Document dnD95nN5pYOpY3RJqjp2VQv1q
AR226-3642
INTERIM REPORT #1 Analysis o f Oakdale W ater Samples
STUDY TITLE Analysis of 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
DATA REQUIREMENTS EPA TSCA Good Laboratory Practice Standards 40 CFR 792
STUDY DIRECTOR Jaisimba 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 s Phone:814-272-1039
STUDY SPONSOR 3M Company
3M Building 0236-01-B-10 St. Paul, MN 55144 Phone: 651-733-6374
PROJECT Protocol Number: P0001400 Exygen Study Number: P0001400
Total Pages: 110
P \ 000024
Interini Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT
Exygen Study Number P0001400, entitled "Analysis o f Perfluorooctanoic Acid (PFOA), Perfiuorobutanesulfonate (PFBS), Perfluorohexanesulfonate (PFHS), and Perfluorooctanesulfonate (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.
Exygen Research
Study Director Weston Solutions, Inc.
Robert A. Paschke Sponsor Representative 3M Company
Exygen Research
//?M Date
%?/gr
Date
o / I|gts
Date
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DUALITY 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 Perfluorooctanesulfcmate (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 were reported to the Exygen Principal Investigator and Management and to the Study Director,
Phase
Date Inspected
Date Reported to Date Reported to
Principal
Exygen Date Reported to
Investigator Management Study Director
1. Protocol Review
03/24/05
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
a s i n n s Date
`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 P0001400, 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:
Date
Exygen Research Facility Management
Richard A President Exygen Research
Study Director, Weston Solutions, Inc.
Jaisimha Kesari P.E., DEE Weston Solutions, Inc.
Sponsor Representative, 3M Company:
r^J lS L
Robert A. Paschke Manager, 3M Corporate Environmental Programs
Exygen Research
Date
oloils
Date Page 4 of 110 00002V
Interim Report #1 -Analysis o f Oakdale Water Samples
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-I 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 42-02-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 of 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
Exygen Research
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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............................................................... 20
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Table I.
LIST OF TABLES
Page
Summary ofPFBS, PFHS, PFOS and PFOA in Water Samples........................................................................ ......... ........................... 22
Table IL Matrix Spike Recovery ofPFBS and PFHS in Water Samples.................. ...24
Table DDL Matrix Spike Recovery of PFOS and PFOA in Water Samples.................... 30
Table IV. Surrogate Spike Recovery of UC 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 o f 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 ED: C0064522, Data Set: 032405CR).........................................................................................46
Figure 5. Typical Calibration Curve for l3C PFOA in Reagent W ater.......................... 47
Figure 6. Extracted Standards o f 13C PFOA in Reagent Water, 25 ng/L and 50 ng/L, Respectively............. ................... ................. ................... ..........48
Figure 7. t3C 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 of 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: 032405C R ).................
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 ED: 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 of 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 perflnorooctanoic acid (PFOA), perfluorobutanesulfonate (PFBS), perfluorohexanesulfonate (PFMS), and perfluorooctanesulfonate (PFOS) according to Exygen Method V001780 (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 of 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% 19, 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, l3CPFOA, in water samples was 83% 21.
2.0 OBJECTIVE
The objective of the analytical part o f 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, C0064467-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-in 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, ,3C 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
l3C P F O A PFBS PFHS PFOS
Exvsen Inventofv-No.. SP0003800 SP0004184 SP0000252 SP0002401 , SP0002694
Lot# 23116HB 3507-195
101 SE036 430180-1
Purity (%,) 97.64 97 96.7 98.6 101.2
Expiration Date 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:
13C PFOA Chemical Name: 1,2-13C perfluorooctanoic acid Molecular Weight: 416 Transition Monitored: 415-370 Structure:
PFBS Chemical Name: Perfluorobutanesulfonate Molecular Weight: 338 supplied as the potassium salt (CiFSCb'K^ 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 (CeFuSOTC^) Transitions Monitored: 399 - 80 Structure:
FF FFF
PFOS Chemical Name: Periluorooctanesulfonate Molecular Weight: 538 supplied as die potassium salt (CsFnSOaTC*) Transitions Monitored: 499 --80 Structure:
F FF F
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 C8 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, 13C 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 o f 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 of 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
(ng/mL)1
<HL)
(xnL)
00
40
10 100
40
10 200
40
10 400
40
100 100
40
100 200
40
100 400
40
13c1o f PFOA, 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 o f 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 o f 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: API4000 Biomolecular Mass Analyzer
Interface: Turbo Ion Spray Liquid Introduction Interface
Computo': DELL OptiPlex GX400
Software: Windows NT, Analyst 1.4.1
HPLC:
Hewlett Packard (HP) Series 1100 HP Quat Pump 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 mM 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: 0.3mL/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
/mini ~12 min. ~12 min. ~12 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 of 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.
Equation 2:
Recovery (%) =
/analyte found ine/L) - analyte in control ing/Lft xl00% amount added (ng/L)
An example of a calculation using an actual sample and results from the PFOA analysis
follows:
Water sample Exygen ID CG064432 Spk F (Set: 032105BR), fortified at 50000 ng/L
with PFOA where:
peak area
1170161
intercept
= 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) = fl 170161 -262001 x 100 1330
From equation 2: % Recovery
86012 ng/L*
(86012 n e /L - 37600 ng/L) 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, PFHS, 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 dupEcate 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 13C PFOA was added. The additional 13C 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 of the normal acceptance range o f 70-130%. Because laboratory control spikes for l3C PFOA were acceptable in every set, instrument washes were free o f 13C PFOA, at least one l3C 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 o f 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 of PFOA, PFBS, PFHS and PFOS in water samples were 93% 19, 141 % 2 1 , 96% 1 5 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 of 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 DATAAND 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 the 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
Exygtn ID
C0064404 C0064404 Rep
C0064405
Client Sample ID
OKLMN-GW-W3-0-050310 OKLMN-GW-W34WJ50310' QKLMN-GW-W3-0-050310 Oup
Samples
Analyte Found (ppt, ngfL) C4 Sulfonate PFBS C8 Sulfonate PFHS C8 Solforai PfOS
312 162 4750 298 160 3350 303 159 3190
Cft Add PFOA
6330 6220 5990
C0064408
OKLMN-GW-W8-04>50310
57.0
ND
59.0
290
C00644408 Rep
OKLMN-GW-W8-O-0S031O*
63.8
ND
55.7
275
C0064409
OKLMN-GW-W8-0-050310 Dup
60.1
ND
56.3
284
C0064412 C0064412 Rep
C0064413
OKLMN-GW-W264WJ50310 OKLMN-GW-W26-0-050310* OKLMN-GW-W26-0-050310 Dup
73400 75700 71400
222000 244000 214000
13500000 14400000 12200000
79300000 70200000 71800000
C0064418 C0064416Rep
C0064417
OKLMN-GW -W 334M 50310 OKLMN-GW-W33-OO60310* OKLMN-GW-W33-04K0310 Dup
26800 23800 25500
92300 84600 81600
4810000
4870000 4540000
1750000 2020000 2790000
CQ064420 C0064420 Rep
C0064421
OKLMN.GW-W205-<M)S0310 OKIMN-GW-W205O-0S0310* OKLMN-GW-W205-0-050310 Dup
8260 8500 7850
6740 6610 7070
146000 119000 116000
147000 150000 158000
C0084424 C0064424 Rep
C0064425
OKLMN-GW-W215-0-050310
OKLhW-GW-W215-0-050310* OKLMN-GW-W2154FO5031O Dup
801 81.2 75.8
769
37100
4400
256
27000 .
3510
270
36900
4070
CQ064426
0KLMN-GW-W2010-0-050310
ND
ND
ND
NQ
C0064429 Rep OKLMN-GW-W2010-0-050310*
ND
ND
ND
ND
C0064429
OKLMN-GW-W2010-0-050310 Dup
ND
ND
ND
ND
C0064432 C0064432 Rep
C0064433
OKLMN-GW-PW7434350310 OKLMN-GW-PW74M3503W OKLMN-GVV-PW7-0-05031Q Dup
4460 4340 4630
4800 5080 5080
71600 67800 72400
37600 38400 36200
C0064436
OKLMN-GW-TRIP1 -0-050310
ND
ND
ND
ND
C0064442 C0064442 Rep
C0064443
OKLMN-GW-PW8-0-050310 OKLMN-GW-FW8-0-050310* OKLMN-GW-PW8-0-05CG10 Dup
13300 14100 14100
23800 23900 23000
34300 35600 33400
81400 60600 58500
C0064446 C0064446 Rep
C0064447
OKLMN-GW-PW9-<M)50310 OKLMN-GW-PW94M)50310* OKLMN-GW-PW9-0-050310 Dup
2110 2140 1930
6160 500C 5140
84400 84900 88600
49000 48700 49600
CC064450
CQ064450 Rep C00644S1
OKLMN-GW.W6102-O435031O
OKLMN-GW-W6102-0-050310* OKU1N-GW-W61Q2-0-050310 Dup
NQ
53.5 NQ
ND
ND ND
NQ 214
NQ 228 ND 227
C0064454
C00644S4 Rep C0064455
OKLMN-GW-W61D4-0-050310
OKLMN-GW-WB104-0-050310* OKLMN-GW-W6104-0-050310 Dup
NQ
NO 51.2
ND
ND ND
109 207
125 189 118 184
C0064458 C0064458 Rep
C0064459
OKLMN-GW-W6201-0-050310 OKLMN-GW-W6201 -0-050310* OKLMN-GW-WB201-0-050310 Dup
74.0 74.1 78.0
ND ND ND
NQ 95.5 ND 88.3 NQ 132
C0O64467 C0064487 Rap
C064488
C0064471 C0064471 Rep
C0064472
OKLMN-GW-W20-0-050309 OKLMN-GW-W20-0-050309* OKLMN43W-W2043-050309 Dup
OKLMN-GW-W22-0-050309 OKLMN-GW-W22-0-050309* OKLMN-GW-W22434350309 Dup
13900 10700 10000
36600 32200 37500
12900 9040 7660
31400 29600 25700
46600 36300 30100
45800 34000 28100
285000 243000 190000
317000 301000 244000
'Lab oratory D uplicate ND = Not detected et or above 26 ngfl_. NO s Mot quantifiable = M easured concantratfon between 25 ng/L and the Lim it of
QuantttaBcn (LO Q ) which w So n jfL .
Exygen Research
Page 22 o f 110
000045
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table I.
Exyo#M D
Summary of PFBS, PFHS, PFOS and PFOA in Water
C lient Sem ple IS
Samples Continued
Analyts Found fppt, ng/U C4 Sulfonat PFBS ce Sutfonst* PFHS C8 Suttonat PFOS
CS Ackf PFOA
C0064475 C0064475 Reo
C0064476
OKLMN-GW-W31-0-050309
OKLMN-GW-W31-CW50309* OKIMN-3W-W31-0-050309 Dup
1300 1360 1360
5130 4780 5190
132000 132000 156000
23100 22300 24900
C0064478 C0064478 Rep
C0064479
OKLMN-GW-W324MS0309 OKLMN-GW-W32-0050309* OKLMN-GW-W32-0-050309 D ip
2180 2290 2960
3000 3120 2940
47100 44400 83000
117000 93300 125000
C0064462 C0064482 Rep
C0064483
OKLMN-GW-W217-0-050309 OKLMN-GW-W217-0-050309* OKLMN-GW-W217-0-050309 Dup
ND NO - ND
NO ND ND
NQ NQ 128
NQ NQ NQ
C0064486 C0064486 Rep
C0Q64487
OKLMN-GW-W20084KI50309 OKLMN-GW-W20O5-0-050309*
CKLMN-GVV-W20084V050309 Dup
6780 7170 ' 6930
10100 10800 10300
15500 17800 18800
59300 58700 60300
C0064490 CC0644S0Rep
C0064491
OKLMN-GW-W2012-0-050309 OKLMN-GW-W2012-0-050309* QKLMN-GW-W2O12-O-O5O3O0 Dup
2210 1960 1920
4700
4470 4420
117000 118000 139000
48900 46400 51400
00084494 C0064494 Rep
C008449S
OKLMM-GW-W80-0-050339 OKIMN-GW-W80-0-050309* OKIMN-GW-W80-0-050309 D ip
ND ND ND
ND ND
ND
ND 302 ND 280 NO 328
00064498 C0064496 Rep
C00644B9
OKLMN-GW-PYV1-0-050310 OKLMN-GW-PW1-0-050310* 0K LW N J3W -PW 1-0-050310O 4)
5620 5650 5560
4180 4150 4170
66900 71600 70900
37300 39300 39100
C0084502
OKLMN-GW-PW2-0-Q60310
641
501
351 3630
C0064502 Rep
OKLMN-GW-PW2-0-050310*
624
491. 383 3890
C0064503
OKLMN-GW-PW2-0O50310 Dup
894
700
303 5160
00064800 C0C645O8 Rep
C0064507
OKLMN-GW-PW3-0-050310 OKLMN-GW-PW3-0-050310* : OKLMN-GW-PW3-0-050310 D tp
6970 6740 6570 '
10000 - 9740
9990
32700 25500 32300
177000 160000 176000
00064510 C0064510Rep
C0064S11
OKLMN-GW-PW4-0-050310 OKLMN-GW-PW4-0-050310* OKLMN-GW-PW4-0-0SO310 Dup .
8130 7700 7810
7890 7480 7550
33800 30300 27800
72100 67800 65900
00064514 C0064514Rep
00064515
C0064518 C 0064518R sp
C0064519
OKLMN-GW-PW3-0-050310 OKLMN-GW-PW8-0-050310* . OKLMN-GW-PW6-0-050310 Dup ':
OKLMN-GW-PW10-0-050010 OKLMN-GW-PW10-0-050310* . OKLMN-GW-PW10-0060310 Due
7930 8000 8130
13100 12700 11900
14500 14600 14600
29200 27400 26800
90000 86000 66400
1400000 1700000 1740000
78400 78700 78500
719000 781000 814000
CO064522 CQQ64522 Rep
C0064523
OKLMN-GW-PW11-0-050310
OKLMN-GW-PW11-0050310*; OKLMN-GW-PW11-0-050310 Dup
6520 6490 7150
.. <
8820 10000 9050
40800 50600 43400
60300 71600 60600
C0064526 C0064528 Rep
C0064527
OKLMN-SW-0-050310 OKLMN-SW-0-060310* : : OKLMN-SW-0-050310 Dup i-V
NQ NQ . NQ
NQ
NQ NQ
1190 1200 1270
491 529 537
C0064530
OKLMN-GW-TRIP2-0-050310
ND
ND
ND
ND
'Laboratory Duplicate NO = Not detectad at or above 25 njyL.
NQ * Not quantifiable = M easured concentration between 25 ng/L and trie Limit erf
Quantitation (LOO ) which is 50 ng/L
Exygen Research
Page 23 of 110
000046
Interim Report #1-Analysts o f Oakdale Water Samples
Exygen Study No.: P0001400
Table H. Matrix Spike Recovery of PFBS and PFHS in Water Samples
S a m p l*
Oaacrtpdoi
C * SuKaM ta PFBS Amount Amt Found Amount S p lk *d InSwnpi Rtcovtrtti Recovery
(%)
Amount Splkad
MJ
C * Sutton* PFHS
Amt Found Amount
fnSorapl* R*ccv*r*d Rneuvnry
fnflft.)
(0*4
t%)
O KLM N -O W .W O -tW IW lO <CM *M M 3pfcC,0ngfl-W b9p*a>
OKU*N<GW-W9-0-06tt10
ICM W W I* 0 .90M0 itg /LLab Spike)
O KLM N -G W -W 3--05C3fO tow S tfik a 5 p pb <000*449*.* m ntft held Spike )
OKLMN-GW-W3~0-W10 H ig h S p ilt* 50 ppb (COMeeer. MM)n^Ln e ts Spike >
5000 50000 5000 50000
312 312 312 312
6960 87400 7450 74700
133 5000 134 50000 143 500C 149 50000
102 162 162 162
5130 47500 5140 54400
99
SS
100 106
O K W W H JW -W I-0-050310
(CtMM440f Spfc , 9400 aqA . L a * Spike}
O K LM N-QW-W8-0-4WW 1 & [COOiMfia 3 |*F .flM M 4.La * Spike! OKUWM3WMW-04903ia LOWSplk* 5 ppb
(co rn u to . 5oe ng*.Frausp it > OXLJdW3W-WB-0-6S031&Nfflh Splk* 60ppb
fC00*M U , 0 W npl FtoUSpille )
OKUffN45W-W2*4<O$O310
{G00M412 S *k 0 , SOOOnpC U k 8pHw)
O K U *N -G W -W -tM )W 10 (COOM412 Spfc H, 90000 n * L U b SpttaJ
OKU4HKJW-WWLO-060310L ow Splk ppb JCMM414.tiMO ryp/LFieldS p ila )
O K LM N *3W 'W 28-# -M 0310 H ig h S p lk * SO ppb (CMB4419, BOOOtin*n. FMd Sp ira )
5000 59000 5000 50000
5000 50000 5000 50000
57.0 57.0 57.0 67.0
73400 73400 73400 73400
7020 70000 7410 70500
73100 125000 79200 147000
138 5000 146 50000 147 500C 141 50000
ND
HD ND ND
* 5000 222000 103 50000 222000 . 5000 222000 147 50000 222000
5120 51400 5610 53300
207000 252000 210000 266000
102 103 110 107
*
O KU AN -G W ^ W 33-0-0M 1D (C W II1 I ftp * i, 9000ffp L Leb Spike)
QKLMN-GW-W33-0-050310
(OOOSMII Spk J . SO n p i. Lab Spike}
O KLM N -G W -W 13-04)6031Q Low Splk* 5 ppb
<004*4411. see* a p t Fld d S^ Ira )
O K IJyiN -G V V < W 4M )B 03l6 H lp h Split* ED ppb (C606M 1*, MOO*ngfLField SpHra )
5000 50000 5000 50000
28600 29800 20800 26800
33000
133000 38700 106000
5000 82300 212 50000 82300
- 500C 82300 162 50000 82300
78000 122000 65200 150000
59
115
0KU4N-W *W 2 0 W )-0 3 i D
(COOM430 B j* K . 5000 n p L Lab S p it* )
O KUM N-QW -W 20*4W )6310
(000*4429 Spk L , 90000 n fl. la b S p in )
O K LM N *G W -W 20B^ M )510 LOW Splk S ppb
(CDoeeeaa. u m nql r u t *fk >
Q KLM H 43W -W 2064M J5C310 M g h Spit* 60 ppb
{cooeeeas, so w o p i. n *ie S p i* >
5000 50000
5000
60000
8200 8260 S26A 8260
15400 72500 15200 82600
143 5000 740 126 50000 740
130 soon 740
149 50000 6740
12500 53100
11 BOO
60600
115 93 101 106
0 K LK N > S W -W 3 1 W 4 )5 0 3 M (C90M41490fc M, WOO n p L le b SpOra )
O KU A N -S W -W 2tt-0-06010 |C M *44SpkN ,M 0M np> LLab S p iU )
0KLM*M3WW21W-0W1Low Splk 6 ppb
(C0M442, 5 K npiL Field Satira >
O KLR W W SW 4V 21M -D C 310 H ig h Splk* 60 ppb
(CeeeeAZF,SU M &L Ftek* S p i )
5000 50000 5000,. 50000
601.0 801.0 801.0
dO t.O
7200 67200 072 86000
126 5000 133 50000 118 5000 132 50000
760 799 769 709
5280 9D300 5240 48500
90 99 89
96
reafctue exceeds Ihe spiking lev) N pnlfcany; Iheretote, an accurst recovery value cannot be calculated
h o Notdetected at or above 25 npA. (ppt)NO - Notquarfiabl* M easured concentration between 2$ rg& (ispt) and d ie Lim it of
Quantitation (LO Q ) which is 50 ng/L <ppt>N ot*: S in t* th is uinm ary a b le sn o w * rounded r u u iU , recovery y a k may v a ry ilg M iy
from the v a lu e * in the raw data.
Exygen Research
Page 24 of 110
000047
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
Senspk Deecriotton
C4 StiNFoM inPFBS
CSSulfonete PFHS
Amount Amt Found Amount
Amount Affit Found Amount
Spiked InSemple Recovered Recovery Spiked bSample Recovered Recovery
OH#. (<"->
m tfu
(%> ma-)
894
w
OKLMN-GW*W2C1MW80310 (Coo*M2oSekC.ieoeAaB-ue 9&uw)
OKJJHIN-GW-W2010-^OSO310 (Caoeeeaa $* o, swo# r^uab Sptte)
OKUW-GW-W201O-0-0SW1DU w Sptk* S ppb (CM*443*.300# HgA.HeWSpU J
OKLMN-GW-W2D1M-06M10 Kfflfl Spfc SOppb iceeea. eeeoo fmuSette >
5000 50000 5000 50000
NP ND NO NO
6500 68500 6700 63600
132 5000 138 50000 134 5000 12B 50000
NO NQ NQ NO
4600 48700 4700 43700
86 97 94 87
OKU*M43W-PW74WMiai0 feoeM32apeUOOCn^LU*3pw |
OKLMIH3W-PW7-M5O310 (CM044S2Spftf. fOOMngAiteb Sp&e)
OKLMN<rW4W7-C-OSOai0 LowSplke 6 ppb (00*14*4.SaOOnpLFMMSette I
OW-MN-3W*PWr43^WW10 High Sette se ppb lCoeem,*eooi) ngn.nieSpntel
QKL14N-GW-TOP1-0-010210 Uw Spile* ft pph <C0H44*7,eeoepgA. HeieSpftu)
QKLMN-GW-TRIP1-CMIM310High Spike SOppb jcoeauat,fono* ngrt. Rei*spo }
000 50000 sa 50000
5000 50000
4400 4450 4400 4400
NO NO
12200 72800 13200 60000
6540 44400
156 5000 4600 137 50000 4600 175 5000 * 151 50000 4600
131 5000
NO
88 XX ND
8310 50800 0370 59000
4500 46100
90 62 91 106
92 92
0KUS*6W *W S44niO <Ceo4442Sek6. SOMnpL LebStSke>
OKUIN*GW*W**0#0310 (COOM4429p* H.KMNMrtlLLa*Bette)
OKLMN-GW-PWS-0-05W10 U w SpHtsS ppb (C0OM44.saoen*LFleMSpila >
OKUWWW-PW8*PO5031CHigh Splk* 00 ppb (CC0I444S.SCOOOnoB.FbWSette |
9000 GOOOO 5000 50000
13300 13300 13300 13300
21400 70700 21000 80700
162 5000 23800 133 50000 23800 154 5000 23600 135 50000 13800
28700 70300 30000 78100
118 83 124 105
OKUNM'GWMW'O-osam tcoeeu*# 8tt I, SOMngA. Ltb S?Um)
OKU*N43W4WMMIHUia (Cmewe S|M4. oeoene^LLe*Sette)
OKLMN-GW-PWt-0-d*W10 Low SpQt#Sppb (Ceeeeeee,eoenpLneteScue )
OKtMN-OWHWO-OBOSIOHigh Splke SOppb <000*444*,MPQQnglt FWdSpbe>
5000 50000 5000 5QC00
2110 2110 2110 2110
0280 66900 8280 74900
144 5000 5160 134 50000 6160 144 5000 5160 146 50000 5150
9310 64400 8350 64800
83 98 64 90
0K1JMN-GW4**1IK<4MMH16 1COOO4BSftt K.BOOOneA.Ub atte >
OKLMN-OW-WS102-0-0501* (Cooeetiositel.aoeoene*,ut apike)
OKLMN43W>WC102-aOOOMOLow SpHu 0 ppb {CQObUCLSOMQA.FieMfSfM |
OKLMN-GW-W102-O-0S0310 High Splke 90 ppb (000*4493,*0000 eglLFleid Botte |
5000 50000 5000 50000
NQ NQ NQ NQ
7360 7500 7120 70700 :
147 135 <42 (41
5000 50000 5000 50000
ND ND ND ND
4890 47400 5040 50600
96 96 101 101
'Sample reedueweeds (hepifclnQtevelgnffleanty;thereof, an accuraterecoveryvalue cannotbe ceteiiated NO * Notdetectit orabove25 nglL {ppi). NQ 3 Not QuottftsOte = M easures ooncemraflon between 25 ngA. (ppQ and fte U srtt of
Quanttattofj{LOQ1whichI50mjA. (ppt).
N ote: S in ce itila a u irw ie ry tab le show rounded re su lts, reco very va lu e* m ay va ry v p itiy
fro m d ie wetuae In th e rtm data.
Exygen Research
Page 25 of 110
00004S
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
templa Daacrlpdon
G4Sulfonate f>FBS
C* SoifonatnPFKS
Amount Amt Found Amount
Amount Ant Found Amount
Spftad Intemp* Recovaras R*COV*ry spited InSompIo Reecverad Recovery
<"4.... <q/14
M tn#/L> Ino/U
<n/U
c*>
OKIMN-GW-Wtl04-0-050*10 (C044M1*W.900 Ute9pte1
OKLMN-GW-Wf1O4-P-030310 (CMMtei SpKN,som nl LabSpite)
OKLMN-QW-W1OAO-OW10 Low Spike Sppb (C0MA4M,SOMr\&LFMtfSpite >
OKLMftGW`Wia4-P4GOS1Q HiflbSpite ppb fC0flSA487sS0060apt-FI*WSpite \
5000 50000 5000 50000
NQ NQ NQ NQ
6680 73000 6730 60700
134 5000 146 50000 135 5000 139 50000
NO NO ND ND '
SOSO 48000 4720 51200
101 96 94 102
OKLMN-GW-W20t-C-0OS10 {COPOOSl SpfcC,WOOnpLUbSplte )
OKLUN-GW-W201-8-956316 (C0M4434Spk0. ffWngrt.LabSpft*)
OKU4N<JW-W*201-(M)5W10 Low Spite 0,5ppb <CaSS44S0,soe FMdSpite)
OKLMfMW>W62610-956316 HlflbSplka 5 ppb (CMM441, Sloe ngfLRaidSpite )
5000 50000 500 5000
74.0 74.0 740 74.0
6360 66600 877 7560
130 9000 131 60000 121 600 150 5000
ND NO ND ND
4610 44400 543 5360
92 68 109 106
QKLMN-GW-WZO-O-CSOJM (CpOeMarSpbE.SBOOng'LLabSpite}
OKLMN-GW-W30-Q-6SOS9 (CWP44P7Spkf, MWa#L UbSpite)
OKLMN-GW-W20-4-080306Low Spike 9 ppfa {CMS4M*.500*i l RaidSpite)
OKLMN-GW4^20-0-050309 Hltfi 3pflK ppb tCOOMtnLsooooi^l noiaSpite)
5000 50000 5000 60000
13000 13000 13900 13900
19400 77100 20900 85000
110 5000 12900 126 50000 12900 140 5000 12900 142 500C 12900
16200 56200 16200 48400
86 65 8 71
OKLMN<GW-Wa24&030* (C00444718pK0,9009 LabSpite)
OKU!N-GW-W220.ft5IMn9 (000*4471 SpKn,50000rqfl*US Spite)
OKLMN-GWW2--05M06low Spite* ppb (COOtOft,5000nqfLFWdSpite >
OKLMN-GW-W22-Q-MO306 Hlflh Spile ppb <CO0t44?4.50000pH.FtedSpite )
5000
flo o o o
5000 50000
36600 36600 36600 36600
44100 109000 44000 111000
5000 31400 145 50000 31400 5000 31400 149 50000 31409
37000 73000 35000 62200
* 83 62
OKLMN-OW-W31-0-P5OM9 (C00SU75Spit 1,5000nglLLab Split*)
OKLMN-GW-W314-0EO3Qt (C0DC447SSpkJs50000rtpTLL*bSpHw)
OKLMN-OW-W11-M50MP High Spike H ppb (COOW477.50000ngff. FtaMSpite}
5000 60000 50000
1300 1300 1300
8450 70500 90900
143 5000 5130-' 138 SOCCO 5130 179 50000 5130
9090 51200 63200
7B 92 118
OKLMN-GW-WJ2-0-50M (Ceoe**7aSpaK,sew pit.LaaSpite)
OKLMN-GW-W32-0-6503C* (CMM47BSpKL.50000aprt.L*b8friX*>
OKLMN*GW-W324)46030B Low Spite 5 ppb (COOB44M.4000ngfl.Fl*toSpiteJ
0KLMN^0W-W32-0-teW Wflb Spite SOppb {C00M4I1,SOboOP0L noteSpite 1
5000
60000 5000 50000
2160 2160 2180 2180
6910 67300 10800 66500
136 5000 3000 130 50000 3000 172 5000 3000 127 60000 3000
7400 50000 7910 52800
66 34 98 100
'Sjw tpLe re sid lace ad a the apflcing le ve l m rtfleand y: theretom. in accurate recovery value cannot be calculated
ND * Notdetected a t Of bo-v* 25 ng/U (ppt). NQ Not quaniiSa&Us = M escured cw cantrafio n between 25 V L (ppl) and the UTO d
Quantitationfl-OQ)which 50ng/t (ppt).
Note; 9tn ca th i* au nim iry tabte sho w rounded re a u to , recovery va lu ta r a y vary alg h U y
from the v a l a s In Uta raw date.
Exygen Research
Page 26 o f 110
000049
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen. Study No.: P000I400
Table II. Matrix Spike Recovery of PFBS and PFHS in Water Samples Continued
Sampl* OmctlDti
C4 Suffimie PiFBS
Amount AmtFound AlRMHlt
Spiked in Sample Recovered Rpcavaiy
W ->
<%>
Amount Spiked
Cl SuHomrtePFH5
Amtf:CNMKt Amount
in Sample Recovered Recovery
CnaX)
m vu
...... <%)
OKLM*FOW-W217-0-O5WM (C0M4413 $pk M.90M no^ Ub Iplke>
0KLMH*GW-W3rt7-0-0603M (C<oa44aapkMtsoeaRafLut4e*> OKLMN-0W*W2174-050300 Low Split* 8 ppb
fee**,9*oongi n*w3*"* >
0LMfWJW-WaiT-0-0<JWa High spike SOppb (CDW*,eoeoongfl.FW Sake 1
5000 50000 9000 50000
NO ND NO NO
0630 66800 7570 71200
134 5000 134 50000 151 5000 1 50000
ND ND NO ND
4680 46500 4590 51300
96 93 92 103
OKU*N-OW-WM#M*WW (CMM4M Si* a 8000o0.Ub Splhe)
OKUW4-OW*W200V^-0MM9 (CaOM SM SpkP. SOOMepiLLW i Spike)
OKLWN-OW-W2MS-0-OSIUOS U rn Spike 5 ppb tCM tM M , BOWngl FW Spit)
OKLMN-GW-W20M-0-4M30S High Spike SOppb tCOOSHH, BOOMba*-RaidSp ike)
5000 50000 5000 SOOOO
6780 6780 5780 8780
14300 73600 18S00 37900
150 6000 10100 134 SOOOO 10100 194 9000 10100 162 50000 10100
16000 56500 19300 84BOO
1TB 93 164 109
OKLMN^3WWV2d12-0-OSOaOO
fC 0 0 M 3 p * c . s m t * n u e s ik j
OKlMM-GW-WiOIM^lSCISW (C*eM4eSpk o , soooea^ L Lab Spiiei|
OKLMN-GW<Wa&12-0-OS3( Low Spite 5 ppb (ceoeeMa,eootn y t n*M spn)
OKLMN43W-W2M2-C-CH30High SpikeSOppb te w e tw , 59000 n p L field Spike >
.5000 50000 5000 SOOOO
22W 2210 . 2210 2210
6600 66400' 8210 71500
132 , 126
5000 50000
4700
'
4700
120 5000 . 4700
139 50000 4700
6140 46900 6950 53800
69
65 96
OKLUN-Qty'WKMM)B030B (C90$4m spk , twonot. U P S p U ")
OKLMii-SVkLWSD-O-OUOO
000*44*4 8 f* F . 9*040 n p l L*U B p tt)
OKJLMN-OW-WiC*0*S0009Low 3 p lk 5 ppb
<COflB44M. SOM * * 1 R *kJ Bptb* )
OKLMN>4W-WN-O-aS00CftHigh SpikeSOppb tCOOMCtr. MOW ngfLnt0 3pik )
5000 30000 5000 50000
ND ND NO NO
6850
64700.
7390 .t 69700
137 m o 129 SOOOO 148 5000 13 50000
ND
ND ND ND
4960 46200 5200 49200
100 92 104 96
OKLMN^W-PWI4-05031*
(C M M M I Spk G, K M n fJL Lab 8pUt)
OKLMW4W4W14-O0O310
p t t u ia i * * h , BOOM e l Lee * f* e >
OKLMN43W4W144S03M LOWSpike 6 ppb
6*044400. 0 0 n g l " Sp ite )
OKLMN-aW-PWt-O-O60308 High Spike 00 ppb (tsoMsot,joeee el Fw$e*w 1
5000 50000 5000 50000
5620 5620 5620 5620
13600 72000 13100 69700!
ISO 5000 4160 133 50000 4160 150 5000 4160 126 50000 4160
8860 52000 7690 47700
94 96 71 87
OKUiM>aW4>Wa-M)S031 (CtWUMaSpfc1.COOPn p l Ud> * p * a )
OKLMKKSW4>m44SM10 tCMM*02 3** 4, fioomft*LU P Spa* )
OIOSdN-gWf*V24o3io Low spike S ppb 90M4SM, M * *1 R*4d Sptfc. )
OKUiN-aw-PWi-o-otojia hhqi>sp* so ppb (CM04MS.aoftcoegft. PWd Spile)
KXJO 64t 50000 641 500CT * 641 50000 641
7720 65900 7030 64300
142 5000 131 50000 126 5000 127 50000
501 501 501 501
5280 47700 5190 44300
95 94 94 69
'Sampleresidue w eed * the spiking le ve l signA cani^ ; Therefore, *n accurate recovery value caonet be calculated NO Motddttoecor Steve 25 nqfl (ppt). NQ e tat*iar6iabie * Mewuradconewitraiton brtwaen25flfl/L(ppt)aivittratJmitcrf
Quantitation <LOQ) wNch is 50 n g /l (pplL N ote: lin e IN * iu t m *fy table ih o w e rounded re su lt*, recovery valu e* m ay vary *ityh tly from the va lu e s in th e raw data.
Exygen Research
Page 27 o f 110
000050
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
Sample Descrlptor
OKU4N-GW-PW-0-060310 {C0eM8M9pfcK,SOMftfifl.Let Spike)
OKLMN^W*PWS-9-0gS1O (COOSiSOSSpkl. SOngA.LebSpltot 0KLMN-RW<FW34>-0S*31 Low 8plke 5 ppb
{CCflMCOf. MMngn.fmmSpnte) 0KLMN-GW-PWJ4WM11&HlffhSpike50 ppb
{COOMSbt, SMOOepiLneldSpIlte)
C4 Sulfonate PFBS
C8 Sulfonate PFHS
Amount Amt Found Amount
Amount Ami Found Amount
Spiked li Stempia Rncwwnd Recovery Spiked InSample Recovered Recovery
m
("VU
(noiU
%> (non.) (no-!
(ns/L)
<*!
5000 90000 5000 50000
0470 8070 5970 6970
13600 90900 15200 92300
137 5000 10000 160 50000 10000 165 5000 ' 10000 171 60000 10000
13600 54400 16300 54900
72 89 126 ec
QKLMN-GW-PW44WW310 {CMMS1SSpaM, 9000 non. Lab Spike)
0 KLMN-GW-PW4-0-OSM10 (COMMI8*kN.90100sort.Ub Spike)
OKLMN-QVhPW4-0-040410Low Spike 3 ppb (C0C44512,SOOOn*LFieldSpike)
OKLMN-GW-PW4-Q-6W10 MghSpfceM ppb {C0W313, WWTO9rt_fleWSpike)
9000 50000 500C 50000
6130 6130 6130 6130
17400 95000 16300 66900
165 5000 7890 174 50000 7880 163 5000 7890 102 50000 7890
13900 53600 13500 58200
120 91 112 101
OKLMN-6W-PWI-M40310 {COOMM4SpkO,9000n^LLabSpike)
0KLMN-CW-PW445O310 (C0M4S14SpkF.MOOOnpLLtbSpike)
OKLMN-GVhPVM-OWSIOLOWSpfc* 4 ppb <000*051.SOOO*wt new Spike3
OKLAIN*W*PW6*(Ml60&1OHighSpike SOppb (COOUS17.JOOOOnpl HeMSpike)
5000 50000 5000 50000
7930 7B3C 7930 7930
17200 60500 17100 &46C0
165 5000 14500 166 50000 14500 163 5000 14500 173 50000 14500
20600 58800 20800 59400
122 89 128 90
OKLMN-GW-PW10-0-031D (Coeoeei9pkCteoew'l Lab Spike)
OKUMN-GW-PW104-050310 ICOOMOMSek CLSOWOnpiLUb Spfiie)
OKLMN-QW-PW10-<MU0410Low Spike5 ppb iCMMMaae,OOagit FieldSpike)
OKLMN-GW-PWlD-0-05310 High SpikeM ppb (CDM4021.SMOOepLfWd Spike)
5000 50000 5000 50000
13100 13100 13100 13100
19300 70700 19000 74000
124 5000 29200 133 50000 29200 118 5000 29200 122 50000 29200
34300 71000 33500 71300
102 64 B6 64
OKJLMN-QW-PW11-0'OSW1C {COeSMZZSpkE.9009npl LabSpiket
OHXMN-GW*PW11-0-MOJ1C (C0SO22Spbr,eoo nLLWSpike)
OKLMN-GW-PW11-0-050310 Low Spflca $ ppb {000*19*. OOMnyLField Spike )
OKLMN-GW-PW1I-0-050314High Spikep p b (cooeesas. sooeoqil neid spike>
5000 50000 5000 50000
520 520 S20 6520
12700 60300 13200 63600
124 5000 8820 124 50000 8820 134 5000 8820 114 50000 6820
14200 65100 13300 54800
10Q 93 90 92
"Sam ple rse ick * exceed iris splicing le ve l sigmAcanAy; therefore, an accurate recovery value cannot be calculated
NO > Not detected a t o r above 25 ng/t ipp t). NQ 3 Not duwitHtebte = M easured concenM fcm between 2$ n p t (ppO and h e Urrrtt of
Quantitation <LQG) which b 30 ng?L (ppt). Notm S in ce th is sum m ery table e lw w * rounded r e e u ti. reco very v a lu e s m ay vary lig h tly from th* value* In the raw data.
Exygen Research
Page 28 of 110
000051
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: PQ001400
Table II. Matrix Spike Recovery of PFBS and PFHS in Water Samples Continued
Sample CaacflpBon
OKUW -sW itwwm <coo*m * * 0.4*00 *9*. Lab8pa>
OKLMN^W-O-omiO (C0N4S BpfcH. ONngft. Uri)Bp ) OKU4N'4W-0-W0310 Low $pfto Sppb
(COOMO,Mao*v*-*MApt }
OKLMN-SW-0-050319High Spit* BOppb (COOMB**OtMftn.FM4S| )
OSuMMUMPfBS
C* SuMonatt PFHS
Amount Amt Found Amount
Amount Anil Found Amount
Iptod InSmph Recovered Racovary Spfltad in Sample Rocovurod Racovary
w
(no.
(ngfl.)
> ._ .. m
in *
i%>
5000 50000 5000 50000
NQ NO NQ NQ
5900 93800 72*0 65000
120 6000 128 50000 145 5000 130 50000
NQ NQ NQ NQ
4790 45100 5250 49400
96 90 105 99
OKUWJW-TKlP2--06M1i>Low SpHta s ppb (C0MB>1.6000aalL 1
OKLMtM3W-TiaPZiMC0310 HJQhSplko0 ppb (OOKMSB,WM itf*. 50t*\
000 50000
NO NO
4480 20100
90 5000 NO 58 S000Q NQ
4970 49000
98 9
Avaraga: 141 Standard DavtaUon: 21
SamplaresiduatwaadalwaiildnB lavai darifcarty, mere, an acculale racavaiyvsluaeannol tiecsfcuMsd NO Moteeisctsdsiorai>ove25neA.(pp(). NO . NotquenMablc.Msesvadoonce'irtraitonbetMeanZSngS.fepQandltielJiritar
Quapwaaon(LOO)101B90 ogrt. (ppi). Nota; Mutatataatumnaiytatuashows roundedreauHe,recoveryvalua*mayvaryillgMIy from tha vatuaa Siatto rawOsta.
Avuthp; Standard Davlalkm;
6 1C
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
Sample Description
Cl Sutton* PFOS
Cl Acid PFOA
Amount Amt Found Amount
Amount Amt Found Amount
SpIkMl In Sample Recovered Recovery Spiked InSample Recovered Recovery
JoglLt tr&Lj
(ngn.)
t%t (ngfl.)
(null)
from
(It)
OKLMN-GW-W3-C-05O310
<CM M 4ftpk C .< O tO o 0 LL& b *tl)
0KLMM-GW-WMH1S 1 0 (CDOVMMSpk 0 .3MOO ngrt. l*& M M )
OKLMN-CW-W3-0-O5O31OLow Splk#5 ppb ICHM4M,SOMD O l FtoW M M )
OKLMN-GWAV34H15W10 High Spikft ppb {CMM4407, MOM 19II.FkidMM \
OKLMfkGMM-0-09031t (CM444CC Spk P, MMng*L.Lab 5 p lh *)
OKLM*GW-W-0-031I>
(C M M 4 M *p k F .B M M a 'L L a b M ta )
OKUtlN-GW-W8-C-O5M10 Low $plk* 9 ppb (CMtnn, com m l Fi*m m m )
OKLMN-GW-WMWM310 WghSplk* ppb <00004411, OMOOnplLPMOSpikl)
000 50000 5000 50000
5000 50000 5000 50000
475G 4750 4750 4750
59.0 56.0 66.0 59.0
12400 73500 10900 84500
4940 55000 5380 S0500
153 5000 138 50000 123 000 160 50000
98 5000 110 50000 106 5000 101 50000
6330 8330 330 330
290 290 290 290
11900 59200 9470 40100
5360 51900 6060 36300
111 106 63 80
1C1 103 115 77
OKLMN-GWW20-Q-0M31Q <000044138pfc 6, M M n g fLU b M*>)
5000 13500000 9450000
*
5000 79300000 65300000
OKLWN-6WW2WJ^5031b
(00004410 S f* H , BOOM ft. ^>b M M )
50000 13S00C00 7390000 50000 70300000 68300000
OKLMN-GW^W2*-0-0M310 Low SpJk*5 ppb
{C0004414,MMrtpft.Ffrki Oplto)
5000 13500000 9050000 - 5000 79300000 73100000
OKUttl^W-Wi8-0*5W1 High SplkP 50 ppb
(CO M M IT MMO ttQfi FW4SpH*)
50000 13500000 7210000 50000 79300000 57900000
OKLMN-eW-W3Wr-050310 <CMM4148pU MOOnpft.Labpika )
5000 4610000 4720000
*
5000 1750000
1520000
OKLMN-GW-WS3-0-O3W1O (COO94410Spk 4. 50000 Aftll.LbM M )
50000 4610000 4730000 50000 1750000 1650000
OKLMN-GW-W33-0-050310 U m Spile*5 ppb
<00004444MOftapTLR*k4S0k >
5000 4610000 4820000 5000 1750000 2350000
OKLMN-GW-W33-0-050310 High SpOtt 50 ppb
{C0004411. MOM npILFM d fipttn)
50000 4610000 4520000 50000 1750000 1630000
.
* *
OKLMN-GW-wzowaimo (ceosscioSpsn. sms sgiLu s Spu)
OKLMK^JW'W205-4V-050310 (C0004420OpbL,4MMnpft.LabMM I OKLMN45W-W2W-0-OWMOLow Spike 5 ppb
(CM 94423,5000 n gfl. fltid SpU u)
OKLMN-GW-W2054HKQ310 HfflfrS p tic SOppb
(C9M 4433,300M ngO. FIvJd M * * )
5000 50000 5000 50000
146000 146000 146000 146000
138000 166000 129000 221000
500 20 50000 5000 150 50000
147000 147000 147000 147000
160000 190000 143000 184000
-
86
74
OKLMN43WW15-04W031O {CQ0C44MSpk M.00MUp. L ift S p rt*)
OKLMNriSW-W215-0-O3C310
(C M M ttS f* N. 50000 A tft. L ib Splba)
OKLklN-GW*W215-0-050310 Low Splk* 5 ppb {C044M 00 n p l. Ff*W M b * l
Ota.MN-GWW*S154CM0J10 High Spike 0 ppb |C SM 4I7. new SOIL FMdIp ilB )
5000 50000 5000 50000
37100 37100 37100 37100
52400 96SOO 50600 101000
5000 120 50000 5000 128 50000
4400 4400 4400 4400
8850 55700 9600 '38200
0 105 35 70
Sam ple residue B a se d ll>e spiking le ve l g nifirantly. therefore, ap accu rate recovery vd u e cannot Be calculated NO Oslscurd a<or ibove 25 r^ L (aptl luQ . Not Quaotifippte > M easured co ncentrator hetween 25 rvjA . (p p t)aed the lim it of
Quantitation (LO Q ) w hich is 50 n o il Ippi)
N o d : S in ce th is au n vn ary U D Ie sh o w s ro u n d K l re su lts , re trw e ty v a lu ta m ay vary slle h tty from the v a lu e s In the raw data.
Exygen Research
A
Page 30 of 110
000053
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: PQ00140Q
Table HI. Matrix Spike Recovery of PFOS and PFOA in Water Samples Continued
Sampla OwertMlon
C8 Sulfonate PFOS
Amount Amt Found Amount
Amount
Spited InSwnpl* Recovered Recovery Spticed
w
tntfL) .... pgft-i_____
(nflfl.)
C l Add PFOA
Ami Found Amount InSimpI* tteCOVOFKi Rccovary
P W (ntfL) . t%)
OKLMN-CW-W201tH3-0Mi0 tcaeeMi*apkc. aooo nn.ub%ik* >
OKLMW-GW-W2010-C-05M10 tcee*44at spao, csoao l*apt >
OKLMhHSW-W2010^-05&310Low Splkft 8 ppb {CC0*443e. MODe^L RMByte*>
OKLMN-GW-W201WFOIOttO High Spfca 50 ppb {cnMMn. som *#. FtoMSo I
5000 50000 5000 50000
. NO ND NO ND
5170 54600 5270 54900
103 $000 109 50000 105 5000 110 50000
NQ NQ NQ NQ
5290 54300 4710 33300
106 108 4 65
OKLMN-GW-PW7-O-0SC310 (C0fe*4*2 S|*E.3WWLUtpa)
5000 71600 78500
woo 37600
OKLMN*0W*PW7"<WMO310 (0WK4 SpkF.sseee aglLUb a#e )
50000 71600 119000 95 50000 37600
OKLMN-GW-PW7-O4W0318Low Splh* S ppb
teeeee*.oe ngruFWdSen i
5000 71600 72600 . 5000 37600
OKLMN-GW'PW7-0-dS03IOHigh Spike SOppb fcoeeteas. seaea as*,new spa )
50000
71800
118000
89 50000
37600
41900 86100 42800 67100
* *7 * 59
OKLMfMWTTOPi-0-05C310 Low Spike 5 ppb (CflMSter.aao*m^LFtawleu )
OKLMN-GW-TR1P1-0415031IJ High Sptk* 56 ppb (<XIHM3I. SOHOalkFWdSU)
5000 50000
ND ND
5780 53500
116 5000 107 50000
ND ND
5360 50500
107 101
0KLMN-W-W*-O4W0J1CI tco*4tu *f* o. bom.on. u t pa )
OKLMH^5W-PWa0090S10 (CWMWSpk H.twwa npL LabpNNl
OIOMIiW-PW-<MWla Low Splkb 5 ppb (CPM4444,X H apl FWU6pn)
OKLMN-GW-PW5-9-P30310 High Spile SOppb {00*4445, SONOnpfl FMdOptea)
5000 50000 5000 $0000
34300 34300 34300 34300
3B500 89600 38400 63100
- 5000 t u 50000
- 5000 166 50000
61400 61400 61400 61400
61000 113000 59300 82200
. 103
42
OKLMM-GW-PyrtMW>50S10 <CeOM4W3|B*J,W''9'lUb*i*te>
OKLMN-GW-PW-<W>50510 {000*4440SpkA 0 *0A Uft Spilte)
OKLMN-CW-PW94W0319Low Spike S ppb (C0M444*.MWo^l FtaklSpite J
OKLMN-GW-PW9-0-050310High SpRw 80 ppb tceeewa, SO**rta-nwe se>
5000 50000 5000 50000
64400 84400 84400 84400
83200 136000 96400 178000
- 5000 107 50000
- 5000 1*0 50000
49000 40000 49000 49000
50400 97900 55200 93200
96 80
0KLMN-GW-W6102-0-050310 (CC04M4SOepicK, SON*gA. Lab9*11 )
OKLMN-GW-W6102*0-050310 (C0N44W8plrL.aeNnBA.Lah Spite)
QKLMN-GW-W8102KI-05W10 Low Spfca 5 ppb tceeewa.w*a*A.Fteo* >
OKU*fWJW-Wi102-0-W0310 Hlflfl Spike 50 ppb (COM*.** eft- FieldSpite |
5000 50000 000 50000
NQ NQ NQ NQ
5300 55800 5480 53200
106 5000 112 50000 110 5000 106 50000
214 214 214 214
5880 52700 5610 35300
113 105 108 70
Sanpte reetatoe axcaads ft*apiunolevel apniflcamfy; therefore, an accurate recoveryvalue cannotbe calculated
NO * N et detected a t o r aboim 26 ng/L (ppt).
MQ = htol t^a/Hlflable* Measured conoentraticir tsehween25 noA.(ppt) and the lim itor Quantitettcn (LOQ) which is 50 ngrt. (ppt).
Mote: Since this nummarytable *how* rounded reeults. recoveryvalue* mayvaryllohlty from the valuta Intha 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
Sarepta PeecrtpUon
CI Sultanat* PFOS
CSAdd PFOA
Amount AmtFound Amount
Amount Amt Found Amount
Spiked mSample Recovered Recovery Spfktd inSampta Recovered
(no>L) (nn/U
tao/U
|S | fna/U Inaiti
inali)
Rocovaiy |%)
OKU4N-GW-WS104-0*050310 (C90M4MS*M.90OPfla.Ubpftft)
OKLMhMSW-WVI04-0-050310 (C0M 44M tpk H, Mtoon*L LibS p ite )
OKLWN^W-W51C4-0-050310 Low Spike S ppb (C90M 4M , 5000 ng/L FtoW9 0 te \
QKLMN-GW-W6104-0-050310 High Spike 50 ppb (COOOUn. CMM ng/L FtaMS p ite )
5000 50000 5000 50000
OKLMN-GW-WI201-0*050a|0 10099449SpkC,30b Oft, le t fell* )
QKLHN-GW-W8201-0-05W10 (C a te H ttS t* Or*0000ngfL LabSpite}
0KLMN-GWW6201-0-050310 Low Spike 03 ppb (C0044440, KMnpM.FieldS p ike}
OKLNhKiWW8201'<M>50310 High Sp4k* 5 ppb (99*44*1, SOW ftp*. Ft*MSpite}
5000 50000 500 5000
109 109 109 109
NQ NQ NQ NQ
5500 58100 5700 56700
4SB0 50000 670 8900
108 5000 116 50000 112 5000 113 50000
1O0 5000 100 50000 134 500 132 5000
207 207 207 207
953 953 953 95.5
5290 57300 5470 35800
4950 50800 606 8130
102 114 105 71
97 101 102 121
OKU4N-GW-W2C-O-OSO309 JCOO*44*7 SpfcE , 5000 nprt_ U Q S p )
OKLNN-GW-W2Q-0-0903Q9 tC d 9 4 4 7$ |*F. 9 0 9 n^LUbSp ite |
OKLMI^W-W29^-0S030a U w Spike 5 ppb (090*4449,9099 nA FM d fe d * )
OKLMN-GW-WZO-C-OSWOSHigh Spike 50 ppb fC M M 47ft.M M iieft. FM d Spite)
0KLMfKiW-W22-0-G50309 <C*DM471 &pkG, SOM ngIL LabS p ite )
OKLMN-GW-W22-0-OS0309
{C999M 71 Sp kH . S O fM fttfL L jiife ite )
OKLMM-GW-W22-0050309 Low Spike 5 ppb
C0M4473,WOO ft. F ield Sp ike)
OKLMN-GW-W22-O-05CMS High Spike ppb <080*4474.50000noA FM d Spite)
OKLMN-GW-W31-0 -0 5 0 3 0
(C0eM 479Spk I.W O e n p L L e d S p **)
OKLHbJ-OW-W31*0*050309 tC0M 7S Spitt, MOM Latatplte ) 0 K U 4 H -C W -W 9 1 -0 4 5 Q 3 Q 9 High Spike 50 ppb
{CM94471,19099ng/L FMd Spite)
OKLMN-GW-W32*0-030309 <cooM47i spkK. woo eed. cab spite)
OKLMN-GW-W32-0-030309 (C0i44744HkL C9090noA U b Spite) OKLMNM3W-W32-0-O5C309 Low $pc 3 ppb
(C80F4AM, WOOngA. Field Spite )
cm iM N -G W w aa-frosow High Spat* so ppb (CMW4S1, B0000 np*. FMd Spite)
5000 50000 5000 50000
46600 46800 46600 46800
300 50000 5000 50000
asaco 45500 45500 45900
5000 132000 50000 132000 50000 152000
5000 47100 5OOD0 47100 5000 47100 50000 47100
49900 92800 41900 59500
44600 96500 41200 65800 116000 168000 218000
62200 115000 74000 120000
. 5000 285000 92 50000 285000 - 500C 285000 26 50000 285000
* 5000 317000 105 50000 317000 - 5000 317000 40 50000 317000
A 5000 72 50000 168 50000
23100 231CO 23100
. 5000 117000 138 50000 117000
> 5000 117000 148 50000 117000
289000 295000 278000 264000
330000 412000 324000 288000
26400 71300 65700
109000 151000 131000 157000
96 65
*50111111* reedu* excaedi m* spUrte levelsignificantly; therefore, an accuiate recovery value cannot De cafculaied
ND =Notdetected at of above 25 noA-(Ppt). NQ Notquanuliabl = Measured concentration bcNreen 25 ngTL {pptfand lit* Until of
QuanBtation (LOQ) wHlcft 1SOnpfL <ppt). Note: S in M s summerytable shows rounce results, rcovry vatu mayvary sligntly front lha valuas In the raw data.
Exygen Research
Page 32 o f 110
vi0 0 5 5
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P00014QQ
Table III* Matrix Spike Recovery of PFOS and PFOA in Water Samples Continued
Sample OeecrlptkMi
OKLMN-GW-W217^M55CMfi (001044SekK we ngU.U*ptiie1
OKLMN43W-W217-0-05030* {OMS44S2SekM.SNMnSLefiScllce>
OKLMN45WWN2174W5034WLow Splka 5 ppb tCeoe4*M,Wgru FW d See)
OKLMK-QWWI7-043090B HfekSpIkaSO ppb <ca4*an * ectiLFMdSetfc)
C* Sulfonate PFOS
C8 Acid PFOA
Amount AmtFound Amount
Amount Amt Found Amount
Sptfcod feSaapla Ractwarad Recovery Spiked InSimple Recovered
(">m____ w n _ J 5 m ________ & a _______i? fla = L
(ntfU
<ns7L>
5000 50000 5000 50000
NQ NO NQ NQ
4790 49700 5600 65300
96 5000 99 50000 116 5000 131 50000
NQ NQ NQ NQ
4860 52200 4880 42600
OKLMN-GW-W200B-0-050 |CQM44MSekO.M8eJLLah *41)
QKLMN-GW-W2009.<M03W {Coesuee%pk p, sow *m l *o Se)
OKLMN-GW-W2WW4J5M09 Law Spka 5ppb tC*44M0MB0fLeW *0M)
OKLMN45W-W20a-<HJ50309HighSpdct 30 ppb iCoeeMM, Meceril nek*5pn*)
5000 50000 . 5000 50000
15500 15500 15500 15500
20800 69300 27000 71300
106 5000 106 50000 230 X X ) 112 * 50000
59300 59300 50300 59300
64800 114000 73600 94600
OKlMN^WAV2O12-0-O5C6 tceoeneeSeec, eeenpLteeSpile>
OKLMN-GW4*2012-0-05C3C (Cees***a<* 6,eeoeo*<yLLabap}
OKLMN-<JW-W2012-4W6M0f Low 8pfce 9 ppb tceeseeee,seeseLp w Sene>
OKLMN-GW-W2012-^5030High Spike 0 ppb (CMSHfd.N O N ap L FMd *41)
5000 117000 143000 soooo 117000 186000 5000 117000 * . 115000 SOOOO 117000 203000
* 5000 46900 136 50000 46900 * 5000 . *0900 172 50000 40900
57700 94700 48500 99500
OKUUN43VWaO-0-8O (COM4*** * * , 9*00a* L LabSpilw)
5000
OKLMN-GVMIVMMMSOaO (CDeeeoMspitf, s e e e p L u b s ^ e )
OKLMW4W-WMWMl5MOt Low Spit 5 ppb (CSMMOO.000 nan.FtaM p e a )
C^LMN-GW-WSO-CHWp HighSpike SOppb {CMU447, ttOMA L FMM p ** )
50000 500C 50000
OKLMN-GW-PW1*(KO<U10 (C00644MSpfcS,MOOATLLsb Spike)
OKLMN43W-PW1-0-050316 {COOSMOI acritK.060n^yLluto o n e )
5000 50000
OKLMN^GW-PWi-O-OSDStOLow Spike S ppb <
(CMMieo,co t ngn. noiespat >
5000
OKUflN-GW-f'W1-O-05C3WHIQ91SpQcf 50 ppb (C0MM001,00000ngA. FM tf * * )
50000
to
' ND NO; NO
66900 66900 60900 66900
5280 52900 5720 57600 72000 116000 66900 '' 95200
106 5000 106 50000 114' 5000 113 50000 * - 5000 102 50000
5000 57 SOOOO
302
302
302 302 37300 37300 37300 37300
SS10 53100 5860 42200 477X 60200 40400 80500
OKLMfWW-pW2^WC31<r '6004*00*ok1, 9*00ngtL Lab SpH * }
OKLMN-GW-PW2-<W>S0310 (0006*902ok4,60M0nA. LobIp lk * )
OKLMN-GW-PW2-M5W10 tow Spike S ppb (CftoeuM,a m *#n. ro w paw >
OKLMN-GW*fW2-<M)3C31C Hlph Spike SOppb (camsos, neeea9x. r m *eu)
5000 351 50000 351 9000 .98.1.' SOOOO 351
5480 , 59800 ... 4280, *0500
103 ,5000 119 50000 79 5000 BO 50000
3830 3830 3630 3630
8720 58800 7860 39500
Recovery
(* )
97 104 91 65
*
109
*
71
.
06
.
85 110
ID S
111
84 *
106 66 102 110 35 72
'Sample residue exceed* the spiking lvf significantly; therefore, an accurate recovery value cannot bo catculeted NO * NotOetectedat oracove25 ng/L ippt). NQ * Not quantifiable Uessured concentration between 25 ng/t (ppt) and the Limit of
Quantitation (LOO) which is 50 ngl. {ppt}. >Mo: Since ttts summary table show rounded resulti, recovery values mayvary illghtty from the values in the raw data*
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 PFGA in Water Samples Continued
Sampi D M ZW on
CSulfon*tPFO$
G8 Acid PFOA
Amount Ami Found Amount
Amount Amt Found Amount
Spiked tn Sample Recovered Recovery Spiked in Sample Recovered
W U -fetfU
(ng/Ll
<%) {aaM
tn flO
_ (ng/L)
Recovery
(%). _
OKLMN-GW-PW3-0-O5031O <coo*so4spa k, tow .itUfaSptw}
OKLMN-CW-PW3-0-O5CJ10 (cemM eepkt, aoeto ng&Ufa**>
OKLWN<6W'PW34436310 Low Spike 5 ppb (CSM45M. SflO#ng/LFNfd 8pUt )
OKLMN<<3W4W34<O50310 High Spike 50 ppfa {ceoeesoe, moos ng/LField tptiie}
5000 50000 5000 50000
32700 32700 32700 32700
43300 6100 33900 90000
5000 177000 87 60000 177000 . S000 177000 55 50000 177000
138000 190000 196000 204000
.,
26 54
OKLMN-GW-FW4-0-0SC310 {C0MS319epk M,5M aoA. Ub apihe>
OKUWM3W-PWM-060310 <C0M4iieSpfcH, 90000neL Ufasou*)
OKLMN-GW<PW4-0-05Q310 LOWSpike 5 ppb <00084812,9000ne/LFieldpike >
OKLMN<-G00W004W4143.-000-000500i3i(1A0
High Spike FloMSpike>
30
ppb
5000 50000 5000 50000
33800 33600 33800 33800
42500 75700 42200 91200
* 5000 72100 84 50000 72100 * 5000 72100 95 50000 72100
77500 121000 870O 116000
* 96 86
OKLMN4aW'PWM*fl00310 (C00045U3pk0. SOODngILUfaSeth)
5000 90000 97600
- 5000 78400
OKLMN-GW-PW9-0450310 <08004514SpfcP, 90000ng/LUfaSplk*)
50000 90000 139000 98 50000 76400
OKLMN*GW4*Wf-0450310 Low SpBce3 ppb <00004114.1000ng*. Reid*pilw)
5000 90000
94100
5000 78400
QKLMN*GW*PW64-05031fl High Spike 50 ppb
(CM04917.90000npL FleWSpike}
50000 90000 124000 88 50000 78400
82900 133000 87000 116000
109 75
OKLMN-GW-PW10-0-050310 (Cweie<* c, 9ooo ne/t Ufa*** s
5000 1400000 1410000 5000 710000
OW_MN-GW4>W104-05P3t0 fCOWdSIStpkO, 9000089. UfaOfOta)
50000 1400000 1390000 90000 719000
OKLMN4<30W00-0P4W3910t,M90M00I1*f9i(n.iOFlaLtdoSwplShpi)ke 5 ppb
5000 1400000 955000
5000 719000
OKLMN-GW-PW11W5<050310 High Spike 3 ppb
(C0os42i,ttoeeA. Rew spfte)
50000 HOOOOO 1910000 * 50000 719000
868000 840000 692000 747000
. >
0KLMN-GW-PW114MI50310 {O0M4OZ2Of* E, 5000 npA.UfaSetiN )
OKLMN-GW<PWl1-0-O5O3lO SpkF. 000 ne>LLabSpifa>
OKLMN-GW-PWI1-0-036310 Low SpIKa 5 ppb (CMMSKK ngfl.RiWSella )
OKLMN-GW*PW11<0-050310 Hffib Spike 50 ppb (CO0C4829, SUN ng/LField Spike}
5000 50000 5000 50000
40800 40800 40900 40800
46900 83100 45400 88500
5000 60300 85 S0000 60300 - 5000 60300 95 50000 60300
64700 105000 83300 96100
* 89 76
Sam ple resid ue exceed s the spiking le ve l eignificaM iy; lhrefon>, an accurate recovery value cannot be calculated
NO = Not detected a t o r above 25 np4.<ppt). NQ = Not quantifiable *M easured concentration between 25 ng/L (ppt| and the Lim it of
Q uantitation (LO Q ) Which is 50 n g fl. (ppt).
Note: Since thl* summaryti bie shows rounded results, recoveryvalues mayvaryslightly from thevalue* in the raw data.
Exygen Research
Page 34 of 110
000057
Interim Report #l-A nalysis o f Oakdale Water Samples
Exygen Study N o,:P 0001400
Table III. Matrix Spike Recovery of PFOS and PFOAin Water Samples Continued
SampM oacrlptfon
CSSutfonaMFFOS
Amount AmtPound Amount
Amount
Spited In Sample Racovarad Racovwy Spited
m (nVU
<*) W 4
CS Add PFOA
Amt Found Amount
InSampt* Recovered
(ntPU
(nofl.)
Racovary <*>
0KLMN-3FMM6M10 (CODMtMftefcQ,4909etTLLehStrike)
OKUMN-SW-04G0310 {COfMOMipha <0*00A*L Ub Spfte)
OKLMH-SW-O-OSMI0 Low S pite 5 ppb (C00M42I, SONA0LFleWSplINi|
OKLMN-SW4M50310High S pite so ppb (Coeitwa.*000*egn. fmi *#w# >
$000 soooo $000 50000
1190 1190 1190 1190
6270 51600 7220 50000
102 5000 101 50000 121 5000 114 50000
491 491 491 491
5520 $3200 6020 44200
101
105 111 87
OKLMN-GW-TRIP2-0-050310 Low Spk* S ppb (CMMttt. 9 m bqA Op*n)
OKLMN"0W-TWP4*O*O3M10Hlflh S pite SOppb (C09040U,SOSOS00*. Strike)
5000 soooo
NO ND
6170 57400
123 5000 115 soooo
NO ND
6040 57300
121
115
Araiag: 110 Standard Deviation: 32
"Sample nwtfue exceeds the piking tevei ilgniScantfy; therefore, * Raccurate recovery value csnnoi be calculated NO NottWected al or abewe2b ng/U(ppt), MQ s Not quartiHablA=MeasuredconcanfcaBonbetaken 25 ngA.(ppl}and fiheUntilof
Quartftetfor) (LOO) which to 50 ngA <ppt). H o t*: n e e 9 9 a u e en w y taW # b o w s rounded r* u tt* . reco very v a lu e s m ay v a ry *H o H V fro m th e v a lu e s In th e raw d ate.
Avaraga: Standard Deviation:
93 1ft
Exygen Research
Page 35 of 110
000058
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table IV. Surrogale Spike Recovery of l3C PFOA in Water Samples
Exygen to
Sam ple D escription
Am ount S p lk e d
("flA -
laC-PFOA
Am ount R e co v e re d
(nort.)
R e co v e ry w
C0064404 Spk C C0064404 Spk D
C0064404 C0064404 Rep
C0064405 C00644G6 C0064407
OKLM N -GW -W 3-0-050310 OKLM N-GW -W 3-0-050310 OKLM N-GW -W 3-0-050310 OKLM N-GW -W 3-0-050310 OKLMN-GW -W3-0-050310 Dup OKLMN-GW -W3-0-050310 Low Spike 5 ppb OKLMN-GW-W3-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5580 53900
431 422 416 4730 34500
101 107 86 04 83 95 69
C0064408 Spk E 00064406 Spk F
C0Q644C8 C 0084408 Rep
C0064409 C0064410 C0064411
OK LMN-GW-W8-0-050310 O KLM N-GW -W 8-0-050310 O KLM N -GW -W 8-0-050310 OKLM N -GW -W 8-0-050310 OKLMN-GW-W8-0-050310 Dup OKLMN-GW-W8-0-050310 Low Spike 5 ppb OKLMN-GW-W8-0-050310 High Spike 60 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
C0064412 C0064412 Rep
C0064413 CO064414 C0064415
O KLM N -GW -W 26-0-050310 OKLM N-GW -W 26-0-C50310 OKLM N -GW -W 28-0-050310 OKLM N-GW -W 26-M 50310 OKLMN-GW-W26-0-050310 Dup OKLMN-GW-W26-0-050310 Low Spike 5 ppb OKLMN-GW-W26-0-050310 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
OKLM N-GW-W33-0-050310 OKLM N-GW-W33-0-050310 0 KLM N-GW-W33-0-050310 OKLMN-GW -W 33-0-050310 OKLMN-GW-W33-Q-050310 Dup OKLMN-GW-W33-0-050310 Low Spike 5 ppb OKLMN-GW -W33-0-050310 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
C0064420 Spk L C004420
C0064420 Rep C0064421 C0064422 C0064423
O KLM N-GW -W 206-0-050310
OKLM N -6W -W 205-0-050310 O KLM N-GW -W 205-C-050310 OKLM N-GW -W 205-0-050310 OKLMN-GW-W205-0-050310 Dup OKLMN-GW-W2C5-0-0S031O Low Spike 5 ppb OKLMN-GW-W205-0-060310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
4940
53000 279 280 307
4240 38000
90 105 56 56 61 85 76
C0064424 Spk M C0084424 Spk N
C0064424 C0064424 Rep
C 0064425 C0064426 C0064427
O KLM N -GW -W 215-0-050310 O KLM N-GW -W 215-0-050310 OKIM N-GW -W 215-0-050310 OKLM N -GW -W 215-0-050310 OKLMN-GW-W215-0-050310 Dup OKLMN-GW-W215-0-050310 Low Spike 5 ppb OKLMN-GW-W215-0-050310 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 PFOA level In the undiluted sample Interfered with **C PFOA recovery. Note: Sines this summary table show rounded results, recovery values may vary slightly from the values In the raw data.
Exygen Research
Page 36 of 110
000059
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
Sample Description
Amount Spiked
(ngiL)
1iC*PFOA
Amount Recovered
Recovery
..-<*>
C0064428 Spk C
OKLMN-GW-W2010-0-050310
CQ064428 Spk D
OKLMN-GW-W2010-0-050310
C0094428
OKLMN-GW-W2010-0-050310
C0064428 Rep
OKLMN-GW-W2Q10-0-050310
00054429
OKLMN-GW-W2010-0-050310 Dup
C0054430 OKLMN-GW-W2010-0-050310 LowSpike 5 ppb
C0064431 OKLMN-GW-W2010-0-050310 HighSpike 50 ppb
5500 50500
500 500 500 5000 50000
5390 53000
432 417 510 4500
30200
98 105 86
83 102 90 60
C0064432 Spk E C0064432 Spk F
C0Q64432 C0064432 Rep
C0064433 C00S4434 CO064435
OKLMN-GW-PW7-0-050310 OKLMN-GW-PW7-0-050310 OKLMN-GW-PW7-0-05C310 OKLMN-GW-PW7-0-05C310
OKLMN-GW-PW7-0-050310 Dup OKLMN-GW-PW7-0-050310 LowSpike 5 ppb
OKLMN-GW-PW7-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5260 51000 341
335 325 4820 33200
96 101 68 67
65 96 66
C0064436 COO54437
C0064438
OKLMN-GW-TRIP1-0-050310
500
OKLMN-GW-TRIP1-0-050310 LowSpike 5 ppb 5000
OKLMN-GW-TRIP1-0-050310 High Spike 50 ppb 50000
510 5100 51300
102 102 103
C0064442 Spk G C0064442 Spk H
COOS4442 C0064442 Rep
C0064443 C0064444
C0064445
OKLMN-GW-PW8-0-050310 OKLMN-GW-PW8-0-050310
OKLMN-GW-PW8-0-050310 OKLMN-GW-PW8-0-050310 OKLMN-GW-PW8-0-050310 Dup
OKLMN-GW-PW8-0-05P310 LOWSpike 5 ppb
OKLMN-GW-PW8-0-050310 High Spiks 50 ppb
5500 50500 500 500 500 5000
50000
5270 52900 321 322 300 3910
25800
96 105 64 64
60 78
52
C0064446 Spk I C006444S Spk J
C0064446 C0064446 Rep
C0084447
C0064448 C0084449
OKLMN-GWrPW8-0-050310 OKLMN-GW-PW9-Q-050310
OKLMN-GW-PW9-0-050310 OKLMN-GW-PW9-0-05031O' OKLMNK3W-PVV9-6-050310 Diip OKLMN-GW-PW9-(F050310 LowSpike 5 ppb OKLMN-GW-PW9*0-050310 High Spike 50 ppb
5500 50500 500 500
500 5000
50000
5250 53900 315 317 338
4230
24800
95 107
63 63 68 85 50
C0064450 Spk K
OKLMN-GW-W6102-0-050310
COO54450 Spk L
OKLMN-GW-W61Q2-0-050310
C0064450
OKLMN-GW-W61Q2-0-050310
C0064450 Rep
OKLMN-GW-W61G2-0-050310
C0054451
OKLMN-GW-W6102-0-050310 Dup
C0064452 OKLMN-GW-W6102-0-050310 LowSpike 5 ppb
C0064453 OKLMN-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
Note: Since this summary table shows rounded results, recovery values may vary slightly from the vaiira* In the raw data.
Exygen Research
Page 37 o f HO
000060
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Table IV. Surrogate Spike Recovery of I3C FFOA in Water Samples Continued
Exygen 10
Sample Description
Amount Spiked (ng/L)
TMC-PFPA
Amount Recovered
(nfl/L)
Recovery w ....
C0064454 Spk M
OKLMN-GW-W6104-0-050310
C0064454 Spk N
OKLMN-GW-W6104-0-050310
C0064454
OKLMN-GW-W6104-0-050310
C0064454 Rep
OKLMN-GW-W6104-0-050310
C0064455
OKLMN-GW-W6104-0-C50310 Dup
C0064456
OKLMN-GW-W6104-0-050310 Low Spike 5 ppb
CQ064457 OKLMN-GW-W6104-0-050310 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 C0034458 Spk D
COO64458 C0064458 Rep
C006445S C0064460 C0064461
OKLMN-GW-W6201-0-050310 OKLMN-GW-W6201-0-050310 OKLMN-GW-W6201-0-050310 OKLMN-GW-W6201-0-050310
OKLMN-GW-W8201-0-Q50310 Dup OKLMN-GW-W6201-0-050310 Low Spike 0.5 ppb OKLMN-GW-W6201-C-050310 High Spike 5 ppb
5500 50600 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 C0064467 Rep
C0064468 C0064469 C0064470
OKLMN-GW-W2O-O-O5O3O0 OKLMN-GW-W20-0-050309 OKLMN-GW-W20-0-050309 OKLMN-GW-W20-0-050309 OKLMN-GW-W20-0-050309 Dup
OKLMN-GW-W20-0-050309 Low Spike 5 ppb OKLMN-GW-W20-0-050309 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
C0Q64471 Spk G C0064471 Spk H
C0064471
C0064471 Rep C0064472 C0064473 CO064474
OKLMN-GW-W22-0-050309 OKLMN-GW-W22-0-060309 OKLMN-GW-W22-0-050309 OKLMN-GW-W22-0-O50309 OKLMN-GW-W22-Q-050309 Dup OKLMN-GW-W22-0-050309 LOWSpike 5 ppb OKLMN-GW-W22-0-050309 High Spike 50 ppb
5500 50500 500 500 500 5000 50000
4380 50700 267 280 256 3830 28800
80 100 53 56 51 77 58
C0064475 Spk l C0064475 Spk J
C0064475
C0064475 Rep CQ064476 C0064477
OKLMN-GW-W31-04)50309 OKLMN-GW-W31-0-050309
OKLMN-GW-W31-0-O5C309 OKLMN-GW-W31-0-050309 OKLMN-GW-W31-0-050309 Dup
OKLMN-GW-W31-0-050309 High Spike 50 ppb
5500 50500
500
500 500 50000
5410
54200
391 391 371
44100
96
107
78 78 74 88
C0064478 Spk K C0064478 Spk L
C0064478 C0064478 Rep
C0064479 C0064480 C0064481
OKLMN-GW-W32-0-050309
OKLMN-GW-W32-0-050309 OKLMN-GW-W32-0-050309 OKLMN-GW-W32-Q-05C309 OKLMN-GW-W32-0-050309 Dup OKLMN-GW-W32-0-050309 Low Spike 5 ppb
OKLMN-GW-W32-0-0503Q9 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
Nate: Sine* this summary tabla shows rounded results, recovery values may vary slightly from the values in the raw data.
Exygen Research
*
Page 38 o f 110
000061
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen. Study No.: P000I400
Table IV. Surrogate Spike Recovery of ,3C PFOA in Water Samples Continued
Exygen ID
Sample Description
13C-PFOA
Amount Amount
spiked Recovered Recovery
(no-) (ngfl.)
<%)
C0064482Spk M
OKLMN-GW-W217-<H)50309
C0064482 Spk N
OKUVIN-GW-W217-0-050309
C0064482
OKLMN-GW-W217-0-O5O3O9
C0064482 Rep
OKLMN-GW-W217-0-050309
CQ064483
OKLMN-GW-W217-0-050309 Dup
C0064484 OKtMNLGW-W217-0-050309LowSpike5 ppb
C0064485 QKLMN-GW-W217-0-050309HighSpike50ppb
5500 50500 500 500
500 5000 50000
5410 52500
428 453 468 4850 44700
98 104 86 91 94 97 89
C0064486SpkO
OKLMN-GW-W2008-Q-050309
C0Q64486Spk P
OKLMN-GW-W2QQ8-0-50309
C0064486
OKLMN-GW-W2008-0-050309
00084488 Rep
OKLMN-GVV-W2008-0-050309
00064487
OKLMN-GW-W2008-0-050309 Dup
C0084488 OKLMN-GW-W2008-0-050309 LowSpike 5ppb
C0064489 OKLMN-GW-W2008-0-050309High Spike 50ppb
5500 50500 500 500
500 5000 50000
5140
52100 318 326 357
6040 37800
93 103 64 65 71 121
76
C0084490SpkC
OKLMN-GW-W2012-0-050309
00084490 Spk D
OKLMN-GW-W2012-0-050309
00064490
OKLMN-GW-W2012-0-050309
C0064490 Rep
OKLMN-GW-W2012-0-060309
C0064491
OKLMN-GW-W2012-0-050309 Dup:
C0064492 OKLMN-GW-W2012-0-050309LowSpike 5 ppb
CO064493 OKLMN-GW-W2012-0-050309HighSpAe50 ppb
5500 50500 500 500 500
5000 50000
5050 50700 344
342 351 5010 37900
92 100 69
68 70
100 76
C0064494Spk C0064494 Spk F
C0064494 C0064494 Rep
C0064495 C0064496 C0064497
OKLMN-GW-W80-0-050309 OKLMN-GW-W80-0-050309 OKLMN-GW-W80-0-050309 OKLMN-GW-W80-0-050309 OKLMN-GW-W80-0-050309 Dtq> OKLMN-GW-W8Q-0-050309 LowSpike 5 ppb
OKLMN-GW-W80-0-050309HighSpike 50 ppb
5500 50500 500 500 500 5000
50000
5650 52400 486
438 502 5410 41700
103 104 07
88
100 108 63
C0064498Spk G G006449Spk H
C0064498 C0064496 Rep
C0064499
C0064500 C0064501
OKLMN-GW-PW1-0-050310 OKLMN-GW-PW1-0-Q50310 0KLMN-GW-PW1-0-050310 OKLMN-GW-RW1-0-05C310 ' OKLMN-GW-PW1-0-050310 Dup
OKLMN-GW-PW1-0-50310 LowSpike 5 ppb OKLMN-GW-PW1-0-050310HighSpike 50 ppb
5500 50600 500 500 500 5000
50000
5150 53000
331 350 352 4420 41600
94 105 66 70 70
88 83
C0064502Spk I C0064502 SpkJ
C0064502 C0064502Rep
C0064503 C0064504
. C0064505
OKLMN-GW--PW2-0-060310 OKLMN-GW-PW2-0-050310 OKLMN-GW-PW2-0-050310 OKLMN-GW-PW2-0-050310. . OKLMN-GW-PW2-0-050310Dup
DKLMN-GW-PW2-0-050310LowSpike5 ppb QKLMN-GW-PW2-0-050310HighSpike 50 ppb
5500 50500 500 500 500
5000 50000
5420 52600
440 440 431 4680 34000
99 104 88 88 86 94
68
Not: Sine this summary tab! shows round! rssults, recovery vslus my vary slightly from th values In the raw data.
Exygen Research
Page 39 o f 110
000062
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: POOOI4QO
Table IV. Surrogate Spike Recovery of 13C PFOA in Water Samples Continued
Exygen
to
Sam ple D escription
Amount Splked (ng/LJ
^C-PFOA
Amount Recovered
Recovery <%>
C0064506 Spk K C0064506 Spk L
C0064508 C0064506 Rep
C0064S07 C0064508 C0064509
OKLMN-GW-PW3-0-050310 OKLMN-GW-PW3-0-050310 OKLMN-GW-PW3-0-050310 OKLMN-GW-PW3-0-050310 OKLMN-GW-PW3-0-050310 Dup OKLMN-GW-PW3-0-050310 Low Spike 5 ppb OKLMN-GW-PW3-0-050310 High Spike 50 ppb
5500
50500 500 500 500 5000 50000
4640 53100 284 275 294 4080 38300
84 105 57 55 59 82 77
C0064510 Spk M C0064510 Spk N
C0064510 C00645010 Rep
C0064511 C0064512 CO064513
OKLMN-GW-PW4-0-0S0310 OKLMN-GW-PW4-0-050310 OKLMN-6W-PW4-C-050310 OKLMN-GW-PW4-0-050310 OKLMN-GW-PW4-0-05031C Dup
OKLMN-GW-PW4-0-050310 Low Spike 5 ppb OKLMN-GW-PW4-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000
50000
5190 52400 320 324 313 4870 36000
94 104 64 65 63 97 76
C0084514 Spk 0 C0064514 Spk P
C0064514 C0064514 Rep
C0064515 C0064516 C0064517
OKLMN-GW-PW6-OO5031Q OKLMN-GW-PW6-0-050310
OKLMN-GW-PW6-0-050310 OKLMN-GW-PW6-0-050310 OKLMN-GW-PW6-0-050310 Dup 0KLMN-GW-PW6-0-050310 Low Spike 5 ppb OKLMN-GW-PW8-0-050310 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
C0064518 Spk C COO04518 Spk D
C0064518 C0Q64518 Rep
COOS4519 C006452C C0064521
OKLMN-GW-PW10-0-050310 OKLMN-GW-PW10-Q-050310 OKLMN-GW-PW10-0-050310 OKLMN-GW-PW10-0-050310
OKLMN-GW-PW10-0-050310 Dup OKLMN-GW-PW10-0-050310 Low Spike 5 ppb OKLMN-GW-PW10-0-050310 High Spike 50 ppb
5500 50500
500 500
500 5000 50000
3670 48500
255 249 258 2980 34100
67 96 51 50 52 60 68
C0064522 Spk 00064622 Spk F
C0064522
C0064522 Rep C0064523 C0064524 C0064525
OKLMN-GW-PW11-0-050310 OKLMN-GW-PW11-0-050310
0KLMN-6W-PW11-0-050310
OKLMN-GW-PW11-0-050310 OKLMN-GW-PW11-0-050310 Dup OKLMN-GW-PW11-0-050310 Low Spike 5 ppb OKLMN-GW-PW11-0-050310 High Spike 50 ppb
5500 50500
500
500 500 5000 50000
5180 51600
319 347 312 4400 36000
94 102
64
69 62 88 72
C0064526 Spk G C0064526 Spk H
C0064526
C0064526 Rep C0064527
C0064528 C0064529
OKLMN-SW--050310 OKLMN-SW-0-050310 OKLMN-SW-0-050310 OKLMN-SW-0-050310 OKLMN-SW-0-050310 Dup
OKLMN-SW-0-050310 Low Spike 5 ppb OKLMN-SW-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5270 52000
124 132 505 5320 41200
96 103 25 26 101 106 82
N o: Sine this summary table how* rounded result*, recovery value* may vary lightly from the values In the raw date.
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Table IV.
Exygen to
Surrogate Spike Recovery of 13C PFOA in Water Samples
Continued
'*C*PFOA
Sample Descriotion
Amount Amount
Spiked Recovered Recovery
(ng/L) _ inoH.
(%)
COO64530 C0064531 C0064532
OKLMN-GW-TRIP2-0-050310
500
OKIMN-GW-TRIP2-0-050310 LowSpike 5 ppb 5000
OKLMN-GW-TRIP2-0-050310 High Spike 50 ppb 50000
494 5520
52900
99 110 106
Average: 83 Standard Deviation: 21
Not: Sine this summary table shows rounded results, recovery values may vary slightly from the values In the raw data.
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FIGURES
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Exygen Study N o.: PQOO1400
Figure 1, Typical Calibration Curve for PFOA in Reagent Water
OXMStC Cnwid W r Hv7.rtb (PFW(t I * ' ItajnMkin o
V * I M n O B * J.3OM (f 1M W 1)
Area, count
Exygen Research
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Figure 2. Extracted Standards of PFO in Reagent Water, 25 ng/L and 50 ng/L, Respectively
XC032U-t - PPOA (Stmrtarrt) 4*$&$&<> Mtmt
2 o f 41 fro 0324O5C.w#
A r r x 44717 ovt/rris H ih jfrt 60 3 3 3 S cf>9 RT: f t 440 ntift
1 1 .0 4
I XCD321W-2 P fOAfSUndirt) 4134010J) *u - anpl 3 f 4im rn 632405C.tf1
fir*a: 7929$ cm **
13708.770 eps RT: H X Tin in
Exygen Research
* .?H : ; ;
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 3. PFOA in Reagent Water, SOng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
A*jg*rca*ninf P PO A ( tto t* o w < lf4 K O f$ 6 9 A ti mv At o ; 5766 c o e s i * H e i g h t 9 9 4 J t 2 epa RT: (1 fff
9 mt*i R o m 03240CCj* W
11J62
c SOOJQO-
0.00 - -- ^ 12
. .. 3 4 B
tpk a WO*(PO4OJ/OI.0 am - sm po 11 trt 4t from Aw; 7WQ3wunts Haight: 10623.T29 ops RT. iMdtmin
......................... > I f >...... .. 7 0 9 10 t1
Tim*, min
i 12
I ni I -- I* ..................................y 13 14 16 10
17
<* 1.3 ao.
f " 600 4
f
aoo
1 2 9 4 6 8 7 8 9 10 11 12 13 1 4 16 17
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.
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Figure 4.
Chromatogram Representing an Oakdale Water Sample Analyzed for PFOA, DF=1O0 (Exygen ID: C0064522, Data Set: 032405CR)
C00G4B22 * PFO*
9<rw- 9 n p f 39 ofG7 from Q&40SCX.wiW
Am * ;979794eow rfo Height 7f6G-l49qp* RT: 1120 min
11.92
Intensity, cpg
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Interim Report #1-Analysis o f Oakdale Water Samples
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Figure 5. Typical Calibration Curve for 13C PFOA in Reagent Water
032ec G r o u n d J ^ r d D
tP*0^ "* * * ^ * ^ * O
f ml.31**CO*Jn-OiC3*l O' " M W )
Arta, counts
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 6. Extracted Standards of 13C PFOA in Reagent Water, 25 ng/L and 50 ng/L, Respectively
I XCC3SU>0-1 - i3CPFGA {S1ndwn)}4i5,0J37O.C ***tp*2of*1fnMC3240l5C-W>W Are: 33102 c-outfit Height 6<999.<13 OP* RT: i 1JSO min 0000-i 4000' 3000 20001000-
11.86
Intensity, cps
12 3 4* 6 78 9 Tim *, min
XCWJ100-2 - t X FFOA&tvvr) 410JV379S>amu samp* 3 of 41 from 932409C.*ff 08017 o*unt* HaiQhl; 1H30.466 cp* RT; 1148 T
10
Hi
12 13 1 4
1 16 17
11S&
intensity, cp s
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Interim Report #1-Analysis o f Oakdale Water Samples
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Figure 7. 13C PFOA In Reagent Water, 50 ng/L Fortified Reagent W ater, and 500 ng/L Fortified Reagent Water, Respectively
fto a g * in C a r i n i fJC P P O A (U ftto m o m ) AW.tUSTQX) a m - s a m p t* a < *44 fr o m Aro: 311 CW<19 HoiQht 36.06400* A7: 1tM4nri*
*&
| RMOtft S*cA - tJC R F[W (Q C)413iW P mw - s a r* * 10of 41 from fi024&6Cjji<1 A ;W ? 9 9 c < u *s Hwght: 106407:3 p RT: 11*23 mm
1 0 0 .6
ao
540*4
0X0 1 2
3 5 7 0 fl 10
Tim, min
| R*acSi* 5J-. 13C0 FFFFOQIA<CK^4lSJV3700arrw: fiiryl l1of 41 fiomMMMCjYW
* * i; 12966 amt* HMBht: 2 0 *) 1 cps RT;1LM3mto
If
12 13 14 15 16 1?
20*5 M&4
if*a <eo5
I
8 0 to 11 12 13 14 16 16 17 Tim*, min
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Interim Report #1-Analysis o f Oakdale Water Samples
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Figure 8. Chromatogram Representing an Oakdale Water Sample Analyzed for 13C PFOA (Exygen ID: C0064522, Data Set: 032405C)
C0064622 >13Cf>FQA iUitkJtomr)Al5jOi37O
mompim23 o f 41 toom0324Q5C.wW
A r w 4U9C3 oott/rto
7M12 ofi* f t T. H . 5 3 TM
<1A5
intensity, cps
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Interim Report #1-Analysis o f Oakdale Water Samples
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Figure 9. Typical Calibration Curve for PFBS in Reagent Water
BMBCRGlwrrfUatvRlwIiUb OFFBSE ~UnW Rr5<Mi (1 t r
f * 13
IM ST)
Area, counts
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Interim 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
. pFSS{S1*tf9ni)299JH9$.0irm/-wn/U9 2vfe7thm*Xi24Q5CR.w*7
wx//ris H tiht
op* ftT; $307 mitt
3.01
t Riandar) 2B0.9i04> w m Mnpfe 3 *wn MWCft.wff 772? w e r H i& t; M .M fitp t FT;3*54flfe
33
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Interim Report #1-Analysis o f Oakdale Water Samples
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Figure 11. PFBS in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
0knotfotmtf)Reagent Control PFBS fiJn kn e3 9 & J)/9 Q .O tm u -ta m p k 9 o f til front Q3240GCP.*ilt
mj
Intensity, cpe
Intensity, cps
3.66
tpk 9 rr $ coq>M jm m j smu * an* 11 rf I? *wn
r u : '96163 c*wi
12O0.$4t c|kf RT:3J17iw >
3JB2
T im *, min
1 1 3 4 i " 0 7 9 10 Time, mift
11
13 14 16 18 17
Intensity, cps
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Interim Report #1-Analysis o f Oakdale Water Samples
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Figure 12. Chromatogram Representing an Oakdale Water Sample Analyzed for PFBS, DF=100 (Exygen ID: C0064S22, Data Set: 0324O5CR)
OJ064G22
fifithnotmj 299JM99 0 - sumpi*
/j* ?7S oovrf*
iffl.4 0 0 op* RT- 3.924frilit
32
t/6 7 fttM f Q324&SCX.mfT
intensity, cp s
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Interim Report #1 -Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 13. Typical Calibration Curve for PFHS In Reagent Water
0M4MC Omwd M u r
`Umm'
+OAOIOI f-O M )
i , r. * . p
Exygen Research.
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 14. Extracted Standards of PFHS in Reagent Water, 25 ng/L and 50 ng/L, Respectively
XC03210Q-1. PFHS {Stlrtir*ta}3$& .0fd0.0 u m / M#npi9 2 o f 41 frotnQ3JM09Cjmtr
Art:
M tbtftt 1440.74? cp* XT: iG.Ste mkr
10.
10
Exygen Research
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Interim Report #1-Anaiysis 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
RMOMtCoff; ntd/bvird)
jm p f 9 o t * 1 from 0 3 7 -K n C .\rU r
40-
a0
20-
C
1a> A f l f 3! 1 ^
3.29
ii , i * l i f
f
12 45 79
I k m f u t Sfk A- PfWS
ifm off*I 10of *41ftwnttMOSCjiM
A te :2d148ceunts Hai8ht:M22.1d2op9i R?: 10.594 nife
1.4
11.79
9 1 firn*, ntsfi
It
12
13 40
2TO 13
,1 0 2 0 14
iM
1 17
I ta M Spk 9 - PFHS (QC)399.1W80.D mu-sam p* II 841 *omKW9C.M A*r.23Sei9oa**ff MogM: 30774.(M om RT:.6Kmfe
Q. 2-0*4
1-0*4
0X>
Tim. min 10.01
Tim*, rfiin
Exygen Research
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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=I00 (Exygen ID: C0064522, Data Set: 0324O5CR)
C9064B22 - PFHS i m j; 5 7 *5 4 eoitflU
a** -
36 4 f6 7 ittuw 2 4 0 5 0 ? .
2339.95 C f* * 7 ; J 0J&3 miff
1 0 .3 8
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figure 17. Typical Calibration Curve for PFOS in Reagent Water
02M0JC Qrouod
(FfC t> ,T>Mr^R*srtiw (1 / x*waghriao): y 311 a 971*'0D3t* PUBM)
Afea, counts
Exygen Research
Page 59 of 110 0000S2
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
Intensity, cos
XCmatOtt - PF09
4W.OWa v n e - sampfe 1 of 4! tw n aa 4 C j itf
Atm; 20033oout* H*ight: 2520.702 qw RT: 12.83$
Intensity, cp s
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Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Figure 19, PFOS in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
Jfrfcpnf Cow* -PFOSfUAHmuxr}460.0*0.0 jwnr
r+s: *0 *4 0 ow H *
87: 2.819 m #
9 of4t
0334O6Cwiff
12.02
VVVy
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Interim Report #1-Analysis o f Oakdale Water Samples
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Figure 20. Chromatogram Representing an Oakdale Water Sample Analyzed for PFOS, DF-100 (Exygen ID; C0064522, Data Set: 032405CR)
In ten siv, c p s
C 0 0 & 4 6 2 2 P F O S f lJ fth m 4W.CM0.0 m m u -
3 6 C /B 7 from 0324OQC& .
Mf : 15Q7G& 0OM & W #^* & 3 3 J H
AT/ J 2 3 min
woo5500-
5000
4500
4000
3600
0000-
2300
2000-
1300
1000-
soo
ol
Tim, min
12.14
1ZI
Exygen Research
)
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Exygen Study No.: P0001400
APPENDIX A
Study Protocol P0001400
(Exygen Study No. P000I400) with Analytical Method: V0001780:"Method of
Analysis for the Determination of Perfluorooctanoic Acid (PFOA) in Water
by LC/MS/MS"
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