Document 15VgrYL1OmzzG09kba0oE3Y8q
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JULY 2002 SURFACE WATER MONITORING REPORT FOR WASHINGTON WORKS FACILITY AND LOCAL, LETART AND DRY RUN LANDFILLS WASHINGTON, WV
Date: September 2002
Project No.: D6WW7423.01 18983635.20000
CORPORATE REMEDIATION GROUP An Alliance between
DuPont and URS Diamond
Barley Mill Plaza, Building 27 Wilmington, Delaware 19805
Surface water Monitoring Report
Table of Contents
TABLE OF CONTENTS
1.0 Introduction...................................................................................................................1 2.0 C-8 Analytical Reporting.............................................................................................2 3.0 Washington WorksFacility..........................................................................................3 4.0 Local Landfill............................................................................................................... 4 5.0 Letart Landfill.............................................................................................................. 5 6.0 Dry Run Landfill.......................................................................................................... 6 7.0 References.................................................................................................................... 7
Table 1.0 Table 2.0 Table 3.0 Table 4.0
Figure 1.0 Figure 1.1 Figure 1.2
Figure 2.0 Figure 2.1 Figure 2.2 Figure 3.0 Figure 3.1 Figure 3.2 Figure 4.0 Figure 4.1 Figure 4.2
TABLES C-8 in Surface Water - Washington Works Facility C-8 in Surface Water - Local Landfill C-8 in Surface Water - Letart Landfill C-8 in Surface Water - Dry Run Landfill
FIGURES Site Location Map - Washington Works Facility Surface Water Sample Location Map - Washington Works Facility C-8 Concentration Map July 2002 - Washington Works Facility Surface Water Site Location Map - Local Landfill Surface Water Sample Location Map - Local Landfill C-8 Concentration Map July 2002 - Local Landfill Outfalls Site Location Map - Letart Landfill Surface Water Sample Location Map - Letart Landfill C-8 Concentration Map July 2002 - Letart Landfill Outfalls Site Location Map - Dry Run Surface Water Sample Location Map - Dry Run Landfill C-8 Concentration Map July 2002 - Dry Run Landfill Outfalls
JULGMR.doc Sep. 17. 02 Wilmington, DE
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Surface water Monitoring Report
Table of Contents
Appendix A Appendix B Appendix C Appendix D Appendix E Appendix F Appendix G Appendix H
APPENDICES Laboratory Analytical Data Reports - Washington Works Facility Chain-of-Custody Records - Washington Works Facility Laboratory Analytical Data Reports - Local Landfill Chain-of-Custody Records - Local Landfill Laboratory Analytical Data Reports - Letart Landfill Chain-of-Custody Records - Letart Landfill Laboratory Analytical Data Reports - Dry Run Landfill Chain-of-Custody Records - Dry Run Landfill
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Surface water Monitoring Report
Introduction
1.0 INTRODUCTION
A multi-media consent order (Order No. GWR-2001-019) was entered into between the West Virginia Department of Environmental Protection (WVDEP), the West Virginia Department of Health and Human Resources - Bureau for Public Health (WVDHHRBPH) and DuPont on November 15, 2001 (Consent Order). The Consent Order identified a series of requirements and tasks to be performed by the parties to determine whether there has been an impact on human health and the environment as a result of releases of ammonium perfluorooctanoate (C-8), CAS Number 3825-26-1, to the environment from DuPont operations at the Washington Works facility and the associated landfills (Local, Letart and Dry Run).
The Consent Order established the C-8 Groundwater Investigation Steering Team (GIST) to oversee investigations and activities that will be conducted to assess the presence and extent of C-8 in drinking water, groundwater, and surface water at and around the Washington Works facility and the Local, Letart and Dry Run Landfills.
An additional component of the Consent Order relates to the National Pollutant Discharge Elimination System (NPDES) permit sampling requirements. In this portion of the Consent Order, specific outfalls and outlets (outfalls) are to be sampled monthly for C-8 by DuPont.
Pursuant to Attachment A of the Consent Order, three tasks will be performed by DuPont and evaluated by the GIST, Tasks A, B, and C. Task A: Groundwater Use and Well Survey/Groundwater Monitoring has been completed (DuPont, 2002a; 2002b). Task B: Assessment of Existing Groundwater and Surface Water Monitoring Data includes the compilation of historical C-8 data, monitoring all wells at the landfills and the development of a Groundwater Monitoring Plan (GMP) for the Washington Works facility. The first part of the task, the historical C-8 data compilation report has been submitted to the GIST for evaluation (DuPont, 2002c). The second part of this task, monitoring C-8 in groundwater at the landfills, began in December 2001 and was performed monthly for four months and quarterly thereafter. The third part of the task, the proposed GMP for the Washington Works facility, was submitted to the GIST for evaluation (DuPont, 2002d) and groundwater sampling on the Washington Works facility began in January 2002. Groundwater sampling at the Washington Works facility was conducted monthly for four months and continues quarterly. Task C: Plume Identification/Groundwater Assessment is ongoing.
This report presents the results of the C-8 sampling that was performed in July 2002. Surface water results are presented for the Washington Works facility and the Local, Letart, and Dry Run Landfills.
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Surface water Monitoring Report
C-8 Analytical Reporting
2.0 C-8 ANALYTICAL REPORTING
The analytical method, method detection limit, and laboratory utilized for C-8 analysis has changed over time. Prior to 1991, DuPont performed C-8 analysis at the DuPont Experimental Station in Wilmington, Delaware. In 1991, when the RCRA Verification Investigation was conducted, the analysis was contracted to the CH2MHill Laboratory in Montgomery, Alabama. Both labs used a Gas Chromatography/Electron Capture Detector (GC-ECD) based analytical method with detection limits for C-8 that ranged from 0.1 to 1.0 ug/1.
CH2MHill conducted C-8 analysis for DuPont into the fall of 1998 when the laboratory ceased operation. At that time, DuPont had completed one round of analysis for the RCRA Facility Investigation (RFI). The analytical work was transferred to Lancaster Laboratories, Lancaster, PA, for the RFI second round analysis in March 1999. Lancaster Laboratories continued to conduct C-8 analysis using GC-ECD for DuPont until October 2001, when development and testing was completed on a new analytical method developed by Exygen Research, Inc. (Exygen; located in State College, PA) that utilizes Liquid Chromatography/Tandem Mass Spectrometry (LC/MS/MS). DuPont adopted the regular use of LC/MS/MS for C-8 analysis in water in November 2001 and Exygen was contracted to perform the analyses for DuPont.
Exygen reports C-8 results for the laboratory replicate of each field sample. These results are evaluated for precision by comparing the field sample result to the corresponding laboratory replicate result.
If both results are less than the practical quantitation limit (PQL), the replicate sample for that analyte is considered to have passed the precision criteria.
If one or both results are between one and five times the PQL, the replicate is considered to have met the precision criteria if the two results differ by less than the PQL.
If one result is less than the PQL and the other is not, and if the two results differed by a value less than the PQL, the replicate is said to have met the acceptance criteria.
Finally, if both results are at least five times the PQL, the replicate is considered to have met the criteria if the relative percent difference (RPD) between the two results is less than or equal to 20%. The RPD is the absolute value of the difference of two measurements divided by their average.
When the precision criteria outlined above are met, Exygen reports the average of the field sample and lab replicate results reported by the laboratory. If criteria for precision are exceeded, Exygen reports the higher of the sample and lab replicate results. Finally, when one result (from the sample/lab replicate pair) is above the PQL and one below, the result that is above the PQLs is reported. C-8 results are recorded in the Corporate Environmental Database (CED) and are reported as FC-143 for consistency with historical results.
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Surface water Monitoring Report
Washington Works Facility
3.0 WASHINGTON WORKS FACILITY
Figure 1.0 shows the location of the Washington Works facility. On July 23rd, 2002, six outfalls were sampled for C-8 (001, 002, 003, 005,007, and 105). All of these outfalls collect process water and stormwater runoff. Sampling of these outfalls is required by the Consent Order and WV NPDES permit No. WV0001279. The locations of these outfalls are shown in Figure 1.1.
Table 1.0 provides the C-8 analytical results for surface water. For each sampling point listed in this table, historical data is summarized with the most recent results listed first. Figure 1.2 presents the C-8 concentration map for the outfalls sampled in July 2002. Laboratory analytical data reports and the Chain-of-Custody records are included in Appendix A and B, respectively.
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06449
TABLES
000450
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Table 1.0 Summary of Analytical Results:
C-8 in Surface Water DuPont Washington Works Facility
Washington, WV
Sample OUTLET 001 OUTFALL 002
OUTLET 003 | OUTFALL 005
Date
7/23/02 6/25/02 5/20/02 4/16/02 3/19/02 2/5/02 1/17/02 12/20/01
7/23/02 6/25/02 6/25/02 (dup) 5/20/02 4/16/02 3/19/02 2/5/02 1/17/02 12/20/01 11/26/01* 10/25/01 9/19/01 7/11/01 6/14/01 5/31/01 4/11/01 3/21/01 2/14/01
7/23/02 6/25/02 5/20/02 4/16/02 3/19/02 3/19/02 (dup) 2/5/02 1/17/02 1/17/02 (dup) 12/20/01
7/23/02 6/25/02 5/20/02 5/17/02 4/16/02 3/19/02 2/5/02 1/17/02 12/20/01 12/20/01 (dup) 11/26/01 10/25/01 9/19/01 8/30/01 7/11/01 6/14/01 5/31/01 4/11/01 3/21/01 2/14/01
C-8 (ugA)
8.63 17.9 22.4
19.7 21.4
9.43 10.9 3.720
2.29 3.86 3.81 4.13 2.45
5.85 4.66 4.23 1.980 4.84 2.8 0.118 0.558 0.594 0.436 1.5 8.54 1.74
0.291 0.175 0.503 2.76 2.91 2.81 1.33 0.956 3.99 0.713
19.2 17.9 98.6 65.7 3.8 9.26 141.0 137.0 31.40 35.20 915 65.7 2.86 2.16 120 7.4 1.43 4.31 199 153
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Table 1.0-doc
Table 1.0 Summary of Analytical Results: C-8 in Surface Water DuPont Washington Works Facility Washington, WV
Sample OUTLET 007
OUTLET 105
Data
7/23/02 6/25/02 5/20/02 4/16/02 3/19/02 2/5/02 2/5/02(dup) 1/17/02 12/20/01
7/23/02 6/25/02 5/20/02 4/16/02 3/19/02 2/5/02 1/17/02 12/20/01
C-8(ug/I)
0.597 0.284 0.490 0.567 0.483 0.320 0.339 0.871 1.99
34.7 3.86 6.27
15.9 13.2 14.6 7.53 9.78
Note: Analytical method changed as of November 2001 (see Section 2.0 for details).
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Table I.O.doc
Table 2.0 Summary of Analytical Results:
C-8 in Surface Water Local Landfill
Washington, WV
Sample OUTFALL 004 (New) OUTFALL 004 (Old)
OUTFALL 005 (New) OUTFALL 005 (Old)/SS1
OUTLET 101
Date
7/1/02 6/13/02 5/21/02 4/29/02 3/26/02
7/1/02 6/13/02 5/21/02 4/29/02 3/26/02 2/20/02 1/24/02 12/13/01 9/27/2000 12/10/1999 6/3/1999 6/2/1998 5/29/1997 4/2/1996 2/16/1994
7/1/02 6/13/02 5/21/02 4/29/02 3/26/02
7/1/02 6/13/02 5/21/02 4/29/02 3/26/02 2/20/02 1/11/02 12/13/01 9/27/2000 12/10/1999 6/3/1999 6/2/1998 5/29/1997 4/2/1996 2/16/1994
7/1/02 6/13/02 5/21/02 4/29/02 3/25/02 2/20/02 1/23/02 12/13/01 9/14/2000 6/3/1999 6/2/1998
C-8(ug/I)
11.2 9.29 No-flow conditions 14.5 14.6
11.6 10.0 No-flow conditions 15
1.54 10.9 11.4 No-flow conditions 4.73 7.1 3.06 12 13 13 11
No-flow conditions No-flow conditions No-flow conditions
34.3 16.0
32.1 27.3 No-flow conditions 40.9 39.0 46.0 51.4 No-flow conditions 13.3 34 6.8 39 41 39 35
63.0 38.0 40.0 48.2 36.4 63.10 81.4 82.40 12 15 54
Note: Analytical method changed as of November 2001 (see Section 2.0 for details).
000453
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Table 2-0.doc
Table 3.0 Summary of Analytical Results:
C-8 in Surface Water Letart Landfill Letart, WV
'Sam ple 002(LEACHATE BASIN)
003 RT 33 STREAM
CAP RUNOFF
S a te
7/30/02 6/23/02 5/30/02 4/30/02 3/28/02 2/19/02 1/25/02 12/14/01 11/27/2001 7/20/01 7/25/2000 4/3/2000 1/14/2000 10/21/1999
7/30/02 mm2 5/30/02 4/30/02 mmz 2/19/02 1/25/02 12/14/01
5/30/02 4/30/02 mm2 2/19/02 1/25/02 7/20/2001 7/31/2000 7/20/1999 7/23/1997 4/17/1996
mm2 5/30/02 4/30/02 mm2 2/19/02 1/25/02
c-8 fue/i)
1410 Not Analyzed*
1630 443 131 355
50.1 36.1 53.2 159 1350 1900 920 3240
No-Flow Conditions Not Analyzed* 0.282 0.0653 0.198
No-Flow Conditions 0.148 0.390
1.570 0.845 1.26 3.92 1.9 2.01 0.573 2.23 2 1.8
Not Analyzed* 371 279
Not Sampled No-Flow Conditions
119
Note: Analytical method changed as of November 2001 (see Section 2.0 for details).
* Samples were taken at the respective surface water locations. However, due to an error by the courier, the samples arrived at the lab warm and were not analyzed.
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Table 3.0.doc
Table 4.0 Summary of Analytical Results:
C-8 in Surface Water Dry Run Landfill Lubeck, WV
Sample OUTLET 001
OUTLET 003 OUTLET 004 PROPERTY BOUNDARY
STREAM SAMPLING POINT#1 STREAM SAMPLING POINT#2
Date
7/31/02 7/1/02 6/28/02 5/28/02 4/24/02 3/25/02 2/25/02 1/28/02 12/12/01 10/3/2000 12/29/1999 5/19/1998 4/9/1996
7/1/02 6/28/02 5/28/02 4/29/02 3/26/02 2/25/02 1/28/02 12/12/01
7/1/02 6/28/02 5/28/02 4/27/02 3/26/02 2/25/02 1/28/02 12/12/01
5/28/02 4/24/02 3/25/02 2/25/02 1/28/02 12/12/01 10/3/2000 12/29/1999 7/14/1998 4/9/1996
5/28/02 4/24/02 3/25/02 2/25/02 1/28/02 12/12/01 10/3/2000 12/29/1999 5/19/1998
5/28/02 4/24/02 3/25/02 2/25/02 1/28/02 12/12/01 10/3/2000 12/29/1999 5/19/1998
C-8 (ur/I)
Noflow conditions Noflow conditions Noflow conditions
30.9 41 71.6 43.9 41.6 Noflow conditions 31.5 66 17 86
25.3 Noflow conditions Noflow conditions
20.1 6.77
Noflow conditions Noflow conditions Noflow conditions
0.70 Noflow conditions Noflow conditions Noflow conditions
158 Noflow conditions Noflow conditions Noflow conditions
9.41 6.69 22.8 3.81 11.1 3.99 10.3 39 0.88 9.9
1.63 0.932 1.06 0.850 0.893 1.19 0.758 0.54 1
51.0 28.9 66.6 24.3 42.4 20.5 27.6 87 4.6
000455
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Table 4-0.doc
Table 4.0 Summary of Analytical Results:
C-8 in Surface Water Dry Run Landfill Lubeck, WV
Sample
Date
C -8 (ag/1)
DRLEACHATE
5/28/02
150
4/24/02
237
3/25/02
334
2125102
256
1/28/02
398
12/12/01
109
10/3/2000
27.4
12/29/1999
34
5/19/1998
56
7/22/1997
62
POND UNDERDRAIN
5/28/02 4/24/02
67.4 33.4
3/25/02
66.7
2125102
37.1
1/28/02
29.3
12/12/01
35.4
Note: Analytical method changed as of November 2001 (see Section 2.0 for details).
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Table 4.0.doc
000457
FIGURES
00045*
SCALE
700 0
700'
OEStCNED
K. DAV IS DRAWN
O.H. EN G LISH CHECKED
K. O A VIS APPRCVED(OES)CH)
INfTViLS
APPROVED(CONSTRUCTION)
<SffPOWt)
Corporate Remediation Group
An Alliance between DuPont and UPS Diamond
Barley Mill Plaza, Building 27 Wilmington, Delaware 19805
SURFACE WATER SAMPLE LOCATION MAP
DuPont Washington Works Facility Washington, West Virginia
SCALE A s Shown
OATC
CAO r a x no.
05/02/2002
FG -1.1
000460
na 1.1
SCALE
700 0
700'
DESIGNED
mn>LS
SUO DRAWN
DEL CHECKED
TDL APPROVED(DES>CN)
ASH APPROVED(CONSTRUCTION)
Corporate Remediation Group
An Alliance between DuPont and URS Diamond
Barley Mill Plaza. Building 27 Wilmington. Delaware 19805
C--8 IN SURFACE WATER JULY 2002
DuPont Washington Works Facility Washington, West Virginia
SUI As shown
turc <JO FU HO. 08/02/2002 74238004
ncusc 1 .2
o in
Source: USGS Little Hocking, Ohio -- West Virginia Quadrangle
SITE LOCATION MAP
Corporate Remediation Group
An Alliance betw een DuPont and URS D iam ond
Barley Mill Plaza, Building 27 Wilmington, Delowore 19805
Local Landfill
Washington, West Virginia
9CM
Not to eeale
one
MNM
DEL /v e n a
CAO F IX MO. 7 *2 1 ADO1
2.0
STATE ROAD #892
SCALE
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DuPont and Tho W-C D iam ond Croup
00465 Barley Mill Plaza, Building 27 m ington, Deloware 19880--0027
SITE LO C ATIO N MAP
Letart Landfill Site Letart, WV
SCALE As shown
EMIC 12/21/9
0C90NCD TOL
OCCKEO
OAMM DEL
apw m p
CAO FLE MO. 7239AOOZ
noue 3 .0
99*000
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LEGEND
SURFACE WATER SAMPLE LOCATION 66.6 CONCENTRATION C -8 (ug/l)
Aon
n
N 257.500
/in n '
< m t>
Corporate Remediation
An Alliance between DuPont and URS Diamond
A \7
Group
uai
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C--8 IN SURFACE WATER JULY 2 00 2
Dry Run Landfill
DuPont Washington Works
Lubeck, West Virginia
scMX
A i thown
f|eaNKM.D{MVS imOuHM. DtCUSH |lown7u42m24o010
APPENDICES
000470
APPENDIX A LABORATORY ANALYTICAL DATA REPORTS
WASHINGTON WORKS FACILITY
RESEARCH
Precise Research. Proven Results.
H I]
Analytical Results Washington Works C8 Sampling 7/02
DuPont Sample Identification
APFO (ng/L)
WWK-Z-Outfall-001 WWK-Z-Outfall-002 WWK-Z-0 utfaII-003 WWK-Z-Outfall-005 WWK-Z-Outfall-007 WWK-Z-Outfall-105 WWK-Z-Outfall-007-2 WWK-K-EQBLK-1
8630 2290
291 19200
597 34700
544 ND
Limit of Detection (LOD) for the procedure is appoximately 10 ng/L
Limit of Quantitation (LOQ) for the procedure is 50 ng/L
ND - Compound not detected
NQ - Compound detected at a level between the LOD and LOQ. Result is not quantifiable.
ND < LOD < NQ < LOQ
Results are calculated according to the following criteria
If the sample and laboratory duplicate are greater than 250 ng/L, and the relative percent difference (RPD) is less than 20, the average value is reported. If the RPD is greater than 20, the higher value is reported.
If the sample and laboratory duplicate are less tha 250 ng/L, and the absolute difference is less than 50, the average value is reported. If the absolute difference is greater than 50, the higher value is reported.
0007
000472
3058 Research Drive State College, PA 16801, USA T: 814.272.1039 F: 8 1 4 .2 3 1 .1 5 8 0 exygen.com
APPENDIX B CHAIN-OF-CUSTODY RECORDS WASHINGTON WORKS FACILITY
000473
6000
f t V s f ARCH
1 v / l C U J I K J U I / M INJM LT 5 D K C U U t b l F O R M
Exygen Research Sample Receiving *3117 Research Drive State College, PA 16801, USA T: 814.231.8032 F: 814.231.1580 exygenresearch.com
P ag e____ of
PROJECT INFORMATION
ANALYSES REQUESTED 1
Client (name & address):
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Composite Number of Containers
SAMPLE ANALYSIS
m u t w : Client Sample Identification
Collection Collection rud.
Date
Time o
Specify Matrix
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PROJECT REQUIREMENTS Results Deadline:
Laboratory Report Options:
Q Sam ple results only Q A d d case narrative I I A d d quality control sum m ary I I A d d calibration sum m ary r~1 A d d raw data D O t h e r _________________
000474
APPENDIX C LABORATORY ANALYTICAL DATA REPORTS
LOCAL LANDFILL
TM
w /P re c ise Research. Proven Results.
RC H
Analytical Results Local Landfill C8 Sampling 7/02
DuPont Sample Identification
APFO (ng/L)
LCL-K-EQBLK-1 LCL-Z-Outfall 004 Old WestStream LCL-Z-Outfall 004 New West Stream LCL-Z-Outfall 005 Old Centrai Stream LCL-Z-Outlet 101
238 11600 11200 32100 63000
Limit of Detection (LOD) for the procedure is appoximately 10 ng/L
Limit of Quantitation (LOQ) for the procedure is 50 ng/L
ND - Compound not detected
NQ - Compound detected at a level between the LOD and LOQ. Result is not quantifiable.
ND < LOD < NQ < LOQ
Results are calculated according to the following criteria
If the sample and laboratory duplicate are greater than 250 ng/L, and the relative percent difference (RPD) is less than 20, the average value is reported. If the RPD is greater than 20, the higher value is reported.
If the sample and laboratory duplicate are less tha 250 ng/L, and the absolute difference is less than 50, the average value is reported. If the absolute difference is greater than 50, the higher value is reported.
0007
000476
,3 0 58 Research Drive LState College, PA 16801
LT: 814.272.1039 Ik F : 814.231.1580
exygen.com
APPENDIX D CHAIN-OF-CUSTODY RECORDS
LOCAL LANDFILL
000477
PROJECT INFORMATION Client (name & address):
v-1 .vniiM u r LU31 UUY/ANALYSIS REQUEST FORM
Exygen Research Sample Receiving *3117 Research Drive State College, PA 16801, USA T: 814.231.8032 F: 814.231.1580 exygenresearch.com
P age____ o f _____
ANALYSES REQUESTED 1
Project Manager (Name & E-mail Address):
Composite Number of Containers
/*# --
0009
/ / //./H i D - ifrc < r
Phone: ...... ~ C 9 iT Fax:____ ~ . ______ t v _______________ S a m p le r:^ ^ v \re Q ^ C \rV % ^ i^ .
/lAtcln>?ff.i>. /4<s&<''<&) (AH Project Name:
/ ? 1**y*JU r f / " P.O. # : Quotation # :
Please fill out this form completely to ensure correct analysis and proper handling of your samples.
SAMPLE ANALYSIS
Client Sample Identification Is m 'irL L C L ~ K ~ l i/-l
Collection Collection
Date
Time.
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1A-G X. O^QCJ
Specify Matrix Comments , 2_ 2 2 < / 9 i j2 T 2 ? 9 H
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CHAIN OF CUSTODY
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Date
Time
OTHER INFORMATION
Cooler ID #
LAB USE ONLY
-.o Cooler Temp. (C) c?.
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PROJECT REQUIREMENTS
Results Deadline:
Laboratory Report Options: 0 Sample results only 1 IAdd case narrative 0 Add quality control summary
0 Add calibration summary 0 Add raw data 0 Other_________________
------- 00047-------
CHAIN OF CUSTODY/ANALYSIS REQUEST FORM
Exygen Research Sample Receiving *3117 Research Drive State College, PA 16801, USA T: 814.231.8032 F: 814.231.1580 exygenresearch.com
P age_____o f _____
PROJECT INFORMATION
ANALYSES REQUESTED I
Client (name & address):
Project Manager (Name & E-mail Address):
Si0<XHn /ify s w /t-r'? --
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CH Other__________ -
000481
C H AIN OF CUSTODY/ANALYSIS REQUEST FORM
Exygen Research Sample Receiving 3117 Research Drive State College, PA 16801, USA T: 814.231.8032 F: 814.231.1580 exygenresearch.com
P age_____o f _____
PROJECT INFORMATION
ANALYSES REQUESTED 1
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0048*
APPENDIX E LABORATORY ANALYTICAL DATA REPORTS
LETART LANDFILL
000483
TM
Proven Results.
RC H
Analytical Results LeTart Landfill C8 Sampling 7/02
DuPont Sample Identification
APFO (ng/L)
LTL-Z-Outlet 002 LTL-K-EQBLK-1
1410000 ND
Limit of Detection (LOD) for th procedure is appoximately 10 ng/L
Limit of Quantitation (LOQ) for the procedure is 50 ng/L
ND - Compound not detected
NQ - Compound detected at a level between the LOD and LOQ. Result is not quantifiable.
ND < LOD < NQ < LOQ
Results are calculated according to the following criteria
If the sample and laboratory duplicate are greater than 250 ng/L, and the relative percent difference (RPD) is less than 20, the average value is reported. If the RPD is greater than 20, the higher value is reported.
If the sample and laboratory duplicate are less tha 250 ng/L, and the absolute difference is less than 50, the average value is reported. If the absolute difference is greater than 50, the higher value is reported.
0007
000484
exygen.com
APPENDIX F CHAIN-OF-CUSTODY RECORDS
LETART LANDFILL
000485
V-FIAHM U l- U J b I U D Y /A N A L Y b lb KfcQUhbT FORAA
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Exygen Research Sample Receiving 3117 Research Drive State College, PA 16801, USA T: 814.231.8032 F: 814.231.1580 exygenresearch.com
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PROJECT INFORMATION
ANALYSES REQUESTED
Client (name & address):
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000486
APPENDIX G LABORATORY ANALYTICAL DATA REPORTS
DRY RUN LANDFILL
000487
Ilf *
Analytical Result? Dry Run Landfill C8 Sampling 7/02
DuPont Sample Identification
APFO (ng/L)
DRL-Z-Outlet 003 DRL-Z-Outlet 004
25300 700
Limit of Detection (LOD) for the procedure is appoximately 10 ng/L
Limit of Quantitation (LOQ) for th. procedure is 50 ng/L
ND - Compound not detected
NQ - Compound detected at a level between the LOD and LOQ. Result is not quantifiable.
ND < LOD < NQ < LOQ
Results are calculated according to the following criteria
If the sample and laboratory duplicate are greater, than 250 ng/L, and the relative percent difference (RPD) is less than 20, the average value is reported. If the RPD is greater than 20, the higher value is reported.
If the sample and laboratory duplicate are less tha 250 ng/L, and the absolute difference is less than 50, the average value is reported. If the absolute difference is greater than 50, the higher value is reported.
0007
000488
,^^3058 Research Drive -# m s ta te College, PA 16801, USA
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APPENDIX H CHAIN-OF-CUSTODY RECORDS
DRY RUN LANDFILL
000489
RESEARCH
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Exygen Research Sample Receiving 3117 Research Drive State College, PA 16801, USA T: 814.231.8032 F: 814.231.1580 exygenresearch.com
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Composite Number of Containers
SAMPLE ANALYSIS
Client Sample Identification
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Exygen Research Sample Receiving 3117 Research Drive State College, PA 16801, USA T: 814.231.8032 F: 814.231.1580 exygenresearch.com
P a g e _____ o f ______
PROJECT INFORMATION
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Cooler Temp. (C) < r TBaaHtpew-{j>f;e';S'iti
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Laboratory Report Options: 0 Sample results only 1 I Add case narrative I I Add quality control summary O Add calibration summary [~~l Add raw data Other
000491