air & soil sampling program, february 23 and 24, 1983, fox

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SDMS Document

112715

AIR & SOIL SAMPLING PROGRAM FEBRUARY 23 & 24, 1983

FOX CHASE II AND BRIAR lAKE

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Prepared by Roy F. Vfeston/Sper Divison Edison, N.J. June 30, 1983

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Introduction

On February 23 and 24, 1983, TAT members John Bee, Anne Benedict, Ed Blanar, Scott Butterfield and Tom Hughes acconpanied by George Zachos, OSC, U.S. EPA conducted air and soil sanpling in the vicinity of G.E.M.S. Landfill, Gloucester Tovmship, Canden County, New Jersey.

Scope and Objective

The scope and objectives of this air and soil sanpling plan were developed by TAT in two separate plans; a "Soil Sanpling Plan" and a "Air Sanpling Plan", for G.E.M.S. Landfill on February 11, 1983.

I. In sumnary, the objective of the air sanpling pletn was to monitor the ambient air for worker safety during the installation of a fence and culvert at Fox Qiase II and Briar Lake. The objective of the?"soil sanpling plan was to collect soil sanples at four locations adjacent to t h e G.E.M.S. Landfill; specifically, behind the Fox Chase II development along the prc xjsed fence line and along Holly Run Creek near Briar Lake at the proposed culvert excavation/fence line. Analysis of the soil sanples were taken to determine disposal requirements under RCRA regulations sliould it be necessary t o remove soil frcm the site. In a^ition, to soil samples, -four piezcneters were installed in four of the borrix)!^^'The — piezometers were to provide a permanent sanpling location for additional uatec sanples that may be requested in the future. X

-*• Synopsis February 23, 1983

The TAT team acccxipanied by George Zachos,'OSC, arrived at the Fox Chase II development at approximately 1030 hour. The weather was cloudy with light rain, the temperature was 45 F.

At 1115 hour TAT member Benedict & Blanar conduct an air survey of the Fox Chase II area including the field behind Ft>x Qiase and along Holly Run Creek. There was prevailing odor in the area. The air survey was conducted in "Level B" protection using the OVA and Bdmont Combustible gas/oxygen monitor. Background readings en the OVA were between 7-9 ppa. In the field, the levels on the OVA varied frcm 9-16 ppn. Along Holly Rjn Creek, at the base of G.E.M.S. Landfill, the levels reached between 20-40 ppn. (See Figure 1).

At 1330, TAT manbers in Level B, using a post hole digger, dug into the field near the proposed fence line at Fox Chase II. The OVA, with a 3* probe was placed immediately into the opening, the re di g4-<>n the OVA recorded greater than a 1000 ppn organivMmqpn: while nethan^ levlesywere between 10-20 ppn. .-. O^VM^ ^ ^ ^ _

?ev*l5 t la>5 - t o « H9M»^ At 1400 hour, TAT members Bee, Butterfield and Hughes, wearing Level B protection, collected split spoon soil sanples. Soil sanples v«re collected at location PI c and P2 (See Figure 1), at depths of 0-2 and 2-4 feet. Duplicate sanples for I Gloucester Township were also taken. At location P2 a piezometer was installed to a depth of five feet. c

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SCALE 90 100 200 Fttt

Air/Soil Sampling Locations Fox Chase II

February 23, 1983

Weston/ SPER - Region II Figure 1

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At a third location, P3, an additional piezometer was installed. On March*?, 1983, this piezometer, adjacent to the base of G.E.M.S. Landfill, was sanpi«d,by the New Jersey Department of Environmental Protection , Division of Water Management, Hazardous Site Mitigation Administration. On March 8, 1983, results from the water sanple collected at this piezometer (P3) showed various organic conpounds totalling 135,749 ppb. A table listing the conpound identified and their concentrations is shown in Appendix I.

All activities at Pox Qiase II ended at 1700 hour.

February 24, 1983

The TAT acconpanied by George Zachos, OSC, arrived at the Briar Lake area at 0800 hour. The weather was clear with tenperatures in the forties. The winds were light and variable.

At 0900 hour, Mr. Allan M. Ttordini, of United States Testing Conpany, Inc., representing Gloucester Towiship arrived on site to monitor the sanpling.

At 0930 hour, TAT members Benedict and Blanar, in Level B, conducted an air mcxiitoring survey, using the OVA and explosimeter. Background readings takeD upwind were 2.0 ppn. Readings around Briar Lake and along the banks of Holly Run Creek were consistently in the range of 2.0 - 2.5 ppm.

At 1000 hour, TAT members Bee, Butterfield and Hughes, in Level B protection, *• collected split spocm soil sanples at location P4 and P5 (See Kioto 1, Figure 2)*.

At 1010 hour, MSA personal sanpling punps with carbon sphere collector tubes, were set-up at location P4 and P5 to monitor for volatile organic conpounds (See ttioto 2 and 3). A background air sanple was set-up on the property of Mr. J. Tieve, located cxie half mile north of the Briar Lake area, off Erial Road (See Figure 3).

At each of the three locations, two MSA sanpling punps were set-up. The purpoea. of this was to provide duplicate air sanples for Gloucester Township. Mr. Tordini, V*K) witnessed the entire sanpling operation, representing the interests of Gloucester Township received four diiplicate sanples, two at^^anple locations P4 ( and P5, one background sanple on the J. Tieve property and one travel blank.

( ^ C' At 1330 hour, piezometers were installed at locations P4 and P5 (See Photos 1 and 4). It should be noted that subsequently in May of 1983 both piezometers, P4 and. P5, were destroyed diaring>' )» immediate removal action to replace two undersized culverts en Holly Yat Cre^»- and install two dual 83" X 67" culvert pipes at the inlet to Briar Lalie.

At 1500 hour all activities at the Briar Lake area were oonpleted and a l l sanples were taken to the U.S. EPA laboratory in Edison, New Jersey, for subsequent 3 analysis.

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Equipment Calibration o o

Prior to the air sanpling program all instruments were calibrated according to o

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Air /So i l Sampling Location Briar Lake area

February 24, 1983

WESTON/SPER I I Figure

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Air/Soil Sampling Locations GEMS Landfill

Gloucester Township, NJ

Weston/SPER - Region II February 25 1983

Figure ,

Instrument Calibration Standard Calibration Results

OVA - 128 102 ppn methane in air

100 ppn @ 3.0 span

"

Edmont Com- 2.5% methane LEL 2.5 methane LEL bustihle gas/ 17% oxygen in 17% oxygen in oxygen meter nitrogen nitrogen .-

As part of the air sanpling program, eight carbon sjAiere collector tubes were used. Prior to use in the field, each collector tube and its respective backup tube was heated at 250 C for approximately 10 minutes and desorbed with the use of a Century Prograraned Thermal Desorber Model PTD - 132A. Presanpling desorption serves to purge the collector tubes of residual volatile organic conpounds to ensure contaminant free tubes. Following desportion, each tube and its backup were placed in 40 ml glass vial with teflon septums for cooling and storage.

Six MSA personal sanpling piaips were utilized in the sanpling program. Prior to and inmediately after sanpling, the punp flowrates were checked against a calibrated rotcineter to determine accurate flowrates and to ensure that the flow remained constant during the sanpling period. /; •

The sanple punps were operated for ajproximately 131 minutes at, 0.30 liters per minute (1/m). Table sanple volume pulled through the punps was 39.3 liters.-. Table I Jists pertinent information relative to the sanple program. The calibration curve GaW be found in i^pendix II. ^ i*-\/'rir'•l^ i *

, , •' 'Table T ^^'X.o^^>' 3 ^ , ,

Sanpling Location

P4 P4 P5 P5 Background Background

Punp#

002891 003429 002893 002917

003212

003144

Rotometer Reading

16 16 16 16

16

16

. Flow Rate l/min

0.30 0.30 0.30 0.30

0.30

0.30

Start Time (hr)

1018 1018 1015 1015

1030

1030

Eiid Time (hr)

1229 1229 1226 1226

1241

1241

Sanpling Total Time Minutes

131 131 131 131

131

131

Soil sanples were collected using a split spoon sanpler. Before and after each soil sanple the spilt spocxi was cleeurted with soap and water, rinsed with distilled water, and air dried. This is dcxie to ensure a representative sanple by eliminating potential residual ccaitaminants from previous sanpling.

Quality Assurance

Chain of custody protocol was followed by the TAT (See Appendix III). Sanples were taken directly to U.S. EPA Region II Laboratory, Edison, New Jersey. Laboratory actions will be reported as per EPA Region II Q.A. Plan.

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Results i:#»*yiP

Table II presents the results of the air sanples taken at the Briar Lake Area. Laboratory analysis of these sanples was for volitale organic conpounds. A total of three carbon sphere collector tube sanples and cxie blank were collected.

Table II Results of Air Sanple

Briar Lake Area February 24, 1983

Location Punp# Sanple#Conpound Concentraticn OSHA mg/m ppb PEL (ppn)

P4 002891 63730

P5 002917 63731

Background 03212 63732

Chloroform 1,1,2, tri-chloro, 1,2,2 triflur-oethane

Benzene Chloroform Toulene

Benzene Chloroform

.600 X 10 "2 1.22

.350 X 10 -'' 6.41

.32 X 10 ""I

.60 X 10 -2

.14 X 10 -''

.30 X 10 ""I

.30 X 10 "''

10.01 1.22 3.72

9.39 0.61

50

1000

1 50 200

I-50

Table III lists the results of the soil sanple at Fox Chase II (PI & P2) and Briar Lake(P4 & P5). A total of four split spoon ocmposite soil sanples were collected. | Sanple at location PI and P4 were analyzed for full pa:i<»ci^ pollutants. Sanples^ P2 and P4 were analyzed for volatile organics, extraction procedure-'(EP)>^ tcaticity and oorrosivity as pH. - J ,/ - ij ^ C

For the oorrosivity analysis, on March 22, 1983, the EAP laboratory, notified EPA/TAT that the corrosivity analysis could not be performed because there was less than 20% liquid in the sanples. The EPA method requires 20% liquid. Therefore, with the approval of Fred Rubel, corrosivity was done as pH.

The EP toxicity test, v^ich includes raetals and^ pesticides was run only for nstals.

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Table III Results of Soil Sanples Ft»x Chase II, Briar Lake February 23, and 24, 1983

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Location Sample# Analysis

Priority Pollutants

Volatile organic

EP Tbxicity

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Priority Pollutants

Cunpound

Mercury Arsenic Selenium Bis (2-ethyl-hexyl Phthalate Diethyl Phthalate Dimethyl Phthalate Lead Barium Toluene Corrosivity

Benezene Ethylbenzene Toluene

Silver Barium Cadmium Chromium Lead Mercury Arsenic Selenium Corrosivity

/

Silver Bariun Cndium Ciironivm Lead Mercury Arsenic Corrosivity Fluoranthene Diethyl Phthalate Kienanthrene Pyrene

None detected

Concentration

.100 X 10-3

.200 X lO"""

.600 X 10-2

*

350 ^/kg *

.130

.140 *

5.4

*

3.6 3.2 '

.60 X 10-2

.65 *

.80 X 10-2

.20 X lO-""

.70 X 10-3 *

.600 X 10-2

.5.2

.70 X 10-102

.34 * * *

.20 X 10-3 *

5.0 * *

* *

Mg/Kg = A '

K-/tl

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PI 63564

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P2

63565

63730

P4 64779

P5 64780

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um^ T^ble III

Results of Soil Sanples Fox Chase II, Briar Lake February 23, and 24, 1983

Location Sample! Analysis Compound ConcentratiCTi Mg/Kg

P5 64781 EP Tbxicity Silver .70 X 10*2 Barium .83 Cadmium .40 X 10"^ Chranium .20 Lead .10 X 10"J Mercury .30 X 10"3 Arsenic .20 X 10"^ Selenium .90 X 10-2 Corrosivity 5.5

*Presence of material vertified but not quantified.

Discussion of Results Air

, * • As was stated in the scope and objective section, the purpose of the air sanpling vfes to obtain data for worker safety. All three air sanples showed two or three organjtb npounds in the low parts per billion (ppb) range. In Table II the OSHA permissible

exposure limits (PEL'S) are given. While the sanple values are very lew in conparison to the OSHA PEL'S the mere presence of these conpounds tends to stress that further sanpling is necessary.*

At the present time, there are no acceptable federal or state "residental air quality standards" to oonpare these values against. Carbon s^iere collector tubes are not the recommended procedure in "NIOSH Manual of Analytical Methods" for volatile organics and, therefore, it is incorrect to make direct conparisons to the PEL values. In addition, the unique ventilation system in the ambient air, as well as low tenperatures, versus indoor atmospheres produces data that does not reflect average daily concentrations.

In ocxiclusions, while the air sanples shewed low concentrations of volatile organics, future sanpling is necessary. An air sanpling program, vAiich could include sanpling during the warmer summer months and include other pollutant and meteorological variables as well would better define existing air quality conditions.

Soil o

The intent of the soil sanpling was to determine soil content in terms of disposal i requirements for RCRA. At the present time there are no aceptable standards for soils. The EP toxicity, test identifies a waste whose ocxistituents have a tendency to § leach or migrate when disposed of in an inproperly designed sanitary landfill. The EP '-' toxicity test has threstolds levels established for the metals dtxie in the EP toxicity analysis. The concentrations of the metals found in sanples P2 and P5 were well below 2 the EP threshold levels. !

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01197,

Sanples P2 and P5 were also analyzed for volatile organic ocnpounds. In sanple P2 benzene, ethyl benzene and toluene were found. Conparing those three conpounds to the proposed Water Quality Criteria ethyl benzene (3.6 ppb) was greater than the proposed standard (1.4 ppb) while benzene (trace) and toluene (3.2 ppb) were below the proposed criteria of 0.66 and 143,300 ppb respectively. Sanple P5 showed no volatile organic conpounds.

Sanples Pi and P4 were analyzed for full priority pollutants. The only significant concentration found, was diethyl jiithalate in 350 Mg/Kg. The proposed water quality criteria for diethyl phthalate is 60 Mg/1. While this was a soil sanple, the presence of this conpound, and other organic conpounds, such as those discovered during the state's piezometer sanpling program, constitute a threat to the aquifers of concern in this area.

The average pH of the four sanples was 5.3. In summary, vAiile the number and CCTicentrations of conpounds found in this study were limited they do not necessarily reflect the actual pollutant concentrations. Further investigaticxi with additional sanpling in air and groundwater is necessary to form a strong data base for proper conclusiois.

•Note

A blank air sanple was analyzed and showed concentrations of chlorobenzene and 1/1,1 -trichloroethane. Subsequently, all 3 air sanples showed chlorobenze and r 1,1,1-trichloroethane. In discussion with th6 EPA laboratory several possibili^es exist to explain this occurrence; contamination during the transport stage, !* contamination from the glass 40 ml vials, oontamination during the laboratory analysis from the thermal disorber or contamination during laboratory holding time. Since one background concentration was higher than a sanple, it was decided to eliminate ^^. conpounds from the air sanple results.

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APPENDIX I STATE'S RESULTS

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NJDEP Sanpling Results Location - Piezcaneter P3

Pox Chase I I Area

NAME CCMCENTRATICM (ppb)

Methylene Chloride 18,400 1,1 Dichloroethene 140 1.1 Dichloroethane 3,280 1.2 Dichloroethene 8,600 Chloroform 600

1,2 Dichloroethane 4,000 1,1,1, Trichloroethane 2,200 Trichloroethylene 10,000 Tetrachloroethylene 5,600 Benzene 3,900 Tbluene 64,000 Ethylbenzene 3,400 P-xylene 10,700 O-xylene 3,400 Styrene 620 Parabromofluorobenzene 327 N-prc^jyl benzene 375 " Bromo benzene . 181 *• 1,3,5 Trimethylbenzene 127 « 1,2,4 Trimethylbenzene 390 Para Dichlorobenzene 286 Meta Dichlorobenzene 200 Ortha Dichlorobenzene 63

135,749

TOTAL CC»K:ENTRATI0N FOUND IN PIEZOMETER = 135,749 ppb

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APPENDIX I I CALIBRATION CURVE

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APPENDIX III SAMPLE RESULTS COMPUTER PRINTOUT

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RCC[:iVE[ -mry

LOCATION c o o t s FOR I D E N T I F I C A T I O N OF SAMPLING POINTS AT I N ' i o S T ' ^ I A L / —^iANtTAwT P A t l L l T i e S * L A N U F l L L S a HAgAMOOUS WASTE M T E 5 .

UUe NUWBtWS bAPPLlNb PUIWIS

DOl - 10- 0 Obi - 109S

EFFLUENT PIPE NUHnEH 001 TO 0-0 OTHE« EFFLUENTS SUCH AS COOi IN(j TOWER CiISCHaReta uic;i:HAtc(it m u m H U L U I N U P U N D S E T C IN PLANT SANPLES - 0URIN6 PROCESS 100

zrr — T T IN WLANI SANPLES AhlkH PHUCESS AND UE U' L TREATMENT OH OISCHARQE

1A5* IN PLAN; SAWPLES - lIUHINb TREATWENI SEPARATE INFLUENT POINTS/WATER SOURCES I

DOO rxx" ooo rtnr-i O O

«oo nnr b O O

^fro-

INFLUENT ASSUHATEU IIIH EFPLUENI—lUAA BLANK FOR VOLATILE ORGANICS AUTO SAHPLEH HLAWK. Al SANPLE HUalllUN IXX< QHOUNO MATER FROM WELL Ol TO 94 3099

3299 seOIWCNT SAWPLE (WATER BOTTOHI SOIL SAMPLE STREAM WATER SAHPLt LAGOON SAMPLE

3399 3*99 3399 3699 3T99

STOffAGK J AUK SAHPH LEACHATE SAMPLE OTHER TYPE SAMPLE—

fAGK

3

tr

o o

011986 -

PAOE

COMPLETED ANALYSIS REPORT REPORT DATE; H3/0A/27

PROJECT NAMEIQEMS LANDFILL PROJECT OaTt" :8J/03/3l

LASNO PAHNO PARAMETER NAME UNITS CHEMlSTRy VALUE (, REMARK

63b64 3*295 BUTYL BENZYL (-MTMALATE UI-N-aUlYLPHHIHALATb OI-N-OCTrL PHTHALATE

U6/K6 SEOIMENT Ub/KG UG/KG

SEUIHENI SEOIMENT StUlMENl SEDIMENT

1*599

3 * 3 4 * n i t l H Y L P H I H A L A I t U I M E T M Y L PHTHALATE

UG/KG UG/KG Ul»/M» UG/i^G

- 3 V 5 Z 9 l t . i - H E ^ I ^ A N I H H A L L N E ST 3 * a S 0 HENZO A 'PYRENE S J A d 3 3 3 t * -HENZUPLU0RAWTHENE S"

S b U l H E N I SEOIMENT SEUIMEWT

JSO.OOO ^ 7 . 0 0 0 0

i r u

J*<J*5 3 * 3 2 3

U t l a - H E N / U I - L U U ' ^ A N T H E N t CHRYSENE

U t i / H 6 UG/KG

SEUIHENT SEOIMENT

3*203 3*223

ACENAPHTHYLENE ANTWRACCNE

UG/KG UU/NO

SEOIMENT 5EUIMEWT

3*32* 1»12-HEN20PERYLENE UG/KG SEDIMENT j*ja* 3**6*

FLUUHENE PHENANTHRENE

"TJTJTKtr UG/KG

SEUIHENI SEOIMENT SEUIMENI SEDIMENT

j*sa<i' 3**06 3**7^ 3*678

l < . ? l b » b - U l U E N / A N I H k A L E N b I N D E N 0 ( l f 2 « 3 - C t U ) PrRENE UG/KG

Ub/KU UG/KG

PTRENE TCOO

SEUIHENI SEUIHENT StUIHENT SEOIMENT

3*71* 3*708

ISOMER M/P UILHLOHOHEWZENES ISOMERS CHRYS/HENZ(A)ANTM S

Utt/RB UG/KG

UU/KG

"TT U

-tr HI9AH 3*710 3V333 99900

ISUHEHS PHENAN/ANIHHALENt S ISOMERS HENZ0(B/K)FL0U»AN S

SEUIRENI SEOIMENT SEUIWENT TOTAL

i r U RLURIN

SILVER UG/HG MG/L Ub/RO MO/L

.SOOO 39383 99903 3V331 39301

UIELUWIN CADMIUM

SEUIHENI TOTAL

ftOE- 02 "TT K .900000E-02

LHLUHUAWE *.*»-00T UG/KG

SEUIMEWI SEOIMENT

3*321—<«»«-ooe ua/KO seoiHgwT 39311 3*36*

*»*»-000 ALPHA CNDOSULPAN

UG/KG UO/KG UG/KG

SEOIMENT SEDIHCNT SEOIMENT 3«3S9 BETA ENOOSULFAN

3*35* ENOOSULFAN SULFATE 393<3 CNBHIN 3*369 ENOHIN ALUEHYOE 39*13—MePTaCLOH 31*23 HEPTACHLOR EPOXIDE

UG/K6 Uq/KG UG/KG Ua/KG UG/KG

SEDIMENT SeOTHENT SEOIMENT SeOtHCNT SEDIMENT

39076 3*g3T

ALPHA-dHC BETA-BHC

UG/KG UO/KO UG/KG

SEDIMENT SCOIMgNT SEOIMENT 3*267 GAMA-BHC

-»»*K CHROMIUM 3*262 OELTA-HHC 99920 C0WR03I»tTT

Ha/L— UG/KG

TOTAL SEOIMENT TOTAL SEOIMENT

SEOIMENT

• JOOOOUE-UI—-J-U

S.*UUDU 39*«9 3938?

PCB-12*2 PCa-125*

39*91 PCH-1221

UG/KG

UG/KG

U V

u

l -A i i >

o 3 r

o o

01198 7 - J

-.4

COMPLETEO JNALYSIS REPORT REPORT OntE; 83/04/27

PROJECT NAMEiGEMS LANi)FILL PROJECT HATE 183/03/31

LAdNO PARNO PARAMETER NAME UNITS CHEMISTRY VALUE t, REMARK

63b6* 39*95 P C H - 1 2 3 2

pCb-12*il 39511 PCtl-1260

llb/KG U(i/KS UO/KG

SEOIMENT SEOIMENT SEDIMENT

3451* 9990ft 39403 3423 7 44;?yv 3430* 44534 345 IJ 9 J4*9>* 3451* J4bl'^ 3431*

34271

345/4

J431M 3450* 345*^ 345** J4bb* 3437* J44c<> 34*? I J441<> 3424 il

343 J IJ 344S1 J 4 3 J * 3*3!> > J44;u 3 4 * (J 3 44*a/ 34*95 342 i J 342 M

LEAU TOAAPHENE BENZENE CARHUN It IRACHLOHIUE CiLOROHENZENE l.ii-UlCHLUHUtlHANt Itlal-THICHLOROETHANE I«1-UICHLUW0EIHANE IfIf2-TRICHL0R0ETHANE l»l.<!.<l-ItlHACHLOROEIHANE CHLOROETHANE

M I S ( C H L O R O M E T H Y L ) E T . UAKIUH 2-CMLOROETHYL V I N Y L E T . CHLUHOFURH lal-OlCHLOROETHYLENE

S M s s s s s s s s s s

s

s s s

1.2-THANS UlUhLUHOtTHyLENES U2.-0ICHL0B0PR0PANE S 1 a J-UKHLURUHRUPTLENE ETHYLBENZENE HtlHTLENE CHLURIUE METHYL CHLOHIOE METHYL aHOHIUt qRONOFORM UlCHLURUBRUMUHEIHiNE THICHLOROFLUOHOMETHANE UICHLORUUIFLUURUMEIHANE CHLOROOIBROMOMETMf.NE 1E1HALHLUHUt1hVLENE TOLUENE TRICHLOROCTMTLENE VINYL CHLORIDE •CROLCIN ACRYLONITRILE

S

s S s s s s s s s s s s s s

OiS/Kfl MG/L bd/KQ Ufi/KG Ub/KG UU/K6

UG/KG UU/Rb U G / R G UU/kG UG/KO

Uti/KG MO/L UG/KO Uti/KG UU/KG W/K(i UG/KG U(]/KO UG/KG Uo/KB U6/K6

UG/KG

Ub/KH UG/KG Ub/RG UG/KG Ub/Kti UG/KG UG/KG UG/KG Ub/«b UG/KG

SEDIHEKJT. TOTAL .130000 SEOINENT SEOIMENT SEUIHENI SEOIMENT SkUIHkNT SEOIMENT SEUIHENT SEOIMENT bbUIMtNl SEOIMENT

SEOIMENT

lUIAL .1*0000 SEDIMENT SEUIHENT SEOIMENT stuiHkwr SEDIMENT t SEDIMENT -» SEDIMENT » SEDIMENT SEDIMENT SEUIHENT SEDIMENT SEUIHENI SEOIMENT SEUIHENI SEDIMENT SbUlMENI SEUIHENT ^.00000 SEOtHCNT SEDIMENT StUlHENI SEDIMENT

U

U U u •

u

u u u u U u

u

u u u u u u u U u u u u u u u u K u u u u

ro l A T F : bOJL L SAMPLE COLLCCieO HT S P L I T SPIIUN

OEPlM I N POA V I » I . 83^183 3 4 ^ J /

3 4 2 9 9 - 3 * 3 n *

3*5J<»

- 5 U l t / R b S UG/KG

^ UO/KS S U( i /KG

SEUIHENI SEDIMENT SEOIMENT SEOIMENT

^.UOOOD T - . HENZEWE CAHBON T E T R A C n L ' l H l J t

1 » 2 - 0 I C H L 0 R 0 E T H A N E

011988

Gf \L 00{ o ^ f i

r- PAGE

c

- 1

COMPLETED ANALYSIS REPORT

PROJECT NAMEIGE

LAUNO HARNU

63565" •3*b09-3**99 J*514 3*519 J * J U 3*271

3*318

3*549

3*544 3*S«4 J*Jf4 3**26 J*42t-3**16 3*290 3*330 J44VI 3*334 J430V ;u*78 3*483 J**«7 .1*498 3*213 J4Z18

Ms LANDFILL

PARAHEtER NAHt

"T 1111 - 1 W 1 r:HLUHUt 1 HiNb 1.1-DICHLOROETHANE I » 1 »2- 1 WRHLURUt 1 HANE Itl i2t2-TETHACHL0R0ETMANE CHLUWUtlH4Nb eiS(CHLOROMETHYLl ET, 2-(,HLURUt IHTL WINYL tl. CHLOROFORM

S S S S S

s s s

l.l-UH.HLURUblHYLENb b 1,2-TRANS DICHLOROETHYLENES 1 ,2-UltHLUHUHRUMANt 1 . 3 - D I C H L O R O P R O P Y L E N E

LlhTLUkNZENb METHYLENE CHLORIDE HtlHTL LHLORlUb METHYL HROHIOE ^HUMUFURH DICHLOflOSROHOHETHANE THlLhLUHUFLUUHUHtlHANt O I C H L O H O D I F L U O H O H E T H A N E

tHLORODlBROHOHCTHANE TETRACHLOROETHYLENE lULUtNE TRICHLOROETHYLENE VINTL LHLURlUb ACROLEIN ACRILONl IHILE

b s s s s s s s s s b

s s s s s s

UNITS

UU/KG UG/KG Ul>/K(» Uti/KG UG/RG U G / K G

UG/RS UG/KG UU/KG UG/KG UG/KG UG/KO Ub/RG UG/KG UU/R6 ^G/KG UG/KG U8/K6 Ub/KU UG/KG Ub/Rb *JG/K6 UG/RU UG/KG Ub/Rb UG/KO Ub/Rb

REPORT OATt

PROJECT HuTt

LMEHISIHV

StUlHENT SEDIMENT SbUlHENT SEDIMENT SbUlHbNT SEDIMENT

• SEUIHENI SEOIMENT SbUlHbNI SEDIMENT SbUlHtNI SEDIMENT SbUlHbNI SEDIMENT SEUIHENI SEDIMENT bbUlHbNI SEDIMENT SbUlHbNT SEOIHENT

bbUIHENT SEDIMENT SEUIHENI SEOIMENT SEUIHENI SEDIMENT SblJlHENt

• tt3/0A/27

:«i3/U3/3I

VALUE A REHIHK

J.'bOOOD

J./OOOO

M

V

u u u u u u u u u u u u

u u U u u u u V u

u u u u

!29 I M A l f • O N T A i

TR HQ CARBON SPHERE COLLECTOR TUHESa

637 JD d2l3V FtNZENE 82140 CARBON TETRACHLUHIDt B214I CHLORUHENZENE a2142 1«2-DICHL0R0ETH«NE

HG/H3 MG/M3 AIR Hb/H3 MCi/H3

TCnr-AlR

.^20000E-01

«2143 82144

-rrr 1*1-

l-IRRHLUHUblHANL DICHLOROETHANE

HG/HJ MG/H3

Tvr-AIR

i 'UGOOOE-0^

-8rt*9 lala2-TRICHL0W0gT>HNe 82168 Itl*2t2-TETRACHL0R0ETHANE -8rr«« CHLOROe THANE 82147 BIS(CHLOROHETHYL) ET,

wa/H3 MG/H3 Hb/H3 HG/H3

-TTTR-AIR

-TV r AIR

U TT

82148 M2149

Z-^LHLUHOgrHTL CHLOROFORM

VINTL Ef, MG/M3

- r p r AlR

-«l*t8« 11 l-DlCMLeROETHTLENt. .iSOOOOOE-02

Ma/H3 MG/M3 M0/H3

AIR TtR-

8216S 82184

1»2-TRANS DICHLOHOtTMYLENE 1 •2"PICHL0R0PWOPANP.

PAOK

C c I -

011989

- 2 ^ PAGE

COMPLETED ANALYSIS*REPORT REPORT DAIE: 83/04/27

PROJtCT NAMEIGFMS L*NOKILL PROJECT O4TEifl3/03/31

LABNO PARNO PARAMETER NAME UNITS CHEMISTRY VALUE k REMARK

63730 821n3 1 a3-DICHL0H0PR0PYLf.NE IJT^TJ—ElMVLdLKiZLNt a2l<)7 METHYLENE CHLQRIOE 82in? H E T H V L CHLORlUk 82 lis 9 METHYL HRQMIOt

HROMOFORM

Mi i /M3 AIR " A T T T

A I R HG/M3 MG/M3 H . 5 / H 3 — m r MG/M3 A I P MG/M3

TT u

i r

AIR 6 2 1 b 3 DICHLOROBROMOMETMANt MG/MJ

821S* T K I C H L O R O F L U O R O M E T H A N E TZl'^Z—DICHL0R0DIFLU0R0HET.1ANE 82161 CHLORDDIBROMOMETHANt

82165 TETHACHLOROETHVLE'^f TOLUENE

MG/H3 "R7I7HT" Mfi/MJ

AIR

"TPr AIR Hu/H3

M6/H3 HG/H3

AIR

U TT

9999-1 - B T T s T — » ; I N Y L CHLOHI

THICHLOHOtTHVLbf^b" H N U E F I N E O t —V.

D t ^

T p r .350000E-01

r s — 26 k'AItl

t ,l .2.-TH.'«HLnK.a " ^r^

HG/HH XTR

T F T NTAINING CARBON SPHERE COLLECTOR TUBES.

6 J / J 1 WIJH—rib l^ /ENE 8 2 1 * 0 CARBON TETRACHLORIDE H ^ U l CHLUROUbNZbNb 8 2 1 * 2 1 . 2 - D I C H L O R O E T H A N E

MG/H3 m r -MG/M3 AIR

AIR

.3<!O00OE-OI

H G / H J MG/M3

llOOOOL-Ol AIR

9 2 1 * 3 l a l a l - T R I C H L O R O t T M A N E 8 t l 4 * 1,1-PTCrlLOROETMRNC « < 1 * S I « l « 2 - T R I C H L 0 R 0 E T H A f < t 8 2 1 ^ 8 l » l t 2 t 2 ^ l t T R A L H L URUbTHANt a21«t> CHLOROETHANE

Mr,/M3 MU/WJ

M(i /M3 H b / M J M6 /M3

A I P

- i r r r AIR

T p r A IR

. 7 O 0 O 9 O E - 0 2

U

8 2 1 * 7 B I S I C H L O R O M E T H Y I . 824 AH a-LMLURUETHTL 821A-9 CH. O R O F O R M

t T . VINTL

Mfi/M3 TT:

AIR H b / M 3 MG/M3

T P r -AIR

B2H»6~ 8216^-

T 2 T E T -a21t:3

T T T 1*2

• l U L H L U H U b l H y L b N b • T R A N S O I C H L O R O t T H Y L E N t

A I R AIR

.^OOOOOE-02 M b / H J M(j/M.1

I t ^ - L I K H L O H U P R U P A N b 1 • 3 - O I C H L O H O P R O " Y L E N E

Hv>/M4 MR/M3 A IR

" W r r n b lHTLHENZENE a Z l ' - T METHYLENE CHLORIDE

- m m r z H b l H T L L H L U R l U b 821«-.9 METHYL HROHIDE

H b / H J MP/MJ

T T T ^ A IR

- I T U

H b / H J M i i /M3

T p r AIR

82l7l HHUHUFURH 821';3 OlCHlOROBROMOME THANE 821'<» TWICHLOHUFLUURUME THANE— a21'i2 O I C M L O R O D I F L O O H O M E THANE

AlH u Hb/HJ' M3/M3 Hb/HH MU/M3

TTP-«IR

-«Tfrr-a2iM> 82133

CHLOROBIHROHUHE fWANE TETHACnLOROETMYLEMt lOLUENE

H b / H J TTR~ M( i /M3 A I P H b / H 3 STR"

U - •

U . I*OOOUE-l l l

O 3

o o

o UI

o

011990

'3^ PAGE T

COMPLETED AN4LV SIS REPORT REPORT DATE: fl3/0*/27

-'E

OF

PROJECT N A M E I O E M S L A N D F I L L

LABNO PARXO

63731 821S6 Hiil'Sf

PARAMETER NAME

TRICHLOROETHYLENE

VINYL CHLORIUL A A

UNITS

Mo/MJ

Hl'/H}

PROJECT i</<TE!H3/i)3/3l

CMEMISTRr VALUE t, REMARK

AIR u

«1« u

u j o - -- • 2*1 TRHIEI AIM — ^ — ONTAINI+(G CARBON SPHERE COLLECTOR TUHESa

»>J7J2 82139-82140

' H2141 H2142 82143 132144 H2145 82168

•12147 H2148 H2149 82166 82165

82163 82130 82167 82162 82169

82183

82134 82132 82181 82160

8219S 82196 82197

BENZENE J CARBON TETRACHLCiRIDE i LHl URUHENZENE 1 1.2-OICrtLOROETHANE 1»1tl-THJCHLORUCTMANE I lal-DICHLOROETHANE l«l«2-IRlLHLURUtlHANt ltl»2»2-TETRACML0R0ETHANE 1 CHLUHUEIHANb i BIS(CHLOROMETHYL) ETa 2-CHLURUtlHTL VINYL tl. CHLOROFORM

l»l-UILHLURUEIHTLbNt \ 1.2-TR4NS OICMLOROETMYLENEl l»2-UII.HLUHUPHUPANt i 1»3-01CMLOROPROPYLENE I CTHTLBENZENE J METHVLENE CHLORIDE / HE IHTL LHLIIRIUE 1 METHYL BROHIDE I

OICHLOROBROHOMETHANE i

OICHLOROOIFLUOHOHETHANE J

C H L O M O O I S R O M O M C T M A N E 1

TETRACHLOROETHYLENE i

TOLUENE i

VINTL CHLORIDE I

I H5/H3 k Mu/H3

\ Hb/HJ » M(5/M3 1 Nb/HJ k MG/H3 I Hb/HJ k MG/M3 \ HU/H3 k MG/H3 ( Hb/HJ k MG/M3 k Nb/HJ k HG/M3 \ Hb/HJ k Hb/H3 k HG/HJ k MG/H3 k Hb/H3 k HCi/H3 \ Hb/NJ k HG/M3 1 H8/N3 k HG/H3 I MW/nj k HG/H3

k MG/M3

k MG/M3

AIR AIR

AIR AIR AIR AIR AIR AIR A H AIR AIR AIR AIR AIR A i K

AIR

AlH AIR AIR AIR AIR AIR Al« AIR AIR AIR

AIR BIN AIR

.JUOOOOb-01

.SbODOOt-Ul

.nouoot-oi

.300000E-02

^

V

U

U

u u U u u u

U u u u u u u

u u U u u

u u u

2*2

TRATEJ AIR ML VIAL C O N T A I W I N O C A R B O N SPHCME UHES.

63T33—8rT99—BCWZENC 82140 CARBON TETRACHLURIOt rrtri—cwLOwoBENZgNe 82142 l t2-UICHL0R0EThANE « 2 t * 9 tTITt^TRlCHLOHOtTHANE

MG/HJ Ma/M3

-rnr-AIR

-HTi7W3 r r T " M6/M3 AIR

.4S0UDDb-Ul

:-ttJot>irt>r»!n 32144 lal-DICHLOROETHANE MG/M3 AIR

PAi i f

n tr

o o

o

011991

3/ PAOF

COMPLETED ANALYSIS REPOi^T REPORT DATE; 63/04/27

PROJECT N A M E : G F M S L A N D F I L L PROJECT OATF. 183/03/31

L A S N O PireNO "PWifflETET NAME UNITS tMtMISTHY T/TfCDT^CWtMAHK

6 J / J 3 aaiAS 82168

l t l f?- lH( lCHLO«OETHANt ' I»l i2t2-TETRACML0R0ETHANE CHLOPOETHAME BIS(CHLOROMETHYL) tT.

HG/M3 MG/H3

"ATTT AIR

BZUS 821*7 8 2 1 * ' ! 821*9

821ftS

821 i3

2 - L H L O ' ^ O E T H Y L V I N Y L t T . CHI OROFORM

HG/M3 Mii/H. A H

Itl-DItriLOOOElHvLENE 1,2-TR4NS DICHLOROtrHYLENE

MG/M3 MG/M3

"TlR-* H

M0/M3 MO/MJ

"ATT AH

"TT u IT u TT u TT u

"cr u TT u

1.2-DICHLOflOPHOPAK|t 1 .3-DICHLOROPHOPYLF.NE

H5/H3 MG/M3

U2IS0 82H7

82169

"TTHTUHFNTENE METHYLENE CMLUhlOE

"xpr

AIR

Al»

HG/HJ MG/H3

MtlHTL LMLURlUt METHYL BROMIDE HHUHUFURH '"

Hb/HJ MG/M3 Hb/HJ

AIR

O I C M L O H U B R O H O M E TMANE TRICHLOROFLUOROMETiANE

MS/H3 MG/H3 8215*

"ATH"

A H U U

821*32 DICHLOROOIFLUOROHETMANE 8 2 H r 82H0

CHLURUUlURUHUHbIHANt TETRACHLOROETHYLENE

Mb/M3 Hb/HJ Mb/M3

A H

A H

u

u a 2 i s s — r u L U F N t 821=6 TRICHLOROETHYLENE H21S/ VINTL CHLUWlUt

HG/HJ MG/H3 HU/HJ

"xpr A H

T H "

TT U

-IT

JU W A T E : SOIL

I L SAMPLE 1 R

. ;ULLe i . l t :U BT b l - L I I bHtlON

6 4 7 7 8 99VU0 9 9 9 0 2 999.1 J 9 9 9 0 * 999; * - . 9 9 9 ' i S 9 9 V i ! l 9 9 9 d / 9 9 9 2 U

•^ILVtrH 84«1UM

T S U H I U H cnyohiuM LEAU MERCURY

SHSENIC SELENIUM

•CORPUS 1V I T T

M M

H H

H M

M M

MU/L MG/L H b / L M b / L H b / L MG/L H S / L MG/L

TOTAL TOTAL T U I A L TOTAL l U I A L TOTAL l U I A L TOTAL TOTAL

tm

.f>000A0E-02

. 6 ' < 0 0 0 0

. V U 0 0 0 0 t - 0 2

.SOOOOOE-02

. 7 0 0 0 0 0 E - 0 1 . 7 0 0 0 0 0 E - 0 3 . 2 O 0 a 0 0 E - 0 1 .<S00OO0E-O2 "•.ZOUOO

J

K J J

J

10 . . . _ - lATkJ bOIL

I L SAMPLES

.'NC 0 TO * COLLECTED BY S P L I T SPOON FT O E P T M •

6 * 7 7 9 9 9 9 0 0 9 9 9 0 2 -999 ' ,H

• — ... - 9 ^ 7 n 5 -

?^lLVh.R

H A m U H C A O M I U "

L H R U H U m

H

•• H

M H

MG/L H ' V L

MG/L M l l / L

TOTAL I 0 1 A L TOTAL l U I A L '

. 7 0 0 0 0 0 E - 0 2

. 3 * 0 0 0 0

. 9 0 0 0 0 0 E - 0 2

. 7 0 0 0 0 0 t - 0 2

J

K

R 999u<> LEAD M-3/L TOTAL . l O O O O O E - 0 1

o o

o Ol NJ

011992

• y i ^ PAGE

COMPLETED ANALYSIS REPORT REPORT 0«TEl 63/0A/27

PROJECT NAMEtOEMS LANDFILL PROJECT . I « T F : : H 3 / 0 3 / 3 1

Y TAHNO PARITO—FAWaHETET?TJAHE~ ITSTWT" V*nrt"H"T<rHJ1TK

HG/L MQ/L Hb/L

lOIAL TOTAL

.2U000Db-UJ

.200000E-01 " 6 *779 VM'JDS—Htm.HRY

99901 ARSENIC 99907 SkLtNlUH 99920 CORROSIVITY -TC5*J 2a*tt»-IRl'HL0RUPHtNUL 1**93 P-CHLORO-M-CRf.SOL J*bg9—;--rHLUWUPHtNUL 3*604 2 » * - 0 I C H L O R 0 P H E N O L 3 4 6 0 9 — 2 « * - ! ' H t H y L P H b . N U L 3 * 5 9 * V'-NITHOPHENOL i *649 *-NITROPHtNUL 3*619 2 t * - n i M T R 0 P H t N O L J*660 4 a b - U H 11 RU-U-LRbSUL

TOTAL TOTAL

.'iU0OOOE-U2 ".00000

UG/K5 UG/^G UG/KG UG/KG UG/KG UG/KG UG/KG UG/KG Ub/RU UG/KG Ub/RU U6/K6 UG/KO U'o/KG Ub/KU UG/KG Ub/RG

SbUlMbNT SEOIMENT 5EUIHEW.r SEDIMENT StHlHtNT SEOIMENT SbUlHbNT-SEOIMENT SbUlMENI SEOIMENT

TT U TT U TT u "IT

PENTACHLOHOPHENOL PHLNUL ACENAPHTHENE

39061 3*695 3*208 " I V m HtN^lUtlNt 3*594 lt2a*-TRICHL0ROHEN7ENE JSI/Bl—HkXAfHLUWUdbNZbNb 3*349 HEXACHLOROETMANE 3*276—HISt2-CHLURUEIHILI tl. 3*98* 2-CMLORONAPHTHALENE 3*939 1 t2-01CHLOROPEN^ENE 3*569 l»3-DICHL0fiO6ENZENE 343T4 l.*-UlLHLURUHEN^bNE 3*634 3t3«-0ICHL0R0UENZlD£NE

S»CVt%—2.**'. ' lNMRUT0LUENe 3*629 2.6- i INITROTOLUENE

-34r j f9 l»2-UlPHtNTLHTURAZtNE

SEUIHENI SEDIMENT SbUHbNI SEDIMENT SEUIHENI SEDIMENT

b^ S -s-s -S" s "S-s -s-s -s-

FLUORANTHENE S •-LHLOROPHtNTL PHbNTL bl. S A-HHOMOPHENYL PHENYL E T . S HiSIZ-CnLUHOISOPROPTL) ETH5 HIS(2-CHL0H0ETM0XV) METM. S HCXACHIURUHUUUIENE S"

StlllHENI SEDIMENT

u -Q-U "IT U

-TT U "TT

UG/KO Ub/Rb UG/KO Ub/Rb UG/KG UG/Rb UG/KO ua/RG UG/KO Ub/Rb UG/KG UG/Rb U U / K G Ub/Rb U i j / K G Uti/RB

SEUIHENI SEDIMENT SEUIHENI SEOIMENT SECUHgNT SEOIMENT SEOIHENT SEDIMENT 3*379

J4644 34639 3*2»6-3*201 J»JS4 3*389 J * * U

SEUIHENI SEDIMENT

AT.QOOO K "D" U "TT SEUIHENI

SEDIMENT SEDIMENT SEDIMENT HEXACHLOHOCYCLOPENTAOIENE S

ISUPHU-IUNt SbUlHtNI SEDIMENT

u "IT U "0" u "0"

3**4$ NAPHTHALENE -S^^t%^—NITMUPgNZgNg 3 * * 4 1 N-NITR0S00IHETHYL6MINE

-3«; j«—WNITWOSOUlPnEN'LAHINe

UG/KO UO/RG UG/KG U6/RS UG/KG Ub/Rb UG/KG ua/Ko UG/KG

SROIMENI SEOIMENT SEUIHENI SEDIMENT 3**31 N-NITHOSODI-N-PHOPYLAHINE S

39102—HIS»2-ErHtLNEATLI PHIHAL. S 3*299 BUTYL BENZYL PHTHALATE S 3^112 Pl-^-8lJTVLPPHTHALATe S" «*S99 OI-N-OtTYL PHTHALATE S

-3•5*9—OlETHYL frlTHALATt T"

StUlHENI SEOIHENT aCDIHgNT SEOIHENT

U - r r u

-ir-SEUlMgNT nT.OOOO

E

c c

011993

COMPLETED ANALYSIS REPORT

3 3 PAbt I "REPORT DATE: 83/04/27

PROJtCT NAHEIGEMS LANDFILL PROJECT DATt:83/03/3l

Hut OF LAMNO PARNO PARAMETER NAME UNITS CHEMISTRY VALUE K REMARl 4Y

6*T7» 343** 3«52-> 3*250 J42JJ 342*5 3432 3 3*203 34223 3452* 343fl4 34*6* J45bJ 34*06 3447? 34678 J471* 34708 81949 34710 39333 393H3 J93bl 39301 J9321 39311 J4Jb* 34359 J4J5*

39393 34369

39*13 39*-" J 39076 J*2b; 3*2e7 3426i! 3949>< 3950/ 39491 39*95 3950 3

IlIMETHYL PHTHALATE 1 t2-BtKiZANTHMACENE fltNZO_A»PYRENt 3»4-HtNZUFLU0RiNTHENt I If l2-HeNZ0FLU0RANTHENE CHRYStNE ACENAPHTHYLENE AKITHRACtNE ltl2-dENZ0PERYLENE

FLOUWEKE PHENANTHRENE 1t2!b»6-UlBtN/ANIMHAttNt INOENOd,2,3-1.0) P Y H E N E

PVHENt TCDD

S

5 S s s

s 5 s s s s s s s

ISOHtH H/P UICHLURUeENZbNbS ISOMERS CHRYS/HtNZ(A»ANTH S ISUHtRS PHF.NAN/ANTHHACtNt ISOMERS BEN20(a/K)FL0UR»N ALUWIM DIELURIN CHLUHUANE *,*«-DDT *,*»-UI)t 4.*«-DD0 ALPHA tNUUSULFAN BETA ENUOSOLFAN ENUOSULFAN SULFA It

ENi'iRIN ENDRIN ALDEHYDE

M E P T A C L O R

HtPr«LHLUR EHOXIUt AL»-HA-BHC HE 1 A-HHC GAMA-BHC UtLli-HHt «CH-12*2

pm-i25* PCh-1221 PCH-I232 •'Cel-12*8

s s s s s s s s s s s 5

s s s s s s s s s s s s

Ufa/KG U G / K G

UG/KG Ub/KG UG/KG UG/KG UG/KG UG/><G UG/KG UG/KG UG/KG UG/KG UG/KG UG/KG UG/KG UG/KG U'J/KG UG/KG Uti/KG U G / R G

UG/KG UG/KG UG/KG UG/KG UG/KO Ub/KB UG/KG Ub/Rb

UG/K6 UG/KG

UG/KG Ub/Rb UG/i^G UU/RG UG/KG Uo/KO UG/ivG Ub/RG US/KG Ub/RU UG/KG

SEOHENT

bbUtMbNI SEOIMENT SEUIHENT SEDIMENT SEDIMENT SEDIMENT SEDIMENT SEOIMENT SEUIHENT bEUlMENI SEDIMENT SEDIMENT SbUlHtNI SEOIMENT SfcUIMENI SEOIMENT SEUHbNI SEDIMENT •SEOIHENT SEDIMENT SEDIHENI SEUIHENT SEDIHENI SEOIHENT btUIMtNl SEOIMENT SEUIHENI

SEr;IHENI SEOIHENT

SEDIMENT

SEUIHENI SEOIMENT SEUIHENI SEOIMENT btUIMtNl SEOIMENT SEUIHENI SEOIMENT SbUlHtNI SEOIMENT

'S7.0O00 *

A7.0000 F

«w L

JVbll 3951* 394*13-3*23 7 3429V

I'L;H-126U oCfl-lOlfc

Ub/KB Ub/KG

SbulHENI SEDIMENT SEDIHbNT SEOHENT SEUIHENT S E O H E N T

lOXAPHENE : •iEN/ENE LAHBON TgTRACMLURIOE

Ub/Rb UG/KG UG/KG UG/KG 3430* CHLOROSENZENE

2

o o

o Ul 4^

011994

PAGE n

COHPLETED ANALYSIS REPORT RtPORT ( n i l i 83/04/27

PROJECT NAMEtOEHS LANUFFLL

I'E "TTBITO PARHD PARAHt I t H TJAHc:"

P R O J E C T O 4 Tt : I* .3 /n 3 / 3 1

U N I IS l . M t H I S H ' ' ffALTir-TRtMARK

6 4 / 7 9 3 4 b 3 « -3 * 5 0 9 J * * 9 V 3 * 5 1 4 J * b l 9 3 4 3 1 * J 4 2 / 1 3 4 5 7 9

~ i 4 3 1 8 3 * 5 0 *

3*544 34564 3*37* 3*426

l.C-UlLMLURUtIH v^t IfItl-TRICHLOROETHANE 1.1-UICHLOWOEIHlNt

U t i / K G U Q / ^ G

S t U l H E N T SEOIMENT

I t l f 2 - T R I C H L 0 R 0 E T H « N E S I f l f 2 f 2 - I K I R A C H L U ' ' U t l H A N t S CHLO><0ETH4Nt S H l S I C H L U R U H t l H V L l b l . S" . - f H L O R O E T H Y L V INYL E T , S LHLOMUFURM S~

l . l - O I C H L O R O E T H ' f L E N E S 1 . 2 - T H A N S D K H L U R U E I H V L t N t S ! . 2 - O I C H L O R O P H O P A N e S 1 , J -U I ' .HLURUPHUPTLENc S~

UG/RI i U O / K G

U'.i/KG UU/. .G Ub /RG Ut i /KG Ub /RG UG/r.G

Ub/RG UG/KG

SEUIHENI SEDIMENT SEDIHET^T SEDIMENT SbUlHtNI SEDIMENT SEUIHENI SEDIMENT SbUlHENT SEOIMENT

ETHYLBENZENE HEIHTLENE LHLUHIUE METHYL CHLORIUE HblHYL HRUHIUE HROMOFORM UlCHLUHUHHUHOHETHlNt TRICHLOROFLUOHOHETHANE UlCHLORUUIFLUURUHtIHANE

Ub/RG UG/KG UG/RG UG/KG

SEUIHENI SEOIMENT SEUIHENI SEOIMENT 3**21

J**16 3*290 J4330 3**91 J4JJ4 34309 C H L O R O D I B R O M O M E T H A N E

-14478 rEIHACHLURUEIHTLENb— 34483 TOLUENE <*4a7 IHlLHLURUtlHTLtNb

"D" U "0" U "0" U

S -r s

-S" s

• 3 -

s -s-s -s-

UU/KG U G / K G Ub/KG UG/KG Ub/RG U G / K G Ub/RU UG/KG Ub/R« UG/KG Ult/RO UG/KG

StUlHENI SEDIMENT !>tl31HENT SEOIHENT ShUlHbNI SEOIHENT SbUlHENI SEOIHENT SEDIHENI SEDIMENT SEDIMENT SEOIMENT

14*95 -3*213

V i N Y L V H L O R I D E • i C R O L t l i l

3 * 2 1 8 HCRYLONITR ILE

0 * 7 riTRTt O I L

-s tn t 'LE TAKEN BY SPLIT SPOON

FT UtfMYT-6 * 7 8 0 3 * 2 3 7

3 * 2 9 9 eENZENE CARBON TETRACHLORlOg

UG/KG UU/R6 UG/KG

SEDIMENT SECHMENT SEDIMENT

U "TT U 3*304 CHLOROHENZENE

34534 If2-DICHL0R0ETH4HE S UG/KG -3*999 111 • 1-TRICHLOWOgTHANg S UO/KO 3**49 If1-OICHLOHOETHANE S UO/KG 3*314—If lf2''THICHL0.90E THANE S UG/RO 34519 IfIf2f2-TETRACML0R0ETHANE S UG/KO 3*314 CHLORUETNANE S Ub/Rb 34271 8IS(CHL0R0METMYL» ET. S UG/KO 3*379 Z-CnLUnegTnYL VINTL CT. S U0/R8 3 * 3 1 8

- > * 9 0 »

CHLOROFORM I t H O I C H L O R O g T r i r L E N E

UG/KG UU/RO

SEOIMENT SEDIMENT SEDIMENT SEUIHENT SEDIMENT SEUIHENT SEDIMENT SEOIHENT SEDIMENT SEDiHgNT

3 * 5 * 9 l f 2 -TRA i> IS 0 ICML0R0ETMYLENE5 UG/KG SEDIMENT

U T T

U T T

U "O-

U " 0 "

U T J -

U

PAliE Ci

tr

o o

o

011995

COhPLETEO ANALYSIS AEPORT

MWOjkCI NAHEJGEHS LA»<UFILL

> < PA l ' t 14

A E P Q R T O A t e i 8 J / 0 A / 2 7

"PTTTnJETrrTuTTrOTirjTTT

OF rryy —

LABNO PARNO PARAMETER NAME UNITS CHEMISTRY VALUE i. REMARK

6*780 3*54* 3456* 3*37* spn?6-

1.2-DICHLOROPWOPANt i f a - o i C M L O R f l P R O P Y L ^ N e ETHYLBENZENE HETHYLENE CHLOklOE

S UG/KG "5 Ui3/KG S UG/KG

3 4 * 2 1 METHYL CHLORIUE 3 4 * 1 6 METHYL rtSOHIUE 3 4 2 9 0 HROMOFORM 3 4 3 3 0 UlCHLUROBftOMOMETH«N^ 3 4 * > ' l T R I C H L O R O F L U 0 R 0 M E T H I \ N E 3 5 3 3 4 D l C h L 0 3 0 0 1 F L O O f i O H E T H * N E " 3 * 3 0 V C H L O R O O I 8 R 0 M 0 H E T H A N E 3 * * 7 8 I t H A C H L O H U t l H Y L t N t 3**d3 TOLUENE 3448/ IRlCHLURUblHVLENb

UG/KG UG/KG

S UG/KG S UG/KG S UG/KG

SEDIMENT ^EDIME^T SEOHENT SEUIHENT SEDIMENT SEDIMENT SEOHENT

UG/KG ^ E O H t N T S E O H E N T

34*9b 34213

VINYL CHLORIDE ALRULblN

"5 UG/K6 S UG/KG "S UG/KG S UG/KG T UG/KG

SEOIHENT SEOHENT SbUlHENT SEOHENT SbUlHENT SEOHENT SEUIHENI

UG/KG Ub/RU UG/KG SEOHENT

U U

U U 0 U

"IT U 11

3*2U ACRYLONITRILE U

1335 STR4III SOIL SOIL SAMPLE TAKEN BY SPLIT SPOON 4 F I I'bPIH

647B1—wnm—nnrvFir 9 9 9 0 2 BARIUM

H WJ7U M M S / L N Wt^TC

TOTAL TOTAL lUIAL

.700060E-0Z

.H30000

.4U00B0b-01 99'<IJJ 9990* 9990 s 999!l5 9V9'J1 9990 7 VV«2J

LAUHIUH CHROMIUH -cnn3 MERCURY ARSENIC SELtNIUH CUHRUMWl IT

• • • E N D O F P R O J E C T ^ » «

c 2 f

o o

o

Ln as

011996

1>

APPENDIX V AIR & SOIL DATA

SHEETS

C 3 tr

c c I -

c

011997

31 Page 1 of 2

O ity Assurance Sanples (Supplied By Sairpler); Gla^s blank

Drilling Reagent (1/Hole); N/A '

Field Blank (1/Day); Yes ^ Background:

Blank Et>r Spiking; (Surrogate) NMie

None

Quality Assurance Reporting Requirements; As per SQP Spike Sanples (1/10):

Reagent Blank (1/Satch); As per Sop Procedure Blank (1/Batcti)i

Method of Detectic« Limit; Standard Priority Pollutant Recovery;^ Initial/Date Batch Rec

Print Out Requested:_

Reporting Units:

Yes _% Itelative Standard; Initial/Datej Batch RSD

Deviation:

%Relative Range: Initial/Date Batdi RR

Instructions to tab; See below Priority: High . Report Results To; OSC

T.ah U.sed:

Parameter(s):

U.S. EPA, Edison

+ 2 sanples 1602 EP Itoxicity, Corrosivity Priority Pollutant Organics, VGA Organics.

Analysis Method; Priority.Pollutant Standard

Deviaticsis from Standard Method: Nc^e

Shipping;

Shipping Container; Cooler

Packing: Vermiculite, Iced.

Transportation Used: EPA Vehicle

Date Shipped: 24 February .1983

Waybill:_

Maximum Holding Time:_

Date Arrived In Lab:

ML 7 days

48 Hrs. c c

o Ln 00

011998

57 SOIL SAMPLING SHEET

PROGRAM: G.E.M.S.

CASE #

COORDINATED THROUGH: George Zachos, OSC

NAME OF PERSON CONDUCTING SAMPLING: John Bee WITNESS: Tan Hughes

TIME/DATE: 1019 Hr./Feb. 23, 1983 LOCATION: G.E.M.S. Landfill

WEATHER: AMBIENT TEMP: 45 F BAROMETRIC PRESSURE

WIND SPEED/DIR: SE 0-10 REIATIVE HUMIDITY 100% Feb. 23, Overcast Feb. 23, Light Rain

CLOUD COVER Feb. 24, Clear PRECIPITATION Feb. 24, Clear Warm

Chemical cx3or noted on road at Pox Chase II.

LAB ID » 63564,63565,64776 to 64781

SAMPLING INSTRUMENT; Split spocai ID # N/A

SAMPLING PROCEDURE: Split spocxi hand driven with round robin filling of sanple containers.

ROUND RCBIN FILLINGS OF SAMPLE CONTAINERS Yes

DEPTH OF SAMPLE { S j : 0-2" 2-4* (POR WELL CONTRUCTICN AND DEVELOPMENT SEE ATTACHED)

PORE WATER COLOR; Turbid

CCOR: Chemical odor noted

DEGONTAMINATICN BETWEEN SAMPLES; Detergent wash, clean water rinse, air dry

DISPOSAL OF EXCESS SAMPLE/PURGED WELL VOLUMES; N/A

222142 (VDA) CONTAINERS: LOT # ID • 521661 (,16.ounce)

CONTAINERS: 16. pz., tqflcxi seal, glass, screw tc^, and V3A vicds

SUPPLIED BY: Ecology & Eaivirconent, Inc, ^ 2 tr

QC/QA # 521661

PREPARATION OF SAMPLE CONTAINERS: As per Ecology & Environment, Inc. QC Plan.

o o

o LABELLING: Time, Date, Sanpler, Witness, Borehole •, Depth, and Field Data f. *j

SAMPLE PRESEEWATION: Iced

Ul

011999

3^ SOIL CLASSIFICATION SHEET

Project G.E.M.S. Job No. 1038 Sheet of Drill Hole No. Pi

Depth

Sairp le

Split Spoon Blows/ 6 In.

12 18 24

In. SOIL DESCRIPTION

Density (or Consistency), Color Soil Type - Accessories

REMARKS Chemical Conp., Geologic Data, Graond Water, Construction Probl^ans, etc..

1 » -

4'

N/A

70% Light brown, silty, clayey, fine to coarse sand fill with fine medium gravel (2" Tarmac at 10")

Soil sanple #63564 - 0-2",

Soil sanple #63565 - 2'4V

Borehole oonpleted at 4'0".

3 tr

o o

o a\ o

012000

IfV

Page 2 of 2

Fi. J Data Sheets: Yes

Analysis Request Forms; Yes

Chain of Custody; Yes

DOT Labelling: N/A

Copy to OSC; Yes

Weston: Yes

Prior Sanpling Results: See Attached.

Air Monitoring: See Data Attached. Calibration: See Data Attached

Signature:

2

o o

o

012001

SPII CIASSIFICATION SHEET tl

Sheet of Project G.E.M.S. Job No. 1038 Drill Hole No. P2

Depth Ft. Sanp le

Split Spoon

6 In.

6 12 18 24|

In. Rec SOIL DESCRIPTION


REMARKS Chemical Conp., Geologic Data, Ground Water, Construction Problems, etc.,

' I i r I • • II I ,1 •! • •

N/A

100% Light brown silty, clayey, fine to coarse sand fill cxrcasional fine to medium gravel.

Soil sample #64778, 0-4" conposite.

100%

Piezaneter ins ta l led, 5' screen to 5 '3" from GL.

2 tr

o o

o

No

012002

SOIL CLASSIFICATION SHEET lf-7^

Sheet of •oject G.E.M.S. Job No. 1038 Drill Hole No. P3

3epth ?t. Sanp le

Split Spoon

6 In.

6 12 18 24



REMARKS Chemical Ccmp,, Geologic Data, Ground Water, Construction Problems, etc..

N/A

Light brown to dark, gray, fine to coarse sand fill, occasional fine gravel.

No soil sanple

Piezometer installed 0-3'6" fully screened.

2 t r

o o

o LO

012003

f3

Project G.E.M.S.

SOIL CLASSIFICATICN SHEET

Job No. 1038 Sheet of Drill Hole No. P4

Depti:' Ft. San?

1'

T"

3*

4'

le

X

X

X

X

^lit Spoon

6 In.

6 12 18 24

N/A



Light brown silty, clayey, fine to coarse sand fill, with frequent fine to medium gravel

•

REMARKS Chemical Conp., Geologic Data, Ground Water, Construction Problems, etc..

ChCTiical odor noted during.

No soil sanpling

,

Borehole 3'5" (5'0" screen inst.alled) with 1'&' stick-up

Q 3 £->

o o h-l

o

012004

G.ci.M.S.

SOIL CLASSIFICATION SHEET

Job No. 1038

¥f Sheet of Drill Hole NO. P5

Split Spoon

le 6 In.

6 12 18 241



REMARKS Chemical Ccatp., Geologic Data, Ground Water, ConstructicMi Problems, etc.,

N/A

100% Dark gray, sandy, clayed, silty, fill.

Soil sanple #64781 - 0-4' Composite for EP toxicity/ oorrosivity.

70% 3'0" Fine to ooarse sand, orange brown, silty, clayed.

Piezometer screened 0-4" 9** stick-up.

2

o o

o

en

012005

" •• • " PdgTjr of _3_

^ ' AIR MONITORING DATA SHEET ^ - - I - - • • , — — . I I - - . ^— - • ' • ' - —

Da 2 / 2 3 / g 3 S i te Iden t i f i ca t ion ; G . E . O H . t ^ . LCuQol f i l l

Person Sanpling: A. ' Q e ^ V l d d i i C : ^ Qualified By: TATLX EPA__ Other

Meteorological Conditions

Tenperature; " ^ ^ *C/(1F) Wind Speed; CTrr ) ( r Jn Direction:

Barcxnetric Pressure: ^ Relative Humidity; / O O ^

Cloud Cover - Type; ( ^ / o ( j C y l l J Amount: -

Prec ip i ta t ion - Type: A S ? / ^ ^ Amount: ,

Instrument Data

EPA St icker Number: / <=fC) d f "^ Calibrat ion/Service Date: Z / 2 L 2 . /<g[3

Person C a l i b r a t i n g : ' ? H | I C^AVV^ Q C A ^ P ' ^ N Qualified By: TATL^ EPA__

Calibrat ion Da t a : (Q y// r&(Adg> <^'i ppYY^ i X i f J ^ ^ ^ p p n m m e A ^ O A n R . f o

HNU: Type of Probe(s) 9 . 5 , 10.27 11.7 eV (Ci t J l e One) j-^^^^r , ^

Date Lens Cleaned:

OVA: Mode Used :_ j^AJ"V< CAA

Type & Number of Column; N / ( \

Type of Probe :

Filters; (jrcu^lA

LaMotte Inpinger: Specific Kit(s) Used:

Flow Rate(s);

Detector Tubes: Type of O i i t : (Bendix, Draeger, e tc . )

^ i e c i f i c TLibe(s):

T\±»e Lot Number; 2

Tube Expirat ion Date; tr

o o

Number of Punp Strokes/Sanple Volume:

o Radiaticm Meter: Type of Radiation Monitored; *>•

(Tl

SCT Meter: Suspected Contaminants:

012006

\ a C O c K O 0 : ^ 3 S g e ^ o f 3 .

Data Sheet

Exac± Location: LOCC<flOn H

Chemical Wonitored: QPCH. H l' C V G ^ p Q l ^ Amount Measured: 1 " IZ p P ^ ^

Tjjne Started: / / 3 Q ^jCoJe. Q - C) ppW->

Exact Location; j-OCCAi'l O O /I ' '

Chemical Monitored; m e^rJAQJniL ^r~C\CJr\ C iC) ATi unt Measured: 1 - ^ n'f^Yr)

Time Started: f j-g / ^ ' i jCpJe. C " I P p t > ^

Exact Location; L^C.<:>^/OO ^ ,

Chemical Monitored; OKTTrU^ / Cll VCXpO/"^ Amount Measured; tZ.-" J(o O t P P ^

Time Started: I 1^5 \ . ^CCUe, O - / Od p p V ^

Exact Location: L.^^^^ô4ldfl S .

Chr 'cal Monitored: ry\£,iHnCU^^dj, ^YriXCJn C:>C Anount Measured: 1 " " ^ p)&^h^

Time Started: I I H S ' , ^CCXê, O ~ I Cpp-iOyy,

Exact location: LcxloJl On C

Chemical Monitored; (^yX^'Qjj/^ j C VCx:ÔOr:^ Amount Measured: Z O ~" ^ O p/pV^

Time Started: J / 5 5 , 3CC>vle, 6 — \00 PpiTr

JL,

Exact Location: j jQCS^ ' t l 0 1 ^ ^

Chemical Monitored: y ^ ^TJOJOLAQg, PyiÔhi <lS/ Amount Measured; S —/Q f ? p / ^

Time Started; I f ^ S âCCLl^^ 6 - / O Q ^C^

- T ^ ^ • / CT? • . I J / ^ \ GML 0 0 1 0 4 6 7 Exact Location; 7^ j ( ^ ^ J T ' ./Q OcVg. / i Q f C ^ ^ _ _ _

Chemical Monitored: C>i^C (AQ / VO piaf^-<^ Amount Measured: .> lOOQ ^jiQ/v^

Time Started; / Z 3 0 ^ ' S o o k l ^ O - / e X > 0 p p l r ^

^ o.\\ ^vSôrs- êxc€i3-l' yvu -VUcxn-e fH\a^^ <^^^

cxDôo. ^ ^^V-hoê ^cbtcîon 012007

Data Sheet

E> t Location: 1>± / " / - ^ '}/) bc^r^ holc.^

Page 3. of 3

. f7 Chemical Monitored; yYyL-'/^CiAr'Xf _ / v g v C-j"! 0/r^ Amount Measured; jQ — ZO p ^

Time Star ted: 12-3 O , ^ C C U e / - / Q O O p p

Exact Location: 7 ^ ^ { / - R - c U p O r ^ . , h o r ^ h C / ) - ^ ^

Chemical Monitored: Q/^C C%V) \ C. VCxy^'^'X^C^ Amount Measured; 7 * 1^ jfyf.

:^x3=U4^' . O - / Q ^g2^/»l Time Started; J Z S S

Exact Location: 7 ^ ^ ^ \ / / T ^ / n l O P r C . h O l -C^

Chemical Monitored; ^>^CCXy7 / d VCXJkDOC^ Amount Measured; > /OC^O O i ^

'_ "^S>cz.oj2,i' o " / O O P p ^ Time Star ted; / :^ . " ^ O

Ebcact Location; Tz. (^/' f i - Cuhov^ hc^r-c ho /^^ Chemical Monitored; Oy^j^JutQ / C [ / " ( X ^ Q ^ - S Anount feasured; "? — / O f^iZ

Time Started; / 3 3 0 . ' -^C^cJUL'. / — / Q ^pp>^

Exact Location; 7 ^ 3 / W F-A / / ^ h O T ^ ^ h o U l ^ ^ ^ f j l l e c ^ ^ / ^ '

Chemical Monitored; OrXZ C^MlI C- yCi^^B^fZ^ Anount Measured; '7.— ^ p p ) / ^

Time Star ted; J S 3 0 ^CL<oJC'. / - / 6 p p r ^

Exact Location: ^ 3 1 ^ ahoY^ hor-^ hol^ Chemical Monitored: / S 3 > Q

Time Started; _- •

Amount Measured: 3 " ^ (pp^^^'^

3Ctxk: ' • ^ ^ / C j:>prn

Exact Location:

Qiemical Monitored:

Time Started;

Anount Measured;

c 2 tr

o o

o <3\ 00

012008

. ' ^ Ptige of

. 1 ' AIR MONITORING DATA SHEET ^ — — - I I— • - . . — — — I — . -

Da*^-: a / z S / S a . S i t e Iden t i f i ca t i on ; S E / ^ l ^ S , L c U i r J f i H

Person Sanpling; £" 7 5 / g v . ^ a r : . ^ (^jalified By: TATLxf EPA Other_


Tenperature; ^ ^ *C/VF) Wind Speed; Q yriOV) Direct ion;

Barometric Pressure; Relat ive Humidity: / < 0 ( ^ ^ n

Cloud Cover - Type; ^ l o l J \ (j)[A Amount; .—

Prec ip i t a t ion - Type; t^CAir\ Amount; ,

Instrument Data

EPA St icker Number; . ( Q 7 '^(o Z ' Cal ibrat ioi \ /Service Date; Z / 2 ^ / g 3

Person Cal ibrat ing; £ c t CB>IO-^ OS" Qualif ied By; TATLX EPA

Cal ibra t ion Data; / ^ g f c / S i B % n ^ ^ - H n O J ^ e ^ C ^ ^ 1 1 2 p ^ ^ ^ ^ n

HNU: Type of Probers) 9 . 5 , 10 .2 , 11.7 eV (Ci rc le One) " ^ - O

Date Lens Cleaned: ' — . '

OVA: Mode Used; — - - • — - - . . . . • _ . 1 - ^ ,

Type & Number of Column;

Type or Probe ;

Filters; ,_-

LaMotte Inpinger; Specific Kit(s) Used:

Flow Rate(s);

Detector Tubes; Type of Uni t ; (Bendix, Draeger, e t c . )

^sec i f ic Tube(s) :

T\jbe Lot Number;_ , _^ 3 ' t-

Tube ExpiraticDn Date; ^ ^ c

Number of Punp Strokes/Sanple Volume;

Radiation Meter; Type of Radiation Monitored: j 0^

SCT Meter; Suspected Contaminants:

^ ^ ' ^ " 012009

Data Sheet

E3 t Location; S l ^ € - A

Page 2 of _^

Chemical Monitored; C o rV)bM.f? | - l 'b id , C O . ' ^ / Q z . Amount Measured; Ci^a \B-L Izf^k

Time S t a r t ed ; / / 3 O

Exact Location; ^ H ' C . ^

Chemical Monitored; C C i Y r \ h i A ^ s i i h k . Q y C k s / 0 2 ^ . Amount Measured; O ^ f n l ^ L l Z l %

Time S ta r t ed ; II H ^ . - .

Exact Location; ^ / T t g , d .

Chemical Monitored; C^yyii 'b}y^=^h^JL <ZG!^ / O Z . Amount Measured; Q ^ ^ l ^ ^ U n % (

Time S t a r t e d ; / / 6 ^ ^ ^ ~- -

Exact Location; 7 ^ / ( I P-h fQ j p O n g , h o l ^ J

Chemical Monitored; C O J ^ J ^ L A S H l - i lc C g ^ S / O ? Amount Measured; Cpr^ lBi l - fA^c , C

Time S ta r t ed ; / Z 3 0 :

Exact l oca t ion : P / / / f h c J ^ O V t . h C r ^ h r ) L e . ^

Chemical Monitored; C P y y ) / L x ^ S & C ^ M ^ ' - ^ ^ ^ O ^ / O z , Amount Measured; ( ^ L B L J T A %

Time S t a r t e d ; / 2 . 3 0 - •

Exact Location; V ^ Z (^ / :ff- / / ? b O n ^ / n C ) b S )

Chemical Monitored: r r ^ i A n L j t A ' ^ H L y U ^ C C K ' ^ / O ? . Amount Measured; 0 % J P I J Z l ^ o C

Time S ta r t ed : f 3 ^ d i T I l - — _ '^' ' '* ~

Exact Location; ^ D Z ^ / " Q " C i U o V < . I p O r e h o l j ^ ^ ^

Chemical Monitored: O0>ry^ h ^ / > f ^ 4 ' O d i : ^ \ S ^ C C ^ ^ /^"Z- Amount M e a s u r e d ; Q * ^ j ^ j j Z \ ^

Time S t a r t ed ; 1 3 ^ 3 0 -.\.-- -

GML 001 0470

012010

Data Sheet

Page S of J^

D t l o c a t i o n : V S ( I ' ' C k h o v O . l r )C»^ , . h k ^ ^ - U ( ^ b ^ I ' / l c c J L O / i

Chemical Monitored; CO'/yi f j lA<jh t I n i j Q ^ C A ^ / O 2 Amount Measured; Cf?/, j ^ L J Zf/

Time S t a r t e d ; f S S O

Ebtact l o c a t i o n ;

Chemical Monitored;

Time S t a r t ed ;

Exact l o c a t i o n :

Chemical Mcwiitored;_

Time S t a r t e d ;

Amount Measured;

Anount Measured:

Ebcact Location;

Chemical Monitored;

Time S t a r t e d ;

Amount Measured:

Exact Ixxration;

Chemical Monitored;

Time S t a r t e d :

Exact Location:

Chemical Monitored:


Amount Measured:

Amount Measured:

Exact Location:

Chemical Monitored:


Anount Measured;

r

c c

012011

ro.je ( of ^

.^ AIR M0NIT0RI>3G DATA SHEET C ^ \

Date; Z . / ^ ^ / * S 2 s i t e I d e n t i f i c a t i o n : ( ^ • € . fKYTS. L c ^ . J ^ ' I j '

Person Ssapling? 1^, r ^ l a j m C i r ' Qual i f ied By; TATEX E:PA__ Other

Meteorolcqical Conditions

Tenperature; HO 'C/CJ) Wind Speed; ^ " f O V^pk Direc t ion; N

Barometric Pressure; -^ - ^ Rela t ive Humidity; fj^L,J>:_

Cloud QaMer - Type; C.I ^ Q ^ Anount; - "" ^ ; _

Prec ip i ta t icx i - Type; / ) ^yZSL^ Amount; ~ *--

Instrument Data

EPA S t i c k e r Number; . / (7 7 g Cg 2 . Ca l ib ra t ion /Se rv ice Date; Z . / z t > l ^

Person Cal ib ra t ing ; ^ . 'SlC^^^C-.^ Qual i f ied By; TATL EPA__

Ca l ib ra t ion Data; rCJZ^C) Z S % / y y u ^ O ^ q ^ ^ e, ^^-J2^, . ^7 t7f> ( H ? UDj-Hv

HNU: Type of Probe(s) 9 . 5 , 10-2 , 11.7 eV (Ci rc l e One) O ^ .

Date Lens Cleaned: ^ , — •* - ^

OVA: Mode Used;

Type & Number of Column;

Type ofProbe;^ «..

Filters; , _ - ..^—. .

LaMotte Inpinger; Speci f ic K i t ( s ) Used:

Flow R a t e ( s ) ;

Detector Tubes: Type of Dn i t : (Bendix, Draeger, e t c . )

Specific Tube ( s ) ; 3

Tube Lot Number: , " o

Tube Expi ra t ion Date: ^ o

Number of Punp Strokes/Sanple Volume; o - J

Radiation Meter; Type of Badiatic»i Monitored: to

SCT Meter; Suspected Qxitaininants:

012012

Page of

Data Sheet ^ 2 -

E> t Location; L o C.oJP\ C O ^

Chemical Mcaiitored; C O ^ i b - d A r ^ L p l g c n < . / Q ? Amount Measured; C>% I ^ L / ^ ^ %

Time S ta r t ed ; 0 9 3 Q .^___

Exact l oca t i on : / , 0 Cc:7>..f'-) C O

Chemical Monitored; CjQ r ^ h W ^ h ' } ^ > l ^ ^ ^ / Or? Amount Measured; O ^ r . L ^ f / Z \ ^ f

Time S ta r t ed ; < 3 9 3 ^ - _-.-

Exact Location; T H ^ Z ' C L h c > V ^ hC:>U^ . j k o U ' ^ I ' / U . C P ^ J H ^ {/^(k'^<S[)

Chemical Monitored; CQy^Vj 1^ -^jp'i l^At < ^ a ^ / O ? ^ Anount Measured; C f ( ( i ^ L l t \ ^

Time S ta r t ed ; l O W ^ '_ " - -

Exact Location; P ^ ( Z ' " a k > 0 ] / - ^ InC^Lp ^ hC> U ^ ' I U Z J C ^ L J / fU U X ^ ' h ^ ' ^

Chemical Itonitored: C O n ^ l ^ ^ ^ \ ^ h i 1 >A <:&.<> I O ^ Amount M e a s u r e d ; 0 % L E L I L I */

Time S ta r t ed ; / V ^ Q ^

Exact loca t ion ;

Chemical Monitored;

Time S ta r t ed ;

Anount Measured;

Exact loca t ion :

Chemical Monitored;

Time S ta r t ed :

Ebcact Location:

Chemical Monitored:

Time S ta r t ed :

Anount Measured:

Amount Measured;

2

o o

o

012013

Pjge_j_ of Z.

AIR MONITOFOhiG DATA SHEET X ^

Daf t Z/Z¥/^P, S i t e I d e n t i f i c a t i o n ; (Q - 6 » OO . S . (jgUA(^^,' H

Person Sanpling; fj . 'E)^y\ C d L C V Qualified By; TATLjN EPA Other


Tenperature; •VQ ' C / ^ Wind Speed; .g"— / p h ^ p l ^ Direct ion; /Q

Barometric Pressure; ^ Relat ive Humidity; / Q U ^

Cloud Cover - Type; ^ ^ / € . 0 ^ Anount; .

P r e c i p i t a t i o n - Type; /? O / 'T-^ ^ Amount;

Instrument Data

EPA St icker Number; . 1 ^ ^ 0 0 1 7 ' Cal ibra t ion/Service Date; 2 / Z Z / ^ 3

Person Cal ibra t ing(P, CL-GA/ys r X X C t h O s Qualif ied By; TATLX EPA_

Calibration Data; Oy^. - y^f^(^_< ' J^^^^ ^ ^ ^ } ^ J^^ P F ^ vnj^^U^J^l^

HNU; Type of Probe(s) 9. 9 .5 , 10 ,2 , 11.7 eV (Ctlrcle One) ^ ^

Date Lens Cleaned;

OVA; Mode Used; S L A T V €M Type & Number of Column; j O / A

Type o r Probe;^ "•_

Filters; K J / A

LaMotte Inpinger; Specif ic K i t ( s ) Used;

Flow R a t e ( s ) ;

Detector Tubes: Type of Dni t : (Bendix, Draeger, e t c . )

^ e c i f i c TUbe(s):

l\jbe Lot Number:

Tube Expi ra t ion Date: 2 tr

o Number of Punp Strokes/Sanple Volume; o

Radiaticxi Meter; Type of Radiat ion Monitored; ^

SCT Meter: Suspected Contaminants: ; *.

012014

Data Sheet

Page 2-of 2.

r^ E: t Location; UOCCX.-h) Q Q T ^

Chemical Monitcjred: Q r C C u ^ / ^ y r V r ^ i o O ^ - ^

Time S t a r t ed ; 0 < 9 . ^ 0

Amount Measured; / — Z p f ^ y y n

/ y ^ Exact l oca t i on ; L ^ O C O c H Q / ^ ^

Qiemical Monitored:

Time S ta r t ed ; Qgjf 3 ^

Amount Measured: / ~ 2 . , ^ Ip^p'v^

S C C U C ' I - I P P ^ Y : > * ^

Exact Location; "P H ( l ' ' r.L^V^ h0.rC hOk, ^ InCsiC ^HUcI K)f"fta

Chemical Mcxiitored; Cl/^CC^AQ I C VGADO C S Anount Measured: fj P P " ' ^ ^

Time S t a r t ed ; / (^ U - ^

Exact Location; ^ 5 ( 2 ^ C ^ ^ V t . hOr€ . ho lc , hoje. ^ I UjCP ivi{^ \k

Anount Measured; S ~ 1 p'p^y^^ Chemical Monitored:_Q>;^^V2s4aL£-:J^i^42Di:^

} H ^ b Time Started; / - /o

Exact location:

Chemical Monitored:

Time Started:

Pfy^.

Amount Measured;

Exact Location:

Chemical Monitored:

Time S ta r t ed :

Exact Location:

Qiemical Monitored:


Anount Measured:

Anount Measured;

o 2

o o

o

-J Ul

012015

^

APPENDIX VI PHOTOGRAPHS

O 2

o o

o

01201G

4 : , :.

Photo #1 I #1- Briar Lake area, location P4, February 24, 1983. TAT members in level "B" protection collecting a "split spoon"

sample. At left is the PVC cas/*>,-which is inserted into the ground prior to the installation of the PVC slotted piezometer pipe.

-' .*>i.:V4^

Photo #2- Briar Lake area, location P4, February 24, 1983. Same view as photo #1. In this picture the two MSA air

sampling pumps with carbon sphere collector tubes are collecting air samples for volatile organic compounds. At center is the PVC slotted piezometer pipe. ^ 0120"* ''

^*^f^

!?<»^,^'^

Photo #3- Briar Lake area, location P5, February 24, 1983. Installation of PVC cas/./< prior to installation of PVC

slotted pipe. Behind the culvert pipe is where two MSA air sampling pumps were located for volatile organic compounds. The gentlemen in the ic^icground is wilth the Camden County Dept. of Healtl"

' 5.-

. * * * > • ^ • . ' • * • » »

: i ^ I

Photo #4- Briar Lake area, location P5, February 24, 1983. TAT members clean the split spoon sampler. Clean-up consists

of detergent wash, clean-water rinse and air drying. PVC slotted pipe and PVC casi»'o can be seen rtn center of photo.

^ 012018 am •P 1

Si

1 Subject: 5"^/

' Date and Time Photographer: Witness : Shutter Speed Lens Opening: Dista:!ce Settj Type of Film:

C SAM/' l , r '^<^

• ^ - J V - P - 3 r . 75 L / i , - ^ / z .

A . 'b(E.rî^Z>tt.T ZS-o /="//

.ng: ^ O O r4 r ^

^ t

t i o t A ^

Subj ect: / ) ' .-a- ^ ^ ' - > ' ^ ^ ^

Date and Time: 2 - 2 ' / - • ^ 3

Jif 2

JZa<? * — Photographer: C ' S u ' * ^ ' ^ ^ Witness : /? • •^Skj£7»<:7 Shutter Sceed: P n Lens Opening;: t S"<? ' Distai ce Setting: — Type of Film: i^to/^SA i

Subject: rs- p/Ci^rêreTz. ^ J

^ - ^ < f ' i ' 3 Date and Time: Photographer: W i t n e s s : / } , 7h£ni£'irC'7~

/ 6 / S ' £ . 7SU^K/«e-

Zô r n

S h u t t e r Speed: Lens Opening: . Dis ta : ice S e t t i n g : Type of F i lm: ^ <o O i^SA

S u b j e c t : p j - J>w/*.^r

Date and Time: P h o t o g r a p h e r : V/ i tness : A.

^ - a^/Z/i^tg. "StEiêh.

Z s a Shutter Speed: Lens Opening:

5 Distance Setting: — / ^ / /

\ T/pe of F i lm: ^ c O r^SA

\

o 2 tr"

o o

o

012019

air & soil sampling program, february 23 and 24, 1983, fox

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