Document r66KMy6yMpvZbYOagwvEzy0ge
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A -fL A . $ 6 2 7
INTERIM REPORT #23 Aaaivsis of Sediment Samples
STUDY TITLE Analysis o f Perfluorooctanoic Acid (PFOA) in Water, Soil, Sediment, Fish, Clams, Vegetation, Small Mammal Liver and Small Mammal Serum Using LC/MS/MS for the
3M Decatur 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 2,2006
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: P0000760 Exygen Study Number: P0000760
Total Pages: 110
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Interim Report #23 - Analysis of Sediment Samples
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GOOD LABORATORY PRACTICE COMPLIANCE STATEMENT
Exygen Study Number P0000760, entitled "Analysis o f Perfluorooctanoic Acid (PFOA) in Water, Soil, Sediment, Fish, Clams, Vegetation, Small Mammal Liver and Small Mammal Serum Using LC/MS/MS for the 3M Decatur Monitoring Program," conducted for 3M Company, is being performed in compliance with EPA TSCA Good Laboratory Practice Standards 40 CFR 792 by Exygen Research, with one exception. The laboratory control and control spikes for the direct injection and alternate SPE methods and the spiking procedures for the surrogate were not recorded promptly at the time o f extraction.
ohn Flaherty Principal Investigator Exygen Research
Study Director Weston Solutions, Inc.
Michael A.. Santoro Sponson Representative 3M Company
Exygen Research
Date
6 Date
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Exygen Study No.: P0000760
QUALITY ASSURANCE STATEMENT
Exygen Research's Quality Assurance Unit reviewed Exygen Study Number P0000760, entitled, "Analysis o f Perfluorooctanoic Arid (PFOA) in Water, Soil, Sediment, Fish, Clams, Vegetation, Small Mammal Liver and Small Mammal Serum Using LC/MS/MS for the 3M Decatur Monitoring Program". All reviewed phases* 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
31. Final Raw Data Review and Interim Analytical Report Review
Date Inspected
5/2/06
Date Reported to Date Reported to
Principal
Exygen Date Reported to
Investigator Management Study Director
5/2/06
5/2/06
5/2/06
affer y / j Lead, Quality Assurance Unit
j/fc / C Date
'Note: All in-lab inspections will be documented in the QA statement for the final
analytical report at the conclusion of the study. This QA statement involves only the review o f the interim report and associated raw data.
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Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0OOO76O
CERTIFICATION OF AUTHENTICITY
This interim report, for Exygen Study Number P0000760, is a true and complete representation of the raw data.
Submitted by:
Exygen Research 3058 Research Drive State College, PA 16801 (814) 272*1039
Principa] Investigator, Exygen:
Exygen Research
Exygen Research Facility Management:
7 /7 7
Richard j<yi izzdni President Exygen Ri
-
ra*n.-ij
Study Director, Weston Solutions, Inc.
Date Date
JaisimhaTiesari P.E., DEE Weston Solutions, Inc.
Sponsor Representative, 3M Company:
Michael M. Santoro Director offRegulatory Affairs
Date
Exygen Research
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Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
STUDY IDENTIFICATION
Analysis o f Perfluorooctanoic Acid (PFOA) in Water, Soil, Sediment, Fish, Clams, Vegetation, Small Mammal Liver and Small Mammal Serum Using LC/MS/MS for the
3M Decatur Monitoring Program
PROTOCOL NUMBER:
P0000760
EXYGEN STUDY NUMBER: P0000760
TYPE OF STUDY:
Residue
SAMPLE MATRIX:
Sediment
TEST SUBSTANCE:
Perfluorooctanoic add (PFOA)
SPONSOR:
3M Company 3M Building 0236-01-B-10 S t Paul, MN 55144
STUDY DIRECTOR:
Jaisimha Kesari P.E., DEE Weston Solutions, Lie. 1400 Weston Way West Chester, PA 19380
STUDY MONITOR:
Michael A. Santoro 3M Company 3M Building 0236-01-B-10 St. Paul, MN 55144
PERFORMING LABORATORY: Exygen Research 3058 Research Drive State College, PA 16801
ANALYTICAL PHASE TIMETABLE:
Study Initiation Date:
11/05/04
Interim Analytical Start Date:
04/27/06
Interim Analytical Termination Date: 04/30/06
Interim Report Completion Date: 05/02/06
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PROJECT PERSONNEL
The Study Director for this project is Jaisimha Kesari at Weston Solutions, Inc. The following personnel from Exygen Research were associated with various phases o f this interim portion o f the study:
Name John Flaherty Karen Risha Paul Connolly Christine Edwards Mark Ammerman Amy Sheehan Brittany Kravets
Scott Crain Frances Crespi Devon Ingram Christa Gallant
Title Vice President
Scientist Technical Lead-LC/MS
Technician Sample Custodian Associate Scientist
Technician Technician Technician Technician Technician
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TABLE OF CONTENTS
Page
TITLE PAG 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....................................................................................................... 10
1.0 SUMMARY.................................................................................................................... 11
2.0 OBJECTIVE................................................................................................................... 11
3.0 INTRODUCTION.........................................
12
4.0 ANALYTICAL TEST SAMPLES.................................................................................12
5.0 REFERENCE MATERIAL........................................................................................... 12
6.0 DESCRIPTION OF ANALYTICAL METHOD.......................................................... 13
6.1 Extraction Procedure For Sediment..................................................................... 13
6.2 Direct Inject Extraction Procedure For Sediment....................................................... 14
6.3 Additional SPE Extraction Procedure For Sediment..................................................14
6.4 Percent Solids Procedure For Sediment..................................................................... 14
6.5 Preparation of Standards and Fortification Solutions.................................................14
6.6 Chromatography..............................................................................
16
6.7 Instrument Sensitivity.............................................................
16
6.8 Description of LC/MS/MS Instrument and Operating Conditions............................16
6.9 Quantitation and Example Calculation........................................................................17
7.0 EXPERIMENTAL DESIGN......................................................................................... 19
8.0 RESULTS....................................................................................................................... 19
9.0 CONCLUSIONS.........................................................................................................20
10.0 RETENTION OF DATA AND SAMPLES...............................................................20
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Table I.
LIST OF TABLES
Page Summary o f PFOA in Sediment Samples......................................................... 22
Table H. Summary of PFOA in Direct Injection Sediment Samples............................. 23
Table HI. Summary o f PFOA in SPE Extracted Sediment Samples............................... 24
Table IV. Matrix Spike Recovery of PFOA in Sediment Samples.................................. 25
Table V. Matrix Spike Recovery of PFOA in Direct Injection Sediment Samples....... 26
Table VI, Matrix Spike Recovery of PFOA in SPE Extracted Sediment Samples......... 27
Table VH. Surrogate Spike Recovery of UC PFOA in Sediment Samples..................... 28
Table VIEL Surrogate Spike Recovery of ,3C PFOA in Direct Injection Sediment Samples.......................................... ................................................................. .29
Table IX. Surrogate Spike Recovery of ,3C PFOA in SPE Extracted Sediment Samples..............................................................................................................30
Table X. Total Percent Solids in Sediment Samples................................ ..................... 31
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Figure 1.
LIST OF FIGURES
Page Typical Calibration Curve for PFOA in Methanol.......................................... 33
Figure 2. Extracted Standards o f PFOA in Methanol, 25 ng/L and 50 ng/L, Respectively.... ....................................
34
Figure 3. PFOA in Reagent Blank, 0.4 ng/mL Fortified Reagent Spk A, and 4.0 ng/mL Fortified Reagent Spk B, Respectively....................................35
Figure 4. Chromatogram Representing a Sediment Sample Analyzed for PFOA (Exygen ID: CO172892, DataSet: 042806D).................................................. 36
Figure 5. Typical Calibration Curve for 13C PFOA in Methanol....................................37
Figure 6. Extracted Standards o f 13C PFOA in Methanol, 25 ng/L and 50 ng/L, Respectively....................................................................................................... 38
Figure 7. ,3C PFOA in Reagent Blank, 0.4 ng/mL Fortified Reagent Spk A, and 4.0 ng/mL Fortified Reagent Spk B, Respectively....................................39
Figure 8. Chromatogram Representing a Sediment Sample Analyzed for l3C PFOA (Exygen ID: C0172892, Data Set: 042806D)............................... 40
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LIST OF APPENDICES
Appendix A Study Protocol P0000760 (Exygen Study No. P0000760) with Analytical Method V0001782: "Method o f Analysis for the Determination o f Perfluorooctanoic Acid (PFOA) in Sediment by LC/MS/MS", and Protocol Amendments.............................
gg .41
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1-0 SUMMARY
Exygen Research extracted and analyzed sediment samples for the determination of pcrfluorooctanoic acid (PFOA) according to Exygen Method V0001782 (Appendix A).
The limit o f quantitation for PFOA in sediment was 2.0 ng/g.
The standard sediment method (V0001782) was originally used to extract all of the samples. Use o f this method yielded poor spiking recoveries for PFO A Because o f this, a direct injection method (Section 6.2) was used, which also yielded poor recoveries. Finally, an alternative SPE column extraction (Section 6J ) was used to analyze for PFOA and UC PFOA.
Analytical results for the analysis o f PFOA in sediment samples extracted according to the method based on dry weight are summarized in Table I. Analytical results for the analysis o f PFOA in sediment samples by direct injection, based on dry weight, are summarized in Table II. Analytical results for the analysis o f PFOA in sediment samples by alternative SPE extraction, based on dry weight, are summarized in Table III. The overall average percent recovery standard deviation for PFOA in sediment samples based on wet weight was 73 16%. Fortification recoveries for the analysis o f PFOA in sediment samples are summarized in Table IV. Fortification recoveries for the analysis o f PFOA in direct injection sediment samples are summarized in Table V. Fortification recoveries for the analysis o f PFOA in SPE extracted sediment samples are summarized in Table VI. The average percent recovery standard deviation for n C PFOA in sediment samples based on wet weight was 97 27%. Fortification recoveries for ,3C PFOA in sediment samples based on wet weight are summarized in Table VII. Fortification recoveries for ,3C PFOA in direct injection sediment samples based on wet weight are summarized in Table VIH. Fortification recoveries for 13C PFOA in SPE extracted sediment samples based on wet weight are summarized in Table IX.
The total percent solids for sediment samples are detailed in Table X.
2.0 OBJECTIVE
The objective o f the analytical part o f this study was to determine levels of perfluorooctanoic acid (PFOA) in sediment according to Protocol P0000760 (Appendix A).
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3.0 INTRODUCTION
This report details the results of the analysis for the determination o f PFOA in sediment using the analytical methods entitled, "V0001782: Method o f Analysis for the Determination of Perfluorooctanoic Acid (PFOA) in Sediment by LC/MS/MS."
The study was initiated on November 05, 2004, when the study director signed protocol number P000076Q. The analytical start date for this interim report was April 27, 2006 and the analytical termination date for this interim report was April 30,2006.
4.0 ANALYTICAL TEST SAMPLES
Three sediment samples (Exygen ID: CO172892-0)172894) were received on wet ice on April 22, 2006 from Tim Frinak at Weston Solutions, Inc. The samples were logged in by Exygen personnel and placed in refrigerated storage.
Sample login 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 Oakwood Products, Inc. and was received at Exygen on March 17, 2005. The surrogate spiking standard, I3C labeled perfluorooctanoic acid (I3C PFOA SP0004184), was received at Exygen on April 15, 2004 from the 3M Company.
The available information for the reference materials is listed below. PFOA was stored ambient and ,3C PFOA was stored frozen.
Compound PFOA
,3CPFOA
Exveen Inventory No. Lot#
SP0005444
203
SP0004184
3507-195
Purity (%) Expiration Date 99 03/31/07 97 C3/29/09
The molecular structure o f PFOA is given below
PFOA Chemical Name: Perfluorooctanoic acid Molecular Weight: 414
Transitions Monitored: 413 369 (for quantification) and 413 -> 219 (for confirmation)
Structure:
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,3C PFOA Chemical Name: 1,2-!3C perfluoiooctanoic acid Molecular Weight: 416
Transition Monitored: 415 --370 Structure:
6 0 DESCRIPTION OF ANALYTICAL METHOD
The analytical method "V0001782: Method of Analysis for the Determination of Perfluorooctanoic Acid (PFOA) in Sediment by LC/MS/MS" was used for the sediment samples in this study.
6.1 Extraction Procedure Far Sediment
Before the samples were weighed for the extraction, they were mixed thoroughly by vigorously shaking the container. A 5 gram portion o f sediment was weighed into a fifty milliliter centrifuge tube for the extraction. After fortification o f appropriate samples, 35 mL of 1% acetic acid in water was added to the samples. The samples were vortexed and allowed to shake on a wrist action shaker for -6 0 minutes. The samples were centrifuged for ~20 minutes at -3000 rpm. The supernatant was then loaded onto a Cu SPE cartridge conditioned with 10 mL o f methanol and 20 mL of water. The eluate was discarded. Twenty milliliters of methanol was added to the sediment samples left in the centrifuge tube. The samples were vortexed and allowed to shake on a wrist action shaker for another 30 minutes. The samples were centrifuged again for -2 0 minutes at -3000 rpm. The supernatant was then loaded onto the same Qg SPE cartridge. The eluate was collected into a 500 mL Nalgene Bottle. The column was washed with 4 mL of methanol. The wash was collected in the same bottle as the eluate. Approximately two
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hundred milliliters of water was added to the bottles. The samples were mixed by shaking and loaded onto another C u SPE cartridge conditioned with 10 mL of methanol and 20 mL of water. The eluate was discarded. Approximately five milliliters of methanol was added to the cartridge. Five milliliters o f eluate was collected into a graduated 15 mL polypropylene centrifuge tube. Each sample was analyzed by LC/MS/MS electrospray.
6.2 Direct Inject Extraction Procedure For Sediment
Before the samples were weighed for the extraction, they were mixed thoroughly by vigorously shaking the container. A one-gram portion of sediment was weighed into a 15-milliliter centrifuge tube for the extraction. Ten milliliters o f 1% acetic acid in methanol was added to each sample. The samples were then shaken by hand, vortexed, and sonicated for thirty minutes. The samples were then centrifuged for ~10 minutes at -3000 rpm. Each sample was analyzed by LC/MS/MS electrospray.
6.3 Additional SPE Extraction Procedure For Sediment
The samples that were prepared in 1% acetic acid for the direct injection method were used for this extraction. Five milliliters o f each sample was aliquoted into a 50-mL polypropylene centrifuge tube and the volume was taken to 40 mL with water. The samples were then centrifuged for -1 0 minutes at -3000 rpm. The supernatant was then loaded onto a Ct SPE cartridge conditioned with 10 mL o f 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.
6.4 Percent Solids Procedure For Sediment
Percent solids were determined using the procedure indicated in Exygen method V0000427. Approximately 20 grams of sample was weighed into a pan. The weight of the sample plus the pan was recorded. The samples were then dried in an oven overnight at 104 2 C. Then the samples were transferred to a dessicator and allowed to cool for -1 5 minutes. Each sample was then weighed again, including the weight o f the pan. The percent solid for each sample was then calculated. See Table X for percent solids results.
6.5 Preparation of Standards and Fortification Solations
A mixed stock standard solution of PFOA and !3C PFOA was prepared at a concentration of 1000 jig/mL by dissolving 100 mg of each o f the standards (corrected for purity and
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salt content) in 100 mL o f methanol. From this solution, the following fortification standards were prepared:
Cone, o f
Fort
Stock or Fort. Volume
Solution
(mL)
(ug/mL)1
1000
10
100 10
10 10
1.0 10
0.1 10
1o f PFOA and 13C PFOA
Final Volume
(mL)
100 100 100 100 100
Final Cone, o f Fortification Std.
(pg/mL)
100 10 1.0 0.1 0.01
A stock solution o f only ,3C PFOA was also prepared at a concentration o f 100 pg/mL by dissolving 10 mg the standard (corrected for purity and salt content) in 100 mL o f methanol. From this solution, the following fortification standards were prepared:
Cone, o f Stock or Fort.
Solution
(MgfaL)1 100 10 1.0
1o f 13C PFOA
Fort Volume
(mL)
10 10 10
Final Volume
(mL)
100 100 100
Final Cone, of Fortification Std.
(pg/mL)
10 1.0 0.1
A set o f non-extractcd calibration standards containing PFOA and ,3C PFOA was
prepared in methanol, as specified in Exygen method V0001782. The following concentrations were prepared
Cone, o f Fort or Calibration
Solution
Fort Volume
(mL)
- M g L ) 1. 100
1.0
100 0.5
100 0.2
10 1.0
5.0 1.0
2.0 1.0
o f PFOA and 13C PFOA
Final Volume
(mL)
10 10 10 10 10 10
Final Cane, o f Calibration Std.
(ug/mL)
10 5.0 2.0 1.0 0.5 0.2
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The standards at final concentrations of 10, 5.0,2.0,1.0, 0.5 and 0.2 ng/mL were used for calibration. Extracted calibration standards were prepared following method V0001780. 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.
6.6 Chromatography
Quantification of PFOA was accomplished by LC/MS/MS electrospray. The retention time o f PFOA was -11.1 min. Peaks above the LOD were not detected in any of the reagent btank samples corresponding to the analyte retention time.
6.7 Instrument Sensitivity
The smallest standard amount injected during the chromatographic run had a concentration of 0.2 ng/mL o f PFOA.
6.8 Description of LC/MS/MS Instrument and Operating Conditions Instrument: API 4000 Biomolecular Mass Analyser Interface: Turbo Ion Spray Liquid Introduction Interface Computer. DELL OptiPlcx GX400 Software: Windows NT, Analyst 1.4.1
HPLC:
Hewlett Packard (HP) Series 1i 00 HP Quat Pump HP Vacuum Degasser HP Autosampler HP Column Oven
HPLC Column: Thermo Fluophase RP, 50 mm x 2.1mm Column Temp. : -30 C Injection Voi.: 15 pL Mobile Phase (A): 2 raM Ammonium Acetate in water Mobile Phase (B): Methanol
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Time iminl 0.0 1.0 8.0 10.0 11.0 18.0
%A 65 65 25 25 65 65
%B 35 35 75 75 35 35
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Total run time: ~18 min Flow Rate: 0.3 mL/min
Ions monitored:
Analvte
PFOA PFOA Confirm Ion
13C PFOA
Mode
negative negative negative
Transition Monitored 413 -> 369 413->219 415 -> 370
Approximate Retention Time
(min) -11.1 min.
-11.1 min. -11.1 min.
6.9 Quantitation and Example Calculation
PFOA concentrations are quantitated in nanogram o f PFOA per milliliter o f extract and then converted to nanogram per gram. The PFOA concentrations were quantitated in nanogram o f PFOA per liter for Set #3 (Set 042806D). 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 seven concentrations of standards. The concentration was determined from the equations below.
Please note that the equations in this section are presented in a different order than the equations in the method (V0001782), but this has no effect on the final calculations.
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 I:
Analyte found (ng/L) = fPeak 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 and 13C PFOA prior to extraction, Equation 2 was used to convert the amount o f PFOA found in ng/L to ng/g (ppb).
Equation 2:
PFOA found (ppb) ** fPFOA found (ng/L) x SPE volume extracted!
[sample aliquot volume x (sample weight / direct inject sample volume)]
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Equation 3 was used to calculate the percent recovery.
Equation 3:
Recovery (%) =
.
(analvte found (ng/g, wet weight) - analyte in control fng/g, wet weight)! xl00%
amount added (ng/g, wet weight)
Note: For the PFOA recovery calculation, the "control" is the unspiked aliquot of the primary field sample.
Equation 4 was then used to calculate the amount o f PFOA found in ppb based on dry weight.
Equation 4: PFOA found (ppb) dry weight = PFOA found (ppb) x [100% i total solids(%)] An example of a calculation using an actual sample follows:
Sediment sample Exygen ID C0172892 Spk D (Set: 042806D), fortified at 4 ng/mL
with PFOA where: peak area
= 236588
intercept
= 4630
slope
= 420
dilution factor
= 100
ng/g PFOA added (fort level)
= 4000
amt in corresponding sample (ng/g) = 586
SPE volume extracted (L)
= 0.04
sample aliquot volume (mL)
=5
sample weight (g) direct inject sample volume (mL) total solids (%)
=' 1 - 10
= 66.54
From equation 1: Analyte found (ng/L)
From equation 3: PFOA found (ppb)
= r236588 - 46301 x 100 420
* 55200 ng/L
= (55200 ne/Lx 0.04 LI [5mLx(l g/10m L)]
= 4420 ppb
From equation 3: % Recovery
= 0 4 2 0 ng/g - 586 ng/g) x 100% 4000 ng/g
= 96%
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From equation 4: PFOA found (ppb) dry weight = 4416 ppb x (100% / 66.54%)
= 6640 ppb
NOTE: This value may be slightly different than that o f the raw data due to rounding.
7.0 EXPERIMENTAL DESIGN
13C PFOA was used as a surrogate for all the samples. UC PFOA was added to the sediment samples in the laboratoty after the samples were weighed for extraction. For sediment samples designated as laboratory matrix spikes, PFOA was also added at a known concentration to the samples in the laboratory after the samples were weighed for extraction.
The sediment samples were extracted in one set. The set included one reagent blank and two reagent blanks fortified at known concentrations. The set contained three sediment samples. For each sample, two laboratory matrix spikes and a duplicate were extracted.
8.0 RESULTS
Analytical results for the analysis o f PFOA in sediment samples based on dry weight are summarized in Table I. Analytical results for the analysis of PFOA in sediment samples by direct injection, based on dry weight, are summarized in Table II. Analytical results for the analysis o f PFOA in sediment samples by alternative SPE extraction, based on dry weight, are summarized in Table III. The overall average percent recovery standard deviation for PFOA in sediment samples based on wet weight was 73 16%. Fortification recoveries for the analysis o f PFOA in sediment samples are summarized in Table IV. Fortification recoveries for the analysis o f PFOA in direct injection sediment samples are summarized in Table V. Fortification recoveries for the analysis of PFOA in SPE extracted sediment samples ate summarized in Table VI. The average percent recovery standard deviation for l3C PFOA in sediment samples based on wet weight was 97 27%. Fortification recoveries for ,3C PFOA in sediment samples based on wet weight are summarized in Table VII. Fortification recoveries for I3C PFOA in direct injection sediment samples based on wet weight are summarized in Table VIII. Fortification recoveries for 13C PFOA in SPE extracted sediment samples based on wet weight are summarized in Table IX.
The total percent solids for sediment samples are detailed in Table X.
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9.0 CONCLUSIONS
The sediment samples were successfully extracted and analyzed for PFOA using an alternative SPE method, which yielded acceptable QC data.
10.0 RETENTION OF DATA AND SAMPLES
All original paper data generated by Exygen Research that pertains to this interim report will be shipped to the study director. 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 o f PFOA in Sediment Samples
Exyqen ID
C 0172892 C0172892 Rap
C017283 CQ172893 Rap
C 0172864 C 0172894 Rep
Client Sample ID
DAL-SO-BPPOVO-OOOO DAL-SD-BPP01-0-0000*
DAL-SD-BPP02-0-0000 DAL-SD-BPP02-0-0000*
DAL-SD-BPP03-0-0000 DAL-SD-BPP03-0-0000*
Analyte Found (ppb, ng/g) Dry Weight C 8 Acid PFOA
Perfluorooctanoic Acid
NR NR
NR NR
NR NR
Laboratory Duplicate N R = Not reported due to quality control result futures. Sea Table It for re-analysis results.
A sse sse d Accuracy
(+ /-% )
NR NR
NR NR
NR NR
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Table II. Summary o f PFOA In Direct Injection Sediment Samples
Exygen ID
C0172892 C 0172802 Rep
C 01728B3 C 0172893 Rep
C 0172894 COt72894 Rep
Client Sample ID
DAL-SD-BPP01-0-0000 DAL-SD-BPP01-0-0000'
O AL-SO -BP P02-0-0000 DAL-SD-BPP02-0-0000'
DAL-SD-BPPQ3-0-0000 D A L -S D -B P P 03-0-0000*
Analyte Found (ppb, ng/g) Dry Weight CAddPFOA
Perfluorooctanolc A dd
NR NR
NR NR
NR NR
'Laboratory Duplicate N R * Not reported due to quality control result failures. See Table III for re-analysis results
Assessed Accuracy
W -%1
NR NR
NR NR
NR NR
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Table III. Summary o f PFOA in SPE Extracted Sediment Samples
E nyuanlO
C0172882 C0172882 Rap
COI 72883 C O I72883 Rflp
C0172894 C0172894 Rap
Taborakwy Duplicato
CBant
Analyta Found (ppb, ng/g) D ry W aight CB Acid PFO A
D AL-SD -BPP01-0-0000
DAL-SD-ePP0 1-0-0000*
D A L -SD -B P P 0 2 -0 -0 0 0 0 D A L-SO -B P P C 2 -0 -0 0 0 0 *
DAL-SO -BPP03-04000 DAL-SD-BPP03-0-0000-
881 943
627 823
2380 2380
AMM$d
A ccu ra cy - ..
30 30
30 30
3D 30
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Table IV. M atrix Spike Recovery o f PFOA in Sediment Samples
Sample Description
OAL-SD-BPP01-0-0000 cornasi spa o,eoo ppbaprite)
DAL-SO-BPP01-0-0000 fCatTU Sl Spk E, 4000 ppt>Spite)
DAL-SD-RPP02-0-0000 (comas* Spkg, stoppe spike)
DAL-SD-OPP02-0-0000 (Cornaas spk h,4m ppe spike)
DAL-SD-BPP03-0-0000 (catnaps Spk J, 4MppbSpike)
DAL-SD-BPP03-D-0000
(C0171to4 Spk K, 4000 ppb Spike)
Amount Spiked W s)
400 4000
400 4000
400 4000
Amt Found in Sample Inert wst weight
C91,A1dd P".F.OA-
Amount
Recovered (nfl/g)wetweigtit
NR NR NR NR
NR NR NR NR
NR NR NR NR
Recovery (%)
NR NR
NR NR
NR NR
Average: Standard Deviation:
NR NR
Sample residua exceeds Hie spiking level significantly (3< spiking level); mentore, an accurate recovery value cannot be calculated.
NR* Not reported due to quality control result failures. See Table Vtor re-analysie resulta.
Note: Sin ce th is sum m ary table sh o w * rounded resulta, recovery values may vary sligh tly from the vetoes In the raw data.
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Table V. Matrix Spike Recovery of PFOA in Direct Injection Sediment Samples
Sample Description
DAL-SD-8PP01-0-0000 (CC1T7SB2 Spk 0, X ppb Splk)
DAL-SO-BPP01-0-0000
<172882 Spk C,<0000 ppb Spike)
DAI-SD-BPP02-0-0000 (com ae* Spk o, <ooo ppb Spfcei
DAi.-SD-BPP02-0-0000 |cot72aajspk h.<ooooppnspnw)
DAL-SD-BPPQ3-0-OOOQ IC0172SMspk J, 4000ppbSpa)
DAL-SD-BPP03-0-0000
(C0172004 Spk K, 40000 ppb Spite)
Amount Spiked
._(nsft) ...
Amt Found
in Sample (ng/o) we* weight
C B A rid P F O A
Amount Recovered (nafolwet weight
Recovery . _. (%)
4000 40000
NR NR
NR NR NR NR
4000 40000
NR NR
NR NR
NR NR
4000 40000
NR NR
NR NR
NR NR
Average; Standard Deviation:
NR NR
"Sample residue exceeds the spiking level significantly (3x spiking level); therefore, on accurate recovery value cannot be C a la istad.
N R Not reported due to quality oonfeol result failure See Table VI for re-analysis results. Not: Sin ce this sum m ary table sh o w s rounded results, recovery values m ay vary sligh tly from the value In the raw data.
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Table VI. M atrix Spike Recovery of PFOA in SPE Extracted Sediment Samples
Sample Description
DAL-SD-BPP01-0-0000 (C017MM*pk D.4M0n/* Iplk.)
DAL-SD-9PP01-0-0000 (CO iruutpk E. 400Mngfc *p#c)
DAL-SD-3PP02-0-0000 (C017MMCpfca . 4MPn*/pSplk.;.
DAL-SD-BPP02-0-0000 (C01mS Spk M,nos n et Spttal
DAL-SD-BPP03-0-0000 |CH7a.*4 apt J, 400Smyp Splk*|
DAL-SD-BPP03-0-0000 ICO-173*SpVK. 400*0 ng/g Sptkt)
Amount Spiked
4000 40000
4000 40000 4000 40000
Amt Found n Sample
589 589 504 504
1060 1060
ca Aod PFOA
Amount Recovered (ng/g) wot weight
4420 25600
3860 25100
4140 23200
A v *rij : SU n d a rt Deviation:
Recover
96 83 84 61 77 55
7j is
N o t.: S in e thl. aum m ary tabl* .h o w * round* r**u lts. m cov.ry v .lu m ay vary .ligh tly from th* v a lu *. In th* orw data.
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Table VII. Surrogate Spike Recovery o f ,3C PFOA in Sediment Samples
Exygen ID
Sample Description
C0172892 COt72892 Rep C0172892 Spk C C 0172892 Spk D C0172892 Spk E
C0172893 CQ172893 Rap C0172893 Spk F CO I72893 Spk G C O I72893 Spk H
C0172894 C0172894 Rep C 0172894 Spk 1 CQ172894 Spk J C 0 172894 Spk K
DAL-SD-BPP01 -0-0000 D A L-SD -B P P O 1-0-0000 DAL-SD-BPP01-0-0000 DAL-SD-BPP01-0-0000 DAL-SD-BPP01 -0-0000
DAL-SD-BPP02-0-0000 DAL-SD-BPP02-0-0000 DAL-SD-BPP02-0-0000 DAL-SD-BPP02-0-0000 DAL-SD-8PP02-0-0000
DAL-SD-BPP03-0-0000 DAL-SD-BPP03-0-0000 DAL-SD-BPP03-0-0000 DAL-SD-BPP03-0-0000 DAL-SD-BPP03-0-0000
Amount Spiked (ng/g)
4 4 4 400 4000
4 4 4' 400' 4000
4 4 4 400 4000
1lC -P F O A Amount Recovered Wet Weight (no/oi
NR NR NR NR NR
NR NR NR NR NR
NR NR NR NR NR
Average: Standard Deviation:
NR = Not reported due to quality control result failure*. See Table VIII for re-analysf* results.
Note: Since this summary labia shows rounded results, recovery values may vary slightly
tom the value* in the raw data.
7
Recovery
(%)
NR NR NR NR NR
NR NR NR NR NR
NR NR NR NR NR
NR
NR
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Table VIH. Surrogate Spike Recovery o f C PFOA in Direct Injection Sediment Samples
Exv s en ID
-------
CO172892 COI 72892 Rep C O I72892 Spk C C 0172892 Sp k D C0172892 Spk E
C0172693 CO172893 Rep C0172893 Spk F C0172893 Sp kG C0172893 Spk H
C0172894 C0172894 Rep C 0172894 Spk 1 C0172894 Spk J CO172864 Spk K
Sample Description
- ..... -
DAL-SD-BPP01-0-0000 D A L -S D -B P P 0 1 -0-0000 D A L -S D -B P P 0 1 -0-0000 D A L -S D -B P P 0 1 -0-0000 D A L -SD -B P P 0 1 -0-0000
DAL-SD-BPP02-0-0000 DAL-SD-BPP02-0-0000 DAL-SD-BPP02-0-0000 DAL-SD-BPP02-0-0000 DAL-SD-BPP02-0-0000
DAL-SD-BPP03-0-0000 DAt-SD-B PP03-0-0000 DAL-SD-BPP03-0-0000 DAL-SD-BPP03-0-0000 DAL-SD-BPP03-0-0000
Amount Spiked (09/9)
40 40 40 4000 40000
40 40 40 4000 40000
40 40 40 4000 40000
wC-PFOA Amount Recovered Wet Weight
t^g)
NR NR NR NR NR
NR NR NR NR . nr
NR NR NR NR NR
Average: Standard Deviation;
NR = Not reported due to quality control result failure. See Table IXfor re-analyjis result*. Note: Since M s summary table shows rounded results, recovery values may vary slightly from the values In the raw data.
Recovery
<%)
NR NR NR NR NR
NR NR NR NR NR
NR NR NR NR NR
NR NR
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Table IX. Surrogate Spike Recovery o f ,3C PFOA in SPE Extracted Sediment Samples
Exyoan ID
C O '72662 C0172892 Rap C O I72892 S p h D C0172892 Spk E
C O t72893 C 0172893 Rap C 0 172883 Spk G COI 72893 Spk H
C01728M C0172894 Rap C O I72894 Spit J COI 72894 Spk K
Sample Datcriplion
DAL-SD-BPP01-0-0000 OAL-SD-BPPOI -0-0000 0AL-SO -8PP01-0-0000 DAL-SD-8PP01 -0-0000
DAL-SD-BPP02-0-0000 DAL-SD-B PP02-0-0000 PAI.-5D-8 PP02-0-0000 DAL-SD-BPP02-0-0000
D A L-SO -BP P0 3-0 -0 000 DAL-SD-BPP03-Q-OQOO D A L-SD -0 P P O 3 -0-0000 DAL-SD-BPP03-0-0000
Amount Spiked (OB'S)
40 40 4000 40000
40 40 4000 40000
40 40 4000 40000
" C-PFO A Amount Recovered W ei Weight <n*9>
52.0 51.0 3750 26800
47.8 51.8 3500 25200
45.2 40.3 3060 22100
Not. Sine#thttaumrrarytablethan roundedreaulte,recoveryvetoes(rayvarygMly fromthevalueIntherawdata
Average: Standard Oevlatlen;
Raoovary (%>
130 128 94 85
120 129 86 63
113 101 7? 55
97 27
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Table X. Total Percent Solids in Sediment Samples
Exygen ID
C0172892 C0172893
CQ172894
S am ple D escrip tio n
D A L -SD -B P P C 1-0-0000 D AL-SD-BPP02-0-0000
D A L-SD -BPP03-0-0000
T o tal S o lid (% ) 6 6 .5 4 5 4 .3 7 4 4 .4 6
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FIGURES
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Figure 1. Typical Calibration Curve for PFOA in Methanol
i 0439000 Sad. SPE.rd* (PFO*> "Una a f
p 7 * MMi|Mt*g y 420 v + 4 63*0Q3 0 - O.QOQ9)
Area, counts
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Figure 2 . Extracted Standards of PFOA in Methanol, 25 ng/L and 50 ng/L, Respectively
I jVCM ZIN*f-PNM ( R W d l^ ^ U N M llM r MMpJff 2 ofM tr*m M N ia w iT T Art#.* n z M w f f i m fgm s f .? 6 t+ M 3 q PT? 11.01
I XjC042609-2 PFOA CStr4Jd) 4134X063X1 *m<j - u n p l i 3 t 48 Item 0428090.** Area: 26169 eeunb H*iiht2.14**<J03 M RT:11.1 min 11J06
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Figure 3. PFO in Reagent Blank, 0.4 ng/mL Fortified Reagent Spk A, and 4.0 ng/mL Fortified Reagent Spk B, Respectively
I ftM fM t Cortiv! -PFOA fUM mm)4txeaa.M amt -tsrnflU t a f jf f t vm HltM Omm >'**4mmm0
1TOO
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Figure 4. Chromatogram Representing a Sediment Sample Analyzed for PFOA (Exygen ID: C0172892, Data Set: 042806D)
I cAirnru: 3n342p*feoeaw(tur*HJt*riefvUn:)4iTnf.cia.Ont.ttcspm*aR7i n.*mittu rrom um tosum
11XM
intansty, cps
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Figure 5. Typical Calibration Curve for ,3C PFOA in Methanol
042006b SihL S P E .d f c C ^ PrCAfc
fUgj&alerts^t JVMriQhUpg): ym 4 0 8 x 0.0 0 1 0 (r 0.0000)
Afea, tourte
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Figure 6. Extracted Standards of 13C PFOA in Methanol, 25 ng/L and 50 ng/L, Respectively
XC U H $*1 tiC P fO {5 tsm fs* )4 1 lP 3 7 * .9 * m *
Am: 1T901****** m igAt:
R 7:11.$min
l* f4 tm m 042tMttwfflr
11.0Q
intensiv, cpe
intensiv, cpe
A**: 26803
2000 1500. 1000
50-
H%ijM:2.^e+CC3 9f *7:11.1 min
11.00
7 7# # ^ o S ! L
9 10 Tin*, min
i
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Figure 7.
,3C PFOA in Reagent Blank, 0.4 ng/mL Fortified Reagent Spk A, and 4.0 ng/mL Fortified Reagent Spk B, Respectively
I t>*t* !**</)ftM fM t Cettrol - rSCPfOA fM ttttm ) 4Ti.V3Tt.ttm -ttm ph tv ftffr rm te fM O w tff
.a .
1 2 4 4 S 0 7 0 10 H Tim*, min
I ft9rrt$-pfcA- 13C PFOA (O C )419.0/370 0 im u - Mfttpl 10 of 40 from O42BQO0 Mlir Am: 2720Q oountr H eigh t2,021+083 <%rt *T : 11JD ml
12 13 W
13 IS
17
1101
11SST
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Interim Report #23 - Analysis of Sediment Samples
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Figure 8. Chromatogram Representing a Sediment Sample Analyzed for 13C PFOA (Exygen ID: C0172892, Data Set: 042806D)
I C H T H 92 *3C P F Q A
raw MMpfe 2T o f 4SfhM i
A rt*; 3 M H 7 cra/rbr HtfgMtzZ9U+094*p9 XT; 11,1mis
2 8*4
11JD7
2.0*4.
2.4*4.
2.2*4
2.0*4.
10*4-
1.6*4
1.4*4-
1.2*4-
1.0*4-
6000.0
60000
40000
2000.0
0.0 J-------- --- ---- 1--------1--- --------------- ---- '-- ---- --------- 1-------- ----------1 1 1 2 3 4 6 6 7 8 9 10 11 Tim*. ml*
" -------- --------- .-------- 1-------- J-------- r12 13 14 13 16 17
Intensity, cps
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APPENDIX A
Study Protocol P0000760
(Exygen Study No. P0000760) with Analytical Method and
Protocol Amendments
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Exygen Study No.: P0000760
Exygro Protocol Num ber POOOQ7IO
STUDY PROTOCOL
Study Title: Analysis of Perfluorooctanoic Acid (PFOA) in Water, Soil, Sediment, Fish, Clams, Vegetation, Small Mammal Liver and Small Mammal Serum Using LC/MS/MS for the 3M Decatur
Monitoring Program
Exygen Protocol Number: P0000760
Parfotmina Laboratory: Exygen Research 3058 Research Drive Stale College, PA 16801 Phone: (814)272-1039
Sepbioc Representative: Michael A. Santoro Director o f Regulatory Affairs 3M Building 0236-01-B -10 St. Paul, MN 55144 Phone:(651)733-6374
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JExyyeitProtocol Number P000076C
DISTRIBLTION: 1) Jaiiimhx K snri, Stady Director, Western Solutions 2) John M. Waherty, Principi) lnvestigalor, Exygen Xeaoirch 3) M ichui A. Samolo, Sponsor Repreienwtivo, 3M Company 4) Exygen Research Quality Anunmee Unii
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Exypo ProtocolNmb P000076Q
PROTOCOL APPROVAL Study Title: Analysis or Perfluorooctanoic Acid (PFOA) in Water, Soil, Sediment, Fish.
Clami, Vegetation, Small Mammal Livers and Small Mammal Serum Using LC/MS/M5 for the 3M Decatur Monitoring Program Exygen Protocol Number: P0000760
APPROVALS
Jaiam&i Kesari, Study Director Weston Solutions
Michael A. Saniro, Sponsor Representative 3M Company '
Exygen Research
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Exyjen Protocol Nuntfeer. POOW7&0
TABLE OF CONTENTS
distributio n _______________________ _____ _________ ____,, . ________________ .,,2 PROTOCOL APPROVAL--------------------- ----------------------------------------------------------------- 3 TABLE OP CONTENTS ___________ . ______________________ - ........... ......................... 4 INTRODUCTION------------------------------------------------------- --- --------------------- -------- ----- TEST MATERIAL____________________________________ _______ ______ ______ ___ _ J SURROGATE FIELD SPIKE COMPOUND___________ __ _______ ________*.________ _____ 5 OBJECTIVE___________________ ___ _____________ ____________ _______ __________ 6 TESTING FACILITY_____________ ___ _________ ____ ...................................................... .. 6 STUDY DIRECTOR.......................................................... ........ .................... ...... .............. ............6 SPONSOR REPRESENTATIVE............................................................. .......................................... 7 PRINCIPAL INVESTIGATOR ...................... .................... .................................. ........... ......,,... 7 PROPOSED EXPERIMENTAL STARTANDTERMINATION DATES.................. ..............................7 IDENTIFICATION AND JUSTIFICATIONOP THETEST SYSTEM............... .......................... ........7 SAMPLE PROCUREMENT, RECEIPTAND RETENTION ........ ................................. .....................g SAMPLE IDENTIFICATION................. ................ ...................................... ............ ..................... 8 ana ly tica l procedure sum m ary__________ ___ _____ ______________ _____ ___ 9 VERIFICATION OP ANALYTICAL PROCEDURE................... ........................ ................................9 METHOD FOR CONTROLOF BIAS............................................................................................... 11 STATISTICAL METHODS......................... ........................ ............................................ .......... II OLP STATEMENT.......................... ........................... .............. ............................... ........ .......... 11
SAFETY AMD HEALTH....................................... ........... ........ .................................................... 12 AMENDMENTS TO PROTOCOL....... ........................... ....... .......... ............... ............................... 13 DATA RECORD KEEPINO.................. ........................... ............. ................. .......................... 13 QUALITY ASSURANCE_____________________ _______________________ _______ ____ 14 RETENTION OF DATA ANDARCHIVING _______________________________ ____________14 APPENDIX l. ANALYTICAL METHOD__ _____________ ____ ____________ _____ ______ IS
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Exygas Protocol Numb-. P0000760
INTRODUCTION
The purpose of thil study is to perform analysis for perfluoroocunoic acid (PFOA) in water, toil, sediment. flab. clams, vegetation, until mammal livers and email mammal serum using LC/MS/MS for the 3M Decatur Monitoring Program.
The study will be audited for compliance with EPA TSCA Good Laboratory Practice Standards 40 CFR 792 by die Quality Assurance Unit of Exygen Retouch.
TEST MATERIAL
The teat material it perfluorooctanoic acid (PFOA) and w at purchased from Sigma-AUtrich.
PFOA Chemical Name: Perfluorooctanoic acid Molecular Weight: 414 Lot Number 23116HB Purity: 97.64% TranaiUona Monitored: 413 -+ 369 (for quantification) and 413 -*219 (for confirmation) Structute:
SURROGATE FIELD SFERE COMPOUND
The starsgate field aptking compound ia UC labeled perfluorooctanoic acid (llC PFOA) and wa* purchased by 3M from Perkin-Elmer Life and Analytical Scieooea.
"C PFO A Chemical Name: 1.2-13C petfluorooctaaaoic acid Molecular Weight: 416 Lot Number. 3507-19S Purity. 97% Transition Monitored: 415 -v 370
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Exyjeu Protocol Number; 1*0000760
o b je c t iv e
The fiuipote of (hit study it to perforin analyst for perfluorooctanoic acid (PPOA) in water, toil, aedintem, fith, dama, vegetation, muli mamma] liven and sudi mammal tenui for the 3M Decatur Monitoring Program using the current vottoni of(tie following Exygen analytical methods
V0001780: "Method of Analyst for the Detominilioo of Perfluorooctanoic Add (PPOA) is Water by LC/MS/MS'*
V0001781; "Method of Analyeit for tie Detenninaiioti of Perfluorooctanoic Acid (PPOA) in Soil by LC/MS/MS"
V0001782: "Method of Analyst far fot Determination of Perfluorooctanoic Add (PPOA) in Sediment by LC/MS/MS**
V0001783: "Method of Analyst for the Determination o f Perfluorooctanoic Acid (PPOA) in Pith and Clams by LC/MS/MS**
VQ001784: "Method of Analyst for foe Determination o f Perfluorooctanoic Acid (PPOA) is Vegetation by LC/MS/MS"
VG001785: "Method of Analyst for foe Determination of Perfluorooctanoic Acid (PPOA) in Small Mammal liv er by LC/MS/MS**
V0001786: "Method o f Analyeit for the Determination of Perfluorooctanoic Add (PPOA) in Small Mammal Scrum by LC/MS/MS"
TESTING FACILITY
Exygen Research 3058 Rotearci) Drive State College, PA 16801 Phone: (814)272-1039
STUDY DIRECTOR
Jaitimha Cestri P.B., DHE Wetton Sohitiona, Inc. 1400 Weaton Way Weal Cheater, PA 19380 Phone: (610)701-3761 Pa*; (610) 701-7401 jAe$ari@weatemohition5.c<xn
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Eyjso Protocol Nwnbtr. W000760
SPONSOR REPRESENTATIVE
Michael A. Sentore 3M Company Director ofRegulatory Affaire 3M Building 0236-01-B-10 St. Paul, MH 55144 Phone: (651)715-6374
PRINCIPAL INVESTIGATOR
John M. Flaherty Exygen Reaearch 3054 Research Drive Sure College. PA 16801 Phone: (814)272-1039 john.flaherty@exygen.com
PROPOSED EXPERIMENTAL STAKT AND TERMINATION DATES
U ir promoted that (he analytical portion of (hit atudy be conducted from October 01, 2004 to December 11, 200$. The actual experimental start and termination dates will be included in the final report.
roENTTFICATION AND JUSTIFICATION OF THE TEST SYSTEM
The following are the teat system! for thia study: Water (groundwater and surface water) Soil Sediment Fiah Ciana Vegstaticn Small Mammal Liver Small Mammal Seram
The samples will be collected by Weston Solutions. The control sample will be purchased and prepared by the toting facility. Purchase and processing
Pm pivfts
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details far toe control sample* will be included in the final report associated with this study.
The test systems won chosen to access the environmental impact o f PFOA in the Decatur, Alabama area.
SAMPLE PROCUREMENT, RECEIPT AND RETENTION
W at; aoil. aedimoA fish, clam, vegetation, small mammal liver and small mammal actum samples will be received at Exygen directly from Weston Solution*. The details o fsample procurement for this study ar* outlined in the 3M wodt plan entitled `This 2 Wot* Plan for Sampling Environmental Media." The numbs and types o f samples collected will vary depending availability in the field. The total number o f samples received and analyzed for each matrix will be documented in the final report associated with this study.
Water, soil, and sediment samples will be used aa received without further processing at Exygen. These samples will be stored refrigerated at 2C-8,>C. Fish, dam , vegetation and small mammal liver samples will be processed according to the appropriate analytical method (see Appendix 1). These samples will be stored frozen at S -1D*C. Small mammal whole blood samples will be centrifuged in the field at the time o f collection and the serum fraction will be used for the study. Small mammal scrum will be stored frozen at S-10*C
The receipt and processing o f foe samples will be documented in the final report and raw data associated with the study.
SAMPLE IDENTIFICATION
Prior to analysis, each sample will be assigned a laboratory sample reference number. The reference number will be unique and will distinguish each laboratory sample that is processed throughout foe analytical procedure. Chromatographic data will be identified by foe laboratory sample reference
Sample storage ccoditiona and locations will be documented throughout the study.
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Eaygea FrancaiNumber POOOOTHO
ANALYTICAL PROCEDURE SUMMARY
Reference: V000I78Q: "Method of Analysia for the Determination of Perfluorooctanoic
Add (PFOA) in Water by LC/M&MS" V0001781: "Method of Analytic for die Detennination ofPerfluoroocianoic
Add (PFOA) in Soil by LC/MS/MS" V0001782: "Method of Analytit for the Determination o f Perfluorooctanoic
Acid (PFOA) in Sediment by LC/MS/MS" V0001783: "Method of Analysis for the Determination of Perfluorooctanoic
Add (PFOA) in Fish and Clam by I.C/MS/MS" V00017M: "Method of Analytit for the Detennination o f Perfluorooctanoic
Acid (PFOA) in Vegetation by LC/MS/MS" VC00178S: "Method of Analytit for the Detennination of Perfluorooctanoic
Acid (PFOA) in Smtll Mammal Liver by LC/MS/MS" V0001786: "Method of Aaalyait far the Determination of Perfluorooctanoic
Acid (PFOA) in Small Mammal Serum by LC/MS/MS"
The above methods use analytical condition capable of separating the isomers of PFOA. The final report will include the isomers summed into total PFOA found.
VERIFICATION OF ANALYTICAL PROCEDURE
A laboratory control sample will be used for the preparation of fortified control samples. The teat tubttaoce will be made into solutions as per the method, and added to the matrices via a micropipette.
For water sampling, Exygen will supply one bottle per sample collected. The bottle will be 500 mL precleaned Sci/Spec Premier wide mouth HDPE bottle*. The bottles have been routinely used far PFOA ample collection at the totting facility and have been thown to be free o f PFOA. All oontainera used for water sample collection will be shipped to the sample location containing 100 eg of ,JC PFOA (equivalent to 500 ng/L in the final sample). Suimle* wiS bo added to each contain la volumetric fill liiw at 200 mL A
field duplicate, a tow field spike and a high Celd spike of each sanqsie will be
collected. The low and high field spikes will contain PFOA u well as perfluorobatanesulfbntte (PFBS). perfluorohexanetulfooate (PPHS), and pcrfiuorooctaneaulfonate (PFOS), These compounds are included in the solutions used to spike the simples. The results for PFBS, PFHS and FFOS will not be reported is this study. Exygen will supply one field blank (control water) and two field blank pikes (controt water fortified with PFOA at a low
Pagt 9 o j 65
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Exygen Study No.: P0000760
Exypo Protocol Niunbei: P0000760
and high level) for every twenty samples collected. At the testing facility, each water temple (excluding field duplicates and field spile) will be
extracted in duplicate and will also be fortified at a low and high concentration with PPQA and proceasod through the described procedure to determine method accuracy and to check for b is.
For oil, sediment, clams, and vegetation, Exygen will supply one 500 mL proctamed Sci/Spec Premia wide moutb HOPE bottle per simple collected or a zip-seal bag. All coatainerWbags used for sample collection will be shipped to the sample location. Sample* will be added to each container or bag in the field.' At the testing facility, each sample will be extracted in duplicate and wilt also be fortified at a known concentrabou with PFOA at both a low sod high level and processed through the deecribed procedure to determine method accuracy and to check for bias. u C-PPOA will also be added to each sample in the laboratory prior to extraction at foe level specified below.
For email mammal liver, Exygen will apply a $0 mL polypropylene centriftige tube. For small mammal scrum, Exygen will supply a collection kit for each ample cmdasning serum separator tub (ted lop), vacuiamers. needle holders and needles, transfer pipettes, and polypropylene tub At the testing facility, each Eves and serum sample will be extracted in duplcate and will also be fortified at a known concentration with PFOA at both a low sod high level and processed through foe described procedure to determine method accuracy and to check for bisa. u C-PFOA will also be added to each simple is the laboratory prior to extraction at foe level specified below.
low and high spfldng levels for each matrix are defined below:
M atrix
Low PFOA
High PFOA
,JC-PFOA
Spiking Level SDiktat Level Spiklut Level
Water
S00bs/L
5000 nj/L
500 ngfiL
Soil
40ng/g
40ng/g
Sediment
4ng/g
40ng/g
40 njFg
Fish
lOngfg ...... lOOngfg
lOOng/g
Cisma Vegetation
lOngfg lOngfg
.... lW .M fc ..... I00ng/g
lOOng/g 100ng/g
Small Mammal Liver
lOnglg
lOOng/g
lOOnf'g
Small Mammal.Semin
lOngfg
lQOng/mL
100ng/mL
Reeovaries we anttcipatad to tie between 70k end 130% of the fortified levels; however, the exact precision and accuracy will be determined by the analysis of foe quality control aaraptos described above. A statement of accuracy will be included in the final repost.
Print to sample analysis, a laboratory control spike itudy will be conducted in wrier to justify the use of 13C PFOA results to establish precision and accuracy of PFOA samptat. The foliowing ismplei are to be prepared
Pa$* /o f S
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Exygen Study No.: P0000760
E xygta Protocol N um ber POO076O
control wtftfMtflk Two control water samples fortified el 250 ng/L with 1}CPFOA Two control waterample# fortified at 250 ngfL with UC PFOA and at
250 ng/L with PFOA. Two control water ample fortified wl 5000 s^ L with " C PFOA and
I 5000 ng/L with PFOA. The hove ample are to be extracted and analyzed according to method V0001780 entitled "Method o f Analyiia for tbs Determination of Pcrfluorooctsnoic Add (PFOA) in Water by LC/MS/MS*
METHOD TOR CONTROL OF BIAS
Control of bias wit] be addressed by taking representative sub-samples from a homogeneoua mixture of each matrix from untreated control ample, and by analyzing at leaal two levels of fortifications.
STATISTICAL METHODS
Statistics will be limited to those specified in the subject methods and to the calculation of average recoveries, as applicable.
GLP STATEMENT
All aspects of this study shall be performed and reported in compliance with EPA TSCA Good Laboratory Practice Standards 40 CFR 792. The final report or data package (supplied to die Sponsor) d u ll contain a statement that the study was conducted in compliance with current and applicable GLP standards and will outline any deviations in the study from those standards. This sutemort will be signed by the Study Director and Sponsor Representative.
RETORT
A final report will be prepared by the principal investigator or their designee at the conclusion of the study. The report will include, bur wtu not be limited to, the following;
Paf* II ofts
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Exygen Study No.: POOOO760
I x r tta Protocol Number: W 000760
The name and address of the Study Dinxto, Sponsor Representative, and ofthe letting faciJtty.
A statement of GLP compliance (any related documentation, inch as chaln-of-custody record, meat be in die study records).
.. The signed and dated etatement by the Exygen Research Quality Assurance Unit regarding dates of study inspections and dates findings were reported to the Study Directorand Management.
A description of die exact analytical conditions employed in the study, (f the subject method was foBowad exactly, it is necessary to include only a copy of the analytical method. Any modifications to this method wilt be incorporated into the report. If the method is photo-redaced, the project number end page number mustbe included on each page.
Description o f`die instrumentation used and operating conditions.
AD results from all sets analyzed. Control and fortified samples will be identified and the data table will include sample number and fortification level.
Representative chromatograms for each analyte in each matrix, including chromatograms ofa standard and a control sample, and a chromatogram at a fortification leveL The location of the analyte peaks will be clearly identified in all chromatograms.
All circumstances that may have affected the quality or integrity o f the data will be documented ia the report.
Locations where raw data and the final report are to bo arehivod.
Additions or corrections to the final report shall be in the form of an amendment signed by the Study Director. The amendment shall clearly identifythst part of the report that is being altered and the reasons for the alterations. Tbe amendment will be signed and dated by the Study Director and tbe Sponsor Representative.
SAFETY AND HEALTH
e Laboratory personnel will practice good sanitation and health habits.
Every resaonable precaution shall be taken to prevent inadvertent exposure of penmans] and the environment to the test or reference subttance(s).
Page 12 o f61
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Page 53 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number P00007SO
r * AMENDMENTS TO PROTOCOL
AO significant changes to die analytical protocol outlined here will be expressed in writing, signed and (Uted by the Study Director aid Sponsor Reprisenative. Amendmeeti usually will be iaauod prior to initiation o f study
plan change. However, what a change it required without sufficient time for the iaauo of a written amendmau, Out clung may be effected verbally with lupporting documentation signed and dated by the Study Director and followed with a written amendment a toon aa possible In this esse, the effective date of the written amendment will be the date o f the documented change. Cepiee o f foe riffled amendments will he appended to all distributed tudy plan copies. The original amendment will be maintained with the original study plan. Any deviathma from foe study plan or from the analytical method as provided will be documented and reported promptly to the Sponsor Representative.
DATARECORD KEEPING
Records to be maintained include the following (as appropriate):
Sample tracking aheet(s)
Sample receipt records, storage history, and chains o f custody History and preparation o fstandards (stock, fortification, calibration) Description o f any modifications to the method Instrument run sheets, bench-sheets or logs Analytical data tables All chromatographic and instrumental conditions Sample extraction and analysis dates A ccmplete listing ofstudy personnel, rignatures and initials Chronological presentation of all study correspondence Any other documentation necessary for the reconstruction of the study
Chromatograms- An chromatograms will contain the following:
Sample identification, injection date, arrow or other indication o f the area of interest, sad injection number corresponding to the run.
Additionally, fortifications will include foe mount o f analyte added and foe sample number offoe sample that w it fortified
Analytical standard chromatograms will additionally concentration (e.g., jig/toL).
the
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Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exyg Protocol Number F00007C0
. As part of the documentation the following sheets will be included in each uulyticsl set; run sheet fating tbe sample* to b cru n in th eset.u K l* n instnimenl conditions sheet describing the instrument type and operating conditions.
All applicable requirements tor reporting of study results as per 40 CFR
QUALITY ASSURANCE
The QA Unit of Bxygen Research will inspect the study at intervals adequate to usure compliance with GLP's, tnd wifi report the findings of audits to the Study Director. Exygea Management, n d tbe Sponsor Representative.
RETENTION OF DATA AND ARCHIV ING
All hud copy raw data, including, but not limited to. the original chrmnatogranu. worksheets, correspondcnee, and results shall be included with the data package submitted to the StudyDirector. These will be archived with the original study p in , amendments, final report, and all pertinent information from the Sponsor.
The testing facility shall keep all electronic raw data and any mstniment, equipment, n d storage logs for the period of time specified in 40 CFR 792.195. An exact copy of the materials submitted to the study director will also be kept at Exygea Research.
Exygon will obtain permission tom tho study director before discarding or returning samples.
Exygen Research
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Exygen Study No.: P0000760
Exyfen PKHQcat Number. POOOC760
APPENDIX I
ANALYTICAL METHODS
V0OQ1780: "Method o f Analyst for the Determination of Perfluorooctanoic Acid (PFOA) in Water by LC/MS/MS"
V0001781: "Method o f Analyst for the Determination of Perfluorooctanoic Acid (PFOA) in Soil by LC/MS/MS"
V0001782: "Method of Analyst for foe Determination of Perfluorooctanoic Acid (PFOA) in Sediment by LC/MS/MS"
V0001783: "Method of Analyst for the Determination of Perfluorooctanoic Add (PFOA) in Fiah and Clama by LC/MS/MS"
V0001784: "Method of Analyst for foe Determination of Perfluorooctanoic Add (PPOA) in Vegetalion by LC/MS/MS"
V0Q017&5: "Method of Andys* fot the Determination of Perfluorooctanoic Acid (PPOA) in Small Mammal Liver by LC/MS/MS"
V001786: "Method of Analytic for foe Determination of Perfluorooctanoic Acid (PFOA) in Small Mammal Serum by LQMS/MS"
Exygen Research
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Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
E xygn Protoooi Number; 0000760
/***
A H A IY D C A L METHOD
M M to k e VDMI7W
* * * * * * * Om nill.u I i r f rT* WNwrlwulA M (fT O A f k V lttr IjllOM Ha
bn B lam d MBKu w ch Oriv teO rta*FAIi0i
Afpmtdly;
f_ J.L
fmalICCmammoUilyr
'
TutaimlLMr.tCW, b )p tom it
SfesM
'p?/JmT ______ __
/M m TU bm f 7 ' Ve rxndml. Opmiom, b y m
-j& k-
Exygen Research
ToalP^m: 7
ta g t I t oft}
Page 57 of 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No,: P0000760
Ejrygt Protocol Number. P000076G
Vjff l Unmh
U iM M itW ilig
I -! ,-ft-:.ft.rft.TtrvnHTA---Lrfynn-cf*f!yMll,i,TIn,,,ona,,!, Ad (TFOA) in W w
LOUMa
l>u mw1
,* , ei* wl^wdiei,
" * * W * l t w bkjiM r b w w im iliy M | U < andem M w
l| * o w * Owe* (LCMSM9 m .
U Mttjr
ll Alwy nhti mh liinn)'pwuim,
).o T--hnm.in--rt
3.1 AtlMM*tfcL4ftaiainc4fcrcmctfc&
y.i Ha ii wy k
mm
3J *m jm n i lafeamtM Mid * aJWvid *qui!csic to won
mjMCtMM.
X4 All
i l k thnriinMyahtid bdbw bw f rampbd feewfaw
3.3 A3M 0 OTtfiWai prirfw * * i bf
u -3900 pm ter -3
wdH aal ft M^vMiaatMd<mUmmvkUm .
U 5aa*J* colaciioA ffocadra wiBbe j e tte d io * t anpUiii pi* far fet
4.0 AaafsntavdSteidaada
AI Waiar-lffLCfnub 4J idi-- l -PLCy*d> J A M diM A iM e.A C i.iN |iD (G r^ A4 hiHwimwiiiiiiii Acid~ 8tp u AMricfc
10
3.1 A feJjh >r t w m ^ad * m Uo^ H opatM af poopia* up *> ?
o h <w ed ^ v a ii^ le ie * eteeer Mpeble ef iaieesfis IX*)
13 Kl e w iri s Iw d* Mw ly e e a n w <LOMSAO). Adrmc m taa am dtf* ftrpaak ia b p u a art qunuwioa
3.3 Aatiyiied W i**ca|M #aimdh|to0Lfl000l *
II 30mL dhp-- Hoplxanpylm nwHhftp mim.
5J llaLBlT--MiylUWtpyln ra--iftptaba*
id Puy-- bWrwrrp p ir. (SD-MOal ttteOOaU ii U^wtUggwrow lawrtkai.
1IjuSf1i0
liaLrtaarHPtCitait*.
AwpiyW*(WHIOO|iLerflO.IOO^U
W aai% takVae6c(3|)iClf OTIcartridpa.
tip*.
A|ff t7of6)
Exygen Research
Page 58 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exyten Protocol Number: P0000760
Uip .1--- e
I
w uuutw,vWti?t<)
AjwiyncALMtnw ...
|
HidCrAidieefcfeCw lMdm N>fleiean eile AcM(WOA)iiyiietty um tm
Mi a iw -- iiiiM t
l.U Owrtfcp m e>l f X L ro irp a vjm * Mb y w o tT
*0 Omi ilm > iig j n
11 Amb^iwIOib-- :WiiiflmeP(IC )elM |tiK ae^ t l m i H i m , tu
(MNitntsumjD) 12 te p w K *rc 11 tM 0eneW : l e U 2 i W V
4. tM e n u a P )-. HrtKmil U (lw i ) > W f :
Vm0S21m A
14 14 000 23 5
HA <1 <5 25 65
FW lau
Hl 35 0.1 35 0.3 15 03 M 1 35 0 1
<.f h^etiee V tte er |5nL (cobincra--<l to * > 30 nt). 4.T foiWtaM, h tk An* - atonal *tawl*4Mlibmion carve. M Rm TSm ; -2 3 mmm.
/ " * l^a*mv<HtitSwema4sdiii|ideedmiyiekiayduigrtti ytfadmWKTlC ryiiim.
7 0 MSMCSjM m 7.1 M W
TU * * nHdhic * iacttM m fuiU a d n iy b <W pd a wfc* oftmm Om MBMS .
I4> hfMntrSilMiNi 4.1 MbUkMu
X.1.1 Z mM H M M M aW a water s p f p--rd Oy a ttis f ft 154 g *f
emdiei i1066eU,efwwir. AUnnh 'iiwl--iw--yUn^piwd.
Exygen Research
Patt18oftf Page 59 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Bxyftct Protocol Kombor. P000076Q
Mnhfadof
ANALYTICAL MCTBOft
rbiirwiiuiwicfywrfWc>rOiin<irAridfffOAiWurby LGWS/M5
0.1.1 FMvweiowkrnfabooof-IOlita^LermXAkywm^BnslOn^
of iljrin l riwilwd (towwHd f a yohty) dilute ICOm i wnh
wflwwt Io 12$Li m bo.
L U A IOj#riaLfadld iiW m of PTOA frpwpwwl by&ofttm lu
*Lof*160#nA*l>wli*looloa6*l vekwof I wiii iaaUInLIJPPf bMtt.
f.lj Am1LJ>ouftfoa1l0f>a*ifitfolLaattrkiuwtiwototfocoofoafrPiPO!A)if*pw?1p0f0dwbiy*brtnitmlmbItmn
kl3S*LL0rb0tte.
0X4 A0.1
fcitilWtoi f a i n afPfO * U p ry w d by fa* Hi
aiLaM* >^|ifhpLlwkwoaiPriiflhwMf IQOwOi *< in
laSaLLMMOa
.1J AM l pgfaL fatiferiMB Mfafai ofPPOA b pifarfa Oybriafi 10 mL Of fa (X! |i#M. MriHtiOB10 4 flMl rataKWf IOQWttti
mAhmIw IV m L U M b tU t.1.4 TVnodr ad faiflntoiawk WAomtob otod A4ratkfVMOf at
topmfadriy#C faM iffaofa wum pwwd oft smmas fa Jd*tfpiayriiij.
92 StandardCabntuaIm m
XI LOMSMI rritofak m r iM t m y y d HPLC au* Tb* lArtti--Mdardt we ptocfftcd ttoa0fc tfa curacy prcdur. idandod ipto yloa.
0X2 Tin fcttowiff it a tjjk ti u m t# m adflHocrt rpnraudoat nay b*
0ml
CaaoMniw ftwiflniM V fam af C w t r i a r f
T M ta d a VoiMtt ftrtHfaftottal C U ta t e
SafafatfaN fvU M a in O j 3tMdH<A*y
40
b
1 40
25
(4 M0 40
SO
I 4M 40
IM
Mft |M
4
0
100 m
40
J40
_____i s ____ 4M ______a ______ ___ SB ___
QdiWiio
MP (aamolt)
XCfaafarH
X O m M fri
X C m ettn t XCbwddyy-1 XOMNtoyy-* XQaflridyyJ XOmddwA
w-- mtfen, d u n k * iin iio ni^ fO tn a d tn i dwtoflto ntraukwCSf&)
Page l9af6S
Exygen Research
Page 60 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.; P0000760
BoteoPfetoeol Numktr PQCQ076C
I - - j i ^ y j j r ' i T "" Hatol afAMlytototo Ptomtotvocinci&tomrtowpow niAdd(FlkU)mWi
JJU A
--*-*-1f--|-- TiMtin --"tti~rr
atafjm totowsnmd.
>W tow li WfcMWdtotoeHealiwdarfr1S-mLyotyyppyfcr ttoa
>1] AAwiatouna>id6MramBettilMMa>yUptpan*M
tO.O B*cb$*Uf
l.) Wtdk to to a tM ftm t t i r w l ftypfciy or Im ) a u t iartudt m t*m m m p a i M M M d t h a t w i HFIC n w ) d taw m m *\ mamk anUM ac fcaeini aMmnafoM (I* cmrcf apU> n vfrify
IdJ
mflqato1yhh r
ItB
im
mpkilitlouitmotiyp*dwvfmHt
m
Md
tfO m
4Mbf
ayofied
11.0 iM jli PHrirtna
114 M Mlin4pLftrM ^I*ta^aticiifipia A iM M 40LrA wMr
to>SOi.ylfrrajylw eMrifhqaMb--(totifr*<w+clupt- aMMd *& U.3 CmmU t o CmI f l cmddlp 0 j 0 14 bf la u fet 10 mL atom l
tt a v a ify im L a fB tlC w m fh ito a ftm l- Deaadvtookmnruadry 1 U I,M i 9 tm h m tm im irtC IW uartridj DtoardtoWa.
11.4 mm M H , I W Unfit, Caaet JMLW*eiektor<h*ii
IS wlynljpwpylMa --miMhp ff* (toO stow a Sat.). U J >Mfrw im y to w*a# riartTNimy LfftdSW .
12.1 dtf1* * * MM MMUtfof sack A n ted , aaMpi Md totifled MMfi mb die IM SA tt q m A ealtom Md--d a m p t - r i t Md IbKew ad M aijMiimpl
U J Slw <w *f?f0A 6m *keihm *w erm reow epew m #l
-- ito toM idfcMm frltotm
3 A* mir* a* a t axfcetiad d t o M ftaatodi o w t W InriaiM * t* t o | i m d t o a d a t > rni pli m . tssao ad m t o * a m te i m i m i b u w i aaay frMMm pto . A* m ahecMtiv, m m to art of
unmd writoii Mstototo way M Md to bayim af A
feHr--bjr Mbadad eatoUlM -- toM h i r f n l m ttry 5*10 Nunpta flw a r n t o a tm ad m or attrau d taodada). h d t n m M t i e w l to to M * im d iwh i-- i> m ftw m iiw ii i iefiBBiaim n it U.4 \>ift Timm toatod o n iw mftMIm liu v m m aitnria t j^ m r n i t o iw eelyta by im w iiem e m m qg 1Awei|Miig ef imk #m
H>al'>
JPa&Xtfi}
Exygen Research
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Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Bxyfcfi Protocol Number. POO0O76O
Mm*VOMITI c).<Hbeo<A*]y*ttftrtUr MAirMmhaiOmo%c/uNrMi!kMrfoMo^Mb in^rAc^(PFQA)tWtlcVy]
IGM3AII
VMM t \ m m ornim i twnmtntirm mt$ M m Lym ) } { t* equivalent) wN ih lyim
12.3 SsapU fl# m m -- U a * m arni w t - l r--iiem . Any mmM
wfl--tl a m im i M pH M MmM H Ibrtwr dttMM MdiMMlysvd.
1J.0 AiMfngCrUm>
13.1 Ch-Hop----lMoipbor*it*--rwoHb--bnop--i
of i l l m l TU <U mm $rnm pnaap-- to a PPOA mmn. wh tf*
*--r Mt
k-- Wcarttaii<**).
1 U lliMftif M--fci -- t at -- MMPPOA x I-- 1 pr-- t -- 0 tOQ. if*
H a* -- fFOA m b*-- pMMTtino SOpft, tf-- i i n r Mm* taiy lt
w * WdHewei w * * * * eewiIm meeMd.
13.3 1-- mrta ofcommi q m m i motri* ipi-- i t te l i n i 7M3QS of
dMrfc-- ah--. If tw l --fcoflJH amp'--* -- --Mil -- >fi
M i O r f --phi --n il to -- od. Aoy otra --bo ommM >0-
1WH a-- bo e*-- * by -- immym fi--nwior if mmnaion n w w M rii
13.4 Aoy h IiVm'm oam hti to m i > poHa bymgibH>--
Enei Taw wnf be cH W tm 0 ml-- too of fi calibra w h
ll--o ii; fi Mil am* of e-- d tibOMmi oknhi *ai emlfi be
4 'n o --rillt Miffii-- (X) fi* fB m ikw o w n t -- i d o--t bc
mm> U D <** ttH S y li a M a ta * w l b AU i M tmm Sm. tm
HuwpMi -- pi
m -- m a * a i tun-- i npcrwtoo. m th
Mafia-- o rto -- --tM e f----fcMabooUbem--lysofi.
134 ftc-- Mi M -- to m * M l-- m 4 wnp-- o-- i oat drill ore iHm
1 4K v- lm al)--* na. Iftaati--i--ftfiri*Keeo6tdh tiew *****
m anlj--al nm m t o -- -- atb* -- lyood.
1*0 Cokoh-- i
H.l Um M>0oM*t n oto min ia taa -- imoofFfOA hm (io np/l. tuoi m ptOk aie) u ug tbMnfierfi con* {Uaur top-- >poreroeurtl pMOr--dby UmM lg-- aoAwvn m y .
rfO A M M l)
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p--4tP
Pof* 2 of 43
Exygen Research
Page 62 of 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Eaygm Protocol Nuntoer *0000760
iiiin i vmim
1
AfOllfnCAI. MlTHOt)
--------------1
MaltolirfAialyihtorfcOto.iMiriiliiiii.ffiiftiwi MtoMliW'ffPOAlicWiMtty LOMS1MS
MJ fWM--tfoldttfototo"iI1*nlIwtaMMmitaoooIvMlk fmmYwfp.rior to unco. ,,c
ImmmyQVi-
Exygen Research
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Page 63 o f l 10
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.; PQ000760
Exyfeq ^iotol Number. POCKXV760
ANALVTJCAL METHOD U u M M u ak V00017I1
Matfcctf
Ar 1M OcmmJMtiM i f M w r w r w ite AcM (PfA> u s+u by lcao/m
AublMT*tg?*;:
fecyf1--wek
VUl IUc--Pt Prfrc
StateC*D*t>A 1*101
TteJwkal Imtr, LC-US,Bxnpa RcmkUi
i6tafUwty ^
/ Vice ftwidiwt, OyiirtteM, l y y Ib waret
'>hh4 -Bete M
Exygen Research
Totti?*** 7
-Paj* </d.J Page 64 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Bxygra Protocol Nurob*r; PWXMO
NwiNrveootm AAtyncALMrraoD * * * * * * hftrunwHiUtMhiHtlfVNHMrr8ftimmxxM*A'id(W<hA)8o.!h,
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Page 65 o f 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Number: P000076Q
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Exygen Research
Page 66 of 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Bxygtn Preloco) Number: F00007M
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Page 67 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: PG000760
Bxyira Piotoeo) Number P00C0760
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Exygen Research
Page 68 o f 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
E z y jta ProtDool N w a b ar P0000760
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Exygen Research
Papi 2 o fSS
Page 69 of 110
interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: PQ000760
Exygeti Protocol Nuoiter: P00007SQ
I * im v n cA i. ttiro
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P o p 19 o f SS
Page 70 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Hxyjeo Protocol Nuanber P0000760
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Page 71 o f 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Bxygra Protocol Norober PQ0Q0760
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Page 72 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exyfen Protocol NwaWr P00007W
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Exygen Research
Page 73 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygcn Study No.: P0000760
S x y |ta Protocol Nunfccr P0000760
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Exygen Research
Page 74 o f 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
xyjci Protocol tfanber P0000760
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Page 75 o f U O
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Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
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Exygen Research
Page 76 of 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
E a y | Protocol Number: P0000760
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Exygen Research
Pa# St ofiS
Page 77 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P000760
Eiygcn Protocol Nim&tr: ("00007(50
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T* * * * * * t f a x t }? pf 65
Page 78 o f 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
E x y |n Pfoiowl N m b c r MOOOTO
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Exygen Research
Page 79 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exygen ?nxscol Number P0000760
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Exygen Research
/H* )9 o f65
Page 80 of 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exyjen Protocol Nitrater P0000760
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Exygen Research
Page 81 o f 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Bcyiw Prometti Number P0000760
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Pag* 4 / o f 65
Exygen Research
Page 82 o f 110
Interim Report #23 - Analysis ofSediment Samples
Exygen Study No.: P0000760
B in PmiocolNumber POOOOTiO
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1
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Exygen Research
Page S3 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exjrjca Prorocoi Nuotwr *0000760
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Exygen Research
Page 84 o f 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygen ProtocW Number P00007$Q
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Exygen Research
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Pag* 44 o f6 i
Page 85 o f 110
interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Ex* Protocol N un*: KMOffMO
ANAlYTTCAt MBTHOD MtowdNurt: VKO|T4
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Exygen Research
Totei PtfM: ? Pn& 45 q f 65
Page 86 o f 110
interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exyfta Protocol Number POOCC7
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P a ft 46 o f61
Exygen Research
Page 87 of 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol N urcten P0000760
mMMk
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Exygen Research
Page 88 of 110
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
E x y g n Protocol N um ber P0000760
1. . M U tractL M IllIO O
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xygen Research
Page 89 of 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygwt Protocol Number P0000760
[ analyticalwrMQO MtoM dAMitymfcrt o OmmmMimilM to n K U M it A4 (M^A) i toratCM
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Exygen Research
Page 90 of 110
Interim Report #23 - Analysis of Sediment Samples
Exygen Study No.: P0000760
Exygca haloed Hwnr P0000760
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Interim Report #23 - Analysis of Sediment Samples
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rn ....... l to OcUoaOlaboaaaoaydaptlceuaaod1t will MifKlOw
1|MnaakayMMfiwnafl t* ft* fifjaai.
noa, o'
Pat t 62 c f iS
Exygen Research
Page 103 o f 110
p. 104
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
Exygen Protocol Nunbbmr 1*0000740
toy* I
MmW Mi.wfcwVOMPU ajuiyuciU. m rn o p
Md)dfAilybllbrM3rairail1iraifT *iinrairaMii Acid (PPQA) to iaull MraMuDmabylC/MSMS
u o Jm tkltneiiM
11.1 I liu m 1raif rarayli n SO I pbtyyrapylra u rariftiy ml (fco.fr m nil 111, wfl Id raid * oU). VtU * u d n * wHanra bf rawm
I U AdaraHrraOraiwMfeH * m Wrauof 2M- Csttgdty
1L3 11.4
VMir iKi tlem-iMl ft . -->1 sky l i pniM r f
m IJ mi
dra|Mblb s n d ig lab*. II. Aral1 ra i of uraaniral mi raubfat ~20ram m ra uut.clran ra4<
II.4 QSddMMrabrara-JSCTryrato-draurara.
1 L? ft rawt o f i s r a r bin i T* i l f
*"*-- *-** '*
l i t QsdM u toC raO T rabidyra l l | 4 m i) 4 p m | 10 I raiinl M m adkr*sl.<H rU ;m M s(-*toy*K ). Ooradls u S su r i* dry
1L4 Lradtommyli ramdkioradCiiirP unndlx. DracradtiiuK.
1 1 .1 6 N s wi* -3 *i iintrail. CKt ] L d u n in (nduMd
II U.rMMnNM SMri*l Wbd(llwl *'- 3 41 11.11 Aradyra IM ill H > l9UxO*xm*yLC/d(3/US.
12.1 bust t o Mraacral of racb llrayirad, n o f h Md feud'd Iranplc into IM
IOUS/US D M . A oSfantia Sradud a m t fraud* *o4 M o dl
lid | lid -- ||lra
IU B r i r*- r~ ' - ------r- ..-j - - . ----- --
i-- i.
amtaiadxM a uMera rat
12J AOdra Ml oruUnWM raillid* sura W lacMmi m lie bcfiiMHU MCII
tbradolraraylHL S r a M i raw b raunyraMd bateua 1 fell iiryl-rr A m U rawIra m din rat 4 ulibnusa *idsdi nray ix
b u n 4 K 0 utlraina t l i Murad by u u m u u uuntt um M riirnirM aM aplM levM iadfc'taM cntN t'j'uMdaftk). m
dtbra M , u&bntiora Mradwdb m m b lira flat ad bral iaicetmi in
124 Ura dura madrail twrara fer uctuuloa LiMU aluidird u n s ut yrarawilto to raraljMby la w ravsraarauno* I/ wiifhlitif atyuk era
rsraa u&bnrtMM>ludd MMelradM bras MrabLyiu )J Ira s r a W O wdraraa lySiSI U U m flt m yUl ibmdd w su e d uindsd m um m . Any nmpla 1M1 urad totdsd nuMMMirauUb* totter dUaudraidrraulyud.
liralor'
Page i l o f i l
Exygen Research
Page 104 o f 110
p. 105
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
ProtocolTfciufecr P0000"?60
tifpmMmmkk
7IliftiiilMn nm VMH H
i
: ANA4VTK4LHlWO.....
..
M rtM c T A S ro fc to & ilM M lto n ^ w te rim rtn iitm A*d(PyOA) in Smalt
.. - - MMriSmaftrlOM&MS
1)4 A M yOM tM l '
)).l O ijaM >pa K t a l t e v i p t a t o f l t a ^ t a t a MM a (me ip v i . . T. 411-- . t a i i n u m * m y f O * naiv tail uw
113 u A iJ M a tt 1 * WO* m h n k m lm a m t a LOQ. If *
UMap*ltm(BmHiImlOCtatMOlAMdMttafltWaOwBmfe*fmtMmWmM1teaIMgtXeLSMtiad. am t a It
U ) M W M tof ntoot ^toft nto MMriaM toi --M to f c w --7CH)0Hof . to o M m M m . H i w i I to M h M t o t o -- M b h bato,
,ii M tf ii a f ( N * N U b iH il itw i. A * y M i* *lmjto ftlm M M to M i l to to t o n aitowim if n-wnrnnan * natal . KM Aay a i i t o M Mm * to M M iil cito to tag t o Hmj
iM bmI Mtol--lorfMMiIqprita
1>4 Ito m m M m tolirtta 0 0 fer i i f t t o cwvw p H n M mm to i M n (R* to-NS). |f itM Irtoi i w l i tJ M to t mm lin , tto* taf* m m bn b * ta t* fcMfMMT apnotia*, md *
toM * to ito--t Mcf--mIh M H torwMlyito
1)4 taM iM tom tatw* aato*i to Mnptw m m w* On moi ton
' i4%witop--lytirilnm. IfiMmto n*cdriftcMAalrnwh,n
mtoyiimln e * * ti M WMto mmttyied.
14.0 Cafctotow
14.1 U m to fc P *M | to M to c M w ta B to m m tofP O A fom d (i* i^m L. tond mi f* k mm) mat t o < M ur* (immr m r w iw yum m ut)
pM M d^teM m L paiitonm pw
totITOA toto tN to ^ (Zaim tjeiHaall * DPa
toter
E * to arto ito t o Itoel voMme WMdtkWd, if aectomry.
Aftor-
142 Per l|iM ktiaA witfaImnm waotaM of PFOA |ver io lumctoe. me to to lowiMto*1-- n mtmhm t o pnrmmmoimy. > " ) (H)
omlmlymM--ngtol) --frwfcMdfatoaanUa/!.)]
_____ ;_____ --M talta6 M U _________
H**'
Pogt t4 * f 6$
Exygen Research
Page 105 o f l 10
Interim Report #23 - Analysis o f Sediment Samples
p. 106 Exygen Study No.: P0000760
Bxy$co Protocol Number P00C0760
Utaiui
AWaUTOCU. METHOD
M ama) i n ty LOM3/MS
VMWI7M iM ti-
t o Um A fe&Mria| a^MliM to m t tiu acxmt fPfOA fniod m ti|ftnL u
" flA
Hwniri fTMrtmt >i Hn^ --tr-~ fnml ti W f b n r f w <l)
Exygen Research
rap?*?
P a p <V o f 6S
Page 106 of 110
p. 107
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
senrE\ygRESEARCH
3058 Research Drive
Phone: 814*272-1039
sute College, PA 14801 Fa: 81A-231-15*0
ERQTPQQLAMENDMENT
Amendment Number: 1 Effective Dele: 01/188 Exygen Study Number..P0Q01131 Clent Study Number
lofi "
Hone
DESCRIPTION OF AMENDED SECTION 1) Analytical Procedure SummaryV0001780:Sectton 9.1 7) Verification of Anetytlcai Procedure
AMENDED TO
1) Add to Section B.1: Section 9.1.8, Alternate weight* at stancfaitf may be ueod pmpam alternate concentrations of stack eolulione as neceeaaty. Alternate level of fortification eotutions may atoo be prepared. 2} Low and high spWnQ lamie of (he analytes tor each matrix may be altered depending on sample size auaHoDle tor extnxaion and/orto cover enMyte concentrations expected In the empiee.
. . . . . ^ BATKme
1) Wgher ooroentretlon# of etandarde need to be prepared In order to pike the sample bottlee at higher level.
29 The ample size avalabte for erne mammal her end aerumwee emaler than expected. Spiking at the predetermined level* in tea protocol pule the spaced concentration tower than the detection limit. Also, the analyte levels In the gnxmd water
eampiee are expected to gmatiy exceed *w predetermined spiking ievela Sited In the protocol. When toe level Intoe ample* graadyemeed the spicing levels, an accurate mammy value cannot be calculated for toe Q C sample. Higher spiking level m the bottlee win cover the tnotyte concentration expected In the weter wangle.
_ ,, IMPACTONm O X
The LOQ is 100 ngfe for a 0.1 g ampia o smell mammal ttvarand it 1000 ngAnL for a 0.01 mL empie of nel mammalaerum.
Higher levels of spiking fo rti* water samples wtf ensure tiat mom Q C recovery data can be used.
ir
Wtm
U SfR V ID :W O O O t2JM
Jfiurfo _ J ^ * L
Exygen QAU Review I A S o zi i f
ADMINISTRATIVEFORM
Exygen Research
Page 107 of 110
p. 108
Interini Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
n
RESEARCH
3058 Research Drive
Rhone: 814-272-1039
Stet* CoUeje, PA 16W1 Tax: 814-231-1580
Amendment Number
Effective Date:
Exygen Study Number
PROTOCOL AMENDMENT
2 03/07/05 P0001131 Client Study Number
PeoelcM
Nona
_*_S_R_S_I_5_i_K_J_K_i .AMENOeOSEgnPN
1) Report, page 11 of 85 2) Teel Materials, page 8 o( 65: PF08 transition monitored 499 -> 89.
AMcNPH>TP
1 ) Instead ofone ftnetreport, interim reportswM be lesuad. 2) PFOS transition monitored may eleo be 499-> 80.
RATIONALE
1) Due to tie excessive storesof the date tele, Interim reports w ll be issued to allow the client to receive dete In a ttmefiermen u m-- '- ei^t/nr -u
2) The API 4000 LC/MS/MS systems detect tie 49 *> 90 PPOS transition with greater ssneflvlty than the 499 -> 99 traneWon.
,, _ _ Jiiu
IMPACIQN STUDY
1 ) The dent will be able to receive and review the date more quidcty,.
2) The 499 - 80 transition can be detected with greater sensMMty; therefere, giving
bettor chromatography.
awdyOndar
Exygan Ummg
55
Spereor acn^CM (lfrqi*J)
o
IBAAJTYICSVW0122W-
Exygen GAU Review U e o lttk s ADMINISTRATIVE FORM
Exygen Research
Page 108 o f 110
p. 109
Interim Report #23 - Analysis o f Sediment Samples
Exygen Study No.: P0000760
n
RESEARCH
3058 Research Drive Phone: 814-272-1039 State College, PA 16801 Fax: 814-231-1580
DEVIATION FORM
G eneral: X Project Specific Deviation
Facility Deviation
Panelo<2 Date of Occurrence: 04/2WW
Exygen Prqject # : P78WP1131
Deviation # :
5
Client Project# :
NA
Reference#: 06-076
Regulatory Driver:
Deviation Type: {lochxto V# far m ethods and SOPS)
GMP GLP Other None
Sam ple Peecrlotion:
X Protocol
_____ Method
V#:NA Notebook reference: NA
____ SOP
Login#:
L0008191
Container#:
NA Lot:
NA
Summary of Deviation:
" ----------------------- --
The three sediment samples in L8191 (C0172892 - C0172894) were originally extracted wing the
sediment method V0001782. Poor recoveries were obtained for PFOS. PFOA and HC PFOA.
Because of this, the study sponsor requested the use of an alternative extraction for these compounds, es follows:
Direct Injection Method: Before the samples were weighed for the extraction, they were mixed
thoroughly by vigorously shaking the container. A one-gram portion of sediment was weighed kilo a
15-mflMitercentrifuge tube for the extraction. Ten mMiters of 1% acetic acid In methanol was added
to each sample. The samples were then shaken by hand, vortexed, and sonicated for thirty minute
The samples were then centrifugad for -10 minutes at -3000 rpm. Each sample was analyzed by
LC/MS/MS elect/osprey.
''
tht* 'n* thod "" aptabte data was obtainedfor PFOS. but tha recoveries fo r PFOA wto UC PFOA were sill poor. Another alternative method ras then wed for PFOA and ,JC PFO A as follows:
Alternative SP E fctethod^The samples thatwere prepared In 1% acetic add for the direct injection n^thod were used for N s extraction. Five m#itterB of each sample we elfouoted Into a SO-mL
n W u o * tubeand file volume was taken to 4 mL with atar. The samples wore than cenWfoged for -10 minutes at -3000 rpm. Tha supernatant m s then loaded onto a C ,, SPE cartrxfo condkionod wlthlOm L of methanol and 5.mL of water. Tha d u e * was dncardod. Approximately five milWters of methanol was added to the cartridge. Five mimitar* of eluata was collected W o a
oindrojpruy8 polyprwten* c<n,,ihjC* h*e. Each sample was analyzed by IC/M S/M S
Cause:
Preparation
Impact:
More usable data was obtained.
Analysis
Instrument
Client Request X Other
LIB R A R Y ID: V0001840-6
fcxygcn Research
ADM tM tSTRATIVE FO RM
Page UW ol 11U
p. 110
Interim Report #23 - Analysis of Sediment Samples
Exygcn Study No.: P0000760
CHEH EHSR 236 1B
651 733 1958
tt-tl-tOM it;Mm FraHifTOI SOLtlTien
05/01 '06 1 3 : MO.106 03/03 m m t.mm t m i *
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Exygen Research
Page 110 of 110