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DECEMBER 2002 SURFACE WATER MONITORING REPORT FOR WASHINGTON WORKS FACILITY AND LOCAL, LETART AND DRY RUN LANDFILLS WASHINGTON, WV
Date: February 2003
Project No.:
D6WW7423.01 18983632.00028 18983633.00026 18983634.00026
Ccum Co
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CORPORATE REMEDIATION GROUP
An Alliance between DuPont and URS Diamond
Barley Mill Plaza, Building 27 Wilmington, Delaware 19805
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WVDEP 17201
0001S5
Surface W a ter Monitoring Report
Table of Contents
TABLE OF CONTENTS
1.0 Introduction...................................................................................................................1 2.0 C-8 Analytical Reporting.............................................................................................2 3.0 Washington Works Facility.........................................................................................4 4.0 Local Landfill............................................................................................................... 5 5.0 Letart Landfill.............................................................................................................. 6 6.0 Dry Run Landfill.......................................................................................................... 7 7.0 References.................................................................................................................... 8
Table 1.0 Table 2.0 Table 3.0 Table 4.0
C-8 in C-8 in C-8 in C-8 in
TABLES Surface Water - Washington Works Facility Surface Water - Local Landfill Surface Water - Letart Landfill Surface Water - Dry Run Landfill
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
FIGURES Site Location Map - Washington Works Facility Surface Water Sample Location Map - Washington Works Facility C-8 Concentration Map December 2002 - Washington Works Facility Surface Water Site Location Map - Local Landfill Surface Water Sample Location Map - Local Landfill C-8 Concentration Map December 2002 - Local Landfill Outfalls Site Location Map - Letart Landfill Surface Water Sample Location Map - Letart Landfill C-8 Concentration Map December 2002 - Letart Landfill Outfalls Site Location Map - Dry Run Surface Water Sample Location Map - Dry Run Landfill C-8 Concentration Map December 2002 - Dry Run Landfill Outfalls
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Surface W ater 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 W a ter 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 West Virginia National Pollutant Discharge Elimination System (WV 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 were performed by DuPont and evaluated by the GIST, Tasks A, B, and C. Task A: Groundwater Use and Well Survey/Groundwater Monitoring was completed (DuPont, 2002a; 2002b). Task B: Assessment of Existing Groundwater and Surface Water Monitoring Data included compiling of historical C-8 data, monitoring all wells at the landfills and developing a Groundwater Monitoring Plan (GMP) for the Washington Works facility. The first part of the task, the historical C-8 data compilation report was 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, developing a GMP for the Washington Works facility, was submitted to the GIST (DuPont, 2002d). Groundwater sampling at the Washington Works facility began in January 2002, and was conducted monthly for four months and quarterly thereafter. Task C: Plume Identification/Groundwater Assessment is ongoing.
This report presents the results of the monthly (December 2002) C-8 surface water sampling that was performed in December 2002 at the Washington Works facility, and the Local, Letart, and Dry Run Landfills.
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Surface W ater Monitoring Report
C-8 Analytical Reporting
2.0 C-8 ANALYTICAL REPORTING
The analytical method, method detection limit, and laboratory utilized for C-B analysis have 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 CFLMHill 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.
CELMHill conducted C-8 analysis for DuPont into the fall of 1998 when the laboratory ceased operation. The C-8 analytical work was transferred to Lancaster Laboratories, Lancaster, PA, 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.
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.
An aliquot of each field sample is also analyzed as a matrix spike (MS). Results of the MS analysis are used to assess accuracy. The MS recovery value must fall between 70 to
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Surface W a te r Monitoring Report
C-8 Analytical Reporting
130%, unless the sample concentration is at least four times the amount spiked. The maximum amount used to spike field samples is 500 ug/L.
All data packages generated by Exygen are reviewed in-house for compliance with the laboratory Standard Operating Procedures (SOP) and data usability, using the checklist provided in the QAPP. Results of the in-house review indicate that data reported by Exygen have been generated in compliance with the laboratory SOP, with few exceptions as noted in the individual review summaries. All data reported by Exygen have been judged usable for the purposes of the project.
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Surface W a ter Monitoring Report
Washington Works Facility
3.0 WASHINGTON WORKS FACILITY
Figure 1.0 shows the location of the Washington Works facility. On December 9, 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. No other changes to routine sampling protocols or other observations were recorded in the field notes during this sampling event. Monthly 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 the 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 December. Laboratory analytical data reports and the Chain-of-Custody records are included in Appendix A and B, respectively.
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Surface W a ter Monitoring Report
Local Landfill
4.0 LOCAL LANDFILL
Figure 2.0 shows the location of the Local Landfill. Monthly sampling of five outfalls is required by the Consent Order and the WV NPDES permit No. WV0076538. These five outfalls collect stormwater runoff. On December 13, 2002, 004(01d), 004(New), and 005(01d)/SSl, and 005(New) were sampled for C-8. Outfall 101 was sampled for C-8 on December 16, 2002. An additional point, Outlet LM1 (Leachate), was also sampled on December 16,2002. This point is a bi-annual permit required monitoring point. On the chain of custody, this point was labeled Leachate Inlet 002. The locations of these six outfalls are shown in Figure 2.1.
Table 2.0 presents the C-8 analytical results for the December surface water samples. The table includes the historic data available for each location sampled. The data are presented with the most recent data first. Figure 2.2 presents the C-8 concentration map for the outfalls sampled in December. Laboratory analytical data reports and Chain-ofCustody records are provided in Appendices C and D, respectively.
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Surface W a ter Monitoring Report
Letart Landfill
5.0 LETART LANDFILL
Figure 3.0 presents the Letart Landfill location map. Monthly sampling of Outfalls 002 and 003 (both containing stormwater runoff) and Cap Runoff (which collects leachate and stormwater runoff) is required by the Consent Order. The location of Outfall 002, Outfall 003, and the Cap Runoff samples are shown in Figure 3.1. On December 30, 2002, sampling was conducted at Outfall 002, and Cap Runoff. Sampling was attempted at Outfall 003 but no-flow conditions were encountered at the time of sampling.
The C-8 results for the December surface water are presented in Table 3.0. For each sampling point listed in the table, historical data is summarized with the most recent results listed first. In the September 2002 monthly monitoring report, a sample taken on 9/27/02 for the Cap Runoff surface water location, was inadvertently named Stormwater Runoff. The incorrect name was carried through the October/Q402 and November 2002 monthly monitoring reports. This data point has been moved to the correct chronological spot under Cap Runoff in Table 3.0.
Figure 3.2 presents the C-8 concentration map for the outfalls sampled in December. Appendices E and F present the laboratory analytical data reports and the Chain-ofCustody records, respectively.
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Surface W ater Monitoring Report
Pry Run Landfill
6.0 DRY RUN LANDFILL
Figure 4.0 shows the location of the Dry Run Landfill. Monthly sampling of Outfalls 001, 003, and 004 is required by the Consent Order and WV NPDES permit No. WV0076244. (Outfall 002 is a required outfall sampling location as stated in WV NPDES permit No. WV0076244. However, it was a temporary relocation of Outfall 001 and no longer exists). Outfall 001 collects stormwater and leachate. Outfalls 003 and 004 collect stormwater only. The locations of the surface water sampling points are shown in Figure 4.1. On December 30, 2002, Outfall 001 was sampled. During the month of December, Outfalls 003 and 004 were not sampled due to no-flow conditions.
Table 4.0 presents the C-8 analytical results for the December surface water samples. For each sampling point listed in the table, historical data are summarized with the most recent results presented first. Figure 4.2 presents the C-8 concentration map for the outfall sampled in December. Laboratory analytical data reports and Chain-of-Custody records are provided in Appendices G and H, respectively.
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Surface W ater Monitoring Report
References
7.0 REFERENCES
DuPont. 2002a. One-Mile Radius Survey and C-8 Sampling Report and Ohio River Public Water Supply Sampling, DuPont Washington Works (December 2001February 2002) January 2002. DuPont Corporate Remediation Group and URS Diamond.
DuPont. 2002b. Two-Mile Radius Survey and C-8 Sampling, DuPont Washington Works Facility/Local Landfill, West Virginia (March-May 2002) August 2002. DuPont Corporate Remediation Group and URS Diamond.
DuPont. 2002c. Compilation o fHistorical C-8 Data, DuPont Washington Works Main Plant and Landfills January 2002. DuPont Corporate Remediation Group and URS Diamond.
DuPont. 2002d. Proposed Groundwater Monitoring Planfo r Washington Works Facility Plant and Landfills January 2002. DuPont Corporate Remediation Group and URS Diamond.
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TABLES 000166
Table 1.0 Summary of Analytical Results:
C-8 in Surface Water DuPont Washington Works Facility
Washington, WV
S am ple OUTLET 001 OUTFALL 002
OUTLET 003
D ate
1 2 /9 /0 2 1 1 /1 3 /0 2 1 0 /1 8 /0 2 9 /2 4/02 8/2 7/02 7/2 3/02 . 6/2 5/02 5/2 0/02 4/1 6/02 3 /1 9/02 2 /5 /0 2 1 /1 7 /0 2 1 2 /2 0 /0 1
1 2 /9 /0 2 1 1 /1 3 /0 2 11/13/02 (dup) 1 0 /1 8 /0 2 9 /2 4 /0 2 8/2 7/02 8 /2 7/02 (dup) 7 /2 3/02 6 /2 5/02 6 /2 5 /0 2 (dup) 5 /2 0/02 4/1 6/02 3/1 9/02 2 /5 /0 2 1 /1 7 /0 2 1 2 /2 0 /0 1 1 1 /2 6 /0 1 * 1 0 /2 5 /0 1 9 /1 9 /0 1 7 /1 1 /0 1 6 /1 4 /0 1 5 /3 1 /0 1 4 /1 1 /0 1 3 /2 1 /0 1 2 /1 4 /0 1
1 2 /9 /0 2 1 1 /1 3 /0 2 1 0 /1 8 /0 2 9/2 4/02 8 /2 7/02 7 /2 3/02 6/2 5/02 5 /2 0/02 4/1 6/02 3 /1 9 /0 2 3 /1 9 /0 2 (dup) 2 /5 /0 2 1 /1 7 /0 2 1/17/02 (dup) 1 2 /2 0 /0 1
c-e ( u b / i)
9 .7 6 1 7 .0 1 0 .5
2 .1 5 2.9 4 8 .6 3 1 7 .9 2 2 .4 1 9 .7 2 1 .4 9 .4 3 1 0 .9 3.7 20
2.3 7 4.7 5 5 .2 8 3.4 9 2.1 4 2.5 6 2 .5 1 2 .2 9 3.8 6 3.81 4.1 3 2.4 5 5.8 5 4 .6 6 4.2 3 1 .9 8 0 4.8 4 2 .8 0.1 18 0 .5 5 8 0.5 94 0.4 36 1 .5 8 .5 4 1 .7 4
0.6 80 1 .2 4 0.8 70 0.3 17 0.2 6 8 0 .2 9 1 0.1 75 0.5 03 2.7 6 2 .9 1 2 .8 1 1.33 0.9 56 3.9 9 0.7 13
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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
S am ple OUTFALL 005
OUTLET 007 OUTLET 105
D ate
1 2 /9 /0 2 12 /9/02 (dup)
1 1 /1 3 /0 2 1 0 /1 8 /0 2 9/2 4/02 9 /2 4/02 (dup) 8 /2 7 /0 2 7 /2 3 /0 2 6 /2 5 /0 2 5 /2 0 /0 2 5 /1 7 /0 2 4/1 6/02 3/1 9/02 2/5 /0 2 1 /1 7 /0 2 1 2 /2 0 /0 1 1 2 /2 0 /0 1 (d u p ) 1 1 /2 6 /0 1 10/25/01 9 /1 9 /0 1 8 /3 0 /0 1 7 /1 1 /0 1 6 /1 4 /0 1 5 /3 1 /0 1 4 /1 1 /0 1 3 /2 1 /0 1 2 /1 4 /0 1
1 2 /9 /0 2 1 1 /1 3 /0 2 1 0 /1 8 /0 2 10/18/02 (dup) 9 /2 4 /0 2 m im 7/2 3/02 7/2 3/02 (dup) 6 /2 5 /0 2 5 /2 0 /0 2 4 /1 6 /0 2 3 /1 9 /0 2 2 /5 /0 2 2 /5 /0 2 (d u p ) 1 /1 7 /0 2 1 2 /2 0 /0 1
1 2 /9 /0 2 1 1 /1 3 /0 2 1 0 /1 8 /0 2 9/2 4/02 8 /2 7 /0 2 7 /2 3 /0 2 6 /2 5 /0 2 mm2 5/2 0/02 (dup) 4 /1 6 /0 2 3 /1 9 /0 2 2 /5 /0 2 1 /1 7 /0 2 12/20/01
C -8 (u g /l)
6 .3 9 6 .6 2 18.1 12.1 4 .6 4 5 .0 2 1 2 .4 1 9 .2 1 7 .9 9 8 .6 6 5 .7 3 .8 9 .2 6 1 4 1 .0 1 3 7 .0 3 1 .4 0 3 5 .2 0 915 6 5 .7 2.8 6 2.1 6 120 7 .4 1 .4 3 4.31 199 153
0 .2 6 3 8.5 6 0 .2 5 1 0.2 09 NQ (< 0.05) 0 .2 0 7 0.5 97 0 .5 4 4 0.2 84 0.4 90 0.5 67 0 .4 8 3 0.3 20 0.3 39 0.871 1 .9 9
6.0 7 1 0 .5 5 4 .6
3.6 9 6 .7 3 34 .7 3 .8 6 6 .2 7 5 .1 6 1 5 .9 1 3 .2 1 4 .6 7 .5 3 9 .7 8
Note: Analytical method changed as of November 2001 (see Section 2.0 for details). NQ = Not Quantifiable. Detected at a concentration above the LOD and below the limit of
quantification (LOQ).
000168
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Table 1 0.doc
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Table 2.0 Summary of Analytical Results:
C-8 in Surface Water Local Landfill
Washington, WV
Sam ple O UTFA LL 004 (N ew ) O UTFA LL 004 (O ld)
OUTFALL 005 (New ) O UTFALL 00 5 (O ld)/SS1
D a te 1 2 /1 3 /0 2 1 1 /3 0 /0 2 1 0 /3 1 /0 2 9 /3 0 /0 2 8 /2 5 /0 2
7/1 /0 2 6 /1 3 /0 2 5 /2 1 /0 2 4 /2 9/02 3 /2 6 /0 2
1 2 /1 3 /0 2 1 1 /3 0 /0 2 1 0 /3 1 /0 2 9 /3 0 /0 2 8 /2 6 /0 2 7 /1 /0 2 6 /1 3 /0 2 5 /2 1 /0 2 4 /2 9 /0 2 3 /2 6 /0 2 2 /2 0 /0 2 1 /2 4 /0 2 12/13/01 9 /2 7 /2 0 0 0 1 2 /1 0 /1 9 9 9 6/3 /1 999 6/2 /1 998 5 /2 9 /1 9 9 7 4/2 /1 996 2 /1 6 /1 9 9 4
1 2 /1 3 /0 2 1 1 /3 0 /0 2 1 0 /3 1 /0 2 9 /3 0 /0 2 8 /2 6 /0 2 7 /1 /0 2 6 /1 3 /0 2 5 /2 1 /0 2 4 /2 9 /0 2 3 /2 6 /0 2
1 2 /1 3 /0 2 1 1 /3 0 /0 2 1 0 /3 1 /0 2 9 /3 0 /0 2 8 /2 6 /0 2
7 /1 /0 2 6 /1 3 /0 2 5 /2 1 /0 2 4 /2 9 /0 2 3 /2 6 /0 2 2/2 0/02 1 /1 1 /0 2 12/13/01 9 /2 7 /2 0 0 0 1 2 /1 0 /1 9 9 9 6/3 /1 999 6 /2 /1 9 9 8 5 /2 9 /1 9 9 7 4/2 /1 996 2 /1 6 /1 9 9 4
C-8 (ue/1) 10.7
No-flow conditions No-flow conditions No-flow conditions No-flow conditions
11.2 9 .2 9 No-flow conditions 1 4 .5 1 4 .6
1 2 .5 No-flow conditions No-flow conditions No-flow conditions No-flow conditions
1 1 .6 10.0 No-flow conditions 15
1.54 1 0 .9 1 1 .4 No-flow conditions
4 .7 3 7.1 3 .0 6 12 13 13 11
9.51 No-flow conditions No-flow conditions No-flow conditions No-flow conditions No-flow conditions No-flow conditions No-flow conditions
3 4 .3 16.0
38.1 No-flow conditions No-flow conditions No-flow conditions No-flow conditions
32.1 2 7 .3 No-flow conditions 4 0 .9 3 9 .0 4 6 .0 51.4 No-flow conditions 13.3 34 6 .8 39 41 39 35
oooiee
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Table 2 0.doc
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Table 2.0 Summary of Analytical Results:
C-8 in Surface Water Local Landfill
Washington, WV
Sample O UTLET 101
OUTLET LM1 (LEACHATE) / INLET 002
-Date
12/16/02 11/19/02 10/31/02 9/30/02 8/26/02
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 12/16/02 11/21/02
C-8 (OR/1) 49.5 76.7 78.6
115.0 70.3 63.0 38.0 40.0 48.2 36.4 63.10 81.4 82.40 12 15 54
81.7 120.0
Note: Analytical method changed as of November 2001 (see Section 2.0 for details).
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Table 2 O.doc
Table 3.0 Summary of Analytical Results:
C-8 in Surface Water Letart Landfill Letart, WV
Sam ple
D ate
C-S (uk/I)
002(LEA C H A TE BA SIN )
1 2 /3 0 /0 2
1170
1 1 /2 5 /0 2
939
1 0 /3 1 /0 2
645
9/2 7/02
4.5 2
8 /3 0 /0 2
2050
7 /3 0 /0 2
1410
6 /2 8 /0 2
Not Analyzed*
5 /3 0 /0 2
1630
4 /3 0/02
443
3 /2 8/02
131
2/1 9/02
355
1 /2 5 /0 2
50.1
1 2 /1 4 /0 1
36.1
1 1 /2 7 /2 0 0 1
5 3 .2
7 /2 0 /0 1
159
7 /2 5 /2 0 0 0
1350
4 /3 /2 0 0 0
1900
1 /1 4 /2 0 0 0
920
10 /21/1999
3240
003
1 2 /3 0 /0 2
No-Flow Conditions
1 1 /3 0 /0 2
No-Flow Conditions
1 0 /3 1 /0 2
No-Flow Conditions
9 /2 7 /0 2
0 .1 7 0
8 /3 0/02
No-Flow Conditions
7 /3 0/02
No-Flow Conditions
6 /2 8 /0 2
N ot Analyzed*
5 /3 0/02
0.2 82
4 /3 0/02
0 .0 6 5 3
3/2 8/02
0.1 98
2/1 9/02
No-Flow Conditions
1 /2 5 /0 2
0.1 48
1 2 /1 4 /0 1
0.3 90
RT 33 STREAM
1 0 /3 1 /0 2
2 .8 3
9 /2 7 /0 2
2 .2 4
8 /3 0 /0 2
No-Flow Conditions
5 /3 0 /0 2
1 .5 7 0
4/3 0/02 3 /2 8/02
0.8 45 1 .2 6
2 /1 9/02
3 .9 2
1 /2 5 /0 2
1 .9
7 /2 0 /2 0 0 1
2.01
7 /3 1 /2 0 0 0
0.5 73
7 /2 0/199 9
2 .2 3
7/2 3 /1 9 9 7
2
4/1 7/199 6
1.8
B R IN K ER RUN
1 0 /1 4 /0 2
0 .0 6 1 2
CAP RUNOFF
1 2 /3 0 /0 2
415
11 /25/02
65.1
1 0 /3 1 /0 2
102
9 /2 7/02
5 0 .9 **
8 /3 0/02
N o-Flow Conditions
6 /2 8/02
N ot Analyzed*
5 /3 0/02
371
4/3 0/02 3 /2 8/02
279 N ot Sam pled
000171
2/1 9/02
No-Flow Conditions
1 /2 5 /0 2
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.
**This sample was inadvertently named Stormwater Runoff in the September/Q302 report
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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
Sam ple O U TLET 001
O UTLET 003 OUTLET 004 PROPERTY BOUNDARY
D ate
1 2 /3 0 /0 2 1 1 /2 1 /0 2 1 0 /3 0 /0 2 9 /3 0/02 8/3 0/02 7/3 1/02
7 /1 /0 2 mm2 mm2 4/2 4 /0 2 3 /2 5 /0 2 2/2 5/02 1/2 8/02 1 2 /1 2 /0 1 1 0 /3 /2 0 0 0 1 2 /2 9 /1 9 9 9 5/1 9/199 8 4 /9 /1 9 9 6
12 /30/02 11 /30/02 1 0 /3 0 /0 2 9/3 0/02 8 /3 0/02
7 /1 /0 2 6/2 8 /0 2 5 /2 8/02 4/2 9/02 3 /2 6/02 2/2 5/02 1 /2 8 /0 2 1 2 /1 2 /0 1
1 2 /3 0 /0 2 1 1 /3 0 /0 2 10 /30/02 9/3 0/02 8/3 0 /0 2
7/1 /0 2 mm2 mm2 4/2 7/02 mm2 mm2 1 /2 8 /0 2 1 2 /1 2 /0 1
1 0 /3 0 /0 2 8/3 0/02 mm2 4/2 4 /0 2 3/2 5/02 mm2 1/2 8/02 1 2 /1 2 /0 1 1 0 /3 /2 0 0 0 1 2 /2 9 /1 9 9 9 7 /1 4/199 8 4 /9 /1 9 9 6
C -*(U R /1 )
5 6 .9 6 4 .6 8 1 .7 No-flow conditions No-flow conditions No-flow conditions No-flow conditions No-flow conditions 3 0 .9 41 7 1 .6 43 .9 41 .6 No-flow conditions 3 1 .5 66 17 86
No-flow conditions No-flow conditions No-flow conditions No-flow conditions No-flow conditions
2 5 .3 No-flow conditions No-flow conditions
20.1 6 .7 7
No-flow conditions No-flow conditions No-flow conditions
No-flow conditions No-flow conditions No-flow conditions No-flow conditions No-flow conditions
0 .7 0 No-flow conditions No-flow conditions No-flow conditions
158 No-flow conditions No-flow conditions No-flow conditions
3 .8 0 No-flow conditions
9.41 6 .6 9 2 2 .8 3.81 11.1 3.9 9 10.3 39 0 .8 8 9 .9
000172
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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
Sam ple
D ate
C-8 (ue/n
STREAM SAM PLING PO INT#1
1 0 /3 0 /0 2 8 /3 0/02 5 /2 8/02 4/2 4/02 3 /2 5 /0 2 2/2 5/02 1 /2 8 /0 2
1 .6 3 No-flow conditions
1.63 0 .9 3 2 1 .0 6 0 .8 5 0 0 .8 9 3
1 2 /1 2 /0 1
1 .1 9
1 0 /3 /2 0 0 0 12/29/19 99
0.7 58 0 .5 4
5 /1 9 /1 9 9 8
1
STREAM SAM PLING P O IN T#2
1 0 /3 0 /0 2 8/2 0/02 5/2 8/02 4/2 4/02 3 /2 5/02
2 9 .2 No-flow conditions
5 1 .0 28 .9 6 6 .6
2/2 5/02 1 /2 8 /0 2
2 4 .3 4 2 .4
1 2 /1 2 /0 1 1 0 /3 /2 0 0 0
2 0 .5 27 .6
12 /29/1999
87
5/1 9/199 8
4 .6
DRLEACHATE
1 0 /3 0 /0 2
704
5 /2 8/02
150
4/2 4/02
237
3 /2 5/02
334
2/2 5 /0 2
256
1 /2 8/02
398
1 2 /1 2 /0 1
109
1 0 /3 /2 0 0 0
2 7 .4
12/29/19 99
34
5/1 9/199 8
56
7/2 2 /1 9 9 7
62
PO N D UNDERD RAIN
10 /30/02 mm2
3 8 .8 6 7 .4
4/2 4 /0 2
3 3 .4
3/2 5/02
66 .7
2/2 5 /0 2
37.1
1 /2 8 /0 2
2 9 .3
1 2 /1 2 /0 1
3 5 .4
Note: Analytical method changed as of November 2001 (see Section 2.0 for details).
02/11/03
2 of 2
000173
Table 4 0.doc
FIGURES 000174
OUTFALL OOSA
I1-DIGAEUSNNTAIIOTERNBOB-PAOICNOS
OUTLET 0 0 7
OUTFALL 0 0 2
A
t-jv OUTLET 105
1f
I -r
1t fsS \0
I.
LEGEND
OUTLET 0 0 5
OUTFALL SAMPLING POINT
00017G
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LEGEND
OUTLET 0 0 5
OUTFALL SAMPLING POINT
000177
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O O O /7 7 #
DGBOMCD
mtmls
SJO MANN
DEL OCCXCD
TDL APPMMD(D9QN)
ASH A*fwwD(coti*ucnotO
(SPUR!)
^
Corporate Remediation Group
/4n A llia nce between DuPont and UBS Diamond
Barley Mill Plaza, Building 27 Wilmington, Delaware 19805
C - 8 IN SURFACE WATER DECEMBER 2002
D u P o n t W a s h in g to n W orks F a c ility W a s h in g to n , W est V irg in ia
wu
mi
m w ic . neunc
A* town 01/31/2003 74230004
1.2
LEGEND
-------- SURFACE WATER SAMPLE
000179
SCAL 400 0
a c c o n ta
800'
OCStONCD
DRAWN
DEL CHECKED
TOL APPKO VtD (M SG N )
MfTVLS
A P P M vnK coN snm cnotO
Corporate Remediation Group
An Alliance between DxLpQnt and URS Diamond
Barley Mill Plaza, Building 27 Wilmington, Delaware 19805
SURFACE WATER SAMPLE LOCATION MAP
Local Landfill Washington, West Virginia
EMUE
OMt
ce ru i& MURE
A* ifccw Ot/07/2003 7421B0U
2.1
SITE LOCATION MAP
fiu oi/9i / m
Letart Landfill Site
Letart. WV
m.
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SITE LOCATION MAP
Corporate Remediation Group
d n Alliance between DuPont and (JRS Diamond
B a rle y Mill P la za , B u ild in g 27 W ilm ington, D elaw are 19805
Dry Run Landfill Lubeck, West Virginia
im i
Am town
mi 1 1 /8 /0 1
cto n s m .
7422BOOS
nam e
4 .0
APPENDICES 000187
APPENDIX A LABORATORY ANALYTICAL DATA REPORTS
WASHINGTON WORKS FACILITY
000188
Proven Results.
Analytical Results Washington Works C8 Sampling 12/02
DuPont Sample Identification
APFO (ng/L)
W W K-Z-Outfall 001 WWK-Z-Outfall 002 WWK-Z-Outfall 003 WWK-Z-Outfall 005 WWK-Z-Outfall 007 WWK-Z-Outfall 105 WWK-Z-Outfall 005-2 WWK-K-EQBLK-1
Limit of Detection (LOD) for the procedure is apipoximately 10 ng/L
Limit of Quantitation (LOQ) for the procedure is 50 ng/L
ND - Compound not detected
9760 2370
680 6390
263 6070 6620
NQ
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 crrteiia
If th e sam ple an d laboratory duplicate are greater than 2 5 0 ng/L, arid th e relative percent difference (R P D ) is less than 2 0 , the a v erag e value is reported. If the R P D is g reater than 20, th e higher value is reported.
If th e sam ple an d laboratory duplicate are less tha 2 5 0 n g /L a n d th e absolute difference is less than
50, the a v e ra g e va lu e is reported. If the absolute difference is g reater th an isp, the higher va lue is
reported.
\
j-0 07
000189
3 0 5 8 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
000190
CHAIN OF CUSTODY/ANALYSIS REQUEST FORM
RESEARCH
Exygen Research Sample Receiving * 3 1 1 7 Research Drive State College, PA 16 8 0 1, USA T: 8 14 .2 3 1.8 0 3 2 F: 8 1 4 .2 3 1 .1 5 8 0 exygenresearch.com
Page
of
PROJECT INFORMATION
ANALYSES REQUESTED
Client (name & address):
___ fih/x M
t^iVv- I
n /
/% ' / v / v V
Phone:
JW - , t A' j7
Fax
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Project Manager (Name & E-mail Address):
____________________^ ..................................................................
________(. . /-I,./-, P frj/k yi
Project Name:
/ Ji /'
RO. # :
$ t c C w . S C i ' , % * # / < . < i ? X 7>"
Quotation #:
Please fill out this form completely to ensure correct analysis and proper handling of your samples.
SAMPLE ANALYSIS
ExytlMS# Client Sample Identification
U W o - f U l y 'i i - - O itT h './f C i i
i 3WC-Z_ t%,L*l( - ^ - C~j// *// }*-A
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outfall
(. JVo+A t^Lsk - U- g A u L t f - f
LAB USE ONLY
Collection Date
|.JrCj'Q2
11
U-^-oc J
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Comments _________
/ If) / V ri Vf 1 I / (ay k'6J
^ x i V t ' / k V 'y > ^ /
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Date
Time
W V 0 3 - V"\ \ 5
OTHER INFO RM ATIO N
Cooler ID # f/o o a tll f
Received fw
>crO '
Cooler Temp. (C)
Date
Time
-n~2,
LAB USE ONLY
jH L
PROJECT REQUIREMENTS Results Deadline:
Laboratory Report Options: [D Sample results only f~l Add case narrative
CD Add quality control summary
0 Add calibration summary 1 I Add raw data
CDO th e r ____
000191
APPENDIX C LABORATORY ANALYTICAL DATA REPORTS
LOCAL LANDFILL
900192
TM
Proven Results.
RCH
Analytical Results Local Landfill C8 Sampling 12/02
DuPont Sample identification
APFO (ng/L)
LCL-Z-Outfall 004 New West Stream LCL-Z-Outfall 004 Old Wst Stream LCL-Z-Outfall 005 New Central Stream LCL-Z-Outfall 005 Old Central Stream LCL-K-EQBLK-1 LCL-Z-Leachate Inlet 002 LCL-Z-Outlet 101
10700 12500
9510 38100
ND 81700 49500
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 25 0 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.
000193
,3058 Research Drive |S ta te College, PA 1 6 8 0 1 , USA
I.T . 814.272.1039 iL F : 814.231.1580
exygen.com
APPENDIX D CHAIN-OF-CUSTODY RECORDS
LOCAL LANDFILL
0 0 1 9 4
CHAIN OF CUSTODY/ANALYSIS REQUEST FORM
Exygen Research Sample Receiving * 3 1 1 7 Research Drive State College, PA 16 8 0 1, USA T: 8 14 .2 3 1.8 0 3 2 F: 8 1 4 .2 3 1 .1 5 8 0 exygenresearch.com
Page
of
PROJECT INFORMATION
ANALYSES REQUESTED
Client (name & address):
Project Manager (Name & E-mail Address):
X'.`7 / V ...f. , - A. -, -, r
/h , li. /r \ t
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SAAAPLE ANALYSIS
E x yLIM S# Client Sample Identification
Collection Collection
Date
Time
tgH^nCOgfrfi-
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V -\\C >
OTHER INFORMATION
Cooler ID # -A?Sent'jt>& Cooler Temp. (C) 5
Received by
^
Date
Time
^Xv^-<s}- c r v ^ o
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PROJECT REQUIREMENTS Results Deadline:
Laboratory Report Options:
0 Sample results only 1 I Add case narrative Add quality control summary Add calibration summary 0 Add raw data 0 Other_______________
APPENDIX E LABORATORY ANALYTICAL DATA REPORTS
LETART LANDFILL
000196
Proven Results.
RC H
Analytical Results LeTart Landfill C8 Sampling 12/02
DuPont Sample Identification
APFO (ng/L)
LTL-Z-Outiet 002 LTL-Z-Cap Runoff LTL-K-EQBLK-1
1170000 415000 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 2 50 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
000197
,3058 Researdi Drive State College, PA 1 6 8 0 1 , USA
exygen.com
APPENDIX F CHAIN-OF-CUSTODY RECORDS
LETART LANDFILL
000198
CHAIN OF CUSTODY/ANALYSIS REQUEST FORM
Exygen Research Sample Receiving 3 1 1 7 Research Drive State College, PA 16 8 0 1, USA T: 8 14 .2 3 1.8 0 3 2 F: 8 1 4 .2 3 1 .1 5 8 0 exygenresearch.com
P a g e _____ o f ______
PROJECT INFORMATION
ANALYSES REQUESTED
Client (name & address):
if-
~ hi ,
h / } it/A
a 7/ /L ? /
Phone:
b /W e r
''
/ ') *
Fax:____- a - . ______ :__ Pk_ A _ _____________
Sampler:
'kN S Q M O
Project Manager (Name & E-mail Address):
A i <A <
b
Project Name:
O u j /J,
C $>
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P- # : . A < f j , - > y ft < ' n ? ,1 ,, 4 * Quotation # :
9v
'S! Vi Vi \
'i
1
C om posite Number of C o n ta in e rs
- ' -f. t
Please fill out this form completely to ensure correct analysis and proper handling of your samples.
SAMPLE ANALYSIS
ExyLlMsr Client Sample Identification
Collection Date
Collection Time
I
-iOr,t
O
L h /c i'l
A it " 7 - 2 + O .rff^
i> t X g,0 Z_
\l-l r T V \ s s
f 7 Z . - 2- ~
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J ... u , 4 - , . ' Xi X
X J y
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L v r jy i ) ^ r ir r v n s - y / v y .jy x
'r js -y / v r U o
\ \
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x_ 1 5 Xy K JC
X ^y>1-"
S S
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60 0 C
O 0
LAB USE ONLY
CHAIN OF CUSTODY
Relinquished by
Date
Time 1)
U V> O o
Cooler ID # J/ecu,r I Cooler Temp. (C) >rJ
Received by !
Date .-VV' Time
ixfnixi^ /C'i 4
OTHER INFORMATION
LAB USE ONLY
000189
PROJECT REQUIREMENTS
Results Deadline:
Laboratory Report Options:
0 Sample results only 0 Add case narrative
0 Add quality control summary 0 Add calibration summary 0 Add raw data 0 Other______________
APPENDIX G LABORATORY ANALYTICAL DATA REPORTS
DRY RUN LANDFILL
000200
Proven Results.
RC H
Analytical Results Dry Run Landfill C8 Sampling 12/02
DuPont Sample Identification
APFO (ng/L)
DRL-Z-Outlet 001
56900
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.
0 0Q7
000201
058 Research Drive .State College, PA 16 80 1, USA
LT: 814.272.1039
ik F : 814.231.1580 exygen.com
APPENDIX H CHAIN-OF-CUSTODY RECORDS
DRY RUN LANDFILL
000202
CHAIN OF CUSTODY/ANALYSIS REQUEST FORM
Exygen Research Sam ple Receiving * 3 1 1 7 Research D rive State College, PA 1 6 8 0 1 , USA T: 8 1 4 .2 3 1 .8 0 3 2 * F: 8 1 4 .2 3 1 .1 5 8 0 ex yg en research.com
P a g e ______ o f _______
ON
oo
o
CHAIN OF CUSTODY/ANALYSIS REQUEST FORM
Exygen Research Sam ple Receiving * 3 1 1 7 Research Drive State College, PA 1 6 8 0 1 , USA T: 8 1 4 .2 3 1 .8 0 3 2 F: 8 1 4 .2 3 1 .1 5 8 0 exyg en research.com
P a g e ______ o f _______
PROJECT INFORMATION
Client (name & address):
/)h C /u
fi'/./, V )
.. A Phone:
_ ju* K-j -j ?> -
Sampler:
b,. aV
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..... .
FYoject Manager (Name & E-mail Address):
Z1-) / A t
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Project Name:
C ,r
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RO. $ _ s ` v \fl~ A/t bj. i //, fC
Quotation # :
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G rab Com posite Number of C o n ta in e rs
SAMPLE ANALYSIS
ExyLIMS#
Client Sample Identification no*
N O SVXWv'AsO
Collection Collection
Date
Time
*
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ANALYSES REQUESTED 1
$ 4
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LAD USE ONLY
CHAIN OF CUSTODY
Relinquished by
Date
Tim e
Cooler ID # Received by
OTHER INFORMATION
tQ 0 0 4
LAB USE ONLY
Cooler Temp. (C) O - . j
Date U /lib ic i
Tim e
V i -VC
PROJECT REQUIREMENTS
Results Deadline:
Laboratory Report Options:
CD Sample results only
f~l Add case narrative
CD Add quality control summary
I I Add calibration summary
CD Add raw data CD Other________________
CHAIN OF CUSTODY/ANALYSIS REQUEST FORM
Exygen Research Sam ple Receiving * 3 1 1 7 Research Drive State College, PA 1 6 8 0 1 , USA T: 8 1 4 .2 3 1 .8 0 3 2 F: 8 1 4 .2 3 1 .1 5 8 0 exyg en research.com
P a g e ______ o f _______
PROJECT INFORMATION
Client (name & address): ru. .l i___
------------------
Phone: Fax: Sampler:
/r .7*>>-<pj> - St <>#
Project Manager (Name & E-mail Address):
_____________ /a7 't
____________/ _____________________ Project Name:
____________ I $ l-'jJl -
________________________ ,________ ____________________________________
PO. # : Z/ZZA-
'jpjro'i'i
Quotation # :
Please fill out this form completely to ensure correct analysis and proper handling of your samples.
SAMPLE ANALYSIS
ExyllMS# Client Sample identification
h t - ~2-c*,tLh 6e j
Collection Collection
Date
Time
o *-
o a.
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uo 3 O Z U Specify Matrix
A -I * ^
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Pi r -*</> / ^ r j y /
ANALYSES REQUESTED
X
*
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N. \ `L
4
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CHAIN OF CUSTODY
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Date
Tim e
O il 1ER INFORMATION
00020S
Cooler ID # Received by
LAB USE ONLY
PROJECT REQUIREMENTS
r Cooler Temp. (C) .z
Results Deadline:
Date
Tim e
/ c W Laboratory Report Options:
\ 0 Sample results only
Add case narrative
n Add quality control summary
D A d d calibration summary
n Add raw data
CD O th e r _______________