Document 6R5X1y0OJbrQ5120DbQqqa2am
AR226-3636
INTERIM REPORT #1 Analysis of Oakdale Water 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 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 0236-01-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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Interim Report #1 -Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT
Exygen Study Number P0001400, entitled "Analysis of Perfluorooctanoic A dd (PFOA), Perfiuorobutanesu1fonate (PFBS), Perfluorohexanesulfonate (PEHS), and Perfluorooetanesulfbnate (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
Date
5f a j t K Date (
tr h \a s
Date
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Exygen Study No.: P0001400
QUALITY ASSURANCE STATEMENT
Exygen Researches Quality Assurance Unit reviewed Exygen Study Number P0001400, entitled, "Analysis o f Perfluorooctanoic Acid (PFOAJ, Perfluorobutanesulfonate (PFBS), Perfluorohexanesulfonate (PFHS), and PerfluoTooctanesulfonate (PFOS) 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 Studv 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
Lydia/Shaffer Technical Lead, Qual: Assurance Unit
a sh fits
Date
1Note: All inspections will be documented in the QA statement for the final analytical report at the conclusion o f the study.
Exygen Research
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CERTIFICATION OF AUTHENTICITY
This interim report, for Exygen Study Number POO014OO, 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:
Robert A. Paschke Manager, 3M Corporate Environmental Programs
Exygen Research
Date
Daft^
41
Jo lo s
Date
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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:
P0001400
EXYGEN STUDY NUMBER: P0001400
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 St. Paul, MN 55144
STUDY DIRECTOR:
Jaisimha Kesaii PJE,,, 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 of 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
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Exygen. Study No.: P0001400
TABLE OF CONTENTS
Page
TITLE PAGE..................................................................................
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 of PFBS, PFHS, PFOS and PFOA in Water Samples..... ........................................... ............. .................. ........................... 22
Table n . Matrix Spike Recovery of PFBS and PFHS in Water Samples..................... 24
Table IU. Matrix Spike Recovery of PFOS and PFOA in Water Samples.................... 30
Table IV. Surrogate Spike Recovery of 13C 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 of 13C 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 ,3C 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: 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 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
Page
Appendix A
Study Protocol P0001400 (Exygen Study No. P0001400) with Analytical Method: VO00178O;"Method of Analysis for the Determination of Perfluorooctanoic Acid (PFOA) in Water by LCZMS/MS" ......... ...................................... ................................................ 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 perQuorooctanesulfonate (PROS) according to .Exygen Method V0001780 (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 of PFOA, PFBS, PFHS and PFOS in water samples were 93% 19, 141% 21, 96% 15 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 of 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 PG001400 (Appendix A).
3.0 INTRODUCTION
This report details the results of the analysis for the determination of PFOA, PFBS, PFHS and PFOS in water vising 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 ED 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 of 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 Coiporation 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
Exvgen InventofvNo.. , Lot#
SP0003&00
23116HB
SP004184 ; v 3507-195
SP0000252
101 - ,
SP0002401 :: , SE036
SP0002694
430180-1
Puritv (%) 97.64 97 , 96.7 98.6 101.2
Expiration 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:
13C PFOA Chemical Name: 1,2-13'C perfluorooctanoic acid Molecular Weight: 416 Transition Monitored: 415 -->370 Structure:
O
13C \ OH
PFBS Chemical N ame ; Perfluorobutanesulfonate Molecular Weight: 338 supplied as the potassium salt (QFgSOjTC*) Transitions Monitored: 299 -->99 Structure:
FF F S03
F FF
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PFHS Chemical Name: Perfluorohexanesulfonate Molecular Weight: 438 supplied as the potassium salt (CgF^SCbTO Transitions Monitored: 399 -- 80 Structure:
FF F
PFOS Chemical Name: Perfluorooptanesulfonate ' Molecular Weight: 538 supplied as the potassium salt (CgFiySOaTC4) Transitions Monitored: 499 - 80 Structure:
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 Cis SPE cartridge conditioned with 10 mL of methanol and 5 mL of 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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T
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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 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
(ng/mL)1
(pL)
(mL)
0 0 40
10 100
40
10 200
40
10 400
40
100 100
40
100 200
40
100 400 . . 40
1o f PFOA, 13C 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 of LC/MS/MS Instrument and Operating Conditions Instrument: API 4000 Biorrtolecular Mass Analyzer
Interface: Turbo Ion Spray Liquid Introduction Interface
Computer: DELL OptiPlex GX400
Software: WindowsNT, Analyst 1.4.1
HPLC:
Hewlett Packard (HP) Series 1100 HPQuatPump HP Vacuum Degasser HP Autosampler HP Column Oven
HPLC Column: Thermo Fluophase RP, 50 mm x 2.1 mm
Column Temp;: 30 C Injection Voi.: 15 pL Mobile Phase (A): 2 mM Ammonium Acetate in water Mobile Phase (B): Methanol
Time (mini 0.0 1.0 8.0 r. 10.0 11.0. 18.0
Total run time: ~18min Flow Rate: 0.3 mL/min
%A T 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) -12 min.
~12 rnin. ~ 12 min. ~5 min. ~11 min. ~13 min.
6.6 Quantitation and Example Calculation
Fifteen microliters of 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 fag/L'i - analyte in control (ng/L)) 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) = IT170161 -262001 x 100 1330
From equation 2: % Recovery
= 86012 ng/L*
= 86012 n s /L - 37600 ne/Ll 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 duplicate o f the primaiy 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 13C PFOAwas 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, t3C PFOA levels were adjusted to require the same dilution as the other analytes.
For each primary sample collected, between die,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 of 70-130%. Because laboratory control spikes for 13C PFOA were acceptable in every set, instrument washes were free of 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 he 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 HI. 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 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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Table I. Summary of PFBS* PFHS, PFQS and PFOA in Water
Enyflen ID
C0064404 C0064404 Rep
C0Q64405
C lien t 3arrvp!s ID
OKLMN-GW-W3-0-050310 OKLMN-GW-W3-O-O5Q310' OKLMN-GW-W3-0-050310 Oup
Samples
Analyte Found (ppt, ngIL) C4 Sulfonate PFBS C6 Sulfonate PFHS C8 Sulfonate PFOS
312 162 4750 296 160 3350 . 303 159 3190
CB Add PFOA
6330 6220 5990
C0064408
OKLMN-GW-W8-0-050310
57.0
ND
59.0
290
000644408 Rep
OKLMN-GW-W8-0-D50310*
63.8
ND
55.7
275
C0064409
OKLMN-GW-WB-0-050310 Dup
60.1
ND
56.3
284
00064412 C0064412 Rep
C0064413
OKLMN-GW-W264WJ50310 CKLM N -GW -W 26-0-050310* OKLMN-GW-W28-0-050310 Dup
73400 75700 71400
222000 244000 214000
13500000 14400000 12200000
79300000 70200000 71800000
C0064418 C0064416 Rep
C0064417
O KLM N -GW -W 33-0-050310 OKLMN-GW-W33-O-O50310* OKLMN-GW-W33-0-050310 Dup
26800 28800 28500
92300 84600 81600
4610000 4870000 4540000
1750000 2020000 2790000
00064420 C0064420 Rep
C0064421
OKLMN -GW-W205-0-05Q310 OKLMN-GW-W205-0-050310* OKLMN-GW-W205-0-05Q310 Dup
8260 8000 7650
6740 6610 7070.
146000 119000 116000
147000 150000 156000
C0064424 C0064424 Rep
C0064425
O KLM N -GW -W 215-0-050310
OKLMN -GW-W215-0-050310' OKLMN-GW-W215-0-050310 Dup
801 81.2 75.8
769
37100
4400
256
27000 .
3510
270
36900
4070
C0084428 C0064428 Rep
C0064429
OKLMN-GW-W2D10-0-050310 O KLM N -GW -W 2010-0-050310* OKLMN-GW-W2010-0-050310 Dup
ND ND ND
ND ND ND
ND NQ ND; ND ND ND
00064432 C0064432 Rep
C0064433
O KLM N -G W -FW 7-0-050310 OKLMN-GW-PW7-CL050310* OKLMN-GW-PW7-0-050310 Dup
4460 4340 4630
4800 . 5080
5030
71600 67600 : 72400
37600 38400 38200
C0064436
OKLMN-GW-TRIP1 -0-050310
ND
ND
ND
ND
C0064442 C0064442 Rep
C0064443
OKLMN-GW-PW8-C-050310 OKLMN-GW-PW8-O-O5031Q* OKLMN-GW-PW8-0-050310 Dup
13300 14100 14100
23SOO 23900 23000
34300
35600 33400
61400 80600 58500
C0064446 00064446 Rep
C0064447
OKLMN-GW-PW9-0-050310 OKLMN-GW-PW&4M)50310* OKLMN-GW-PW9-0-050310 Dup
2110 2140 1930
5160 5000
5140
64400 84900 > 88600
49000 46700 46900
00064450
C0064450 Rep C0064451
O KLM N -GW -W 6102-0-050310
OKLMN-GW-W6102-0-050310* OKLMN-GW-W6102-0-050310 Dup
NG
53.5 NQ
ND
ND ND
NQ 214 NQ 226 ND
C 0064454
C0064454 Rep 00064455
OKLM N -GW -W 6104-0-050310 OKLMN-GW-W8104-0-05031Q* OKLMN-GW-W6104-0-050310 Dup
NQ
NQ 51.2
ND
ND ND
109 207
125 189 118 184
C0O64458 C0064458 Rep
C0064459
OKLM N -GW -W 6201-0-050310 OKLMN-GW-W6201 -0-050310* DKLMN-GW-W6201-0-050310 Dup
74.0 74.t 78.0
ND ND ND
NQ : NO NQ
95.5 88.3 132
C0O64467 C0064467 Rep
C0O64468
OKLMN-GW-W2Q-O-C50309 DKLM N -GW -W 20-0-050309* OKLMN-GW-W20-0-050309 Dup
13600 10700 10000
12900 9040 7860
46*300 : 36300 30100
285000 243000 190000
C0O64471 C0064471Rep
C0064472
OKLMN-GW-W22-0-0503D9 OKLM N -GW -W 22-0-050309* OKLMN-GW-W22-0-050309 Dup
36600, 32200 37500
31400 29500 25700
45800 34000 28100
317000 301000 244000
' La b o ra to ry D u p lica te ND = Not detected at or above 25 ng/L.
NO * Not quantifiable =Measured concentration between 5 ng/Land the Limit of
Q u antltaB o n (LO Q ) w h ich is S o n g /L.
Exygen Research
Page 22 of 110
000045
Interim Report #I-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table I.
& yan ID
Summary of PFBS, PFHS, PFOS and PFOA in Water
C lie n t Se m ole ID
Samples Continued
Anatyta Found fppt; ng/L] C4SulfentPFBS C Sudori* PFHS C Sulfonate PFOS
C8 Acid PFOA
C0D64475
C0064475 Rep C0Q64476
OKLM N -GW -W 31-0-050309 OKLMN-GW-W31-0-050309* QKLMN-GW-W31-0-050309 Dup
1300 1380 1360
5130 4760 5190
132000 132000 156000
23100 22300 24900
C0064478 CQ064478 Rep
C0064479
OKLM N -GW -W 32-0-050309 OKLMN-GW-W32-0-05Q309" OKLMN-GW-W32-0-05Q309 Dup
2180 ` 2290 2960
3000 3120 2940
47100 44400 83000
117000 93300 125000
00064432
OKLMN-GW-W217-0-050309
ND
- ND
NQ
NQ
C0064482 Rep
OKLMN-GW-W217-0-050309*
NO -.
ND
NQ
NQ
C0064483
OKLMN-GW-W217-C-O50309 Dup
ND
ND
128
NQ
0006448$ C0O64486 Rep
C0064487
OKLMN-GW-W2OO8-O-O5O3O0 OKLMN-GW-W2008-0-050309* OKLMN-GW-W 2008-0050309 Dup
6780 7170 ' ; 6930
10100 10800 10300
15500 17800 18800
58300 58700 60300
C0064490 C00644SO Rep
C0064491
OKLMN-GW-W2012-0-050309 OKLMN-GW-W2012-0-05Q309* OKLMN-GW-W2Q12-0-06309 Dup
2210 1960 1920
4700
4470 ' 4420
117000 118000 139000
48900 46400 51400
C00B4484 C00644S4 Rep
C0064495
OKLMN-GW-W80-0050309 ' OKLMN-GW-W8O-O-050309* .
OKLMN-GW-WS0-O-05Q309 D l*i
ND ND ND
ND ND ND
NO 302 ND 280 ND 328
00084498 C006449B Rep
C00644B9
CKLM N-GW -PW 1-0-050310 OKLMN-GW-PW1-0-050310* OKLMN-GW-PW1-0-050310 Dup
5620 5650 5580
4160 . 4160 4170
66900
71600 70900
37300 39300
39100
C0064S02
OKLMN-GW-PW2-0-060310
$41
' 501
351 3630
00084502 Rep
OKLMN-GW-PW2-0-050310*
624
401-
383 3880
C0064503
OKLMN-GW-PW2-0-050310 Di*)
894
700
303 5160
C0064508 C0064508 Rep
C0064507
QKLMN-GW-PW3-O-05O31O OKLMN-GW-RW3-0-050310' ; ' : OKLMN-GW-PW3-0-050310 Dup
6970 6740 6570-,
10000 - . 9740
9990
32700 25500 32300
177000 160000 176000
C0064510
C0064510Rep C0064511
OKLMN-GW-PW4-0-050310 OKLMN-GW-PW4*0-050310* ' OKLMN-GW-PW4-0-050310 Dup .
8130 7700 7810
7890 ; . . 7480 .
7550
33800
30300 27800
72100 67800 65900
C0064514 C0064514 Rep
C0064515
C0064518 C0064516Rep
C0064519
OKLMN-GW-PW6-0-050310 OKLMN-GW-PW6-0-050310* '... v; OKLMN-6W-PW8-0-050310 Dup ;
OKLMN-GW-PW10-0-050310 OKLMN-GW-PW10-0-050310* . : OKLMN43W-PW10-04)50310 Dup
7930 8000 8130.
13100 12700 11900 , ,,
14500 14600 14600 ;
29200 27400 -, 28800
90000 86000 85400
1400000 1760000 1740000
78400 78700 78500
719000 781000 614000
C0064522 C0084522 Rep
C0064523
O KLM N -GW -PW 11-0-050310 OKLMN-GW-PW11-04)50310* . OKIM N-GW -PW 11-0-050310 Dup
6520 6490. 7150. -. ..y
8820 10000 9050
40800 50800 43400
,.
60300 71600 60600
C0064526 C0064528 Rep
C006+527
OKLMN-SW-0-050310 OKLMN-SW-0-050310* o f OKLMN-SW-Q-050310 Dup u>'.
NQ NQ i; . . NQ
NQ
NQ NQ
1190
1200 1270
491 529 537
00064530
OKLM N-GW-TRiP2-0-050310
ND
ND
ND
ND
'Laboratory Duplicate
NO = Mot detected, at or above 25 ng/L. NQ * N otquantrfiabia = ^ su r d co n ctn tfa tQ n t tw 6 n 2 S n g /La n ijth e L riiit crf
Q uantitation (LO Q ) which is 50 ng/L.
Exygen Research
Page 23 of 110
00004
Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table II. Matrix Spike Recovery of PFBS and PFHS in Water Samples
Sam ple . Oeecrfpde
Amount! Spiked in a li
C4 Suttonale P F B S
Amt Found Amount
In Sam ple Recovered Recovery
Ino-)
inm u
m
Amount Spiked
C l Sulfonate PFHS
Amt Found
Amount
hi Sample
Recovered
fngfL)
CnBflJ
Rwv<*y <*)
OKIMN-GW-WW MBOMO {COOftUMSpit CtW ngflLU b Splks)
OKLMN'GW-VW-O-O&KHD ICC0W4C4 S j* 0, 50000 nflfl-Leb Spike)
OKLMN-GWW3-0-05C310 la w Spike 5 ppb fCQCet-fQft.H npl. FteMSpike )
OKLMN-GW-W3-0-35031D High S p lk eS O ppb (000*44*7, aoooon fL rWte Spike >
5000 50000 5000 50000
312 312 312 312
6980
133
67400 ' 134
7450 74700
143 149
5000 soooo 5000 5DGO0
163 162 102 182
5130 47500 5140 54400
59 SS 100 10e
O K LM N -CW -W I-0-O 50310 (CD0044WSpk E, 5000 ft^/LU& Spike]
OKLMN-OW-W5-0-050310 (COOM4M SpftF. awMflO^UA Splkal
OKLMN*OWAW-C-WD31iJ LOW S p ik e B ppb (C00M410,9000 n9IL FleW Spike)
OKLMfWW-WB-d-OSOaiO High Sp ik e 50 ppb (00364411, WOOng*. FWd Spike f
50G 50000 500C 50000
57.0 57.0 57.0 67.0
7020 70000 7410 70500
73 5000 140 50000 147 5000 141 50000
ND MJ ND ND
5120 51400 5510 53300
102 103 110 107
OKLMN43W-W25-0-050310 (C0MU128kS.tKW n ^ U b Spike)
O K LM H -G W -W 2W -0$031C (C00U412 Spk h,, SWW RtfL U b Spi|
O K U 4 N 'OW-W2S43-050310 L o w S p ik e 5 ppb (00654414s 8100 ng/L Field Spiki)
OKLM H-3W .W 2i-D-O M J10 High S p ik e SC ppb (CMK441S. BCObOn&l FMd 3p*e )
5000 aOCOO 500C 60000
73400 -
73100
73400
125000
73400
73200
73400
147000
*'
500C
222000
103
50000
222000
.
500
222000
147
50COO
222000
207000 252000 210000 266000
<
OKLMM-GW-WA3-0-OWS1D (COOM41S Spk l, SOM rtpfLUb Splhe)
GKLM N -GW.W33-O-0S0310 (C0C54416 Spk J. 5000 nga. U b Spike)
OKLMN43W-W13-D-056310 L o w S p ik e S ppb (C06A441I. sew nglL Field Sfjke )
OKLM M -GW -W 334K)M 3lO High S p ik e ppb (C006441S. BOOOOngfL Fliht S p # a }
5000 50000 5000 50000
26600 26600 26 BOO 26600
33600 133000 38700 1C60Cf>
*:
5000
212 50000 - SOOO
102 50000
S2300 92300 92300 92300
78000 122000 65200 150000
59 115
OKU*N*3WAV2D5-04)5C310 (COM4420 Sp*C K, 5000 ng*- U b Spik* >
O KLM N-QW-W205-tW)M31O (CWM420 Spk L, 5 R ffl U b S p k *}
OKLMN*GW*W205*04SQS10 Low Spike 5 ppb {CDOU422.800 ngft. fW d Spile* )
OKLMH-GWJW2C6-W IM J1D h S p k e 56 ppb {C0flW4Z3,500TO <**1. Field Splk* }
500Q 50000 sooo 50000
6260 0280 6260 62eo
15400 72500 15200 82800
143 5000 1Z6 50000 1S soon 149 50000
6740 6740 740 6740-
12500 53100 11600 60600
115 3 11 100
OKLMN~S W*W215-0-056310 (C00S4424 Sfk U, WOOn^L U b Spike )
CKLM N -SW -W 215-0*060310 jCMMtt* Snk N, 50000 ngO. U b Spike)
OKLMN-GW<W21W-OSQ3ie L o w Sp lk * 5 ppb (C0C6442C, StOO F)*Jd Spike >
OKLM H-GW-UV215*0-OJW310 H igh S p ik e 50 ppb ,'CH47, SOOOOft0/L Field SpiXm)
5000 50000 5000,. 50000
601.0 601.0. SC1.C 31.0
7200 67200 . 6720 66SCO
128 133' 118 132
500C 50000 5000 50000
769 769 760 769
5280 50300 5240 ' " 48500 \
90 99 33 95
'San p te residue- exceeds the apiking level sigrklftcantiy: ihwefore, an w cu rtte recovery value canrsol be calculated
ND Notd e U iisd 3* o r above 25 ng0 . (ppt). NQ = Noiquertofable ~ Measured eorcentraben between 25 r/L (ppt) and the Limit of
Quantitation (LOO) which i$.SO n&L (ppt>. Not: Since thfc $wnm*ry table ehowe rounded ru u ltt, recovery value m*y v*Y*ftM ty from the varie in the raw data.
Exygen Research
Page 24 of 110
090^47
Interim Report #1-Analy$is of Oakdale Water Samples
Exygen Study No.: P0001400
Table II. Matrix Spike Recovery of FFBS and FFHS in Water Samples Continued
Sarnph : Detcriotlort
C4 SutfonalaPFBS
Amount Amt Found Amount
Splksd In Sam ple Recovared Recovery
(>m!U
(n an j ...... PM.......
Amount SpMcad
(ton.)
Ct Sulfonate PFHS
Amt Found
Amount
In Sam ple Racovarad
in *)
(ru st)
Recovery m
OKLMN-OW-W2O10-O4SO310 (Ctt6H28SpfcC. SOMft[lLLb SpOut)
DKLMN-GW4W2010-4M)5031 S (CCM42S 3p* D, 3WOO ngft.tab SpiW)
O K U W -W .m i< W IS10 Lo w Sp lk* 5 ppb [COM4,JMU (A FkM Splk. )
0 KUMN-GW-W2 0 1 tMMHSWIO Hfflh Spike SO ppb 100094431.SWObrtgd.n*IS SNIte )
5000 50000 6000 50000
ND ND ND ND
6500 6&5Q0 6700 83B00
132 5000 130 50000 134 5000 128 50000
ND ND ND ND
4800 48700 4700 43700
96 97 94 87
OKUM M-GW-PW?0-6S&310 fC0SS4432Spiee ,9000119ft. UbSpSw |
QKLMN-GW-PW7-0-058310 <COG6*4*2 Spk F, SOOOSng/L tab Spike)
OKLWbM5Vf-PW7-0-C50310 U m S p ite ppb (00094434,3HWnpA. FMd Spike )
OKLMN-OW-PW7-O-O6W10 HfcH S p ft* BO ppb |C009443S,OOOCO ngft.Field Spike |
5000 50000 5000 50000
0KLUN-GW -TRIP1-0-0H31D Low Splfca I ppb {C0W4437,COWogtL Reid S p i* )
QKLMN-GW-TR1P1-0-1W310 High Spike 50 ppb (C009443S,5WO0 atfL Fkid Spike >
500C Scoto
OKLMN-OW-FWfl-0-050310 {CCCW4425okG.5000n.l LsbSpike)
OKUW N-GVMW 8-W S0310 (COOS444S5p* H.WOODr/l Lab Soil )
OKLMN4SW-PW8-0-C5C310 Low Spike 5 ppb (C00W444.3HWnflrt. Fleto Spike }
OKLMN'QW-Mtt4W>5031C High S p lks M ppb (C00S4445.90000 up*. FWd 3pik* )
9000 BOOOQ 5000 50000
0KLW N -6W W 3-0-0S0310 {C0Mi44&ok I, SOOdnotUb Split*)
OKUAN4SW4PW94MM31Q ^esserne spK j. com n^L tb Sp*e )
OKLMN-GW-PWS-O-ti50310 LovrSpIkO Sppb (C0fl6444e,M<* n^neta'S****)
OKLHH-QW -m>-0-060310 High SpUre 50 ppb (C00M44B,so m ntf. ft#!* Spike )
5000 50000 500' 50COO
0 KiJWN-GVV-V*702-<>-050310 0 *0 Spk K, SOObnpT. Lab* )
OKLM N -aW -W fil02'0-5031b (C09S4450Sfik L, 50000 npfU Leb Spike)
OKLMN<lW-W102^-OSO31O Low Spike 5 ppb {C o rn a c 6W0 n^L Fitta Spila >
OKlMN-GW-vyi02>o-05oaio High Spite so ppb ICMS44S3,3WJC0 ntf. Field 8ptt )
5000 50000 5000 50000'
4400 4400 4400 4460
12200 72800 13200 60000
ND 6540 ND ' 44400
13300 13300 13300 13300
21400 79700 21000 80700
2 110 2 110 2 110 2 110
S290 63800 ' 8260 74800
NQ NQ NQ ' NQ
7360 ! .67500
712 70700 !
155 5000 137 50000 175 5000 151 50000
131 5000 89 50000
162 5000 133 50COO 164 5000135 50000
144 5000
134 50000
144 '
000
146 50000
147 5000 135 50000 142 5000 14) 60000
4600 4SOO 4600 4800
ND ND
23300 23600 23600 23800
51 BO 5160 5160 5160 ND ND ND ND
8310 50800 9370 59000 4600 46100
2S70C 70300 30000 76100
9310 64400 9950 54600 4890 47400 5040 50600
90 92 91 106
92 92
118 93 124 105
83 98 64 99 96 95 10 1 10 1
'Sample roeidi^ exceeds thespiking isvsl s^nMcsnUy;therefore, artaccurate recovery value cannot be calculated
NO * Notdetected at or above 26 ngll (ppi).
QuanfrbstkmfLOQ!wfikcfnt.50NQ =Notquantifiable = featured ooocenvefkw between 25 n^t <ppt>and tiielJrrtt of
Note;Sino#this summarytable shows rounded rsiufts, recoveryvalues mayvaryslightly fromtti values Inth raw data.
Exygen Research.
Page 25 of 110
000048
Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table II. Matrix Spike Recovery of PFBS and PFHS in Water Samples Continued
Sam ple D e sc rip tio n
Amount Spiked
C4 Sulfonate PFBS Ami Found Amount InSom pi* Recovaren Reccuety
........... ( " M - l ........M . _
Amount Spfced
(9*L>
C8 S v lfe ite te P n tS
Amt Found
Amount
in Sam ple R ecovered Recovery
(npn-i
(nail.)
no
OKU*N^W -W *fW -e-OSa31b (CtfoMiM 3pk U, 9000 VL Ufo 9<te I
OKUWN-GW-W8RM-9-0M310 (CKHU4H 8pkK, BOOMntfL Lab Spite)
OK LM hi-aw-w*io4-o^>m io low s p u n ,s ppb (COO*, iW ) nj/L Fh*d Spite )
OKLWNXJW-WaifUJKoSOSin H igh S p ik e SO p p b (C0C*US7.96000 ngiL Fl*kj pika \
5000 50000 5000 50000
NQ 6660 m 73000 m ; 730 NQ 69700
134 5000 146 50000 135 5000 139 50000
uo UD
`ND m'
5050 48D00 4720 51200
101 96 94 102
OKLMN-GW-weao-wi-esoMO (CHH4$a SpfcC, WWr>eT-LjbSpJte!
DKLWN-OW-W82O1-0-OSJW10 (C0M4il 3pk 0 .5OW0 npIL U b Spite)
OKlMN<GW<m01>tM)503l0 Low Spike 0 ppb {MQM4M, SOCw l FWd Sf*te >
OKLMN'OW>VW2Q1*(Ml5031fr High Spike 5 pp b (C0064W. SlflO *dTLFiald5pflu )
5000 50000
500 5000
74.0 74 0 74.0 74.0
6560 65500
877 7550
130 5000 131 50000 121 500 150 5000
nd
NO ND ND
4810 44400 543 5300
92 69 109 106
OKt^N-QW-W2CMM)&030B (00094407 Spfc E, 0 0 r0. Uto 3 ^ t e )
0KLMN-GW-W2d-d-0WW (COOM497SpKF. MQQOrtgfL Lab Spite >
OKLMN^GW-WWI-iKISCJO L ow Splk S pp b (C00944, 500* no*. Flriri S p ite)
OKLMN-GW.W20^^5Q3Ci9 High S p ik e 50 p p b {0006470.3DCKM*.*- FUld Spite >
5000 50000 5000 $0000
13900
19400
13-300
77100
13OO
20900
13500 5000
110 5000 126 50000 140 5000 142 , 50000
12900 12900 12900 12900 .
16200 55200 16200 46400
66 65 68 71
OKLMN -GW-W22^-0&050ft (C00e4471 Sp* G, 5000 nyfluLab Spite)
0KLMN-GW*W224WlMi3Di {COO64471 s p k h .80000 r h .u b spite)
OKLN N-CW-W2-<H)&<}3<> l o w SpH 4 p p b (CWW4T4, WOOaq/L FWd Spite )
OKLMN-GW-W2i-O.OM3W High S p H SO pp b (C06M474,50000 npiVFWd Spite )
OKLMN-GW-VMl-a^FSOSO (C60U475 Spk 1,5000 npO. Lab Spite)
O K LM N ^3W -W 3t^J5O SO 0 [C006447S $f^c J s000 ^L UtoSfUte )
O K LM N -O W -m U M jM W High S p ik e 50 p pb (C0094477. 009 n & L Field S pite}
OKU*N-GW-W32-O-&501O9 (COOM47-S Spk K, 3000 n$n_ Lftb Spite)
OKLMN GW-W32-O-&5W0 (CODB447B SpK LSMOOnp/L U b Spite)
OKLN-OW-W i2*0-309 Law Spike 5 ppb (C0064440.03 r*/L FIWSpite j
OKLMN-OW-WMWl-tWW H igh S p ik e SO p p b {CMM4I1, SOW tiftlL FWd Spite )
5000 50000 5000 50000 5000 50000 50000
5000 60000 5000 50000
368Q0 38600 36600 36600
1300 13O 1300 2160 2160 2160 2100
44100 109000 44000 111000
, 500C 31400
145 50000 31400
*
5000
31400
149
50000
31400
6450 70930 90900
143 138 .. 179
5000
5130;
SOOOO 5130
SOCCO
5130
0910 67300 10600 65500
13 5000
3000
130
50000
.3000
172 5000 3000
127 50000 3000
37000 73003 35000 62203 9090 51200 63200 7400 50000 7910 52600
* 63 * 62 7 92 110 66 94 98 100
Sftfnpleresidue BxcaaC& the spiking ierv^t sjgniftcartfty: therefore, an accurate recoveryvalue cannot be calculated
NO * Ntrtdefect^tf oretov*Sng/'L(ppt),
NO Not quantifiable * Measured concentration between 25 n^L(ppl) andlhe UmH oi QuaftUttLort (LOQ) which 50 ng/l {ppt}-
Note; S lnte thi* summary table howv rounded r**uits, reiajvery valuta m iy vary SgbUy fromthe values ki the ra%date.
Exygen Research
CK;
Page 26 of 110
.000049
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: POQ01400
Table II. Matrix Spike Recovery of PFBS and PFIIS in Water Samples Continued
Sample O w riM ton
OKLMN-OW-W2tr-045O3M ICMSMI*SpkM.W ng/Llab Spite )
QKUIN-GW-W217-4-0503 (CM44ft*Spk N, *0000 Ub Spite > OKLMN-OW^V217-0-050306 Low Spike * ppb
tfttOfrUM,9W ng/LField Spite )
OKLMN^W-WSIT-O-oSOSO* HSflh Spike SOppb (CDOMtaS.S0600nfilL FtetdSUw l
OKUUN-GW-W2dOM>4M (CDC444I8Spk 0 .5000ngfl. Lab Spite 1
OK!_MN4W-WtOOa-0-05030* (CMNM4MSpkP, 5COOnpO.Lab Spite) OKLMN-OW-W2&OB4-0WMM lo w Spike 5 ppb
(CM*Ua>Btm ngU FWd Spite ) OKLWN-GWWJOOfi-O-OMMi High Spike 50 ppb
(Cooeail. 6OQ0On/L FMd Spite )
OKLWN-QW-WJOIJ-O-OBOaOB fC0WSp*C,}0<>CoSA.Ui>5eite 1
OKLHN-GW -W 201I445fl30* (CKWMee3p*co, ooooontft. u& Spite |
OKLMN-QW-W20124-0503 Low Spfea 5 ppb {COOM402,9000npft. Flat* Spite )
QKLMN-GW-W2012-04SD3Q Hiph Splice 0 ppb (CDOMW,50000 ngA.Field Spite}
OKLMN-QW-W6O4-0EO3O9 flCWMW SpieS , s m n a fl tab Spite r
OKLMN-GW-W80-04M3C* (OO06UMBpkF, 96000ntfL U p Spite )
OKUdN-QW-WM-O-OSKHH L w Spike 5 ppb <C0MU4M,SOMngft.Rett Spite )
OKLMKJJW-WM-O-05030 High Spike p p b teoo&ur.&o<Honninm spue* )
OKLMN4W-PW14MKW3W (COOPU9I Sfk 6, B00nplLCab Spite)
OKLMN-3W-RWl-0-050310 (COMMAS* Bp* H. 0000n pl Lab Spite)
OKU4N-QW-7W144S036 Low Spike 6 ppb (00004500,4000ngflLField Spite)
OKLMN-OW-PW14460300 HHJh Spike50 ppb [C&OMKM.50400npA.FMdSpBw )
OKLMN.QW-J>VY2-0-050310 (C0M45O2 Spk1.000 Lab Spite )
OKLMN-GW-PW2-0-050310 (CftOM023f* 00W nrt.Lat>Spite >
OKUAN-W-FWJZ-O-OWSID Low Spike 5 ppb (C&M4504, SIX npiL Field Spike)
OKLMN-aW-PW2-<Mii03'IO High Spike SO ppb {CMMttS. S0OO0D0IL Raid Spite )
C4 Sutfoneto PFBS
Amount Amt Found Amount
Spiked in Semple Recovered Recovery
(n fl'L) (h0L)
in tfL )
.<*>
Amount Spiked
(iwM-i
Ct Sulfonat* PFHS
Amt Found Amount
In Sample Recovered Recovery
tnfl/L)
<n#rt.)
... m
5000
ND
6660
134 5000
ND
48BO
98
.50000
ND
66800
134 50000
ND
48500
93
. 0 0
ND
7570
151 6000
ND
4590
92
50000
ND
71200
142 50000
ND
51300
103
5000 50000 5000 50000
6780 6780 780 6780
14300 73800 16500 67600
150
SOOO
10100
134
50000
10100
194
SOOO
10100
162 50000 1Q100
18000 56500 16300 64BOO
1TB $3 184 109
,,5000 50000 5000 50000
22 W
SflOO
2210. ! ew oo:
2210
8210
2210
71500.
T32 .. SOOO
4700
128 50000 4700
120 5000 .. 4700
138 ' 50000
4700
8140 46600 SOSO 53800
35 84 65 S6
5000 500 5000 50000
WD ND ND ND
8860
137
647D0. 125
7390
140
697D0
139
5000 5000C 5000 50000
ND No NQ ND
4980 46200 5200 46200
100 92 104 98
sooo
5620 13600
50000 5000
5620 5620
72CXX1 13100
50000
5620
sooo
641
50000
641
500Cr ` 641 >.
50000
641
69700! .. '
7720
85900
7030
64300
160 133 150 128 142 131 126 1Z7
5000 50000 5000 50000 SOOO 50000 5000 50000
4160 4160 4160 4180 , 501 501 501 501
6360 2000 7690 47700 5260 47700 5190 44300
S4 9$ 71 87 95 94 94 sa
'Bam pitt residue exceeds the spiking levol sig n ific a n t: therefore, en accorale recovery value,ca rro t be calculated
ND * ^k#Ctetela*<1^tor^^)cv25r>9M PPfr NQ * Not quantifiable h teyred COncentraUon between 25 ng/L(ppt) ancf tha Lim it of
OuBrrtitatkxi (LOQ) vhich la 50 oqA. (ppl). Not: Sine* the* untmary table chow* rounded result*, recovery value* may very from the value in tha taw data.
Exygen Research
Page 27 of 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 Deeciiptto
OKLN-(3W-PWa-tJ-TO031O (0006*90So*K,9000ftfifLLed Spike)
QKLKN*GW-FVW-iM)W310 (CO.3pku *00 n9fl. U b Splkt
OKUHN-QW'Wa-O'WOaiO Low 8plke 5 ppb {ConttM , woo ngflLReid Sjxt* y
OKLMN-GW-PW3-0-0W31& HfflhSptke 50 ppb {Coowsoa $00900*- Field Spike)
C4 Sulfonate PFBS
Amount Amt Found Amount
Spiked in Sample Recovered Recovery
W4
fnoiU
(%)
Amount Spiked
m
C6 Sulfonate PFHS
Amt Found Amount In Sample Recovered
tn a iL)
Recovery
5000 soooo 5000 50000
9970 6970 5070 6970
13600 98900 1.5200 92300
137 5000 10000 180 50000 10000 165 5000 ' 10000 171 60000 10000
13800 6440C 16300 54900
72 8 126 9C
OKLM N-GW*PW4*8-0&0310 (C0 4i 1 l SpkM,5004nofl-Lab Spike 5
QKUflN-GW-fW4-IWSa3tO (COCWiic StfcN. 86900natl U b Spike)
OKLMN-QW-FW4-0-0M310 Low Spite 5 ppb (C00MS12,$000ng/LField Spike )
OKLMN-GW-PW4-Q-U50310 High Spice 50 ppb (CWWIA wwcpiu fWd 9p(k)
5000 50000 5000 50000
9150 9130 *130 8130
17400 95000 18300 96900
185 5000 7890 174 50000 7890 163 5000 7890 162 50000 7690
13900 53600 13500 58200
120 S1 112 101
OKLMN-GW-PW9-tLOWS10 4C0A64M4Spk0. DOnffl- U b Spite)
QKLMN4?W-FWIMM)50310 {CO064514Spk P.40000 n&.U b Spike)
OKLM N*GW*PW8-0-050310 Low Spite 5 ppb (C0C44514.9000ngil Ft*W Spike)
OKLMN-^W-PWfi-O-OOOStO High S p ite SO ppb (COOW17,50000 ngO. Field Spike)
500C 50000 5000 50000
7gao . . 17200 793C 90500 7930 17100 7930 94600
185 5000 14500 166 50000 1450Q 183 5000 14500 173 50000 14500
20600 5S300 20800 594QC
122 $3 126 90
OKLMN-GW-PW104L0W310 (C0W4314 Spk CrSDOQn p l U b Spite l
OKLM N-GW -PW 104-05031C (C0OO4M-9Spk &, SOMOnpfi. U b Spike)
OKLMM-GW-fW104M60310 Low Spite 5 ppb fCDOeeiZtL,8DCHJnpfL FW4 Spike )
OKLMNH3W-W10-0-C5C31G High Spite 50 ppb (COOMSaLSO0OOng/LfWd Spite )
5000 50000 5000 50000
13100 13100 13100 13100
19300 70700 19000 74000
124 5000 29200 133 50000 29200 118 5000 2920C 12 2 50000 29200
34300 71000 33500 71300
102 34
88
84
OKLMN-GW-PW114LWW10 {COT045ZZSpkE, 9000r>gfLU b Spike)
OKLMN-GW'PWH-O-OKJaiO (C0004522 Spkf ,0000ng/LUb Spike)
QKLMN43W-PW11-0-&50310 Low Spike 5 ppb {C0M45&KAd n<AFM4 Spite )
OKLM N4JW-PW11*0-050310 Hfgh SplkoWppb (CM4S2S. SOWOno- Field Spite)
5000 50000 5000 50000
520 5520 520 9520
1Z700 66300 13200 63800
124 5000 S8ZO 124 50000 6820 134 5000 8820 114 50000 8820
14200 55100 13300 54800
106 93 90 92
"Sample residue exceeds the piking level signifcarfty; teretere, an accurate recovery value cannot be cateuieted
NO Not detected at or aiywe 25 r ^ l ippi)NQ = Not gyeniiieb)e= Measured concentration between 25 <ppri) and the UmH of
Quantitation (LOG) which h SO ng/L (ppt). IM k Since thleaunwnery table chow rounded reeut, reccviry valL*rniy very IlgTrtiy bomthevalue Inthe rawdata.
Exygen Research
Page 28 of l l O
000031
interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table II. Matrix Spike Recovery of PFJBS and PFHS in Water Samples Continued
Sample . . . Description
CtSulfoiuttPFBS
SuMcnataPFHS
Amount Amt Found Amount
Amount Amt Found Amount
Spiked In Sample RMovured Recovery Spired In Sample Recovered Recovery
w w u (ngJL) p y ....... (non.) fmrt.)
i*>
OKLMM-SW^-050310 <CtWiSpfcQ, 000 ilpt U b &piW*)
OKt_MN^W-C-060310 (coousae sr* h, mmo u b fie)
. OKLMN-SW-0-06Q310 U rn Spike Sppb
(COOtHtO,
)
QKLMN-SW-fi-OKmO Htflh Spike 50 ppb (C0MM329, *H htf/LFkld Spilt)
5000 50000 5000 50000
NQ NQ NQ NQ
5800 63600 7260 65000
120 5000 126 50000
NQ NQ
145 5000
NQ
130 50000 NQ '
4700 45100 5250 40400
90 90 105 99
OKLAIN<IW-TR1P2-0-OW310Low Spike 5 ppb (CflOSMW,6000 ntfL Splk*)
OKUdN-QW-TRiP2-<KJfi03io High Spike 0 ppb fCOWtfSi, Moao n^n/Splk,)
500C 50000
NO NQ
4480 20100
90 5000 59 50000
NO NO
4970 49000
SB SB
Average: Standard Deviation:
141 21
'Sample residue exceeds the pikinglevelSlgrlficarriv, therefore. an accurate tecovery value cannol be calculated MO * Motselected el or above 25 rg/l (ppl). NQ * Not quenttflable * Measured concentration between25 np/L (ppt) and the Limit of
Qoarwtafiorv(LOG)which te60 og/t (ppi>. Note; Since thl* summary uWe show rounded reeuh*. recovery value* may varyallBlrtty
from the value* In the 1 * date-
Average: Standee Deviation:
SB 16
Exygen Research I
Page 29 o f 110
000052
interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table III. Matrix Spike Recovery of PFOS and PFOA in Water Samples
Sample Description
CBSulfonate PFOS
Amount Amt Found Amount
Amount
Spiked in Sample Recovered Resovwy Spiked
("s'L) w
.. <no/L)
[% ) "Vi
CSAddPFOA
Amt Found Amount
in Sample Recovered
(non.)
"V)
Reeovay (%)
OKLMN-GW-WWJ-OSWIO {CDM44MSpk C. SOMntfL Ub Spike )
OKLMN-GWAV3-C-C50210 (CDM44D4SfkD. 5MOOnpfLUb Spike)
OKLMN-GW-W3-0-050310 Low Splk*5ppto (CW44PL$0001)01 Relit Spikfr}
OKLMN-GVV-VV3-MJ5W10 High Spike 50 ppb CMM4407,SOOMitsIL wdpc* I
5000 soooo sooo 50000
4750 4750 4750 4750
12400 73500 10800 84500
153 5000 13a 50000 123 5000 160 50000
6330 8330 5330 8330 .
11900 59200 9470 40100
111 106 83 80
OKLM^lAMWS-0-050310 (CM44M3<*e, MOOgiLLab Spike}
OKLMl*GW-WB-0-050310 (COOS440S8ekF.5W04fliJJi.Ub Spite)
OKU*fK5W-Wfl-04)$03l0 Low Spike 5 ppfa (C0M4410, M0*tLFlemSfrfk )
QKLMN-GWAMB-iJ-0503-10 High Spike p p b (C0M4411, WOOnpa. *WSpike>
5003 59.0 4940
50000 5000 50000
59.0 69.0 59.0
55000 5300 50500
95 5000 110 50000 106 5000 101 soooo
290 290 290 280
5350 51900 6050 38900
101 103 115 77
OKLMN-GW-W26-0-050310 (CM4tt3pk G. MMntfLUb ftlke )
5000 13500000 9450000
-
5000 79300000 65300000
OKLHN-GW-W26-0-OW310 (OOMM4iaSpkH, BMOOnoft.UbpUce)
500G 13500000 7390000 * SOOOO 79300000 88300000
OKLMN-GW-W26-0-06Q310 Low Spike 5 ppb (000*4414. MMnflfl. field Spike)
5000 13500000 9050000
5000 79300000 73100000
OKLMN-GW-W2&4M)5031G High Spike 50 ppb
(CtW*44fi, so m nqfL FlewSpike )
50000 13500000 7210000 50000 79300000 57500000
*
OKLMN*GW-W33'4t"050310 (CW441Spk i, MM npft. Ub Spite )
5000 4610000 4720000
*
5000 1750000
1520000
OKLMN-GW-W33-0-050310 10000441Spi J. 50000 OR.UbSpIte )
50000 4610000 4730000 * 50000 1750000 1650000
OKLMN-GW-WSi'O-OSOilO Low SpikeS ppb
{00*441, SM tfign. Held Spilt)
5000 4610000 4920000
5000 1750000
2350000
OKLMN-GW-WM-fl-050310 High Spike ppb
(CM04411,10000r*IL FMd Spike )
50000 4610000 4520000 50000 1750000 1630000
*
OKLMN-GW-W205-CW350310 {CODM420fipkK. SOWng!L UUSpike)
OKLMN*GW-W20S4L050310 (COM4420Spk L Mfieonprt. UDSpike )
OKl^N43W-W20tHM>W10 Lew Spike 6 ppb ictoswai, 5000ngO. F ie ld sulk. 1
QKLMN-WW2084HKCW Hfflfir Spike 50 ppb (Co***433, SOcbOngfL FieldSpike >
5000 50000 5000 50000
148000 , 136000 *
148000 .166000 146000 129000
20 v
146000 221000 150
5000 50000 5000 50000
147000 147000 147000 147000
160000 190000 143000 184000
8$ * 74
OKLMN-GW-mi 5-04)50310 {C0W4424Spk M,MOOIHJILUb Spite}
OKLMN-GW-W215-04KW31Q (CMfi4424Spk N. 50000npILUb Splka )
QKLMM-GW-W215-C-05031Q Low Spike 5 ppb StW M .iW O^FW dSpiM |
OKLMN-GW4AH1WW50310 High Spike M ppb 1C0QO4427, SOofiOngiLFieldSpilo}
5000 SOOOO 5000 50000
37100 37100 37100 37100
52400
* , 5000
96900
120 50000
58600
SOW
101000 , 128 50000
4400 4400 4400 4400
&650 567O0 9880 '39200
89 105 as 70
`Sam ple re sid i exceeds Ihe spikino le ve l sig rifica n tly; therefore, an accurate recovery value cannot be calculated
ND * Ncrtdatacted at or above 25 rupL. (ppt|. NQ * No! Quantifiable * M easured concentration between 25 n aA (ppt)and the lim it of
Quantitation {LOG) which a 50 (ppt) Nota: Since this eummry u&to show* rounded re*t4t*, recovery value mayvaryaiighpy 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.: PQ00140
Table III. Matrix Spike Recovery of PFOS and PFOA in Water Samples Continued
Sam ple
C8 Sulfonate PFOS
C8 Add PFOA
Amount Amt Found Amount
Amount Amt Found Amount
Spiked In Sample Recovered Recovery Spiked in Sample Recovered Recovery
KLM N-GW -W 2010-0-0310 (C m e m e p k C . aow agn.Labpti )
OKLMN-GW-W2010-0-050310 iCOMMat Spko, seoeo ngiL me spue*}
OKUHN-GW-W201Q-0-050310 Low Spike 9 ppb (C0Oet49Q, MODngiL FWd spike )
XLMN-GW-W201IH K H K B tO High Sp *8 50 ppb { a m m eoeee ngn. FMd spike )
500C , 50000
5000 50000
O KLM N -G W -PW 7^ Kl5m iO (C0W 432 Spk e , SOM I10L Lab Spike )
0KlAtN *6W -FW 7-<W >503l0 (CeosM epk f. a n it Leb Spike )
OKLMN*CW-PW7<'O8(l310 Low Spike 5 ppb tCeWS4, 3W0ns-'Lriete pike I
OKLAHN-GW-PW7-0-05030 High Spike SOppb (00*444*5, SDOM nafL riW Spite )
5000 50000 000 50000
0KLMN-GW-TraPHHHC31C LowSpIko S ppb (00*4427. SODOnfr'L Field Spite )
OKLMM-GW-TR]P1<0-4)50310 High Spike 5C ppb (CSD443S. MODO n^lt FNM 8pliie )
5000 50000
OKLMN-GW-PWfl-tWWOSIO (C0M4442 Spk G, DOWnpIL Leb Spite )
OKLMN-GW*PWe^<KW0310 {CCCM44I S t* H, S o m nfliL Leb Spite )
- OKUHN-GW-PVW4KW610 U w Spike 5 ppb (C0M4444, sow n tfL Field Spite )
OKUWN-GW-PW5-0-M0310 High Spite SO ppb (C0M4446* WWWng/L Field Spike )
5000 50000 5000 50000
OKLMN*W-PW*-frb5C310 (C*044444* I, WOOng/L U b Sfifc i
OKLMN-GW-PWil-<MK03t0 C44444 5 p *J, 50000 nn. Ut>5pH#)
OKLMN-CW^W-b-OSOW Low Spike 5 ppb (CW4444*, WOOnoTLriete Splk}
OKUWN43W-FW9--0503M) High Spike 00 ppb (Cw ***w , owe note me**sp>h* >
5000 50000 5000 50000
O KLHKW j W -W S102-KI50310 (Cw ew so 3pfcK, SM npit U b Spike )
KLMN-GW-WB102^0-050310 (CW44W Spk L , KOSCOnV Let Spike ]
OKLMN*OW-WV6102'<l-050310 Low Spike 5 ppb |COO84452.5000ApO.Field 8lk| >
OKLMM5WW10-0-050310 Hiatt Spike SOppb (CO0A44S.MOOOngIL Fkdd Spike |
5000 50000 000 50000
. ND ND NO NO
71600 71600 71600 71600
ND ND
34300 34300 34300 34300
84400 84400 64400 84400
NQ NQ NQ NQ
5170 54600 5270 54900
103 5000 109 50000 105 5000 110 50000
NQ NQ NQ'. NQ
7B50C
5000
37600
119000 05 50000 37600
72600
.
5000
37600
118000 88 5D000 37600
5700 5350
116 5000 107 50000
ND ND
38300 89800 38400 83100
- 5000 i n 50000
- 5000 166 50000
61400 61400 61400 51400
63200 138000 98400 178000
5000 107 50000
5000 183 50000
49000 46000 49000 49000
5300 ; . 106
55800
112
5480
110
53200
106
5000 50000 5000 50000
214 214 214 ` 214
'Sam ple reeldtiB axesada the asking level significantly; Otarefore, an accurate recovery value cannot bo calculated
NO * Not detected at or above 26 ng/L (ppt).
NO s Nor quantlflatte * Maasored concenbaticn betoeen 25 n^A. (ppt) and the lim it of
Ouantitetlcn(kOQ)wWchls5drip/L(ppt)-
...... ......
Note: Since thie ummary table hows rounded mentis, recoveryvalues may vary eliantiy
from the value* In the raw cate.
5290 54300 4710 32300
41900 86100 42600 67100
5360 50500
61000 113000 59300 62200
50400 97900 55200 93200 5600 52700 5610 35300
108 10S 94 65
97 * 59
107 101 . 103 42
96 88 113 105 108 70
Exygen Research
Page 31 of 110
000054
Interim Report #1-Analysis of Oakdale Water Samples
Exygeti Study No.: P0001400
Table III. Matrix Spike Recovery of PFOS and PFOA in Water Samples Continued
Sim ple Description
CBSulfonate PFOS Amount Ami Found Amount
C* Acid PFOA Amount Amt Found Amount
Spilled in Sample Recovered Recovery Spiked \n Sample Recovered
WU WU
<atfU
i%i tr>g/U m 0.1
W t)
Recovery f* i
OKLMH*GW-W610*-0-050310 (CK444H S*khi. 9000 *VU U b >
OKLHhW3W-W5104-0-050310 (C0SS44MSpk N, 50000 ntfL Lab Sblkt )
OKLMN-GW-W41C4-0-0SO310 L o w Spike 5 PPb (CD0M4M. BOMnplL FiM 9pw $
OKLMN-GW<WeiC44M)50310 High Spike 50 ppb iCteSi4.B7, SMM ng^. FtaWSpik )
6000 50000 5000 50000
109 109 109 109
5540 56100 5700 56700
109 5000 116 50000 112 5000 113 50000
207 207 207 207
5290 57300 5+70 35800
102 114 105 71
OKLMM-<3W-W201-0-OW310 |C00*445Spk C, 50W OtfL U P 8*M*)
OKLMN<GW-W52Ch-0-050310 (C ttH ttt *f* D>040 Lab Splk*) DKlMN-GW'WUOI-O-tlSU'ID U rn Spike 0.5 ppb
(CMH4W, SWng/LFKMpit* )
OKLMN'GW`W201`O-6$<tt1O High Spike 5 ppb (CWS44S1, sow npiLFMd pika}
OKLMN^?W-W20-0-050309 (090M447 Spk C,5800 itgiL Lb Spat* )
OKLWM45W-W20-0-09W0 iCMMMdTSpkF, $0*0nglLUb Spite 1
OKLMK-GW-WZO'O'OSOSOfi Low Spike 5 ppb /COOfM. W ntfLFleW 1
0 KLWN-GW-W2 0 -0-050300 High Spike 50 ppb JCW64470, 0000 noA. FMd Spike)
5000 50000
500 5000
5000 50000 5000 50000
NQ NQ NQ NQ
46500 46600 466D0 46600
4280 50000 670 6600
49900 92800 41900 59500
100 5000 100 50000 134 500 132 5000
95.5 95,5 95.5 95.5
5000 285000 92 50000 285000 - 5000 295000 26 50000 295000
4*50 50800 606 6130
239000 295000 278000 264000
97 101 102 121
OKLMK-GW-W220-05030? Spk0 , SONnpA Uh Spike )
OKLMW-CW-W3!2-O-0S030e {C0MW1 Spk H. 50HMI fi/LLab &pilM}
OKLMN-GW-W2 2 -0 -050309 Low Spike 5 ppb (C0C44473, MH r>y/LFtokl Splk)
OKLMN-GVV-W224L050M High Spike 50 ppb (CWW4474,MHO n&LFieM Spike J
OKLMN-GW-W31-0-05D309 ( C m 475 spk I. 44 n p l Lab Sp*w}
OKLMN-CW-Wa*-0-050309 JCW4475 Spfc^ soeec rn^L Ufa Sptto ) OKUAH-QW-W31-0-05030 High Spike 50 ppb
{C9H4471. UOMegfL Flald 3pll)
OKLMN-GW-W32M)503W icoo***ri SpfcK. 00 nga. i t b )
DKLMN-OW-W32-0-03030$ (CWW+71-Spk L.40999 r*gfLLab *pih)
OKLMN-GW-W32-0-0M3 0A Low Spfce 3 ppb (caotuto, woa ngn.n*w 8p** >
DKLMN-GW-W32-0-050309 High Spate 50 ppb (CMbUSI, BOOOOn|^L FMd&ptk*}
5000 50000 5000
15000 46800 45600
44600 98500 41200
. .5000 105 50000
- 5000
50000 4580D
66800
40 50000
5000 .132000 . 116000 - 5000 50000 132000 159000 72 50000 50000 132000 216000 168 50000
5000 50000 6000 50000
47100 47100 47100 47100
62200
115000 136
74000
-
120000 146
5000 50000 5000 50000
317000 317000 317000 317000
330000 412000 324000 286000
23100 23100 23100
26400 71300 65700
117000 : 109000
117000
151000
117000
131000
117000
1570CK
96 05 -
Sam ple residue exceed th e piking level significantly'; therefore, an accu iate recovery valu e cannot be calculated N D = Not detected a l c r above 25 n fl/L (ppt}. NQ * Not quantifiable = M easured concentration between 25 ngA. (pp0 and the Umft of
Quanetation (LO Q )v^ ilch 18 50 n g il.ip p t). Mote: SJac* W s um nw y ta.We show * rounded re su lts, recovery value* may vary slightly from ttu value* lit the raw data.
Exygen Research
. Page 32 of 110
000055
Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table III, Matrix Spike Recovery of PFOS and PFOA in Water Samples Continued
Sam ple D escription
OKLMN-GW-W217-0415C30 CC4M4442 Spk til ttOO Lab pika)
OKLMN/3W-W217-0-OSCa09 (C06644I2 Sek N. S0Q66 ng/L Lab Spike 1
GKLMN-C3W-V21T4KHi0309 L o w S p ik e 5 p p b <CW44*4,tt<fi*fLFl*WS|>iM)
QKLMN-GW-W2ir-iM>50JOB Hlfiil S p lk * S 0 p p b ( W W W , b*m o n o n ^ M d sw i
C8 Sulfonate PFOS
Amount Amt Found Amount
Amount
S p ik ed in Sam ple R ecovered Recovery Spfkad
t n a ' U ____W D
("fW
(%) ( 9
C5 A dd PFOA
Airrt F o u n d
Amount
Ir Sam ple R ecovar!
(np/L)
(n o flj
5000 .50000
5000 50000
NQ NO NQ NQ
4790 49700 5800 65300
86 5000 99 50000 116 5000 131 SOOOO
NQ NQ : NQ NQ
4860 52200 4880 42600
OKLMN-GW-W2Q084)-OK>999 (C0W44W SpkO. 0 0 R01 Lab Spike 1
QKLMN-GW-W200Q-0-05030 (toe4444.j* K ROOM UitiSpliui}
OKLMN-GW-W8-(M>5WO Lo w S p ik e 5 p p b {SiiM M H.Ewgngn.wa Spa)
OKLMN'OW-W2OOB-(Kl5O30i H ig h S p ik e SO p p b (COMM, sooOb n^L Field 3 p * )
5000 50000 , 5000 50000
15500 15500 15500 15500
20800 68300 27QD0 71300
106 5000 108 50000 230 5000 1 1 2 ' SOOOO
53300 59300 5 S300 59300
G4800 114000 73600 04600
O K LM N ^W -W 2012-O -Q 503M {C0M44WSpk C, <009 ngA. Lab Sputa }
OKUMN-CW-W2012>0-O30ft (COB 00 St* D, <0000 n tf l u i> Splk*}
OKLMN-GW-W2O12O-O5O30S L o w S p ik e 5 p p b (COftMOM, 5000 eplL FIMti Se'** >
OKLMN'CW-W2012-0*0503W H igh S pike 0 0 p pb (C0004493.90090;a9IL FMd Splka)
5000
117000
143000
5D00Q 117000
186000
5000
117000 : , 115000
SDOGO -117000
203000
W 5000
46900
136 SOOOO * 5000
46900 46900
172 50000 . 46900
57700 94700 48500 69500
O K L M N -G W -W a0'O -050S 0S (CM644 Sole *, 9*00 n p l Lab Spite)
OKLM N -G W -W 60-M 50 (CMM4M $pk. F, OCP p p ll U b Spfc*)
OKLMfWWAVSO-ii^SOSO L ow S pike 5 p pb (900+406, MOO ngfl l*iaUI 8 pfca)
c k l m n -g w -w r o ^k w j o s H lo h s p a t e s o p p b ( c w u - w , soooo n # L FMd * p * >
5000 - :ND
50000 5000
ND ND ;
50000
ND
5 2 8 0 52900 5720 57600
JOB- 500C 106 ' ' 50000 114' 5000 115 50000
OWLMN-GW4*W1-{H>50310 (C0M449I3pk G, 0 0 n ^L Lob Spite )
5000
OKLM ^rG W -FW 1 -OrOSOMO U W 4 H St* H. BOOMn ^ L U b 9iW* )
50000 `
OKLMN-GW-PW1-0-050310 Low Spike 5 p p b > - i
(CwwBOD. eoot ng n n o u 6p * o >
5000
O K LM N -6W -W 1 *0*050310 Hl0 b S pike 50 p p b (COOftCeai, B0600 ngA. PMd Sfika J
5OCQ0
66800 *66800 66900 66900
72000 ` 116000
86900 ' &5200
* SflOO 10 2 SOOOO
5000 5 7 ' SOOO
OKLM N-GW fW 2-0*03C3r |C994SQe $pk t, Shoo ng/L Lab Spik)
OKUWN-W-FW2-0-O5O31O (C00945C2 $ j* j. GOMOl>0JLLab S p ite)
QKLMN-GWPW2-0-050310 Low S pike 5 p p b - {Goomom, sow a p n fh* space *
OKLWtH*GW-PW2-<Kl5C31C H lg h S p lk * 50 p p b (C0064MS, Bbooo npiL Raid Spite )
5000
3S1
5480 i: . 103. .6000
50000
351
5980Q
119. 5 0 000
5000 . =.9 5 i; . .. , , 4.280. .
5000
50000
351
40500
8 0 ' 50000
302 302
302 302 37300 37300 37300 '3 7 3 0 0 3630 3830 3630 3830
SS10 53100 5880 42200 47700 80200 40400 80500 8720 58800 7860 39500
''Sample residue exceed* the spiking <eud significantly, therefore, so accurate recovery value cannot be calculated ND Not detected at orabove 25 ng/L {pptjt NO - Nrrt quantifiable Measured concentration between 25 ng/L ippt) and the Limit of
Quantitation (LOQ) wttlcb la 50 n g tl {ppt}. >We: Since this summary tibie show rowictod m u t a , recovery values may vary slightly front the values in the raw data.
Recovery BU 97 104 98 85 * 109 * 71 .
96 .
85 110 108 111 84
. 106
* 86 102 110 85 72
Exygen Research
Page 33 of 110
000Q56
Interim Report #1 -Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table III. Matrix Spike Recovery of PFOS and PF0A in Water Samples Continued
Sample Description
OKLMN-GW-PW3--050310 <CWS4S0>Spk K. SOfiOP9lLUb Splk)
QKLMN-0W*PW3-(M0310 (C***4W48p*L0W"9k-Leb Spike) OKLHN-GW-PW34MW310 Low Spike 5 ppb
(CMSfm. 8409n^LFfeMbplk* > OKLMN-GW-PW3-0-O50310 High Spike 50 ppb
(csoeiMs, boooonon. Flaw ftplk*)
OKLM)M5W-WUM)5as10 (COOM51#Sp* M, SOMna. Ub Sp)k>
KLMN-GW-FW4-0-050310 (C09S4S10Spk N, 9W09n&L. Ub Stfl* 1 OKLMN-GW-PW4-O-05Q31& LOWSpike 5 Dpt)
(C00S4812,5000npfLFlekl W k#}
OKLWN-CW-PW4-0-KW10 High Spike 50 ppb ICW***13. 80000 nga. PisMSpfiu >
OKLMN-GWT'Wi-0-050310 (CowS14fipfco, 6000npfi. LabSplka)
QKLMN-GW-FWe-fl-050310 (QMMS14SpkP, 59000tigiLLabSplk*)
OKLMN-OW-PW6-0-050310 L ow SpfteSppb (CfiOWil*, *090r& L B*dSpike)
QKLMfrW5W-PWC-iHi5031fl High Spike 50 ppb (00**451?, 5000Cn f LFl*4d Spike}
OKLMN43W-PW10-6-511 (0004*51*Spk C, 5000 nffil LebSplk )
OKLMN-GW-PW10-fl-O5031O (009*451*pk O, S0090agO. LbSpike}
OKLNN-GW-FWlO-C-fiaalO LOWSpike S ppb <000*45, BoaongiL FlOd Splk*)
DKLWN-GW-PW10--05310 High Spike 50 ppb (C0954521,50*09 rvgA. FmMO )
OKLMN-GW-PW11-0-05310 (COC54A225pk E, 5000 HiLLebtylM)
OKLMN-GW-PWmW)50310 iCM*4S22Spk F. 50000npiL Uk Spike} QKLMN-GW-PW11-Q-0W310 Low SplK* 5 ppb
tCM*M, 5000null.Ftod Sill) OKLMN-GW-PW11-0-050310 High Spike 50 ppb
(CM64525, soot ngfLField Spike V
Ua III
C* Sulfonate PFOS
Amt Found Amount
Amount
In Sample Recovered Recovery Spiked
tofl/U
fn a fU
f%) w
CS Acid PFOA
Amt Found Amount
in Sample Recovered
tu rn
(noiL)
Recovery M
5000 3270D 43300
5000
177P0D
138000
50000 5000
32700 32700
. 66100 33800
87 50000 ; 177000
... SGOO
177000
190000 196000
26
50000 32700
SOOOO
55 50000 177000
204000
54
5000 50000 5000 5000
33800 33BOO 33300 33800
42500 75700 42200 81200
* 5000 72100 64 50000 7210D 5000 72100 35 50000 72100
77500 121000 80700 116000
* 98 B3
5000 90000 5DQOO 90000 5000 90000 50000 90000
97600 139000 94100 124000
5000 98 50000
5000 68 50000
78400 78400 78400 78400
82900 133000 87000 116000
105
75
5000 1400000 1410000 tr 5000 719000 50000 1400000 1390000 50000 719000 5000 1400000 955000 5000 719000 50000 1400000 1910000 * 50000 718000
866000 840000 692000 747000
5000 50000 5000 50000
40800 40800 40800 40800
45900 83100 45400 63500
-
5000
60300
85 90000 80300
- 5000 60300
95 50000
80300
64700 105000 63300 98100
so 76
Sem ple residue exceed s the spiking le ve l sig nificantly; therefore, an accurate recovery value cannot be calculated
ND - Not detected a t or above 25 ng4_<ppl).
NO - Not quantifiable *Measured concentration between 25 ng/L {ppt| and the Limit of QuaniiiaUon (LOO) which is 50 ng/L (ppt).
Note; Since this summary table shows rounded results, r*ocv*ry values may vary sligtafy from the values In the raw data.
Exygen Research
Page 34 of 110
-00M S7
Interim Report #I-Analysis of Oakdale Water Samples
Exygen Study No,: P0001400
Table III. Matrix Spike Recovery of PFOS and PFOA in Water Samples Continued
Sam ple D m crlp tio n
C8 Sulfonate PFOS
Am ount Am t fo u n d Am ount
Am ount
Sp iked b i Sam p le R eco vered R e co ve ry Sp iked
re 0m
fn sfL i
WW
<n -)
C* Acid PFOA
Amt Found Am ount
In Sam p le R eco vered
..J n s A i
<nB ->
2OKtM N-svwwsosm
(Cm>MS s gpk o . n a r t - L e b s#ik* >
O KLM N *SVV -0tO 60310 <ComCH Spk a eeooon^ i. U b Spite 1
OKLMN-SW -O-OKKHO Lo w S p ik e $ ppb (COOS4S2I, sow ft?L Flew Spike 1
OKLMN-SW 4>*O50J10 H K)h S p ik e 50 ppb {C em eat, soooc no. new sp ite>
5000 50000 5000 50000
USD 1190 1180 1190
6270 51600 TZ20 58000
102 5000 101 SOCOO 121 5000 114 50000
491 401 491 491
5520 53200 6020 44200
OKLMN-GW-TRIP2-IW)50310 Lo w Sp R ce 5 ppb (C M ttU f. WOOn 0 i. Spite )
OKLMN-QW-TFIP2-CM}W310 High S p ik e 50 ppb tCPWWOTt.SOWr**. Spite)
5000 50000
ND J 6170 ND 57400
123 5000 115 50000
ND ND
6040 57300
R eco very f
101 105 111 B7
121 115
A verag e: Stand ard D eviatio n :
110 32
*$ample residue exceeds trie spiking level significantly; therefore, an accurate recovery value cam el be calculates
ND * Notdelected al or above 29 ng/L (ppt). NO - Not qusnttflablM Measured concanfcrabon between 25 ngA (ppt) and die Umll of
Quantitation (LOO)which 150 ngA (ppt). Note: Since We summery table bows rounded rasutts, recovery values mayvary IlgM* from tbs values In trie raw date.
A verag e: Stan d ard D eviatio n :
83 1
Exygen Research
Page 35 of 110
000058
Interim Report #1-Analysis of Oakdale Water Samples
- Exygen Study No.: P0001400
Table IV. Surrogate Spike Recovery of 3C PFOA in Water Samples
Exygen ID
Sample Description
Amount Spiked
{m m
13c -pfo a
Amount Recovered
(nart-l
Recovery m
C0064404 Spk C CD064404 Spk D
C0064404 C0064404 Rep
C0 0 6 4 4 0 5 C0064406 C0064407
OKLMN-GW-W3-0-050310 DKLMN-GW-W3-0-D50310 OKLMN-GW-W3-0-050310 OKLMN-GW-W3-0-050310 OKLMN-GW-W30-0E0310 Dup OKLMN-GW-W3-0-050310 Low Spike 5 ppb OKLMN-GW-W3-0-050310 High Spike 50 ppb
5500 50500
500 500 500 6000 50000
5580 53900
431 422 416 4730 34500
101 107 86 B4 83 95 69
C0064408 Spk E C0064408 Spk F
C0064408 C0064408 Rep
C0064409 C00B4410 00064411
OKLMN-GW-W8-0-Q50310 OKLMN-GW-W8-0-D50310 OKLMN-GW-W8-0-Q5031O OKLMN-GW -W 3-0-0 5 0 3 1 0
OKLMN-GW-W8-0-050310 Dup OKLMN-GW-W8-0-C5310 Low Spike 5 ppb OKLMN-GW-W8-0-050310 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
C0054412 C0064412 Rep
C0064413 CO064414 CO064415
OKLMN-GW-W26-0-C50310 OKLMN-GW-W26-D-05O310 OKLMN-GW-W26-0-C50310 OKLMN-GW-W26-0-050310 OKLMN-GW-W26-0-050310 Dup OKLMN-GW-W26-Q-050310 Low Spike 5 ppb OKLMN-GW-W26-0-Q50310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
C0064416 Spk 1 C0064416 Spk J
C0064416 C0064416 Rep
C0064417 C0064416 C0064419
O KLMN-GW-W33-0-05G310 OKLM N-GW-W 33-Q-050310 OKLM N-GW -W 3 3 -0 -0 5 0 3 10 OKLMN-GW-W33-CL050310 OKLMN-GW-W33-Q-05C310 Dup OKLMN-GW-W33-0-050310 Low Spike 5 ppb OKLMN-GW-W33-0-Q50310 High Spike 50 ppb
5500 50500
500
500 500 5000 50000
C0064420 Spk K
C0064420 Spk L C0064420
C0064420Rep C0064421 C0064422 C0064423
OKLMN-GW-W205-0-050310 OKLMN-GW-W2Q5-0-50310 OKLMN-GW-W2C5-0-05C31D
OKLMN-GW-W205-0-050310 OKLMN-GW-W2O5-O-05Q31O Dup OKLMN-GW-W2C5-0-050310 Low Spike 5 ppb OKLMN-GW-W205-Q-C5Q310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
C0064424 Spk M C0064424 Spk N
C0064424 C0064424 Rep
C0064425 C0064426 C0064427
OKLMN-GW-W215-0-050310 OKLWIN- G W -W 2 15-0-050310 OKLMN-GW -W 2 1 5-0-05031 OKLMN-GW-W215--05C31 . OKLMN-GW"W21SK)-050310 Dup OKLMN-GW-W215-O-O5Q310 Low Spike 5 ppb OKLMN-GW-W215-0-050310 High Spike 50 ppb
5500
50500 500 500 500 5000 50000
5430 32900 7720 7660 7540 5210 28000
3160 46000
262 256 . 261 2750 42500
4940 53000
279 280 307 4240 . 38000
5S50 56700 1010 434 464 4960 35600
99 65 * *
104 56
57 95 52 51 52 55 85
90 105 56 56 61 85 7S
106 112 202 87 93 99 71
The very high PFOA leval In tha undiluted sample Interfered with ,SC PFOA recovery. Note: Since this summary table shows rounded results* recovery values may vary slightly from the value* in the raw data.
Exygen Research
Page 36 of 110
000059
Interim Report #1 -Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table IV. Surrogate Spike Recovery of 13C PFOA In Water Samples Continued
Exygen !D
Sample Description
Amount Spiked ingiL)
1iC*PFOA
Amount Recovered
fng/L)
Recovery __{%)
C0064428 Spk C C0064428 Spk D
C0084428 C0064428 Rep
C0064429 C0064430 CO064431
OKLMN-GW-W2010-Q-05031Q OKLMN-GW-W2010-0-050310
OKLMN-GW-W2010-0-050310 OKIMN-GW-W2010-0-050310 OKLMN-GW-W210-0-050310 Dup OKLMIM-GW-W2010-0-050310 Low Spike 5 ppb OKLMN-GW-W2010-0-D50310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5390
53000 432 417 510 4500 30200
98 105 86 83 102 90
60
C0084432 Spk E C0064432 Spk F
C00S4432 C0064432 Rep
C0064433 C0064434 C0084435
OKLMN-GW-PW7-0-050310 OKLMN-GW-PW7-0-050310 . 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 QKLMN-GW-PW7-Q-Q50310 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
C00S4436 C0064437 COO64438
OKLMN-GW-TRIP1-0-Q50310 OKLMN-GW-TRIP1-0-050310 Low Spike 5 ppb QKLMN-GW-TRIP1-0-050310 High Spike 50 ppb
500 5000 50000
510 5100 51300
102 102 103
C0064442 Spk G C0064442Spk H
C0064442 C0064442 Rep
C0064443 C0064444
C0064445
OKLMN-GW-FW8--G50310 OKLMN-GW-PW8-0-050310 OKLMN-GW-PW8-0-050310 OKLMN-GW-PW8-0-050310 OKLMN-GW-PW8-0-50310 Dup OKLMN-GW-PW8--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
C0064446 SpkI
COO0 4 4 4 6 S p k J
C064446 C0064446 Rep
C0064447 C0064448 C0064449
OKLMN GW-PW9-0-050310
O K LM N -G W -PW & -0-050310
OKLMN-GW-PW9-0-050310 OKLMN-GW-PW9-0-0531 O' OKLMN-GW-PW9--050310 Diip OKLMN-GW-PW9-0-50310 Low Spike 5 ppb OKLMN-GW-PW9--Q5Q310 High Spike 50 ppb
6500
50500
500 500 500 5000 50000
5250
53900
315 317 338 4230 24800
95
107
63 63 68 85 50
C008445Q Spk K COO64450 Spk L
C0064450
C0064450 Rep C0054451 C0064452 C0064453
OKLMN-GW-W6102-0-05D310 OKLMN-GVV-W6102-0-050310 OKLMN-GW-W6102-0-050310
OKLMN-GW-W6102-0-050310 OKLMN-GW-W6102-0-050310 Dup OKLMN-GW-W6102-0-050310 Low Spike 5 ppb OKLMN-GW-W6102-Q-050310 High Spike 5Q ppb
5500 50500 500
500 500 5000 50000
5640 53200 424 439 480 5050 32500
103 105 85
88 96 101 65
Note: Since th is sum m ary table show s rounded results, recovery values m ay vary slightly from th e v a lu e s in th e raw data.
Exygen Research
Page 37 of IlO
000060
Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table IV. Surrogate Spike Recovery of 13C PFOA in Water Samples Continued
Exygen ID
S am ple Description
13C-f>FOA
Amount Amount Splked Recovered (ig 4 -L _ (ng/L)
Recovery
m
C0064454 Spk M C0064454 Spk N
C0064454 C0064454 Rep
C0064455 C0064456 C0064457
OKLMN-GW-W6104-0-050310 OKLMN-GW-W6104-0-5031Q OKLMN-GW-W610 4 - 0 -0 5 0 3 1 0 OKLMN-GW-W6104-0-050310 OKLMN-GW-W6104-0-C50310 Dup OKLMN-GW-W6104-0-5Q310 Low Spike 5 ppb 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 0064458 Spk D
C0064458 C0064458 Rep
C00B4459 C0084460 C0064461
OKLMN-GW-W6201-0-05Q310 OKLMN-GW-W6201-0-Q50310 OKLMN-GW-W6201-0-050310 OKLMN-GW-W6201-0-50310 OKLMN-GW-W8201 -0-050310 Dup OKLMN-GW-W201-0-050310 Low Spike 0.5 ppb OKLMN-GW-W6201-0-050310 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
CO064467 Spk E C0064467 Spk F
C0064467 C0064467 Rep
C005446S C0064469 COO64470
OKLMN-GW-W20-0-05C309 OKLMN-GW-W20-0-05Q309 O KLMN-GW-W20-0-050309 OKLMN-6W-W2O-0-O5Q3Q9 OKLMN-GW-W20-0-50309 Dup OKLMN-GW-W20-0-50309 Low Spike 5 ppb OKLMN-GW-W20-0-05Q309 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
C0O64471 Spk <3 C0064471 Spk H
C0064471 C0064471 Rep
C00B4472 C0064473 C0064474
OKLMN-G W-W22-0-S0309 OKLMN-GW-W22-Q-050309 OKLMN-GW-W22-0-050309 OKLMN-GW-W22-Q-O50309 OKLMN-GW-W22-0-05Q3Q9 Dup : OKLMN-GW-W22-0-5Q3Q9 Low Spike 5 ppb OKLMN-GW-W22-Q-0503Q9 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 1 C0064475 Spk J
C006447S
C0064475 Rep C0064476 C0064477
QKLMN-GW-W3 i -0-050309 OKLMN-GW-W31-0-050309
OKLMN-GW-W31-0-050309 OKLMN-GW-W31 -0-050309 , OKLMN-GW-W31-0-05Q309 Dup .
OKLMN-GW-W31-0-050309 High Spike 50 ppb .
5500 50500
500 500 500 50000
541Q
54200
391 391 371 44100
98
107
7 78 74 88
C0064478 Spk K C0064478 Spk L
CO064478 CtX)64478 Rep
CO064479 C0064480 C0064481
OKLMN-GW-W32-0-050309 OKLMN-GW-W32-0-05C1309 OKLMN-GW-W32-0-05C309 . OKLMN-GW-W32-0-050309 OKLMN-GW-W32-0-05D309 Dup OKLMN-GW-W32-0-0503Q9: Low Spike 5 ppb 0 KLMN- GW-W32-0-050309 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: Sines this summary tabl shows rounded results, recovery values may vary slightly from the values in the raw data.
Exygen Research
Page 38 of 110
000061
Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No,: P000140Q
Table IV. Surrogate Spike Recovery of 13C PFOA in Water Samples Continued
Exygen ID
Sample D escrip tio n
Amount Splked (og/L)
13c -p f o a Amount Recovered
<ne/L>
Recovery (%)
C0064482 Spk M C0064482 Spk N
C0064482 CO064482 R ep
C0064483 C0064484 CQ064485
OKLMN-GW-W217-0-050309 OKLMN-GW-W217-0-050309 OKLMN-GW-W217-Q-Q50309 OKLMN-GW-W217-0-050309 OKLMN-GW-W217-0-050309 Dup OK1MN-GW-W217-0-05030 Low Spike 5 ppb OKLMN-GW-W217-0-050309 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
C0064488 Spk O C0Q64486 Spk P
C0064486 00084486 Rep
C0064487 C0064488 C0064489
OKLMN-GW-W200&-0-050309 OKLMN-GW-W2008-0-050309 OKLMN-GW-W2008-0-05Q309 OKLWN.GW-W2008-0-050309 OKLMN-GW-W2OO8-O-05O3O9 Dup OKLMN-GW-W2008-0-050309 Low Spike 5 ppb OKLMN-GW-W2008-0*050309 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5410 52500 428 453 468 4850 44700
5140 52100
318 326 357 6040 37800
98 104 86 91 94 97 89
93 103 64 65 71 121 76
C0084490 Spk C C0084490 Spk D
C0064490 C0064490 Rep
C064491 C0064492 -C0064493
OKLMN-GW-W2012-0-05Q309 OKLMN-GW-W2012-0-050309 OKLMN-GW-W20120-050309 OKLMN-GW-WJ12-0-050309 OKLMN-GW-W2012-0-050309 Dup. OKLMN-GW-W2012-0-050309 LowSpike 5 ppb OKLMN-GW-W2012-0-050309 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
C0064494 Spk C0064494 Spk F
C00S4494 C0064494 Rep
C0064495 C006449S C0064497
OKLMN-GW-W80-0-050309 OKLMN-GW-W80-0-050309 OKLMN-GW-W80-0-050309 OKLMN-GW-W80-0-050309 OKLMN-GW-W8W3-050309 Dup OKLMN-GW-W80-G-O5O3O9 Low Spike 5 ppb OKLMN-GW-W80-0-050309 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5650 , 52400
486 438 502 5410 41700
103 104 97 88 100 108 63
C064498 Spk G C0064498 Spk H
CQ064498 C00S4498 Rep
C0064499 C064500 C0064601
OKLMN-GW-PW1-0-050310 OKLMN-GW-PW1-0-050310 OKLMN-GW-PW1-O-O50310
OKLWIN-GW^PWI-04350310 ' OKLMN-GW-PW1-0-050310 D u p : OKLMN-GW-PW1-0-50310 Low Spike 5 ppb OKLMN-GW-PW1-0-050310 High Spike 50 ppb
C0064502 Spk 1 C0064502 Spk J
C0064502 C064502 Rep
0064503 C0064504 . COO64505.
OKLMN-GW-PW2-0-O5D31O OKLMN-GW-PW2-CH35C310 OKLMN-GW-PW2-0-050310 . OKLMN-GW-PW2-0-050310. . OKLMN-GW-PW2-0-050310 Dup OKLMN-GW-PW2--05031Q Low Spike 5 ppb OKLMN-GW-PW2-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5500 50500
500 500 : 500 5000 50000
5150 53000
331 350 352 4420 41600
5420 52600
440 440 431 4880 34000
94 105 66 70 70 88 83
99 104 88 88 86 94 68
Note: Since till* sum m ary tabl* shows rounded results, recovery value* may vary slightly fromthe values In the raw data.
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study Np.: POOOI4QO
Table IV. Surrogate Spike Recovery of 13C PFOA in Water Samples Continued
Exygen ID
Sample Description
Amount Spiked
" C-PFOA
Amount Recovered
{ttsfl-i
Recovery (*>
C0064506 Spk K C0064506 Spk L
C0064508 C0064506 Rep
C0064S07 C0064508 C0064509
OKLMN-GW-PW3-0-050319 OKLMN-GW-PW3-0-05031D OKLMN-GW-PW3-0-Q50310 OKLMN-GW-PW3-Q-050310 OKLMN-GW-PW3-0-050310 Dup 0 KLMN-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
C006451Q Spk M C0064510 Spk N
C0064510 C0645010 Rep
C0064511 C0064512 C0064513
OKLM N-GW- PW 4--050310 OKLMN-GW-PW4-0-050310 O KLMN-GW-PW4-C-050310 OKLMN-GW-PW4-0-050310 OKLMN-GW-PW4-0-050310 Dup OKLMN-GW-PW4-0-Q50310 Low Spike 5 ppb OKLMN-GW-PW4-0-050310 High Spike 50 ppb
5500 50500
500 500 500 5000 50000
5100 52400
320 324 313 4870 38000
94 104 64 65 63 97 76
CQ064514 Spk 0 C0064514 Spk P
C0064514 C0064514 Rep
C0064515
C0064516 CQ064517
OKLMN-GW-PW6-0-05Q310 OKLM N-GW -PW 6-0-050310 OKLMN-GW-PW6-0-050310 OKLMN-GW-PW6-0-050310 OKLMN-GW-PW6-0-050310 Dup OKLMN-GW-PW6-0-050310 Low Spike 5 ppb OKLMN-GW-PW6-0-050310 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 C0084518 Spk D
C0064518 C0064518 Rep
C0064519 C0064520 C0064521
OKLMN-GW-PW10-0-050310 OKLMN-GW-PW)0-0-050310 OKIMN-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-PW 10-0-050310 High Spike 50 ppb
5500 50500
500 500
500 5000 50000
3670 48500
255 249 258 2980 34100
67 96
51 50 52 60 66
C0Q64522 Spk E C0064522 Spk F
C0O64522
C0064522 Rep C0064523 C0064524 C0064525
OKLMN-GW-PW11-0-050310 OKLMN-GW-PW11-0-050310 OKLMN-GW-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-PWt 1-0-050310 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
C0Q64526 Spk G C0064526 Spk H
C0064526
CQ064526 Rep C0064527 C0064528 C0064529
OKLMN-SW-O-5031 OKLMN-SW-O-050310 OKLMN-SW-O-050310 OKLMN-SW-O-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 5200Q
124 132 505 5320 41200
96 103 25 26 101 106 82
Note: Since this summary table shows rounded results, recovery values may vary slightly from the values In the raw date.
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Interim Report #1 -Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Table IV.
xygen ID
Surrogate Spike Recovery of 13C PFO in Water Samples
Continued
wC-PFOA
Sample Description
Amount Amount
Spliced Recovered Recovery
<ng/L} _ fno/L>
(%)
COO64530 C0064531 C0064532
OKLMN-GW-TRIP2-0-050310
500
OKLMN-GW-TRIP2-0-050310 Low Spike 5 ppb 5000
OKLMN-GW-TRIP2--5310 High Spike 50 ppb 50000
494 5520 52900
99 110 106
Average: 83 Standard Deviation: 21
Note; Since this sum m ary table show s rounded results, recovery values m ay vary slightly from the v alu es In th e raw data.
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Interim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
FIGURES
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Interim Report #l~Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Figure 1, Typical Calibration Curve for PFOA ie Reagent Water
*i QXMCSCGroundWaMfRvvTjdbCPFO<$rUmsc"R*Qf*ionfl
*l^5-*0C3x+?.3*)4(r*0jW41)
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Exygen Study No.: P001400
Figure 2. Extracted Standards of PFOA in Reagent Water, 25 ng/L and 50 ng/L, Respectively
XC032tO3-J-PP.*
! c f 4 1 from O S iAO S C .trf
A w 4 4 n T counts Hrtgirt 6&3336 qtw RT: V 4 4 6 min
11.64
XCIJ32HW-2 FF0A ^*>dart)4WWW.lJamu - smpl 3 *? 4Mrom D3245C.arfi A na: 782* oowits K*^R: 12703.770 cm RT: U.W2mn
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Interim Report #1-Analysis of 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
Co**; PFOA {U ntoow(ii413j0& 6$# am v - a*mfair9 o t*1 tom<>3Jl4C6C.wMf Anw; 5766 ccx/fffc JMgMr994,922 op RT: t1.94e ml*
11.86
Note: A linear lot o f PFOA was used to calibrate the instrument. The two peaks shown in Figure 4 are due to different isomers present in environmental samples. The area counts for all isomers present are included to report one total PFOA value.
Exygen Research tlKV;
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Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Figure 4.
Chromatogram Representing an Oakdale Water Sample Analyzed for PFOA, DF=100 (Exygen ID: C0064522, Data Set: 032405CR)
I C6Q64B22 -PFQ* (U*HiWn}413Jt)t$G9.9*<rtv* Sjwwpl* 38
f t w 0324O3R.wr1f
Ar*: 87874 counts fr ig h t' 7 f8 0 1 & 4 9 c s R7: t1 2 0 m ln
11,52
intensify, cp s
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Exygen Study No.: P0001400
Figure 5. Typical Calibration Curve for 13C PFOA in Reagent Water
P324D5C OnHTKj R*v7 t (I3C P F O ^ c"U r * r Regression C*
'040341 0 C .ttiir)
Area, courts
Exygen Research
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Interim Report #1-Analysis of 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
P XCO33i05-i - iSCPFOA
2 o f 4? frcni C3143C.w)r
Arv>: 33102 counts Ni/rJt5iS.f13<y7* R 7 :11J5C min
6000 -t
4000
ii.es
8 9 10 11 12 13 14 16 16 17 Tim *, min
p XCP3ZHK-2 - 13C PFQAC&ntnQ 416,0/370.0 amu swnpta 3 of 41 from Q32405C.<jiff *9017 a u n ts Htitft: tj436.4*cpff RI: 1154? rr*.
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Interim Report .#!-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
ft*geCoi*irof- fJC F'POA (UnhfTvwa) iMS GKiroa - sanrpt? $ o? 41 ffotTr0324C5C H*fr A r*a : Z 1t o o w t* H a itfrt 56,564 c*>j fi7 : ifA 3 4 * n iit
11.83
Intensity, cps
Aw;W fl?8tcoo<*s Haflhtj lOWOT^a# ep ffM IX B in *
intensity, Dps
A * i; 12M65B oowtr h ^ lt: 23388H13cps RT; 1!.M 3flifc
Intensity, cps
Exygen Research
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Interim Report #1-Analysis of 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)
006492?
1$CPFQA *mtr-*
|te k flo *w J4 ?5 .0 .i3 7 0 .0
**in p J*2 3
Mf fnom032405C.w!r
A n : 418903 e&trrfo WWjpAt
R i: l i . 855 m h
11,89
intensity, cps
Exygen Research
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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
fyT ' ttfWOSCR O rcxni u o u t R*v1 jU i (P F9 S ): "LM a f R w u sto n (1 *#**!<'. y 135 x -tD C H C /ir >
Area, counts
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Exygen Study No.: POOOI400
Figure 10, Extracted Standards of PFBS in Reagent Water, 25 ng/L and 50 ng/L, Respectively
P*SS {Staa<f*ri)259jM99.0
2 ofSTfrov?
A m : 421 i vxifrts tf&sht? ti)6 S 3 4 c fi9 RT: 3307 min
3.61
I X C 04W S* - PFBS CSMhdtri) 266409.0 *mM- rapfe 3 of 57 'rem Q3M05Cft.iff A w 7H' W r tW *; lT.i4 ej fm 3 *5 4 fl*i Sfl
Tim e, min
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Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Figure 11. PFBS in Reagent Water, SO ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
Cewrinoi - P F B S f l J t t , 3 9 9 . 0 J 9 & - 0 jw u . sampkt 9 o f B T from Q324t><5CR.*r/f (pM kxoitw fra)
I ftogft Spk A- P FIS ( Q C ) 3 S 9 m u a n y! 19 of 97 from 03M05Cfi.wft A t i: 4 wnte hW^T. 1D6.400 cps R7:3.6S2 min 3 65
Mi:f9>92<unta Hwjht: De.W RT: 3.017 min
(Qf>. fOOO
H&
T9 C
300.
I, 0.53
1
3-02
i
3 .1 0
A4
2i
4
5 .0 2 ..
8
.7
9.05 11j03
8 0 10 11 12' 13 14 15 19 17 Tim .
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' Exygen Study No.: P0Q0I400
Figure 12. Chromatogram Representing an Oakdale Water Sample Analyzed for PFBS, DF=100 (Exygen ID: C0064522, Data Set: 0324O5CR)
CQQe4522 - f>FBS Unknown) 2$9JM9$.Q mstu *
38 o fe 7 frtrtt 0324&SCJt.irr
Ar9:877&oouitiv WWgiri 215.40$cp# flT:-3S24m)n
3432
intensity, cps
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M erim Report#!-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Figure 13. Typical Calibration Curve for PFHS in Reagent Water
W 2W C Grcimd irftertsr RtvT.ndb (P f K3> ` linear* Reijnrssioo(*1 t x ' y - <WSx +0OCM01 $*C-96&8)
Are, counts
Exygen Research
Page 55 of 110.
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Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No.: P0001400
Figure 14. Extracted Standards of PFHS in Reagent Water, 25 ng/L and 50 ng/L, Respectively
' PFHS (S&Stt?*r3)S$$,<>fdG.OMfrta mirnpl* 2 o ( 4 i fm m Q 3 2 4 0 5 C .w ilt
A r t : 12966 GQdltti
XT: 10.626 rnirr
40JB3
Exygen Research
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Interim Report#!-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
Figur 15. PFHS in Reagent Water, SOng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
. p f h s ( U n k n o w n ) * m t awnpM 9 o f* i kem M 4 P3 C .fr {JoVwt not found}
oa . 3000
* 2000
c
f 1000
RM0MC Sfk 6 - PFHS (QCJ MO WSOJOvtw- sampte 11 trf 4\ ffvn KT2WC.il * '.2 3 8 6 1 8 Mcrntt W*s*<:39774.188op* RT: 10.886*
10.50
110.19-*
B 10 11 12 13 14 . 1a 15 17 Timt. mift
Exygen Research
er}'!- >
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Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No,: P0001400
Figure 16. Chromatogram Representing an Oakdale Water Sample Analyzed for PFHS, DF=JO0 (Exygen ID: CG064522, Data Set: 0324O5CR)
CQ064H2 - PFHS (Uttkno*n}3$9X>&0to MMtt - * i m&f 33 CF67 !h>m 0324v5CR.wifr A w : 373S4-otxin1* H+tgHf: 2939.956 c p s XT: i0363frtk>
icjsa
Exygen Research
(ft $
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Interim Report #1-Analysis of Oakdale Water Samples
Exygeix Study No.: P0001400
Figure 17. Typical Calibration Curve for PFOS in Reagent Water
0324D5C Orouiid V ttrR *W .rtb(FrO S> '^ r"R *jn issic> n O /x*i*iglrtW>$): y * 329 >+C>1<nC03$->*OS**}
Exygen Research
Page 59 of 110 0000S2
Interim Report #!-Analysis of Oakdale Water Samples
Exygen Study No,: P0001400
Figure 18. Extracted Standards of PFOS in Reagent Water, 25 ng/L and 50 ng/L, Respectively
- PFOS
j w s jfn p lt 2<*<41 fi-wrr 032406C.*ifT
A r* ,:1 $ 4 $ ev* 'rts Hakfirt 1B9QJ2&opc R7; 12&3B fahr
1 2 .8 4
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Exygsn Study No.: P0001400
Figure 19. PFQS in Reagent Water, 50 ng/L Fortified Reagent Water, and 500 ng/L Fortified Reagent Water, Respectively
t0#48 owwrf# iWffW11ifi3.3?6 Cpss R7: t2,81$mt*
12.02
intensity, cpn
* v a .Z lW tM * S nW F *:37i,tn cps BT; 12.Biir>r>
1**1
intensity, cps
A m : 160532oaums Htfflta: 15it8.73 cps RT: 12.328 mb
Intensity, cps
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Interim Report #1-Analysis of Oakdale Water Samples
Exygen Study No;: P0001400
Figure 20. Chromatogram Representing an Oakdale Water Sample Analyzed for PFOS, DF=100 (Exygen ID; C0064522, Data Set: 032405CR)
CAQ0w&4;G1252075P$FO>oS*(wUfenkHnovwignh)t46330.3M32904.&C<0 K- *T:*iin2p.f1*363tuCir/t&7 0324QX#.w#r
eooo-i
5500
5X0
3000
Intensiv, cps
3 A S 6 7 8 0 10 11 12 13 14 19 10 17
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intrim Report #1-Analysis o f Oakdale Water Samples
Exygen Study No.: P0001400
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/M S/M S"
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