Document ZJ2v3BnNN1O5NKn16z5L1wpOO
226-3648
INTERIM REPORT #1 Analysis o f Oakdale W ater Samples
STUDY TITLE Analysis o f Perfluorooctanoic Acid (PFOA), Perfluorobutanesulfonate (PFBS), Perfluorohexanesulfonate (PFHS), and Perfluorooctanesulfonate (PFS) in Water, Soil, Sediment, Fish, and Clams Using LC/MS/MS for the 3M Cottage Grove Monitoring
Program
DATA REQUIREMENTS EPA TSCA Good Laboratory Practice Standards 40 CFR 792
STUDY DIRECTOR Jaisimha Kesari P.E., DEE
Weston Solutions, Inc. 1400 Weston Way
West Chester, PA 19380 Phone: 610-701-3761
INTERIM REPORT COMPLETION DATE May 19, 2005
PERFORMING LABORATORY Exygen Research
3058 Research Drive State College, PA 16801 , Phone:814-272-1039
STUDY SPONSOR 3M Company
3M Building 0236-1-B-10 St. Paul, MN 55144 Phone: 651-733-6374
PROJECT Protocol Number: P0001400 Exygen Study Number: P0001400
Total Pages: 110
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GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT
Exygen Study Number P0001400, entitled "Analysis of Perfluorooctanoic Acid (PFOA), Perfluorobutanesulfonate (PFBS), Perfluorohexanesulfonate (PFHS), and Perfluorooctanesulfbnate (PFOS) in Water, Soil, Sediment, Fish, and Clams Using LC/MS/MS for the 3M Cottage Grove Monitoring Program," conducted for 3M Company, is being performed in compliance with EPA TSCA Good Laboratory Practice Standards 40 CFR 792 by Exygen Research.
Study Director Weston Solutions, Inc.
Robert A. Paschke Sponsor Representative 3M Company
Exygen Research lx - i *i ; ;:
c //? M Date
s f a j( K Date
/ 1Jg -s Date
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QUALITY ASSURANCE STATEMENT
Exygen Research's Quality Assurance Unit reviewed Exygen Study Number P0001400, entitled, "Analysis o f Perfluorooctanoic Acid (PFOA), Perfluorobutanesulfonate (PFBS), Perfluorohexanesulfonate (PFHS), and PerfluoTooctanesuIfonate (PFQS) in Water, Soil, Sediment, Fish, and Clams Using LC/MS/MS for the 3M Cottage Grove Monitoring Program." All reviewed phases1 were inspected for conduct according to Exygen Research's Standard Operating Procedures, the Study Protocol, and all applicable Good Laboratory Practice Standards. All findings ware reported to the Exygen Principal Investigator and Management and to the Study Director.
Phase 1. Protocol Review
Date Inspected
03/24/05
Date Reported to Date Reported to
Principal
Exygen Date Reported to
Investigator M saasmept Studv Director
03/25/05
03/29/05
05/19/05
2, Extraction Review
03/24/05
03/25/05
03/29/05
05/19/05
3. Raw Data Review and Interim Analytical Report Review
05/16-17/05
05/18/05
05/19/05
05/19/05
'Note; All inspections will be documented in the QA statement for the final analytical report at the conclusion o f the study.
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CERTIFICATION OF AUTHENTICITY
This interim report, for Exygen Study Number PO0OI4OO, is a true and complete representation o f the raw data.
Submitted by:
Exygen Research 3058 Research Drive State College, PA 16801 (814) 272-1039
Principal Investigator, Exygen:
Exygen Research
Date
Study Director, W eston Solutions, Inc
Jaisimha Kesari P.E., DEE Weston Solutions, Inc. Sponsor Representative, 3M Company:
Robert A. Paschke Manager, 3M Corporate Environmental Programs
Exygen Research
i- f fc$
6 / q ;/os~ Date
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Exygen Study No.: P0001400
STUDY IDENTIFICATION
Analysis o f Perfluorooctanoic Acid (PFOA), Perfluorobutanesulfonate (PFBS), Perfluorohexanesulfonate (PFHS), and Perfluorooctanesulfonate (PFOS) in Water, Soil,
Sediment, Fish, and Clams Using LC/MS/MS for the 3M Cottage Grove Monitoring Program
PROTOCOL NUMBER:
POOO1400
EXYGEN STUDY NUMBER: POOO1400
TYPE OF STUDY:
Residue
SAMPLE MATRIX:
Water
TEST SUBSTANCE:
Perfluorooctanoic acid (PFOA), Perfluorobutanesulfonate (PFBS), Perfluorohexanesulfonate (PFHS), and Perfluorooctanesulfonate (PFOS)
SPONSOR:
3M Company 3M Building 0236-01-B -10 S t Paul, MN 55144
STUDY DIRECTOR:
Jaisimha Kesari P.E., DEE Weston Solutions, Inc. 1400 Weston Way West Chester, PA 19380
SPONSOR REPRESENTATIVE:
Robert A. Paschke 3M Company 3M Building 42-2-E-27 St. Paul, MN 55144
PERFORMING LABORATORY : Exygen Research 3058 Research Drive State College, PA 16801
ANALYTICAL PHASE TIMETABLE:
Study Initiation Date:
03/03/05
Interim Analytical Start Date:
03/21/05
Interim Analytical Termination Date:04/21/05
Interim Report Completion Date: 05/19/05
Exygen Research
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PROJECT PERSONNEL
The Study Director for this project is Jaisimha Kesari at Weston Solutions, Inc. The following personnel from Exygen Research were associated with various phases o f this interim portion o f the study:
Name John Flaherty Karen Risha Paul Connolly Chrissy Edwards Mark Ammerman Amy Sheehan Eric Edwards James Miller Edward Kaiser
Title Vice President
Scientist Technical Lead-LC/MS
Technician Sample Custodian Associate Scientist Sample Custodian
Scientist Scientist
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TABLE OF CONTENTS
Page
TITLE PA G E............................................................................................................................ 1 GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT....... ......................2 QUALITY ASSURANCE STATEMENT............................................... ...........................3
CERTIFICATION OF AUTHENTICITY............................. ...................!.......................... .4
STUDY IDENTIFICATION.......................... ..................... .............. .......... ......................... 5
PROJECT PERSONNEL.........................................................
6
TABLE OF CONTENTS.........................................................................................................7
LIST OF TABLES....................................................................................................................8
LIST OF FIGURES.......................................................................................................... 9
LIST OF APPENDICES........................................................................................................ 11
1.0 SUMMARY....................................................................................................................12
2.0 OBJECTIVE.....................................................................
12
3.0 INTRODUCTION.................................................................
12
4.0 ANALYTICAL TEST SAMPLES.......................................
13
5.0 REFERENCE MATERIAL.................................................
13
6.0 DESCRIPTION OF ANALYTICAL METHOD......................................................... 15
6.1. Extraction Procedure......................................................... ........................................ 15 " 6.2. Preparation o f Standards and Fortification Solutions...... ......................................... 16
6.3. Chromatography...............................................................
17
6.4. Instrument Sensitivity..................................................................................................17
6.5. Description o f LC/MS/MS Instrument and Operating Conditions...........................17
6.6. Quantitation and Example Calculation....................................................................... 18 7.0 EXPERIMENTAL DESIGN........................................................................................ 19
8.0 RESULTS...................................................................................................................... 20
9.0 CONCLUSIONS........................
20
10.0 RETENTION OF DATA AND SAMPLES.............................................................. 2 0
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Table I.
LIST OF TABLES
Page
Summary of PFBS, PFHS, PFOS and PFOA in Water Samples..... ............................................................................ .......................... 22
Table EL Matrix Spike Recovery of PFBS and PFHS in Water Samples......................24
Table IH. Matrix Spike Recovery of PFOS and PFOA in Water Samples.....................30
Table IV. Surrogate Spike Recovery o f I3C PFOA in Water Samples...........................36
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Figure 1.
LIST OF FIGURES
Page Typical Calibration Curve for PFOA in Reagent Water................................. 43
Figure 2. Extracted Standards of PFOA in Reagent Water, 25 ng/L and 50 ng/L, Respectively............................................................................ ...........................44
Figure 3. PFOA in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively............................................. 45
Figure 4. Chromatogram Representing an Oakdale Water Sample Analyzed for PFOA, DF=100 (Exygen ID: C0064522, Data Set: 032405CR)......................................................................................... 46
Figure 5. Typical Calibration Curve for l3C PFOA in Reagent W ater.......................... 47
Figure 6. Extracted Standards o f n C PFOA in Reagent Water, 25 ng/L and 50 ng/L, Respectively....................................
48
Figure 7. !3C PFOA in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively......................................49 .
Figure 8. Chromatogram Representing an Oakdale Water Sample Analyzed for 13C PFOA (Exygen ID: C0064522, Data Set: 032405C)......... 50
Figure 9. Typical Calibration Curve for PFBS in Reagent Water.................................. 51
Figure 10. Extracted Standards o f PFBS in Reagent Water, 25 ng/L and 50 ng/L, Respectively.....................................................
52
Figure 11. PFBS in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively..............................................53
Figure 12. Chromatogram Representing an Oakdale Water Sample Analyzed for PFBS, DF=100 (Exygen ID: C0064522, Data Set: 032405CR)....................................................
54
Figure 13. Typical Calibration Curve for PFHS in Reagent W ater................................. 55
Figure 14. Extracted Standards of PFHS in Reagent Water, 25 ng/L and 50 ng/L, Respectively....................................................................................................... 56
Figure 15. PFHS in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively............................................. 57
Figure 16. Chromatogram Representing an Oakdale Water Sample Analyzed for PFHS, DF=100 (Exygen ID: C0064522, Data Set: 032405CR)........................................................
58
Figure 17. Typical Calibration Curve for PFOS in Reagent W ater.................................59
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LIST OF FIGURES Continued
Figure 18. Extracted Standards o f PFOS in Reagent Water, 25 ng/L and 50 ng/L, Respectively....................................................................................................... 60
Figure 19. PFOS in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively............................................. 61
Figure 20. Chromatogram Representing an Oakdale Water Sample Analyzed for PFOS, DF=100 {Exygen ID: C0064522, Data Set: 032405CR)........................................
62
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LIST OF APPENDICES
Appendix A
Study Protocol P0001400 (Exygen Study No. P0001400) with Analytical Method: V0001780:"Method o f Analysis for the Determination of Perfluorooctanoic Acid (PFOA) in Water by LC/MS/MS" ............................................................... .................
Page 63
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1.0 SUMMARY
Exygen Research extracted and analyzed water samples for the determination of perfluorooctanoic acid (PFOA), perfluorobutanesulfonate (PFBS), perfluorohexanesulfonate (PFHS), and perfluorooctanesnlfonate (PFOS) according to Exygen Method V01780 (Appendix A).
The limit o f quantitation for PFOA, PFBS, PFHS and PFOS in water was 50 ng/L and the limit o f detection for PFOA, PFBS, PFHS and PFOS in water was 25 ng/L.
Analytical results for the analysis o f PFOA, PFBS, PFHS and PFOS in water samples are summarized in Table 1. The overall average percent recoveries standard deviations for all fortifications o f PFOA, PFBS, PFHS and PFOS in water samples were 93% 1 9 , 141% 21, 96% 1 5 and 109% 32, respectively. The overall average percent recovery standard deviation for all fortifications of the surrogate field spike compound, ,3CPFOA, in water samples was 83% 21.
2.0 OBJECTIVE
The objective o f the analytical part of this study was to determine levels of perfluorooctanoic acid (PFOA), perfluorobutanesulfonate (PFBS), perfluorohexanesulfonate (PFHS), and perfluorooctanesulfonate (PFOS) in water according to Protocol P0001400 (Appendix A).
3.0 INTRODUCTION
This report details the results of the analysis for the determination of PFOA, PFBS, PFHS and PFOS in water using the analytical method entitled, "V0001780: Method of Analysis for the Determination of Perfluorooctanoic Acid (PFOA) in Water by LC/MS/MS."
The study was initiated on March 03, 2005, when the study director signed protocol number P0001400, The analytical start date for this interim report was March 21, 2005, and the analytical termination date for this interim report was April 21,2005.
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4.0 ANALYTICAL TEST SAMPLES
One hundred and twenty-one water samples, which correspond to twenty-nine sample sites, (Exygen ID C0064404-C0064438, C0064442-C0064461, C0C64467-C0064532) were received at ambient temperature on March 15, 2005 from Tim Frinak at Weston Solutions, Inc. The samples were logged in by Exygen personnel and placed in refrigerated storage.
Sample log-m and chain o f custody information is located in the raw data package associated with this interim report. Storage records will be kept at Exygen Research.
5.0 REFERENCE MATERIAL
The analytical standard, PFOA, was purchased from Sigma Aldrich and was received at Exygen on December 08, 2003. The surrogate spiking standard, 13C labeled perfluorooctanoic acid (13C PFOA), was received at Exygen on April 15, 2004 from the 3M Company. The analytical standards, PFBS and PFHS, were supplied by 3M. PFBS was received from 3M at Exygen on July, 06, 2000. PFHS was received from 3M at Exygen on January 20, 2003. PFOS was purchased from Fluka Corporation and was received at Exygen on April 23,2003.
The available information for the reference materials is listed below. PFOA was stored ambient. PFBS, PFHS and 13C PFOA were stored frozen and PFOS was stored refrigerated.
Comoound PFOA
i3C PFOA PFBS PFHS PFOS
Exveen Inventory No.. SP0003800 SP0004184 SP0000252 SP0002401 . SP0002694
Lot# 23116HB 3507-195
101 SE036 430180-1
Purity (%_) 97.64 97 96.7 98.6 101.2
Exoiration E 12/08/05 03/29/09 12/04/06 10/18/06 04/23/06
The molecular structures of PFOA, 13C PFOA, PFBS, PFHS and PFOS are given on the following pages:
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PFOA Chemical Name: Perfluorooctanoic acid Molecular Weight: 414 Transitions Monitored: 413 -> 369 (for quantification) and
413 -* 219 (for confirmation) Structure:
I3C PFOA Chemical Name: 1,2-13C perfluorooctanoic acid Molecular Weight: 416 Transition Monitored: 415 --v 370 Structure:
PFBS Chemical Name; Perfluorobutanesulfonate Molecular Weight: 338 supplied as the potassium salt (CiFsSChTC4) Transitions Monitored: 299 - 99 Structure:
FF
F F F so3
FF FF
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PFHS Chemical Name: Perfluorohexanesulfonate Molecular Weight: 438 supplied as the potassium salt (CsF^SOs'K4)
Transitions Monitored: 399 80 Structure:
PFOS Chemical Name: Perfluorooctanesulfonate Molecular Weight: 538 supplied as the potassium salt (CgFnSOa'K*) Transitions Monitored: 499 - 80 Structure:
F FF
FF FF
6.0 DESCRIPTION OF ANALYTICAL METHOD
The analytical method "V0001780: Method o f Analysis for the Determination of Perfluorooctanoic Acid (PFOA) in Water by LC/MS/MS" was used for this study,
6.1. Extraction Procedure
A 40 mL aliquot o f the water sample was used for the extraction procedure. After fortification o f appropriate samples, the samples were loaded onto a Cjg SPE cartridge conditioned with 10 mL of methanol and 5 mL o f water. The eluate was discarded. Approximately five milliliters o f methanol was added to the cartridge. Five milliliters of eluate was collected into a graduated 15 mL polypropylene centrifuge tube. Each sample was analyzed by LC/MS/MS electrospray.
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6.2 Preparation of Standards and Fortification Solutions
Individual stock standard solutions o f PFOA, UC PFOA, PFBS, PFHS and PFOS were prepared as specified in Exygen method V0001780. The stock standard solutions were prepared at a concentration o f 100 pg/mL by dissolving 10 mg o f each of the standard (corrected for purity and salt content, if necessary) in methanol. From these solutions, 1.0 pg/mL fortification standard solutions were prepared by taking 1 mL o f the appropriate stock and bringing the volume up to 100 mL with methanol. By taking 10 mL o f the appropriate 1.0 pg/mL fortification standard and bringing the volume up to 100 mL with methanol, 0.1 pg/mL fortification standards were prepared. By taking 10 mL of the appropriate 0.1 pg/mL fortification standard and bringing the volume up to 100 mL with methanol, 0.01 pg/mL fortification standards were prepared.
Several sets of standards containing PFOA, 13C PFOA, PFBS, PFHS and PFOS were prepared in water and processed through the extraction procedure, identical to samples. The following concentrations were prepared:
Cone, o f Fort
Fort
Volume o f
Solution
Volume Fortified Sample
(ngfaiL)1
(UL)
(mL)
0 0 40
10 100
40
10 200
40
10 400
40
100 100
40
100 200
40
100 400
40
1 o f PFOA, I3C PFOA, PFBS, PFHS and PFOS
Final Cone, of Calibration Std.
(ng/L) 0 25 50 100
250 500 1000
An additional mixed stock solution of PFOA, 13C PFOA, PFBS, PFHS, and PFOS was prepared at 1000 pg/mL and diluted to 100 and 10 pg/mL for bottle spiking purposes. Complete details can be found in the raw data package associated with this study.
The stock standard solution and all fortification and calibration standard solutions were stored in a refrigerator (4 2C) when not in use. Documentation of standard preparation is located in the raw data package associated with this interim report.
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6.3 Chromatography
Quantification o f PFOA, PFBS, PFHS and PFOS was accomplished by LC/MS/MS electrospray. The retention time of PFOA, PFBS, PFHS and PFOS was ~12 min, ~5 mins, ~11 mins, and -13 mins, respectively. Peaks above the LOD were not detected in any of the reagent blank samples corresponding to the analyte retention time.
6.4 Instrument Sensitivity
The smallest standard amount injected during the chromatographic run had a concentration o f 25 ng/L o f PFOA, PFBS, PFHS and PFOS.
6.5 Description o f LC/MS/MS Instrument and Operating Conditions Instrument: API 4000 Biomolecular Mass Analyzer
Interface: Turbo Ion Spray Liquid Introduction Interface
Computer: DELL OptiPlex GX400
Software: Windows NT, Analyst 1.4.1
HPLC:
Hewlett Packard (HP) Series 1100 HP Quat Primp HP Vacuum Degasser HP Autosampler HP Column Oven
HPLC Column: Thermo Fluophase RP, 50 mm x 2.1 mm
Column Temp. : 30 C Injection VoL: 15 pL Mobile Phase (A): 2 xnM Ammonium Acetate in water Mobile Phase (B): Methanol
Time (mini . 0.0
1.0 8.0 ' 10.0 11.0 18.0 Total run time; -18 min Flow Rate: 0.3 mL/min
%A 65 65 25 25 65 65
%B 35 35 75 75 35 35
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Ions monitored:
Analyte
PFOA PFOA Confirm Ion
13CPFOA PFBS PFHS PFOS
Mode
negative negative negative negative negative negative
Transition Monitored 413 -> 369 413 ->219 415 -> 370 299 -> 99 399 -> 80 499 -> 80
Approximate Retention Time
(min) ~12min. ~12 min. -1 2 min. -5 min. ~11 min. ~13 min.
6.6 Quantitation and Example Calculation
Fifteen microliters o f sample or calibration standard were injected into the LC/MS/MS. The peak area was measured and the standard curve was generated (using 1/x fit weighted linear regression) by Analyst software using six concentrations o f standards. The concentration was determined from the equations below.
Equation 1 calculated the amount o f analyte found (in ng/L, based on peak area) using the standard curve (linear regression parameters) generated by the Analyst software program.
Equation 1: Analyte found (ng/L) = (Peak area - intercept) x DF slope
Where: DF = Dilution Factor, factor by which the final volume was diluted, if necessary.
For samples fortified with known amounts of PFOA, PFBS, PFHS, PFOS and 13C PFOA prior to extraction, Equation 2 was used to calculate the percent recovery.
Eouation 2: Recovery (%) =
(analvte found (ng/L) - analyte in control (ng/LY) *100% amount added (ng/L)
An example o f a calculation using an actual sample and results from the PFOA analysis
follows: Water sample Exygen ID C0064432 Spk F (Set: 032105BR), fortified at 50000 ng/L
with PFOA where:
peak area intercept
= 1170161 = 26200
slope
= 1330
dilution factor
= 100
ng/L PFOA added (fort level)
= 50000
amt in corresponding sample (ng/L)* = 37600
(*The primary sample result was used for all calculations)
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From equation 1: Analyte found (ng/L) = IT170161 - 262001 x 100 1330
From equation 2: % Recovery
86012 ng/L*
(86012 n e /L - 37600 n e/O x 100% 50000 ng/L
= 97%
(values are slightly different from raw data due to rounding)
7.0 EXPERIMENTAL DESIGN
13C PFOA was used as a surrogate for all the samples, 13C PFOA was added to the sample collection bottles in the laboratory before being shipped to the field for sampling. For samples designated as field matrix spikes, PFBS, PEHS, PFOS and PFOA were also added at a known concentration to the bottles in the laboratory before being shipped to the field. The samples were filled to a 200 mL volumetric fill line in the field.
The samples were extracted in five sets. Each set consisted o f one reagent blank and two reagent blanks fortified at known concentrations. The first set contained six sample sites, the second set contained six samples sites, along with a trip blank and two trip blank spikes. The next two sets contained seven sample sites each. The fifth set contained three sample sites, along with a second trip blank and two trip blank spikes. For each site, a sample, a field duplicate and two-matrix field spikes were collected. For each site, a laboratory duplicate o f the primary sample was extracted and two laboratory matrix spikes were also extracted. For the two laboratory matrix spikes, two 40 mL portions of the primary sample collected for the site was poured from the bottle and fortified. Not only were PFBS, PFHS, PFOS and PFOA added in the laboratory prior to extraction, but also l3C PFOA was added. The additional I3C PFOA was added because the levels o f PFBS, PFHS, PFOS and PFOA spiked into the samples were known to exceed the calibration ranges and were not analyzed without dilution; therefore, 13C PFOA levels were adjusted to require the same dilution as the other analytes.
For each primary sample collected, between the field and lab, seven individual QC results were reported for 13C PFOA. Some samples gave recoveries for ,3C PFOA outside o f the normal acceptance range of 70-130%. Because laboratory control spikes for 13C PFOA were acceptable in every set, instrument washes were free o f 13C PFOA, at least one ,3C PFOA recovery per the seven done for the sample was acceptable and no evident errors in spiking or extracting could be found, no re-extractions were performed. 13C PFOA recoveries outside o f 70-130% are deemed indicative of matrix effects.
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8.0 RESULTS
Analytical results for the analysis of PFOA, PFBS, PFHS, and PFOS in water samples are summarized in Table I.
Fortification recoveries for PFOA, PFBS, PFHS and PFOS in the water samples are detailed in Tables II and III. The overall average percent recoveries standard deviations for all fortifications o f PFOA, PFBS, PFHS and PFOS in water samples were 93% 19, 141% 21, 96% 15 and 109% 32, respectively. Fortification recoveries for 13C PFOA in the water samples are detailed in Table IV. The overall average percent recovery standard deviation for all fortifications o f 13C-PFOA in water samples was 83% 21.
9.0 CONCLUSIONS
The water samples were successfully extracted and analyzed for PFBS, PFHS, PFOS and PFOA according to analytical method V0001780. There were no circumstances that may have affected the data quality or integrity.
10.0 RETENTION OF DATA AND SAMPLES
All original paper data generated by Exygen Research that pertains to this interim report will be shipped to the sponsor. This does not include facility-specific raw data such as instrument or temperature logs. Exact copies of all raw data, as well as a signed copy of the interim analytical report and all original facility-specific raw data, will be retained in file Exygen Research archives for the period o f time specified in EPA TSCA Good Laboratory Practice Standards 40 CFR 792.
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TABLES
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Table I. Summary of PFBS, PFHS, PFOS and PFOA in Water
E m m ID
C0064404 C0064404 Rep
C0064405
Client Sam ple ID
O KLM N -G W -W 3-O 435C310 OKLMN-GW 4N34W >5031<r OKLMN-GW -W 3-0-050310 Dup
Samples
Analyte Found (ppt, ngfl.) C4 SulfonaU PFBS C9 Sulfonate PFHS C8 SuHonst PfO S
312 162 4750 298 160 3350 303 15 3190
C Add PFOA
6330 6220 5990
C0064408 C00644408 Rep
C0064409
OKLMN-GW -W8-O4>50310 OKLMN-GW -W 8-CL050310* OKLMN-GW -W 8-0-050310 Dup
57.0 63.8 60.1
ND ND ND
59.0 290 55.7 275 56.3 284
C0064412 C0064412 Rep
CO064413
OKLMN-GW -W 264W J50310 OKLMN-GW -W26-0.05031CT OKLMN-GW -W 2$4W )50310 Dup
73400 75700 71400
222000 244000 214000
13500000 14400000 12200000
78300000 70200000 71BDCOOO
C0064418 C0064416 Rep
C0064417
O KLMN-GW -W 33-0-050310 OKLMN-GV-W 334Xk5C31 O ' OKLMN-GW -W 33-CM)50310 Dup
28800 28800 28500
92300 84600 81600
4610000 4870000 4540000
1750000 2020000 2790000
C0064420 C0064420Rep
C0064421
OKLMN-GW -W 205-0-050310 OKLM N-GW -W 2054M S031 O' OKLMN-GW -W 205-0-050310 Dup
8260 8800 7850
6740 6610 7070
146000 119000 116000
147000 150000 158000
C0064424 C0064424 Rep
C0064425
O KLM N-G W -W 215-0-050310 O KLM N-G W -W 215-0-050310* OKLMN-GW -W 2154K)50310 Dup
801 81.2 753
769
37100
4400
258
27000
3510
270
36900
4070
CO064428 C0064428 Rep
C0064429
OKLMN-GW -W 20100-050310 O KLMN-GW -W 2010 0 0 5 0 3 1 0 ' OKLMN -GW -W 2010 0 0 5 0 3 1 0 Dup
ND ND ND
ND ND ND
ND NQ ND ND
ND ND
C0064432 00064432 Rep
C0064433
O KLM N-GW -PW 7OO50310 OKLMN-GW -PW 7-0-050310* OKLM N43W -PW 7-0O50310 Dup
4460 4340 4830
4800 5080 5080
71600 67800 72400
37800 38400 38200
C0064436
O KLM N-G W -TRIP1 -0050310
ND
NO
ND
ND
C0064442 C0064442Rep
C0064443
O KLM N-G W -PW 80050310 OKLMN-GW -FW 8-O-O50310* O KLM N-G W -PW 8 0 0 5 0 3 1 0 Dup
13300 14100 14100
23800 23900 23000
34300 35600 33400
81400 80600 56500
C0064446 C0064446 Rep
C0064447
OKLMN-GW -PW 9-0-050310 O KLM N-G W -PW 00050310* O KLM N -G W -PW 00050310 Dup
2110 2140 1930
5160 5000 5140
84400 84900 88800
49000 46700 49900
C0064450
CQ064450 Rep C0064451
OKLMN-GW -W 6102-0050310 OKLMN-GW -W 61C2-0-050310* OK1_MN-GW-W6102-0-050310 Dup
NQ
53.5 NO
ND
ND NO
NQ 214
NQ 223 ND 227
C0064454
C0064454 Rep C0064455
O KLM N-G W -W 6104-0050310 OKLMN-GW -W 8104-0050310* OKLMN-GW -W 8104-0050310 Dup
NQ
N 51.2
ND ND ND
109 207
125 189 118 184
C0O64458 C0064458Rep
C 0064459
OKLMN-GW -W 6201 -0060310 0KLM N-GW -W 62010 0 5 0 3 1 O' OKLMN-GW -W 62010 0 5 0 3 1 0 Dup
74.0 74.1 78.0
ND ND ND
NQ 95.5 ND 68.3 NQ 132
C0O64467 C0064467 Rep
C0O64468
O KLM N-G W -W 200050309 OKLM N-GW -W 200050309* O KLM N -G W -W 200050309 Dup
13900 10700 10000
12900 9040 7860
46600 36300 30100
285000 243000 190000
C0O64471 C0064471 Rep
C0O64472
OKLM N-GW -W 22-00503D9 OKLM N-GW -W 220-050309' OKLMN-GW -W 22-0-050309 Dup
36800 32200 37500
31400 29500 25700
45300 34000 28100
317000 301000 244000
'Lsboratofy Duplicate ND = Notdetected at of above 25 ng/L. NO s Not quantifiable = Measured concentration between 25 noil, and the Limitof
Quantitation (LOQ) which e SO ng/L.
Exygen Research
Page 22 o f 110
000045
Interim Report #I-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table I.
enyBOntP
Summary of PFBS, PFHS, PFOS and PFOA in Water
CIUM Sample ID
Samples Continued
Anatyt* Pound fppt, C4 Suifonat P fBS C t Sutforat PFHS CB Sutfonat PFOS
CtAchfPFOA
C0W 4475 C0064475 Rep
C0064476
O K LM N -G W -W 31-0-05Q 309 OW.MN-GW-W31-04WO3O9* OKLMN-0W-W31-O-O5O3O9 Dup
1300 1360 1360
5130 4780 5190
132000 132000 156000
23100 22300 24900
C0084478 C0064478 Rep
C0064479
OKLMN-GW-W324M5503Q9 O K LM N -GW -W 32-0-050309* OKLMN-GW-W32-0-050309 Dup
C0064462 C 0064482R ep
00064483
O K LM N-GW -W 217-0-0 5 0 3 0 9 OKLMN-GW-W217-0-050309* OKLMN-GW-W217-0-050309 Dup
C0064486 C0O64+B6Rep
C0064487
C0064400 CC064490 R ep
C0064491
O K LM N -G W -W 200B-0-05030S OKLMN-GW-VV2008-0-050309* OKLMN-GW-W2008-04150309 Dup
OKLMN-GW-W2012-0-050300 OKLMN-GW-W2012-0-050309* OKLMN-GW -W 2012-0-050309 Dup
2180 2290 2960
ND ND ND
6780 7170 ' 6930
2210 1960 1920
3000 3120 2940
NO NO NO
10100 10800 10300
4700 4470 4420
47100 44400 83000
NQ NQ
128
15500 17800 18800
117000 118000 139000
117000 93300 125000
NQ NQ NQ
59300 58700 60300
48900 46400 51400
C0064494 C0064494 Rep
C006449S
OKLM N-GW -W 80-0050309 OKlM N^GW -W SO-0-050309* OKLMN-GW-W8O-O-050309 D tp
NO NO ND
ND ND ND ND ND . ND
302 250 328
00064498 00064498 Rep
C0064499
C0064502 CDC64502 R ep
C0064503
OKLMN-GW-PW1 -0-050310 OK LM N -G W -PW 1-0-050310* OKLMN-GW -PW 1-0-050310 Dup
OKLM M -GW -PW 2-0-050310 O K LM N -G W -PW 2-0-060310* OKLMN-GW-PW2-O4KO310 D tp
5620 5650 5580
641 624 694
4180 4150 4170
'5 0 1 4 S I700
66900 71600 70900
351 383 303
37300 39300 39100
3630 3890 5160
C0064S06 CCC64S08 Rftp
C0064507
C0064510 C0064510 Rep
C0Q64511
C0064514 C0064S14 Rep
00064515
C0064818 C0064518 Rep
C0064519
C0064522 CQ084522 Rp
C0064523
C0064526 C0064528 Rep
C006+527
OKLMN-GW-PW3-0-050310 OKLMN-GW-PW3-04350310* : OKIW N-GW -PW 34J-050310 D tp
O K LM N -G W -PW 4-0-050310 OKLMN-GW-PW4-Q-050310* OKLMN-GW-PW4-0-060310 Dup .
O K LM N -G W -PW 6-0-050310 OKLMN-GW-PW6-0-05GS10* : OKLMN-GW-PW8-0-0S0310 D up : :
OKLMN-GW-PW10-0-050310 OKLMN-GW-PW10-0-050310* , OKLMN-GW-PW10-0-050310 DUR
O KLM N-GW -PW 11 -0 0 5 0 3 1 0 OKLM N-GW -FW 11-Q-0503A 0* 0KLMN43W-RW11-0-050310 Dup
OKLM N -SW -0-050310 OKLM N-SW -0-050310* OKLMN-SW -0-050310 Dup
6970 6740 6570 V
8130 7700 7810
7930 8000 8130
13100 12700 11900 . .
6520 6490 7150
NQ NQ NQ
10000 9740 9990
7690 7480 7550
14500 14600 14800
29200 27400 . 26800
8820 10000 8050
NQ NQ NQ
32700 25500 32300
33600 30300 27800
90000 86000 86400
1400000 1760000 1740000
40800 50600 43400
1190 1200 1270
177000 160000 176000
72100 67800 65900
76400 78700 78500
719000 781000 614000
60300 71600 60600
491 529 537
C0064530
OKLM N-GW -TRIP2-0 -0 5 0 3 1 0
ND
ND
ND
ND
'Laooratary Duplica NO = Not detected at or abcrv25 ng/L. NQ * Not quantifiable = Maesurad concentration between 25 r>gfl- anq the Limit of
Quantitation (IO C ) which ts 50 ng/L
Exygen Research
Page 23 of 110
000046
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No. : P0001400
Table EL Matrix Spike Recovery of PFBS and PFHS in Water Samples
Sam ple Oeeeripti&n
C* Sulfonate PFBS Amount Amt Found Amount Spiked In Sem ple Recovered R ic c v r y
te u ~ -
< *>
Am ount S p ta d fotfL)
C tSulfeeetePFH S
Amt Found
Am ount
ft Sam pln Recovered
fnofU
Recovery m
O K U # NGW -W S-O-OM S10 See c, aeoo ngn. Lb SpM
O KLM N-G W .W 3-C-06W 10 ICboe444 * j * o, soooo r^n. Lab Spite)
O KLM N -G W -W 34-050310 Low Sp ike 5 ppb fCOOeMOt. #900 AtfLFted Spite)
O KLM N -G W -W 3-0-OW 31 D H igh S p fte 58 ppb (COMUffT, MOOP FM 0 Spite >
5000 90000 5000 50000
312 312 312 312
698Q
133
67400 ' 7450
134 143
74700
149
500C soooo 5000 50000
toe 162 182 182
5130 47500 5140 54400
09 55 100 100
OKLM fH#W -W 9~0-05031Q (COMMOt 3pk Ev.9000 apA. Lab spite)
O fO JH N -W -IW -O -e W W fl 00*440 Sp* F. fm M fl*L Lte SpUwl
O nU W M JW 'W S-0-05031a LOW Sp ike 9 ppb 00*4410. soot *i*L FWd Spite >
O KU IM -GW -W B-0-OS0310 H igh S p ik e SO ppb fCOOeMtt. #0000 up. fWW Bpite)
5000 50000 500C SOOOO
67.0 S7. 57.0 67.0
7020 70000 7410 70500
139 5000 140 50000 147 5000 141 50000
ND SO SO ND
5120 51400 5610 53300
102 103 110 107
O KLM N -G W W 2*^'O5OS10 (C00*4412Ssh <X 6000 *p*. L*b Spite)
OKLAIN-G W -W 28-0-DW 310 (C0M4412 SpS H. SOON n ?L tb Spite)
O KLI4N-GW -W 26-0-060310 Low Sp ike 8 ppb {COOS4414.#100 npA. Fkild Spite )
O K L M N -G W W i-8 -O M J W H igh S p ik e ppb (coeewts, so n s p <l f m v )
5000 50000 5000 60000
73400 73400 73400 73400
73 WO 125000 73200 147000
*
5000
222000
103 SOOOO 222000
5000
222000
147
socco
222000
207000 2S200Q 210000 266000
* '
O K LM N*GW -W 334)-OflGI1D <CP0*H1*spb 1,9000 rtgLU b S^kW
O K L M N 'O W -W tt-8-050310 <0006441* $pn J, scoot ngfl. U b Spite)
O KLM N-G W -W 33-(M l60310 L ow S p ik e 5 ppb <C006*4lt,5100up, F W S p ite )
M C LM M -SW -vm -O -O BM lO H igh S p ik e ppb (C006441*. 80000 ngft. FtWSpite )
500C soooo 5000 50000
26000 26600 26600 26600
33600 133000 38700 106000
*
5000
92300
212
50000
92300
5000
92300
102
soooo
92300
78000 122000 65200 150000
59 115
O KU 4N -G W -W 20S-0-05C310 (C0004420 3 (* X. 000 ngtL Lib Spite }
O KLM t^aW 'W 205-tM >B03l4 |COOM4 Spk L 40000 n/l Lab Spite)
OKUWN-GW-W205<046G1310 LOW Sp ike 6 ppb CCMS44ZX W M tupft.rW d Spite )
OKLM H 4JVM N2O6-O4)W J10 M g h S p * e M ppb {COfl*4433<SOOOOft*1. Ft*W Spite >
5000 50000 sono 60000
8200 6260
8240
15400 72500 tsaoo 62800
143 5000 6740 126 soooo 740 130 soon 6740 149 50000 6740
12500 53100 11BOO 60600
115 93 101 108
O KLM N-3W -W 21 *-0-056318 (C006443* Sfk II, 9000 np<L U b Spite)
0KLM N -G W -W 21S-0-0M 31P (COOI4424 SpkN. H0 noli. Lab Spite )
O KLM M*OW-W21 w - e s o n s LOW sp ike 6 ppb
(00004420, $400
S p ite )
0XLM H -G W 4N 215 4-0*0 31 0 H ig h S p ike ppb <0000443/. 60000 04. Fbk* SpiM )
5000 SOOOO 5000. soooo
001.0
7200
801.0
67200
01.0 , 6720
aot.o
669CO
128 5000 133 50000 118 5000 132 50000
76 769 760 769
5200 50300 240 48500
90 99 89 98
Saripie residue exceeds the spiking level sfeiUAcarnty; theretore, an w ain * * recovery value eaiwat be calculated ND * Not detected -at or above 25 nfifl- (ppt). N O - Noiquattfifiabl* M easured concentration between 25 ngA. (ppi) and the Limit of
&i*nflta(tan (LOO) which fe SOng/L <ppt). Note: Since tht* eummary (able snow* rounded m u lt i, recovery v iIm may v*ry*Hhtty from the valu es n th * raw data.
Exygen Research
Page 24 of 110
000047
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: PQQG140O
Table II. Matrix Spike Recovery of PFBS and PFHS in Water Samples Continued
3 * n ip l, O m crfD tlon
AmGunt 9p#w d f a ' 1-)
C4 S ulfonate PFB S
Amt Found Amount
In S em p le R eco v e re d R eco v ery
lV L)
tntfu
w
A m ount Spum i
l"0 0
C6 Sulfonate PFH3
Amt Found
A m ount
to Sem ple
R ecovered
(n#ft.)
f#A 4
R ecovery <%>
OHLM N -<3W *W 20H W W 550310 (C M * Spie C .< ttO nflA .U b S pite |
OKLMN43W4Y2O1O4W5O310 (CQMM42I Spk D. 0000 n * . t a b S pite)
OKUAN-4W -W 201O-0-0W 510 L o w S p ik e 5 p p b (CM*490, <000 * . Fiate pike )
OKUMN-GW-W2D1 <M)-060310 H ig h S p ik e 50 p p b IO0NM31. MOCO FI*M S te te )
5000 50000 5000 50000
NO NO NO NO
osso 6B600 700 83600
132 5000 139 50000 134 5000 128 50000
NO ND ND NO
4800 46700 4700 43700
96 97 94 87
OKUM N-GW-PWT4MWOS10 (COOSMS2 Spk e.9000 ru p i U b S p lM I
O K L M N -t SW -S * W 7 -C W )5 C S tO <CMM4J2 SfA f . IMOO n t f . t a b Spike)
OKLMN-GW -PW 7-W JM510 L ow p ik e p p b (CBOftMM. soeo rtpL F w e Spika )
OKLMN-GW 'PW 7*<W XW 10 H igh S pStbS O p p b iCecsuas.aoocg n * . f* w s > u \
5000 50000 5000 50000
4400 4400 4400 460
12200 72800 13200 00000
155
5000
137 50000
175 5000
151 5 0 0 0 0
4600 4600 4600 4800
10 50800 9370 59000
90 62 91 108
O K LU N -G W -TW P1-M 10210 Low S pike ppb CC00M4J7, O d PpL Raid S p ite )
O K L M N -G W -1R 1P1-041W 310 H ig h S p i t e SO p p b {CMWA43Sraooce a g l R eid Spike )
500C 60000
NO NO
640 44400
131 5000 88 50000
ND NO
4600 46100
92 92
O K U H N -O W -fW M -W 0310 (C0004442 Sek G. 900e n * L U b S p ite \
O K L M N <Q M N PW 8^K I0310 (COOM442S{M H, FOQM nf/LUb S pite)
OIOJWN43W W W W W W 1 0 L ow S p ik e 5 p p b 10000444. 0*0 f t * . Field S p ite >
OKLMN*GW-f>YW-OOS031C H ig h S p lit 60 p p b (COOW445.90000 n * . F ted S p ite )
5000 50000 5000 50000
13300 13300 13300 13300
21400 79700 21000 00700
162
5000
23000
133
50000
23600
154
5000
23800
135
50000
23800
29700 70300 30000 76100
118 93 124 105
QKLM N ^W rPW B-IHI60310 {C000444S Sfk I, SOOOnod. U b Spite )
OKLM N>GW ^W 9^^)60S1Q {CMieteM Spie J, 00000 n p L U b Spite ) O K LM H ^W -PV n-O O lD SIO L ow S p ik e s p p b
icoep4o, seoe n * . FieidSpite ) O K U lH -G W W -O -o M w io H igh S pik e So p pb
(00004441,90000 n t f . Field S p ite )
O K lJW N ^W -rttellkM i-M O M O 4COOS44SOSk K, MMOnbL U b Spfto >
OKLM N-OW -W 01M ^-P5W 10 (COOM490 Spk L, 40000 R * . U b S p ite )
OKLJ4N45W<W61G24L066!I10 Lo w S p ik e 5 p p b {C0M44K, 6003 K * . F te d S p ite |
OKXMN-GW Vyei02-CH>50ait H igh S plit 90 p p b IC0M4433, OOQOO n t f . FUM S p ite I
5000 50000 5000 50000 5000 50000 5000 50000
2110 2110 2110 2110
NQ NQ NQ NQ
0200 66000 9200 74800 7360 67500 7120 70700
144
SOO
5160
134 50000 6160 144 5000 5180
146 50000 5180
147 5000 135 50000 142 5000 141 50000
ND ND ND ND
9310 64400 9350 54800 4890 47400 5040 50600
83 90 84 99 98 95 101 101
*Sarr*>e reeidue exceeds the piking level geMesnSy; ff*refer, m accurate recovery value carro t be catenated
NO * Not detected at or above 25 npMPPONQ a Not Quantifiable = Measured ooncertfraftofl between 25 ncrt. (ppt) m d the UtrU ot
Quantttattan (LOQ) which Is $0 n * L (ppt). Note: Since this sum m ary table m o w s rounded results, recovery vsluee may vary eHgmty 1rm t i e values in th e raw dat&
Exygen Research
Page 25 of 110
000048
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table II. Matrix Spike Recovery of PFBS and PFHS in Water Samples Continued
Sam p i* D escription
4 Sulfonate P F B S
Amount Am tFound Am ount
Spiked in Sam ple Recovered RCOvw y
(n flit)
t e U .. !niU
_ (*)
Am auflt Sp ite d
ew
C t Sulfonate P F K $
Am tFound
Am ount
in Sam ple Recovered Recovery
(noJU
(nfl/U
(*>
O K LM N -O W -W tl04-P -O SW 9 {C06M454 9fei U. 90*0 004. Ufo Seite I
O K L M fW 5 W -w io * s io [C m U U Sp K K , IM M elLUrtSptt)
O K LM N-OW -W M 0 *0 4 1 D L ow Splka 5 ppb (C0N44M ,M M n^LFIaM Spite)
O KLM hM 3W -W 1IW -tM tKi3ia H lflh Sp ik e W ipph (COOtetfZ.800W nfeL PWd Belte I
5000 50000 5000 50000
NQ NQ NQ NQ
6680 73000 730 60700
134 SOOO 146 50000 135 5000 139 50000
NO NO NO NO
5050 48000 4720 51200
101 96 04 102
O K LM N-QW -W 201-C-06W 70 (CoosMSa Spk c, woo r * L ta b le >
O K LM N-GW-VVA201-0-O5PM0 (C004+4M Spk 0. sote ngfl U b afoe)
O K LM hW 3W -W 01-<M SW lO Low Spike 0 ppb (CttSitefl, SM noA.nate Spite >
OW J4fW 3W *V82P1-0-050319H lflb Spike 5 ppb (COOM4S1.fOM npfl. FieldSpite }
SGOO 50000
500 5000
74.0 74.0 74.0 74.0
6580 65500
077 7550
130 3000 131 60000 121 500 150 000
NO NO NO ND
4610 44400 543 5360
92 6 109 106
OKLM N-GW -W 20--0330t (Ce047 Spk E.seoe n^L LSb SHte )
0KLM N-G W -W 20-0- 60300 (COOiaUTSex MOOOnyTLU b BfeM )
OKLW N-W -W 2O-O-O0M09 L ow Sp r* 9 ppb (C M M M I. 5D0S t&L TiaM Spite )
OKUW 4*GW *W 2D*0*0503M HtQil S p lk a M ppb tCOOMm,900M s^ L FUI Spite )
5000 50000 5000 soooo
13000 13900 13900 13900
19400 77100 20900 85000
110 5000 12900
126
50000
12900
140
SOOO
12900
142 50000 12900
16200 56200 16200 48400
66 85 66 71
OKLM N -G W -W 32-M 503 (C0Q04O1 Spa C, 0000 nfrt.U b Spite )
OKLM N-W -W 22-0-&5IM O {COO94471 SJM -H.90000 r^ L Leb Sette)
O tO JflN -6V W 24-O S030 LOW S p A * 5 ppb (CMSMtt, 5000 r*JL FWd Spite >
O K LM N -G W <W 224*0603M H lflh Sp lka 50 ppb (000*4474, SMMO npL Flete Spite )
O KLM N-G W -W 31 0*050509 (C6044473 Spfc 1,9000 npLLab Spite )
O KU M K-G W -W St-lV O SO (CaeewT* Spk J, eneo - Ufo Spite |
OKLM M -OW -W S1 -0-050309 H igh Sp ike SO ppb IC0094477. MOOO nglL FteW Spite >
5000 50000 5000 50000 5000 60000 60000
36800 36600 36600 36600 1300 1300 1300
44100 109000 44000 111000
0450 70500 90900
*
5000
31400
145
50000
31400
5000
31400
149
50000
31400
143 5000 5130 138 50000 5130 179 50000 5130
37000 73003 35000 62203 9090 51200 63200
83 62 70 92 110
0KLM N-G W -W 32-0-D5O M 9 <C9CM47 Spk K, SOOO*0. U B Sptte }
O KLM N GW -W 32-0-05040 (C00e47B Spk L,50000 np/l.U b Spite)
O KU UM -G W -W 324M H 030 Low Spike 5 ppb (COOS4UO.09 i*fl. FieldSpite )
0KU U M *Q W -W 32-(M U 0 H lflh Sp ike 50 ppb {C00MU1,50000 A p t FtedSpite |
sooo 50000 5000 50000
21*0 2160 2180 2180
0910 67300 10800 66500
136 5000 3000 130 50000 3000 172 5000 3000 127 60000 3000
7400 SOOOO 71C 52600
66 94 96 100
resid* exceeds Ihe
level iprtiteantN: therefore. an accurate recovery value carsI'd be cdcuated
ND Not detected at or beve 25 neA*<PPb NQ Not quantSatte Meeeured cOTcantrartton between 25 rVL (ppl) end the Umrt at
Ojentlteton (LOQ) wNd> W ny/L (ppt). Note; Since thie summary feble show* rounded rssulfe recovery value* may vary styhWy
from the values to the raw data.
Exygen Research
Page 26 o f 110
000049
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table II. Matrix Spike Recovery of PFBS and PFHS in Water Samples Continued
Sam ple O ncriotka
Amount SpiXKl t>QX)
C4 Sulfonate PFBS
I
I
Am M t
m Stm pI* Recovered Recovery
NW
<u
<%)
Amount S p in e l (mUL)
C9 Suifenete PFHS
Amt fo u n d
Amount
M Sim pl ( 0
Fecovw id
R ucw w y
tn # X )
... J%)
O K LW W 3W -V IM 74>W iCOOeMI2$pkM.MOQnrLlafa Seim}
QKLMN-OW-W217-0-06MM (Cm m j m pk hs t o m an. u b spim >
OKU4kKlW.W217-<I.ASMO L ow S p lln p p b Field 3pM*|
OKLMN-aW-W217-0-OM30* H fch S p ik e SO p p b (CMM4M. 60* eeV FteW Spite 1
5000 50000 5000 50000
NO ND ND NO
6680 86800 7570 71200
134 5000 134 50000 151 5000 142 50000
ND NO ND ND
4880 46500 4590 51300
as 93 92 103
OKU4N-QW-W2O0-0-OW5W ICCW44Ms*i( a . w # na. u b seine >
OKLMN-OW-mOOe-O-OMMS C40*UM Spit P, 9000* Bflrt. U b Spike)
0KU4N-GW -W 2MW 4-MU0t Low Splk 5 ppb (ce*M*w> npw Beni s p n )
OKLMN-GW-W20M-0^33OS Hlfl h S p ik e 60 p p b tCOOM*. MOOnILFWfcl M W )
5000 soaoo 5000 50000
78 6780 67S0 6780
14300 73800 18500 6T9QQ
150 6000 i o n
134
50000
10100
194
5000
10100
182 50000 10100
16000 56500 16300 84000
its 93 184 109
OKLMN^3W-W2IH3'O*OSO300 (co m tm ip k C .W C o eA U 5 * to i
OK LM N -G W -V #20i2^-0503M (Caosetet 8p* 0, nooe a p t te e ipwe >
0 K U IN 4 W '-m S 1 2 - 4 3 m Low S p in 5 ppb {CO0M4CLSOM npft. Reid Spite)
O K U IN 4 3 W -M a tt-0 4 H K HJph Splk* SO p p b (C M *, WOODn p t Held Spike}
.5000 50000 5000 50000
2210
8800
2210. 1 66400
2210
8210
2210
71500
132 , 30 00 128 50000 120 5000 138 50000
4700 4700 4700 4700
6140 46900 6960 53800
88 84 8$ 96
OKLMN-GW-VWO-0-05030 {CWWW spk e, OM npl U P SpWcf *
5000
ND
850
137 5000
ND
4960
too
OKUHH-GWWttO"*-a63W {COOeMM Spk F, 90MDne*LU b Bplhe)
OK1JMN-CM'WD4M>HOS L ew S p ik e 5 p p b {CMM4U. SOMA<pLRete Spike )
0KLMR<OW'WMMHtS030ft Hlffh S p ik e W p p b tcoeeewr. m m * neo. nwe t b m >
30000 5000 50C00
ND NO ND
64700
7380 ,f 88700
12B 50000 148 5000 139 50000
ND NO ND
46200 5200 40200
92 104 98
0KLM H-QW W 1*0-0503 icsMMei Spec, n ee n ev u ib *pn)
O K LM ^W -PW 1-0-0<W 10 SM U I* Spfc R 80000 nfH. U b Spike)
OKLMN-OW-PWI-O-OSOSM L e w S p ik e 6 p p b (00004400, 9000 R*Jd Spite )
0KLMN-0W-PW1-0-06030 High Spike 0 ppb (CMM901, W npA. FleWISpfce )
sooo 50000 5000 50000
5B20
5020 r
5620
5620
13800 77000 13100 69700!
160 5000 4160 133 50000 4180 150 5000 4180 128 50000 4160
8880 52000 7690 47700
94 96 71 87
OKLMN-QW-PW2*0*050310 <C0M4Stt2 Spk i.eaMnpALabSpte}
OKU4N-GW-PW2-0-06310 {CMMI02 3f* J, 60000 ft*L U b Spite >
OKLMN-qW -PW 2-0-e310 Low Spike S ppb (C0M4SU4. StM up*. Reid Spite >
OKLMN-OW-PWi-S-OSDSIfl High S p * SO p p b {C0e*4d0S. 40000 np*. Field Spite )
5000
641
50000
641
s o a r - 641
50000
641
7720 65900 7030 64300
142 5000 131 50000 126 5000 127 50000
51 501 501 501
5280 47700 5190 44300
95 94 94 88
'Sample residue weed* (he piting level eigniAeanl^; therefore, en curate recovery value, cannot be calculated nd * NotQetecteCitoratcve 25 r>giL {ppt>. MQ a htotquandMbieBMeeeur3<aoncentretori between 25 no^Lfppti and the limit at
Q usntbtkw <LOQ} vhlch i> SOng/L (ppfi. Mote: Since tM i eummefy tib i sbow e rounded result*, recovery value* may vary*l>gfttly from the valve* In ih* **** data.
Exygen Research
Page 27 o f 110
000050
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study Np.: P0001400
Table II. Matrix Spike Recovery of PFBS and PFHS in Water Samples Continued
Sam ple D eo crlo d o n
Amount
$pik*d (nD
C4 8utfofiata PFBS
Amt Found Amount
in Sam pi* ROCOVWWl R eco v ery
tno/L)
(%>
A m ount Spiked
{no"-}
C6 Sulfonate PFHS
Amt Found
Amount
In S a m p I* R ecov--w j R ecovery
(*U
(%>
OtOMN-GW-PVWW-060310 (COOMH* 9pfc K.WM no. UO Spike)
OK LK N *G W -FW 3-0-0m it (000645 *pk U WeOOa*A. Lab Spike)
O K LM N -6W -FW 34460310 LOW 8 p lk * 6 p p b {COOMCM. BOO# ng/L FieM Spike >
OKUMN-GW-PWa-lWJWJiO H ig h S p lk * SO p p b {COOMSQ6, $ 0 0 e*CField Spike)
5000 soooo 5000 50000
9970 8970 6970 6070
13800 86900 15200 92300
137 5000 10QQ0
180 50000 10000
165
5000
` 1QOOO
171
50000
10000
13600 54400 16300 54900
72 69 126 9C
0KL M N -G W -P W 4-04H S 10 {COQMSII Spfc M, 5000 nofL Lab Spike)
0 KUVtN-GW-fW4-(M>5OS10 icoowci o Sait h. #oeoe av l Lab spoie)
OKLMN-GW-PW4-9-4W310 Low Split* 5 p p b (C0C645M, seoo n*/L FMd Spike)
OKLMN-CW-PW4-0-050310 High S p * e 00 p p b (OOOW91a. 500 ikpL. New Spike)
5000 50000 9000 50000
8130 8130 8130 8130
17400 95000 16300 86900
105 5000 7 0 174 5 0 0 0 0 7 8 163 5000 7690 162 50000 7690
13900 53600 13500 58200
120 91 112 101
DKLMN-GW-PWS-04B0SI0 {C0M4M4 SpkO, SOMa*#L La* Spite }
OKLMN-OW-PWS-tWSWIO <CMM514 Spit W,M#oa n y t U b Spike)
O K LM FW JW -PW W -0KJ10 LOW S p tk * 0 p p b (0044514. 9000 ng&. Flekf Spike)
OKLMN-GW-PW6-0-060310 H ig h SpUt* SOp p b (C0M4M7 .80000 n p l Held Spike)
5000 50000 5000 50000
7930 793C 7330 7930
17200 90500 17100 94600
185
5000
14500
166
50000
1450Q
183
5000
14500
173
50000
14500
20600 58800 20800 59400
122 66 128
OKLM N-GW-PW10-6-0*031 D fCMMrt SpkCrSflognan. u * spue)
OKLM N-GW-PW1 0-0-050310 00*4*14 Spk fc S0M0 npA. U h Spike)
OKLMH-GW-PWi 0-<M)60310 L ow S p ik e 5 p p b (CBOM83#, 6WOhq/L FId4 Spike)
(MOM N-aw-mift'O-CSOSIQ High Spik# 50 ppb (CDO44021.SIXMOi # l FWd Spike )
5000 50000 5000 50000
13100 13100 13100 13100
19300 70700 19000 74000
124
5000
29200
133
50000
29200
11S 5000 29200
122
50000
29200
34300 71000 33500 71300
102 04 06 54
0K1MN-GW-PW11-G-M031Q (COCMKZSpit E, MW npL Leb Spike )
OKLMN-GW-PW11 -O-DSOJI0 (COOMI215pk A, <9400 ngrt. LN>Spike)
OKLMN-GW-PW11-C-050310 Low Spike 5 p p b 4000*41, W -sA PM* *plk*)
OKLMN-GW-PW114)450310 Hlgh Split* 0 ppb icoOO40SS. 500*0 ng/L Field Spike)
5000 SOOOO 5000 50000
6520 6520 6520 520
12700 66300 13200 63600
124 5000 8620 124 50000 8820 134 5000 8S20 114 50000 8820
14200 65100 13300 54800
100 93 90 92
'Semple r e e tt* excaede the spiting level irgi*fican#y; fterefere, an accurate recovery value cannot be calculated NO Not detected a t or above 25 K^L iptf). N O * Not quaniiftebi* Measured concertarifon between 25 ng/t (ppt) * * 4 the UmR of
Q uartflM un 4LOO) which is 50 ngfl. {ppt). Nook Since th is a u m n w y Ubie show rounded reeu te, recovery value* mey vary nightly from dt* value In ib# raw data.
Exygen Research
Page 28 of 110
000051
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table II. Matrix Spike Recovery of PFBS and PFHS In Water Samples Continued
Sam pl*
P-crtP*"
C* Sulfonate PFBS
Amount Amt Found Amount
Spfltad In Sam plo RocovoroO R oeovoiy
tW W
t*>
A m ount
S p fta d
("A)
C * SuHb m I P FH S
Amt Found
Amount
in SM ipio
(")
Rocovorad
Rocom ry
(*)
OKLW N-5W ^080310 {Cooeme apa o . saoo n p i u rn 9po >
O laM N oSW -o-afio& io (C0M4S33 Byh H, 90000 nglL Lab Spike )
OKLM N^^O-OCaaiO Low S pike 5 ppb
(cooewo,K
spu )
OKLUN-SWO-OBW^O HlQb S p f c t BD p p b tC0**4$Za. 4OM0 FUid SpMw)
5000 50000 5000 50000
NQ NO NQ NQ
5900 63000 7260 65000
120 6000 12S 50000 145 5000 130 50000
NO NQ NQ NQ
4790 45100 52SO 49400
96 00 105 SO
OKLMN-aW-TNlP2-0-06fl3lO L o w S pike 5 p pb (CC0*6n. 9000 DOS.SpllUk )
DRUMN-<jyy-TRIP2*006031 o H igh s p ik e SO p p b (00*04332. WO n U l k | I
500C 50000
NO NO
4460 20100
90 5000 NO
50000
NQ
4970 49000
90 SB
Avenge: S ten d er Deviation:
141 21
`Sample residue exceeds t w spWr t a e l e&rtkcarttf, tberetore, an accurate itcovety value cannot be calculated
NO ^Md(Heeted<<>rauM25noA-<PPt}NQ Not tpjentflaw - M ured conoefitr^ior* between 2Srttf.(ppQ and fee Limit of
QuM ttaawt (LOO) w ncn s do oq/l (ppi). Note; Mace bite aummary UbW hmve rounded neoH e, recovery value* may vxryiUgMty from Uievelu-- In the raw det*.
Avtm tw : StM t4vd D w iaU am
a 16
lllfllliv-
EXygen Research
Page 29 o f 110
000052
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table III. Matrix Spike Recovery of PFOS and PFOA in Water Samples
Sam ple D escription
OKLMN-GW-WWJ-03O310 {C0DS44O4SafeC. COSOIttfL uta Spike )
OKLMN-GW-W3-0-C5O310 (Coset Ipfc P. SWOTngflUP Spate)
OKLMN-GW-W3-0-OSOMO L o w S p ik e 5 p p b (CW4449*,50Wflel Ft Sdite)
OKLMN-GW-W34HJ50310 High S pike 50 p pb ICSO4440?, m o m gii.fw **pjw i
C8 SuHonete PFOS
Am ount A m t Found Ammani
Amount
SpO ted I n S a m p la R a c o v a ra d R a c o v w y SpikMT
w (ng*U
C9 Add PFOA
Amt Found Amount
In Sam ple Racovam d
n L>
(nom
R aeo v ary (%)
5000 50000 5000 soooo
4750 4750 4750 4760
12400 73500 10800 84500
153 5000 135 50000 123 5000 160 50000
6330 8330 330 6330
11900 59200 9470 40100
111 106 63 80
OKdkkGW -W t-0-050310 [Co sm o 3ek f , aooo ngu, u b spike )
OKLM K-G -V tt-C-050315 (CWM4M f t * F, MOO*neTLUb Spite)
OKLM N-GW -W J4 -0 S 0 3 10 L o w S p ik e J p p b ICOMtMS, COOSnp&.R**d Sphw )
QKLMN-GW-WS-o-OSiiS'lO H ig h S p ik e 0 p p b <CQ0S441t. MOP ngiu nradpOv )
5000 50000 5000 50000
69.0 59.0 59-0 59.0
4940 55000 5380 50500
99 5000 110 50000 106 5000 101 50000
290 280 290 290
5350 51800 6050 33900
101 103 115 77
O K LM N (SW 'W 2t-0-05O 3i0 {CPM44t2Spk 6 , COMngfLU b 9 * te )
5000 13500000 9450000
*
5000
79300000
66300000
0KUUN^W 'W 26-<HUO31O (0WM4iSFfcH,seeeene*. u b b rfh i)
50000 13SOOO 7390000
$0000 79300000
68300000
OKLMN-GW-W2-0-0W310 Low Spike 9 ppb (CM44414. MOOrttyt Field 9pHn )
5000 13500000 9050000
-
5000
79300000
73100000
OKLMN-GW-W28-0-C50310 H igh S pike 50 p p b
(COMMIT SOCOCngfL OM Spike j
50000 13500000 7210000
50000 79300000
57900000
OKUWN-GW-WJWr-OMJIO |C0aM1gpt 1, 0 0 ngA.U b S p ite )
5000 4610000 4720000
.
5000
1750000
1520000
OKLMN-OW-W3J-0-OSOJ10 [COOQMtSSpkJ. SOM nolLUbSpih)
50000 4510000 4730000
50000
1750000
1650000
0KUUN-GW-W31*0-050310 L ow S p ik e S p p b
{OoosMte, soaiL fi* Sfris >
SOOO 4610000 4820000
.
5000
1750000
2350000
OKLMN-GW -W M-0-05M10 H igh SpOte 5 0 p p b
{COO0441. HOPOi p l FMd Spite )
5000D 4510000 4520000
50000
1750000
1630000
OKLMN-GW-VY205-0-03W10 (OM 44M SpK K. SOM *qlLLib Spi*)
OKLMN-GW-WJOS4L050S10 [CoeeMaaSpki-, rT ipa.u& 4pte i
OKLMH-GW-W206-0-0W310 L ow S pike 8 ppb ICW4MM, SOWnftO. Field Spite )
CKLM N-G**W 2054W $f0 W lS p ito e ppb (CaceMaa. sao qil fw <i saw *}
5000 50000 5000 50000
145000 145000 146000 148000
136000 156000 129000 221000
.
SOOO
147000
20
soooo
147000
*
5000
147000
150 50000
147000
160000 190000 14300) 164000
. 66 * 74
OKLMN-GW.WJ15 -0050310 <COWMMSpkM. SMS [*L UbSpik* )
OKLMN-GW -W 215-0*080310 SpfcN. 5000 flpIL U b SpiM )
OKLMN-GW-W21S41-05031Q L ow S pike 5 p pb
jCftOeMM,
Ftets Spite I
OKLMN-GW-W215-0-050310 High Spike 50 p p b (C0Q044S7. MOWnpL FMtf S p ite}
5000 50000 6000 soooo
37100 37100 37100 37100
52400 96900 66600 101000
* 5000 120 50000
. 5000 128 50000
4400 4400 4400 4400
8850 56700 9860 33200
09 105 85 70
Sample residua exceeds the spiking level significantly, therefore, an accuraterecovery value cannotbe calculated NO Notdetected at or above 25 ngA.(ppt| n q Nol Quantifiable * Measured concentration between 25 ng,t {ppt}and the Umit erf
Quantitation (LOQ) which is 50 ngL (ppO Note: Since ihl eummary tab) shows rounded results, recovery values mayvary slightly from the values in the raw data.
Exygen Research
Page 30 of 110
000053
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table HI Matrix Spike Recovery of PFOS and PFOA in Water Samples Continued
S w npJ* O afcrip tiO f
Amount Spiked (n tfD
li!
{a
C8SulfonalPF0S
Amount
Amount
R so o v sn d Recovery Spiked
(gm?______ c a _____ fc&o-)
Amt Found in S im p le
("fl-)
C l Acid PFOA
Amount R ico v eraci
R ecovery <%>
O KLM N-GW -W 2O 1O -O -06M 1O (C a to H zs apitCn so m &pflu b e p >
OKLM N-OW-W2010-0-050310
|C M M 4at 9 |* o. AMO otfts La
>
QKLMN-GW-W2010-0-050310 L ow S plke 9 pp b {C0QM430, M S *<*. FU N I 8pik* )
O KLM N -O W ttN 201 170-040310 Hlflt S p M SO p p b {CMW 44H, s o m boa. f m #i pii )
5000 - 50000
5000 30000
. ND NO NO NO
5170 54600 5270 54800
103 500C 109 50000 105 5000 110 50000
NQ NQ NQ NQ
5290 54300 4710 32300
106 108 94 85
OKU*M -GW 4W -^<W 50310 (C ow H tt * * c, * u * *p* >
OKLM N-GW -PW 7-0-050310 (0909# #91 Sptl F. M S bb*>U b df#m )
OKLMN-GW-PW7-04W0318 L ow S pfc S p p b (C ern # , o o n e ^ F ip d 8pnt* >
OKLM N 43W -PW 7-0-05W 10 H ig h A pik SOp p b (C0M M 35, S09M n ^ L F*H S O p to >
So d o 50000 5000 60000
7ieoo 71600 71600 71600
78500 110000 72600 118000
6000 95 50000 < 5000 89 50000
37800 37600 37600 37600
41900 88100 42800 87100
. 97 . 59
0KLM N -G W -TTO P1 -0-050310 L o w S p lk e S pp b (00044437, SO M np L Ftakl Spilla )
OKUKM -GW-TRJP14WI50310 H ig h S p ili 59 ppb (01094499. MODO A p i. P b ld 8pMb >
5000 50000
ND ND
5700 535D
116 5000 107 50000
ND ND
5360 50500
107 101
OKLM N -G W -P W I-< M 01 1 0 (CM444U tp k G, EMOngfl. Lab SfUt. )
QKXMN'GWPVWM>O5031O (CD0M4413pb H, 9MM ftflit Lab tpM n I
- OK LM N-GW *PV4Hto10 U w Splk* S ppb (00944444, M O in p lL Ffekl 8 p u * )
O KLM N -G W -P W S-0-030310 H igh S p i * SO ppb (C000444C. 804C0 npL FiaM 9ptk* )
5000 50000 5000 50000
34300 34300 34300 34300
38500 89800 38400 63100
5000 m 50000
- 5000 166 50000
81400 61400 81400 81400
61000 113000 59300 82200
103
42
OKUI4W-PVWW W W 0310 (CC044444 Spk 1. OMOnpA U b Opfci 1
OKLM M-GW-PW9-O-O50J1 0 (09094448 $pk 4, S0999rtpA. U M fp H )
OKLMN-GW-PWP^WWOa+O L o w S p tt 5 p p b (C094444*. 9900igA. FWW 8ptka )
aK U U M -G W -PW b-0-050310 H ig h S p i SO pp b tCPP4M#a, eoe n e i. fu ae >
OKLM N-GW-W6102-0-050310 (C00944M SpK K, SOM ap L Lab Sfrik >
OKUH4CW -W 810Z-0-05W 10 (c w a w * p u . m o n o , u n Stami
OKLM N-GW -W eiO2 '0 -0 W 1 0 L o w S p tk e 5 p p b |COO44413.9900 f t ? l Ft*M 9* i# 5
OKLUH-GW -W S102-0-050310HlQhSplk8 50ppt> (C 0M 44M , JMM npL Plaid SpUoi |
5000 50000 5000 $0000
5000 50000 5000 50000
84400 84400 84400 6X400
NQ NQ NQ NQ
83200 136000 98400 176000
5300 55800 5460 53200
5000 107 50000
- 5000 m 90000
106 5000 112 50000 110 5000 106 50000
40000 49000 49000 49000
214 214 214 214
50400 97900 55200 93200
5880 52700 5610 35300
. 96 88
113 105 108 70
Sample ratldua ax caad t tha afiikinQ levs! aipnlflcantiy. tharalorn. an accurate recovery vahra cannot be calculated MO - Notdatectnd a to r abcwo26 ng/L (ppt). NQ = Not quantnabta Maaaured concentration behmnn 25 nglL (ppt) and the U nit of
Quantilation (LOQ) wHdi ia 50 n oM ppt)Mctt: Since Blit nummary tibia thaw s rounded raatdte.tscovtry valuta may vary aBohfly tram tha valuta In thn raw data.
Exygen Research
Page 31 of 110
000054
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table III. Matrix Spike Recovery of PFOS and PFOA in Water Samples Continued
Sam ple D escrfcU o n
CI Sulfonate PFOS
Amount Pant Found A m ount
Amount
Spiked hi S am p le R eco v ered R ecovery S piked
W4
______ m m ______ r w _ _ man.)
CS A dd PFOA
Amt Found Amount
In Sam ple R ecovered
noto *
[nglL)
R eco v ery m
QKLN-GW-WS1O<LO-QSC310 (OMM4S4 Sah M9MWAert. U b S p fte )
0K L W hW 3W -W f104-0-05C 310 (C0M44S4 Spk H, MOC ngfl. Lab Spike >
OKLMN~GW -W 91W -0-050310 L o w S p ik e 5 p p b
(C00U 4M. BOMngtLFMd SpHw1
OKLMN-GW-W6104-0-C5031 H igh S p ik e 50 p p b <0*4*4*17, cm m n t. fu m Sp* 1
5000 50000 5000 50000
109 109 109 109
5540 59100 5700 56700
108 5000 116 50000 112 5000 113 5 0 000
207 207 207 207
5290 57300 5470 35800
102 114 105 71
OKLN*<3W -W 1201*0-050310
ICM444M 9pk C, 9000non U ti Spite)
O K LM N -G W -W S201-0-030310
(OM444Ct Spit 0. MOMn p L Lab Spike J
0KU4N43W-W821-0-050310 L ow S pike 0.5 p p b (CMfrMtt, m n pLFM d Spike)
OKLMF<KaW*WS2014 4 5 0 3 1 0 H ig h S p lk 5 p p b (C9M4441. 9 0 f tp ! FWd Spike)
5000 50000
500 5000
NQ NQ NQ NQ
49B0 50000
670 9000
10Q 5 0 0 0 100 50000 134 500 132 5000
95.5 95.5 9 5 JS 95.5
4950 50800
605 6130
97 10T 102 121
QKLM NW 3W -W20-S- 0 5 0 3 0 9 (C00I4447 Spk E. MOOngn. u e Spue >
OKLN hM5W*W204-09M0S
|CCde47SptcF. to t nplLLabSpike}
OKLMW-GW-W20-O-OSWO9 L o w S p ik e 5 p p b fC40f44M, SPMns/t Field S pite)
Q K L M N -G W -W 20445090 H ig h S p ik e SO p p b (CMU470. MOMnot Field S uite)
5000 50000 5000 50000
46600 49800 46600 46800
49900 92800 41900 59500
5000
285000
92 50000 285000
5000
285000
20 50000 285000
289000 235000 278000 264000
0K L M N -G W -W 22-0-0 3 0 3 0 9 Spk 0 , SAMftpft. Leb Spike)
O K LM N -G W -W & 44SO SO
{C0M44T13j* H, SOHNAtfL Lab SptM J
OKLM M 43*<W 2244H30* Low Spike 5 ppb (C0M4473, MOO ng/L Field Spike)
O K L M N -G W -W 2 2 4 4 5 0 3 H ig h S p ik e SO p p b (CW44474,30000 n tf. FM d Spike)
O K L M N -G W -W 31445Q 309
(CMM47S Spk L SOMn&L U * S p M )
OKLMkMeW-Wai4 4 5 0 3 0 9
90*44759* 4, MMflntfL Ufa Spite) OKUMN-aW-WS1 4 4 BOSOS High Spike SO ppb
(06044477, MOMftpfL Field Spike)
5000 50000 5000 50000
45000 45000 45000 45800
5000
132000
50000 50000
132000 132000
44600 99500 41200 66800
116000 160000 216000
*
5000
317000
105 50000 317000
-
5000
317000
40
50000
317000
.
5000
23100
72 50000 168 50000
23100 23100
33000C 412000 324000 286000
26400 71300 65700
96 85
0KLMN-GW -W 32443DW 9
{COOM47SpkK. M0nek. Leb 8pte )
5000 47100
62200
*
5000
117000
t3K LM H <W -W 3244S0309 (CM4M74Spk U MOM n * L LabSpdte)
50000
47100
115000
138 50000 117000
OK LiW 5W -W 334450309 Low Spice 5 ppb
(CftOOUM, MM 1TLFteM SpOt*)
6000
47100
74000
5000
117000
KLMN-GW-WS2-6-O5M0 H igh S p ice 50 p p b
(CM4ttt, MPMnelL FMd Spike)
50000
47100
120000
148 50000
117000
109000 151000 131000 1S70QQ
*
Sample residue exceed the spiking level significantly, therefore, an accurate recovery value cannot be calculated ND 3 Notdetected a lo r above 25 ngA (ppt}. NQ * Noi quantifiable - Measured concentration between 25 ngA (ppt) and the Llmh of
Quantitation (LOQ) vrfticfo le 50 ng/L (ppt). Note: Since i d * ummarylaW sh o w rounded result, recovery value may vary HgMiy
from the value In the raw date.
Exygen Research
Page 32 o f 110
000055
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P00OI400
Table III. Matrix Spike Recovery of PFGS and PFOA in Water Samples Continued
Sample Oeecrtotkm
OKLMN-GWW217-0-tiM3M tceeeeeu si*m ,eaeo ngitu e Spa i
OKLMN*GW-W217-0-050309 fcaeeeeiaSe* n .seesBflfliLebsc)
O K U M U 3 W A V 2 i 7 O S 0 3 M L o w Splka 5 ppb
(Cowim.
r *w spe* >
OKLMK-<SW-Wai7-M50J09 Hlflk Splka SO ppb {Oboeeea^ s m m no.F W d Sew)
Cl Sulfonate PFOS
C l Acid PFOA
Amoutt Amt Found Amount
Amount Amt Found Amount
Splkad kl Sawpl* Recovered Recovery Spliced kiSampln Recovered
("VU
O W ' D .frtf______ & } ____ i S & L ... ("STM
(tlBrt.)
5000 50000 5000 50000
NQ NQ NQ NQ
4790 700 5900 65300
96 5000 99 50000 116 5000 131 50000
NQ NQ NQ NQ
4880 52200 4880 42600
OKLMN-GW-W2OOB-O-OWd09 (COWMM SekO.000 &.LSb SgUe \
OKLMN-QW^f2D08490M* (Ceee44ese a,aowe nn.taban 1 OKLMN-GW-WaMS-<M)M309 L o w Splk* 5 ppb
<C0MMM. SWOaa'LFWO SOM)
O K L M N-GW^V2004m50je HlflhSpJk* M ppb (COeMe, soeoeneiLfieldSoftie)
SQOQ 50000 6000 50000
1550Q 15500 15500 15500
2Q800 69300 77000 71300
109 5000 108 50000 230 5000 t12 50000
59300 59300 59300 59300
04900 114000 73600 94800
OK1^N-<3W'W2O12-O-O5C309 <c o m 4S*Sj* c,sooo non.m e Spike)
500C 117000 143000
* 5000 46900
QKU*N-GW-W2013WK>50ai <cob<iiso See D,eooco g i u b spitwj
SOOOO 117000 185000
138 50000
46900
OKLMN-GW-W201 2-4W6M00 L o w 8pfce 3 ppb fCOfliMMt, MMfteLFfeM Spike)
5000
-117000 . 115000
'
5000 . 46900
OKLMN-<3W-W2012-0*050309 High Spike 90 ppb (00004403.MOMneA. FleM SpOn)
S0D00
-117000
203000
172 50000
46900
57700 94700 48500 69500
OKLNN-GW-WSO'O-OMSO {C0664464Spfcfe,M M neALe* Spike)
OKLM)NGW-WS0.M503O {CB0044M $pk r,90000epL U b Spfee)
O KLWffGW-WSO-O^MSOO L o w Spice 5 ppb toeeeMee.om ngn.n d e spam)
OKLMN-GW-W8O-<K0309 HlfihSplk* 50 ppb {CMS44t9, M M o nee.fieldOpto*>
5000 V 'ND
50000 '"'NO
'5000
NO;
'50000
ND
5280 52900 5720 57600
106 5000 106 50000 114' 5000 115 50900
302 302 302 302
5910 53100 5880 42200
OKLMNK5W>4*WHK0310 (000*440tp k G,M04 ngILm b Spike)
OKLMN-GW-PW1-O-&50J10 (00004400 SfcK.M O M n*L Lab StflW)
OKLMN-GW-PW1-0-050310 Lo w Spike 5 ppb 4CDM400C, 00 ngrvnote spot>
QKLIAN-GW-PW1 *0*050310 HlQh Splk SO PPb (C0MCM1. 00600 BO* FWcl OpU )
5000
66900
50000 ` *66900
500C
66S00
SOOOO 66900
72000 116000 96900 '95200
-T 5000 102 50000
5000 57 SOOOO
37300 37300 37300 37300
47700 90200 40400 80500
OKLN-GW^W20-05031<r (COOMMt i,M60 ng/L Lab Splka>
5000
351
5490 , 103
sobo
OKLMN-GVV-FW2-0-9S0310 (CQ0045Q2Spfc4.0000 ngA.Lak Spike)
50000
351
59000
119 50000
Q K LMN-GW-PW2-M50310 L o w Splk* S ppb {C60eU64r90M ege.F1M Spite3
5000 . . .35.7 . 4280,
79 5000
QKLMK-GW*FW2-O'Q9031<l Hlgb Spike SO ppb (C0004MB, BOOM apA.F M4 tpH* )
50000
351
40500
50 SOOOO
3630 3830 3630 3630
8720 58800 7860 39500
Reeowy 0*t 97 104 98 85 109 * 71 -
86 .
85
110 106 111 84
* 106
ae 102 110 85 72
Sam ple reeidue exceed* th e piking lev d significantly; therefore, an accurate recovery value cannot b e edcuiated
NO s Not detected a t or above 25 ng/L (ppt).
NQ - Mm quanttfabte * Vtesauf&d corvc&n*Bori betw een 25 ng/L (ppt) and th e U n it a t
Quantitation (LOO)whichIs 50 opT. (ppt). Note: Since this sommarytable howrounded resuRi, recoveryvalues mayvarysligftdy front the values Inthe rawdata.
Exygen Research
Page 33 of 110
000056
Interim Report #1 -Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table III. Matrix Spike Recovery of PFOS and PFOA in Water Samples Continued
Sample
C4 Sulfonate PFOS
C l Acid PFOA
Amount Amt Found Amount
Amount Amt Found Amount
Spiked in Sample Recovered Recovery Spiked in Sample Recovered Recovery
O K L M N -SW -PW 3-W 031P {em etto* Spk K. seso nglL Lab S p ite )
OKLM N-OW PW 3*0050310 tc e e e e w ip * l. seeee ngiu u b sp u e )
OK LM N-GW -PW 341-65031D L ow S p ik e 5 p p b (coo, sqm hc/l f h w en * >
O K L K N -W -P W 34'050310 H ig h S p ik e 90 ppfa (cao s * , looes * & . fu m S p ite }
5000 50000 5000 50000
32700 32700 32700 32700
43300 66100 33800 60000
5000 67 60000 * SOOO 55 50000
OKLM N K JW -PY M -W K O ll0 IC00W9 t u t N. MM n tfl 1*6 8plk )
OKLM N-GW -PW 4-0-06031Q <C 0m *1PSrtH , SNOOrroL U fr S p ite )
OKLM N -G W -PW 4-045G 310 LOW S p ik e 9 p p b SOM nafLFW d S p ite }
OKLM N-G V W V 4 -0 -0 5 0 3 1 0 H ig h S p ik e SO p p b { C aeeo n . looeo noli- F ie * S p ite y
5000 SOCCO 5000 50000
33600 33800 33800 33600
42500 75700 42200 81200
5000 84 50000 * 5000 95 50000
O K LM N-GW -W 0-0-O5O 31O (C0M514 9g k O.M OOrigfLUh S p ite )
OKLM N -O W -PW l-0-050310 (c e e e ts te spk p, seeeo npiL Lab sp ite }
OK LM N-GW W O-O -O SOSIO L o w S p ik e 5 p p b fCOOetCte WOOngiL Field Spite )
O K LM *G W -PW 8-0450310 H ig h S p ik e 5 0 p p b 1CMS4517. WOO n *L P M * Spite ]
5000 50000 5000 50000
90000 90000 90000 90000
97600 139000 94100 124000
* 5000 9 6 SOCCO 5000 66 50000
O K LM N -G W -PW 10-0-050310 (0004491 Spk C, SOM ngCL U b S p te )
O K LM N -G W -PW 10-0-050310 (C004441S tpk O, SOOOOngt. Lab S p ite }
5000 1400000 1410000 50000 1400000 1390000
5000 50000
OKLM N -G W -FW l M N 0M 310 L ow S p ik e S p p b
{ O ttstsae, o n t*gn- f m S p ite )
5000 1400000 955000
5000
O K LM N -G W -PW 10-0-05031 H igh S p ik e 50 p p b
(COIttCM, 0 1*90. FM d Spite )
50000 1400000 1910000 90000
O K LU N -G W -PW 114H 3 310 (co a e e a a spx e , sodo npa. Laespnw )
OKLM N-GW -FW 1 1-0 -0 5 0 3 1 0 IC SM te a Spk F, BSOOan^L Lab Spite } 0KLM N -6W -PV * H M J5 0 1 0 L o w SpIK a S p p b
(CM 4M K M M nafLPtoM S o d * )
OKLM N-GW -FW 1 1<0-050310 H ig h S p ik e 90 p p b (CMS4B29, sooei nprt.Field Spite >
5000 50000 9000 50000
40600 40800 40800 40000
48900 03100 45400 68500
* 5000 as 50000 * 5000 85 50000
Sample residue exceed (he spiking tevei tignifteantly; therefor*, an accural recovery value cannot be catenated
N O s Not detected at or above 25 ngA (ppi). N Q - Not (tuardnabie * Measured concentration between 2 5 npA. {pptj and the Limit of
QuanmeUon (LOQ5 which is SO ng/L. (pptL
Note: Since Pile ummarytable snows rounded leeuita* recoveryvslues mayvaryslightly from thevalues In the raw data.
177000 177000 177000 177000
72100 72100 72100 72100
76400 78400 78400 76400
719000 719060 719000 719000
60300 60300 60300 60300
138000 190000 196000 204000
77500 121000 80700 118000
82800 133000 67000 116000
868000 40000 692000 747000
64700 105000 63300 88100
26 54 * 96 68 108 * 75
* . 89 * 76
Exygen Research
Page 34 of 110
000057
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table III. Matrix Spike Recovery of PFOS and PFOA in Water Samples Continued
Sampl* M crlotioa
OKLMM-SW-O-050310 (C8H4CM*f* G.9909fttftLa*tyfm)
OKLMN-SW-04S0110 <ceetm* * a soona* l ue Spu*) OKLMH-SW-O-OSMH) Low Spike 5 ppb
(Casetta, som a^l two aereej
OKLMN-SW-0-050J10 Hlflh Spike SOppb (Ceeeem.tow e*.two Sere*>
OKLMN-GW-TR1P2-0-050310 Low Spfce 5 ppb (CMMMMI.9eOOn9rt.SpeV)
OKLHN-3W-TFIP2-!WOJ10 Hlflh Spin 50 ppb (C00MS3Z.SOMnort.Spike)
CISulfonaM PFOS
Amount Amt Found Amount
Spiked MSample
W
(ngfU
(ntfU
W
5000 50000 5000 50000
1190 1190 1190 1190
6270 51600 7220 58000
102 101 121 114
5000 50000
ND ND
8170 57400
123 115
& S 3
Amount
Spiked (9*4
C3 Acid PFOA
Amt Pound Amount
in Sampl Recovered
Jns*U
(np/L)
Recovery <%>
5000 50000 5000 50000
01 401 491 491
5520 53200 8020 44200
101 105 111 B7
5000 50000
ND NO
6040 57300
121 115
Average: 110 Standard Deviation: 32
"Sam ple ewiduft exceeds the spiking level significantly, therefore, an accurate recovery value esnriol be calculated
NO * Notdelactedai orabove33 ng/L(ppt).
NO = Not quanW bblo =*M easured concentration betw een 25 ngA. (ppt) an d the Lbril of Quamtatfon (LOO) which le 50 ng/L (ppt).
Not*:Since lliia summarytablebows roundedreeutt*.recoveryvaluesmayvarysHohtV fromthevaluesintherawdata.
Average: Standard Deviation:
4 1
Exygen Research
/ Page 35 of 110
000058
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table IV, Surrogate Spike Recovery of 13C PFOA in Water Samples
Exygen ID
Sam p le D e sc rip tio n
Am ount S p lk e d (n g /y .
T -P F O A
Am ount Recovered
(n o *)
Recovery m
C0064404 Spk C C0064404-Spk D
C0064404 C0064404 Rep
C0064405 C0064406 C0064407
OKLM N-GW -W 3-0-050310 O KLM N-GW -W 3-0-050310 OKLMN-GW -W 3-0-050310 OKLMN-GW -W 3-0-050310 OKLM N-GW -W 3-0-0S0310 Dup
OKLMN-GW -W 34>-050310 Low Spike 5 ppb OKLMN-GW -W 3-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5580 53900
431 422 416 4730 34500
101 107 86 B4 83 95 69
C0064408 Spk E C 0064408 Spk F
C0064408 C 0084408 Rep
C0064409 C0064410 C0064411
OKLMN-GW -W 8-0-050310 OKLMN43W -W 8-04J50310 OKLMN-GW -W8-O-05O31O O K LM N -G W -W 8-0-050310 OKLMN-GW -W 8-0-050310 Dup OKLM N-GW -W 8-0-C50310 Low Spike 5 ppb OKLMN-GW -W 84J-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5840 55900
466 452 483 5550 39400
106 111 93 90 97 111 79
C0064412 Spk G C0064412 Spk H
COO64412 C0064412 Rep
C0064413 CO064414 C0064415
OKLMN43W -W 26-O-C50310 O KLM N-GW -W 26-0-050310 OKLMN43W -W 26-0-C50310 OKLMN-GW -W 26-0-050310 OKLMN-GW -W 26-0-050310 Dup OKLMN-GW -W 26-0-05Q310 Low Spike 5 ppb OKLMN-GW -W 26-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5430 32900 7720 7660 7540 5210 28000
99 65 * *
104 56
C0064416 Spk I C0064416 Spk J
C0064416 C0064416 Rep
C0064417 C0064418 C0064419
O KLM N-GW -W 33-0-050310
OKLMN-GW -W 33-0-050310 OKLM N-GW -W 33-0-050310 O KLM N -G W -W 33-0-050310 OKLMN-GW -W 33-0-050310 Dup OKLMN-GW -W 33-0-050310 Low Spike 5 ppb OKLMN-GW -W 334M350310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
3160 48000
262 256 261 2750 42500
57 95 52 51 52 55 85
C0064420 Spk K
C006442D Spk L CO06442O
COC64420 Rep C0064421 C0064422 C0064423
OKLMN-GW -W 206-0-050310 OKLM N-GW -W 2054)4)50310 O KLM N-SW -W 2O 5-C-050310 OKLMN-GW -W2Q5-0-05C310 OKLMN43W-W20545-O50310 Dup OKLM N-G W -W 205-04)50310 Low Spike 5 ppb OKLMN-GW -W 205-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
4940 53000
279 280 307
4240 38000
90 105 56 55 61 85 75
C0064424 Spk M C0064424 Spk N
C0064424 C0064424 Rep
C0O64425 C0064426 C0064427
O KLM N-GW -W 215-04)50310 OKLMN-GW -W 215-04)503tO OKLM N43W -W 215-04)50310 OKLMN-GW -W 215-0-050310 OKLMN43W -W 2154W 50310 Dup OKLMN-GW-W215-0-Q5Q310 Low Spike 5 ppb
O KLM N-G W -W 215-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5850 56700 1010 434 464
4960 35600
106 112 202 87 93
99 71
The very high PFO A level In the undiluted sam ple Interfered with '*C PFO A recovery. Note: Since thl sum m ary table show s rounded results, recovery values may vary slightly from the valuee In the raw data.
Exygen Research Hi ^
Page 36 of 110
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table IV. Surrogate Spike Recovery of 13C PFOA in Water Samples Continued
Exygen ID
Sam ple Description
Amount Spiked ing/L)
1lC -P F O A
Amount Recovered
(nS>L)
Recovery .._<*)
C0064428 Spk C CQ064428 Spk D
C0084428 C0064428 Rep
C0054429 C0064430 C00B4431
O KLM N -G W -W 2010-0-050310 OKLMN-GW-W2010-0-050310
OKLMN-GW-W2010-0-050310 OKLMN-GW-W2010-0-050310 OKLMN-GW-W2010-0-050310 Dup OKLM N-GW-W2010-04)50310 Low Spike 5 ppb OKLMN-GW-W2010-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5390 53000
432 417 510 4500 30200
98 105 80 83 102 90 60
C0084432 Spk E C0064432 Spk F
C0064432 C0064432 Rep
CO064433 C0064434 COOS4435
OKLMN-GW-PW7-0-050310 OKLMN-GW-PW7-0-05Q310 OKLMN-GW-PW7-0-050310 OKLMN-GW-PW7-0-050310 OKLMN-GW-PW7-0-050310 Dup OKLMN-GW-PW7-0-050310 Low Spike 5 ppb OKLMN-GW-PW7-0-050310 High Spike 50 ppb
5500 500C
503 500 500 5000 50000
5260 51000
341 335 325 4820 33200
96 101 68 67 65 96 66
C0064436 C0064437 COO64438
OKLMN-GW-TRIP1-0-050310 OKLMN-GW-TRIP1-0-050310 Low Spike 5 ppb OKLMN*GW-TRIP1 -0-050310 High Spike 50 ppb
500 5000 50000
510 5100 51300
102 102 103
C0064442 Spk G C0064442 Spk H
C0064442 C0064442 Rep
C0064443 C0064444
C0064445
O KLM N -G W -PW 8-0-050310 O KLM N -G W -PW 8-0-050310 OKLMN-GW-PW8-0-050310 OKLMN-GVV-PW8-0-050310 O K I WN-GW-PW8-0-050310 Dup OKLMN-GW-PW8-0-050310 Low Spike 5 ppb
OKLMN-GW-PW8-0-050310 High Spike 50 ppb
5500 50500 500
500 500 5000
50000
5270 52900
321 322 300 3910 25800
96 105 64 64 60 78 52
COO64446 Spk I
COO64446 Sp k J
C0064446 C 0064446 Rep
C0084447 C0064448 C0064449
OKLMN-GW-tPW9-0-050310
O K LM N -G W -PW S-Q -050310
OKLMN-GW-PW9-0-050310 OKLMN-W-PW9-0-05310` OKLMN-GW-PW9-0-050310 DUp OKLMN-GW-PW9-0-50310 Low Spike 5 ppb OKLMN-GW-PW &-.Q-050310High Spike 50 ppb
5500 5O500
500 500 500 5000
50000
5250 53900
315 317 338 4230 24800
95
107
63 63 68 85 50
C0064450 Spk K COO64450 Spk L
COO64450
C0064450 Rep C0064451 C0064452 C0064453
OKLMN-GW-W6102-0-050310 OKLM N-GW-W6102-0-050310 OKLMN43W-W61024)-0503t0 OKLMN-GW-W6102-0-050310 OKLMN-GW:W 6102-0-050310 Dup OKLM N-GW-W6102-0-050310 LowSpike 5 ppb QKLMN-GW-W6102-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5640 53200
424 439 480 5050 32500
103 105 85 88 96 101 65
Not: Sine th is sum m ary tab: sh o w s rounded results, recovery valu e s m ay vary sligh tly from the valu e s In the raw data.
Exygen Research
Page 37 of I10
000060
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table IV. Surrogate Spike Recovery of ,3C PFOA in Water Samples Continued
Exygen ID
Sam ple D e sc rip tio n
1JC -P F O A
= s s = .............. s a a g a t --
Amount Amount
Spiked Recovered Recovery
(n g /L )
(rtfl/L) _ {% ) ...
C0064454 Spk M C0064454 Spk N
C0064454 C0064454 Rep
C0064455 C0064456 CQ064457
O KLM N -G W -W 6104-0-050310 O KLM N-GW -W 6104-0-050310 O KLM N -G W -W 6104-0-050310 O KLM N-G W -W 6104-0-050310 0 KLM N -G W -W 8104-0-050310 Dup O K LM N -G W -W 6104-0-050310 Low Spike 5 ppb O K LM N -G W -W 6 104-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5510 54500
398 417 487 4920 33800
100 108 80 83 97 98 68
C0064458 Spk C COO04458 Spk D
C0064458 C0064458 Rep
C0064459 C00644S0 C0064461
OKLMN-GW -W 6ZC1-0-050310 OKLM N-GW -W 6201-0-050310 OKLM N-GW -W 6201-0-050310 OKLM N-GW -W 6201-0-050310 O KLM N-G W -W 8201-0-050310 Dup OKLM N-GW -W 6201-0-050310 Low Spike 0.5 ppb OKLMN-GW -W 6201-0-050310 High Spike 5 ppb
5500 50500
500 500 500 500 5000
5460 50300
388 391 496 491 5440
99 100 78 78 99 98 109
C0064467 Spk E C0064467 Spk F
C0064467 C 0064467 Rep
C0064468 C0064469 C0064470
OKLMN-GW -W 20-0-050309 OKLM N-GW -W 20-0-050309 OKLMN-GW -W 20-0-05309 OKLMN-GW -W 20-0-050309 OKLMM-GW -W 20-0-05C309 Oup O KLM N -G W-W 20-0-050309 Low Spike 5 ppb OKLW IN-GW -W 20-0-050309 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
4090 46500
272 270 270 3790 26600
74 92 54 54 54 76 53
C0064471 Spk G C0064471 Spk H
COO64471 C0064471 Rep
C0064472 COO64473
COO64474
OKLM N-GW -W 22-0-050309 OKLMN-GW -W 22-0-OS0309 OKLMN-GW -W 22-0-50309 OKLM N-GW -W 22-0-050309 OKLM N-GW -W 22-0-050309 Dup OKLM N-GW -W 22-0-050309 Low Spike 5 ppb OKLM N-GW -W 22-0-050309 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
4380 50700
267 280 255 3830 28800
80 100 53 56 51 77 58
C0064475 Spk l CQ064475 Spk J
C0064475 C0064475 Rep
C0064476 C0064477
O K LM N -G W -W 31-04)50309 O K LM N -G W -W 31-0-050309
O K LM N -G W -W 31-0-050309 OKLM N-GW -W 31-0-050309 O KLM N-G W -W 31-0-060309 Dup O KLM N-G W -W 31-0-050309 High Spike 50 ppb
5500 50600
500 500 500 50000
5410 54200
391 391 371
44100
98 107
78 78 74 88
C0064478 Spk K C0064478 Spk L
C0064478 C0064478 Rep
C0064479 C 0064480 C0064481
OKLMN-GW -W 32-0-0539 OKLMN-GW -W 32-0-050309 OKLMN-GW -W 32-0-D50309 OKLMN-GW -W 3Z-0-050309 OKLM N-GW -W 32-0-050309 Dup OKLMN-GW -W 32-O-050309 Low Spike 5 ppb
OKLMN-GW -W 32-0-0503Q9 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
4840 51000
287 289 328 4750 49000
88 101 57 58 66 95 98
Note: Since this sum m ary table show * rounded results, recovery values m ay vary slightly from the values in the raw data.
'? H, H
Exygen Research
Page 38 o f 110
000061
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table IV. Surrogate Spike Recovery of 13C PFOA in Water Samples Continued
Exygen ID
Sem ple D escription
Amount
S p ik e d
,aC-PTOA Amount
Recovered (ngrt.)
Recovery <%>
C0064482 Spk M C0064482Spk N
C0064482 CQ064482Rep
COO64483 C0064484 C0064485
OKLM N-G W -W 217-0-050309 O KLM N-G W -W 217-0-050309 O KLM N-G W -W 217-0-050309 O KLM N-G W -W 217-0-050309 O KLM N -G W -W 217-0-050309 Dup O K LM N -G W -W 217-0-050309 Low Spike 5 ppb O K LM N -G W -W 217-0-050309 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5410 52500
428 453 468 4850 44700
98 104 86 91 94 97 89
C0064486 Spk O C006446 Spk P
C0064486 C0064486 Rep
C0064487 C0064488 C0064488
OKLMN-GW -W 2008-0-050309. OKLMN-GW -W 2008-0-050309 OKLM N-GW -W 2008-0-0503C9 OKLMM-GW -W 2008-0-050309 OKLM N-GW -W 2008-0-050309 Dup QKLMN-GW -W 2008-0-050309 Low Spike 5 ppb OKLM N-GW -W 2008-0-050309 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5140 52100
318 326 357 6040 37800
93 103 64 65 71 121 76
COO64490 S p k C C0064490 Spk D
C0064490
C0064490 Rep C0064491 C0064492 C0064493
OKLMN-GW -W 2012-0-05Q309 OKLM N-G W -W 2012-0-050309 OKLM N-GW -W 2Q12-0-050309 O KLM N-G W -W 2012-0-050309 O KLM N-GW -W 2012-0-050309 DupiOKLM N-GW -W 2012-0-050309 Low Spike 5 ppb OKLM N-GW -W 2012-0-050309 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5050 50700
344 342 351 5010 37900
92 100 69 66 70 100 76
COO64494 Spk E C0064494 Spk F
C0064494 C0054494 Rep
C0064495 C0064496 C0064497
OKLM N-GW -W 80-0-050309 OKLM N-GW -W 80-0-050309 OKL M N-GW -W 80-0-050309 . O KLM N-G W-W80-0-050309 OKLM N-GW -W 80-0-050309 Dup OKLM N-GW -W 80-0-050309 Low Spike 5 ppb OKLM N-GW -W 80-0-050309 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5650 52400
486 438 502 5410 41700
103 104 97 88 100 108 83
C0064498 Spk G C0064496 Spk H
C0064498 CO064498 Rep
C0064499 C0064500 C0064501
OKLM N-GW -PW 1-0-050310 OKLM N-GW -PW 1-0-050310 O K LM N -G W -PW 1-0-050310 O KLM N -G W 4sW1 -0-50310 ' OKLMN-GW -PW 1-Q-050310 D u p :
OKLM N-GW -PW 1-0-50310 Low Spike 5 ppb O K LM N -G W -PW 1-0-050310 High Spike 50 ppb
5500 50600
500 500 500 5000 60000
5150 53000
331 350 352
4420 41600
94 105 66
70 70 88 83
C0064502 Spk I C0064502 Spk J
C0064502 C0064502 Rep
C0064503 C0064504 C0064505
OKLMN-GW -PW 2-0-O50310 OKLM N-GW -PW 2-0-05C310 O K LM N -G W -PW 2-0-050310 O K LM N -GW -PW 2-0-05C310 . . OKLM N-GW -PW 2-0-050310 Dup OKLM N-GW -PW 2-0-050310 Low Spike 5 ppb OKLM N-GW -PW 2-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5420 52600
440 440 431 4680 34000
99 104 68 88 86 94 68
Note: Sin e s this sum m ary table show s rounded results, recovery values m ay vary slightly from the value In the raw data.
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table IV. Surrogate Spike Recovery of l3C PFOA in Water Samples Continued
Exygen ID
'
Sam ple D e sc rip tio n
Am ount S p ik e d ("9 /U
1>C-PFOA
Am ount Recovered
nsfL)
Recovery <%)
C0084506 Spk K C0064506 Spk L
C0064508 C0064506Rep
C0064S07 C 0064508 C0064509
OKLM N-GW -PW 3-0-050310 OKLM N-GW -PW 3-0-050310 O KLM N-GW -P W 3-0-050310 OKLM N-GW -PW 3-0-050310 OKLM N-GW -PW 3-0-050310 Dup 0 K LM N -G W -PW 3-0-050310 Low Spike 5 ppb O K LM N -G W -P W 3-0-050310 High Spike 50 ppb
C0064510 Spk M C0064510Spk N
C0064510 C00645010 Rep
C0064511 C0064512 CC064513
OKLM N-GW -PW 4-0-050310 OKLM N-GW -PW 4-0-05G310 O K LM N -G W -PW 4-0-050310 O K LM N-GW -PW 4-0-050310
OKLM N-GW -PW 4-0-050310 Dup OKLM N-GW -PW 4-0-050310 Low Spike 5 ppb 0 KLMN-GW -PW 4-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5500 50500
500 500 500 5000 50000
4640 53100
284 275 294 4080 38300
5190 52400
320 324 313 4870 36000
84 105 57 55 59 82 77
94 104 64 65 63 97 76
C0064514 Spk 0 C0064514 Spk P
COO64514 C0064514 Rep
C0064515
C0064516 C0064517
OKLMN-GW -PW 6-O-O50310 OKLM N-GW -PW 6-0-050310 O K LM N -G W -PW 6-0-050310 O K LM N -G W -PW 6-0-050310 O K LM N -G W -PW 6-0-050310 Dup O K L M N -G W -PW 6-0-050310 Low Spike 5 ppb OKLM N-GW -PW 6-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5050 52300
304 311 313 4740 35100
92 104 61 62 63 95 70
C0064518SpkC C0084518 Spk 0
C0064518 C0064518 Rep
C0064519 C0064520 C0064521
O K LM N -G W -PW 10-0-050310 OKLM N-GW -PW 10-0-050310 O KLM N -G W -PW 10-0-050310 O KLM N -G W -PW 10-0-050310 O K LM N -G W -PW 10-0-050310 Dup OKLM N-GW -PW 10-0-050310 Low Spike 5 ppb O K LM N -G W -P W 10-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
3870 48500
255 249 258 2980 34100
67 96 51 50 52 60 68
C0064522 Spk E C0064522 Spk F
C0064522
C0064522 Rep C0064523 C0064524 C0064525
O KLM N -G W -PW 11-0-050310 O K LM N -G W -PW 11-0-050310 O K LM N -G W -PW 11-0-050310 O K LM N -G W -PW 11-0-050310 O KLM N -G W -PW 11-0-050310 Dup O K LM N -G W -PW 11-0-050310 Low Spike 5 ppb OKLMN-GW -PW 11-0-05031Q High Spike 50 ppb
5500 50500
500 500 500 5000 50000
C0064526 Spk 6 C0064526 Spk H
C0064526 C0064526 Rep
C0064527 C0064528 C0064529
OKLMN-SW -O-05310 OKLMN-SW -O-050310 OKLMN-SW -O-050310 OKLMN-SW -0-050310 OKLM N-SW -0-050310 Dup OKLMN-SW -O-050310 Low Spike 5 ppb OKLM N-SW -0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5180 51600
319 347 312 4400 36000
5270 52000
124 132 505 5320 41200
94 102 64 69 62 58 72
96 103 25 26 101 106 82
Note: Sine# this summary table hows rounded result, recovery valoss may vary slightly from the values In the raw data.
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Interim Report #1 -Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table IV.
Exygen ID
Surrogate Spike Recovery of 13C PFOA in Water Samples
Continued
1*C*PFOA
Sam ple Description
Amount Amount
Spiked Recovered Recovery
(ng/L)
fnoyy
(%)
C006453 C0064531 C0064532
O KIM N -G W -TRIP2-0-050310
500
OKLMN-GW-TRIP2-0-050310 Low Spike 5 ppb 5000
OKLMN-GW-TRIP2-0-050310 High Spike 50 ppb 50000
494 5520 52900
99 110 106
Avorage: 83 Standard Deviation: 21
Note: S in c e th is su m m ary table sh o w s rounded results, recovery v alu e s m ay v ary slig h tly from the valu e s In the raw data.
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Interim Report #1 -Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
FIGURES
Exygen Research
Page 42 of 110
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Interim Report #1-Analysts of Oakdale Water Samples
Exygen Study No.: P0001400
Figure 1. Typical Calibration Curve for PFOA in Reagent Water
I 03MQ6C firour^ H&Mr tovlsib (PFCMSt 'Um * ' ffc jiw io rtO
* !J6**0C3* *7.3**004 (r* O ^M I)
Area, tounts
0 0 ;,
Exygen Research
Page 43 of 110
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P 0001400
Figure 2. Extracted Standards of PFOA in Reagent Water, 25 ng/L and 50 ng/L, Respectively
X C032TttW - PFOA (Sfrtrdtni)
1 c f 41 ttm * Q224QQC.wiW
A r t* 4 4 H 7 ootNTtt
$033,636 c p * KT: 114 4 6 m in
11.84
XCD321PM P f O A ^U ndart) 1T3V3WD v n u sanpl 3 f 41 n o n C32405C^iff A u : 7*29$ oaufts ritigM: 12793.?1U eps RT: IlK n t n
11.84
Exygen Research
>;*' ?'! Si 5| 4
Page 44 of HO
000067
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 3, PFOA in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
Ann. 97$$
'P F O A (U rtt* to w n )4 \3 6 f3 6 3 fi i w m p i+ V o f t l 9 9 4 * 2 2 o p i R7: M.&4S m in
C
*
V c 3
fteapent S p k A - J>POA(OC>4I9J)/069.S mu- u m p k tOof 41 fram 0324KC.aM A m : W W < w Ha*ht: 19075.481 opa R L l1 J 1 t n * >
Note: A linear lot o f PFOA was used to calibrate the instrument. The two peaks shown in Figure 4 are due to different isomers present in environmental samples. The area counts for all isomers present are included to report one total PFOA value.
Exygen Research
Page 45 of 110
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 4.
Chromatogram Representing an Oakdale Water Sample Analyzed for PFOA, DF=100 (Exygen ID: C0064522, Data Set: 032405CR)
C00*462? -PFOAWthitaHHi4t2JH$G9.P
ofS7from03t406CB.^W
Ap m :
H itg h t 7fG G 1& 49t>fl* BT: i1 2 Q m fn
11.82
In tsfiflfy , c p s
Exygen Research
Page46 of II0
000069
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 5. Typical Calibration Curve for 13C PFOA In Reagent Water (PCPF0^"UnMT,'R*MfeAC1trm&tmfryUlnOB*-Ci**frft.WU)
Arsa, counts
Exygen Research
Page 47 of 110
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Interim Report #1 -Analysis o f Oakdale Water Samples
Exygen Study No.: P00I40O
Figure 6. Extracted Standards of 13C PFOA In Reagent Water, 25 ng/L and 50 ng/L, Respectively
I
Ar+:XC32*05-f S 3 tOff
1JC cuN
rPfP* CA{Si9n5d33aSi}.4f1135^.Wfl3*7R0.t0:llJ36Cmim
2
from<3324OtSCMW
<5000-<
11.86
4000
intensity, cps
3000
2000
1000
i2 3
40
6788
Tim*, mm
XCS 1 0 4 -2 '13C F F0A CmsnO 41*JX37&.0 amu samp** 3 of 41 fmm o a jW C w f f Aa: 88017 ooums Htifll*: 11438.486 cp* RT; !1<848
10
H
12 13 14 10 10 17
11*5
lntenSty.eps
Exygen Research
Page 48 of 110
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 7. 13C PFOA in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
I fre#ge*?Cav4roJ f3C P F O A (Vfrhtmwn} 4t9.0f376fi m u A n : Z1 f otumi Hwttrt 96.664 co 67: lf A 3 4 m i
9 of44 hvrt 63t409C.mtr
3*s
I R n oM SpfcA- 13C PrOA(QQ419JV3M.Pmu-ssn|)tt lO of 41 fnm 832&Cjj11 Wght: 1 M 7 3 o p < RT: H-S23rr*t
1006
<ft Qu . SflO4
5 6 7 9 Q 10 11 12 13 14- 15 10 17 Tim, rmrv
I ftaGMt pk a - 13C PFaA(QC) 4t$JV3700 wnu - Kampfe 116f 41 t W 0324D6CjuN1 A ti; 128964 ooww* M ehC 2038*1 ,018cp* RT; 11,843 mir
2 .0 * 6 1 wa..
to* TSCa>
8 0 10 11 12 13 14 16 16 Tim *, min
V ttO>O5-., <J }k
Exygen Research
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 8. Chromatogram Representing an Oakdale Water Sample Analyzed for 13C PFOA (Exygen ID: C0064522, Data Set: 032405C)
15 0C0064032 C P P O (UakJH3mr}4l5f370 m o . tnpJ*2 3 1*41 from 022406C.uW
Aro*; ocv.rH41*903
# 7 f f .059 mi
11A3
Intensity, cp s
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Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Figure 9. Typical Calibration Curve for PFBS in Reagent Water
034MCR a w i < UftW jtfe (PFMft "Una** t y m t o O ^ w gonq): t 138 n t& tw r Cr tA9$T)
Are, counts
Exygen Research
Page 51 of 110
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Interini Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 10. Extracted Standards of PFBS in Reagent Water, 25 ng/L and 50 ng/L, Respectively
XC 04M 03* 1 . PFBS tS ti* fr n i) 2 9 9 M 9 9 .0 pentf -
2 o f t 7 WflT
4 $ i i oow/its H t ^ h t } i) 6 3 4 c & * RT: 3J907 <jtni
3.91
.irff
I *Cft4M I4 - r r a s (ftandart) ISB-DdO-O rmt - sm p k 3 of 07 Own QiJMOdCA wff
A u;7727coM r
tp* ftT:34$4ffii
39
Ihn, min
Exygen Research
y*'; < .. " -j i: t
Page 52 of 110
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interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 11. PFBS in Reagent Water, SOng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
fio n g tn i Con to ) - P F B S fiJnhno*m ) 399& f99. 0nnM<jn a ftthtd)
front O Si4O O Cfi.m 0
Intensity, cp s
Intensity, cp s
Intensity, cp s
omt*MA w ; -H192
Ha)*; 12M .94I apt RT: 3.917 min
Time, r&ift
* " ^ * 0 O *'&/ &
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Interim Report #1-Anaiysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 12. Chromatogram Representing an Oakdale Water Sample Analyzed for PFBS, DF=100 (Exygen ID: C0064522, Data Set: 032405CR)
C0064622 -PFSS (U lthrrotm ) 2 9 9 0 8 9 .0
* Mmpj SS QfG7 frAt 0324WSCX.MfT
f : 7 7 oow r#f H e ig h t i f <5.406 R T :3 .9 2 4 m ln
3*2
intensity, cps
Exygen Research
Page 54 of 110
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IhterimReport#!-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 13. Typical Calibration Curve for PFHS in Reagent Water
(found ttb rtr
KSX 'U nw r' Regression fx* wi^hthg); y s h t 04)0101 $ CJ#M )
At, counts
Exygen Research
Page 55 of 110
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Interim Report #1 -Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 14. Extracted Standards of PFHS in Reagent Water, 25 ng/L and 50 ng/L, Respectively
* C 0 3 f 0 S - f - PFHS(Stamtwr)3 $9 .0 f9 0 .0 srrtu w n p to 2 of4 * I r a n fcL?4 0 S C j* rff
An*: 1
c o tffffr Hltybt 1 4 6 9 .7 4 7 cp* RT: 10 .6 2 6 nwrr
10.62
Exygen Research
h'
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 15. PFHS in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
ftf(rtspoMftf fCtoo#tr/bimeorfPjFHS
3 9 $ .o a O G *m t n m p f 9 of 4 f from
Intensity, cps
intensity, c p s
I n o f M t S*< A PfWS
amu *arfa 10 r t 4H m m B ttttS C .ttff
A m : 3 4 1 * eountc Hai|ht : 422.193 op* RT: 10.5*4 m b
3000
2000
1000' 0
9
I A M 0M spk ' ?rHS (QQ399.IMB0. a m i- 5
fl * 4 1 from W?405Crf1
A f c r . t t t o W u u t r W a tf ;3 *7 7 A lM o w AT: 1C.8Mmi
1 0 ,1 9 ^
9 10 Tim *, mtft
10.61
?4'
1-0*4'
0-0 i ---------- 1----------.----------- 1............................. .
~i r
12
3 4' 3 6 7 8
TInh , n iti
14 16 16 17
Intensity, c p s
Exygen Research
0 - / / 'i t'i s i * \ * ' v *
Page 57 o f 110
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No,: P0001400
Figure 16. Chromatogram Representing an Oakdale Water Sample Analyzed for PFHS, DF=100 (Exygen ID: C0064522, Data Set: 032405CR)
CW64S22 -
(Uh m o m r)3 2 9 X>W tra - m ai* 39 < /6 7 fh u ir Q32405CS.wUT
* ^ 3 7 ^0 9 *1 ^
3 9 3 9 5 9 6 cp s ST:
2900-
2900 -
2*0022002000-
1900-
10-39
tu
e 1200-
1000' 900-
4CO200-
0
i
32 4 O B 7 9 Q 10 11 12 13 14 15 19 17
Tim *, mir
Exygen Research
Page 58 of 110
o o o o ls i
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 17. Typical Calibration Curve for PFOS in Reagent Water
Area, count
**
.. * a :
Exygen Research
Page 59 of 110
OOOOSH
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 18. Extracted Standards of PFOS in Reagent Water, 25 ng/L and 50 ng/L, Respectively
XC $3?f05-f -f*FO$ fStaArd}'4G4j0&0J j* w
2 <X4i fro*r$32406C .i*/y
Hiq)rt 1B9Q.120cpc ,97: 12438 rnt*
12m
Exygen Research
<* ( s ji
'
Page 60 o f 110
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 19. PFOS in Reagent Water, SO ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
I f h H y ir 1 C&wpf. A P Q S flJAkn*>H*r) 48B.aOO.O mar - 9 **y ji+ 9 o f4 t
r+s; tO *46cow fe
AT; fi.8 1 0 mi*
Q 3}40C *uff
12.62
intensity, cp s
intensity, cpe
Am : 180532tftts
Jt.t373cps RT: t i m * m
12*1
Intensity, c p *
Exygen Research
Page 61 of 110
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No;: P0001400
Figure 20. Chromatogram Representing an Oakdale Water Sample Analyzed for PFOS, DF^lOO (Exygen ID: C0064522, Data Set: 032405CR)
C0A0f&tA:S1252C7P&F9OS 0 G43324*qo 87:12.133*6 Of*7
8000
9900
CO
4600-
4000-
390030002900
20001900-
tOOO-
900
0` " t ' I
1 I..... ....T ' l----- " 1 !"'
I
i
1 2 3 -5 5 6 7 9 0 1 0
Tim , min
12.14
12-00
10 1?11 12 13 14 15
Intensiv, cps
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Intrim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P000I400
APPENDIX A
Study Protocol P0001400
(Exygen Study No. P0001400) with Analytical Method: V0001780:"Method of
Analysis for the Determination of Perfluorooctanoic Acid (PFOA) in Water
by LC/MS/MS"
Exygen Research
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