Carbon disulfide** **Chlorobenzene Chloroform** **Ethylbenzene Methylene chloride** **Styrene Tetrachloroethene** **Toluene Xylenes (total)** Semivolatiles**1,4-Dichlorobenzene Bis(2-ethylhexyl)phthalate** **Dibenzofuran Di-n-butyl phthalate** Polycyclic Aromatic Hydrocarbons**2-Methylnaphthalene Acenaphthene** **Acenaphthylene Anthracene** **Benzo(a)anthracene Benzo(a)pyrene** **Benzo(b)fluoranthene Benzo(k)fluoranthene** **Benzo(g,h,i)perylene Carbazole** **Chrysene Dibenzo(a,h)anthracene** **Fluoranthene Fluorene** **Indeno(1,2,3-cd)pyrene Naphthalene** **Phenanthrene Pyrene** **PAHs, total**Ratio ofRatio ofRatio ofRatio of SD-3SD-3 May-08 Detected SD-3 Oct-08 Detected SD-3 May-09Detected Relocation Sept-09 DetectedMay-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria**3.70E-02 J --- ND --- NA --- NA --- 4.10E-02 J --- ND --- 1.46E-02 J --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **1.20E-02 J 4.72E-02 ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- 9.30E-04 J 7.62E-04 ND --- ND --- ND --- ND --- NA ---** **6.30E-03 J 1.98E-02 ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **NA --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **5.70E-01 J 1.78E+00 ND --- 4.03E-02 J 1.26E-01 1.43E-02 J 4.4 7E-02** **7.00E-01 J 1.89E+00 ND --- 4.71E-02 J 1.27E-01 ND --- 6.60E-01 J 6.35E-02 ND --- 4.31E-02 J 4.14E-03 ND ---** **7.50E-01 J 3.13E+00 ND --- 3.56E-02 J 1.48E-01 ND --- 2.90E-01 J 1.71E+00 ND --- 3.41E-02 J 2.01E-01 ND ---** **ND --- ND --- ND --- ND --- 8.70E-01 J 2.56E+00 ND --- 4.79E-02 J 1.41E-01 1.44E-02 J 4.2** **4E-02 ND --- ND --- ND --- ND ---** **1.40E+00 J 1.87E+00 ND --- 8.60E-02 1.15E-01 ND --- ND --- ND --- ND --- ND ---** **3.00E-01 J 1.50E+00 ND --- 2.91E-02 J 1.46E-01 ND --- ND --- ND --- ND --- ND ---** **4.20E-01 J 7.50E-01 ND --- 2.80E-02 J 5.00E-02 ND --- 9.80E-01 J 2.00E+00 ND --- 6.67E-02 1.36E-01 ND ---** **2.04E+01 5.09E+00 ND --- 6.24E-01 1.56E-01 NA ---**SD-3 RelocationSD-3 SD-3SD-3C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** **4,4'-DDT DDT and Metabolites** **Dieldrin Endosulfan-II** **gamma-Chlordane**Polychlorinated Biphenyls**Aroclor 1254**Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Cadmium** **Calcium Chromium** **Cobalt Copper** **Cyanide Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Silver** **Sodium Thallium** **Tin Vanadium** **Zinc**Ratio ofRatio ofRatio ofRatio of SD-3SD-3 May-08 Detected SD-3 Oct-08 Detected SD-3 May-09Detected Relocation Sept-09 DetectedMay-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening CriteriaSD-3 RelocationSD-3 SD-3SD-3**ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- NA --- NA ---** **8.40E+03 J 3.29E-01 5.00E+02 1.96E-02 1.72E+03 6.75E-02 4. 33E+02 1.70E-02** **ND --- ND --- ND --- ND --- ND --- 5.40E-01 J 9.00E-02 ND --- ND ---** **1.36E+02 J --- ND --- 2.10E+01 J --- ND --- ND --- ND --- 1.70E-01 J --- ND ---** **6.10E-01 J 1.02E+00 ND --- 2.00E-01 J 3.33E-01 ND --- 5.81E+03 J --- ND --- 3.30E+02 J --- ND ---** **1.29E+01 J 4.96E-01 2.70E+00 1.04E-01 8.10E+00 3.12E-01 1. 80E+00 6.92E-02** **2.19E+01 J 4.38E-01 ND --- 1.90E+00 J 3.80E-02 ND --- 8.10E+00 J 5.06E-01 ND --- 5.50E+00 J 3.44E-01 ND ---** **7.20E-01 J 7.20E+00 NA --- NA --- NA --- 7.99E+04 J --- 1.25E+03 --- 8.03E+03 --- 1.70E+03 ---** **3.85E+01 J 1.24E+00 2.70E+00 J 8.71E-02 7.00E+00 2.26E-01 N D ---** **9.77E+02 J --- 7.58E+01 J --- 2.05E+02 J --- 6.90E+01 J --- 8.20E+02 J 1.30E+00 7.20E+00 J 1.14E-02 4.51E+01 J 7.16E-02** **8.90E+00 1.41E-02 2.20E-01 J 1.10E+00 NA --- NA --- NA ---** **ND --- 6.60E-01 J 4.13E-02 ND --- 3.80E-01 J 2.38E-02 NA --- NA --- 3.55E+02 J --- 1.61E+02 J ---** **ND --- ND --- ND --- ND --- 2.20E-01 J 4.40E-01 ND --- ND --- 2.30E-01 J 4.60E-01** **ND --- 1.08E+01 J --- 3.27E+01 J --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- 2.00E+01 J --- 1.40E+00 J --- ND --- ND ---** **1.72E+02 J 1.43E+00 6.60E+00 5.50E-02 1.86E+01 J 1.55E-01 3 .20E+00 2.67E-02** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**2-Butanone Acetone** **Benzene Carbon disulfide** **Chlorobenzene Chloroform** **Ethylbenzene Methylene chloride** **Styrene Tetrachloroethene** **Toluene Xylenes (total)** Semivolatiles**1,4-Dichlorobenzene Bis(2-ethylhexyl)phthalate** **Dibenzofuran Di-n-butyl phthalate** Polycyclic Aromatic Hydrocarbons**2-Methylnaphthalene Acenaphthene** **Acenaphthylene Anthracene** **Benzo(a)anthracene Benzo(a)pyrene** **Benzo(b)fluoranthene Benzo(k)fluoranthene** **Benzo(g,h,i)perylene Carbazole** **Chrysene Dibenzo(a,h)anthracene** **Fluoranthene Fluorene** **Indeno(1,2,3-cd)pyrene Naphthalene** **Phenanthrene Pyrene** **PAHs, total**Ratio ofRatio ofRatio ofRatio ofRatio ofSD-4 May-08 Detected SD-4 Oct-08 Detected SD-4-DUP Oct-08 Detected SD-4 May-09 Detected SD-4-DUP May-09 DetectedMay-08 Concentration to Oct-08 Concentration to Oct-08 Concentration to May-09 Concentration to May-09 Concentration to Sep-09(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)**ND --- ND --- ND --- NA --- NA --- NA 5.10E-02 J --- ND --- ND --- 3.45E-02 J --- 4.66E-02 J --- ND** **1.90E-03 J 1.34E-02 ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- ND --- ND --- 3.90E-04 J** **ND --- ND --- ND --- 2.00E-03 J 6.87E-03 1.60E-03 J 5.50E-03 5. 90E-04 J** **ND --- ND --- ND --- ND --- ND --- ND ND --- 7.40E-04 J 4.23E-03 ND --- ND --- ND --- ND** **1.10E-02 J 6.92E-02 ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- ND --- ND --- ND** **8.40E-03 J 8.48E-03 ND --- ND --- ND --- ND --- ND ND --- 1.10E-03 J 9.02E-04 1.40E-03 J 1.15E-03 1.30E-03 J 1.0** **7E-03 2.10E-03 1.72E-03 ND ND --- 5.20E-03 1.20E-02 1.34E-02 3.09E-02 ND --- 7.80E-04 J** **1.80E-03 NA ND --- ND --- ND --- ND --- ND --- ND** **1.20E-01 J 6.59E-01 ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- ND --- ND --- ND** **ND --- ND --- ND --- ND --- ND --- ND NA --- ND --- ND --- ND --- ND --- ND** **ND --- ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- ND --- ND --- ND** **ND --- ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- 3.43E-02 J 1.07E-01 ND --- 1.94E-02 J** **ND --- ND --- ND --- 3.92E-02 J 1.06E-01 ND --- ND ND --- ND --- ND --- 3.93E-02 J 3.78E-03 ND --- ND** **ND --- ND --- ND --- 2.81E-02 J 1.17E-01 ND --- ND ND --- ND --- ND --- 3.07E-02 J 1.81E-01 ND --- ND** **ND --- ND --- ND --- ND --- ND --- ND ND --- ND --- 3.38E-02 J 9.94E-02 4.00E-02 J 1.18E-01 ND --- 1.** **38E-02 J ND --- ND --- ND --- ND --- ND --- ND** **1.20E-01 J 1.60E-01 ND --- 5.13E-02 J 6.84E-02 7.44E-02 9.92 E-02 4.06E-02 J 5.41E-02 ND** **ND --- ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- 2.76E-02 J 1.38E-01 ND --- ND** **ND --- ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- 5.17E-02 9.23E-02 2.99E-02 J 5.34E-02 ND** **ND --- ND --- 4.55E-02 J 9.29E-02 5.94E-02 1.21E-01 3.31E-02 J 6.76E-02 1.61E-02 J** **1.41E+01 3.53E+00 ND --- 5.76E-01 1.44E-01 5.78E-01 1.45E- 01 4.64E-01 1.16E-01 NA** SD-4SD-4-DUPSD-4 SD-4 SD-4-DUP SD-4C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** **4,4'-DDT DDT and Metabolites** **Dieldrin Endosulfan-II** **gamma-Chlordane**Polychlorinated Biphenyls**Aroclor 1254**Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Cadmium** **Calcium Chromium** **Cobalt Copper** **Cyanide Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Silver** **Sodium Thallium** **Tin Vanadium** **Zinc**Ratio ofRatio ofRatio ofRatio ofRatio ofSD-4 May-08 Detected SD-4 Oct-08 Detected SD-4-DUP Oct-08 Detected SD-4 May-09 Detected SD-4-DUP May-09 DetectedMay-08 Concentration to Oct-08 Concentration to Oct-08 Concentration to May-09 Concentration to May-09 Concentration to Sep-09(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)SD-4SD-4-DUPSD-4 SD-4 SD-4-DUP SD-4**ND --- ND --- 2.90E-03 3.63E-01 3.30E-03 4.13E-01 ND --- ND 1.50E-02 J 3.00E+00 ND --- 1.78E-02 3.56E+00 7.20E-03 1.44E** **+00 5.90E-03 1.18E+00 ND ND --- ND --- 3.70E-03 4.63E-01 ND --- ND --- ND** **2.56E-02 3.66E+00 ND --- 2.44E-02 3.49E+00 1.10E-02 1.57E+ 00 6.75E-03 9.64E-01 ND** **ND --- ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- ND --- ND --- ND** **ND --- ND --- ND --- ND --- ND --- ND ND --- ND --- ND --- NA --- NA --- NA** **2.32E+03 J 9.10E-02 9.95E+02 3.90E-02 1.17E+03 J 4.59E-02 1 .29E+03 5.06E-02 1.03E+03 4.04E-02 6.07E+02** **ND --- ND --- ND --- ND --- ND --- ND ND --- 1.90E+00 J 3.17E-01 1.50E+00 J 2.50E-01 ND --- ND --- ND** **2.43E+01 J --- ND --- ND --- 1.23E+01 J --- 1.37E+01 J --- ND ND --- ND --- ND --- 4.60E-02 J --- 6.90E-02 J --- ND** **ND --- ND --- ND --- 1.20E-01 J 2.00E-01 ND --- ND 3.31E+03 J --- 1.04E+03 --- 1.18E+03 J --- 1.29E+03 --- 9.62E** **+02 --- ND 6.20E+00 J 2.38E-01 3.60E+00 1.38E-01 4.10E+00 J 1.58E-01 4** **.20E+00 1.62E-01 3.50E+00 1.35E-01 1.70E+00 7.70E+00 J 1.54E-01 ND --- ND --- 3.30E+00 J 6.60E-02 5.10E+0** **0 J 1.02E-01 ND 6.00E+00 J 3.75E-01 6.60E+00 4.13E-01 5.10E+00 J 3.19E-01 7** **.40E+00 J 4.63E-01 6.10E+00 J 3.81E-01 ND 6.00E-01 J 6.00E+00 NA --- NA --- NA --- NA --- NA** **1.02E+04 J --- 3.42E+03 --- 2.93E+03 J --- 2.78E+03 --- 4.01E +03 --- 2.18E+03** **4.71E+01 J 1.52E+00 2.30E+01 J 7.42E-01 2.13E+01 J 6.87E-01 2.60E+01 8.39E-01 2.10E+01 6.77E-01 1.26E+01** **1.91E+02 J --- 8.67E+01 J --- ND --- 1.27E+02 J --- 1.04E+02 J - -- ND** **5.92E+01 J 9.40E-02 4.06E+01 J 6.44E-02 5.37E+01 J 8.52E-02 2.06E+01 J 3.27E-02 2.20E+01 J 3.49E-02 1.50E+01** **1.70E-01 J 8.50E-01 5.40E-02 2.70E-01 7.50E-02 J 3.75E-01 4 .20E-02 J 2.10E-01 5.00E-02 J 2.50E-01 ND** **ND --- 1.30E+00 J 8.13E-02 9.50E-01 J 5.94E-02 ND --- ND --- 5. 20E-01 J** **NA --- NA --- NA --- 1.05E+02 J --- 9.95E+01 J --- ND ND --- ND --- ND --- ND --- ND --- ND** **3.30E-01 J 6.60E-01 ND --- ND --- ND --- ND --- 3.90E-01 J ND --- 1.23E+01 J --- 1.58E+01 J --- 2.31E+01 J --- 2.65E+01 J -** **-- ND ND --- 3.80E-01 J --- ND --- ND --- ND --- ND** **2.40E+00 J --- ND --- ND --- ND --- ND --- 6.80E+00 1.22E+01 J --- 3.90E+00 J --- 4.00E+00 J --- ND --- ND --- ND** **2.41E+01 J 2.01E-01 7.60E+00 6.33E-02 1.02E+01 J 8.50E-02 1 .05E+01 J 8.75E-02 1.02E+01 J 8.50E-02 5.30E+00** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**2-Butanone Acetone** **Benzene Carbon disulfide** **Chlorobenzene Chloroform** **Ethylbenzene Methylene chloride** **Styrene Tetrachloroethene** **Toluene Xylenes (total)** Semivolatiles**1,4-Dichlorobenzene Bis(2-ethylhexyl)phthalate** **Dibenzofuran Di-n-butyl phthalate** Polycyclic Aromatic Hydrocarbons**2-Methylnaphthalene Acenaphthene** **Acenaphthylene Anthracene** **Benzo(a)anthracene Benzo(a)pyrene** **Benzo(b)fluoranthene Benzo(k)fluoranthene** **Benzo(g,h,i)perylene Carbazole** **Chrysene Dibenzo(a,h)anthracene** **Fluoranthene Fluorene** **Indeno(1,2,3-cd)pyrene Naphthalene** **Phenanthrene Pyrene** **PAHs, total**Ratio ofRatio ofRatio ofRatio ofRatio ofSD-4 Sept-09 Detected SD-5 May-08 Detected SD-5 Oct-08 Detected SD-5 May-09 Detected SD-5 Sept-09 DetectedConcentration to May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration toScreening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria**--- ND --- ND --- NA --- NA --- --- 7.30E-02 --- ND --- 2.18E-02 J --- 6.20E-02 ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- 4.20E-03 ---** **2.03E-03 ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- 1.10E-03 J 9.02E-04 ND --- ND --- ND --- --- ND --- ND --- ND --- NA ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- NA --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **6.06E-02 ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **4.06E-02 ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- 3.29E-02 ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- NA ---**SD-5 SD-5 SD-5 SD-5C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** **4,4'-DDT DDT and Metabolites** **Dieldrin Endosulfan-II** **gamma-Chlordane**Polychlorinated Biphenyls**Aroclor 1254**Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Cadmium** **Calcium Chromium** **Cobalt Copper** **Cyanide Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Silver** **Sodium Thallium** **Tin Vanadium** **Zinc**Ratio ofRatio ofRatio ofRatio ofRatio ofSD-4 Sept-09 Detected SD-5 May-08 Detected SD-5 Oct-08 Detected SD-5 May-09 Detected SD-5 Sept-09 DetectedConcentration to May-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration toScreening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening CriteriaSD-5 SD-5 SD-5 SD-5**--- 1.10E-02 J 1.38E+00 1.61E-02 2.01E+00 ND --- 5.30E-03 6. 63E-01** **--- 4.70E-02 9.40E+00 3.16E-02 6.32E+00 1.83E-02 3.66E+00 4.10E-03 8.20E-01** **--- 2.90E-02 3.63E+00 ND --- 6.50E-03 NJ** **8.13E-01 ND --- --- 8.70E-02 1.24E+01 5.02E-02 7.17E+00 2.51E-02 3.59E+00** **1.01E-02 1.45E+00 --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- NA --- NA --- 2.38E-02 7.86E+02 J 3.08E-02 2.92E+03 J 1.15E-01 4.28E+02 1** **.68E-02 4.06E+02 1.59E-02 --- ND --- ND --- ND --- ND ---** **--- ND --- 5.60E+00 J 9.33E-01 ND --- ND --- --- 2.51E+01 J --- 7.59E+01 J --- 2.01E+01 J --- ND ---** **--- ND --- ND --- 2.80E-02 J --- ND --- --- ND --- ND --- 4.20E-02 J 7.00E-02 ND ---** **--- 3.40E+02 J --- 1.27E+04 J --- 1.74E+02 J --- ND --- 6.54E-02 1.60E+00 J 6.15E-02 7.70E+00 J 2.96E-01 ND --- ND --** **- --- ND --- 1.00E+00 J 2.00E-02 ND --- ND ---** **--- 2.60E+00 J 1.63E-01 1.35E+01 J 8.44E-01 3.60E+00 J 2.25E -01 ND ---** **--- ND --- NA --- NA --- NA --- --- 1.39E+03 J --- 1.46E+05 J --- 4.97E+02 --- 1.75E+03 ---** **4.06E-01 3.17E+01 J 1.02E+00 4.88E+01 J 1.57E+00 1.84E+01 5 .94E-01 8.00E+00 2.58E-01** **--- ND --- ND --- 2.41E+01 J --- ND --- 2.38E-02 3.60E+00 J 5.71E-03 1.92E+02 J 3.05E-01 2.60E+00 J** **4.13E-03 6.20E+00 9.84E-03 --- 6.30E-02 J 3.15E-01 1.90E-01 J 9.50E-01 ND --- ND ---** **3.25E-02 ND --- ND --- ND --- 3.10E-01 J 1.94E-02 --- NA --- NA --- 3.61E+01 J --- ND ---** **--- ND --- 5.00E+00 J --- ND --- ND --- 7.80E-01 ND --- ND --- ND --- 4.40E-01 J 8.80E-01** **--- ND --- 8.22E+01 J --- 2.00E+01 J --- ND --- --- ND --- ND --- ND --- ND ---** **--- ND --- ND --- ND --- ND --- --- 4.00E+00 J --- ND --- ND --- ND ---** **4.42E-02 1.35E+01 J 1.13E-01 4.01E+01 3.34E-01 5.30E+00 J 4 .42E-02 6.20E+00 5.17E-02** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**2-Butanone Acetone** **Benzene Carbon disulfide** **Chlorobenzene Chloroform** **Ethylbenzene Methylene chloride** **Styrene Tetrachloroethene** **Toluene Xylenes (total)** Semivolatiles**1,4-Dichlorobenzene Bis(2-ethylhexyl)phthalate** **Dibenzofuran Di-n-butyl phthalate** Polycyclic Aromatic Hydrocarbons**2-Methylnaphthalene Acenaphthene** **Acenaphthylene Anthracene** **Benzo(a)anthracene Benzo(a)pyrene** **Benzo(b)fluoranthene Benzo(k)fluoranthene** **Benzo(g,h,i)perylene Carbazole** **Chrysene Dibenzo(a,h)anthracene** **Fluoranthene Fluorene** **Indeno(1,2,3-cd)pyrene Naphthalene** **Phenanthrene Pyrene** **PAHs, total**Ratio ofRatio ofRatio ofRatio ofRatio ofSD-6 May-08 Detected SD-6 Oct-08 Detected SD-6 May-09Detected SD-6 Sept-09 Detected SD-6-DUP Sept-09 DetectedMay-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to Sep-09 Concentration to(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria**ND --- 5.78E-02 J --- 5.72E-02 J --- NA --- NA --- 2.20E+00 D --- 7.95E-01 --- 3.77E-01 J --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- 2.63E-02 J --- 1.32E-02 J --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- NA --- NA ---** **5.40E-03 J 1.70E-02 ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- 4.33E-02 J 2.38E-01** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **NA --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- 2.08E-02 J 6.50E-02 ND --- ND --- ND --- ND --- 1.78E-02 J 4.81E-02** **ND --- ND --- ND --- ND --- 2.46E-02 J 2.37E-03 ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- 1.93E-02 J 1.14E-01 ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- 1.88E-02 J 5.53E-02 ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- 2.60E-02 J 3.47E-02 2.18E-02 J 2.91E-02 ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- 1.70E-02 J 8.50E-02 ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- 2.39E-02 J 4.88E-02 2.37E-02 J 4.84E-02** **ND --- ND --- ND --- NA --- NA ---**SD-6-DUPSD-6 SD-6SD-6 SD-6C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** **4,4'-DDT DDT and Metabolites** **Dieldrin Endosulfan-II** **gamma-Chlordane**Polychlorinated Biphenyls**Aroclor 1254**Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Cadmium** **Calcium Chromium** **Cobalt Copper** **Cyanide Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Silver** **Sodium Thallium** **Tin Vanadium** **Zinc**Ratio ofRatio ofRatio ofRatio ofRatio ofSD-6 May-08 Detected SD-6 Oct-08 Detected SD-6 May-09Detected SD-6 Sept-09 Detected SD-6-DUP Sept-09 DetectedMay-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to Sep-09 Concentration to(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening CriteriaSD-6-DUPSD-6 SD-6SD-6 SD-6**ND --- 2.39E-02 2.99E+00 ND --- 9.00E-03 1.13E+00 1.15E-02 1 .44E+00** **ND --- 3.13E-02 6.26E+00 1.57E-02 J 3.14E+00 4.07E-02 8.14E +00 4.42E-02 8.84E+00** **ND --- ND --- 8.10E-03 1.01E+00 2.04E-02 2.55E+00 1.90E-02 2 .38E+00** **ND --- 5.78E-02 8.26E+00 2.45E-02 3.50E+00 7.01E-02 1.00E+ 01 7.47E-02 1.07E+01** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- NA --- NA --- NA ---** **4.23E+02 J 1.66E-02 1.11E+03 J 4.35E-02 1.26E+03 J 4.94E-02 1.18E+03 4.63E-02 4.97E+02 1.95E-02** **ND --- 3.89E+01 J --- ND --- ND --- ND --- ND --- 2.37E+01 J 3.95E+00 ND --- ND --- ND ---** **1.13E+01 J --- 1.26E+02 J --- 3.58E+01 J --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- 2.20E-01 J 3.67E-01 ND --- ND --- 2.00E+03 J --- 3.52E+03 J --- 6.39E+03 J --- 2.50E+03 --- 1.00** **E+03 --- ND --- 7.10E+00 J 2.73E-01 4.90E+00 J 1.88E-01 3.40E+00 1.31** **E-01 1.70E+00 6.54E-02 ND --- ND --- 4.40E-01 J 8.80E-03 ND --- ND ---** **ND --- ND --- 1.94E+01 J 1.21E+00 8.30E+00 5.19E-01 3.70E+00 2.31E-01** **ND --- NA --- NA --- NA --- NA --- 1.54E+04 J --- 3.50E+05 J --- 3.04E+04 J --- 2.11E+03 --- 1.04** **E+03 --- 1.24E+01 J 4.00E-01 2.35E+01 J 7.58E-01 3.58E+01 J 1.15E+00** **2.32E+01 7.48E-01 1.14E+01 3.68E-01 9.84E+01 J --- 1.17E+02 J --- 3.34E+02 J --- ND --- ND ---** **1.05E+01 J 1.67E-02 1.67E+02 J 2.65E-01 3.05E+01 J 4.84E-02 1.44E+01 2.29E-02 9.20E+00 1.46E-02** **1.20E-01 J 6.00E-01 1.70E-01 J 8.50E-01 ND --- ND --- ND --- ND --- ND --- ND --- 4.90E+00 J 3.06E-01 1.40E+00 J 8.75E-02** **NA --- NA --- 1.19E+02 J --- ND --- ND --- ND --- ND --- 1.60E+00 J --- ND --- ND ---** **ND --- ND --- ND --- 5.70E-01 J 1.14E+00 3.40E-01 J 6.80E-01 ND --- 2.00E+02 J --- 1.07E+02 J --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- 6.50E+00 J --- ND --- ND --- ND --- 4.02E+01 J 3.35E-01 1.59E+02 J 1.33E+00 5.36E+01 J 4.47E-01** **2.75E+01 2.29E-01 1.23E+01 1.03E-01**C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**2-Butanone Acetone** **Benzene Carbon disulfide** **Chlorobenzene Chloroform** **Ethylbenzene Methylene chloride** **Styrene Tetrachloroethene** **Toluene Xylenes (total)** Semivolatiles**1,4-Dichlorobenzene Bis(2-ethylhexyl)phthalate** **Dibenzofuran Di-n-butyl phthalate** Polycyclic Aromatic Hydrocarbons**2-Methylnaphthalene Acenaphthene** **Acenaphthylene Anthracene** **Benzo(a)anthracene Benzo(a)pyrene** **Benzo(b)fluoranthene Benzo(k)fluoranthene** **Benzo(g,h,i)perylene Carbazole** **Chrysene Dibenzo(a,h)anthracene** **Fluoranthene Fluorene** **Indeno(1,2,3-cd)pyrene Naphthalene** **Phenanthrene Pyrene** **PAHs, total**Ratio ofRatio ofRatio ofRatio ofSD-7 May-08 Detected SD-7 Oct-08 Detected SD-7 May-09Detected SD-7 Sept-09 DetectedMay-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria**ND --- NA --- NA --- NA --- ND --- NA --- NA --- NA ---** **ND --- NA --- NA --- NA --- ND --- NA --- NA --- NA ---** **ND --- NA --- NA --- NA --- ND --- NA --- NA --- NA ---** **ND --- NA --- NA --- NA --- ND --- NA --- NA --- NA ---** **ND --- NA --- NA --- NA --- ND --- NA --- NA --- NA ---** **ND --- NA --- NA --- NA --- ND --- NA --- NA --- NA ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- 7.61E-02 J --- ND --- 4.20E-02 J 3.77E-02 ND --- 1.62E-01 1.45E-01 ND ---** **NA --- ND --- 2.78E-01 1.38E+01 ND --- ND --- 2.27E-02 J 3.38E+00 ND --- ND ---** **4.30E-02 J 7.33E+00 3.64E-02 J 6.20E+00 5.39E-02 9.18E+00 N D ---** **ND --- 1.30E-01 5.91E-01 6.76E-02 3.07E-01 ND --- 7.60E-02 J 2.38E-01 9.42E-01 2.94E+00 1.65E-01 5.16E-01 ND** **--- 8.90E-02 J 2.41E-01 1.13E+00 3.05E+00 1.88E-01 5.08E-01 ND** **--- 9.60E-02 J 9.23E-03 1.10E+00 1.06E-01 1.87E-01 1.80E-02 ND** **--- 8.50E-02 J 3.54E-01 8.98E-01 3.74E+00 1.10E-01 4.58E-01 ND** **--- 4.30E-02 J 2.53E-01 9.23E-01 5.43E+00 1.50E-01 8.82E-01 ND** **--- ND --- 5.33E-02 J --- 2.76E-02 J --- ND ---** **1.30E-01 J 3.82E-01 1.02E+00 3.00E+00 2.32E-01 6.82E-01 ND ---** **ND --- 2.92E-01 4.87E+00 5.92E-02 9.87E-01 ND --- 1.60E-01 J 2.13E-01 1.46E+00 1.95E+00 2.91E-01 3.88E-01 1.** **82E-02 J 2.43E-02 ND --- 2.72E-02 J 1.43E-01 ND --- ND ---** **4.20E-02 J 2.10E-01 7.73E-01 3.87E+00 1.23E-01 6.15E-01 ND ---** **ND --- ND --- 1.68E-01 9.55E-01 ND --- 1.00E-01 J 1.79E-01 5.04E-01 9.00E-01 2.92E-01 5.21E-01 ND** **--- 1.20E-01 J 2.45E-01 1.31E+00 2.67E+00 2.70E-01 5.51E-01 ND** **--- 3.18E+00 7.95E-01 8.96E+00 2.24E+00 2.59E+00 6.47E-01 NA -** **--**SD-7 SD-7 SD-7 SD-7C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** **4,4'-DDT DDT and Metabolites** **Dieldrin Endosulfan-II** **gamma-Chlordane**Polychlorinated Biphenyls**Aroclor 1254**Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Cadmium** **Calcium Chromium** **Cobalt Copper** **Cyanide Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Silver** **Sodium Thallium** **Tin Vanadium** **Zinc**Ratio ofRatio ofRatio ofRatio ofSD-7 May-08 Detected SD-7 Oct-08 Detected SD-7 May-09Detected SD-7 Sept-09 DetectedMay-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening CriteriaSD-7 SD-7 SD-7 SD-7**ND --- 9.70E-03 1.21E+00 3.69E-02 J 4.61E+00 ND --- 8.90E-02 1.78E+01 8.59E-02 1.72E+01 7.70E-01 1.54E+02 ND -** **-- 7.70E-02 9.63E+00 9.64E-02 1.21E+01 7.56E-01 9.45E+01 ND -** **-- 2.05E-01 2.93E+01 1.92E-01 2.74E+01 1.56E+00 2.23E+02 ND -** **-- ND --- 8.70E-03 J 4.35E+00 ND --- ND ---** **ND --- ND --- 4.10E-03 J --- ND --- ND --- 2.30E-03 J 3.29E-01 ND --- ND ---** **ND --- 1.12E+00 J 1.87E+01 NA --- NA --- 2.25E+03 N 8.82E-02 5.18E+03 2.03E-01 4.80E+03 1.88E-01 7.** **89E+02 3.09E-02 ND --- 8.60E+00 J --- 3.70E+00 --- ND ---** **ND --- 4.70E+00 7.83E-01 5.80E+00 9.67E-01 ND --- 1.47E+01 J --- 1.60E+02 --- 4.44E+01 --- ND ---** **ND --- ND --- 2.20E-01 J --- ND --- ND --- 1.50E+00 2.50E+00 4.20E-01 J 7.00E-01 ND ---** **2.55E+02 J --- 3.03E+03 --- 3.14E+03 --- ND --- 7.00E+00 J 2.69E-01 2.35E+01 9.04E-01 1.69E+01 6.50E-01 1.** **70E+00 6.54E-02 7.00E-01 J 1.40E-02 ND --- 1.90E+00 J 3.80E-02 ND ---** **8.00E+00 J 5.00E-01 8.11E+01 5.07E+00 1.90E+01 J 1.19E+00 1 .57E+01 9.81E-01** **1.30E-01 J 1.30E+00 NA --- NA --- NA --- 4.94E+03 N --- 1.39E+04 --- 1.47E+04 --- 1.40E+03 ---** **7.71E+01 J 2.49E+00 9.00E+02 J 2.90E+01 1.09E+02 3.52E+00 4 .55E+01 1.47E+00** **9.27E+01 J --- 1.03E+03 --- 6.66E+02 J --- ND --- 2.60E+01 J 4.13E-02 1.64E+02 J 2.60E-01 9.86E+01 J 1.57E-01** **2.50E+00 3.97E-03 1.10E-01 5.50E-01 1.00E-01 5.00E-01 1.50E+00 7.50E+00 ND -** **-- ND --- 1.22E+01 7.63E-01 7.80E+00 4.88E-01 6.50E-01 J 4.06E** **-02 NA --- NA --- 4.82E+02 J --- ND ---** **ND --- ND --- 6.80E-01 J --- ND --- 1.10E-01 J 2.20E-01 5.80E-01 J 1.16E+00 ND --- 2.30E-01 J 4.6** **0E-01 ND --- 1.22E+02 J --- 3.56E+01 J --- ND ---** **ND --- ND --- ND --- ND --- 6.80E+00 J --- 1.41E+01 --- 2.92E+01 --- ND ---** **8.90E+00 J --- 1.86E+01 --- 1.79E+01 J --- ND --- 3.58E+01 J 2.98E-01 6.95E+02 5.79E+00 1.19E+02 J 9.92E-01 4** **.20E+00 3.50E-02**C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**2-Butanone Acetone** **Benzene Carbon disulfide** **Chlorobenzene Chloroform** **Ethylbenzene Methylene chloride** **Styrene Tetrachloroethene** **Toluene Xylenes (total)** Semivolatiles**1,4-Dichlorobenzene Bis(2-ethylhexyl)phthalate** **Dibenzofuran Di-n-butyl phthalate** Polycyclic Aromatic Hydrocarbons**2-Methylnaphthalene Acenaphthene** **Acenaphthylene Anthracene** **Benzo(a)anthracene Benzo(a)pyrene** **Benzo(b)fluoranthene Benzo(k)fluoranthene** **Benzo(g,h,i)perylene Carbazole** **Chrysene Dibenzo(a,h)anthracene** **Fluoranthene Fluorene** **Indeno(1,2,3-cd)pyrene Naphthalene** **Phenanthrene Pyrene** **PAHs, total**Ratio ofRatio ofRatio ofRatio ofSD-8 May-08 Detected SD-8 Oct-08 Detected SD-8 May-09Detected SD-8 Sept-09 DetectedMay-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria**1.60E-01 J --- 4.26E-02 J --- NA --- NA --- 5.60E-01 J --- 7.49E-01 --- 3.34E-01 J --- ND ---** **ND --- ND --- ND --- ND --- 9.40E-03 J --- ND --- ND --- 3.50E-04 J ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- NA ---** **1.50E-02 J 4.72E-02 ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **NA --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- 1.72E-02 J 3.51E-02** **ND --- ND --- ND --- NA ---**SD-8SD-8SD-8 SD-8C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** **4,4'-DDT DDT and Metabolites** **Dieldrin Endosulfan-II** **gamma-Chlordane**Polychlorinated Biphenyls**Aroclor 1254**Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Cadmium** **Calcium Chromium** **Cobalt Copper** **Cyanide Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Silver** **Sodium Thallium** **Tin Vanadium** **Zinc**Ratio ofRatio ofRatio ofRatio ofSD-8 May-08 Detected SD-8 Oct-08 Detected SD-8 May-09Detected SD-8 Sept-09 DetectedMay-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening CriteriaSD-8SD-8SD-8 SD-8**ND --- 2.89E-01 3.61E+01 9.80E-03 J 1.23E+00 ND --- ND --- 1.57E-01 J 3.14E+01 1.96E-02 J 3.92E+00 ND ---** **ND --- 2.95E-02 J 3.69E+00 2.03E-02 J 2.54E+00 ND --- ND --- 4.76E-01 6.79E+01 4.97E-02 7.10E+00 ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- NA --- NA ---** **4.17E+03 J 1.64E-01 6.10E+03 J 2.39E-01 3.17E+03 J 1.24E-01 9.62E+02 3.77E-02** **ND --- ND --- ND --- ND --- ND --- 9.80E+00 J 1.63E+00 ND --- ND ---** **1.06E+02 J --- 1.38E+02 J --- 2.61E+02 J --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- 3.06E+03 J --- 2.95E+03 J --- 6.99E+03 J --- ND ---** **9.40E+00 J 3.62E-01 1.56E+01 J 6.00E-01 9.60E+00 J 3.69E-01 3.20E+00 1.23E-01** **ND --- 1.24E+01 J 2.48E-01 4.30E+00 J 8.60E-02 ND --- 1.03E+01 J 6.44E-01 1.80E+01 J 1.13E+00 2.43E+01 J 1.52E+00** **ND --- ND --- ND --- ND --- ND ---** **1.36E+04 J --- 1.05E+05 J --- 8.06E+04 J --- 4.67E+03 --- 2.71E+01 J 8.74E-01 3.46E+01 J 1.12E+00 3.09E+01 J 9.97E-01** **ND --- 2.31E+03 J --- 1.79E+03 J --- 4.04E+03 J --- ND ---** **8.64E+01 J 1.37E-01 2.05E+02 J 3.25E-01 5.18E+02 J 8.22E-01 1.33E+01 2.11E-02** **1.90E-01 J 9.50E-01 2.00E-01 J 1.00E+00 ND --- ND --- ND --- 1.70E+01 J 1.06E+00 ND --- 1.30E+00 J 8.13E-02** **NA --- NA --- 5.78E+02 J --- ND --- ND --- 3.70E+00 J --- 4.10E+00 J --- ND ---** **1.50E-01 J 3.00E-01 ND --- ND --- 4.00E-01 J 8.00E-01 3.43E+02 J --- 2.97E+02 J --- 4.23E+02 J --- ND ---** **ND --- ND --- 1.70E+00 J --- ND --- ND --- ND --- ND --- ND ---** **1.40E+01 J --- ND --- ND --- ND --- 6.45E+01 J 5.38E-01 1.14E+02 J 9.50E-01 5.24E+01 J 4.37E-01** **6.40E+00 5.33E-02**C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**2-Butanone Acetone** **Benzene Carbon disulfide** **Chlorobenzene Chloroform** **Ethylbenzene Methylene chloride** **Styrene Tetrachloroethene** **Toluene Xylenes (total)** Semivolatiles**1,4-Dichlorobenzene Bis(2-ethylhexyl)phthalate** **Dibenzofuran Di-n-butyl phthalate** Polycyclic Aromatic Hydrocarbons**2-Methylnaphthalene Acenaphthene** **Acenaphthylene Anthracene** **Benzo(a)anthracene Benzo(a)pyrene** **Benzo(b)fluoranthene Benzo(k)fluoranthene** **Benzo(g,h,i)perylene Carbazole** **Chrysene Dibenzo(a,h)anthracene** **Fluoranthene Fluorene** **Indeno(1,2,3-cd)pyrene Naphthalene** **Phenanthrene Pyrene** **PAHs, total**Ratio ofRatio ofRatio ofRatio ofRatio ofSD-9 May-08 Detected SD-9 Oct-08 Detected SD-9 May-09Detected SD-9 Sept-09 Detected SD-10 Sept-09 DetectedMay-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to Sep-09 Concentration to(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria**ND --- ND --- NA --- NA --- NA --- 1.20E-01 J --- 1.03E-01 --- 4.63E+00 J --- 7.50E-03 J --- ND --** **- ND --- ND --- ND --- ND --- ND ---** **ND --- 4.60E-03 J --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- 1.00E-02 J 8.26E-02 ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- NA --- NA --- ND --- NA --- NA --- NA --- ND ---** **ND --- NA --- NA --- NA --- ND --- ND --- NA --- NA --- NA --- ND ---** **ND --- NA --- NA --- NA --- ND --- NA --- NA --- NA --- NA --- ND ---** **ND --- NA --- NA --- NA --- ND --- ND --- NA --- NA --- NA --- 1.13E-02 J 1.93E+00** **ND --- NA --- NA --- NA --- ND --- ND --- NA --- NA --- NA --- 4.51E-02 1.41E-01** **ND --- NA --- NA --- NA --- 3.76E-02 1.02E-01 ND --- NA --- NA --- NA --- 6.52E-02 6.27E-03** **ND --- NA --- NA --- NA --- 3.30E-02 J 1.38E-01 ND --- NA --- NA --- NA --- 3.69E-02 2.17E-01** **ND --- NA --- NA --- NA --- ND --- ND --- NA --- NA --- NA --- 7.34E-02 2.16E-01** **ND --- NA --- NA --- NA --- 1.35E-02 J 2.25E-01 1.90E-01 J 2.53E-01 NA --- NA --- NA --- 8.15E-02 1.09E-01** **ND --- NA --- NA --- NA --- ND --- ND --- NA --- NA --- NA --- 3.47E-02 1.74E-01** **ND --- NA --- NA --- NA --- ND --- ND --- NA --- NA --- NA --- 2.73E-02 J 4.88E-02** **ND --- NA --- NA --- NA --- 8.06E-02 1.64E-01 2.54E+01 6.35E+00 NA --- NA --- NA --- NA ---** SD-9SD-10SD-9 SD-9 SD-9C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** **4,4'-DDT DDT and Metabolites** **Dieldrin Endosulfan-II** **gamma-Chlordane**Polychlorinated Biphenyls**Aroclor 1254**Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Cadmium** **Calcium Chromium** **Cobalt Copper** **Cyanide Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Silver** **Sodium Thallium** **Tin Vanadium** **Zinc**Ratio ofRatio ofRatio ofRatio ofRatio ofSD-9 May-08 Detected SD-9 Oct-08 Detected SD-9 May-09Detected SD-9 Sept-09 Detected SD-10 Sept-09 DetectedMay-08 Concentration to Oct-08 Concentration to May-09 Concentration to Sep-09 Concentration to Sep-09 Concentration to(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening Criteria(mg/kg)Screening CriteriaSD-9SD-10SD-9 SD-9 SD-9**1.30E-01 J 1.63E+01 8.70E-03 1.09E+00 2.13E-02 J 2.66E+00 N D --- ND ---** **1.50E-01 3.00E+01 6.43E-02 1.29E+01 1.88E-01 3.76E+01 ND - -- ND ---** **ND --- 1.51E-02 1.89E+00 5.31E-01 6.64E+01 ND --- ND --- 3.72E-01 5.31E+01 8.81E-02 1.26E+01 7.40E-01 1.06E+02 ND -** **-- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **ND --- ND --- NA --- NA --- NA --- 6.35E+03 J 2.49E-01 8.72E+03 J 3.42E-01 2.10E+03 J 8.24E-02** **4.75E+01 1.86E-03 1.91E+03 7.49E-02 ND --- 3.10E+00 J --- 1.80E+00 J --- ND --- ND ---** **ND --- 9.40E+00 J 1.57E+00 ND --- ND --- ND --- 2.27E+01 J --- 1.03E+02 J --- 1.41E+01 J --- ND --- ND ---** **ND --- ND --- 9.80E-02 J --- ND --- ND --- ND --- 1.10E+00 J 1.83E+00 2.60E-01 J 4.33E-01 ND --- ND ---** **5.74E+02 J --- 1.47E+04 J --- 2.55E+02 J --- ND --- 2.38E+03 -- -** **5.70E+00 J 2.19E-01 2.36E+01 J 9.08E-01 9.00E+00 J 3.46E-01 3.40E-01 J 1.31E-02 2.10E+00 8.08E-02** **ND --- ND --- 9.80E-01 J 1.96E-02 ND --- ND --- 3.23E+01 J 2.02E+00 3.26E+01 J 2.04E+00 1.79E+01 J 1.12E+00** **ND --- 3.59E+01 2.24E+00 ND --- NA --- NA --- NA --- NA ---** **1.52E+03 J --- 1.44E+04 J --- 6.38E+03 J --- 2.43E+02 --- 6.48 E+03 ---** **4.34E+02 J 1.40E+01 1.60E+02 J 5.16E+00 1.01E+02 J 3.26E+00 7.80E-01 J 2.52E-02 ND ---** **9.05E+01 J --- ND --- 1.81E+02 J --- 6.90E+00 J --- 1.00E+03 -- -** **1.62E+01 J 2.57E-02 2.66E+02 J 4.22E-01 2.13E+01 J 3.38E-02 ND --- 1.22E+02 1.94E-01** **3.20E-01 J 1.60E+00 5.20E-01 J 2.60E+00 1.70E-01 J 8.50E-01 3.70E-01 1.85E+00 ND ---** **ND --- 1.26E+01 J 7.88E-01 ND --- ND --- 2.00E+00 J 1.25E-01 NA --- NA --- 3.98E+02 J --- ND --- ND ---** **ND --- ND --- 1.30E+00 J --- ND --- ND --- 1.50E-01 J 3.00E-01 5.00E-01 J 1.00E+00 ND --- ND --- 4.40E-0** **1 J 8.80E-01 ND --- 9.89E+01 J --- 1.22E+02 J --- ND --- ND ---** **ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND --- ND ---** **2.52E+01 J --- 2.52E+01 J --- 1.90E+01 J --- ND --- 2.36E+01 -- -** **5.09E+01 J 4.24E-01 3.34E+02 J 2.78E+00 6.14E+01 J 5.12E-01 9.00E-01 J 7.50E-03 1.39E+01 1.16E-01** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$WP'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)CQH\CIJ&JL&)CQH\CIJ&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCX**Note: Shading indicates the maximum detection exceeds the benchmark. LEL = Lowest effect level.** **mg/kg = Milligrams per kilogram. NA = Not analyzed.** **ND = Not detected. NBA = No benchmark available.** **a NJDEP (New Jersey Department of Environmental Protection). Ecological Screening Criteria (ESC): 2009.** **b Chlordane value used as a surrogate.** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXFresh water(FW2)Ratio ofFrequencyCriteriaaSW-1 Sept-09 DetectedofChronic Sep-09 Concentration toChemical Detection(μg/L) (μg/L)ScreeningCriteriaVolatiles**1,1-Dichloroethane 1/15 4.4E-01 - 4.4E-01 NB A** **N A** **--- Acetone 2/9 5.8E+00 - 5.8E+00 NBA NA ---** **Carbon Disulfide 2/15 1.3E+00 - 1.7E+00 NBA NA --- Chloromethane 1/15 1.0E-01 - 1.0E-01 NBA NA ---** **cis-1,2-Dichloroethene 1/15 3.1E-01 - 3.1E-01 NBA NA --- trans-1,2-Dichloroethene 1/15 3.1E-01 - 3.1E-01 9.70E+02** **NA --- 1,2-Dichloroethene (total) 1/9 6.2E-01 - 6.2E-01 NBA NA --** **- Toluene 1/15 1.0E+00 - 1.0E+00 2.53E+02 NA ---** Semivolatiles**3-Methylphenol & 4-Methylphenol 1/13 1.1E+00 - 1.1E+00 N BA NA ---** **Bis(2-ethylhexyl)phthalate 2/13 1.2E+00 - 1.4E+00 3.00E- 01 NA ---** **Butyl Benzyl Phthalate 1/13 1.7E+00 - 1.7E+00 2.30E+01 NA --- Phenol 1/13 5.2E+00 - 5.2E+00 1.80E+02 NA ---** Polycyclic Aromatic Hydrocarbons**Anthracene 1/13 1.8E-01 - 1.8E-01 3.50E-02 NA --- Benzo(a)anthracene 1/13 5.8E-01 - 5.8E-01 2.50E-02 NA ---** **Benzo(a)pyrene 1/13 4.4E-01 - 4.4E-01 1.40E-02 NA --- Benzo(b)fluoranthene 1/13 7.7E-01 - 7.7E-01 9.07E+00 NA --** **- Benzo(k)fluoranthene 2/13 2.3E-01 - 3.9E-01 NBA NA ---** **Benzo(g,h,i)perylene 1/13 2.8E-01 - 2.8E-01 7.64E+00 NA -- -** **Chrysene 1/13 5.9E-01 - 5.9E-01 NBA NA --- Fluoranthene 2/13 3.0E-01 - 9.9E-01 1.90E+00 NA ---** **Fluorene 1/13 2.0E-01 - 2.0E-01 1.90E+01 NA --- Indeno(1,2,3-cd)pyrene 1/13 3.1E-01 - 3.1E-01 4.31E+00 NA** **--- Phenanthrene 3/13 2.7E-01 - 5.1E-01 3.60E+00 NA ---** **Pyrene 2/13 1.9E-01 - 9.3E-01 3.00E-01 NA ---**(μg/L)SW-1ConcentrationsRange of DetectedC:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXFresh water(FW2)Ratio ofFrequencyCriteriaaSW-1 Sept-09 DetectedofChronic Sep-09 Concentration toChemical Detection(μg/L) (μg/L)ScreeningCriteria(μg/L)SW-1ConcentrationsRange of DetectedPesticides**4,4'-DDD 2/10 2.1E-02 - 4.7E-02 NBA NA --- 4,4'-DDE 1/10 2.2E-02 - 2.2E-02 4.51E-09 NA ---** Inorganics**Aluminum 18/27 2.4E+01 - 1.7E+04 NBA 4.26E+02 --- Antimony 1/27 2.3E+02 - 2.3E+02 8.00E+01 ND ---** **Arsenic 3/27 4.0E+00 - 3.6E+02 1.50E+02 ND --- Barium 18/27 3.4E+01 - 1.8E+03 2.20E+02 5.79E+01 J 2.63E-01** **Beryllium 1/27 5.3E+00 - 5.3E+00 3.60E+00 ND --- Calcium 27/27 7.2E+03 - 8.7E+04 NBA 1.09E+04 ---** **Chromium 11/27 7.0E-01 - 1.1E+02 3.48E+01 b** **9.00E-01 J 2.58E-02 Cobalt 7/27 6.0E-01 - 5.5E+01 2.40E+01 ND ---** **Copper 7/27 3.0E+00 - 1.9E+02 4.07E+00 b** **ND --- Iron** **27/27 1.8E+02 - 4.0E+06 NBA 8.60E+02 --- Lead 8/27 2.2E+00 - 2.4E+02 9.10E-01** **b ND ---** **Magnesium 24/27 2.4E+03 - 2.5E+04 NBA 3.05E+03 J --- Manganese 27/27 2.2E+01 - 2.7E+03 NBA 3.85E+01 ---** **Mercury 6/19 5.6E-02 - 4.8E-01 7.70E-01 2.30E-01 2.99E-01 Nickel 11/27 1.1E+00 - 4.4E+01 2.38E+01** **b ND ---** **Potassium 19/27 1.3E+03 - 1.0E+04 NBA 1.39E+03 J --- Selenium 1/27 1.6E+02 - 1.6E+02 5.00E+00 ND ---** **Sodium 25/27 6.3E+03 - 3.7E+04 NBA 1.25E+04 --- Thallium 3/27 1.6E+00 - 1.9E+00 1.00E+01 ND ---** **Tin 1/27 3.3E+01 - 3.3E+01 1.80E+02 ND ---** **Vanadium 1/27 1.9E+02 - 1.9E+02 1.20E+01 ND --- Zinc 19/27 3.2E+00 - 8.4E+02 5.41E+01** **b 1.95E+01 J 3.60E-01** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-2 May-08 DetectedCriteriaaSW-2 Oct-08 DetectedChronic May-08 Concentration to Chronic Oct-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **ND --- NB A** **N A** **--- NBA ND --- NBA NA ---** **NBA ND --- NBA NA --- NBA 1.00E-01 J --- NBA NA ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 ND --- 3.00E-01 NA ---** **2.30E+01 ND --- 2.30E+01 NA --- 1.80E+02 ND --- 1.80E+02 NA ---** **3.50E-02 ND --- 3.50E-02 NA --- 2.50E-02 ND --- 2.50E-02 NA ---** **1.40E-02 ND --- 1.40E-02 NA --- 9.07E+00 ND --- 9.07E+00 NA ---** **NBA ND --- NBA NA --- 7.64E+00 ND --- 7.64E+00 NA ---** **NBA ND --- NBA NA --- 1.90E+00 ND --- 1.90E+00 NA ---** **1.90E+01 ND --- 1.90E+01 NA --- 4.31E+00 ND --- 4.31E+00 NA ---** **3.60E+00 2.70E-01 B 7.50E-02 3.60E+00 NA --- 3.00E-01 ND --- 3.00E-01 NA ---** SW-2SW-2C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-2 May-08 DetectedCriteriaaSW-2 Oct-08 DetectedChronic May-08 Concentration to Chronic Oct-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-2SW-2**NBA ND --- NBA NA --- 4.51E-09 ND --- 4.51E-09 NA ---** **NBA ND --- NBA 4.53E+01 J --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 4.91E+01 J 2.23E-01 2.20E+02 6.45E+01 J 2.93E-01** **3.60E+00 ND --- 3.60E+00 ND --- NBA 1.35E+04 --- NBA 1.87E+04 ---** **4.22E+01 b** **ND --- 5.49E+01 b** **1.20E+00 J 2.19E-02 2.40E+01 ND --- 2.40E+01 6.00E-01 J 2.50E-02** **4.98E+00 b** **ND --- 6.55E+00 b** **ND --- NBA 1.76E+02 --- NBA 2.43E+02 ---** **1.18E+00 b** **ND --- 1.69E+00 b** **ND --- NBA 4.03E+03 --- NBA 5.50E+03 ---** **NBA 2.97E+01 --- NBA 4.42E+01 --- 7.70E-01 ND --- 7.70E-01 5.60E-02 J 7.27E-02** **2.91E+01 b** **ND --- 3.82E+01 b** **2.40E+00 J 6.29E-02 NBA ND --- NBA ND ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 1.09E+04 N --- NBA 1.49E+04 ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 6.60E+01** **b 1.65E+01 J 2.50E-01 8.66E+01** **b ND ---** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-2 May-09 DetectedCriteriaaSW-2 Sept-09 DetectedChronic May-09 Concentration to Chronic Sep-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **N A** **--- NB A** **N A** **--- NBA NA --- NBA NA ---** **NBA NA --- NBA NA --- NBA NA --- NBA NA ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 NA --- 3.00E-01 NA ---** **2.30E+01 NA --- 2.30E+01 NA --- 1.80E+02 NA --- 1.80E+02 NA ---** **3.50E-02 NA --- 3.50E-02 NA --- 2.50E-02 NA --- 2.50E-02 NA ---** **1.40E-02 NA --- 1.40E-02 NA --- 9.07E+00 NA --- 9.07E+00 NA ---** **NBA NA --- NBA NA --- 7.64E+00 NA --- 7.64E+00 NA ---** **NBA NA --- NBA NA --- 1.90E+00 NA --- 1.90E+00 NA ---** **1.90E+01 NA --- 1.90E+01 NA --- 4.31E+00 NA --- 4.31E+00 NA ---** **3.60E+00 NA --- 3.60E+00 NA --- 3.00E-01 NA --- 3.00E-01 NA ---** SW-2SW-2C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-2 May-09 DetectedCriteriaaSW-2 Sept-09 DetectedChronic May-09 Concentration to Chronic Sep-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-2SW-2**NBA NA --- NBA NA --- 4.51E-09 NA --- 4.51E-09 NA ---** **NBA 5.54E+01 J --- NBA 5.59E+02 --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 6.33E+01 J 2.88E-01 2.20E+02 5.66E+01 J 2.57E-01** **3.60E+00 ND --- 3.60E+00 ND --- NBA 1.38E+04 --- NBA 1.05E+04 ---** **4.44E+01 b** **ND --- 3.33E+01 b** **1.50E+00 J 4.50E-02 2.40E+01 7.00E-01 J 2.92E-02 2.40E+01 ND ---** **5.25E+00 b** **ND --- 3.89E+00 b** **2.20E+01 5.66E+00 NBA 2.51E+02 --- NBA 9.61E+02 ---** **1.27E+00 b** **ND --- 8.57E-01 b** **5.40E+00 6.30E+00 NBA 4.64E+03 J --- NBA 2.78E+03 J ---** **NBA 3.53E+01 --- NBA 3.62E+01 --- 7.70E-01 1.40E-01 J 1.82E-01 7.70E-01 3.00E-01 3.90E-01** **3.07E+01 b** **1.50E+00 J 4.89E-02 2.28E+01 b** **ND --- NBA 2.03E+03 J --- NBA 1.29E+03 J ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 1.46E+04 --- NBA 9.85E+03 J ---** **1.00E+01 1.60E+00 J 1.60E-01 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 6.96E+01** **b 1.86E+01 J 2.67E-01 5.17E+01** **b 2.48E+02 4.80E+00** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-3 May-08 DetectedCriteriaaSW-3 Oct-08 DetectedChronic May-08 Concentration to Chronic Oct-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **ND --- NB A** **N A** **--- NBA ND --- NBA NA ---** **NBA ND --- NBA NA --- NBA ND --- NBA NA ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 ND --- 3.00E-01 NA ---** **2.30E+01 ND --- 2.30E+01 NA --- 1.80E+02 ND --- 1.80E+02 NA ---** **3.50E-02 ND --- 3.50E-02 NA --- 2.50E-02 ND --- 2.50E-02 NA ---** **1.40E-02 ND --- 1.40E-02 NA --- 9.07E+00 ND --- 9.07E+00 NA ---** **NBA 2.30E-01 --- NBA NA --- 7.64E+00 ND --- 7.64E+00 NA ---** **NBA ND --- NBA NA --- 1.90E+00 ND --- 1.90E+00 NA ---** **1.90E+01 ND --- 1.90E+01 NA --- 4.31E+00 ND --- 4.31E+00 NA ---** **3.60E+00 ND --- 3.60E+00 NA --- 3.00E-01 ND --- 3.00E-01 NA ---** SW-3SW-3C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-3 May-08 DetectedCriteriaaSW-3 Oct-08 DetectedChronic May-08 Concentration to Chronic Oct-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-3SW-3**NBA ND --- NBA NA --- 4.51E-09 ND --- 4.51E-09 NA ---** **NBA ND --- NBA 3.43E+01 J --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 ND --- 2.20E+02 4.33E+01 J 1.97E-01** **3.60E+00 ND --- 3.60E+00 ND --- NBA 1.14E+04 --- NBA 1.32E+04 ---** **3.44E+01 b** **ND --- 3.83E+01 b** **ND --- 2.40E+01 ND --- 2.40E+01 ND ---** **4.02E+00 b** **ND --- 4.50E+00 b** **ND --- NBA 2.01E+02 --- NBA 1.08E+03 ---** **8.96E-01 b** **ND --- 1.04E+00 b** **ND --- NBA 2.61E+03 --- NBA ND ---** **NBA 3.59E+01 --- NBA 2.16E+01 --- 7.70E-01 ND --- 7.70E-01 NA ---** **2.36E+01 b** **ND --- 2.63E+01 b** **ND --- NBA 3.33E+03 J --- NBA ND ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 1.73E+04 N --- NBA 2.21E+04 ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 5.34E+01** **b ND --- 5.97E+01** **b ND ---** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)SW-3Ratio of SW-3CriteriaaSW-3 May-09 DetectedCriteriaaRelocation Sept-09 DetectedChronic May-09 Concentration to Chronic Sep-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **N A** **--- NB A** **N A** **--- NBA NA --- NBA NA ---** **NBA NA --- NBA NA --- NBA NA --- NBA NA ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 NA --- 3.00E-01 NA ---** **2.30E+01 NA --- 2.30E+01 NA --- 1.80E+02 NA --- 1.80E+02 NA ---** **3.50E-02 NA --- 3.50E-02 NA --- 2.50E-02 NA --- 2.50E-02 NA ---** **1.40E-02 NA --- 1.40E-02 NA --- 9.07E+00 NA --- 9.07E+00 NA ---** **NBA NA --- NBA NA --- 7.64E+00 NA --- 7.64E+00 NA ---** **NBA NA --- NBA NA --- 1.90E+00 NA --- 1.90E+00 NA ---** **1.90E+01 NA --- 1.90E+01 NA --- 4.31E+00 NA --- 4.31E+00 NA ---** **3.60E+00 NA --- 3.60E+00 NA --- 3.00E-01 NA --- 3.00E-01 NA ---** RelocationSW-3C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)SW-3Ratio of SW-3CriteriaaSW-3 May-09 DetectedCriteriaaRelocation Sept-09 DetectedChronic May-09 Concentration to Chronic Sep-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaRelocationSW-3**NBA NA --- NBA NA --- 4.51E-09 NA --- 4.51E-09 NA ---** **NBA 3.52E+02 --- NBA ND --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 4.98E+01 J 2.26E-01 2.20E+02 ND ---** **3.60E+00 ND --- 3.60E+00 ND --- NBA 1.34E+04 --- NBA 1.45E+04 ---** **3.91E+01 b** **1.10E+00 J 2.81E-02 4.01E+01 b** **ND --- 2.40E+01 1.20E+00 J 5.00E-02 2.40E+01 ND ---** **4.60E+00 b** **ND --- 4.72E+00 b** **ND --- NBA 5.95E+03 --- NBA 1.29E+03 ---** **1.07E+00 b** **ND --- 1.10E+00 b** **ND --- NBA 3.00E+03 J --- NBA ND ---** **NBA 7.08E+01 --- NBA 2.91E+01 --- 7.70E-01 NA --- 7.70E-01 NA ---** **2.69E+01 b** **2.10E+00 J 7.82E-02 2.76E+01 b** **ND --- NBA 5.81E+03 J --- NBA 6.42E+03 J ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 1.93E+04 --- NBA 2.05E+04 ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 6.10E+01** **b 1.31E+01 J 2.15E-01 6.26E+01** **b 4.60E+00 J 7.34E-02** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)SW-3Ratio of SW-3 DUPFresh water(FW2)Ratio ofCriteriaaRelocation Sept-09 DetectedCriteriaaSW-4 May-08 DetectedChronic Sep-09 Concentration to Chronic May-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **N A** **--- NB A** **ND --- NBA NA --- NBA ND ---** **NBA NA --- NBA ND --- NBA NA --- NBA ND ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 NA --- 3.00E-01 ND ---** **2.30E+01 NA --- 2.30E+01 1.70E+00 J 7.39E-02 1.80E+02 NA --- 1.80E+02 ND ---** **3.50E-02 NA --- 3.50E-02 1.80E-01 J 5.14E+00 2.50E-02 NA --- 2.50E-02 ND ---** **1.40E-02 NA --- 1.40E-02 ND --- 9.07E+00 NA --- 9.07E+00 ND ---** **NBA NA --- NBA ND --- 7.64E+00 NA --- 7.64E+00 ND ---** **NBA NA --- NBA ND --- 1.90E+00 NA --- 1.90E+00 3.00E-01 1.58E-01** **1.90E+01 NA --- 1.90E+01 2.00E-01 1.05E-02 4.31E+00 NA --- 4.31E+00 ND ---** **3.60E+00 NA --- 3.60E+00 4.50E-01 B 1.25E-01 3.00E-01 NA --- 3.00E-01 1.90E-01 J 6.33E-01** Relocation DUPSW-4C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)SW-3Ratio of SW-3 DUPFresh water(FW2)Ratio ofCriteriaaRelocation Sept-09 DetectedCriteriaaSW-4 May-08 DetectedChronic Sep-09 Concentration to Chronic May-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaRelocation DUPSW-4**NBA NA --- NBA ND --- 4.51E-09 NA --- 4.51E-09 ND ---** **NBA ND --- NBA ND --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 ND --- 2.20E+02 4.10E+01 J 1.86E-01** **3.60E+00 ND --- 3.60E+00 ND --- NBA 1.43E+04 --- NBA 1.36E+04 ---** **3.97E+01 b** **ND --- 3.79E+01 b** **ND --- 2.40E+01 ND --- 2.40E+01 ND ---** **4.67E+00 b** **ND --- 4.45E+00 b** **ND --- NBA 1.26E+03 --- NBA 7.91E+02 ---** **1.09E+00 b** **ND --- 1.02E+00 b** **ND --- NBA ND --- NBA 2.46E+03 ---** **NBA 2.83E+01 --- NBA 6.25E+01 --- 7.70E-01 NA --- 7.70E-01 7.40E-02 J 9.61E-02** **2.73E+01 b** **ND --- 2.60E+01 b** **ND --- NBA 6.45E+03 J --- NBA 7.18E+03 N ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 2.04E+04 --- NBA 2.05E+04 N ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 6.20E+01** **b 6.10E+00 J 9.84E-02 5.90E+01** **b ND ---** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-4 Oct-08 DetectedCriteriaaSW-4-DUP Oct-08 DetectedChronic Oct-08 Concentration to Chronic Oct-08 Concentrationto(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **N A** **--- NB A** **N A** **--- NBA NA --- NBA NA ---** **NBA NA --- NBA NA --- NBA NA --- NBA NA ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA ND --- NBA ND --- 3.00E-01 ND --- 3.00E-01 ND ---** **2.30E+01 ND --- 2.30E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **3.50E-02 ND --- 3.50E-02 ND --- 2.50E-02 ND --- 2.50E-02 ND ---** **1.40E-02 ND --- 1.40E-02 ND --- 9.07E+00 ND --- 9.07E+00 ND ---** **NBA ND --- NBA ND --- 7.64E+00 ND --- 7.64E+00 ND ---** **NBA ND --- NBA ND --- 1.90E+00 ND --- 1.90E+00 ND ---** **1.90E+01 ND --- 1.90E+01 ND --- 4.31E+00 ND --- 4.31E+00 ND ---** **3.60E+00 ND --- 3.60E+00 ND --- 3.00E-01 ND --- 3.00E-01 ND ---** SW-4SW-4-DUPC:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-4 Oct-08 DetectedCriteriaaSW-4-DUP Oct-08 DetectedChronic Oct-08 Concentration to Chronic Oct-08 Concentrationto(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-4SW-4-DUP**NBA NA --- NBA NA --- 4.51E-09 NA --- 4.51E-09 NA ---** **NBA 2.43E+01 J --- NBA 3.06E+01 J --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 ND --- 2.20E+02 4.58E+01 J 2.08E-01** **3.60E+00 ND --- 3.60E+00 ND --- NBA 1.44E+04 --- NBA 1.43E+04 ---** **3.99E+01 b** **ND --- 3.97E+01 b** **ND --- 2.40E+01 ND --- 2.40E+01 ND ---** **4.70E+00 b** **ND --- 4.67E+00 b** **ND --- NBA 2.03E+03 --- NBA 1.84E+03 ---** **1.10E+00 b** **ND --- 1.09E+00 b** **ND --- NBA ND --- NBA 2.66E+03 J ---** **NBA 5.64E+01 --- NBA 5.81E+01 --- 7.70E-01 ND --- 7.70E-01 ND ---** **2.75E+01 b** **ND --- 2.73E+01 b** **ND --- NBA ND --- NBA ND ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 2.35E+04 --- NBA 2.35E+04 ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 6.23E+01** **b ND --- 6.19E+01** **b ND ---** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-4 May-09 DetectedCriteriaaSW-4-DUP May-09 DetectedChronic May-09 Concentration to Chronic May-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **N A** **--- NB A** **N A** **--- NBA NA --- NBA NA ---** **NBA NA --- NBA NA --- NBA NA --- NBA NA ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA ND --- NBA ND --- 3.00E-01 ND --- 3.00E-01 1.20E+00 J 4.00E+00** **2.30E+01 ND --- 2.30E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **3.50E-02 ND --- 3.50E-02 ND --- 2.50E-02 ND --- 2.50E-02 ND ---** **1.40E-02 ND --- 1.40E-02 ND --- 9.07E+00 ND --- 9.07E+00 ND ---** **NBA ND --- NBA ND --- 7.64E+00 ND --- 7.64E+00 ND ---** **NBA ND --- NBA ND --- 1.90E+00 ND --- 1.90E+00 ND ---** **1.90E+01 ND --- 1.90E+01 ND --- 4.31E+00 ND --- 4.31E+00 ND ---** **3.60E+00 ND --- 3.60E+00 ND --- 3.00E-01 ND --- 3.00E-01 ND ---** SW-4SW-4-DUPC:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-4 May-09 DetectedCriteriaaSW-4-DUP May-09 DetectedChronic May-09 Concentration to Chronic May-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-4SW-4-DUP**NBA NA --- NBA NA --- 4.51E-09 NA --- 4.51E-09 NA ---** **NBA 9.81E+02 --- NBA 4.91E+02 --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 3.47E+01 J 1.58E-01 2.20E+02 3.43E+01 J 1.56E-01** **3.60E+00 ND --- 3.60E+00 ND --- NBA 1.64E+04 --- NBA 1.60E+04 ---** **4.54E+01 b** **2.40E+00 J 5.29E-02 4.42E+01 b** **1.30E+00 J 2.94E-02 2.40E+01 3.40E+00 J 1.42E-01 2.40E+01 2.60E+00 J 1.08E-01** **5.37E+00 b** **3.00E+00 J 5.59E-01 5.22E+00 b** **2.47E+01 4.73E+00 NBA 2.98E+04 --- NBA 2.84E+04 ---** **1.30E+00 b** **5.30E+00 4.06E+00 1.26E+00 b** **2.20E+00 J 1.75E+00 NBA 3.40E+03 J --- NBA 3.22E+03 J ---** **NBA 1.67E+02 --- NBA 1.73E+02 --- 7.70E-01 ND --- 7.70E-01 ND ---** **3.13E+01 b** **2.20E+00 J 7.02E-02 3.05E+01 b** **1.90E+00 J 6.23E-02 NBA 4.13E+03 J --- NBA 4.50E+03 J ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA ND --- NBA ND ---** **1.00E+01 1.90E+00 J 1.90E-01 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 7.11E+01** **b 2.27E+01 3.19E-01 6.92E+01** **b 3.63E+01 5.24E-01** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-4 Sept-09 DetectedCriteriaaSW-5 May-08 DetectedChronic Sep-09 Concentration to Chronic May-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **N A** **--- NB A** **ND --- NBA NA --- NBA ND ---** **NBA NA --- NBA ND --- NBA NA --- NBA ND ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 ND --- 3.00E-01 ND ---** **2.30E+01 ND --- 2.30E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **3.50E-02 ND --- 3.50E-02 ND --- 2.50E-02 ND --- 2.50E-02 ND ---** **1.40E-02 ND --- 1.40E-02 ND --- 9.07E+00 ND --- 9.07E+00 ND ---** **NBA ND --- NBA ND --- 7.64E+00 ND --- 7.64E+00 ND ---** **NBA ND --- NBA ND --- 1.90E+00 ND --- 1.90E+00 ND ---** **1.90E+01 ND --- 1.90E+01 ND --- 4.31E+00 ND --- 4.31E+00 ND ---** **3.60E+00 ND --- 3.60E+00 ND --- 3.00E-01 ND --- 3.00E-01 ND ---** SW-4SW-5C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-4 Sept-09 DetectedCriteriaaSW-5 May-08 DetectedChronic Sep-09 Concentration to Chronic May-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-4SW-5**NBA NA --- NBA ND --- 4.51E-09 NA --- 4.51E-09 ND ---** **NBA 8.25E+02 --- NBA 1.05E+02 J --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 ND --- 2.20E+02 ND ---** **3.60E+00 ND --- 3.60E+00 ND --- NBA 1.60E+04 --- NBA 1.66E+04 ---** **4.25E+01 b** **ND --- 4.29E+01 b** **ND --- 2.40E+01 ND --- 2.40E+01 ND ---** **5.01E+00 b** **ND --- 5.06E+00 b** **ND --- NBA 1.12E+04 --- NBA 2.12E+03 J ---** **1.19E+00 b** **5.00E+00 4.19E+00 1.21E+00 b** **ND --- NBA ND --- NBA 2.39E+03 ---** **NBA 1.00E+02 --- NBA 4.87E+01 --- 7.70E-01 ND --- 7.70E-01 ND ---** **2.93E+01 b** **ND --- 2.96E+01 b** **ND --- NBA 5.88E+03 J --- NBA 4.13E+03 J ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 1.66E+04 --- NBA 1.93E+04 N ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 6.64E+01** **b 1.84E+01 J 2.77E-01 6.71E+01** **b 7.00E+00 J 1.04E-01** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-5 Oct-08 DetectedCriteriaaSW-5 May-09 DetectedChronic Oct-08 Concentration to Chronic May-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **ND --- NB A** **ND --- NBA NA --- NBA 5.80E+00 J ---** **NBA ND --- NBA ND --- NBA ND --- NBA ND ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA ND --- NBA 1.10E+00 J --- 3.00E-01 ND --- 3.00E-01 1.40E+00 J 4.67E+00** **2.30E+01 ND --- 2.30E+01 ND --- 1.80E+02 ND --- 1.80E+02 5.20E+00 2.89E-02** **3.50E-02 ND --- 3.50E-02 ND --- 2.50E-02 ND --- 2.50E-02 5.79E-01 2.32E+01** **1.40E-02 ND --- 1.40E-02 4.35E-01 3.11E+01 9.07E+00 ND --- 9.07E+00 7.69E-01 8.48E-02** **NBA ND --- NBA 3.86E-01 --- 7.64E+00 ND --- 7.64E+00 2.81E-01 3.68E-02** **NBA ND --- NBA 5.86E-01 --- 1.90E+00 ND --- 1.90E+00 9.93E-01 5.23E-01** **1.90E+01 ND --- 1.90E+01 ND --- 4.31E+00 ND --- 4.31E+00 3.07E-01 7.12E-02** **3.60E+00 ND --- 3.60E+00 5.10E-01 1.42E-01 3.00E-01 ND --- 3.00E-01 9.30E-01 3.10E+00** SW-5SW-5C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-5 Oct-08 DetectedCriteriaaSW-5 May-09 DetectedChronic Oct-08 Concentration to Chronic May-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-5SW-5**NBA NA --- NBA NA --- 4.51E-09 NA --- 4.51E-09 NA ---** **NBA 6.68E+01 J --- NBA 1.83E+02 J --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 4.82E+01 J 2.19E-01 2.20E+02 5.55E+01 J 2.52E-01** **3.60E+00 ND --- 3.60E+00 ND --- NBA 4.03E+04 --- NBA 2.90E+04 ---** **8.33E+01 b** **7.00E-01 J 8.41E-03 6.55E+01 b** **1.10E+00 J 1.68E-02 2.40E+01 ND --- 2.40E+01 8.00E-01 J 3.33E-02** **1.01E+01 b** **ND --- 7.87E+00 b** **ND --- NBA 9.39E+03 --- NBA 2.64E+04 ---** **2.94E+00 b** **ND --- 2.13E+00 b** **ND --- NBA 3.56E+03 J --- NBA 3.30E+03 J ---** **NBA 2.32E+02 --- NBA 2.05E+02 --- 7.70E-01 NA --- 7.70E-01 NA ---** **5.87E+01 b** **ND --- 4.58E+01 b** **1.60E+00 J 3.50E-02 NBA ND --- NBA 5.68E+03 J ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 1.87E+04 --- NBA 2.00E+04 ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 1.33E+02** **b ND --- 1.04E+02** **b 9.50E+00 J 9.14E-02** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-5 Sept-09 DetectedCriteriaaSW-6 May-08 DetectedChronic Sep-09 Concentration to Chronic May-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **ND --- NB A** **ND --- NBA NA --- NBA ND ---** **NBA ND --- NBA ND --- NBA ND --- NBA ND ---** **NBA ND --- NBA NA --- 9.70E+02 ND --- 9.70E+02 NA ---** **NBA ND --- NBA NA --- 2.53E+02 ND --- 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 ND --- 3.00E-01 ND ---** **2.30E+01 ND --- 2.30E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **3.50E-02 ND --- 3.50E-02 ND --- 2.50E-02 ND --- 2.50E-02 ND ---** **1.40E-02 ND --- 1.40E-02 ND --- 9.07E+00 ND --- 9.07E+00 ND ---** **NBA ND --- NBA ND --- 7.64E+00 ND --- 7.64E+00 ND ---** **NBA ND --- NBA ND --- 1.90E+00 ND --- 1.90E+00 ND ---** **1.90E+01 ND --- 1.90E+01 ND --- 4.31E+00 ND --- 4.31E+00 ND ---** **3.60E+00 ND --- 3.60E+00 ND --- 3.00E-01 ND --- 3.00E-01 ND ---** SW-5SW-6C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-5 Sept-09 DetectedCriteriaaSW-6 May-08 DetectedChronic Sep-09 Concentration to Chronic May-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-5SW-6**NBA NA --- NBA ND --- 4.51E-09 NA --- 4.51E-09 ND ---** **NBA 2.17E+02 --- NBA ND --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 ND --- 2.20E+02 ND ---** **3.60E+00 ND --- 3.60E+00 ND --- NBA 2.63E+04 --- NBA 2.41E+04 ---** **5.98E+01 b** **ND --- 5.80E+01 b** **ND --- 2.40E+01 ND --- 2.40E+01 ND ---** **7.16E+00 b** **ND --- 6.94E+00 b** **ND --- NBA 1.23E+04 --- NBA 4.83E+03 ---** **1.89E+00 b** **6.10E+00 3.23E+00 1.81E+00 b** **ND --- NBA 2.75E+03 J --- NBA 3.39E+03 ---** **NBA 1.45E+02 --- NBA 9.27E+01 --- 7.70E-01 NA --- 7.70E-01 ND ---** **4.17E+01 b** **ND --- 4.04E+01 b** **ND --- NBA 5.58E+03 J --- NBA ND ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 1.85E+04 --- NBA 2.00E+04 N ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 9.47E+01** **b 1.28E+01 J 1.35E-01 9.17E+01** **b ND ---** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-6 Oct-08 DetectedCriteriaaSW-6 May-09 DetectedChronic Oct-08 Concentration to Chronic May-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **ND --- NB A** **ND --- NBA NA --- NBA 5.80E+00 J ---** **NBA 1.70E+00 J --- NBA 1.30E+00 J --- NBA ND --- NBA ND ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 NA --- 3.00E-01 NA ---** **2.30E+01 NA --- 2.30E+01 NA --- 1.80E+02 NA --- 1.80E+02 NA ---** **3.50E-02 NA --- 3.50E-02 NA --- 2.50E-02 NA --- 2.50E-02 NA ---** **1.40E-02 NA --- 1.40E-02 NA --- 9.07E+00 NA --- 9.07E+00 NA ---** **NBA NA --- NBA NA --- 7.64E+00 NA --- 7.64E+00 NA ---** **NBA NA --- NBA NA --- 1.90E+00 NA --- 1.90E+00 NA ---** **1.90E+01 NA --- 1.90E+01 NA --- 4.31E+00 NA --- 4.31E+00 NA ---** **3.60E+00 NA --- 3.60E+00 NA --- 3.00E-01 NA --- 3.00E-01 NA ---** SW-6SW-6C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-6 Oct-08 DetectedCriteriaaSW-6 May-09 DetectedChronic Oct-08 Concentration to Chronic May-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-6SW-6**NBA NA --- NBA NA --- 4.51E-09 NA --- 4.51E-09 NA ---** **NBA 1.68E+04 --- NBA 1.59E+02 J --- 8.00E+01 2.32E+02 2.90E+00 8.00E+01 ND ---** **1.50E+02 3.63E+02 2.42E+00 1.50E+02 4.00E+00 2.67E-02 2.20E+02 1.75E+03 7.95E+00 2.20E+02 1.41E+02 J 6.41E-01** **3.60E+00 5.30E+00 1.47E+00 3.60E+00 ND --- NBA 8.66E+04 --- NBA 2.52E+04 ---** **1.48E+02 b** **1.08E+02 7.30E-01 5.85E+01 b** **1.20E+00 J 2.05E-02 2.40E+01 5.52E+01 J 2.30E+00 2.40E+01 ND ---** **1.84E+01 b** **1.88E+02 1.02E+01 7.00E+00 b** **3.94E+01 5.63E+00 NBA 3.97E+06 --- NBA 1.74E+05 ---** **6.23E+00 b** **2.40E+02 3.85E+01 1.84E+00 b** **ND --- NBA 4.01E+03 J --- NBA 2.92E+03 J ---** **NBA 2.69E+03 --- NBA 1.34E+02 --- 7.70E-01 NA --- 7.70E-01 NA ---** **1.06E+02 b** **4.42E+01 J 4.16E-01 4.07E+01 b** **2.70E+00 J 6.63E-02 NBA ND --- NBA 3.66E+03 J ---** **5.00E+00 1.63E+02 3.26E+01 5.00E+00 ND --- NBA ND --- NBA 1.98E+04 ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 3.26E+01 J 1.81E-01 1.80E+02 ND ---** **1.20E+01 1.88E+02 1.57E+01 1.20E+01 ND --- 2.42E+02** **b 8.44E+02 3.49E+00 9.25E+01** **b 2.83E+01 3.06E-01** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-6 Sept-09 DetectedCriteriaaSW-7 Sept-09 DetectedChronic Sep-09 Concentration to Chronic Sep-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **ND --- NB A** **N A** **--- NBA NA --- NBA NA ---** **NBA ND --- NBA NA --- NBA ND --- NBA NA ---** **NBA ND --- NBA NA --- 9.70E+02 ND --- 9.70E+02 NA ---** **NBA ND --- NBA NA --- 2.53E+02 1.00E+00 3.95E-03 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 NA --- 3.00E-01 ND ---** **2.30E+01 NA --- 2.30E+01 ND --- 1.80E+02 NA --- 1.80E+02 ND ---** **3.50E-02 NA --- 3.50E-02 ND --- 2.50E-02 NA --- 2.50E-02 ND ---** **1.40E-02 NA --- 1.40E-02 ND --- 9.07E+00 NA --- 9.07E+00 ND ---** **NBA NA --- NBA ND --- 7.64E+00 NA --- 7.64E+00 ND ---** **NBA NA --- NBA ND --- 1.90E+00 NA --- 1.90E+00 ND ---** **1.90E+01 NA --- 1.90E+01 ND --- 4.31E+00 NA --- 4.31E+00 ND ---** **3.60E+00 NA --- 3.60E+00 ND --- 3.00E-01 NA --- 3.00E-01 ND ---** SW-6SW-7C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-6 Sept-09 DetectedCriteriaaSW-7 Sept-09 DetectedChronic Sep-09 Concentration to Chronic Sep-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-6SW-7**NBA NA --- NBA ND --- 4.51E-09 NA --- 4.51E-09 ND ---** **NBA 1.18E+03 --- NBA ND --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 ND --- 2.20E+02 ND ---** **3.60E+00 ND --- 3.60E+00 ND --- NBA 4.76E+04 --- NBA 2.94E+04 ---** **9.66E+01 b** **ND --- 6.40E+01 b** **ND --- 2.40E+01 ND --- 2.40E+01 ND ---** **1.18E+01 b** **2.98E+01 2.52E+00 7.68E+00 b** **ND --- NBA 1.13E+04 --- NBA 1.87E+03 ---** **3.57E+00 b** **3.20E+01 8.95E+00 2.07E+00 b** **2.20E+00 J 1.06E+00 NBA 4.71E+03 J --- NBA 2.47E+03 J ---** **NBA 1.58E+02 --- NBA 4.74E+01 --- 7.70E-01 NA --- 7.70E-01 ND ---** **6.84E+01 b** **ND --- 4.47E+01 b** **1.10E+00 J 2.46E-02 NBA 5.68E+03 J --- NBA 8.68E+03 J ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 1.98E+04 --- NBA 2.35E+04 ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 1.55E+02** **b 1.14E+02 7.33E-01 1.01E+02** **b 1.99E+01 J 1.96E-01** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-8 May-08 DetectedCriteriaaSW-8 Oct-08 DetectedChronic May-08 Concentration to Chronic Oct-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **ND --- NB A** **ND --- NBA ND --- NBA NA ---** **NBA ND --- NBA ND --- NBA ND --- NBA ND ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 NA --- 3.00E-01 NA ---** **2.30E+01 NA --- 2.30E+01 NA --- 1.80E+02 NA --- 1.80E+02 NA ---** **3.50E-02 NA --- 3.50E-02 NA --- 2.50E-02 NA --- 2.50E-02 NA ---** **1.40E-02 NA --- 1.40E-02 NA --- 9.07E+00 NA --- 9.07E+00 NA ---** **NBA NA --- NBA NA --- 7.64E+00 NA --- 7.64E+00 NA ---** **NBA NA --- NBA NA --- 1.90E+00 NA --- 1.90E+00 NA ---** **1.90E+01 NA --- 1.90E+01 NA --- 4.31E+00 NA --- 4.31E+00 NA ---** **3.60E+00 NA --- 3.60E+00 NA --- 3.00E-01 NA --- 3.00E-01 NA ---** SW-8SW-8C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-8 May-08 DetectedCriteriaaSW-8 Oct-08 DetectedChronic May-08 Concentration to Chronic Oct-08 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-8SW-8**NBA ND --- NBA 2.10E-02 J --- 4.51E-09 ND --- 4.51E-09 ND ---** **NBA ND --- NBA 7.38E+01 J --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 7.82E+01 3.55E-01 2.20E+02 6.48E+01 J 2.95E-01** **3.60E+00 ND --- 3.60E+00 ND --- NBA 7.16E+03 --- NBA 1.14E+04 ---** **6.64E+01 b** **ND --- 9.32E+01 b** **1.50E+00 J 1.61E-02 2.40E+01 ND --- 2.40E+01 ND ---** **7.99E+00 b** **ND --- 1.14E+01 b** **9.80E+00 J 8.62E-01 NBA 7.05E+03 --- NBA 1.66E+04 ---** **2.17E+00 b** **ND --- 3.41E+00 b** **ND --- NBA 1.69E+04 --- NBA 2.52E+04 ---** **NBA 2.90E+02 --- NBA 4.78E+02 --- 7.70E-01 ND --- 7.70E-01 ND ---** **4.64E+01 b** **ND --- 6.59E+01 b** **5.70E+00 J 8.65E-02 NBA 1.01E+04 N --- NBA ND ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 3.00E+04 N --- NBA 3.74E+04 ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 1.05E+02** **b 1.10E+01 J 1.04E-01 1.50E+02** **b ND ---** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-8 May-09 DetectedCriteriaaSW-8 Sept-09 DetectedChronic May-09 Concentration to Chronic Sep-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **4.40E-01 J --- NB A** **ND --- NBA ND --- NBA NA ---** **NBA ND --- NBA ND --- NBA ND --- NBA ND ---** **NBA NA --- NBA 3.10E-01 J --- 9.70E+02 NA --- 9.70E+02 3.10E-01 J 3.20E-04** **NBA NA --- NBA 6.20E-01 J --- 2.53E+02 NA --- 2.53E+02 ND ---** **NBA NA --- NBA NA --- 3.00E-01 NA --- 3.00E-01 NA ---** **2.30E+01 NA --- 2.30E+01 NA --- 1.80E+02 NA --- 1.80E+02 NA ---** **3.50E-02 NA --- 3.50E-02 NA --- 2.50E-02 NA --- 2.50E-02 NA ---** **1.40E-02 NA --- 1.40E-02 NA --- 9.07E+00 NA --- 9.07E+00 NA ---** **NBA NA --- NBA NA --- 7.64E+00 NA --- 7.64E+00 NA ---** **NBA NA --- NBA NA --- 1.90E+00 NA --- 1.90E+00 NA ---** **1.90E+01 NA --- 1.90E+01 NA --- 4.31E+00 NA --- 4.31E+00 NA ---** **3.60E+00 NA --- 3.60E+00 NA --- 3.00E-01 NA --- 3.00E-01 NA ---** SW-8SW-8C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-8 May-09 DetectedCriteriaaSW-8 Sept-09 DetectedChronic May-09 Concentration to Chronic Sep-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-8SW-8**NBA 4.70E-02 J --- NBA ND --- 4.51E-09 2.20E-02 4.88E+06 4.51E-09 ND ---** **NBA 1.58E+03 --- NBA ND --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 5.30E+00 3.53E-02 1.50E+02 ND --- 2.20E+02 3.26E+02 1.48E+00 2.20E+02 ND ---** **3.60E+00 ND --- 3.60E+00 ND --- NBA 1.12E+04 --- NBA 1.24E+04 ---** **8.11E+01 b** **5.60E+00 J 6.91E-02 6.84E+01 b** **ND --- 2.40E+01 2.00E+00 J 8.33E-02 2.40E+01 ND ---** **9.83E+00 b** **4.02E+01 4.09E+00 8.24E+00 b** **ND --- NBA 1.09E+05 --- NBA 6.99E+03 ---** **2.83E+00 b** **1.03E+01 3.63E+00 2.26E+00 b** **ND --- NBA 2.03E+04 --- NBA 1.45E+04 ---** **NBA 4.65E+02 --- NBA 3.16E+02 --- 7.70E-01 ND --- 7.70E-01 ND ---** **5.71E+01 b** **6.80E+00 J 1.19E-01 4.79E+01 b** **1.70E+00 J 3.55E-02 NBA 7.84E+03 J --- NBA 6.58E+03 J ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 2.85E+04 --- NBA 6.32E+03 J ---** **1.00E+01 1.80E+00 J 1.80E-01 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 1.30E+02** **b 4.81E+01 3.71E-01 1.09E+02** **b 3.20E+00 J 2.94E-02** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalVolatiles**1,1-Dichloroethane Acetone** **Carbon Disulfide Chloromethane** **cis-1,2-Dichloroethene trans-1,2-Dichloroethene** **1,2-Dichloroethene (total) Toluene** Semivolatiles**3-Methylphenol & 4-Methylphenol Bis(2-ethylhexyl)phthalate** **Butyl Benzyl Phthalate Phenol** Polycyclic Aromatic Hydrocarbons**Anthracene Benzo(a)anthracene** **Benzo(a)pyrene Benzo(b)fluoranthene** **Benzo(k)fluoranthene Benzo(g,h,i)perylene** **Chrysene Fluoranthene** **Fluorene Indeno(1,2,3-cd)pyrene** **Phenanthrene Pyrene** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-9 Sept-09 DetectedCriteriaaSW-10 Sept-09 DetectedChronic Sep-09 Concentration to Chronic Sep-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteria**NB A** **N A** **--- NB A** **N A** **--- NBA NA --- NBA NA ---** **NBA NA --- NBA NA --- NBA NA --- NBA NA ---** **NBA NA --- NBA NA --- 9.70E+02 NA --- 9.70E+02 NA ---** **NBA NA --- NBA NA --- 2.53E+02 NA --- 2.53E+02 NA ---** **NBA NA --- NBA NA --- 3.00E-01 NA --- 3.00E-01 ND ---** **2.30E+01 NA --- 2.30E+01 ND --- 1.80E+02 NA --- 1.80E+02 ND ---** **3.50E-02 NA --- 3.50E-02 ND --- 2.50E-02 NA --- 2.50E-02 ND ---** **1.40E-02 NA --- 1.40E-02 ND --- 9.07E+00 NA --- 9.07E+00 ND ---** **NBA NA --- NBA ND --- 7.64E+00 NA --- 7.64E+00 ND ---** **NBA NA --- NBA ND --- 1.90E+00 NA --- 1.90E+00 ND ---** **1.90E+01 NA --- 1.90E+01 ND --- 4.31E+00 NA --- 4.31E+00 ND ---** **3.60E+00 NA --- 3.60E+00 ND --- 3.00E-01 NA --- 3.00E-01 ND ---** SW-9SW-10C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCXChemicalPesticides**4,4'-DDD 4,4'-DDE** Inorganics**Aluminum Antimony** **Arsenic Barium** **Beryllium Calcium** **Chromium Cobalt** **Copper Iron** **Lead Magnesium** **Manganese Mercury** **Nickel Potassium** **Selenium Sodium** **Thallium Tin** **Vanadium Zinc** Fresh water(FW2)Ratio ofFresh water(FW2)Ratio ofCriteriaaSW-9 Sept-09 DetectedCriteriaaSW-10 Sept-09 DetectedChronic Sep-09 Concentration to Chronic Sep-09 Concentration to(μg/L) (μg/L)ScreeningCriteria(μg/L) (μg/L)ScreeningCriteriaSW-9SW-10**NBA NA --- NBA NA --- 4.51E-09 NA --- 4.51E-09 NA ---** **NBA ND --- NBA ND --- 8.00E+01 ND --- 8.00E+01 ND ---** **1.50E+02 ND --- 1.50E+02 ND --- 2.20E+02 3.54E+01 J 1.61E-01 2.20E+02 ND ---** **3.60E+00 ND --- 3.60E+00 ND --- NBA 5.01E+04 --- NBA 1.63E+04 ---** **1.09E+02 b** **ND --- 4.28E+01 b** **ND --- 2.40E+01 ND --- 2.40E+01 ND ---** **1.33E+01 b** **ND --- 5.05E+00 b** **ND --- NBA 5.68E+02 --- NBA 1.66E+03 ---** **4.17E+00 b** **ND --- 1.20E+00 b** **ND --- NBA 8.36E+03 --- NBA ND ---** **NBA 4.68E+01 --- NBA 2.90E+01 --- 7.70E-01 4.80E-01 6.23E-01 7.70E-01 ND ---** **7.72E+01 b** **ND --- 2.95E+01 b** **ND --- NBA 2.38E+03 J --- NBA 7.03E+03 J ---** **5.00E+00 ND --- 5.00E+00 ND --- NBA 1.33E+04 --- NBA 2.35E+04 ---** **1.00E+01 ND --- 1.00E+01 ND --- 1.80E+02 ND --- 1.80E+02 ND ---** **1.20E+01 ND --- 1.20E+01 ND --- 1.75E+02** **b 3.50E+00 J 1.99E-02 6.70E+01** **b 7.90E+00 J 1.18E-01** C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003,O[BC&$W8'L\NOMHFLI&LK&/CJCGJCQ&'LIGCIJMOJHLIF&HI&)EMKOGC&6OJCM&JL&)EMKOGC&6OJCM&)GMCCIHI]&'MHJCMHO!LMJ&/HD&#.%&%OIQKHBB&)HJC!LMJ&/HD5&#C^&2CMFCX**Note: Shading indicates the maximum detection exceeds the benchmark. NBA = No benchmark available.** **μg/L = Micrograms per liter. a** **NJDEP (New Jersey Department of Environmental Protection). Ecological Screening Criteria (ESC): 2009. b** **Criterion is a function of hardness (μg/L as CaCO3), in the water column. Values are based on a sample-specific hardness.**C:\Users\mbrewin\AppData\Local\Microsoft\Windows\TemporaryInternetFiles\Content.Outlook\UIIT6F6E\\March_2010_Tables_valued(3)11/18/2003