SDMS Document
105209
COMPARATIVE REVIEW OF SPLIT SAMPLE DATA
REMEDIAL INVESTIGATION CORTESE LANDFILL
Work Assignment: C02067 (Ref. No. 1-635-200)
Prepared for: U.S. Environmental Protection Agency
Contract: 68-W9-0003
TRC TRC Environmental Corporation
300802
l ^ p p H ^ ^ g ^ 291 Broadway, Suite 1206 M flVl^T New York, NY 10007
g g ^ ^ ^ f o r m e r l y Alliance Technologies Corporation -ff (212) 349-4616 Tor- c • I 1 / - i- Fax (212) 349-4648 IKL hnvironmental Corporation .
HAND DELIVERY
January 10, 1994
Erwin Smieszek Regional Project Officer U.S. Environmental Protection Agency Emergency and Remedial Response Division 26 Federal Plaza, Room 737 New York, NY 10278
Reference: Contract No. 68-W9-0003, TES 6 Work Assignment No. C02 067 Cortese Landfill RI/FS Compliance Oversight (Ref. 1-635-200)
Subject: Deliverable - Comparative Review of Split Sample Data
Dear Erwin,
In accordance with the reporting requirements of the subject Work Assignment, enclosed is the Comparative Review of Split Sample Data for the Cortese Landfill. This submittal satisfies a deliverable requirement for this Work Assignment. This deliverable is being submitted before the due date of January 12, 1994.
At the request of the WAM, Mark Granger, a copy has been delivered directly to him.
Questions regarding this submission should be directed to the TRC Project Manager, Jeffrey Healey, at (508) 970-5600, or me at (212) 349-4616.
Sincerely,
Douglas Sullivan Regional Manager
DS/cs
CC: Mark-Granger/EPA Work Assignment Manager Jean Poovey/EPA TES-6 Contracting Officer (letter only) Jeffrey Healey/TRC Project Manager TES ZPMO (letter only)
offices in Alobcma, California, Colorado, Connecticut. Illinois, Louisicnc, Masscchusetts, New Jersey, New York, North Carolina, Pennsylvania, Texas, Wosfi ington, Washington, D .C, end P-jerro Rico A TRC Componv
™- = 300803
COMPARATIVE REVIEW OF SPLIT SAMPLE DATA REMEDIAL INVESTIGATION
CORTESE LANDFILL
Prepared for
U.S. ENVIRONMENTAL PROTECTION AGENCY Emergency and Remedial Response Division
26 Federal Plaza New York, New York
Work Assignment No.:
EPA Region:
EPA Site/Facility ID. No.:
Contract No.:
TRC Document No.:
TRC Project No.:
TRC Project Manager:
Telephone No.:
Subcontract No.:
Subcontractor Project Manager:
Telephone No.:
EPA Work Assignment Manager:
Telephone No.:
Date Prepared:
C02067
n NYD980528475
68-W9-0003 (TES 6)
NY-067.RP5
1-635-200-0-2PX9-0
Jeffrey Healey
(508) 970-5600 ext. 5224
N/A
N/A
N/A
Mark Granger
(212) 264-9588
January 7, 1994
TRC ENVIRONMENTAL CORPORATION 291 Broadway, Suite 1206
New York, New York 10017 (212) 349-4616
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TABLE OF CONTENTS
Section Page
1.0 INTRODUCTION 1
2.0 OBJECTIVES 3
3.0 SPLIT SAMPLE COMPARISON PROCEDURE 3
4.0 RESULTS OF DATA COMPARISON ANALYSIS 4
5.0 CONCLUSIONS AND RECOMMENDATIONS 7
Appendices Page
A Data Comparison Analyses A-1
TABLES
Number Page
1 Cortese LandfiU - Summary of Split Sample EPA Identification Numbers 2 2 Cortese Landfill - Split Samples Displaying Inadequate Comparability 6
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1.0 INTRODUCTION
The U.S. Environmental Protection Agency (EPA) has requested that TRC Environmental Corporation (TRC - formerly Alliance Technologies Corporation) to provide technical oversight assistance to EPA with respect to the Remedial Investigation/Feasibility Study (RI/FS) activities being performed at Cortese LandfiU, Narrowsburg, Sullivan County, New York. TRC performed this work under Contract No. 68-W9-0003 (TES 6), Work Assignment No. C02067. The investigative work was performed at the Cortese Landfill by Golder Associates, Inc. of Mount Laurel, New Jersey (Golder).
As directed by EPA, TRC obtained a total of 12 split samples (7 soil/sediment, 3 ground water and 2 surface water samples) at Cortese Landfill during the sampling period of April 13, 1993 through April 20, 1993 and June 7 to June 10, 1993. The results of these activities are described in TRC's oversight progress reports dated July 2, 1993. AU split samples were obtained in accordance with TRC's EPA-approved Remedial Investigation (RI) and Site Investigation (SI) Oversigiit Work Plan/Quality Assurance Project Plan (Work PlanlQAPjP) dated March 1993.
This comparative review of split sample data compares the EPA/TRC analytical data with Golder's analytical data for the Remedial Investigation. A total of three ground water spUt samples were collected from monitoring weUs MW-IB, MW-2B, and MW-6B and one subsurface soil split sample from boring SL-1 located near the eastern septage lagoon, two split sediment samples from SS-13 and SS-15 within the Cortese landfill property boundaries, two spUt surface water and their respective sediment samples from SW-ll/SS-21 and SW-12/SS-22 located in White's Pond, and three sediment split samples designated as R2-05, R3-07, and R4-12 from three reaches along the Delaware River.
Ground water and surface water split samples were analyzed through the Contract Laboratory Program (CLP) for Target Compound List (TCL) volatile organic compounds by low concentration, TCL semi-volatiles (including BNAs and PCBs/pesticides) and Target Analyte List (TAL) metals and cyanide. ShaUow soil and sediment samples were analyzed for TCL VOCs, pesticides/PCBs and for TAL inorganics (metals and cyanide). VaUdation of the EPA/TRC data set was performed in accordance with Region n guideUnes described below:
• Organics: SOP No. HW-6, Revision #8, CLP Organics Data Review and Preliminary Review, January 1992.
Inorganics: SOP No. HW-2, Revision #11, Evaluation of Metals Data for the CLP (based on SOW 7/88, Rev. 2/89), January 1992.
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TABLE 1. CORTESE LANDFILL - SUMMARY OF SPLIT SAMPLE EPA IDENTIFICATION NUMBERS
Sample Location (Deptii)
1 MW-IB
1MW-2B
| M W - 6 B
1 SW-11
1 SW-12
|sS-13(0-0.5')
:[sS-15(0-0.5')
|sS-21(0-0.5')
|sS-22(0-0.5')
|sL-l(3-3.5')
|R2 -05 (0 - .5 ' )
|R3 -07 (0 - .5 ' )
|R4 -12 (0 - .5 ' )
Date Collecled
04-14-93
04-15-93
04-15-93
06-08-93
06-09-93
04-15-93,
04-13-93
06-08-93
06-09-93
06-09-93
06-10-93
06-10-93
06-10-93
1 Malrix
ground water
ground water
ground water
surface water
surface water
soU
soil
sediment
sediment
sediment
sediment
sediment
sediment
Voiatlles
vSB3543^
SB3544
SB3545
SB3547
SB3548
BGE90
BGE91
BGE88
BGE92
BGE93
BGE85
BGE86
BGE87
BHAs
BGE78
BGE79
BGE80
BGE83
BGE82
BGE90
BGE91
BGE88
BGE92
BGE93
BGE85
BGE86
BGE87
1 Fest./PCBs
BGE78
BGE79 (
BGE80
BGE83
BGE82
BGE90
BGE91
BGE88
BGE92
BGE93
BGE85
BGE86
BGE87
Isorganks
(MBHL78"'
^MBHL79^|
MBHL80 1
MBHL83 1
MBHL82 1
MBHL90 1
MBHL91
MBHL88 1
MBHL92 1
MBHL93
MBHL85 1
MBHL86 1
MBHL87 1
BNAs - Base-Neutral Acid-Extractabies Pest./PCBs - Pesticides/Polychlorinaied Biphenyls
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AU validated TRC data has been approved by the EPA Region n Monitoring Management Branch (MMB). A complete cross reference Ust of spUt sample locations and parameters analyzed, along with their respective EPA sample identification numbers, is presented in Table 1.
2.0 OBJECTIVES
The primary objective of this spUt sample coUection and data comparative analysis is to quantitatively compare analytical results obtained by Goldeir's laboratory(s) with the results obtained by EPA/TRC through the CLP to determine if data useabiUty problem(s) exists with Golder's data set.
As directed by EPA, additional objectives established for this data comparative effort are as follows:
• to evaluate whether Golder has reported aU analytical data for spUt samples and, if data have been omitted, whether Golder has cited reasons for these omissions;
• to evaluate whether data compares favorably or unfavorably including an analysis of cases where: (1) the EPA/TRC data reflects significantiy higher concentrations than those reported by Golder, (2) the contaminant of concern for that particular site is involved, or (3) the data discrepancy is a result of sampling problems noted during TRC's oversight effort; and
• to evaluate the data comparison results in light of the overaU conclusions of the RI report and the regulatory framework for the field investigation program.
3.0 SPLIT SAMPLE COMPARISON PROCEDURE
EPA has not pubUshed guidance pertaining to the quantitative comparison of spUt samples which are analyzed by two different laboratories. Consequendy, TRC has developed a comparison procedure that calculates the relative percent difference (RPD) of detected compounds in each data set The RPD is calculated by taking the absolute value of the difference between the two concentration values and then dividing this value by their average. This value is then multiplied by 100. A quantitative comparability goal, which originated from Region II data vaUdation guidance for the evaluation of field dupUcates, is then appUed to the calculated RPD to evaluate the comparabiUty of the spUt samples. The comparabiUty goal for organic results and inorganic results equal to or above five times the contract required quantitation limit (CRQL) for organics and five times the contract required detection limit (CRDL) for inorganics, is-a RPD of 50 percent for water samples and 100 percent for soil samples. For inorganic results where one or both spUt sample results are below five times the
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CRDL, the comparabiUty goal is an absolute difference of less than the CRDL for water samples and less than twice the CRDL for soUs.
For resiUts that were outside the quantitative comparabiUty goal, professional judgement was used to determine if a data useabiUty problem existed. GeneraUy, data would be considered to have a useabUity problem if the foUowing additional conditions were encountered: (1) if one or both results were above the CRQL/CRDL and were outside the comparabiUty goal; (2) if the compound or analyte was detected by EPA/TRC at a concentration above the CRDL and was not detected by Golder's laboratory; and (3) if the EPA/TRC result was significantly greater than the Golder result.
4.0 RESULTS OF DATA COMPARISON ANALYSIS
Quantitative analytical data comparisons for spUt samples obtained at the Cortese LandfiU are presented in Appendix A. Data comparisons for soU and sediment samples coUected are presented in Tables A-la (volatUe organics). A-lb (semi-volatile organics), A-lc (pesticides/PCBs) and A-ld (inorganics). Data comparisons for ground water and surface water samples collected are presented in Tables A-2a (volatUe organics), A-2b (semi-volatUe organics), A-2c (pesticides/PCBs) and A-2d (inorganics). Results of the spUt sample comparison results are discussed below.
The overaU data comparabiUty for soU/sediment analysis at the Cortese LandfiU site was generaUy acceptable. As indicated in Table 2, TRC determined 9 of the 32 soil/sediment split sample data sets to have inadequate data comparability. A brief description of the incomparable analyses is provided below.
• Methylene chloride was detected by EPA/TRC in one sediment spUt sample, SL-1, at 88,000 micrograms per kilograms (ug/kg) and Golder detected this analyte at 9,600 ug/kg resulting in an RPD of 161.
• Acetone was detected in five of the soil/sediment spUt samples (R3-07, R4-12, SS-22, SS-13, and SS-15) by EPA/TRC at concentrations ranging from 6 ug/kg to 32 ug/kg. The Golder analysis at these locations did not detect this analyte.
• Phenanthrene was detected in one sediment spUt sample at R3-07 by EPA/TRC at 200 ug/kg and detected at 62 ug/kg by Golder resulting in an RPD of 105.
• Dieldrin was detected at one subsurface spUt soU sample SL-1 by EPA/TRC at 19 ug/kg and detected by Golder at 3.6 ug/kg resulting in an RPD of 136.
• Methoxychlor was detected at SS-13 by EPA/TRC at 27 ug/kg and this analyte was not detected by Golder.
• Chromium was detected at two soil/sediment split samples, R4-12 and SS-21 by EPA/TRC at 13 milUgrams per kilograms (mg/kg) and 10.5 mg/kg and
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Golder detected these analytes at 5 mg/kg for both samples resulting in an RPD of 89 and 71, respectively.
• Copper was detected at two soil/sediment spUt samples, R4-12 and SS-15, by EPA/TRC at 26 mg/kg and 48.4 mg/kg and Golder detected these analytes at 5.8 mg/kg and 14 mg/kg resulting in an RPD of 127 and 110, respectively.
• Lead was detected at two soil/sediment spUt samples, SS-21 and SL-1, by EPA/TRC at 4.3 mg/kg and 33.4 mg/kg and Golder detected these analytes at 1.9 mg/kg and 4.6 mg/kg resulting in an RPD of 77 and 152, respectively.
The overaU data comparabUity for ground water and surface water analysis at the Cortese LandfiU site was generaUy acceptable. As indicated in Table 2, TRC determined that 5 of the 20 ground water/surface water spUt sample data sets have inadequate data comparabiUty. As discussed in the Cortese LandfiU RI Report and TRC's Field Oversight Report, Golder did not sample for PCB/pesticides in any ground water weUs. PCB/pesticide results for EPA/TRC ground water spUt samples were all non-detections. A brief description of the incomparable analyses is provided below.
Chloroethane was detected by EPA/TRC in MW-IB at 4 ug/L and was not detected by Golder.
1,1-Dichloroethane was detected by EPA/TRC in MW-IB at 13 ug/L and was not detected by Golder.
1,1,1-Trichloroethane was detected by EPA/TRC in MW-IB at 2 ug/L and was not detected by Golder.
Trichloroethene was detected by EPA/TRC in MW-IB at 1 ug/L and was not detected by Golder.
Benzene was detected by EPA/TRC in MW-IB at 9 ug/L and was not detected by Golder.
1,3-Dichlorobenzene was detected by EPA/TRC in MW-IB at 3 ug/L and was not detected by Golder.
1,2-Dichlorobenzene was detected by EPA/TRC in MW-IB at 5 ug/L and was not detected by Golder.
Phenol and 4-methylphenol was detected by EPA/TRC in SW-11 at 27ug/L and 75 ug/L, respectively and were not detected by Golder.
Chromium was detected by EPA/TRC in MW-IB and MW-2B at 13 ug/L and 38 ug/L, respectively, and was not detected by Golder.
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TABLE 2. CORTESE LANDFILL - SPLIT SAMPLES DISPLAYING INADEQUATE COMPARABILITY
Sample Location (Depth)
1 MW-IB
1MW-2B
| M W - 6 B
1 SW-11
1 SW-12
|sS-13(0-0.5')
|sS-15(0-0.5')
|sS-21(0-0.5')
SS-22(0-0.5')
SL-l(3-3.5')
R2-05(0-.5')
|R3-07(0-.5 ')
|R4-12(0-.5 ')
Dale Coaected
04-14-93
04-15-93
04-15-93
06-08-93
06-09-93
04-15-93
04-13-93
06-08-93
06-09-93
06-09-93
06-10-93
06-10-93
06-10-93
Matrix
ground water
ground water
ground water
surface water
surface water
soU
soU
sediment
sediment
sediment
sediment
sediment
sediment
VoJatries
X
X
Bf As
X
X
FestJPCBB
X
X
Inorganics
X
X
X
X 1 X 1
1 X X
X 1
BNAs - Base-neutral acid-extractables. X - The split sample data were not comparable.
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Arsenic was detected by EPA/TRC in SW-12 at 52.1 ug/L and was not detected by Golder.
• Cyanide was detected by EPA/TRC in MW-IB at 11 ug/L and was not detected by Golder.
5.0 CONCLUSIONS AND RECOMMENDATIONS
A total of three ground water spUt samples were coUected from monitoring wells MW-IB, MW-2B, and MW-6B and boring SL-1 located near the eastern septage lagoon, two split sediment samples from SS-13 and SS-15 within the Cortese landfiU property boundaries, two split surface water and their respective sediment samples from SW-ll/SS-21 and SW-12/SS-22 located in White's Pond, and three sediment spUt samples designated as R2-05, R3-07, and R4-12 from three reaches along the Delaware River.
Each of these spUt samples were analyzed for volatUe organic compounds, BNAs, PCBs/pesticides, and inorganics. The results of these analyses indicate that 14 of the 52 sample data sets were not comparable. The majority of the non-comparable results were from the inorganic analyses. Based on the results of the comparison analysis, the foUowing recommendations are made:
• All analyses exhibiting inadequate comparability should be confirmed for acciuracy by Golder.
• EPA should note the above analytical discrepancies for future users of the Golder data set
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APPENDIX A
DATA COMPARISON ANALYSES
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Table A-1 a SPUT SAMPLE COMPARISON - CORTESE LANDFILL VOLATILE ORGANICS IN SOIUSEDIMENT (ug/Kg)
Page 1 of 3
Mm RPD mmm RPD i»-i2 RPD
o o 00
00
Chloromethane Bromomethane
Vinyl Chloride Chloroethane Methylene Chloride Acetone Carbon Disulfide 1,1-Dichloroethene
1,1 DIchloroethane 1,2-Dichloroethene (total) Chloroform 1,2-Dichioroethane 2-Butanone 1,1,1 -Trichloroethane Carbon Tetrachloride Bromodichloromethane 1,2-DichlorQpropane cis-1,3-Dichloropropene Trichloroethene Dibromochloromethane 1,1,2-Trichloroethane Benzene trans-1,3-Dichloropropene Bromoform 4-Methyl-2-Pentanone 2-Hexanone Tetrachloroethene 1,1,2,2-Tetrachloroethane
Toluene Chlorobenzene Ethylbenzene Styrene Xylene (total)
EPA/TRC PRP EPA/TRC PRP
BGE85
11 U 11 U 11 U 11 U 16U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U t l U 11 U 11 U 11 U 11 u 11 u 11 u 11 u 11 u 11 u 11 u
BGE86
13 U 13 U 13 U 13U
17 UJ 18 UJ 13U 13 U 13 U 13 U 13 U 13 U 13 UJ 13 U 13 U 13 U 13 U 13 U 13 U 13U 13 U 13 U 13 U 13 UJ 13 U 13 UJ 13 U 13 U 13 U 13 U 13U 13 U 13 U
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
14U 14U
14 U 14U 20 U 16J 14 U 14U
14U 14U 14 U 14U 14U 14 U 14U 14U 14 U 14U 14U 14 U 14U 14U 14 U 14U 14 U 14U 14U 14U
14U 14 U 14 U 14U 14U
16U 16U 16 U 18U 18U 16 UJ 16U 16U
16U
16 U 16U 16 U 16U 16 U 16U 16 U 16 U 16U 6 J
16U 16U 16U 16U 16U 16U 18U 3 J
16 U 16U 16U 16 U 16U 16U
EPA/TRC BGE87
PRP
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
12U 12U 12U 12U 21 U 12J 12U 12 U
12U
12U 12U 12U 12U 12U 12U 12U 12U 12U 12U 12U 12U 12U 12U 12U 12U 12U 12U 12 U
12U 12U 12 U 12U
12 U
11 U 11 U 11U 11 U 45 U 34 UJ 11 U 11U 11U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 U 11 u 11 u 11 u 11U 11 u 11 u
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
U •= Analyte was nol-detected at the concentration listed. J a Quantitation Is approximate due to limitations identified during the quality control review. R = Value was rejected due to laboratory quality control problems. RPD B Relative percent difference; RPD is calculated only when analytes are detected In both samples ' o Results outside the quantitative comparability goal tor split samples - RPD > 100% + = Analyte was detected by EPA/TRC but not by the PRP NR = Data point was not reported NA = Calculation of a quantitative comparability goal was not neccessary
» \
o o c^
e o C5>
iff * i
Table A-1 a
Chloromethane Bromomethane
Vinyl Chloride Chloroethane Methylene Chloride
Acetone
Carbon Disulfide 1,1-Dichloroethene 1,1-DIchloroethane
1,2-Dichloroethene (total) Chloroform 1,2-Dichioroethane 2-Butanone 1,1,1-Trichloroethane Carbon Tetrachloride
Bromodichloromethane 1,2-Dichioropropane cis-1,3-Dichloropropene Trichloroethene Dibromochloromethane 1,1,2-Trichloroethane Benzene trans-1,3-Dichloropropene Bromoform 4-Methyl-2-Pentanone 2-Hexanone Tetrachloroethene 1,1,2,2-Tetrachloroethane
Toluene Chlorobenzene Ethylbenzene Styrene Xylene (total)
SPLIT SAMPLE COMPARISON - CORTESE LANDFILL VOLATILE ORGANICS IN SOIUSEDIMENT (ug/Kg)
dd-21 EPA/TRC
BGE88
14 U 14U 14 U 14 U 14 U 17 UJ
14U 14 U 14U
14 U 14 U 14U 14 U 14 U 14 U 14U 14U 14 U 14 U U U 14 U 14U 14 U 14U 14 U 14 U 14 U 14U
14 U 14U 14U 14 U 14 U
PRP
23 UJ 23 UJ
23 UJ 23 UJ 23 UJ 45 UJ
23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ 23 UJ
23 UJ 23 UJ 23 UJ 23 UJ 23 UJ
23 UJ 23 UJ 23 UJ 23 UJ 23 UJ
RPD
NA NA
NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA
NA NA NA NA NA
si^iiiiliiili EPA/TRC
BGE92
13U 13U
13U 13 U 14U 32 J 13U 13U 13U
13U 13U 13U 13U 13U 13U
13U 13U 13U 13U 13U 13 U 13U 13U 13U 13U 13 U 13U 13U
13U 13U 13U 13U 13U
PRP
12 UJ 12U 12U 12U 12 UJ 12 UJ
12U 12U 12U 12U 12U 12U 12 UJ 12U 12U 12U 12U 12U 12U 12U 12U 12U 12U
12U 12 UJ 12 UJ 12U 12U
12U 12U 12U 12U 12U
Page 2 of 3
RPD
NA NA
NA NA NA NA +
NA NA NA
NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA NA NA NA
sbi EPA/TRC
BGE93
29000 UJ 29000 U 29000 U 29000 U 88000 29000 UJ 29000 U 29000 UJ 17000 J
8700 J 29000 U 29000 U 29000 U 29000 29000 U 29000 U 29000 U 29000 U
690000 J 29000 U 29000 U 29000 U 29000 U
29000 U 29000 UJ 29000 U
180000 29000 U
220000 J 29000 U
110000 29000 U
410000
PRP
2100 U 2100 U 2100 U
2100 R 9600 2100 UJ 2100 U 2100 U 8600
7600 2100 U 2100 U 2100 UJ
14000 2100 U 2100 U 2100 U 2100 U
440000 2100 U 2100 U
450 J . 2100 U
2100 U 2100 U 2100 U
130000 2100 U
180000 2100 U
82000 2100 U
320000
RPD
NA NA NA NA NA NA
NA NA
67
13 NA NA NA
70 NA NA NA NA
44 NA NA NA NA
NA NA NA
32 NA
20 NA
29 NA
25
U = Analyte was not detected at the concentration listed J > Quantitation is approximate due to limitations identified during the quality control review. R = Value was rejected due to laboratory quality control problems RPD = Relative percent difference; RPD is calculated only when analytes are detected In both samples * 3 Results outside the quantitative comparability goal for split samples - RPD > 100% + = Analyte was delected by EPA/TRC but not by the PRP NR = Data point was not reported. NA = Calculation of a quantitative comparability goal was not necces^
' #
¥9
CO
OD
Table A-1 a SPLIT SAMPLE COMPARISON - CORTESE LANDFILL VOLATILE ORGANICS IN SOIUSEDIMENT (ug/Kg)
|S3-1$ 1
Chloromethane Bromomethane Vinyl Chloride Chloroethane Methylene Chloride Acetone
Cartxjn Disulfide 1,1-Dichloroethene 1,1-Dichloroethane 1,2-Dichloroethene (total) Chloroform
1,2-Dichloroethane 2-Butanone 1,1,1-Trichloroethane Carbon Tetrachloride
Bromodichloromethane 1,2-Dichloropropane
cis-1,3-Dichloropropene
Trichloroethene
Dibromochloromethane 1,1,2-Trichloroethane Benzene
trans-1,3-Dichloropropene Bromoform 4-Methyl-2-Pentanone 2-Hexanone Tetrachloroethene 1,1,2,2-Tetrachloroethane Toluene
Chlorobenzene Ethylbenzene Styrene
Xylene (total)
EPAn-RC
BGE90
13U 13U 13 U 13U 13U 23 J 13U 13U 13U 13U 13U 13 U 13U 13 U 13U
13U 13U 13U
13U
13U 13U 13U 13U 13U 13U 13U 13 U 13 U 13U 13U 13 U 13 U
13U
PRP
13 U 13 U 13 U 13 U 13 U 13 UJ 13 UJ 13 U 13 UJ 13 UJ 13 U 13 U 13 UJ 13 U 13 U
13 U 13U 13U
13 U
13 U 13 U 13 U 13 U 13 U 13 U 13 UJ 13 U 13 U 13 U 13 U 13 U 13 U
13 U
RPD
NA NA NA NA NA NA + NA NA NA NA NA NA NA NA NA
NA NA
NA
NA
NA NA NA NA NA NA NA NA NA NA NA NA
NA NA
siiiiiiiiiiiiiiiiiii EPAn"RC
BGE91
13U 13U 13 U 13U 13U 6 J
13U 13U 13U 13U 13U 13 U 13 U 13 U 13U
13U 13 U 13 U
13U
13U 13U 13 U 13U 13U 13U 13U 13 U 13U 13U 13U 13 U
13U 13U
PRP
13U 13U
13 U
13 U 15U 22 UJ 13U 13U 13U 13U 13U 13 U 13 UJ 13U 13U
13U 13 U 13U
13U
13U 13U 13U 13U 13U 13U 13 UJ 13 U 13 U 13U 13U 13 U 13U
13U
Page 3 of 3
RPD
NA NA NA NA NA NA + NA NA NA NA NA NA NA NA NA
NA NA
NA
NA
NA NA NA NA NA NA NA NA NA NA NA NA
NA NA
U = Analyte was not detected at the concentration listed. J = Quantitation Is approximate due lo limilalions identified during the quality control review. R = Value was rejected due to laboratory quality control problems. RPD - Relative percent dillerence; RPD is calculated only when analytes are delected in both samples * • RBSUHB outside the quantitative comparability goal for split samples - RPD > 100% + » Analyte was delected by EPA/TRC but not by the PRP. NR = Data point was not reported. NA = Calculation of a quantitative comparability goal was not neccessary
{Table A-1 b
j Analyte
Phenol bis(2-Chloro9lhyl)Ether 2-Chloroph6nol 1.3-Dichlorobdnzene 1.4-Dichlorob6nzene 1,2-Dichlorobenzene 2-Mathylphenol 2,2'-Oxybis( 1 -Chloropropane) 4-Melhylphenol N-Nilroso-Di-n-Propylamine Hexachloroethana Nitrobenzene Isophorone 2-Nitro phenol
2,4-DimBthylphBnol 1 Benzoic acid (1)
1 bis{2-Chlorosthoxy)Methane 2,4-Dichlorophenol 1,2,4-Trichlorcbenzene
1 Naphthalene
4-Chloroanilin9
Hexachlorobutadiene 4-Chloro-3-Methylphenol 2-Methylnaphthalene Hexachlorocyclopentadiene 2,4.6-Trichlorophenol 2.4.5-Trichloroph9nol 2-Chloronaphthalene 2-Nitroanilino
Dimethyl Phthalate
Acenaphthylene 2,6-Dinitrotolu9ne 3-Nitroaniline
Acenaphthene
2,4-Dinitroph6nol 4-Nitrophenol
Dibenzoturan
2.4-Dinitrotolu«ne Diethylphthalate 4-Chlorophenyl-phBnylether Flucrene 4-Nitroaniline
4,6-Dinitro-2-MeIhylphenol N-Nitrosodiphenylamine 4-8romopheny|-phenylether Hexachlorobenzene Pentachlorophenol Phenanthrene Anthracene Carbazole
Di-n-Butylphthalale Fluoranthene
Pyrene Butylbenzylphthalate
3.3'-Dichlorob6nzidin9 Benzo(a)Anthracen9 Chtysane
bis{2-Ethylhexy|)Phthalat9 Di-n-Octyl Phthalat9 BenzolbjFluorantnene
Benzo(k)Ruoranth9n9 Benzo(a)Pyr9n9 lnd9no(1.2,3-cd)Pyrene Dib9nz(a.h)Anthracene
Benzo(g,h,i)P9rylene
SPUT SAMPLE COMPARISON - CORTESE LANDRIX SEMI-VOt.AT1LE ORGANICS IN SOIL/SEDIMENT (ug/Kg)
!HZ«oa 1 EPAH'RC BGE85
380 U 380 U 380 U 380 U 380 U 380 U 380 U 380 U 380 U 380 U 380 U 380 U 380 U 380 U 380 U
NR 380 U 380 U 380 U 380 U
380 U 380 U 380 U 380 U 380 U 380 U
920 U 380 U 920 U 380 U 380 U 380 U 920 U
380 U
920 U 920 U 380 U 380 U
380 U 380 U 380 U 920 U 920 U 380 U 380 U 380 U 920 U 380 U 380 U 380 U
380 U
380 U 380 U 380 U
380 U 380 U 380 U 380 U 380 U
380 U 380 U 380 U 380 U 380 U 380 U
IPRP
430 U 430 U 430 U 430 U 430 U 430 U 430 U 430 UJ 430 U 430 U 430 U 430 U 430 U 430 U 430 U
4300 U
430 U 430 U 430 UJ 430 U 430 U
430 UJ 430 U 430 U 430 U, 430 U
1100U 430 U
1100U 430 U 430 U 430 U
1100U 430 U
1100 U
1100U 430 U 430 U 430 U
430 U 430 U
1100U 1100U 430 U 430 U
430 U 1100U
85 J 430 U 430 U
430 U
82 J 76 J
430 U 430 U
430 U . 430 U 430 U 430 U 64J
64J 430 U 430 UJ 430 UJ 430 UJ
JRPD
NA NA NA NA NA
U M
Uw NA NA NA NA NA NA
\HA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA
NA
NA NA NA NA
NA NA NA NA NA NA NA NA NA 1 ^ NA
NA NA
NA NA hW NA
NA NA NA NA NA NA NA NA NA
:83M)ir EPAn-RC IPRP
{BGEBS 1
( 460 U j 460 U 1 460 U j 460 U
460 U 460 U 460 U 460 U 60J
1 460 U i 460 U j 460 U
460 U
460 U 460 U
NR
460 U 460 U 460 U 460 U 460 U
460 U 460 U 460 U 460 U
460 U 1100 U 460 U
1100U 460 U
460 U 460 U
1100U 460 U
1100U
1100U 460 U 460 U 64 J
460 U 460 U
1100U 1100U 460 U 460 U 460 U
1100U 200 J 460 U 460 U
460 U
230J 230 J 460 U 460 U
110J B8J
460 U 460 U 140 J 140 J
78J 51J
460 U 52 J
520 U 520 U 520 U
1 520 U 1 520 U
520 U 520 U 520 UJ 520 U
1 520 U 520 U 520 U 520 U 520 U 520 U
5200 U 520 U
520 U 520 UJ 520 U
520 U
520 UJ 520 U 520 U 520 U
520 U 1300 U 520 U
1300 U 520 U 520 U
520 U 1300 U 520 U
1300 U
1300 U 520 U
520 U 520 U
520 U 520 U
1300 U 1300 U 520 U 520 U 520 U
1300 U 62J
520 U 520 U
520 U 110J
too J 520 U 520 U 53J
520 U 520 U 520 U 99J
99J 520 U 520 UJ 520 UJ
520 UJ
Page 1 of 3
| H P D
NA NA NA NA NA IW NA NA NA + NA N4A NA NA NA NA NA
NA NA NA NA
NA NA NA NA NA NA
NA NA NA NA NA
NA NA NA
NA
NA NA
NA NA +
NA NA NA
NA NA NA NA NA
1 0 5 ' NA NA NA
71
79 NA NA
70 NA + NA NA
34 34
NA + NA + NA NA t
fRWSis;;:;:;:;;;:; EPAn'RC BGE87
390 U 390 U 390 U 390 U 4SJ
390 U 390 U 390 U 390 U 390 U 390 U 390 U 390 U 390 U 390 U
NR 390 U
390 U 390 U 390 U 390 U
390 U 390 U 390 U 390 U
390 U 950 U 390 U 950 U 390 U 390 U 390 U 950 U 390 U
950 U 950 U 390 U 390 U
390 U 390 U 390 U 950 U 950 U 390 U 390 U
• 390 U 950 U 390 U 390 U 390 U
390 U
390 U 390 U 390 U 390 U 390 U
390 U 390 U 390 U 390 U
390 U 390 U 390 U 390 U 390 U
JPRP
350 U 3S0U 350 U 350 U
4SJ 350 U 350 U 350 UJ 350 U 350 U 350 U 350 U 350 U 350 U 350 U
3500 U 350 U 350 U 350 UJ 350 U 350 U
350 U 350 U 350 U 350 UJ
350 U 850 U 350 U 850 U
• 350 U 350 U
350 U 850 U
350 U 850 U 850 U 350 U 350 U
350 U 350 U 350 U 850 U 850 U 350 U 350 U 350 U 850 U
47 J 350 U 350 U 350 U
60J 54J 43'J
350 U 350 U 350 U 350 U 350 U
350 U 350 U 350 U 350 UJ 350 UJ
• 350 UJ
iRPD
NA NA NA NA
0 NA NA NA NA I M NA NA NA
NA NA NA NA NA NA NA NA NA
NA NA NA
NA NA NA NA NA NA NA NA NA NA
NA NA NA NA
NA NA NA NA NA NA
NA NA NA NA NA I M
NA NA NA NA
NA NA NA NA NA NA NA NA NA NA
U • Anatyto was not dvttctod al Ih* ooncvnration listad. J > Quantitibon is «pproximal» diw to (imilitrcns tdantifi»d during th« quality oontrd r«vT«M'. R • VaJu* was rsjactad dua to laboratory quaily conffol prcUams. RPD « Ralativa parcsnt diffar«noa; RPO is calouistad onty ot Mn onaJytss ara dstactad in both sampj« ' - Rasults outsida the c^antilaliva oomparabiity god tcr split samptas - RPD > 10(rC •t- - Analyta was datoctod by EPA/TRC but not by t ia PRP, NR • Data poinl was not raportad. NA a Calculation ot a qjantitaliva comparatility god was not naocsssa/y.
1 -Banzoic add is not a TCL compound but anaiyzad by PRP
300821
Table A - l b
Analyte
1
Phenol tbis(2-Chlor09thyl)Eth9r
2-Chloroph9nol 1,3-DichlorobenzenB
1,4-Dichlorobenzene
1.2-0ich(orobenzene 2-Methylph9nol 2.2'-Oxybls(1 -Chloropropane)
4-Methylphenol N-Nitroso- Di-n-Propylamine HexachloroBthane Nitrobenzene isophorone
2-Nitrophenol 2.4-DimethylphBnol
Benzoic acid (1) bis(2-Chlcroethoxy)MethanB
2.4'DichlorophBnol
1,2,4-TnchlorobBnzBne NaphthalBne
4-Chloroaniline Hexachlorobutadiene
4-Chtoro-3-Methylphenol 2-MethyinaphthalenB
1 H8xachlorocycloperTtadi9ne 2,4,6-TrichlQroph9not 2.4.5-Trichloroph9nol 2-Chloro naphthalene 2-Nitroaniline Dimethyl Phthalate
Acenaphthylene
2.5-DinitrotoluenB 3-NitroaniiinB AcenaphthsnB
2.4-DiniIrophBnol
4-Nitrophenol Dibenzoturan 2.4-DinitrotoluenB
DiethyiphthalatB 4-Ch)oroph8nyl-phenylethBr
FluorenB
4-Nilroaniline 4,6-Dinitro-2-Methylphenol
N-NitrosodiphenylaminB 4-BromophBnyl-phenyl9thBr
HBxachlorobBnzenB
pBntachlorophenol
Phenanthrene Anthracene
Carbazole
Di-n-Butylphthalate
Fluoranthene
Pyrene Butylbenzylphthalate
3.3'-Dichlorobenzidin9
Benzo(a)Anthracene
Chryseno bis(2-Ethylh9xyl)Phthalate
Di-n-Octyl Phthalate Benzo(b)Fluoranthene
Benzo(k)Fluoranthen6 Benzo(a)Pyren9
lndeno{1,2.3-cd)Pyrene
Oibenz(a.h)Anthrao9n9 B9nzo(g,h,i)Perylen9
SPUT SAMPLE COMPARISON - CORTESE LANDFILL SEMI-VOLATILE ORGANICS IN SOIUSEDHIENT (ug/Kg)
\ssmwmm • EPAn-RC
'BGEB8
470 UJ
j 470 UJ 1 470 UJ
i 470 UJ
76 J
470 UJ 470 UJ 470 UJ
1 470 UJ
470 UJ 470 UJ 470 UJ 470 UJ
470 UJ
1 470 UJ NR
470 UJ
470 UJ
' 470 UJ i 470 UJ
470 UJ 470 UJ
470 UJ 470 UJ
470 UJ 470 UJ
1100 UJ 470 UJ
1100 UJ 470 UJ
470 UJ
470 UJ 1100 UJ
470 UJ
1100 UJ
1100 UJ
470 UJ 470 UJ
470 UJ 470 UJ 470 UJ
1100 UJ
1100 UJ
470 UJ 470 UJ
470 UJ
1100 UJ
100 J
470 UJ 470 UJ
470 UJ
190 J
120 J 470 UJ
470 UJ
93J
67 J 470 UJ
470 UJ
110J 110J 64J
470 UJ
470 UJ
470 UJ
SSSSHS::;;?™;:®^^^^
PRP
710 U J
710UJ 710 UJ 710UJ
320 J
710 UJ 710UJ 710UJ
710UJ
710UJ 710UJ 710 UJ
710 UJ
710 UJ
710 UJ
7100 UJ
710UJ
710UJ
710 UJ 710UJ
710UJ 710UJ 710UJ 710UJ 710UJ 710UJ
1700UJ 710 UJ
1700 UJ
710 UJ
710 UJ
710 UJ 1700UJ
710UJ 1700 UJ
1700 UJ
710UJ 710UJ
710UJ 710UJ 710 UJ
1700UJ
1700UJ
710 UJ 710UJ
710UJ
1700UJ
200 J
710UJ 710UJ
710UJ
540 J
600 J 710 UJ
710 UJ
470 J
260 J 710 UJ
710 UJ
510J
510J 260 J
220 J
710UJ
290 J
RPD
NA
NA NA
NA
123"
NA NA NA
NA
NA NA NA NA
NA
NA NA
NA NA
NA NA
NA NA
NA NA NA NA NA NA NA NA
NA
NA NA NA
NA
NA
NA NA
NA NA NA
NA
NA
NA NA
NA
NA
67
NA NA
NA
96
133-NA
NA 134-
118* NA
NA
129* 129* 121 •
NA
NA
NA
mammmmmmmmm EPA/TRC BGE92
430 UJ 430 UJ 430 UJ
430 UJ
430 UJ
430 UJ 430 UJ 430 UJ
430 UJ
430 UJ 430 UJ 430 UJ 430 UJ
430 UJ
430 UJ NR
430 UJ 430 UJ
430 UJ 430 UJ
430 UJ 430 UJ 430 UJ 430 UJ
430 UJ 430 UJ
1100 UJ 430 UJ
1100 UJ 430 UJ
430 UJ
430 UJ 1100 UJ 430 UJ
1100 UJ
1100 UJ
430 UJ
430 UJ 430 UJ
430 UJ 430 UJ
1100 UJ
1100 UJ 430 UJ 430 UJ
430 UJ
1100 UJ
430 UJ
430 UJ
430 UJ
430 UJ
430 UJ
430 UJ
430 UJ
430 UJ
430 UJ
430 UJ 430 UJ
430 UJ
430 UJ
430 UJ 430 UJ
430 UJ
430 UJ
430 UJ
PRP
400 U
400 U 400 U
400 U
400 U
400 U 400 U 400 UJ
59 J
400 U 400 U 400 U 400 U
400 U
400 U
4000 U
400 U
400 U
400 UJ 400 U
400 U 400 UJ 400 U 400 U
400 U 400 U 980 U 400 U
980 U 400 U
400 U
400 U 980 U
400 U 980 U
980 U
400 U 400 U
400 U
400 U 400 U
980 U-
980 U
400 U 400 U
400 U
980 U
400 U
400 U 400 U
400 U
400 U
400 U 400 U
400 U
400 U
400 U 400 U
400 U
400 U 400 U 400 U
400 U
400 U
400 U
Page 2 o< 3
RPD
NA
NA NA
NA
NA
NA NA NA
NA
NA NA NA NA
NA
NA NA
NA NA
NA NA
NA NA NA NA NA
NA NA NA NA NA
NA
NA NA
NA NA
NA
NA
NA NA
NA NA
NA
NA NA NA
NA
NA
NA
NA NA
NA
NA
NA NA
NA
NA
NA NA
NA
NA
NA I M NA
NA
NA
iammmm EPA/TRC BGE93
4000 UJ
4000 UJ 4000 UJ
4000 UJ
4000 UJ
4000 UJ 4000 UJ
4000 U
4000 UJ
4000 UJ 4000 UJ 4000 UJ 4000 UJ
4000 UJ
4000 UJ NR
4000 UJ
4000 UJ 4000 UJ
87000 J
4000 UJ
4000 UJ 4000 UJ
22000 J
4000 UJ 4000 UJ 9600 UJ 4000 UJ 9600 UJ
4000 UJ 930 J
4000 UJ 9600 UJ
27000 UJ
9600 UJ
9600 UJ
19000 J
4000 UJ
4000 UJ 4000 UJ
20000 J
9600 UJ
9600 UJ
4000 UJ 4000 UJ
4000 UJ
9600 UJ
62000 J
8700 J 12000 J
5200 J
28000 J
18000 J
4000 UJ
4000 UJ
7300 J
5200 J 2400 J
4000 UJ 4600 J
4600 J 1300 J 1300 J
550 J
1500 J
Wmiiimim PRP
160000 U
160000U 160000U
160000U
160000u
160000 u 160000 u 160000U
160000U
160000 U 160000 u 160000U 160000 U
160000u
160000U 3200000 U
160000U 160000u
160000 UJ 260000
160000U 160000 UJ
160000 U 46000 J
160000u 160000U 410000U 160000U 410000U
160000 u 160000U
160000U 410000U
51000 J
410000u
410000u
37000 J
160000U 160000U
160000 u 40000 J
410000U
410000U
160000U 160000u
160000 U
410000 U
140000 J
26000 J 17000 J
160000U
65000 J
41000 J 160000U
160000 U
160000U
160000 U 160000U
160000 U
160000U 160000U 160000U
160000 u
160000 u
160000 u
RPD
NA
NA NA
NA
NA
NA NA NA NA
NA NA NA NA NA
NA
NA
NA
NA NA
100
NA I M NA
74
NA
NA NA NA NA NA
I M +
NA NA
NA NA
NA
64
NA
NA NA
67
NA
I M
NA NA
NA
NA
77
100 34
I M +
80
78 NA
NA
NA +
NA + I M +
NA
NA + NA + NA +
NA +
NA +
NA +
U M Andyls was not datoctod at tha oonoanration listad. J M Quantitation is approximato dua to linitotions idantifiad durng tha quality oontrd raviaw. R • Valua was rajactad dua to iaboratcry qja i ty control problams. RPD - Ralativa parcant (ftffaranoa; RPD is caloulatad only whan anatytae ara datactad in both samplas. ' -Racul lB outsida tha quanbtaliva oomparabiity goal for splitsamphia - RPD > 100% *• - Analyta was datoctod by EPA/TRC but not b^ »ia PRP. NR > Data point was not raportad NA m Calculation of a quantitativa oomparabiiity goal was not naocassary.
1 'Banzoic add is not a TCL compowid but anaiyzad by PRP
300823
Table A - l b SPUT SAMPLE COMPARISON - CORTESE LANDFILL SEMI-VOLATILE ORGANICS IN SOIUSEDIMENT (ug/Kg)
Page 3 of 3
Analyte SSiWSHSSS .•RPD EPA/TRC
Phenol bis(2-Chloro9thyl)Ether 2-Chloropnenol 1,3-Dichlorobenzene 1,4-Dichtorabenzene 1,2-DichloroberTzene 2-M9thylph9nal 2.2'-0!tybis(1 -Chloropropang) 4-M9thylphenol N-NKroso-Di-n-Propylamine Hexachloroethane Nitrobenzene
Isophorone 2-Nitrophenot
2.4-Dimethylph9nol Benzoic acid (1) bis(2-ChloroethoxyjMethane
2,4-Dichloroph9nol
1,2,4-Trichlorobenzen9 Naphthalene
4-Chloroaniline
Hexachlorobutadiene
4-Chloro-3-M9thylphenol 2-Methylnaphthalene
Hexachlorocyclop9ntadi9ne
2,4,6-Trichloroph9nol
2,4,5-Trichloroph9nol 2-Chloronaphthalene
2-Nitroaniline
Dimethyl Phthalate
Acenaphthylene
2,6-DinitrotolU9n9 3-Nitroanilin9
Ac9naphth9n9
2.4-Dinitrophenol
4-Nitrophenol Dibenzoturan
2,4-Dinitrotoluene
Diethylphthalate
4-Chlorophonyl-ph9nylether Fluorene
4-Nitroaniline 4,6-Dinitro-2-M9thylph9nol
N-Nitrosodiphenylamine
4-B romo ph9nyl-ph9nylether
Hexachlorobenzene
Pentachlorophenol Phenanthrene
Anthracene
Carbazole
Di-n-Butylphthalate
Fluoranthene
Pyrene Butylbenzylphthalate
3,3'-Dichlorobenzidin9
B9nzo(a)Anthracane Chrysen9 bis(2-Ethylhexyl)Phthalate Di-n-Octyl Phthalate
B9nzo(bjFluoranthane
Benzo(k)Fluoranthene Benzo(a)Pyrene lndeno(1,2,3-od)Pyrene Dibenz(a,h)Anthracene
Benzo(g,h,i)Peryl9n9
BGE90
400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ
NR 400 UJ I 4O0UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 980 UJ 400 UJ 980 UJ 400 UJ 400 UJ 400 UJ 980 UJ 400 UJ 980 UJ 980 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ
R 980 UJ 400 UJ 400 UJ 400 UJ 980 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ 400 UJ
msmmmm PRP
400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U
4000 UJ 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U. 400 U 980 U 400 U 980 U 400 U 400 U 400 U 980 U 400 U 980 U 980 UJ 400 U 400 U 400 U 400 U 400 U 980 U 980 U 400 U 400 U 400 U 980 UJ 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 U 400 UJ 400 UJ 400 U 400 U 400 U 400 U 400 U 400 U
NA NA NA NA NA NA NA NA NA NA NA
NA
NA NA
NA NA
NA
NA
NA NA
NA
NA
NA NA
NA
NA
NA NA
NA
NA
NA
NA
NA
NA
NA
NA NA
NA
NA
NA
NA
NA NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA NA NA NA
NA
NA I M NA NA
NA
EPA/TRC BGE91
480 U 480 U 480 U 480 U
4aou 480 U 480 U 480 U 430 U 480 U 480 U 480 U 480U 480 U 480 UJ
NR 480 U 480 U 480 U 480 U 480 U 480 UJ 480 U 480 U 480 U 480 U
1200 U 480 U
1200 U 480 U 480 U 480 U
1200 U 480 U
1200 U 1200 U 480 U 480 U 480 U 480 U 480 U
R 1200 U 4S0U 480 U 480 U
1200 U 70J
480 U 480 UJ
25 J 5SJ 82J
380 J 480 U 480 U 480 U 480 UJ 480 UJ 480 U 480 U 480 U 480 U 480 U 480 U
420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U
4200 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U
1000 U 420 U
1000 U 420 U 420 U 420 U
1000 U 420 U 1000 U 1000 U 420 U 420 U 420 U 420 U 420 U
1000 U 1000 U 420 U 420 U 420 U
1000 UJ 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U 420 U
RPD
NA
NA NA NA NA NA NA NA NA NA NA
NA NA
NA
NA NA
NA
NA
NA NA
NA
NA
NA NA NA
NA
I M NA
NA
NA
NA
NA
NA
NA
NA
NA NA
NA
NA
NA NA
NA
NA
NA NA
NA
NA
NA
NA
NA
NA
NA
NA NA
NA
NA I M NA NA
I M
NA NA NA NA
NA
U - Anajyto was not datoctod at tf>» conoenration iistad. J « Quantitation is afsproximato dua to limitilions idsntifiad durng the quaUty oonird raviaw. R * Valua was rafactad dua to labcralcry quaity (xntrol probJams, RPD « Rataliva parcant diffaranca; RPO is calculatad only wttan analytaa ara datactad in l30th sampta) ' « Rasults outsida (ha quaiibtativacomparabiity goal for split aamplas - RPD > 100% •. - Anatyta waa dalaclad by EPA/TRC tut not Ijy t ia PRP. NR > Data point was not ropoftod NA « Calculation of a qjantitativa oomparabiiity goal was not naccaeaary.
1 -Banzoic add is not a TCL compound but anaJyzad by PRP
SS80D! 300823
m m
CO
o OJ A»
Table A- lc
Analyte
alpha-BHC beta-BHC (delta-BHC Lindane Heptachlor Aldrin Heptachlor epoxide
Endosulfan 1 Dieldrin 4,4'-DDE Endrin Endosulfan II 4,4'-DDD Endosulfan sulfate 4,4'-DDT Methoxychlor Endrin ketone Endrin aldehyde afpha-Chlordane gamma-Chlordane Toxaphene Aroclor-1016 Aroclor-1221 Aroclor-1232 Aroclor-1242 Aroclor-1248
Aroclor-1254 Aroclor-1260
SPLIT SAMPLE COMPARISON - CORTESE LANDFILL P E S T I C I D E / P C B S I N S O I L / S E D I M E N T (ug/Kg)
^^^^^K^^SmlmM EPA/TRC BGE85
1.9 U 1.9 U
0.4 J 1.9 U 1.9 U 1.9 U 1.9 U 1.9 U 3.8 U 3.8 U 3.8 U 3.8 U 3.8 U 3.8 U 3.8 U 19U
3.8 U
0.84 J 1.9 U 1.9 U 190 U 38 U 77 U 38 U 38 U 38 U 38 U
38 U
PRP
2.3 U
2.3 U 2.3 U 2.3 U 2.3 U 2.3 U 2.3 U 2.3 U 4.4 U 4.4 U 4.4 U 4.4 U 4-4 U 4.4 U 4.4 U 23 U
4.4 U
4.4 U 2.3 U 2.3 U 230 U 44 U 89 U 44 U 44 U
44 U 44 U 44 U
RPD
NA
NA NA -I-NA NA NA NA NA
NA NA NA NA NA NA NA NA NA
NA -1-NA NA NA NA NA NA NA NA NA NA
Wmm^mmmmm EPA/TRC BGE86
2.4 U 2.4 U 2.4 U 2.4 U 2.4 U 2.4 U 2.4 U 2.4 U 4.6 U
R R
4.6 U 4.6 U 4.6 U 4.6 U 4.6 U 4.6 U
4.6 U R
2.4 U 240 U 46 U 93 U 46 U 46 U 46 U 46 U 46 U
PRP
2.7 U
2.7 U 2.7 U 2.7 U 2.7 U 2.7 U 2.7 U 2.7 U 5.2 UJ 5.2 U 5.2 U 5.2 U 5.2 U 5.2 U 5.2 U 27 UJ 5.2 U 5.2 U 2.7 U 2.7 U
270 U 52 U
110U 52 U 52 U
52 U 52 U 52 U
Page 1 of 3
RPD
NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
NA NA
iiliiiiiiiiii« ^ ^ ^ ^ ^ EPA/TRC BGE87
2U 2U 2U 2U 2U
0.075 J 2U 2U
3.9 U 0.19 J 3.9 U 3.9 U 3.9 U 3.9 U 3.9 U 20 U 3.9 U
3.9 U 2U
R 200 U 39 U 80 U 39 U 39 U 39 U 39 U 39 U
PRP
1.8 U 1.8 U 1.8 U 1.8 U 1.8 U 1.8 U 1.8 U 1.8 U
3.5 UJ 3.5 U 3.5 U 3.5 U 3.5 U 3.5 U 3.5 U 18 UJ
3.5 U
3.5 U 1.8 U 1.8 U 180 U 35 U 72 U 35 U 35 U
35 U 35 U 35 U
RPD
NA
NA NA NA NA NA + NA
NA NA NA + NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA
NA NA NA
U = Analyte was not detected at the concentration listed. J = Quantitation Is approximate due to limitations identified during the quality control review. R = Value was rejected due to laboratory quality control problems. RPD = Relative percent difference; RPD Is calculated only when analytes are detected In both sample * = Results outside the quantitative comparability goal for split samples - RPD > 100% + = Analyte was delected by EPA/TRC but not by the PRP. NR = Data point was not reported. NA = Calculation of a quantitative comparability goal was not neccessary.
Table A- lc S P L I T S A M P L E C O M P A R I S O N - CORTESE LANDFILL
P E S T I C I D E / P C B S I N S O I L / S E D I M E N T (ug/Kg)
Page 2 of 3
Analyte !$S-21 RPD SS-22 RPD wm RPD
alpha-BHC beta-BHC delta-BHC Lindane Heptachlor Aldrin Heptachlor epoxide Endosulfan I Dieldrin 4,4'-DDE Endrin Endosulfan II 4,4'-DDD Endosulfan sulfate 4,4'-DDT Methoxychlor Endrin ketone Endrin aldehyde alpha-Chlordane gamma-Chlordane Toxaphene Aroclor-1016 Aroclor-1221 Aroclor-1232 Aroclor-1242 Arodor-1248 Aroclor-1254 Aroclor-1260
EPA/TRC PRP EPA/TRC BGE88
R 2.4 UJ 2.4 UJ 2.4 UJ 2.4 UJ
R 2.4 UJ 2.4 UJ 4.7 UJ
0.56 J 4.7 UJ 4.7 UJ 4.7 UJ
R 4.7 UJ 4.7 UJ
0.11 J 4.7 UJ
0.092 J 2.4 UJ 240 U
47 U 95 U 47 U 47 U 47 U 47 U 47 U
3.8 UJ 3.8 UJ 3.8 UJ 3.8 UJ 3.8 UJ 3.8 UJ 3.8 UJ 3.8 UJ 7.5 UJ 7.5 UJ 7.5 UJ 7.5 UJ 7.5 UJ 7.5 UJ 7.5 UJ 38 UJ 7.5 UJ
7.5 UJ 3.8 UJ 3.8 UJ
380 UJ 75 UJ
150 U J 75 UJ 75 UJ 75 UJ 75 UJ 75 UJ
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
BGE92
R 2.2 UJ 2.2 UJ 2.2 UJ 2.2 UJ
0.07 J 2.2 UJ 2.2 UJ
R 4.3 UJ 4.3 UJ 4.3 UJ 4.3 UJ 4.3 UJ 4.3 UJ
22 UJ 4.3 UJ 4.3 UJ 2.2 UJ
R 220 UJ 43 UJ 88 UJ 43 UJ 43 UJ 43 UJ 43 UJ 43 UJ
PRP EPAn"RC
2.1 U 2.1 U 2.1 U 2.1 U 2.1 U 2.1 U 2.1 U 2.1 U 4.0 U 4.0 U 4.0 U 4.0 U 4.0 U 4.0 U 4.0 U 21 UJ 4.0 U
4.0 U 2.1 U 2.1 U 210 U
40 U 82 U 40 U 40 U 40 U 40 U 40 U
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
BGE93
U = Analyte was not detected at the concentration listed. J = Quantitation Is approximate due lo limitations Identified during the quality control review. R = Value was rejected due to laboratory quality control problems. RPD = Relative percent difference; RPD is calculated only when analytes are delected in both samples. * = Results outside the quantitative comparability goal for split samples - RPD > 100% + = /\nalyte was detected by EP/\/TRC but not by the PRP^ NR = Data point was not reported. NA = Calculation of a quantitative comparability goal was in^pbcessary.
R R
I U N 10 UJ 10 UJ 10 UJ
3.6 J 10 UJ 19J
R 25 J 20 UJ 20 UJ 20 UJ 13J
100 UJ R R
29 J 10 UJ
1000 UJ 200 UJ 400 UJ 200 UJ 200 UJ 200 UJ 200 UJ 200 UJ
PRP
R 3.2 J
R R R R R R
3.6 J R R R R R R R R R R R R R R R R R R R
NA NA NA NA NA NA NA NA
136 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
CO
o
Table A-1 c SPLIT SAMPLE COMPARISON - CORTESE LANDFILL PESTICIDE/PCBs IN SOIL/SEDIMENT (ug/Kg)
Page 3 of 3
CO o o 00
Analyte
alpha-BHC beta-BHC delta-BHC
Lindane Heptachlor
Aldrin Heptachlor epoxide Endosulfan I Dieldrin 4,4'-DDE Endrin Endosulfan II 4,4'-DDD Endosulfan sulfate 4,4'-DDT Methoxychlor Endrin ketone Endrin aldehyde alpha-Chlordane gamma-Chlordane Toxaphene Aroclor-1016 Arocior-1221 Aroclor-1232
Aroclor-1242 Aroclor-1248 Aroclor-1254 Aroclor-1260
^mm EPA/TRC BGE90
2.1 UJ 2.1 UJ 2.1 UJ 2.1 UJ 2.1 UJ 2.1 UJ 2.1 UJ 2.1 UJ 4.0 UJ 4.0 UJ 4.0 UJ 4.0 UJ 4.0 UJ
4.0 UJ
7.1 J 27 J 4.0 UJ 4.0 UJ
2.1 UJ 2.1 UJ 210 UJ 40 UJ 82 UJ 40 UJ 40 UJ 40 UJ 40 UJ 40 UJ
PRP
J_
2.2 U 2.2 U 2.2 U 2.2 U 2.2 U 2.2 U 2.2 U 2.2 U 4.2 UJ 4.2 U 4.2 UJ 4.2 U 4.2 U
4.2 U 4.3 J 22 U 4,2 U 4.2 U 2.2 U 2.2 U
220 U 42 U 85 U 42 U 42 U 42 U 42 U 42 U
RPD
NA NA NA NA NA NA NA NA NA NA NA NA NA NA
S3-15 EPA/TRC BGE91
49
NA NA NA NA NA NA NA NA NA NA NA NA NA
2.5 U 2.5 U 2.5 U 2.5 U 2.5 U 2.5 U 2.5 U 2.5 U 4.8 U 4.8 U 4.8 U 4.8 U
PRP
2.2 U 2.2 U 2.2 U 2.2 U 2.2 U 2.2 U 2.2 U 2.2 U 4.2 U 4.2 U 4.2 U 4.2 U
4.8 U 4.8 U 4.8 U 25 U 4.8 U 4.8 U
2.5 U 2.5 U 250 U 48 U 97 U 48 U
48 U 48 U 48 U 48 U
4.2 U 4.2 U 4.2 U 22 UJ 4.2 U 4.2 U
2.2 U 2.2 U 220 U 42 U 85 U 42 U 42 U 42 U 15J 42 U
U = Analyte was not detected at the concentration listed. J = Quantitation is approximate due to limitations identified during the quality conUd review. R = Value was rejected due to laboratory quality control problems. RPD = Relative percent difference; RPD is calculated only when analytes are detected in both samples. * = Results outside the quantitative comparability goal for split samples - RPD > 100% + = Analyte was detected by EPA/TRC but not by the PRP. NR = Data point was not reported. NA = Calculation ol a quantitative comparability goal was not neccessary.
CO
o CO
Table A-1 d
Analyte
Aluminum
Antimony Arsenic Barium Beryllium Cadmium Calcium Chromium Cobalt Copper Iron Lead Magnesium Manganese Mercury Nicl^el Potassium Selenium Silver Sodium Thallium Vanadium Zinc Cyanide
SPLIT SAMPLE COMPARISON - CORTESE LANDFILL INORGANICS IN SOIL (mg/kg)
CRDL
40 12 2
40
1 1
100 2 4 5
20 0.6
1000 3
0.04 8
1000 1 2
1000 2
10 4 2
j | | | | | i | | | | | | ^ ^ 1 EPAH-RC MBHL85
4580 6.3 UJ 2.6 J
51.5 0.23 U 0.7 U 317 4.6 4.3 4.9
9100 8.9 J
1600 288
0.12 U 7.6 736 0.7 1.6U
89.9 0.7 U 4.8
31.8 0.58 U
PRP
4350.00 12.20 U
1.80 33.40 J
0.53 U 1.30 U
442.00 2.90 3.30 6.60 U
9170.00 5.30 J
1720.00 231.00
0.13 U 8.20 UJ
693.00 0.80 UJ 2.70 U
49.20 1.10U 3.60
41.10 R 0.66 U
RPD
5 NA
36 43
NA NA NA
45 NA NA
1 51
7 22
NA NA NA NA NA NA NA NA NA NA
"^^^^^^^^^^K^S,! EPA/TRC MBHL86
5050
7.1J 7.8 J
54.7 0.27 0.79 U 292 5.2 7.9 5.8
9300 6.1 N
1840 307 0.13 U
9.7 835
0.79 U 1.8 U
87.9 0.79 U
5.1 36.5 0.66 U
PRP
3990.00
11.40 UJ 9.20
53.90
0.32 U 1.60 U
451.00 4.50 5.00 5.70
10100.00 7.40
1570.00 331.00
0.16 U 8.10
641.00 0.95 UJ 2.20 U
79.40 U 1.30 U 2.70
35.90 R 0.79 U
Page 1 of 3
RPD
23 NA -I-
16 1
NA NA NA
14 NA NA
8 NA
16 8
NA NA NA NA NA NA NA NA NA NA
W ^ ^ ^ ^ ^ ^ ^ ^ M EPATFRC MBHL87
10600
6.7 UJ 3.5 J
65.1 0.5
0.74 U 621
13 11.8
26 18600
6.1 J 3480
751 0.12 U 18.4 1000 0.74 U
1.7U 186
0.74 U 10.6 90.9 0.62 U
PRP
4240.00 7.70 UJ 3.80
47.00 0.24 1.10U
300.00 5.00 6.10 5.80
9580.00 6.30
1570.00 245.00 R
0.11 U 7.60
527.00 0.65 UJ 1.50 U
54.00 U 0.86 U 2.60
32.30 R 0.54 U
RPD
86 NA
8 32
NA NA NA
89* NA
127* 64
3 76
NA NA
83 NA NA NA NA NA NA NA NA
U = Analyte was not detectetd at the concentration listetd. J = Quantitation is approximate cJue to limitations identified during the quality control review R = Value was rejected due to laboratory quality control problems. RPD = Relative percent difference; RPD is calculated only when analytes are detected in both samples. * = Results outside the quantitative comparability goal for split samples - either the RPD > 100% or one or both split samples had a concentration < 5 x CRDL and an absolute difference > 2 x CRDL + = Analyte was detected by EPA/TRC and not b ^ ^ ^ R P NR = Data point was not reported ^ ^ B NA = Calculation of a quantitative comparability go^^as not neccessary,
e ^
CO
00
Table A- ld
Analyte
Aluminum Antimony Arsenic Barium
Beryllium Cadmium Calcium Chromium Cobalt Copper Iron Lead Magnesium Manganese Mercury Nickel Potassium Selenium Silver
Sodium Thallium Vanadium Zinc
Cyanide
CRDL
40 12 2
40
1 1
100 2 4 5
20 0.6
1000 3
0.04 8
1000 1 2
1000 2
10 4 2
SPLIT SAMPLE COMPARISON - CORTESE LANDFILL INORGANICS IN SOIL (mg/kg)
iiiliiiiii EPAn-RC MBHL88
10100 J 12.8 UJ 10.2 J 174 J
0.61 J 1.4 UJ
1150J 10.5 J 9.7 J
17.5 J 16400 J
20.9 J 2890 J
693 J 0.24 UJ 17.3 J
1500 J 1.4 UJ 3.3 UJ 187 J 1.4 UJ 12J
91.1 J 1.2 UJ
^;:;:S^^^^SS^^^^^i:^^v'^yo^^--^-:S>^
PRP
7590.00 J 21.10 UJ 9.90 J
126.00 J
1.70 J 2.30 UJ
1060.00 J 5.00 J 4.10 UJ
11.40 UJ 14000.00 J
20.20 J 2040.00 J
559.00 R 0.23 UJ
14.20 UJ 1820.00 J
1.40 U 4.60 UJ
89.50 J 1.80 UJ 8.80 J
77.50 R 14.40 J
RPD
28 NA
3 32
94 NA
8 7 1 *
NA -1-NA -1-
16 3
34 NA NA NA -1-
19 NA NA
71 NA
31 NA NA
iiiiiiiiii EPA/TRC MBHL92
20.3 6.6 J
3J 1.7U
0.24 U 0.73 U
41 U 1.2U 1.5U 1.5U 2.9 4.3 J
41.5 U 0.24 U 0.12 U
3.6 U 111 U
0.73 U 1.7U
52.9 U 0.73 U
1.2U 0.49 U 0.61 U
T^mimm mmm.
PRP
5720.00 11.20 U 2.50 J
108.00 J 1.20 1.20 U
18600.00 J 4.10 3.20 6.10 U
10700.00 1.90 J
1690.00 305.00 R
0.12 U 7.50 UJ
1080.00 0.73 UJ 2.40 U
131.00 0.97 U 4.50
33.60 R 0.61 U
Page 2 of 3
RPD
NA NA +
18 NA
NA NA NA NA NA NA NA
77* NA NA NA NA NA NA NA
NA NA NA
NA NA
siiiiiiii EPA/TRC MBHL93
6480 7.8 UJ 7.6 J
52.2
0.33 0.87 U 408 5.7 7.9 5.9
13500 33.4 J 2850
332 0.39 13.7 132 U
0.87 U 2 U
87.4 0.87 U
4.9 43.7
1.1
lllll illlllli PRP
12800.00 16.30 U 8.10
85.50 J 0.85 1.80 U
1040.00 15.70 12.90 42.50 J
22000.00 4.60 J
3610.00 595.00 R
0.37 R 22.90 J
2020.00 10.60 UJ 3.50 U
232.00 1.40 U
13.90 202.00
0.89 U
RPD
NA NA
6 NA NA NA NA
93* NA NA
48 152* 24
NA NA
50 NA NA NA NA NA NA
129* NA -h
U = Analyte was not detected at the concentration listed. J = Quantitation is approximate due to limitations identified during the quality control review. R = Value was rejected due to laboratory quality control problems. RPD = Relative percent difference; RPD is calculatad only when analytes are detected in both samples. * = Results outside the quantitative comparability goal for split samples - either the RPD > 50% or one or both split samples had a concentration < 5 x CRDL and an absolute difference > 2 x CRDL + = Analyte was detected by EPA/TRC and not by the PRP NR = Data point was not reported NA = Calculation of a quantitative comparability goal was not neccessary.
O o
Table A - l d SPLIT SAMPLE COMPARISON INORGANICS IN SOIL (mg/kg)
CORTESE LANDFILL Page 3 of 3
o o 00
Analyte
Aluminum Antimony Arsenic Barium Beryllium Cadmium Calcium Chromium Cobalt Copper Iron Lead Magnesium Manganese Mercury Nickel Potassium Selenium Silver Sodium Thallium Vanadium Zinc Cyanide
CRDL
40 12 2
40 1 1
100 2 4 5
20 0.6
1000 3
0.04 8
1000 1 2
1000 2
10 4 2
SS'13 EPA/TRC
MBHL90
3970 3UJ
2.8 42.8 0.27 0.51 U 863 3.7 5.9 9.9 J
8560 12.1 J 1940
394 0.11 U
8.7 460 0.24 U 0.54 U 71.9
0.1 U 3.3
41.2 J 0.12 U
PRP
5880.00 11.80 UJ 4.90
52.70 0.51 U 1.30 U
939.00 9.20 J 6.90
12.30 J 13400.00
11.30 J 2190.00 423.00 J
0.13 UJ 11.10
1450.00 0.77 U 2.60 U
83.90 1.00 U 7.00
44.90 0.64 U
RPD
39 NA
55 NA NA NA NA
85 ' NA
22 44
7 12 7
NA NA NA NA NA NA NA NA
9 NA
88-15 EPA/TRC
MBHL91
6990 3.5 UJ 4.8
52.2 0.34 0.58 U 696 7.5 9.1
48.4 J 16300
18.6 J 2460
565 0.12 U 16.5 581 0.28 U 0.61 U 84.6 0.14
8 88.1 J 0.51
PRP
6900.00 11.80 UJ 4.50
41.30 0.51 U 1.30 U
573.00 10.20 J 5.40
14.00 J 13900.00
13.70 J 2060.00 346.00 J
0.13 UJ 11.70
737.00 0.77 U 2.60 U
87.50 1.00 U 7.80
67.00 0.75
RPD
1 NA
6 NA NA NA NA
31 NA
110* 16 30 18 48
NA 34
NA NA NA NA NA NA
27 NA
U = Analyte was not defected at the concentration listed. J = Quantitation is approximate due to limitations identified during the quality control review. R = Value was rejected due to laboratory quality control problems. RPD = Relative percent difference; RPD is calculated only when analytes are detected in both samples. * = Results outside the quantitative comparability goal for split samples -• either the RPD > 50% or one or both split samples had a concentration < 5 x CRDL and an absolute difference > 2 x CRDL + = Analyte was detected by EPA/TRC and not b^ jM PRP NR = Data point was not reported ^ ^ B NA = Calculation of a quantitative comparability g M R a s not neccessary.
€*5 €0 O O
CO o o CO
Table A-2a
Analyte
Chloromethane
Bromomethane .
Vinyl Chloride
Chloroethane Methylene Chloride Acetone
Carbon Disullide
1,1-Dichloroelhene
1,1-Dichloroethane
cis-1,2-Dichloroelhene trans-1,2-Dichloroethene Chloroform 1,2-Dichloro6thane
2-Bulanone
1,1,1-Trichloroethane Caibon Tetrachloride
Bromodichloromethane 1,2-Dichloropropane
cis-1,3-Dichloropropene Trichloroethene
Dibromochloromethane
1,1,2-Trichloroethane
Benzene
trans-l .S-Dlchloropropene Bromoform
4-Methyl-2-Pentanone 2-Hexanone
Tetrachloroethene
1,1,2,2-Tetrachloroethane Toluene
Chlorobenzene Ethylbenzene Styrene
Xylene (total)
1,2-Dibromo-3-Chloropropane
1,3-Dichlorobenzene 1,4-Dichlorobenzene
1,2-Dibromoethane 1,2-Dichlorobenzene
SPUT SAMPLE COMPARISON - SErCORTESE LANDFILL
VOLATILE ORGANICS IN WATER (ug/L)
m' ^ 1 EPA/TRC
SB3547
1U
1 U
1 U
1 U 2 U
R
1 U 1U
1 U
1 U 1U
1 U 1 U
9 J
1 U 1 u
1 u 1 u 1 u 1 u
1 u
1 u 1 U
1U 1U 5 U
R 1 U
1 U
1 U
1 U 1 U 1U
1 u 1 u
1 U
1 J
1 u 1 u
PRP
1U
1U
1 U
1U
1U
R
1U
1U 1U
1 U 1U
1U
1 u
R
1 U 1 U
1 u 1 UJ 1U
1 u
1 u
1U 1U
1U
1U 5 U
R 1U
1 U 1 U
1 U 1 U 1U
1 u 1 u
1U
1U
NR 1 U
RPD
NA
NA
NA
NA
NA
NA
NA
NA NA
NA NA
NA NA
NA
NA NA
NA NA NA NA
NA
NA
NA
rA NA NA NA
NA
NA NA
NA NA
NA
NA NA
NA NA +
NA NA
$W-U \ EPA/TRC
SB3548
1U
1U
1 U
1 U 2 U
R
1 U
1 U
1 U 1 U 1U
1 U 1 U
R 1 U 1 U 1U
1 U 1 U 7 U
1 U
1U
2 U
1 U 1 U SU
R
U
1 U
1 U
1 U 1 U
1 U
1 U 1 U
O.SJ
4
1 U 0.8 J
PRP
1 UJ
1 U
1 U
1 U 3UJ
R 1 U
1 U 3
1 U 1 U
1 U 1 U
R 1 U 1 U
1 U 1 UJ 1 U 5
1 U
1 U
1
1U 1 U
1 u
R 0.6 J
1 U
1 U
0,9 J 1 U
1U
1 U
R
1U 3
NR 0.6 J
RPD
NA
NA
NA
NA NA
NA
NA
NA
NA
NA NA
NA NA
NA NA NA
NA NA
NA NA
NA
NA
NA
NA NA
NA NA
50
NA
NA
NA NA
NA
NA NA
NA +
29
NA
29
w«ii:iiiiilii^^ EPAyTRC
SB3543
1 U
1 U
1UJ
4 J
1 U
R 1 U
1 U 13J
1 U 1 U
1 U 1 U
R 2 J 1 U
1 U 1 U
1 U 1 J
1 U
1 U
9 J
1U
1 U 5 U 5 U
l U
1 U 38 J
11 J 17J
1 U
50 J 1 U
3 J 15J
1 U 5 J
PRP
28 UJ
28 U
28 UJ
28 U 56 UJ
140 R
28 U
28 U 28 U
28 U 28 U
28 U 28 UJ
140 R 28 U 28 U
28 U 28 U 28 U 28 U
28 UJ
28 U 28 U
28 U 28 U
140 R 140 R
28 U
28 U
610
14J 24 J
28 U
79 28 U
28 U
22 J
1 U 28 U
RPD
NA
NA
NA
NA +
NA NA
NA
NA
NA +
NA NA
NA NA
NA NA + NA
NA NA
NA NA +
NA
NA
NA +
NA
NA
NA NA
NA
NA 177*
24 34
NA 45
NA
NA + 38
NA NA +
U - Analyte was not dotsctod at the conoentration listed. J - Quantitation is approximate due to limitations identified during the quality control review. R - Value was rejected due to laboratory quality control problems. RPD - Relative percent difference: RPD Is calculated only when analytes are detected in both samples. * • Results outside the quantitative oomparabiiity goal for split samples - RPD > 50% * m Analyte was detected by EPA/TRC but not by the PRP. NR - Data point was not reported. NA - Calculation of a quantitative comparability goal was not neccessary
Table A-2a SPLIT SAMPLE COMPARISON - SEICORTESE LANDFILL VOLATILE ORGANICS IN WATER (ug/L)
Analyte
Chloromethane Bromomethane
Vinyl Chloride Chloroethane
Methylene Chloride Acetone
Carbon Disulfide
1,1-Dichloroethene 1,1.Dichloroethane
cis-1,2-Dichteroethene
trans-1,2-Dichloroethene Chloroform 1,2-Dichloroethane 2-Butanone
1,1,1-Trichloroethane Carbon Tetrachloride
Bromodichloromethane 1,2-Dichloropropane
cis-1,3-Dichloropropene Trichloroethene
Dibromochloromethane
1,1,2-Trichloroethane
Benzene
trans-1,3-Dichloropropene Bromoform 4-Methyl-2-Pentanone 2-Hexanone
Tetrachloroethene
1,1,2,2-Telrachloroef hane Toluene Chlorobenzene Ethylbenzene
Styrene Xylene (total) • 1,2-Dibromo-3-Chloropropane
1,3-Dichlorobenzene 1,4-Dichlorotienzene
1,2-Dibromoethane 1.2-Dichlorobenzene
Mw.«e 1 EPA/TRC
SB3544
1 U
1U
1 UJ 4
1 U
R 1 U
1 U 20
1 U 1 U
1U 1 U
R
1 U 1 U
1U 1U
1 U 1 u
1 u
1 u 3
1 U 1 u 5 U 5 U
1 U 1U
1 U 1 U 1 U
1 U
1 U 1 U
2 9
1 U 1 U
PRP
1U
1 U
1 U 3 2UJ
5R
1 U
1U
23 1 U
1 u 1U
0.8 J
5R 1U
1U
1U
O.SJ
1 u 1 u 1U
1U
3
1U 1 U 5 U 5R
1U
1 U 1 U 4 1 U
1 U
1U
1 UJ
1U 1 U
1 U 1 u
RPD
NA
NA
NA 29
NA NA
NA
NA 14
NA NA
NA NA
NA
NA NA
NA
NA
NA NA NA
NA 0
NA NA
NA NA
NA
NA NA NA NA
NA
NA NA
NA + NA +
NA NA
mmmmmmmmmmm EPA/TRC
SB3545
4UJ
4UJ
4UJ 4UJ
4UJ
R 4UJ
4UJ
11 J 4UJ 4UJ
4UJ 4UJ
20 UR
4UJ 4UJ
4UJ 4UJ
4UJ 8 J 4UJ
4UJ
6 J
4UJ 4UJ
20 UJ 20 UJ
4UJ
4UJ 76 J
4 J 4UJ
4UJ
17J 4UJ
4UJ 7 J
4UJ
NR
PRP
7 U 7 U
7 U 7 U 7 U
14 UJ
36 R
7 U
11 7 U 7 U
7 U 7 U J
36 R
7 U 7 U
7 U 7 U
7 U
10 7 U 7 U
6 J
7 U 7 U
36 U 36 R
7 U
7 U
97 7 U 7 U
7 U
13 7 U J
7 U
5 J 7 U J 7 U
RPD
NA
NA
NA NA
NA NA
NA
NA 0
NA NA
NA NA
NA
NA
NA
NA NA
NA 22
NA
NA
0
NA NA
NA NA
NA
NA 24
NA + NA
NA
27 NA
NA
33
NA NA
U - Analyte was not detected at the concentration listed. J - Quantitation is approximate due to limitations identified during the quality control review. R - Value was rejected due to laboratory quality control problems. RPD - Relative peroent difference; RPO is calculated only when analytas are detected in both samples. ' - Results outside the quantitative oomparabiiity goal for split samples - RPD > 50% • - Analyte was detected by EPA/TRC but not ijy the PRP NR • Data point was not reported. NA - Calculation of a quantKative comparatiility goal was not neccessary.
j Table A-2b
1 Analyte
Phenol !bs(2-Chloro9thyl)Ether
i 2-ChlorophBnol 11,3-Dichloroben28ne
11 ..i-Oichlorobenzene
1.2-DichlorobBn2en8 J2-Methylphenol j bB(2-ChlorDisopropyl)Ether
14-Methylphenol 1 N-Nitroso-Di-n-Propylamine 1 Hexachloroetfiane 1 Nitrobenzene 1 IsoDtiorone
; 2-Nitroph9nol
|2.'i-Dimethylph9nol
j Benzoic Acid (1) i bJS(2-Chloro8thoxy)Methan8 2.^DichlQroph8nol
j 1.2.4-Trichlorobenzene
Naphthalene 4-Chloroaniline
Hexachlorobutadiene 4-Chloro-3-lvlBthylphenol 2-Methylnaphthal8ne
i Hexachlorocyclopentadiene j 2.4 6-Trichioroptienol
2.4.5-Trichlorophenol 2-Chloronaphthalen8.
!2-Nitroanilin8 1 Dimethyl Phthalate
\Acsnaphthyiena
i2.5-Dinitrotoluene
13-Nitroaniline
j Acenaphthene j2.4-Dinitrophenol
j4-Nitro phenol 1 DitJenzofuran j2.4-Dinitrotoluene
Diethylphthalate 14-Chlorophenyl-phenylether Fiuorene
[ 4-Nitroaniiine
j4,S-Dinitro-2-Methylphenol
j N-Nitrosodiphenylamine i4-8romophenyl-phenylelher
Hexachlorobenzene
Pentachlorophenol
I Phenanthrene
Anthracene Carbazole
Di-n-Butylphthalate
Fluoranthene Pyrene
Butylbenzylphthalate 3.3'-Dichlorobenzidine
Benzo(a)Anthracene
Chrysene
bis(2-Ethylh8xyl)Phthalate
Di-n.Octyl Phthalate
B9nzo{b)Fluoranth8ne B8nzo{k)Fluoranth8ne Benzo(a)Pyrene
lndeno(1,2,3-cd)Pyr8ne
Dibenz(a,h)Anthracene
Benzo{g,h,i)Perylen8
SPUT SAMPLE COMPARISON . CORTESE LANDFILL SEMI-VOLATILE ORGANICS IN WATER (ugrtj
ISMMB EPA/TRC
10 U
10 U 10 u
2 J 15
4 J 10
10 u
u
10 u 10 UJ 10 u 10 u 10 u
8 J NR
10U 10 U
5 J
10
10 U
10 U 10U 4 J
10 U 10U
25 UJ 10 U 25 U 10 U
10 U
10 U 25 UJ
10U
25 U
25 UJ lOU
10 u
2 J 25 U 25 U
25 U
25 U
10U 10 UJ
10 U
25 U
10U
10U 10U
10U
10U
10 U 10 u
10 u
10 u
10U 4 U
10 U
10 u
10 U 10 U
10 u
10 u
10 u
M M M M m i i IPRP
10 u
10 u 10U 2 J
15
4 J 9 J
10 U 14
10 U 10U 10U 10 U
10 U 6 J
2 J
10 u
10 U 6 J
10 U
10 u 10 u 3 J 4 J
10U
10 U
25 U 10 U
25 U 10 U
10 u 10 u
25 U
10 U
25 U
25 U 10 U 10 U
3 J
10 U 10 U
25 U
25 U
10 U 10 U
10 U
25 U
10 U
10 U 10U
1 J
10 U
10 U 10 U
10 u
10 U
10 u 10 UJ
10 UJ
10U
10 u 10 u
10 u
10 u
10U
I R P D
NA
NA NA
0
0
0 NA
NA
NA
NA NA NA NA NA
29 NA
NA
NA
18 NA
NA
NA f ^
0 NA
NA
NA NA NA NA
NA
NA NA
NA
NA
NA NA
NA
40 NA NA
NA
NA
NA NA
NA
NA
NA
NA
NA
NA
NA
f ^ NA
NA
NA
NA NA
NA
NA NA
NA
NA j
NA NA
[ M W i » ; H ; » ; EPA/TRC
IsGETg
lOU
10 u 10U
10 U
9 J
2 J 10 U
' t o u
10 u
10 u 10 u lOU 10 u 10 u
10 UJ NR
10U
10 u
10 u 10 u
10 u
10 u 10 u 10 u
10 u 10 u
25 U 10 U
25 U 10 U 10 u
10U 25 UJ
10U
25 U
25 UJ 10 U
10 U
10 U
10 u 10 u
25 U
25 U
10 U 10 U 10 U
25 U
10U
10U 10 U
10 U
10 U
10 U
10 u 10 u
10 u
10 u 10 u
10 u
10 u
10 u 10 u
10 u
10U
10U
m r n m r n s m PRP
10 u
10 u 10 U
2 J
10
2 J 10 U
1 10 u
10 u
10 u 10 u 10 u 10U 10 u
10 u
100 u 10 u
10U
u 10 u
10 u
t o u 10 u 10 u 10 u
t o u
25 U 10 u
25 U
10 U 10 U
10 u 25 U
10 u
25 U
25 U 10U
10 U
10 U 10 U 10 U
25 U
25 U
10 U 10 U 10 U
25 U
10 U
10U 10 U
10U
10 U
10 U
10 U 10 u
10 u
10 u 10 u
10 u
10 u
10 u 10 u
10 u
t o u
10 u
Pa9«1c4 2
JRPD
NA
NA
NA
l>IA
11 0
NA
NA
NA
NA f>IA
NA fvIA
NA f ^
NA
NA
NA
NA f>IA
NA
NA NA NA
f>JA
NA f>IA
NA
NA f ^ NA
NA NA
NA
NA
NA NA NA
t ^
NA NA
NA
NA
NA NA
NA
NA
NA
NA
NA
NA
NA
r>IA
NA
NA
NA
NA NA
NA
NA NA NA
NA
NA
NA
; i i w « G i
i EPA/TRC •;BGE80
i 10 U
i 10 U i 10 U
10 U
i *•' ! ' J 1 10 u
i \ 10 u
1 10 u i 10 u 1 10 u
10 u
10 u u
; NR
j 10 u 1 10 u
1J 10 u
10 u
10 UJ
1 10 u i 10 u
2SU
10 u
25U 1 10 u
25U
i 10 u 1 10 u
10 u 25 U
10 U
25 U
25 U 10 U
10 U
10U
10 U 10 U
R
25U
10 U 10 U 10 u
25U
10 U
10 U 10 UJ
10 U
10 U
10 u 10 UJ
10 u
10 u
10 u 10 UJ
10 UJ
10 u
10 u 10 u
10 u
10 u 10 u
I P R P
10 u
1 10 u j 10 u
1 1J
1 ° 6 J 10 u
10 u
10 u
10 u 10 u 10U 10 u 10 u
10U 100 u
10 u
10 u
2 J 10 u
10 u
10 u 10 u 10 u
10 u
10 u 25 U 10 u
25 U 10 u 10 u
10 u 25 U
10 u
25 U 25 U 10 u 10 u
10 u
10 u 10 u
25 U
25 U
10 u
10 u 10 UJ
25 U
10 U
10 U 10 u
10 u
10 u
10 u 10 u
10 u
10 u
10 u 10 UJ
10 UJ
10 u
10 u 10 u
10 u
10 u
10 u
I R P D
NA
NA NA NA
8 6 -1 4 3 '
NA NA
NA
NA NA f ^ NA NA
NA +
NA 1 ^
NA
6 7 '
NA NA
NA
NA NA NA
NA NA NA
f ^ NA
NA
NA NA
NA 1 NA 1 NA NA
NA
NA NA NA
NA
NA
NA NA NA
NA
NA
NA NA
NA
NA
NA NA
NA
NA
NA NA
NA
NA
NA NA
NA
NA
NA
U - Anajyts was not d«t»ci»d at the conc«nration listod. J ' Quanbtabon m apprceonato du» to limiialicne idanliftad during Ih* quality contrd raviaw. R > V«)u* was f0i*ct»d dua to laboratory quality control profaiania. RPO - RaJaliva parccnt d^ffaranca; RPO is calculatad only Mhan analytaa ara datactad in both umptai * - Racults outsida ttia <^antitatrvo comparabiity goai for sff t samplas - RPO > 50% * • An^yta waa dalaclad by EPA/TRC but not by t ia PRP. NR - Data pdnl waa not raportad
4A a Calculation of a quanOtativa oomparabiiity goal was not naccaasory.
t -Baruoie add is rx>t a TCL compound but anaiyzad by PRP
300832
Table A-2b SPUT SAMPLE COMPARISON - CORTESE LANDFILL SEMI-VOLATILE ORGANICS IN WATER (ug/L)
P a g e 2 a l 2
Analyte
Phenol bis(2-Chloroethyl)Eth8r 2.Chlorophenol 1,3-Dichlorobenzen8 1,4-Dichlorobenzen8 1,2-Oichlorobenzene 2-Methylphenol bis(2-Chloroisopropyl)Ether 4-M8thyiphenol N-Nitroso-Oi-n-Propylamine Hexachloroetf^ane Nitrobenzene Isophorone 2-Nilrophenol 2.4-Dimethylphenol Benzoic Acid (1) bis(2-Chloro6thoxy)Methane 2,4-Dichlorophenol 1,2.4-Trichlorobenzene Naphthalene 4.Chloroaniline Hexachlorobutadiene
14-Chloro-3-Methylphenol 12-M8thylnaphthal6ne ! Hexachlorocyclopentadiene 12,4,6-Trichlorophenol 2,4.5-Trichlorophenol 2-Chloronaphthai8ne 2-Nitroaniline Dimethyl Phthalate Acenaphthylene 2.6-Dinitrotoluene 3-Nitroaniline Acenaphthene
!2,4-Dinitrophenol j 4-Nitrophenol Dibenzoturan 2,4-Dinitrotoluen8 Diethylphthalate 4-Chiorophenyl-ph8nylether Fluorene 4-Nitroaniline
4,6-0initro-2-i\/lethyiphenol N-Nitrosodiphenylamine 4-Bromopnenyl-phenylether Hexachlorobenzene Pentachlorophenol Phenanthrene Anthracene Carbazole Di-n-Butylphthalate Fluoranthene Pyrene
Butylbenzylphthalate 3.3'-Dichlorobenzidine Benzo(a)Anthrac8ne Chrysene
b is(2- Ethylhoxyl) Phthalate DJ-n-Octyl Phthalate Benzo(b)Fluoranthene Benzo(k)Fluoranthene Benzo(a)Pyrene lndeno(1,2,3-cd)Pyrene Dibenz(a,h)Anthrac8ne Benzo(g,h,i)Peryleno
s w t . a EPAH'RC BQEB2
10 U 10 U 10 U lOU 3 J
10 U 10 U 10 U 10 U 10 U 10 U 10 U 10 U lOU 10 UJ
NR 10 U 10 U 10 u 10 u lOU 10 u 10 u 10 u 10 u 10U
25U 10 u
25U
10 U
10 U
10 U
25U 10 U
25 U
25 UJ
lOU
10 U
10U
lOU 10 U 25 U
25 U
10 U 10 U
10 U
2SU
10 U
10 U
10 U 2 J
10 U
10 U 10 U
10 U
10 U
lOU 10 u 10 u
10 u
10 u 10 u
10 u
10 u
10 u
PRP
10 UJ 10 UJ 10 UJ 10 UJ 3 J
10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ
7J 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 25 U 10 UJ 25 U 10 UJ 10 UJ 10 UJ 25 UJ 10 UJ 10 UJ 25 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 25 UJ 25 UJ 10 UJ 10 UJ 10 UJ 25 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ 10 UJ
RPD ®W»1t •EPA/TRC !BGE83
NA NA NA NA
( NA NA NA NA
NA NA NA NA
NA
NA NA NA
NA
NA NA NA
NA
NA
NA NA NA NA NA NA f ^ NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
27 10 U 10 U 10 U 10 U 10 U 10 U 10 U 75 10 U 10 U 10 U 10 U 10 U 10 UJ
NR 10 U 10 U 10 U l O U 10 U 10 UJ 10 u 10 u 10 UJ
10 u 25 U
10 U
25 U
10 U
10 U
10 U 25 UJ
10 U
25 U R
10 U
10 U 1 J
10 U 10 U
25 UJ 25 U
10 U 10 U
10 U
25 U
lOJ
10 U
10 UJ
10 J
10 J
10 J 10 U
10 U
10 U
10 U 10 UJ 10 UJ 10 u
10 u 10 u
10 u
10 u
10 u
PRP
2 J 10 u 10 u 10 u 10 u 10 u 10 u 10 u 10 u 10 UJ
10 u 10 u 10 u 10 u 10 u
7J
10 u 10 u 10 u 10 u 10 u 10 u 10 u 10 u 10 u 10 u 25 U 10 u 25 UJ 10 u 10 u 10 u 25 UJ 10 u 25 U 25 U 10 u lOU lOU 10 u 10 u 25 U 25 U 10 U 10 U
l o u
2 J 10 U 10 U 10 u 10 u 10 u 10 u 10 UJ 10 u 10 u 10 u 10 u 10 u lOU lOU 10 u 10 u 10 u 10 u
RPO
NA NA NA NA NA NA NA NA l>IA NA NA NA NA I4A I>1A NA NA NA NA NA fvlA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA NA NA NA f<IA NA NA NA f M NA NA NA NA NA NA NA NA NA NA NA NA NA NA f M NA NA
U - Anilyto waft not dfttoctod at the ooncankalion fislad. J - QuanMaljon ts apprcKJmato dua to limitationft idantfiad Airing tha quality contrd rvtnaw. R > Vaiua was rqactad dua to laboratory quaity conrol problama RPD - Ralaliva parcant diffaranoa; FVO is calculatad only whan analytaa ara datactad in tMtfi samfjas. * - Raaulb outsida tha cfjantitabva cocnparabiily god for sf^lit samplas - RPD > 50V. * . Analyta waa dMacM by EPA/TRC but not by t>a PRP. NR - Data poalt was not raportad NA - Calculalion ol a qjantitativa oomparabiiity goai was not naccaesary.
300833
§ ^•. >
CO o o OD CO
Table A-2c
Analyte
alpha-BHC
beta-BHC delta-BHC Lindane Heptachlor Aldrin Heptachlor epoxide Endosulfan 1 Dieldrin 4,4'-DDE Endrin Endosulfan II 4,4'-DDD Endosulfan sulfate 4,4'-DDT
Methoxychlor Endrin ketone
Endrin aldehyde alpha-Chlordane gamma-Chlordane Toxaphene Aroclor-1016 Aroclor-1221 Aroclor-1232 Aroclor-1242 Aroclor-1248
Aroclor-1254 Aroclor-1260
SPLIT SAMPLE COMPARISON - CORTESE LANDFILL PESTICIDE/PCBs IN WATER (ug/L)
WK^^mi^i^Mi EPAn-RC
BGE78
0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U
0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0.5 U 0.1 U
0.1 U 0.05 U 0.05 U
5U 1 U 2U 1 U 1 U 1 U 1 U 1 U
U = Analyte was no J = Quantitation is i
PRP
NR
NR NR NR NR NR NR NR NR
NR NR NR NR NR NR NR NR
NR NR NR NR NR NR NR NR NR NR NR
t detected at the co ipproximate due lo
RPD
NA NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA
ncentration 1 imitations id
Page 1 of 2
WMMS^mm^^m EPA/TRC
BGE79
0.05 U
0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U 0.05 U
0.1 U
0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0.5 U 0.1 U
0.1 U 0.05 U 0.05 U
5U 1 U 2U 1 U 1 U 1 U 1 U 1 U
sted. entified during the q
PRP
NR
NR NR NR NR NR NR NR NR
NR NR NR NR NR NR NR NR
NR NR NR NR NR NR NR NR NR NR NR
ualily control review
RPD
NA
NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA
ililiiiiiH ^ ^ ^ ^ ^ EPA/TRC
BGEBO
0.05 U
0.05 U 0.05 U 0.05 U 0.05 U
0.05 U 0.05 U 0.05 U
0.1 U 0.1 U 0.1 U 0.1 U
0.1 U 0.1 U
: 0.1 U 0.5 U 0.1 U
0.1 U 0.05 U 0.05 U
5U 1 U 2U 1 U 1 U 1 U 1 U 1 U
PRP
NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR
NR NR NR NR NR NR NR NR NR NR NR
RPD
NA
NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA
NA NA NA NA NA NA NA NA NA NA NA
R = Value was rejected due to laboratory quality control problems. RPD = Relative percent ditlerence; RPD is calculated only when analytes are detected in both samples. * = Results outside the quantitative comparability goal (or split samples - RPD > 50% + = Analyte was detected by EP/VTRC but not by the PRP. NR = Data point was not reported. NA •< Calculation of a quanlilaliva compar^llity goal was not neccessary.
^ ?
Table A-2c SPLIT SAMPLE COMPARISON - CORTESE LANDFILL PESTICIDE/PCBs IN WATER (ug/L)
Page 2 of 2
Analyte
^ alpha-BHC beta-BHC delta-BHC
Lindane
Heptachlor Aldrin Heptachlor epoxide Endosulfan I Dieldrin 4,4'-DDE Endrin Endosulfan II 4,4'-DDD Endosulfan sulfate 4,4'-DDT Methoxychlor Endrin ketone Endrin aldehyde alpha-Chlordane gamma-Chlordane Toxaphene Aroclor-1016 Aroclor-1221 Aroclor-1232
Aroclor-1242 Aroclor-1248 Aroclor-1254 Aroclor-1260
SW-IZ EPA/TRC
BGE82
R 0.050 U 0.050 U
0.050 U
R 0.050 U 0.050 U 0.050 U
0.10 U
R 0.10 U 0.10 U 0.10 U 0.10 U 0.10 U 0.50 U 0.10 U 0.10 u
0.050 U 0.050 U
5.0 U 1.0 U 2.0 U 1.0 U
1.0 U 1.0 U
1.0 U 1.0 U
PRP
RPD
0.05 U 0.05 U 0.05 U
0.05 U 0.05 U 0.05 U 0.05 U 0.05 U
0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0.5 UJ 0.1 U 0.1 U
0.05 U 0.05 U
5U 1 U 2 U 1 U 1 U 1 U
1 U 1 U
NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
SW-I I EPA/TRC BGE83
0.050 U 0.050 U 0.050 U
0.050 U
R R
0.050 U R
0.10 U
R 0.10 U
R 0.10 U 0.10 U
0.012 J 0.011 J 0.10 U 0.10 U
0.0012 J 0.050 U
5.0 U 1.0 U 2.0 U 1.0 U
1.0 U 1.0 U
1.0 U 1.0 U
PRP
0.05 U 0.05 U 0.05 U
R 0.05 U .0.05 U 0.05 U 0.05 U
0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0.1 U 0.1 U
. 0.5 UJ ;.0.1 U
0.1 U 0.05 U 0.05 U
5U 1 U 2 U 1 U 1 U 1 U 1 U 1 U
RPD
NA NA NA,
NA NA NA NA NA NA NA NA NA NA'
NA NA NA NA NA NA NA NA NA NA NA
NA NA
NA NA
U = Analyte was not detected at the concentration listed. J = Quantitation is approximate due to limitations identitied during the quality control review. R = Value was rejected due to laboratory quality control problems. RPD = Relative percent difference; RPD Is calculated only when analytes are detected in both samples. * 3 Results outside the quantitative comparability goal for split samples - RPD > 50% + = Analyte was detected by EPA/TRC but not by the PRP.^ NR = Data point was not reported. NA = Calculation ol a quantitative comparability goal was nS^^R^ssary.
o o CD C0
Table A-2d
Analyte
Aluminum Antimony Arsenic Barium Beryllium Cadmium Calcium Chromium Cobalt Copper Iron Lead Magnesium Manganese Mercury Nickel Potassium Selenium Silver Sodium Thallium Vanadium Zinc Cyanide
SPLIT SAMPLE COMPARISON • CORTESE LANDFILL INORGANICS 1 IN WATER (ug/L)
CRDL
200 60 10
200 5 5
500 10 50 25
100 3
5000 15
0.2 40
5000 5
10 5000
10 50 20 10
iiiiiliiiiiiiii EPA/TRC MBHL83
2250 27 U
91.6 533
1 U 3 U
16100 5 U 6 U
6.8 42600
20.4 3490
12900 0.2 U 15 U
8750 J 3 U 7 U
9260 J 3 U
5.9 47.5
10 UJ
PRP
14700.00 J 36.00 U 90.60 J
662.00 1.00 U 5.00 U
15400.00 15.70 18,60 27.00
61100.00 38.40
5700.00 10700.00 R
0.20 U 28.10
9320.00 3.00 UJ 7.00 UJ
7500.00 40.00 UJ 8.00
171.00 J 10.00 U
RPD
147* NA
1 22
NA NA
4 NA NA
120 36 61 * 48
NA NA NA
6 NA NA
21 NA
30 NA NA
iiiiiiiiiii EPA/TRC MBHL82
250 27 U
52,1 312
1 U 3 U
8880 5 U 6U 6U
14500 2.6
2220 5860
0,2 U 15 U
5110J 3U 7U
5560 J 3U 5 U
10.6 ,, 10 UJ
:!:!:::^!^!:^^;;!:;^!:!^;:i:i:fe^
PRP
215.00 J 36.00 U 36.60 J
326.00 1.00 U 5.00 U
8860.00 8.00 U 8.00 U 4.00 U
11000.00 , 2.90 J
2090.00 5430.00 R
0.20 U 17.00 U
5040.00 3.00 UJ 7.00 UJ
4850.00 4.00 UJ 6.00 U
68.60 J 10.00 U
Page 1 of 2
RPD
15 NA
35* 4
NA NA
0 NA NA NA
27 11 6
NA NA NA
1 NA NA
14 NA NA
146* NA
iiiliiiiii EPA/TRC MBHL78
200 U 60 U 55
835 5 U 5 U
39000 38 50 U 25 U
53500 3
8000 14000
0.2 U 40 U
15000 5 U
10U 10000
10U SOU 20 U
11
Hiiiiiiiii PRP
163.00 36.00 U 57.80
862.00 1.00 U 5.00 U
41100.00 8.00 U 8.00 U 4.00 U
55400.00 2.00 U
8150.00 14000.00
0.20 U 17.00 U
15300.00 3.00 UJ 7.00 U
10100.00 4.00 UJ 6.00 U 4.10
10.00 U
RPD
NA NA
5 3
NA NA
5 NA + NA NA
3 NA
2 0 +
NA NA
2 NA NA
1 NA NA NA NA -1-
U = Analyte was not detected at the concentration listed. J = Quantitation is approximate due to limitations identified during the quality control review. R = Value was rejected due to laboratory quality control problems. RPD = Relative percent difference; RPD is calculated only when analytes are detected in both samples. ' = Results outside the quantitative comparability goal tor split samples - either the RPD > 50% or one or both split samples had a concentration < SxCRDL and an absolute difference > CRDL + = Analyte was detected by EPA/TRC and not by the PRP NR = Data point was not reported NA = Calculation of a quantitative comparability goal was not neccessary.
Table A-2d SPLIT SAMPLE COMPARISd^*(iORTEaEst>5^li5|^^ INORGANICS IN WATER (ifgi^i^J
!^iGif^2^
Analyte
Aluminum Antimony Arsenic Barium Beryllium Cadmium Calcium Chromium Cobalt Copper Iron Lead Magnesium Manganese Mercury Nickel Potassium Selenium Silver Sodium Thallium Vanadium Zinc Cyanide
CRDL
200 60 10
200 5 5
500 10
50 25
100 3
5000
15 0.2 40
5000 5
10 5000
10 50 20 10
MW-2B EPA/TRC MBHL79
200 U 60 U 10U
200 U 5 U 5 U
12000
13 50 U 25 U
153 3 U
5000 U 1480
0.2 U 40 U
5000 U 5 U
10U 32000
10U 50 U 20 U 10U
PRP
93.10 36.00 U
3.00 U i 134.00
1.00 U 5.00 U
13000.00 8.00 U 8.00 U 4.00 U
108.00 2.00 J
2970.00 1500.00
0.20 U 17.00 U
3870.00 3.00 UJ' 7.00 U
32200.00 4.00 UJ 6.00 U 4.00 U
10.00 U
mm- .
NA '
^ ^ NA--
NA NA
8 NA -I-NA NA
34 NA NA ; 1 NA NA;
N A
m NA
1 NA NA NA NA
^0 jm^ . fn^ m&^
363
•' . 3 ^ ^ '••
230^'-" : 5 J U -
10 u 50 U 25 U
SQiOfim >
40 M i 500(iU :
5,0 U 10 U
fsoob' 10.0 u
50 U 20 U 10 U
730:00 ; 36.o©iyiU • 32Mf'^J
: 2i5*5Miw "
1.00;U.y
S.OQy;;^
17000.00
8.0a4J,w
8:^0i^J.i-
4;p)paj
48iO;iO ; i-40--: '
; 3300.00 13200.00 •
0.20 U 17.00 U
2640.00 3.00 UJ 7.00 U
121'00.00 4.00 UJ 6.00 U
25.10 10.00 U
: .65^^
:• iP-':
I • 7
6
NA N A
NA,
NA NA
10
NAv
M r
NA
7 NA NA NA NA
U = Analyte was not detected at the concentration listed. J = Quantitation is approximate due to limitations identified during the quality control review. R = Value was rejected due to laboratory quality control problems. RPD = Relative percent difference; RPD Is calculated only when analytes are detected in both samples. * = Results outside tha quantitative comparability goal for split samples -- either the RPD > 50% or one or both split samples had a concentration < SxCRDL and an absolute difference > CRDL + = Analyte was detected by EPA/TRC and not b^ i ie PRP NR = Data point was not reported NA = Calculation of a quantitative comparability
b ^ i e
l^as not neccessary.