Document qa3V008MQZKLyavj99b1avBaK
ARA9.G - 136S
Study Title
T e n n e s s e e R iv e r V a l l e y S a m p l e s
Author
M ark E. Ellefson
Study Completion Date
17 Decem ber 2002
Revised Report
06 January 2003
Performing Laboratory
3M Environmental Laboratory Building 2-3E-09 935 Bush Avenue
S t Paul. MN 55106
Project Identification
3M Environm ental Laboratory Study # E 02-0443
Total Number o f Pages 276
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Table of Contents
List of Tables.......................................................................................................................................... 3 Study Inform ation................................................................................................................................... 4 S um m ary................................................................................................................................................. 5 P u rp o se ................................................................................................................................................... 6 Test and Analytical Reference Substances......................................................................................... 6 Test System s......................................................................................................................................... 7 Method Summaries................................................................................................................................ 8 Preparatory Methods..............................................................................................................................8 Sample Analysis..................................................................................................................................... 11 Analytical Method................................................................................................................................... 12 Analytical Results................................................................................................................................... 13 Data Sum m ary....................................................................................................................................... 20 Statistical Methods.................................................................................................................................25 Statement of Conclusion....................................................................................................................... 26 References............................................................................................................................................. 26 List of Attachments.................................................................................................................................26 Signature Page....................................................................................................................................... 27 Attachment A: Analytical Method and SOP Deviations........................................................................28 Attachment B: Data Summary Tables.................................................................................................. 40 Attachment C: Sample Chromatograms.............................................................................................. 67 Attachment D: Sample Prep Sheets, Test Substance, and Test System Inform ation.......................230 Attachment E: Notes to F ile .................................................................................................................. 270
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List of Tables
Table 1. Sample Location, Sample Type, and Analytical Data Summary..........................................5 Table 2: Characterization of the Test and Analytical Reference Substances.................................... 6 Table 3a. Description of Fish Tissue Analyzed in this S tudy.............................................................7 Table 3b. Description of River Water Analyzed in this S tud y............................................................ 7 Table 3c. Description of River Sediments Analyzed in this S tu d y.................................................... 7 Table 4a. Fish Tissue Sample Preparation Method........................................................................... 8 Table 4b. Preparation of Extracted Calibration Curves for the Fish Tissue....................................... 9 Table 4c. Fish Tissue Analytical Data Quality Objectives................................................................... 9 Table 4d. River Water Sample Preparation M ethod.......................................................................... 9 Table 4e. River W ater Sample Data Quality O bjectives.................................................................... 10 Table 4f. River Sediment Sample Preparation Method.......................................................................10 Table 4g. River Sediment Sample Data Quality Objectives............................................................... 11 Table 5. Sample Analysis Information................................................................................................. 11 Table 6a. PFOS Calibration Standard Reprocessing Summary........................................................ 14 Table 6b. FOSA Calibration Standard Reprocessing Summary........................................................ 15 Table 6c. PFOA Calibration Standard Reprocessing Summary........................................................ 16 Table 6d. PFHS Calibration Standard Reprocessing Summary........................................................ 17 Table 6e. PFBS Calibration Standard Reprocessing Sum m ary........................................................ 18 Table 7a. Catfish Analytical Data......................................................................................................... 21 Table 7b. Large mouth and Small mouth Bass Analytical Data..........................................................22 Table 7c. River Water Analytical Data.................................................................................................23 Table 7d. River Sediment Analytical Data........................................................................................... 24 Table 8. Sample Location, Sample Type, and Analytical Data Summary......................................... 25
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Study Information
R e q u e s to r
Dale L. Bacon 3M Environmental Laboratory Bldg. 2-3E-09 935 Bush Avenue St. Paul, MN 55106 651-778-4736
Study D irector Mark E. Ellefson 3M Environmental Laboratory Bldg. 2-3E-09 935 Bush Avenue St. Paul, MN 55106 651-778-5405
Study Location
Testing Facility 3M Environmental Laboratory Bldg. 2-3E-09 935 Bush Avenue St. Paul, MN 55106
William K. Reagen, Laboratory Manager Mark L. Anderson, Analytical Chemist Cindy M. Carlson, Analytical Chemist Ognjenka Krupljanin, Analytical Chemist
Experimental Dates
Sample Analysis Initiation: 26 June 2002 Sample Analysis Completion: 12 November 2002
Location o f Archives
All original raw data and the report have been archived at the 3M Environmental Laboratory according to 3M Standard Operating Procedures. Remaining specimens pertaining to the analytical phase of this study will be archived at the 3M Environmental Laboratory for as long as the quality of the preparation affords evaluation.
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Summary
Fish, river water, and river sediment samples were collected from three locations in the Tennessee River near the 3M Decatur, Alabama facility. The samples were analyzed for perfluorobutane sulfonate (PFBS), perfiuorohexane sulfonate (PFHS), perfluorooctanoate
(PFOA), perfiuorooctane sulfonylamide (FOSA), and perfluorooctane sulfonate (PFOS). The analyses were accomplished by extracting the samples using Solid Phase Extraction (SPE) and then analyzing them using HPLC-Electrospray/Mass Spectrometry (HPLC/ES/MS).
Sampling Location 1 (SL-1) was located near the 3M facility outfall. Sampling Location 2 (SL-2) was across the reservoir from the 3M facility outfall. Sampling location 3 (SL-3) was downstream from the facility near the Fox Creek confluence.
Analytical results are presented in Table 1:
Table 1. Sample Location, Sample Type, and Analytical Data Summary. Fish Tissue
Sampling Location & Species Sampled
PFBS (ng/g)
PFHS (ng/g)
PFOA (ng/g)
FOSA (ng/g)
PFOS (ng/g)
SL-1, C (n=6) SL-2, C (n=7) SL-3. C (n=6) SL-1, LM (n=6) SL-2, LM (n=4) SL-3, LM (n=7) SL-3, SM (n=1)
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
River Water
<LLOQ <LLOQ <LLOQ
64.3 <LLOQ <LLOQ <LLOQ
60.9 <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
113 <LLOQ
22.3 553 281 <LLOQ <LLOQ
SL-1, RW SL-2, RW SL-3, RW
PFBS (pg/mL)
84 <LLOQ <LLOQ
PFHS (pg/mL)
PFOA (pg/mL)
196 550 8 <LLOQ 7 <LLOQ
River Sediments
FOSA (pg/mL)
25 <LLOQ <LLOQ
PFOS (pg/mL)
491 <LLOQ <LLOQ
PFBS (pg/g)
PFHS (pg/g)
PFOA (pg/g)
FOSA (pg/g)
PFOS (pg/g)
SL-1, RS
577
130
732
1440
3130
SL-2, RS
437
<LLOQ
<LLOQ
141
457
SL-3, RS
452 <LLOQ 131
68 416
C CatFish, LM Large mouth bass, SM >Small mouth bass, RW = River water, RS = River Sediments, and n number offish per sampling group.
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Purpose
The purpose of this study is to perform quantitative screening for PFBS, PFHS, PFOA, FOSA, and PFOS in sport-caught fish, river water, and river sediments from three sampling locations of the Tennessee River near Decatur, Alabama.
Test and Analytical Reference Substances
Table 2: Characterization o f the Test and Analytical Reference Substances.
Test and A nalytical Reference Substance
PFHS
FOSA
PFOA
Compound
Source
Storage Conditions 3M Laboratory Identification Number Physical Description Purity
PFHS, Perfluorohexanesulfonate
3M Specialty Materials, Bldg. 236-2B-11 Frozen
FOSA, Perfluorooctanesulfbnamide
3M Specialty Materials, Bldg. 236-1B-10
Frozen
PFOA Perfluorooctanoate Ammonium
3M Specialty Materials, Bldg. 236-1 B-10
Frozen
TCR-083
TCR-029
TCR-123
White Powder 98.6%
Light yellow waxy solid White Powder
Undetermined
95.0%
T est and A nalytical Reference Substance
PFBS
PFOS
Compound
Source
Storage Conditions 3M Laboratory Identification Number Physical Description Purity
PFBS, Potassium Perfluorobutane Sulfonate
Wildlife International
Frozen
TCR-359
White crystals 97.3%
PFOS, Potassium Perfluorooctanesulfonate 3M Specialty Materials, Bldg. 236-1B-10 Frozen
TCR-129
White Powder Undetermined
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Test Systems
Table 3a. Description o f Fish Tissue Analyzed in this Study
Fish Tissue
Source
Types
Storage Conditions Location 1 Location 2 Location 3
Tennessee River
Catfish Large Mouth Bass Small Mouth Bass Frozen Near the 3M facility outfall Across the reservoir from the 3M facility outfall Downstream of the Fox Creek confluence
* The fish were filleted and representative aliquots of the fillets were analyzed.
Table 3b. Description o f River W ater Analyzed in this Study
Source Storage Conditions Location 1 Location 2
Location 3
River Water
Tennessee River Chilled (approximately 4 C.) Near the 3M facility outfall Across the reservoir from the 3M facility outfall Downstream of the Fox Creek confluence
Table 3c. Description o f River Sediments Analyzed in tills Study
River Sediments
Source Storage Conditions Location 1 Location 2
Location3
Tennessee River Chilled (approximately 4 C.)
Near the 3M facility outfall Across the reservoir from the 3M facility outfall Downstream of the Fox Creek confluence
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Method Summaries
The concentrations o f PFBS, PFHS, PFOA, FOSA, and PFOS in Fish Tissue, River Water, and River Sediments were determined by using Solid Phase Extraction (SPE) and High Performance Liquid Chromatography-Electrospray/Mass Spectrometry (HPLC/ES/MS).
Preparatory Methods
# The following tables describe the sample preparation methods for the Fish Tissue, River Water, and River Sediment samples. Data Quality Objectives (DQO) are also given for each sample preparation method.
Fish Tissue Sam ple Preparation Method
Table 4a. Fish Tissue Sample Preparation Method
Step
Fish Tissue Sample Preparation Method
1 Approximately 2 g of Fish Tissue and 8 mL of ASTM Type 1Water were homogenized.
2
The homogenate was centrifuged to eliminate the foam and then shakerWortexed to re suspend the homogenate.
3
Each homogenate was aliquoted into triplicate samples. This was accomplished by transferring 1.0 mL of homogenate to 3 separate 15 mL centrifuge tubes.
Matrix spikes (MS) were prepared for every other homogenate. In this case, an addibona!
4
(4th) 1.0 mL of homogenate was transferred to another 15 mL centrifuge tube. TheMS's were spiked with 100 uL of a 1.0 ug/mL spike solution containing each ofthe test
substances.
5
5.0 mL of acetonitrile was then added to the centrifuge tubes. The tubes were capped and i shaken for 20 min at 300 rpm.
6
After mixing, the samples were centrifuged at 3000 reffor 10 minutes to clarify the supernatant
7
The supernatant was decanted into new 50 mL centrifuge tubes and diluted with 4 0 mL of
w ater.
Waters C-18 Tri-functional, Sep-Pak 1g, 6cc SPE columns with attached 70 mL reservoirs were placed onto vacuum manifolds and pre-conditioned in the following manner. Approximately 10 mL of methanol was added to the columns and the vacuum was applied. 8 Once most ofthe methanol had been pulled through, ASTM Type 1Waterwas added (5-10 mL). When most of this was pulled through, more water was added (5-1OmL). When there was only a small amount of water left in the reservoir, the stopcock was turned to stop the vacuum to the column. The columns were not allowed to go dry.
9
The supemates from step 7 were passed through the pre-conditioned SPE columns. The aqueous eluentwas not collected. The columns were allowed to dry for at least 3 minutes.
10 The analytes were eluted from the SPE columns with 2.0 mL of methanol into autovials.
See the preparation worksheets for other exact amounts, times, speeds, etc.
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Table 4b. Preparation o f Extracted Calibration Curves fo r the Fish Tissue.
Step
Preparation of Extracted Calibration Curves for the Fish Tissue
There were two extracted Fish Tissue calibration curves: Large Mouth Bass and CatFish. Rangefinding experiments were done to determine which Fish Tissues had the lowest endogenous levels ofthe analytes. Then, one Large Mouth Bass and one CatFish sample containing the least amount of endogenoustest substances were selected as the matrix to construct the calibration curves. The Smalt Mouth Bass was analyzed using the Large Mouth Bass calibration curve.
The procedure for preparing the extracted calibration curves is the same as the Fish Tissue sample preparation, except the volumes were scaled-up to provide a homogeneous batch of fish tissue matrix. The differences are as follows:
1
Approximately 10 g of Fish Tissue and 40 mL of ASTM Type 1Water were combined and homogenized.
2 1.0 mL of homogenate was transferred to the appropriate number of tubes.
3 Each tube was spiked with the predetermined amount of spike solution.
Table 4c. Fish Tissue Analytical Data Quality Objectives.
Step
Fish Tissue A nalytical Data Quality Objectives
1 All samples were prepared in triplicate. The %RSD should be s 25%
Matrix spikes were performed on half ofthe fish of each type from each sampling location. 2 Recovery should be within 30% from expected values. A total of 18 matrix spikes were
prepared for the Fish Tissue samples.
Water blanks, consisting of an aliquot ofwater run through the entire sample preparation and
3
extraction process were prepared with samples from each sampling location. Water blanks containing < % LLOQ of each analyte for the data set in which they were run were
considered acceptable.
Extraction blanks, consisting of an aliquot of methanol run though a pre-conditioned SPE 4 cartridge, were prepared for each sampling location. Extraction blanks containing < !4
LLOQ of each analyte for the data set in which they were run were considered acceptable.
5 I Mid-level calibration curve points were used as CCVs.
River W ater Sam ple Preparation Method
Table 4d. River W ater Sample Preparation Method
Step
River Water Sample Preparation Method
1 Waters G-18 Tri-functional, Sep-Pak 1g, 6cc SPE columns with attached 70 mL reservoirs were placed onto vacuum manifolds and pre-conditioned in the following manner. Approximately 10 mL of methanol was added to the columns and the vacuum was applied. Once mostof the methanol had been pulled through, ASTM Type 1 Water was added (5-10 mL). When most of this was pulled through, more water was added (5-1OmL). When there was only a small amount ofwater left in the reservoir, the stopcock was turned to stop the vacuum to the column. The columnswere not allowed to go dry.
2
40 mL ofthe RiverWater was passed through a pre-conditioned SPE column. The columns were allowed to dry for at least 3 minutes.
3 The analytes were eluted from the columns with 2.0 mL of methanol into autovials.
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Table 4e. River W ater Sample Data Quality Objectives
Step
River W ater Sample Data Quality Objectives
1 Water blanks, consisting of an aliquot ofwater run through the entire preparation and extraction process, were prepared with samples each day samples were extracted. Water blanks containing < 14LLOQ of each analyte for the data set in which they were run were considered acceptable.
2 A non-extracted solvent calibration curve was used to quantitate the River Water samples. No extracted CCVs were prepared, a mid-level calibration curve point was used for this purpose.
3 No matrix spikes were preformed during the sample preparation ofthe River Water samples.
R iver Sedim ent Sam ple Preparation Method
Table 4f. River Sediment Sample Preparation Method
Step
River Sediment Sample Preparation M ethod
There were 3 River Sediment samples, one from each sampling location. Triplicate samples plus a matrix spike were prepared for each location.
Initially, sedimentwas transferred to 50 mL centrifuge tubes and centrifuged at 6000 RCF for 1 20 min. The liquid was decanted off and the remaining sedimentwas used for the sample
preparation
2
Approximately 20g of sediment and 35mL of 1% Acetic Add (aqueous) were combined into 50mL centrifuge tubes.
3
Matrix spikes were prepared by adding 100 uL of 1.0 ug/mL spike solution to the predetermined MS tubes.
4 The tubes were capped, vortexed, and then shaken for 60 min at 300 RPM.
5 They were then centrifuged at 6000 RCF for 20 minutes.
Waters C-18 Tri-functional, Sep-Pak ig , 6cc SPE columns with attached 70 mL reservoirs
were placed onto vacuum manifolds and pre-conditioned in the following manner. Approximately 10 mL of methanol was added to the columns and the vacuum was applied.
6 Once most of the methanol had been pulled through, ASTM Type 1Waterwas added (5-10 mL). When most ofthis was pulled through, more water was added (5-10mL). When there
was only a small amount of water left in the reservoir, the stopcock was turned to stop the vacuum to the column. The columns were not allowed to go dry.
7
The aqueous solutions from step #5 were decanted from the samples and passed through pre-conditioned SPE cartridges. The aqueous eluates were discarded.
8
i 20 mL of methanol was then added to the sediment samples. The samples were vortexed, shaken for 30 min at 300 RPM, and then centrifuged at 6000 RCF for 20 minutes.
9
The methanol was decanted, passed through the SPE cartridge and collected. An additional 4 mL of methanol was used to wash the reservoir and the column.
10 The collected methanol was then added to approximately 200mL of ASTM Type 1 Water.
11
This solution was then passed through a new pre-conditioned SPE cartridge. The aqueous eluate was discarded.
12 The analytes were eluted from the SPE cartridges with 2.0 mL of methanol into autovials.
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Table 4g. River Sediment Sample Data Quality Objectives
Step
River Sediment Sample Data Quality O bjectives
1 All samples were prepared in triplicate. The %RSD should be 25%
2
Matrix spikes were performed on each sample. Recovery should be within 30% of expected values.
Two lab control samples, consisting of spiked water carried through the entire extraction
3
process and analyzed with the samples, were prepared. However, the information was not used because the data suggested it was impossible to recover spiked analytes 'from acidified
waterwhen river sediment was not present
Water blanks, consisting of an aliquot ofwater run through the entire preparation and 4 extraction process, were prepared. Acceptable values were <%LLOQ for the data set in
which they were run.
5
The River Sediment samples were quantitated using a non-extracted solvent calibration curve. Mid-level calibration curve points were used as CCVs.
Sample Analysis
The samples were analyzed using HPLC/ES/MS. The analytical method was based on the 3M Environmental Laboratory Method ETS-8-155.1 ` Analysis of Waste Stream, W ater Extracts or Other Systems Using HPLC-Electrospray/Mass Spectrometry".
The following table details sample run information, including the sequence and the run start date of each sample.
Table 5. Sample Analysis Information.
Sampi e
L ocation
1 i i
2
Catfish Lange Mouth Bass
3 Small Mouth Bass 4 River water
5 River Sediments
SL-1 SL-2 SL-3 SL-1 SL-2 SL-3 SL-3 SL-1 SL-2 SL-3 SL-1 SL-2 SL-3
Sequence
D020629 D020629 D020702 D020626 D020628 D020628 D020628 D020812 D020812 D020812 1021112 1021112 1021112
Date Sequence W as S TARTE U
29 Jun 02 29 Jun 02 02 Jul 02 26 Jun 02 28 Jun 02 28 Jun 02 28 Jun 02 12 Aug 02 12 Aug 02 12 Aug 02 12 Nov 02 12 Nov 02 12 Nov 02
0 0 1 ,6 0
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Analytical Method
Sample analysis was based on ETS-8-155.1 "Analysis of Waste Stream, W ater Extracts Or Other Systems Using HPLC-Electrospray/Mass Spectrometry". Methanol extracts were analyzed using HPLC/ES/MS in the negative ion mode. PFBS, PFHS, PFOA, FOSA and PFOS levels were evaluated versus calibration standards ranging in concentration from 11000 ng analyte/mL. The target ions were as follows: m/z = 299 (PFBS), m/z = 399 (PFHS), m!z = 413 (PFOA), m/z = 498 (FOSA), and m/z = 499 (PFOS). The analytical method used for analysis is presented below; modifications may be necessary to optimize the method for individual instruments.
A n a lytica l E quipm ent
Liquid C hrom atograph: Agilent/Hewlett-Packard* Series 1100 Liquid Chromatograph system Analytical column: Keystone* BetasilTM C182x50mm, 5pm particle size Column temperature: 30 C Cycle Time: 9.5 minutes Flow rate: 300pL/min Injection volume: 4 to 20pL Mobile phase components:
Solvent A: 2.0 mM ammonium acetate in water Solvent B: HPLC Grade Methanol
Solvent G radient
T0.im00e
0.50 0.80
3.50 5.50
6.50 9.50
%10
B %
10 %
60 %
100 %
100%
10 %
10 %
Mass Spectrom eter: Agilent/Hewlett-Packard* Series 1100 API/Mass Spectrometer Detector Software: Agilent ChemStation,A.08.03 Fragmentor Voltage: m/z 299 = 100V
m/z 399 = 120V m/z 413= 100V m/z 498 = 80V m/z 499= 140V
Capillary Voltage: 4000 V Gain = 1.0 EMV Mode: Electrospray Negative Gas Temperature: 350 C Drying Gas: 8.0 L /min. Nebulizer Pressure: 30 psig Analysis Type: Single Ion Monitoring (SIM)
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Analytical Results
Data quality objectives outlined in the Preparation Methods section were m et
R egressions. Quadratic curve fit was applied to calibration standards and sample data to improve quantitation over the concentration range appropriate to the data. All calibration curves had least-square fits of 0.990 or greater.
C alibration Standards. Standards ranging in concentration from approximately 1.0 to 1000 ng/mL were used for the calibration curves. The standard curve points had an injection volume of 10 uL. In some instances, the 1.0 ng/mL standard was injected at smaller volumes (1 ,2, and 5 uL), this was done to extend the low end of the calibration curve. Calibration curves were run before every analytical sequence. Percent deviations o f each calibration standard were calculated. High-end curve points that were outside the 20% criteria o f the target concentration were excluded from the curve calculations. Low-end curve points that were outside the 20% criteria were included in the curve calculations but excluded from the Lower Limit o f Quantitation (LLOQ).
C ontinuing C alibration V erifica tion (CCV). For quantitative determinations, a mid-level matrix calibration check was analyzed at least every ten samples to monitor instrumental drift, with a lim it of 20% deviation of the target concentrations.
Low er L im it o f Q uantitation (LLOQ). The LLOQ was equal to the lowest standard in the calibration curve, with a level o f accuracy within 20%, that demonstrated a response greater than two times the response o f analyte in the blank samples.
System S u ita b ility. Five system-suitability standards were analyzed before each initial calibration curve to measure the precision of the retention times and peak area. The precision criterion o f 5% for the mean area recovery was achieved.
Lab C ontrol Spikes (LCS). LCSs were performed for the River Sediments. However, the information was not used because the data suggested it was impossible to recover spiked analytes from acidified water when river sediment was not present.
Matrix Spikes (MS). Matrix spikes were performed for the Fish Tissue and the River Sediment samples. Desirable matrix spike recoveries are 30%. Not all matrix spikes met this criteria.
The Fish Tissue data was quantitated using an extracted calibration curve while the River Water and River Sediment samples were quantitated using unextracted calibration curves. The calibration curve range that was injected was from 1 ng/mL to 1000 ng/mL, but the range used differed. The tables that follow contain either the calibration standard or the sample preparation method Lower Limit of Quantitation (LLOQ) for the analytes for each sample at each location along with batch used and the analysis date. The sample preparation method LLOQs will be annotated in the tables.
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Table 6a. PFOS Calibration Standard Reprocessing Summary
PFOS CONCENTRATION
Sam pleT ype and Location
Batch and A nalysis Date
Lower Limit of Quantitation (LLOQ)
Catfish, SL-1
0020629,29 Jun02
2.5ngfe
Catfish, SL-2 Catfish, SL-3
D020629,29 Jun02 D020702,02 Jul02
2.5ng/g 1.0ng/g
Large Mouth Bass, SL-1
D020626,26 Jun02
1.0ng/g
Large Mouth Bass, SL-2
D020628,28 Jun02
2.5ng/g
Large Mouth Bass, SL-3
D020628,28 Jun02
2.5 nglg
Small Mouth Bass, SL-3
D020628,28 Jun02
2.5ng/g
RiverWater, SL-1
0020812A, 12Aug 02
125pg/rtiL*
RiverWater, SL-2
D020812A, 12Aug 02
125 pg/mL*
RiverWater, SL-3
0020812A, 12Aug 02
125pg/mL*
RiverWater, SL-1
D020812B, 12Aug 02
1.25 ngfaiL*
RiverWater, SL-2
0020812B, 12Aug 02
1.25 nmL*
RiverWater, SL-3
0020812B, 12Aug 02
1.25ng/mL*
RiverSediment SL-1 raver Sediment SL-2
1021112,12 Nov02 1021112,12 Nov02
250 pg/gT 250pg/g*
RiverSediment SL-3
1021112,12 Nov02
250pg/g*
* Denotes sam ple preparation method LLOQ. Method LLOQ = Instrument LLOQ/Method Concentration
Factor.
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Table 6b. FOSA Calibration Standard Reprocessing Summary
FOSA CONCENTRATION
Sample Type and Location
Batch and A nalysis Date
Lower Limit of Quantitation (L L O Q )
Catfish, SL-1
D020629,29 Jun02
2.5ng/g
Catfish, SL-2
D020629,29 Jun02
2.5ng/g
Catfish, SL-3
D020702,02Jul 02
2.5ngig
Large Mouth Bass, SL-1
D020626,26 Jun02
5.0ng/g
Large MouthBass, SL-2
0020628,28 Jun 02
5.0ng/g
Large MouthBass, SL-3
D020628,28 Jun02
S.Ong/g
Small Mouth Bass, SL-3
D020628,28 Jun 02
5.0ng/g
RiverWater, SL-1 RiverWater, SL-2
0020812A, 12Aug02 D020812A, 12Aug02
25 pg/mL* 25 pg/mL*
RiverWater, SL-3
D020812A, 12Aug02
25 pg/mL'
RiverWater, SL-1
D020812B, 12Aug 02
1.25ng/mL*
RiverWater, SL-2 RiverWater, SL-3
020812B, 12Aug 02 D020812B, 12Aug02
1.26ng/hnL* 1.25 ngimL*
RiverSediment SL-1
1021112,12 Nov02
50pg/g*
RiverSediment SL-2
1021112,12 Nov02
50pg/g*
RiverSediment SL-3
1021112,12NOV02
!
50 pg/g*
*FaDcetonro.tes sample preparation method LLOQ. Method LLOQ * Instrument LLOQ/Method Concentration
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Table 6c. PFOA Calibration Standard Reprocessing Summary
PFOA CONCENTRATION
Sample Type and Location
Batch and A nalysis Date
Lower Liiy.ii orQ uantitation (LLOQ)
Catfish. Sl-1
D020629,29 Jun02
5.0 ng/g
Catfish, SL-2
D020629,29 Jun02
5.0 ng$
Catfish, SL-3
D020702,02 Jul 02
5.0 ng/g
Large Mouth Bass, SL-1
D020626,26 Jun02
2.5ngfg
Large Mouth Bass, SL-2
D020628,28 Jun02
5.0 ng/g
Large MouthBass, SL-3
D020628,28 Jun02
5.0 ng/g
Small Mouth Bass, SL-3
D020628,28 Jun02
5.0 ng/g
RiverWater, SL-1
D020812A, 12Aug 02
50pg/mL*
RiverWater, SL-2
D020812A, 12Aug 02
50pg/mL*
RiverWater, SL-3
D020812A, 12Aug02
50pg/mL*
RiverWater, SL-1
D020812B, 12Aug 02
1.25 ng/mL*
RiverWater, SL-2
D020812B, 12Aug 02
1.25 ng/mL*
RiverWater, SL-3
D020812B, 12Aug 02
1.25 ng/mL*
RiverSediment SL-1 RiverSediment SL-2
1021112,12 Nov 02 1021112,12 Nov02
250pg/g* 250pg/g*
RiverSediment SL-3
1021112,12 Nov02
250pg/g*
* Denotes sample preparation method LLOQ. Method LLOQ - Instrument LLOQ/Method Concentration Factor.
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Table 6d. PFHS Calibration Standard Reprocessing Summary
PFHS CONCENTRATION
Sample Type and Location
Catfish, SL-1
Catfish, SL-2
Batch and A nalysis Date
0020629,29 Jun02 0020629,29 Jun 02
Lower Limit of Quantitation (L L O Q )
2.5ng/g
2.5ng/g
Catfish, SL-3
D020702,02 Jul02
2.5 ng/g
Large Mouth Bass, SL-1
D020626,26 Jun 02
1.0ng/g
Large Mouth Bass, SL-2 Large Mouth Bass, SL-3
D020628,26 Jun 02 D020628,28 Jun 02
1.0ng/g 1.0ng/g
SmallMouthBass, SL-3
D020628,28 Jun02
LOng/g
RiverWater, SL-1
D020812A, 12Aug 02
25pg/mL*
RiverWater, SL-2
D020812A, 12Aug02
25pg/mL*
RiverWater, SL-3
020812A, 12Aug 02
25pgAnL*
RiverWater, SL-1
D020812B, 12Aug02
1.25ng/mL'
RiverWater, SL-2
D020812B, 12Aug 02
1.25 ng/mL*
RiverWater, SL-3
D020812B, 12Aug 02
1.25 ng/mL*
RiverSediment SL-1
1021112,12 Nov02
100 pg/g*
River Sediment SL-2
1021112,12 Nov 02
100 pg/g*
RiverSediment SL-3
1021112,12 Nov02
100 pg/g*
* Denotes sample preparation method LLOQ. Method LLOQ = Instrument LLOQ/Method Concentration Factor.
001766
Report E02-0443
Tenn. River Valley Sam ples
Table 6e. PFBS Calibration Standard Reprocessing Summary
PFBS CONCENTRATION
Sample Type and L ocation Catfish, SL-1
Catfish, SL-2 Catfish, SL-3
Batch and A nalysis Date
D020629,29 Jun02 0020629,29 Jun02 D020702,02 Jul02
Lower Limit of Quantitation (L L O Q )
S.Ong/g
5.0 ng/g
5.0 ng/g
LargeMouth Bass, SL-1 Large Mouth Bass, SL-2 Laige Mouth Bass, SL-3
D020626,26 Jun02 D020628,28 vlun02 D020628,28 Jun02
1.0 ng/g 2.5 ng/g 2.5 ng/g
Small MouthBass, SL-3
D020628,28 Jun02
2.5 ng/g
RiverWater, SL-1 RiverWater, SL-2 RiverWater, SL-3 RiverWater, SL-1 RiverWater, SL-2 RiverWater, SL-3
D020812A, 12Aug 02 D020812A, 12Aug02 D020812A, 12Aug02 D020812B, 12Aug 02 D020812B, 12Aug 02 020812B, 12Aug02
50pg/mL* 50pg/mL* 50pg/mL* 1.25 ng/mL* 1.25 ng/mL* 155 ng/mL*
RiverSediment SL-1
1021112,12 Nov 02
100pg/g*
RiverSediment SL-2
1021112,12 Nov02
100pg/g*
RiverSediment SL-3
1021112,12 Nov02
1
100pg/g*
* Denotes sample preparation method LLOQ. Method LLOQ = Instrument LLOQ/Method Concentration Factor.
001767
Report E02-Q443
Tenn. River Valley Sam ples
B la n k s .
Method blanks, Milli-Q water taken through the solid phase extraction process, provided a measure o f method background. In this experiment, they were labeled as "WB". One set was prepared for each location. In the Fish Tissue portion o f the experiment, they were run with the Catfish samples. Acceptable values for the blanks were less than 50% o f the Lower Limit O f Quantitation (LLOQ). All method blanks in this study met this criterion.
The Fish Tissue segment of the experiment also contained method blanks for the SPE cartridges. These were labeled as "SB" and consisted of methanol that was used to extract pre-conditioned columns that did not have any sample added. All o f these method blanks met the previous criterion.
Solvent blanks/Methanol blanks (methanol injections) provided a measure of instrument contamination. Acceptable solvent blanks must contain levels of target analyte less than 50% o f the Lower Limit O f Quantitation (LLOQ). A ll of the solvent blanks in this study met this criterion except the following:
Note - Solvent Blanks that were before the System Suitability injections and did not pass the criteria are not recorded below.
D020626 extracted samples 0050 (PFBS, PFHS, and PFOA) and 0051 (PFHS). These were caused by carryover from higher level standard curve points. The solvent blanks that were run after these points showed minimal carryover.
D020628 sample 0051 (PFBS, PFHS, and PFOA), 0052 (PFHS), and 0053 (PFHS). This was caused by carryover from the high-level standard curve point. The solvent blanks that were run after showed minimal carryover.
D020629 samples 0059 (PFHS, PFOA, FOSA, and PFOS), 0060 (PFOS), and 0061 (PFHS, PFOA, and PFOS). This was caused by carryover from high-level standard curve points. The 0061 Methanol Blank had a significant level of analytes but this had no effect on the quality of the data. The next sample had trace amounts of analyte and was below the LLOQ for all analytes. Therefore, the 0061 Methanol Blank did not influence the sample. The next solvent blank (0067) had nominal analyte concentration.
D020702 samples 0042 (PFOS), 0059 (PFHS and PFOS), 0060 (PFOS), and 0061 (PFOS). This was caused by carryover from the high-level standard curve point The solvent blanks that were run after showed minimal carryover.
D020812(A) samples 0016 (PFOA and FOSA) and 0031 (PFOA). These were caused by carryover from higher level standard curve points or system suitability points. The solvent blanks that were run after these points showed minimal carryover. Samples 0037 (PFOA) and 0039 (PFBS, PFHS, and PFOA) had carry-over from samples. Subsequent blanks showed minimal contamination.
1021112 samples 012 (PFBS, PFOA, and FOSA), 027 (PFBS, PFOA, and FOSA), 039(FOSA), 066, (PFOA and FOSA), 068 (FOSA), and 071 (FOSA). All of these can be attributed to carryover from high-level standards or samples.
001768
Report E 02-0443
Tenn. R iver Valley Sam ples
Data Summary
Tables 7a, 7b, 7c, and 7d present the data for individual samples. Table 8 summarizes the average data for sample groups. Representative chromatograms are presented in Attachment C. Tables 7a, 7b, 7c, and 7d display the on-column and corrected concentrations for individual samples. Also included are the average concentrations for each set o f samples standard deviation, and % Coefficient of Variation, when applicable. The final values reported are corrected for dilution/concentration factors introduced during sample preparation and by injection volume differences. The reported values were not adjusted for Matrix Spike Recoveries. The abbreviations are as follows: SL - Sample Location, C - Catfish, LM - Large mouth bass, SM Small mouth bass, RW - River Water, and RS - River Sediment
001769
Report E02-0443
Tenn. River Valley Sam ples
Table 7a. Catfish Analytical Data.
LIMS
U
Sam pio Name
A im
42778 42779 42780 42781 42782 42783 42784 42785 42786 42789 42790 42791 42792 42793 42794 42795 42796 42797
SL-1; C-1-1 SL-1; C-1-2 SL-1. C-1-3
SL-1. C-2-1 SL-1. C-2-2 SL-1. C-2-3
SL-1. C-3-1 SL-1. C-3-2 SL-1. C-3-3
SL-1. C-4-1 SL-1. C-4-2 SL-1. C-4-3
SL-1. C-5-1 SL-1. C-5-2 SL-1. C-5-3
SL-1. C-6-1 SL-1. C-6-2 SL-1. C-6-3
SL-2; C-1-1 SL-2; C-1-2 SL-2. C-1-3 SL-2. C-2-1 SL-2. C-2-2 SL-2. C-2-3
SL-2. C-3-1 SL-2. C-3-2 SL-2. C-3-3
SL-2. C-4-1 SL-2. C-4-2 SL-2. C-4-3
SL-2. C-5-1 SL-2. C-5-2 SL-2. C-5-3
SL-2. C-6-1 SL-2. C-6-2 SL-2. C-6-3
SL-2. C-7-1 SL-2. 07-2 SL-2. C-7-3
SL-3; C-1-1 SL-3; C-A-2 SL-3. 01-3
SL-3. 02-1 SL-3. C-2-2 SL-3. C-2-3
SL-3. 03-1 SL-3. 03-2 SL-3. 03-3
SL-3. 04-1 SL-3. C-4-2 SL-3. C-4-3
SL-3. 05-1 SL-3. 05-2 SL-3. C-5-3
SL-3. 06-1 SL-3. 06-2 SL-3. C-6-3
PFBS
(ng'g)
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ
<LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
PFHS
(ng/g)
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ
<LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
PFOA
(^g/g)
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ
<LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
FOSA On-
column
(ng/g)
5.9 5.3 5.2
4.4 4.2 3.9
7.0 7.1 7.4
3.9 3.7 3.8
9.1 9.1 8.8
7.0 6.9 7.0
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ
<LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
FOSA Corr. for
Smpl Prep
(ng/g) 58.7 53.5 52.0
44.5 41.7 39.1
70.5 70.8 73.8
39.3 36.7 38.2
91.0 90.7 87.5
69.8 69.1 69.8
Ave. Strici. D
and 7oC.V.
54.7 3.49 6.4%
41.8 2.67 6.4%
71.7 1.85 2.6%
38.1 1.30 3.4%
89.8 1.95 2.2%
69.5 0.41 0.6%
PFOS Oncolumn
(ng'g)
10.5 10.0
9.8 9.2 8.6
16.1 17.9 19.2
17.1 16.2 16.6
8.1 8.0 7.8
5.9 6.0 5.9
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<l l o q <LLOQ <LLOQ <LLOQ <llo q <LLOQ
<LLOQ <LLOQ
<LLOQ
<LLOQ <LLOQ <LLOQ
1.9 1.9 1.4
1.2 1.1 1.2
<LLOQ <LLOQ <l l o q
3.7 3.5 4.0
<LLOQ <l l o q <LLOQ <LLOQ
2.3 2.3
PFOS Corr. f or Smpl Prep
(ng/g)
112 105 100
97.6 91.8 86.1
161 179 192
172 165 166
80.8 80.2 77.5
58.8 59.7 58.7
Ave. Stnd. D
and
%C.V.
106 6.00 5.7%
91.8 5.77 6.3%
178 15.67 8.8%
166 4.82 2.9%
79.5 1.74 2.2%
59.1 0.57 1.0%
18.8 17 18.7 2.75 14.0 16.0% 11.5 11.7 11.5 0.44 12.2 3.7%
36.9 37.4 35.1 2.72 40.4 7.3%
23.3 23.5 23.2
001770
Report E 02-0443
Tenn. River Valley Sam ples
Table 7b. Large mouth and Small mouth Bass Analytical Data.
LIMS it
Sample Name
PFBS PFHS (ng/g) (ng/g)
42798 42799 42800 42801 42802 42803 42804 42805 42806 42807 42808 42809 42810 42811 42812 42813 42814 42815
SL-1; LM-1-1 SL-1; LM-1-2 SL-1. LM-1-3
SL-1. LM-2-1 SL-1. LM-2-2 SL-1. LM-2-3
SL-1. LM-3-1 SL-1. LM-3-2 SL-1. LM-3-3
SL-1. LM-4-1 SL-1. LM-4-2 SL-1. LM-4-3
SL-1. LM-5-1 SL-1. LM-5-2 SL-1. LM-5-3
SL-1. LM-6-1 SL-1. LM-6-2 SL-1. LM-6-3
SL-2; LM-1-1 SL-2; LM-1-2 SL-2. LM-1-3
SL-2. LM-2-1 SL-2. LM-2-2 SL-2. LM-2-3
SL-2. LM-3-1 SL-2. LM-3-2 SL-2. LM-3-3
SL-2. LM-4-1 SL-2. LM-4-2 SL-2. LM-4-3
SL-3; LM-1-1 SL-3; LM-1-2 SL-3. LM-1-3 SL-3. LM-2-1 SL-3. LM-2-2 SL-3. LM-2-3
SL-3. LM-3-1 SL-3. LM-3-2 SL-3. LM-3-3
SL-3. LM-4-1 SL-3. LM-4-2 SL-3. LM-4-3
SL-3. LM-5-1 SL-3. LM-5-2 SL-3. LM-5-3
SL-3. LM-6-1 SL-3. LM-6-2 SL-3. LM-6-3
SL-3. LM-7-1 SL-3. LM-7-2 SL-3. LM-7-3
SL-3. SM-1-1 SL-3. SM-1-2 SL-3. SM-1-3
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <l l o q
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ
<LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ
<LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ
<LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <llo q
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ 6.4
<LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ
<LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LL0Q <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
PFOA
Corrected
for Smpl
Prep (ng/g)
64.3
FOSA
Corrected
(ng/g)
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <aoa
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ
<LL0Q <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <lloq <llo q
18.5 13.0 14.0
63.6 61.4 57.2
73.2 80.8 82.4
68.8 75.7 65.3
46.6 41.5 38.9
69.3
5669..90
<LL0Q <LLOQ <LLOQ
2.6 <LLOQ <LLOQ
9.7 11.8 8.5
53.1 54.1 56.9
<LLOQ <LLOQ <LLOQ
<LLOQ
<LL0Q <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOO <LLOQ
<LLOQ <LLOQ <LLOQ
PFOS Coi rccteci
for Smpl
Prep
(ng/g)
186 130 140
636 614 572 732 808 824
688 757 653
466 415 389
693 599 660
152 29.6 19.5%
607 32.5 5.4%
788 49.2 6.2%
700 52.7 7.5%
423 39.0 9.2%
651 47.8 7.3%
25.6
96.7 100
118 16.7 84.7 16.7% 531 547 541 20.0 569 3.7%
1771
Report E 02-0443
Tenn. River Valley Sam ples
Table 7c. raver W ater Analytical Data.
LIMS #
38025 38026 38033 38034 38037 38038
LIMS n
38025 38026 38033 38034 38037 38038
LIMS It
38025 38026 38033 38034 38037 38038
LIMS #
38025 38026 38033 38034 38037 38038
LIMS n
38025 38026 38033 38034 38037 38038
Sample Name
SW01 SW01-Dup
SW03 SW03-Dup
SW02 SW02-Dup
(,nPgJF/,BmSL, ,)
3.0 3.7
<LLOQ <LLOQ
<LLOQ <LLOQ
Sample Name
SW01 SW01-Dup
SW03 SW03-Dup
SWQ2 SW02-Dup
Sample Name
SW01 SWOl-Dup
SW03 SW03-DUP
SW02 SW02-Dup
Sample Name
SW01 SWOl-Dup
SW03 SW03-Dup
SW02 SW02-Dup
Sample Name
.nPg3F/.Hm.SL.)
7.7 8.0
<LLOQ 0.3 0.4 0.2
(.n,,PgJFr/.Om_..AL. )
21.3 22.7 <LLOQ <LLOQ
<LLOQ <LLOQ
,nFgJO/,mSALa, ,)'
1.0 1.0
<LLOQ <LLOQ
<LLOQ <LLOQ
,nPngF/,OmSL r
SW01 SWOl-Dup
SW03 SW03-Dup
SW02 SW02-Dup
I 18.5 20.8
I <LLOQ 1 <LLOQ
<LLOQ <LLOQ
f,oA(.rndl.ngju/j,ms.VteL.o)d.l,. 1.50 1.85
f,oA,rndl,gnju/j,ms.Vt,eL,,od.l,. 3.86 3.98
0.13 0.20 0.12 f.oA(,rndl:gnju/fjm.s.Vt.eL.o)d,l. 10.7 11.3
t.oA(,rndI:gj1nu/jms. tVeL, o)d, l,. 0.48 0.51
f,oA(.rdnlj,gnu//jm-s.VtL,eo)d.l. 9.25 10.4
Adjusted for cS-am.ppgl,/e,mPnL1 r),ep.
75 93
S,,Aadm(,jpupgsl,/et,medP_L, )r.feop1r. 193 199
6.5 9.8 6.2 Adjusted for So ampl1e Pnrep. ,pg/,mL, ), 533 566
S_Aadm,'jpupgsl./et.medPL, r),feopr. 24 26
SAadm(,jpupgsl/e,tmed,,PL, r),feop1r. 462 520
A,pvcejrimagL,e,)' 84
<UOQ <LLOQ
A,pvgJe/r.ma.gL.e 196 6.5 8.0
A,pvge/r.ma.gL.e)' 550
<UOQ <LLOQ
A, pvge/r,magL, e,)
' 25 <LLOQ <LLOQ
A,pvgJe/r.ma.gL.e 491
<LLOQ <LLOQ
The sample extracts were analyzed several times using different sized injection volumes in order to match the appropriate analytical ranges for extracted samples, matrix spikes, and calibration curves. Table 7c incorporates data using 20 uL extracted sample injection volumes, 2 uL matrix spike injection volumes, and 10 uL calibration curve injection volumes.
001772
Report E02-0443
Tenn. River V alley Sam ples
Table 7d. River Sediment Analytical Data.
UMS #
38044 38044 38044 38045 38045 38045 38046 38046 38046
l IMS ft
38044 38044 38044 38045 38045 38045 38046 38046 38046
l#
38044 38044 38044 38045 38045 38045 38046 38046 36046
LIMS #
38044 38044 38044 38045 38045 38045 38046 38046 38046
LIMS
38044 38044 38044 38045 38045 38045 38046 38046 38046
Sample Name
38044-1, SL-1 38044-2, SL-1 38044-3, SL-1
38045-1 ,SL-3 38045-2, SL-3
38045-3, SL-3
38046-1, SL-2 38046-2, SL-2 38046-3, SL-2
Sample Name
38044-1, SL-1 38044-2, SL-1 38044-3, SL-1
38045-1, SL-3 38045-2, SL-3 38045-3, SL-3
38046-1, SL-2 38046-2, SL-2 38046-3, SL-2
Sample Name
38044-1, SL-1 38044-2, SL-1 38044-3, SL-1
38045-1, SL-3 38045-2, SL-3 38045-3, SL-3
38046-1, SL-2 38046-2, SL-2 38046-3, SL-2
Sample Name
38044-1, SL-1 38044-2, SL-1 38044-3, SL-1
38045-1, SL-3 38045-2, SL-3 38045-3, SL-3
38046-1, SL-2 38046-2, SL-2 38046-3, SL-2
Sample Name
38044-1, SL-1 38044-2, SL-1 38044-3, SL-1
38045-1, SL-3 38045-2, SL-3 38045-3, SL-3
38046-1, SL-2 38046-2, SL-2 38046-3, SL-2
On Column PFBS (ng/g)
10.6 10.6 13.5
8.9 8.3
10.0
8.9 6.2 11.7
On Column PFHS (ng/g)
2.7 2.6 2.5
<LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
On Column PFOA (ng/g)
16.2 14.1 13.7
<LLOQ 2.6
<LLOQ <LLOQ <LLOQ <LLOQ
On Column FOSA (ng/g)
29.7 32.4 24.5
1.2 1.2 1.7
2.9 2.5 3.2
On Column PFOS (ng/g)
67.7 70.3 50.4
9.1 6.8 9.1
9.0 8.5 10.5
Adjusted for Inj Vol. (ng/g)
5.3 5.3 6.7
4.4 4.1
5.0
4.5 3.1 5.8
Adjusted for Inj. Vol. (ng/g)
1.4 1.3 1.2
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
Adjusted for Inj. Vol. (ng/g)
8.1 7.1 6.9
<LLOQ 1.3
<LLOQ
<LLOQ <LLOQ <LLOQ
Adjusted for Inj. Vol. (ng/g)
14.8 16.2 12.2
0.6 0.6 0.8
1.5 1.3 1.6
Adjusted for Inj. Vol. (ng/g)
33.8 35.1 25.2
4.5 3.4 4.6
4.5 4.2 5.3
Adjusted for Sample Prep, (pg/g)
530 530 674
444 415
502
447 309 583
Adjusted for Sample Prep, (pg/g)
136 132 124
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
Adjusted for Sample Prep, (pg/g)
810 705 686
<LLOQ 131
<LLOQ <LLOQ <LLOQ <LLOQ
Adjusted for Sample Prep, (pg/g)
14B0 1620 1220
62 60 83
146 126 161
Adjusted for Sample Prep, (pg/g)
3380 3510 2520
454 342 456
452 425 525
Average, Std. Dev., and VuC.V. (pg/g)
577 84 14%
452 44
10%
437 137 31%
Average, Std. Dev., and 7oC.V. (pg/g)
130 6 5%
<LLOQ <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
Average, Std. Dev., and %C.V. (pg/g)
732 67 9%
131 <LLOQ <LLOQ
<LLOQ <LLOQ <LLOQ
Average, Std. Dev., and %C.V. (pg/g)
1440 201 14%
68 12 18%
141 17 12% Average, Std. Dev.. and %C.V. (pg/g)
3130 541 17%
416 65 16%
457 52 11%
001773
Report E02-0443
Tenn. River Valley Sam ples
Summaries for the average analyte concentration per sampling group and location are given below.
Table 8. Sample Location, Sample Type, and Analytical Data Summary. Fish Tissue
Sampling Location & Species Sampled
PFBS (ng/g)
PFHS (ng/g)
PFOA (ng/g)
FOSA (ng/g)
PFOS (ng/g)
SL-1, C (n=6) SL-2, C (n=7) SL-3, C (n=6) SL-1, LM (n=G) SL-2, LM (n=4) SL-3, LM (n=7) SL-3, SM (n=1)
<LL0Q <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LL0Q
<LL0Q <LLOQ <LL0Q <LLOQ <LLOQ <LLOQ <LL0Q
River Water
<LLOQ <LLOQ <LLOQ
64.3 <LLOQ <LLOQ <LLOQ
60.9 <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ <LLOQ
113 <LLOQ
22.3 553 281 <LLOQ <LLOQ
SL-1, RW SL-2, RW SL-3, RW
PFBS (Pg/mL)
84 <LLOQ <LL0Q
PFHS (pg/mL)
PFOA (pg/mL)
196 550 8 <LLOQ 7 <LLOQ
River Sediments
FOSA (p g /m L )
25 <LLOQ <LLOQ
PFOS (pg/mL)
491 <LLOQ <LLOQ
PFBS (pg/g)
PFHS (pg/g)
PFOA (pg/g)
FOSA (pg/g)
PFOS (pg/g)
SL-1, RS
577
130
732
1440
3130
SL-2, RS
437
<LLOQ
<LLOQ
141
457
SL-3, RS
452 <LLOQ 131
68 416
ICn nCuamtFbIsehr,ofLHMah Lpaerrgetmriopulitnhg bgarsosu,p.SM Small mouth bass, RW River water, RS River Sediments, and
Attachment B contains additional data summary tables.
S t a t is t ic a l M e t h o d s
Statistical methods were limited to calculating averages, standard deviations and % coefficient of variation.
001774
Report E02-0443
Tenn. River Valley Samples
Statement of Conclusion
Fish Tissue: Fish tissue obtained from Sample Location 1 contained quantifiable levels of PFOA, FOSA, and PFOS. Fish tissue obtained from Sample Locations 2 and 3 contained quantifiable levels of PFOS only. River W ater: W ater from Sampling Location 1 contained quantifiable levels o f PFBS, PFHS, PFOA, FOSA, and PFOS. W ater obtained from sample Locations 2 and 3 contained quantifiable levels of PFHS only. River Sedim ents: River Sediment obtained at Sample Location 1 contained quantifiable levels of PFBS, PFHS, PFOA, FOSA, and PFOS. River Sediment obtained at sample Location 2 contained quantifiable levels of PFBS, FOSA, and PFOS. River Sediment obtained at sample Location 3 contained quantifiable levels of PFBS, PFOA, FOSA, and PFOS.
References
1. 3M Environmental Method ETS-8-155.1 "Analysis of W aste Stream, W ater Extracts Or Other Systems Using HPLC-Electrospray/Mass Spectrometry".
List of Attachments
Attachm ent A: Analytical Method and SOP Deviations Attachment B: Data Summary Tables Attachment C: Sample Chromatograms Attachment D: Sample Prep Sheets, Test Substance, and Test System Information Attachment E: Notes to File
Report Revisions
Typographical errors for the unit designators for Tables 1 ,6a-e, 7a, 7b, 7d, and 8 were corrected. The number of fish sampled at each location was also added to Tables 1 and 8.
U0 1 7 7 3
Report E02-0443
w
Tenn. R iver V alley Sam ples
Signature Page
We certify that this report is a true and complete representation of the data for this study:
*****>!* --
---------------
W illiam K. Reagen,
Testing Facility Management
Date
'* 3
001776
Report E02-0443
Tenn. River Valley Sam ples
Attachment A: A nalytical Method and SOP Deviations
001777
Report E02-0443
Tenn. River Valley Sam ples
Document may be used, i f current, for 14 days from 11/21/2002
3M Environmental Laboratory
M ethod Ana ly sis o f W aste Stream , W ater Extracts o r Oth er System s U sing
h p l c -E lectrospray/M ass Spectrom etry
M ethod N um ber: ETS-8-155.1 \
Author: Mark L. Anderson, Mark E. Ellcfson Approved By:
A doption Date: | / 1 00
Revision D ate:
o /* ^
001778
Report E 02-0443
Tenn. River Valley Samples
Document may be used, if current, for 14 days from 11/21/2002
1.0 Scope andApplication_______________________________
1.1 Ssycsotpeme:sTuhsiinsgmHetPhLoCd -deelescctrriobsepsrtahye/manaasslysspisecotfrowmasetterys.tream, water samples or other 1.1.1 Specific analytes, ions, matrices, solvents, solutions, quality controls, internal standard(s) and other parameters w ill be defined in the protocol or the sample preparation worksheets).
1.2 Applicable Compounds: Electrospray ionizable compounds. 1 3 M atrices:
1.3.1 Wsysatsetme Sstorreaams ds easnigdnoattheedrisnysthteempsromtoacyocloonrssiastmopfleaqpureepouarsaatniodn/owroorrkgashneicetsso)l.vent 1.3.2 WsolautetiroSnas.mTphleesminactlruidxewtailpl bweadteerf,ingerdoubnydtwheatperro, twoacsotleowrastaemr apnledporthepearraaqtiuoenous
worksheet(s).
2.0 Summary of Method__________________________________________
2.1 This method describes the analysis of electrospray ionizable compounds, using HPLCelectrospray mass spectrometry (HPLC-ES/MS). The analysis is performed by the mass selection o f a single ion characteristic o f a particular compound.
3.0 Definitions____________________________________________________________
3.1 Atmospheric Pressure Ionization (API): Commercially available HPLC-ES/MS single quadrupole systems allow for various methods of ionization by utilizing a variety o f sources, probes, and interfaces. These include but are not limited to: Electrospray Ionization (ESI), Atmospheric Pressure chemical Ionization (APcI), Thermospray, etc. The ionization in these processes occurs at atmospheric pressure (i.e., not under a vacuum).
3.2 Electrospray Ionization (ES, ESI): A method o f ionization performed at atmospheric pressure, whereby ions in solution are transferred to the gas phase via tiny charged droplets. These droplets are produced by the application o f a strong electrical field.
3 3 M ass Spectrometer (MS): Commercially manufactured MS systems are equipped with single quadrupole mass selective detectors. Ions are selected on the basis o f mass to charge ratio (m/z) and subsequently detected.
3.4 M icromass MassLynx / HP ChemStation Software: System software designed for the specific operation o f an HPLC-ES/MS. Please refer to the manual for the specific instrument software.
3M Environmental Laboratory
Analysis Using HPLCE-TESle-cMtro5s5p.1ray/Mass Spectrometry
001779
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Report E 02-0443
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Document may be used, if current, for 14 days from 11/21/2002 4.0 Warnings and Ca u t io n s______________________ ______________________
4.1 Health and Safety Warnings: 4.1.1 Use caution with the voltage cables for the electrospray probe. When engaged, the probe employs a voltage o f approximately 5000 Volts. 4.1.2 When handling samples or solvents wear appropriate protective clothing, gloves, and eyewear.
4 2 C autions:
42.1 Operate solvent pumps below a backpressure o f400 bar (5800 psi). If the backpressure exceeds 400 bar, the HP1100 will initiate automatic shutdown.
4.2.2 Do not run solvent pumps to dryness.
5.0 Interferences______ ,
______________________________________
5.1 To minimize interferences when analyzing samples, Teflon should not be used for sample storage or any part o f instrumentation that comes in contact with the sample or extract
6.0 Equipment____________________________________________________________
6.1 Equipment listed below may be modified in order to optimize the system. Document any modifications in die raw data as method deviations. 6.1.1 Micromass Platform LCZ Mass Spectrometer (or equivalent) equipped with an electrospray ionization source. 6.1.2 HP1100 low pulse solvent pump, solvent degasser, column compartment, and autosampler or equivalent HPLC system.
7.0 Supplies and Materials
7.1 Supplies
7.1.1 High purity grade nitrogen gas regulated to approximately 100 psi (or house air system .).
7.1.2 HPLC analytical column, such as a Betasil C18 column (50x2mm, 5 pm particle size) or equivalent
7.13 Capped autovials or capped 15 mL centrifuge tubes.
8.0 Reagents and Standards____________
8.1 Reagents: 8.1.1 Methanol, HPLC grade or equivalent
001780
3M Environmental Laboratory
Analysis Using HPLCE-TESlc-8ct-r1o5s5p.1ray/Mass Spectrometry
Page 3 of 10
Report EQ2-0443
Tenn. River Valley Sam ples
Document may be used, if current, for 14 days from 11/21/2002
8.1.2 Milli-QTM water (ASTM type I), all water used in this method should be Milli-QTM water or equivalent, and may be provided by a Milli-Q TOC Plus system or another vendor.
8 .1 3 Ammonium acetate, reagent grade or equivalent 8.13.1 When preparing different amounts than those listed, adjust accordingly. 8.13.2 2.0 mM ammonium acetate solution: Weigh approximately 0.300 g ammonium acetate. Pour into a 2000 L volumetric flask, add the aSptoprreopartiraoteomvotleummpeeoraftMureil.li-Q water, mix until all solids are dissolved.
8.1.4 Other solvents and solutions may be used as stated in the protocol or the sample preparation worksheet.
8 3 C a lib ra tio n Standards:
8.2.1 Typically two method blanks (Milli-Q water), two matrix blanks, and a minimum o f 5 solvent standards are analyzed with each group o f samples.
9.0 Sample Handling ________ ________________________________________
9.1 Standards and prepared samples may be stored in capped autovials, capped 15 mL centrifuge tubes or other suitable containers until analysis.
9.2 If analysts will be delayed, standards and prepared samples may be refrigerated at approximately 4 C until analyses can be performed (refrigerator temperatures may have a detrimental affect on the solubility o f saturated solutions).
10.0 Quality Control__________________
10.1 Blanks:
10.1.1 Solvent blanks, method blanks, and matrix blanks ore prepared and analyzed 'with
each sample set to determine contamination or carryover. 10.1.1.1 When the study matrices consist of highly purified solvents such as Type 1
water or HPLC grade organic solvents, the method and matrix blanks may be represented by a single solvent blank. 10.1.2 Solvent blanks should be analyzed prior to each calibration curve. Method blanks and matrix blanks should be analyzed after the initial calibration curve but prior to the study samples. If carryover is a problem, consecutive solvent blanks may be necessary. 103 M atrix Spikes: 10.2.1 Matrix spikes may be prepared for each set of extracted samples (if applicable to the study) and analyzed to determine extraction efficiency.
3M Environmental Laboratory
Analysis Using HPLCE-TESIe-8ct-r1o3s5p.r1ay/Mas* Spectrometry
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Tenn. River Valley Samples
Document may be used, if current, for 14 days from 11/21/2002
10.2.2 Matrix spike duplicates may be prepared periodically to measure the precision associated with the analysis.
10.2.3 Analyze the matrix spike and matrix spike duplicate (if prepared) in the same run as the original sample.
10.2.4 Matrix spike and matrix spike duplicate concentrations should fidi in the mid range o fthe initial calibration curve or should be prepared at 1.5-5 times the endogenous concentration of the analyte. Spike concentrations should fidi in the low-range o f the initial calibration curve if extremely low levels are expected.
10.3 Continuing Calibration Verifications: 103.1 Continuing calibration verifications (CCV) are analyzed to verify the continued accuracy o f the calibration curve. 10.3.2 Analyze a mid-range calibration standard after every tenth sample, with a minimum o f one per sample set
10.4 Internal Standard/Surrogate Standard: 10.4.1 An internal standard (IS) may be used to quantify the target analytes by establishing a relationship between the ratio o f analyte response to IS response and a known concentration of the analyte o f interest. The IS should be spiked at an amount that will fall within the mid-range o f the calibration curve. The IS should be added after the extraction process and before analysis. 10.4.2 A surrogate standard may be used for quality control. The surrogate is used to quantitatively evaluate the entire analytical procedure including sample preparation and analysis. The surrogate should be spiked at the beginning o f the sample preparation and should fall within the low to mid-range o f the calibration curve.
11.0 Calibration and Standardization______________________________________
11.1 Analyze the standard curves prior to and following each set of samples. The average o f two standard curves may be plotted by linear regression (y = mx + b) weighted 1/x, or quadratic fit (y = axJ+ bx + c) using MassLynx or other suitable software. The calibration curves should not be forced through zero. 11.1.1 The closing calibration curve may be excluded if the CCV's meet acceptable criteria. If only the first curve is used, the calibration and standardization parameters are the same.
11.2 If the initial calibration curve does not meet acceptance criteria perform routine maintenance or prepare a new standard curve (if necessary) and reanalyze.
11.3 For purposes o f accuracy when quantitating low levels o f analyte, it may be necessary to use the low end of the calibration curve rather than the full range. Example: when
3M Environmental Laboratory
Analysis Using HPLCE-TESle-cgt-rtoSsSp.rlay/Mass Spectrometry
Page 5 of 10
Report E02-0443
Tenn. River Valley Samples
Document may be used, if current, for 14 days from 11/21/2002
attempting to quantitate approximately 10 ppb o f analyte, generate a calibration curve consisting o f the standards from 5 ppb to 100 ppb rather than the full range o f the curve (5 ppb to 1000 ppb). This will reduce inaccuracy attributed to linear regression weighting o f high concentration standards. 11.4 High and/or low points may be excluded from the calibration curves to provide a better fit over the linear range appropriate to the data or because they did not meet the pre determined acceptance criteria. Low-level curve points should also be excluded if their area counts are not at least twice that o f the method blanks. Justification for exclusion o f calibration curve points will be noted in the raw data. 11.4.1 A minimum o f 5 points will be used to construct the calibration curve.
12.0 Procedures____________________________________________________________
12.1 Acquisition set-up - please reference the SOP that pertains to the specific instrum ent. Actual parameters will be recorded on the instrument printouts.
12.1.1 Set up the sample list
12.1.1.1
Assign a sample list filename using the first letter o f the name o fthe instrument (T for Tucker), the year (00 for 2000), the month (04 for April), and the day (T001012 for October 12,2000 on Tucker). If more than one list is made on the same day, use increasing letters of the alphabet starting with A at the end of the list
12.1.1.2 Assign a method (MS) file.
12.1.13 Assign an HPLC program (Inlet file).
12.1.1.4 Type in sample descriptions and vial position numbers.
12.13 Tspoecctrreoamteeatemr hetehaoddin, gclsicakndonsemleectthSoIdRi.n Stheet iAoncqizuaitsiiotnionmcoodnetraoslappapnreolptrhiaetnemanadss mass to 499 or other appropriate masses. A full scan is usually collected in addition to the SIRs. Save acquisition method. See the Micromass MassLynx GUIDE TO DATA ACQUISITION for additional information.
12.13 Typically the analytical batch run sequence begins and ends with a set o f solvent standards.
12.1.4 Samples are analyzed with a continuing calibration verification (CCV) injected after every tenth sample. Solvent blanks should be analyzed periodically to monitor for possible analyte carryover.
123 Using the Autosampler/Column Heater 12.2.1 Place sample vials into the sample tray according to the sample list prepared in Section 12.1.1.
0 0 1 7 S3
3M Environmental Laboratory
Analysis
Using
ETS-g-155.1 HPLC-Eleetrospray/Mass
Spectrometry
Page 6 of 10
Report E02-0443
Tenn. River Valley Samples
Document may be used, if current, for 14 days from 11/21/2002
12.2.2 Attach the proper analytical column in the column heater compartment. If using the switching valve, ensure that the tubing is run to the appropriate ports.
12.3 Using the Inlet Editor
12.3.1 Set-up the HP1100 using the following conditions or at conditions the analyst considers appropriate for optimal response. Record actual conditions in the instrument logbook:
12-3.1.1 Sample size 10 pL injection
123.1.2 Flow rate = 300 pL/min.
12.3.1.3 Cycle time = 10.0 minutes
123.1.4
Mobile phase components:
Solvent A: 2.0 mM Ammonium Acetate in Water
Solvent B: Methanol (MeOH)
Solvent Gradient: Time (xnixi)
%B
0.00 5.00%
1.00 5.00%
4.50 95.0 %
8.00 95.0%
8.50 5.00%
10.0 Stop
12.4 Instrument Set-up
12.4.1 Refer to the Platform LCZ User's Guide, the MassLynx NT User's Guide, the ETS-9-36, "Operation and Maintenance o f the Micromass Platform LCZ Electrospray/Mass Spectrometer", or the SOP that pertains to the specific instrument
12.4.2 Checkthe solventlevelinreservoirs andrefill ifnecessary. 12.4.3 Check the rip o f the stainless steel capillary at the end o f the probe with an
eyepiece. The tip should be flat with no jagged edges. If the tip is found to be unsatisfactory, disassemble the probe and replace the stainless steel capillary.
12.4.4 Turn on the nebulizing gas.
12.4.5 Open the tune page. Click on `Operate' to initiate the desolvation heaters.
12.4.6 Open the Inlet Editor.
12.4.6.1 SetHPLCpumpto"On".
12.4.63 Set the solvent flow to the desired flow rate.
12.4.6.3 Observe droplets coming out of the tip of the probe. A fine mist should be
expelled with no nebulizing gas leaking around the tip o f the probe.
Readjust the tip of the probe if no mist is observed.
, ^_
U 01784
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Analysis Using HPLCE-TESle-8c-t1ro5sSp.r1ay/Mass Spectrometry
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Report E02-0443
Tenn. River Valley Samples
Document may be used, if current, for 14 days from 11/21/2002
12.4.6.4 Allow to equilibrate for at least 10 minutes.
12.4.7 The instrument uses these parameters at the following settings. These settings may change in order to optimize the response. Actual parameters will be recorded on the instrument printouts.
12.4.7.1 Drying gas 250-425 liters/hour 12.4.7.2 ESI nebulising gas 10-15 liters/hour 12.4.7.3 HPLC constant flow mode, flow rate 10 - 500 pL/min 12.4.7.4 Pressure <400 bar (This parameter is not set, it is a guide to ensure the
HPLC is operating correctly.) 12.4.7.5 Source Block temperature 150. 12.4.7.6 Desolvation temperature 250. 12.4.8 Print the tune page with its parameters, the Inlet page, sample list, mass
spectrometer information, and all other applicable information and store it in the study binder with copies taped into the instrument run logbook. 12.4.8.1 All copies must be initialed and dated. 12.4.9 Click on start button on the MassLynx toolbar. Ensure beginning and ending sample numbers encompass all samples to be analyzed.
13.0 Data Analysis andCalculations______________________________________
13.1 Calculations (including, but not limited to): 13.1.1 Calculate matrix spike percent recoveries using the following equation:
% Recovery = Observed Result - Background Result x 100 Expected Result
13.1.2 Calculate percent difference using the following equation: % Difference** Expected Cone. - Calculated Cone, x 100 Expected Cone.
13.1.3 Calculate actual concentration o f analyte in matrix (pg/mL):
On-Column Concentration (pg/mL) x Dilution Factors = Calculated Concentration
14.0 Method Performance__________________________________________________
14.1 The Limit o f Quantitation (LOQ) is method, analyte, and matrix specific. For many analytes, the LOQ concentration is selected as the lowest acceptable non-zero standard in the calibration curve.
O'
3M Environmental Laboratory
Analysis Using HPLECT-SE-le8c-1tr5o5s.p1ray/Mass Spectrometry
Page * of 10
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Tenn. River Valley Samples
Document may be used, if current, for 14 days from 11/21/2002
14.2 Solvent and method blank area counts must be < V%that o f the lowest standard used in the calibration curve.
143 The coefficient o f determination (i2) value for the calibration curve must be greater than or equal to 0.980.
14.4 Continuing Calibration Verification (CCV) percent recoveries must be 30% o f the standard concentration.
14 3 Internal Standard recoveries should be within 50% o f the spiked concentration. 14.6 If criteria listed in this method performance section are not met, maintenance may be
performed on the system and samples reanalyzed or other actions as determined by the analyst Document all actions in the raw data. 14.7 If data is to be reported when performance criteria have not been met, the data must be footnoted on tables and discussed in the text o f the report
15.0 Pollution Prevention and Waste Management___________________________
15.1 Sample extract waste and flammable solvent is disposed in high BTU containers, and glass pipette waste is disposed in broken glass containers located in the laboratory.
16.0 Recoups______________________
16.1 Bach page generated for a study must have the following information included either in the header or hand written on the page: study or project number, acquisition method, integration method, sample name, extraction date, dilution factor (if applicable), and analyst
16.2 Print die tune page, sample list acquisition method and all other applicable information trouninlcolgubdoeoikn.the appropriate study folder. Copy these pages and tape into the instrument
163 Plot the calibration curve then print these graphs and store in the study folder. 16.4 Print data integration summary, integration method, and chromatograms and file in the
study binder. 1 63 Summarize data using suitable software and store in the study binder. 16.6 Back-up electronic data to appropriate medium. Record the file names and location o f
backed-up electronic data in the study binder. 16.7 Documentation o f analyte(s) and all reference substances will include trace numbers,
lot #'s, purity, expiration, and storage conditions.
17.0 Attachments
17.1 None
3M Environmental Laboratory
Analysis Using HPLCE-TESle-cHtro5sJp.1ray/Mass Spectrometry
001786
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Tenn. River Valley Samples
Document may be used, if current, for 14 days from 11/21/2002
18.0 References
18.1 Platform LCZ User's Guide, Micromass UK Limited, Tudor Road, Altrincham, WA14 SRZ; or Floats Road, Wythenshawe M23 9LZ; United Kingdom.
18.2 MassLynx NT User's Guide, Micromass UK Limited, Tudor Road, Altrincham, WA14 5RZ; or Floats Road, Wythenshawe M23 9LZ; United Kingdom.
183 MassLynx NT Guide To Data Acquisition, Micromass UK Limited, Tudor Road, Altrincham, WA14 5RZ; or Floats Road, Wythenshawe M23 9LZ; United Kingdom.
18.4 ETS-9-34.0, "Operation and Maintenance o f Hewlett Packard HPLC 1100 System Equipped with a Mass Spectrometer Detector and/or a Photo Diode Array Detector".
18.5 ETS-9-36.0, "Operation and Maintenance o f the Micromass Platform LCZ Electrospray/Mass Spectrometer".
19.0 Affected Documents________________________________________________
19.1 None
20.0 Revisions
Revision
Revision
Number
Reason For Revision
Date
1 TitleChange
09 May 01
Section 1: Enlarged the scope of the method by including additional matrices. Also added
comments about specific parameters will be defined in the protocol or prep sheets.
SSSSeeeeccccttttiiiioooonnnns3381::: aCARnheddmad2neo:gdveRepddaetrmopaagoarrvlaalegopdrwharpaedlhfilefoofrweenrnieCncngeotsnfstvoyoersnsttehptimeeocnsuiasfailencvdocsfso.aoZmlft-tpeSworpnaurranaetdyi.vsp.ersoobleveinnttesralancdes.olutions.
Section 9: Broadened the types of storage containers and conditions.
Section 10: Added comments to allow for flexibility in quality controls for different types of
studies and applicability.
SSeeccttiioonn 1111:: AAddddeedd aa ppaarraaggrraapphh (a1ll1o.w4)inagllofowritnhgefeoxrctlhuedidnrgopopfidnigeosefccounrvdecpuorvinet.s and minimum
number of curve points needed.
Section 12: Added comments to reference the specific SOP's for set-up.
Section 12: Corrected numbering.
SSeeccttiioonn 1186:: AAddddeedd preafreargernacpehtoonthreecmoredthsoodffaonratlhyeteHs aenwdlestut-bPsatacnkcaerds.LC/MS.
3M Environmental Laboratory
Analysis Using HPLCE-TESI-cSc-t1ro5Ssp.1nyrMass Spectrometry
001787
Page 10 of 10
Report E02-0443
Record of Deviation
Tenn. River Valley Samples
I. Identification
Study / Project No. TN River Valley E02-0443
Deviation Type:
D SO P ^M ethod Equipment Procedure
(Check one)
Protocol Other:
Document Number: ETS-4-04.0 _________________________________
________
-
D ate(s) n Tu ^
o f occurrence: 3
r,sf
,9,
II. Description:
Required Procedure/process:_ ETS-4-04.0 section 4 states, "It is the responsibility o f anyone handling samples to record the movement o f those samples on the internal chain o f custody
f^ " _
1 .j.
,z ._ ' _ 7 1 7 ........ .
Actual Procedure/process: The internal chain o f custody forms were not generated or used in the course o f this study.
III. Actions Taken:
(such as amendment issued, SOF[revision, etc.) N o additional actionw ill be taken, as the information cannot be recalled solqng afterthefact.
Recorded By:
/'t "
'
/>
( { i t'l t- ^
)
7
IV. Impact on Study / Project
This deviation does not adversely affect the quality o f the data.
Date:
P h r <TL
Authorized By: (StudypirCctor JEr.oiect Lead)
/t
7T "
(-'/s . -
Dae:
r
XJUX788
3S i E nvironm ental Laboratoiy
Deviation N o .__ / (assigned by Study Director or Project Lead at the end ot`study or project)
Report E02-0443
Attachment B: Data Summary Tabues
Tenn. River Valley Samples
017S9
Report E02-0443
Term. River Volley Samplee
. ___
D020626Extrectad
O1 90
3M Environm ental Laboratory
Page 41 of 276
001791
Raport E02-0443
Tann. R iver V aley Sampias
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Page 42 o f 276
Report E02-0443
I I1
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3M Environm ental Laboratory
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D020628
Lars Mouth, Extnetod Curvo Sam * Location! 2 and 3
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s w n i T K oS T d MaOH S tar* ~ 3a m P C T " S jd E o D s h u m j
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OUOCQOB7.D S L4.LM O E
SAMPLE DU0E809BD SL-S .U LS A P O C B toa iC S L A IM S MS
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m & F o r B utitto b MaOHMfik - fs s R r
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Tenn. River V a le y Samples
Page 43 o f 276
001792
R tp o it E02-0443
3M Environm ental Laboratory
............ .e.
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Page 44 o f 276
01793
U01794
Report E02-0443
Tenn. River Valley Sample
5
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I
3M Environm ental Laboratory
Page 45 o f 276
001795
Report E02-0443
Tenn. River Valley Samples
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3M Environm ental Laboratory
Page 46 o f 276
Report E02-0443
.
D020702
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---TTTfaaannn~IMNtR*MOpmMHwrVrOVVVMOtMMMMMcyv^rTAnAA1MHMHHir.0PP7A0>rmra1n^p1.a*.101ll7:7770JJJ6JumwmJnui0O0n033H3O...COCaCiMUCmGAC)Q;MMMMMAAAAUM333000.63JAJEImJamii0033a
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TTTTTaanaaanWnnnA.MWWWaMrMwVPwrrkMvVvVOaMMaMaasncyyyrTAAAAANHSHHHHAPM4PHAPBnSmnm1p^p^h1-1--311*1i7:777*70J*JJJJ6nmmmm*J0mn000033333.0A..C..8CCCCMa0MMMMMeCCCCC:AsMMHMMHiIUUUAUfAe....3333MJh0000OJJJJEmmmmJun00CnO303Bat
016737 UM13327
2300006 10140
110760 30337 30071 0140 17404
231703
LOO ILO O
IU
00LL10OO00OQ0 *0LOQO
07J
MJOLOO
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133%
0% 133%
0%
231010
3071 3303
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210 3077
414111000
261130 707 3347 304
4413440330
ILO Q
W4iMOQ 0%
ILO O
LO O
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1010
ILO O
ILO O
0f.4lft-.~Jf%
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100 111100
0L0O0O
14441 161
LOQ
1470
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0337
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4332 LOO
LO Q
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1000
4% 47 86 7 103.1
LO O
3047
LOQ _ ILO Q
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LO Q
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3600 301010
640 10
MJLOQ
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346010
61001 138306
OLOO ILO Q
LO Q LO Q
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WLOUO.1
6t% 043 1163633
460 6446
UTM
ILO Q
ILO Q
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ILOO n*
17100
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7060
1 0 .4
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% 0%
100%
0%
7u2%
Laboratory
Tenn. River V a le y Samples
Page 47 of 276
001796
D020812A
001797
Report E02-0443
Tenn. River Valley Samples
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Pape 48 of 276
D020812A
Report E02-0443 3M Environm ent*! Laboratory
Tenn. River Valley Sample
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Page 49 of 276
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R poit E02-0443 3M Environmental Laboratwy
T0 8 T0 0
Tenn. River Valley Semples Page 52 of 276
Report E02-0443
Tenn. River Valley Samples
1021112 River Sediments
Sample Locations 1,2, and 3.
PFBS(299)
|VmuLoi-i) 222222222000000000
SampleMama 000000000444444444445904500333333333---------330333333880686868000000000444444444640454800---------111332223
Samplebite Area EEEEEEEEE000000000222222222---------OO0000000444444444444444444333333333---------333333333888888888000000000444444444443568845---------233312211;;;;;;;;;SSSSSSSSSLLLLLLLLL---------111332322;;:;;;;;; 4414111 343233433288862320532354720280106370585308647149408099
OnA(n-mCg/oomhuLinm)tnOAn(n-vCfalfortnahLgaa)nn fCo(ornrbgr/iemi.cLtVe)di
11111888803001....9..32..9.85607
11. 9.1 8.9
456454535.........117430538
CSaomr(rpP0444a95535lS741322c007e333tW199802Pedrafopr.
%SAtuCvdVer0(apgagen/g,d) 113544148041753343%%%7274
PFHS (399)
20 0443-30044-1 E02-0443-38044-1 ; SL-1; 1 122635 20 0443-30044-2 E02-0443-36044-2; SL-1; 1 110901 20 0443-30044-3 E02-0443-38044-3; SL-1; 1 111724 20 0453-30045-1 E02-0443-38045-1; SL-3; K 13341 20 0453-35045-2 E02-0443-38045-2; SL-3; 1 11489 20 0453-38045-3 02-0443-38045-3; SL-3; 1 12125 20 0463-38040-1 E02-0443-38046-1: SL-2; 4 17353 20 0403-38040-2 E02-0443-36046-2; SL-2; 4 19434 20 0463-38046-3 E02-O443-38046-3; SL-2; 1 25494
27 2.0 25 BLOQ BLOQ
BLOQ BLOQ BLOQ BLOQ
2.6 BLOQ BLOQ
PFOA (413)
20 0443-38044-1 E02-0443-38044-1; SL-1; 1 295590
16.2
14.7
20 0443-38044-2 E02-0443-38044-2; SL-1; 1 260003
14.1
20 0443-38044-3 E02-O443-38O44-3; SL-1; 4 253343
13.7
20 0453-38045-1 E02-O443-35O45-1; SL-3; 4 48045
BLOQ
2.8
20 0453-35045-2 E02-O443-38045-2; SL-3; 60231
26
20 0463-36045-3 E02-0443-3804S-3; SL-3: t 54999
BLOQ
20 0463-38040-1 E02-0443-38046-1; SL-2; 1 53375
BLOQ
BLOQ
20 0463-38046-2 E02-0443-38046-2: SL-2; 1 35197
BLOQ
20 0463-38046-3 E02-O443-38O46-3; SL-2; 1 40917
BLOQ
POSA (493)
20 0443-38044-1 E02-044S-3844-1; SL-1; 41250415
29.7
28.8
20 0443-38044-2 E02-0443-38044-2; SL-1; 1361450
32.4
20 0443-38044-3 E02-0443-38044-3; SL-1; 41033771
24.5
20 0453-38045-1 E02-0443-38045-1; SL-3; 4 48310
1.2
1.4
20 0453-38045-2 E02-0443-30045-2; SL-3; 4 48172
1.2
20 0453-38045-3 E02-0443-3804S-3; SL-3; 1 65768
1.7
20 0463-30046-1 E02-0443-38046-1; SL-2; i 120487
29
2.9
20 0463-30040-2 E02-0443-38048-2; SL-2; 4 103503
2.5
20 0463-30046-3 E02-0443-38046-3; SL-2; 133252
3.2
PFOS (499)
20 0443-36044-1 E02-O443-38044-1; SL-1; 42785277
67.7
62.8
20 0443-38044-2 E02-0443-38044-2: SL-1; 42885124 20 0443-38044-3 E02-0443-36044-3; SL-1; 42109105
70.3 50.4
20 0453-38045-1 02-0443-38045-1; SL-3: 418454
9.1
8.3
20 0453-35045-2 E02-0443-36045-2; SL-3; 4 323943
6.8
20 0453-38045-3 E02-0443-38045-3: SL-3; 420485
9.1
20 0463-38046-1 E02-0443-38046-1; SL-2; A 417236
9.0
9.3
20 0483-38046-2 E02-0443-38046-2; SL-2; 4 393650
6.5
20 0463-38046-3 E02-Q443-38046-3; SL-2; 4 478587
10.5
1.4 1.3 1.2 BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
8.1 7.1 0.9 BLOQ 1.3 BLOQ BLOQ BLOQ BLOQ
14.8 16.2 12.2 0.6 0.6 0.8 1.5 1.3 1.6
33.8 35.1 25.2 4.5 3.4 4.6 4.5 4.2 5.3
136 132 124 BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
806 704 685 BLOQ 13t BLOQ BLOQ BLOQ BLOQ
1481 1615 1221 62 60
82 143 124 157
3377 3506 2514 452 341 455 443 415 S14
130 6 s% BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
732 80 9% 131 BLOQ BLOQ BLOQ BLOQ BLOQ
1439 200 14% 60 12 18% 141 17 12%
3132 540 17% 416 85 16% 457 51 11%
R333a885g333000M588444S000f584ai444---wMMMm456npSSSplHeiWmt221w222(009g000m...03)..9.140y100m ci tmtw--watphn.
Average o t triplicata C orra cte d fo r In i. Voi. On-Col Amount * 0.5 C orrected fo r Sam ple Pran O ii-C o lA m o u n t*Q .8 *2 * 1008
Sample W eight (Ava)
T ! tie Final V d of the Extract (mL)
S M C onM w ttal
1/3/2003
001802
Pag 13 o f 21
Report E02-0443
Tenn. River Valley Samples
E02-0443
Combined Large Mouth Bass Data Table
PFOA 413)
! PFOS (499) I
J
U MS
Sample Name
Amount ng/g
Amount ng/g
Amount ng/g
Corrected forSm pt Prep (ng/g)
Amount ng/g
Amount ng/g
Corrected Ave, Stnd forSm pI Dev, and Prep (ng/g) %CV
42798 SL-1 ; LM-1-1 BLOQ
BLOQ
BLOQ
SL-1; LM-1-2 BLOQ
BLOQ
BLOQ
SL-1. LM-1-3 BLOQ
BLOQ
BLOQ
42799 SL-1. LM-2-1 BLOQ
BLOQ
BLOQ
SL-1. LM-2-2 BLOQ
BLOQ
BLOQ
SL-1. LM-2-3 BLOQ
BLOQ
BLOQ
42800 SL-1. LM-3-1 BLOQ
BLOQ
BLOQ
:
SL-1. LM-3-2 BLOQ
BLOQ
BLOQ
SL-1. LM-3-3 BLOQ
BLOQ
BLOQ
42801 SL-1. LM-4-1 BLOQ
BLOQ
BLOQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
18.5 13.0 14.0 63.6 61.4 57.2 73.2 80.8 62.4 68.8
185.5 130.0 139.7 635.5 614.0 571.7 732.1 807.7 824.4 688.4
152 29.61 19.5% 607 32.49 5.4% 788 49.18 6.2% 700
SL-1. LM-4-2 BLOQ
BLOQ
6.4
64.3
BLOQ
75.7
757.0
52.70
42802
SL-1. LM-4-3 SL-1. LM-5-1
BLOQ BLOQ
BLOQ BLOQ
BLOQ BLOQ
BLOQ BLOQ
65.3 46.6
653.3 465.5
7.5% 423
SL-1. LM-5-2 BLOQ
BLOQ
BLOQ
BLOQ
41.5
415.0
39.03
;
SL-1. LM-5-3 BLOQ
BLOQ
BLOQ
BLOQ
38.9
388.7
9.2%
3
42803 SL-1. LM-6-1 BLOQ
BLOQ
BLOQ
SL-1. LM-6-2 BLOQ
BLOQ
BLOQ
BLOQ BLOQ
69.3 59.9
693.2 599.1
651 47.78
SL-1. LM-6-3 BLOQ
BLOQ
BLOQ
BLOQ
66.0
660.2
7.3%
J
42804 SL-2; LM-1-1 BLOQ
BLOQ
BLOQ
I1
SL-2; LM-1-2 BLOQ
BLOQ
BLOQ
BLOQ BLOQ
BLOQ BLOQ
A
SL-2. LM-1-3 BLOQ
BLOQ
BLOQ
42805 SL-2. LM-2-1 BLOQ
BLOQ
BLOQ
BLOQ BLOQ
BLOQ 2.6
25.6
SL-2. LM-2-2 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
SL-2. LM-2-3 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
42806 SL-2. LM-3-1 BLOQ
BLOQ
BLOQ
BLOQ
9.7
96.7
100
SL-2. LM-3-2 BLOQ
BLOQ
BLOQ
BLOQ
11.8
117.6
16.68
SL-2. LM-3-3 BLOQ
BLOQ
BLOQ
BLOQ
8.5
84.7 16.7%
42807 SL-2. LM-4-1 BLOQ
BLOQ
BLOQ
BLOQ
53.1
530.8
547
SL-2. LM-4-2 BLOQ
BLOQ
BLOQ
11
SL-2. LM-4-3 BLOQ
BLOQ
BLOQ
42808 SL-3; LM-1-1 BLOQ
BLOQ
BLOQ
BLOQ BLOQ
BLOQ
54.1 56.9 BLOQ
540.9 569.4
20.02 3.7%
SL-3; LM-1-2 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
SL-3. LM-1-3 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
\
42809 SL-3. LM-2-1 BLOQ
BLOQ
BLOQ
't
SL-3. LM-2-2 BLOQ
BLOQ
BLOQ
BLOQ BLOQ
BLOQ BLOQ
;;j
SL-3. LM-2-3 BLOQ
BLOQ
BLOQ
42810 SL-3. LM-3-1 BLOQ
BLOQ
BLOQ
,,4
SL-3. LM-3-2 BLOQ
BLOQ
BLOQ
,t
SL-3. LM-3-3 BLOQ
BLOQ
BLOQ
42811 SL-3. LM-4-1 BLOQ
BLOQ
BLOQ
BLOQ BLOQ BLOQ
BLOQ BLOQ
BLOQ BLOQ BLOQ
BLOQ BLOQ
SL-3. LM-4-2 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
SL-3. LM-4-3 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
42812 SL-3. LM-5-1 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
SL-3. LM-5-2 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
SL-3. LM-5-3 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
42813 SL-3. LM-6-1 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
SL-3. LM-6-2 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
SL-3. LM-6-3 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
''
42814 SL-3. LM-7-1 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
SL-3. LM-7-2 BLOQ
BLOQ
BLOQ
I 1
SL-3. LM-7-3 BLOQ
BLOQ
BLOQ
42815 SL-3. SM-1-1 BLOQ
BLOQ
BLOQ
BLOQ BLOQ BLOQ
BLOQ BLOQ
BLOQ
SL-3. SM-1-2 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
SL-3. SM-1-3 BLOQ
BLOQ
BLOQ
BLOQ
BLOQ
Corrected for santole Dien. = Amount (ng/g) * 10
3M Confidential
____________ SL-1, LM_________
PFOa
PFS
Average (ppb) : 64.3
553.4
Stnd. D.: NA
220
1/3/2003
SL-2, LM PFOS
Average (ppb) : 280.8 Stnd. D.:
251 0 0 1 8 0 3
Page 14 o f 21
Report E02-0443
Tenn. River Valley Samples
E02-0443
Combined CatFish Data Table
UMS# 42777 42778 42779 42780 42781 42782 42783 42784 42785 42786 42789 42790 42791 42792 42793 42794 42795 42796 42797
E frH rflfl l M tE U I t a i l
Sem ple Neme
Am ount
n g/g
A m o u n t ng/g A m ount ng/g
SL-1; 0-1-1 SL-1; C-1-2 S L-1.C -1-3 SL-1. C-2-1 SL-1. C-2-2 SL-1. 0 2 -3 SL-1. C-3-1 SL-1. 0 3 -2 SL-1. 0 3 -3 SL-1. 0 4 -1 SL-1. C-4-2 SL-1. C-4-3 S L -1 .0 5 -1 SL-1. 0 5 -2 S L -1 .0 5 -3 SL-1. c-e-1 S L -1 .0 6 -2 SL-1. 0 6 -3
S L -2 ;0 1 -1 SL-2; 0 1 -2 S L -2 .0 1 -3 S L -2 .0 2 -1 SL-2. C-2-2 SL-2. C-2-3 S L -2 .0 3 -1 S L -2 .0 3 -2 SL-2. 0 3 -3 S L -2 .0 4 -1 SL-2. 0 4 -2 SL-2. 0 4 -3 SL-2. 0 5 -1 SL-2. 0 5 -2 S L-2 0 5 -3 SL-2. C-6-1 SL-2. C-6-2 S L -2 C-6-3 S L -2 0 7 -1 S L -2 0 7 -2 S L-2 0 7 -3
SL-3; 0 1 -1
SSLL--33.; 0C1-1--23
S L-3. C-2-1 SL-3. C-2-2 SL-3. 0 2 -3 SL-3. 0 3 -1 SL-3. 0 3 -2 S L -3 .0 3 -3 S L -3 .0 4 -1 SL-3. C-4-2 SL-3. C-4-3 SL-3. 0 5 -1 S L -3 .0 5 -2 SL-3. 0 5 -3 SL-3. C-6-1 SL-3. 0 6 -2 SL-3. C-6-3
8L0Q BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BLOQ
BBLLOOQQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BLOQ
BLOQ
BLOQ BLOQ BLOQ BLOQ
BLOQ BLOQ BLOQ BLOQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BLOQ BLOa
BLOQ BLOQ
BLOQ
BBLLOOQQ
BLOQ
BBLLOOQO
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOO BLOQ BLOQ BLOQ BLOQ
BLOQ BLOQ BLOQ
BLOQ BLOQ ' BLOQ
Am ount n g /g
S.9 5.3 5.2 4.4 4.2 3.9 7.0 7.1 7.4 3.9 3.7 3.8 9.1 9.1 8.8 7.0 6.9 7.0
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
BBLLOOQQ
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
P A (4) '
C orrected fo rS m p l P rep (n g/g )
58.7 53.5 520 44.5 41.7 39.1 70.5 70.8 73.8 39.3 36.7 36.2 91.0 90.7 87.5 69.8 69.1 69.8
A ve, S tnd Dev, end
%CV 54.7 3.49 6.4% 41.6 2.67 6.4% 71.7 1.85 2.6% 38.1 1.30 3.4% 89.8 1.95 2.2% 69.5 0.41 0.6%
Am ount n g /g
11.2 10.5 10.0 9.6 9.2 6.6 16.1 17.9 19.2 17.1 16.2 16.6 8.1 8.0 7.8 5.9 6.0 5.9
BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOO BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ BLOQ
1.9 1.9 1 .4 1.2 1.1 12 BLOQ BLOQ BLOQ 3.7 3.5 4.0 BLOQ BLOQ BLOQ BLOQ 23 2.3
PFOS (499)
C orrected fo r Sm pl Pm p (ng/g)
112.1 104.7 100.3 97.6 91.6 86.1 161.2 179.4 192.4 171.5 181.9 165.8 80.8 80.2 77.5 58.8 59.7 58.7
I
A ve, S tnd Dev, end
%CV 106 6.00 5.7% 91.B 5.77 6.3% 176 15.67 8.8% 166 4.82 2.9% 79.5 1.74 2.2% 59.1 0.57 1.0%
18.6 17.21
ie.o%18.7
1 4 .0
2.75
11.5
11.73
11.5
0.44
1 22 3.7%
36.9 35.1 40.4
37.45 2.72 7.3%
23.5 23.2
23.32 0.19 0.8%
C orrected fo r am ple orno. Am ount (ng/g) * 10
_______________ S L-1.C ____________
________________ FOSA
PFOS
A verJ g * (p pb ) :
60.8
1 13.4
S tnd. 0 .:
18.6
45.6
________ SL-3, C
_______________ PFOS
A ve n g e (ppb) :
223
Stnd. D.: 10.6
00X804
3M giMwnm--UH aban to y
3M Environmental Laboratory
1/3/2003
PQt 1 9 *2 1
Page 55 of 276
ReportE02-0443
Tend. River V atey Samples
!
II* 9 9
99
JM
M
I999
999999
|3* 2 ai
l! <M
i Hi
gso *%*
9 9 9 9 9 9 9 9 9 9 9 9 fiil?1
13 s
w
1! ^
99
99
9
9
9
9
9 9 9 9 9 9 9 9
lu
i<f
llib 9 9 ; 9 9 9 9 9 9 9 9 9 m i
mm
lili l l'iiiilliiif ili|2
Uhi!
11
II
%
.
l .il
l
1112
II!! in imlis si!lm'Iilii*s il
f
ni
t
illlilil I ! |! !!!h
f i f i I ifjl i 11
m ft
iii ii i
i*
535353:31
i 335
3J3 m i B*
i!I i!
i i
3M Environm ental Laboratory
Page S6 o f 276
SOSTOO
4
1021112
Condensed R iver S edim ents Dets Table
001606
Report E02-0443
$5
Tenn. River VaRey Samplee
\i
3M Environmental Laboratory
l
Page 57 o f 276
E02-0443
R iver Sedim ent! M atrix S pite % Ri
Report E02-0443
3M Environmental Laboratory
001S07
Tenn. River VaOey Sam plet
s*9 l
1
Page 58 o t 276
E02-0443
Combinad Rivar Water Cata Tabla
Report E02-0443 3M Environm ental Laboratory
80STO0
Tann. Rtvar V atey Sam ple* Page SB o f 276
Report E02-0443
Tenn. River Valley Samples
E02-0443 Condensed River Water Data Table
LIM S
3B025 38026 38033 38034 38037 38038 38028 38030 38036 38040 38042
38025 38028 38033 36034 36037 38038 38028 38030 38036 38040 38042
38025 3802 38033 38034 38037 38038 38028 38030 38038 38040 38042
38025 38026 38033 38034 38037 38038 38028 38030 38036 38040 38042
38025 38028 38033 38034 38037 38038 38028 38030 38036 38040 38042
Sam ple Name
SW01 SW01-Dup
SW03 SWOS-Oup
SW02 SW02-Dup SWOl-Med FSC01-Med SWD3-Med SW02-Med FSC02-Med
SW01 SW O l-D up
SW03 SWOS-Dup
SW02 SW02-DUP SWOl-Med FSC01-Mad SW03-Med SW02-Med FSC02-Mad
SWQ1 SWOt-Dup
SW03 SW03-DUP
SW02 SW02-0UP SWD1-Med FSC01-Med SW03-Mad S V 2-M ed FSC02-Mad
SW01 SWOl-Oup
SVW03 SWOS-Dup
SW02 SW02-DUP SVW1-Mad FSCOI-Med SWD3-Med SW02-Med FSC02-Med
SW01 SW01-Dup
SW03 SW03-DUP
SW02 SW02-DUP SWOl-Med FSC01-Med SWD3*Med SW02-Med FSC02-Med
In). V oi. (u L )
20 20 20 20 20 20 2 2 2 2 2
20 20 20 20 20 20 2 2 2 2 2
20 20 20 20 20 20 2 2 2 2 2
20 20 20 20 20 20 2 2 2 2 2
20 20 20 20 20 20 2 2 2 2 2
PFBS (299)
E SAr r 0 n * Adjusted fo r > "iV b l.(n g h n L )
3.0 3.7 <LOQ <LOQ <LOQ <LOQ
<LOQ <LOQ <LOQ <LOQ <LOQ
PFHS (399)
1.50 1.85
Adjuetad fo r Semple Prep.
ipg/lm L) 75 93
7.7 8.0 <LOQ 0.3 0.4 0.2 392.6 424.9 404.9 418.9 413.1
PFOA (413)
3.88 3.98
0.13 0.20 0.12 1963 2124 2024 2079 2066
193 199
6.5 9.8 6.2
21.3 22.7 <LOQ <LOQ <LOQ <LOQ 388.4 427.9 398.5 407.0 416.9
FOSA (498)
1Q.66 11.33
1942 2139 19S2 2038 2065
533 566
1.0 1.0 <LOQ <LOQ <LOQ <LOQ
302.1 300.2 324.5 209.2 308.3
PFOS (499)
0.48 0.51
1511 1501 1623 1498 1542
24 28
18.5 20.8 <LOQ <LOQ <LOQ <LOQ
361.8 423.7 365.3 358.0 426.8
9.25 10.40
1809 21' 8 1826 1790 2134
462 520
Average (pg/m L)
84 <LOQ <LOQ
196 6.5 6.0
550 <LOQ <LOQ
25 <LOQ <LOQ
491 <LOQ <LOQ
A dueted to r In i. Vol (no/m U For 20 uL injection * A m o u n t/2 For 2 uL injections A m o u n t's Adlueted fo r Semple Prap (paM lL) (A dietad for Inj. Voi. / 20) * 1000 20 it the factor o f original concentration 1000 Is the conversion from ng to pg.
o o is o s
3M C onfidante
1/3/2003
Psg 20 a l 21
3M Environmental Laboratory
Page 60 of 276
Report E02-0443
Tenn. River Valley Samples
E02-0443
Tenn. River Valley Samples
Sum m ary Table
Catfish, Sample Location 1
Catfish, Sample Location 2
Catfish, Sample Location 3
Large Mouth, Sample Location 1
Large Mouth, Sample Location 2
Large Mouth, Sample Location 3
Small Mouth, Sample Location 1
River Water, Sample Location 1
River Water, Sample Location 2
RiverLWo caatetiro, nS3ample
River Sediments, Sample Location 1 River Sediments, Sample Location 2 River Sediments, Sample Location 3
PFBS (ng/g) <LOQ
<LOQ
<LOQ
<L0Q
<LOQ
<LOQ
<L0Q PFBS
(pg /m L )
84
<LOQ
<LOQ
PFBS (pg/g)
576.9
436.9
452.0
Location Averages
PFHS (ng/g)
PFOA (ng/g)
FOSA
(ng/g)
<L0Q
<LOQ
60.9
<L0Q
<LOQ
<OQ
<L0Q
<LOQ
<LOQ
<L0Q 64.3 <LOQ
<L0Q
<LOQ
<LOQ
<LOQ
<LOQ
<LOQ
<LOQ PFHS
(pg /m L )
196
<LOQ
PFOA
(pg /m L )
550
<LOQ FOSA
(pg/m L)
25
8
<LOQ
<LOQ
7
PFHS (pg/g)
130.5
<LOQ
PFO A (pg /g)
732.4
<LOQ FOSA
(pg/g)
1439.0
<LOQ
<LOQ
141.4
<LOQ
130.5
68.0
The Fish Tissue results are calculated by taking the average of the averages. Please refer to Combined Large Mouth and Catfish Data Tables for averages of samples.
PFOS (ng/g)
113
<LOQ
22.3
553
281
<LOQ
<LOQ PFOS
(pg /m L )
491
<LOQ
<LOQ
PFOS (pg/g)
3132.3
457.3
416.2
3M Confidential 3M Environmental Laboratory
1/3/2003
001810
Page 21 of 21
Page 61 of 276
Report E02-0443
3MPm/irnnmpnlalIahAralnrv
Solvent Curve: 02003-50 SWeBqMuHeVnIcVe*:. Dfc020626Extracted
-Am* /' CurveCne?
DUDE0013 1
OUDE0014 2.5
DUDE001S 5
OUDE0010 10
OUDE0017 25
E E H ilD
50 100
DUDE0020 250
DUDE0021 500
DUDE0022
DUDE0023
1 1 1 1
D020626Extracted
CCV Calculation
41605 89393
162263 313633 739433 1369316 2407273 5416416 6696793
PFBS
_
w
m 1
fT?r?`V.
't1.'jr r -r/'
1.000 . _ 41605:
>0.04
j-
. 1 2.500 : .. . 89393 .. .1.61 m s
1 5.000
162283'
4.65 -6.9 `
-0.T..
0.0 V 0.0'V:
r.. 10.000 : 313833
1
25.000
739433
1 . 50.000
1369316
10.59: 5.9 . 0.0 27.51. '10.0- - .0.0- ;; 53.25 6.5 * 0.0
1
100.000 2487273
101.29' 1.3
0.0 .
i 250.000. 5416416- . 246.66 -1.3 10:0
1 1
500:000 0.000
8896793 0
50132 -1.65
HmHSim|
0.0 ,, 0.0 * t
0.000 .. . 0
1! 0
1.65 H H
0.0
kggRSBai
j 0.00
jTfromxhartiaa
I.62E+01 b-i.i.ii 25774.0409
42668.7254
.: ''neV-!;-.
DUOEO65 DUDE0078 DUDE0061
rMparne.r cone,Jtencuva ^CCVlnifci
2463356 .101.11
100 10196. *
2451622 99.70
100 . 100% -
2445634
99.44 1.65
100 . 99% ,o
1.65
0
1.65
0
-1.65
0
1.65
0
1.65
0
1.65
0
IMConMntl
12/12/2002
flirtCcW dOrti1 DO
n
P a g tlo fd
, Tenn. River Valley Samples
001811
Report E02-0443
D020626Extracted
CCV Calculation
PFHS
-2.216*01 31284.4258 487S4.7S31
od
dd
o d
o d
oo'
Oo oo
o d
Oo dd
od i|hg
so
i7 i
r>. d
s
CM d
y d
13
i*?
sy
foc8R
N
5o
8 s<Ns
8
a
Ij
BN
o> rt
1 2
i01 d b io
1
|
oi
uj
o
8
1 8
1 80 SN 1
id
d
v- o
I
11 ii
3 s Na %0 5
!
I
i
iS o
-
m d
o8s88
f- s|J
n m <0
i-:n
i I' I 1 I 3Ol i iiQ
S '3
3M Environm ental Laboratory
Solvent Curve 02003-50 IDUDE0019I (OUOEOQ23I
001812
Tann. River Valley Samples
I
N
|. 103% |
1 %0l i
g b o b o o o' o ff
l i g8 8
n
vi "I
1
3
i
8 o
2
'S
it'j
II 331
* aas8
s lOI 38
louoEooaij
Pan fi* n f 57fi
Report E02-0443
Tenn. River Valley Sam ple*
n* !
CTSTOrt
IOUDE0055J| 1459295-11- 109.37 I ! 111.66 |
| 1477410 |
P1 O p b o p 6
O
1881 -
H
&
wNN N N 4 7 fji <vi rji Cs
fl
m S
1
mf*8i i
o
3
Report E02-0443
o
n
5..
o d
oo
o
o o
d d
oo' od
t- a
----------
3M Environm ental Laboratory
3a
3 8
40 0 Q IIU
l !',5'n
i
SolventCurve: 02003-50
1OUOE00141 IDUDE0015I IDUDE0017I 10UDE0018I IDUDE0020I IDUDE00211 IDUDE00221
8
- ciMin o 8 8
I; *4
I UVSIZ I
iI
| i F i
I 2665321 | I 6144956 | 1 11083740 |
POOO'OOS 1
D020626Extracted
CCV Calculation
FOSA
s cgfsa I
o
sI
3
1'2.500 :|| I 5.000 | I 10.000 :| i 25.000 I ,50.000.1 \ 100.000 I I250.000 I
ii $i
I
5> tv
s
-71306
I
0.000 | 0.000 I
f OO
m wf i
? 88
$ 1 S'
d R0 4 5).
8*
8
j i'101.39^:1
2
<0 9d
dd
od
odmi3g
so
9701.53073
Tenn. River Valley Samples
f
001814
Report E02-0443
"I'tiLfll".
s
3
-1.10E+01 25197,6029 ;%? 316501.997
Tenn. River Valley Samples
rt
001815
4
1 * 1
S 8 o o o O o <s o
i fc8 8 8
S
CD o3
n r<4
r V) & r4 H
s (n Cr to
oi <4 <4 cJ
1 300424 1
# !1 a g
m o
jj
i S''l
1
Q
Report E02-0443
Attachment C: Sample Chromatograms
Tenn. River Valley Samples
3M Environmental Laboratory
Q01816
Paae fi7 nf ?7fi
Report E02-0443
Tenn. River Valley Samples
Data File: DUDE0056.D Report Date: 27-Aug-2002 13:27
" Page 1
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020626Extracted.b\DUDE0056.D
Lab Smp Id SL-1. LM-1-3
Inj Date 26- JUN-2002 23:16
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info
Comment
Method Meth Date
\27\-EtsAtuagr-g2e0t0\2ta1r3g:e2t2\cdhuedme\jdru.diejr.Qiu\aDn0t20T6y2p6eE:xtErSaTcDted.b\D020626extra
Cal Date 26-JUN-2002 22:00
Cal File: DUDE0049.D
Als bottle 43
Dil Factor 1 .0 0 00 0
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compounds Il PPBS(299)
20PFH3 (399)
21PPO(413) 22POSA(499) 22POS(499)
MAASQUANT SZ8 RT EXPRT OLTRTRESPONSEON(Cn-CgOO/NmLCULEM)NNTRATI(OnPNgINS/mALL) 442223344439191999999939939999999 333433344443............797913049154027570947700S33539919451 333333444334............733779911377999999977199211220044122*----000000000000............013320341000010921430190735711217340 190911135159214594439300532979378475299809254294757194 95599901115905.39345030519371.83973991..70......2775334547..530219399955313949495905 0111.19998855588418233505500.500803744999
Exact C o r/c f Orig - n ii-s\
Initiai Dais
001S17
Report E02-0443
Tenn. River Valley Samples
Data Filat SSEtstar(ttStarttSchaSduda,Jr.iSD02062fiExtractad.bSDUDE0056.D
PC 2
Exact Crpy nf Original
( i ll( /.-3//n//'>--
Initial Dato
o l lv i
Report E02-0443
Tenn. River Valley Samples
Oata F ila i SSEt i t i r fatSlircatSchmSdudajr. 1\D02026Exfcrctd. bSDUDE0056,D
21 PFOft <413)
Pt 3
23 PFOS <499)
Eact Copy o Origino!
f - i :-r
initial
Data
0 0 1 8 4 .9
Report E02-0443
Tenn. River Valley Samples
Data Pile: DUDE0058.D Report Date: 27-Aug-2002 13:27
" Page 1
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chera\dudejr.i\D020626Extracted.b\DUDE0058.D
Lab Snip Id Inj Date
SL-1. LM-2-2 26- JUN-2002 23:38
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
II
Misc Info Comment
Method Meth Date Cal Date
\2\7E-tstAaurgg-e2t0\0t2arg1e3t:2\2chedmu\ddeujdre.jir.i\QDu0a2n0t62T6yEpex:traEcStTeDd.b\D020626extra
26-JUN-2002 22:00
Cal File: DUDE0049.D
Als bottle 45
Dil Factor 1 .0 0 00 0
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
4
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Coapoundo 1 PFBJ law)
30 PPHa (3)
21 PPOA (413)
32
22
PpOroSAs
(454) (499)
QUHANATSS810 22223434499991919999339*9 449P9*
ST BXP RT DLT RT RESPONSI ON(Cn-COgO/NLCULEM)NNTRATI(OnPNgIN/SmALL)
333333443.........387173825024948024C37028895 333333343.........333379977888899499111120202 ----000000000.........11020302029714403033115770 44..157045 44..117744 00..040341
331011441S22132745424045419124397228558563C7372084348
555085815553.5.0940333739659......<3555855.2947889456454814879 1C(l1.400.03(
01.6558855.951355055660844934 1<618.40
Exact Copy of Orignal
d rU I
i initial Data
I
P nw irnnm pnfal I ahrtratnrv
* U 01 20
D e n a *74 T 7C
Report E02-0443
Tenn. River Valley Samples
Data Fil: SSEtsUrc*tSUrtt\eb\dud*jr. i\D020626Extrcti.bSDUBEOOSB.D
Pt 2
1
20 PFH8 <399)
I
-
Cm /rnnm A ntal I horatorv
Exact Copy r.' Origin,i!
-C W Initiai
oate
001821
Pan 79 of 276
Report E02-0443
Tenn. River Valley Samples
Bat F it: SSEtstai*e*t\targatSchM>Sdudjr.iSB0226Extract*d.bM>UDE00S8.D 21 PFOA <413)
22 FOSA <498)
23 PFOS <499)
Exact Copy of Origina! 1 3 / h i/ X.
Initta) Date
001822
Report E02-0443
Tenn. River Valley Samples
Data File: DUDE0063.D Report Date: 27-Aug-2002 13:27
Page 1
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020626Extracted.b\DUDE0063.D
Lab Smp Id SL-1. LM-3-2
Inj Date 27-JUN-2002 00:33
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Misc Info
Comment
Method Meth Date
\27\-EAtusgt-a2r0g0e2t\1t3a:r2g2etd\ucdheejmr\.diudejrQ.uia\ntD02T0yp6e2:SExEtSrTDacted.b\D020626extra
Cal Date 26-JUN-2002 22:00
Cal File: DUDE0049.D
Als bottle 49
Dil Factor 1 .0 0 00 0
Integrator Falcon
Compound Sublist: all.stob
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Congpound Variable
Compound*
IBPPM{39)
30PPHS(399)
31PPQA<413) 33POSA(491) 23proa <499)
QIAMTSXG MASS
RT EXPRT DITRTRESPONSEON(nC-CgOO/NmLCULEM)NNTRAT(IOnPNgINS/mALL)
229999 2233999999 444441991933999
3333334333444.............3B7717945159BC97137470951BB4355453732 3333333334444.............3373397711977BB9389997759(2222411043101-00000000000O0.............122303410004o304404383000o757902141767o 39262113465123145(337354509434717734673773553368095602870 48555588118300550359605.79.3397138937..87....0..2.5637476317..43730419467S1371C079875169 4811968805555888.928305355510.8800837944409
Exact Copy of Origina!
J j y i . L-xJ/lQ T-
Initial Date
01 23
Report E02-0443
Tenn. River Valley Samples
Data F il#: S\EttarsttStarstt\chtaSfcJdtjr.:M020i26Extractl.b\Din)E0063.J
Pagt 2
Exact Copy t;.f Original 001824
Report E02-0443
Tenn. River Valley Samples
Data Fila; SSEt*trjtStaretSch*i.Sdudajr.i\T0202Extraetad.bSDUDE0063.D 21 PFOA (413)
paCa 3
OECt Copy of Origin's!
Initial
001825
Report E02-0443
Tenn. River Valley Samples
Data File: DUDE0068.D Report Date: 27-Aug-2002 13:27
Page 1
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020626Extracted.b\DUDE0068.D
Lab Smp Id: SL-1. LM-4-2
Inj Date : 27-JUN-2002 01:28
Operator : mla
Inst ID: dudejr.i
Smp Info : Tenn. River valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info :
Comment :
Method Meth Date
: :
\27\-EAtusgt-a2r0g0e2t\1t3a:r2g2etd\ucdheejmr\.diudejQru.ain\tD0T2y0p6e2:6EExStTrDacted.b\D020626extra
Cal Date : 26-JUN-2002 22:00
Cal File: DUDE0049.D
Al s bottle: 52
Dil Factor: 1 .0 0 0 0 0
Integrator: Falcon
Compound Sublist:all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compounds 1PFBSUt)
20P7HSUt)
222121PPtvOPoOSaAA(((4449193l)))
QUNAANSTSSIO RT BXPRT DLTRTRBSPOKSBON<O-nCOgO/NmLCULSM>NNTRATX(OnFHIgNS/AaLli) 223334444241999999999939999999999 33333334434..........7.353177914(C5O5929997*7433299974S33443333344...........397137731179999997977(22101224144----00000000000...........241300003403390000430039975702107 34114951543971521115019535054(6352575071114745092959 50507105991...55500.455459939993.132340...0.776555379..3924952371(56459459195 0006711...569659965.51433511995.93737400040
Exact Copy c i Origina!
biitial Oats
001826
Report E02-0443
Tenn. River Valley Samples
Stata Fil*: VsEtstargetStar-f*tSch*nSdud*jr.i\D020624Extr*ct*d,bSDUBE4468,9
pe* 2
18 PFS8 <299) Pnuirnnmantal I aKrtPotnni
Efct Ccpj n'
Z a h l ., i v / t c l t r .L-
JnitlaJ
osta
001827
Report E02-0443
Tenn. River Valley Samples
Data File: SSEtstartetStartetSchenSdudejr,i\D02062{Extraete<l.bSSUDE0068.D 21 PFOA <413)
Pit 3
22 FOSA <498)
23 PFOS < 4 >
iIaI ikrtenli
Exact Copy of Origina! 1-2-J/n /ni
Oats
001828
n ...
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020628.b\DUDE0058.D Page 1 Report Date: 09-Dec-2002 13:07
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020S28.b\DUDE0058.D
Lab Smp Id: SL-2. LM-2-1
Inj Date : 29-JUN-2002 02:15
Operator : mla
Inst ID: dudej r .i
Smp Info : Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info :
Comment :
Method : \\Etstarget\target\chem\dudejr.i\D020628.b\D020628.m
Meth Date : 09-Dec-2002 13:01dudejr.i Quant Type: ESTD
Cal Date : 29-JN-2002 00:48
Cal File: DDDE0050.D
Als bottle: 28
Dii Factor: 1 .0 0 0 0 0
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Conpounds It FFB5 (299)
20 PFHS (399) 21 PFOA (413)
pros22 POSA (499)
23 (499)
QUANT Sir, MASS
299 299 299 399 399 413 490 499 499
COHCENTRAT-CNS
ON-COLUMN PINAL
RT BXP RT DLT RT RBSPOKSS
(ng/raL)
tng/mL)
3.390 3.103 3.757 3.005 3.545 4.004 4.776 4.101 4.605
3.308 3.300 3.380 3.798 3.790 3.997 4.769 4.174 4.174
0.000 -0.205
0.369 0.007 -0.2S3 0.007 0.007 0.007 0.431
15144 2946 2208 10047 540
25432 65904
1348329 20726
569.524 569.996 570.025 786.229 786.477 815.277 1805.85
2.56372 1659.69
570 570 570 786 786 8 1 5 (M) 1880
2.56 1660
QC Flag Legend M - Compound response manually integrated.
Exact C o p y of Original
001829
Report E02-0443 D ata F ila : \\E ts ta rs a t\ta rc a tS c h a n S d u d a jr,i\D -)Z 0 6 2 8 .b S D U D E 0 9 S 8 .D
Tenn. River Valley Samples Paca Z
Exact Copy of Origina! x a a l_ j.3. f / t r t.
Initia] Date
0011,30
Report E02-0443
Data FU: SSEt*t*re*tStarttSch*Sdud*Jr. tSD020628. b\DUBE00S8. D
21 PFOft (413)
Tenn. River Valley Samples Pat 3
22 FOSA (498) 23 PFOS (499)
Exact Copy of O r#;;
teiaJ Osts
001831
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020628.b\DUDE0064.D Page 1 Report Date: 09-Dec-2002 13:07
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020628.b\DUDE0064.D
Lab Smp Id: SL-2. LM-3-2
Inj Date : 29-JUN-2002 03:21
Operator : mla
Inst ID: dudejr.i
Smp Info : Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Misc Info :
Comment
Method : \\Etstarget\target\chem\dudejr.i\D020628.b\D020628.m
Meth Date : 09-Dec-2002 13:01 dudejr.i Quant Type: ESTD
Cal Date : 29-JUN-2002 00:4B
Cal File: DUDE0050.D
Als bottle: 33
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compound
IB PPBS (a s s )
20 PFHS (399) 21 PPOA (413) 23 POSA (498) 23 PFOS (499)
Quurr sic MASS
299 299 299 399 413 499 499 499
CONCENTRATIONS
OH-COLKN FINAL.
RT EXP RT DLT RT RESPONSE
Ing/oiL)
(ng/mL)
3.401 3.210 3.771 3.818 4.017 4.789 4.194 4.825
3.388 3.388 3.388 3.798 3.997 4.769 4.174 4.174
0.013 -0.178
0.383 0.020 0.020 0.020 0.020 0.451
22037 3476 3793
17063 38939 98985 1627015
1774
569.257 569.976 569.964 0.08850 814.559 0.72476 11.7650 1660.28
569 570 570 0.0885(H) 814 (M) 0.725 11.8 1660
QC Flag Legend M - Compound response manually integrated.
initial
>03Cat
I0 1 L 3 Z
Report E02-0443 D a t F ila s V t * t * r g t \ t a r { t \ e h * \ d u d Jr . i\L ')2 0 6 2 8 .bMHIDEOOW. D
Tenn. River Valley Samples P * l* 2
P m /ir^ n m a n tflil I ahrtref
f ci Copyof Original
initial Dqq
C 1633
Report E02-0443
Data Filai SSEttarial\tartt'*cha\dudajr,iM20628,bSDUDE0064.B
21 PFOfl <413)
Tenn. River Valley Samples
Paca 3
22 FOSA <498)
Exact Copy of Orloina;
initiai Date
C u io 3 4
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020628.b\DUDE0070.D Page 1 Report Date: 09-Dec-2002 13:07
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020628 .b\DTJDE0070 .D
Lab Smp Id: SL-2. LM-4-3
Inj Date : 29-JUN-2002 04:26
Operator : mla
Inst ID: dudejr.i
Smp Info : Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info :
Comment :
Method : \\Etstarget\target\chem\dudejr .i\D020628.b\D020628.m
Meth Date : 09-Dec-2002 13:01 dudejr.i Quant Type: ESTD
Cal Date : 29-JUN-2002 00:48
Cal File: DUDE0050.D
Als bottle: 37
Dil Factor: 1 .0 0 0 0 0
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compounds
IS PFBS (299)
20 PFHS (399) 21 PPOA (413) 22 POSA (498) 22 P?OS (499)
QUANT SIG MASS
299 299 299 399 413 491 499 499 499
CONCENTRATIONS
OK>COLUMN PINAL
RT EXP RT DLT RT RESPONSE
(ng/mL)
ng/mL)
3.388 3.183 3.757 3.805 4.003 4.774 4.174 3.805 4.605
3.388 3.388 3.388 3.798 3.997 4.769 4.174 4.174 4.174
0.000 -0.205
0.369 0.007 0.006 0.007 0.000 -0.369 0.431
13695 1232 1592
10665 23745 120542 2949014
2773 32944*
569.580 570.062 570.049 786.213 115.366 1.45583 56.9432 1660.25 1659.31
570 570 570 7 8 6 (M) *15 <M) 1.46 56.9 1660 1660
QC Flag Legend M - Compound response manually integrated.
Staci Copy of Originai
A* C iniiia)
Date
aoxss
Report E 02-0443
Data F ile t \\E t t ta r je t \ tarjetSchenSdudj r . iSD020628. bM)UIIE007').D
Tenn. River Valley Samples
Pate 2
18 PFBS <299)
Exact Copy of Origina
X2L_ <3Ji.qI q initiai Oats
001836
Report E02-0443
Data F ila ; NSEtstarttStarfetSeh*iSdu<l*jr.lSIW20628,bSllUlJE0070.D 21 PFOA (413)
Tenn. River Valley Samples P*S* 3
22 POSA (4 9 6 )
23 PFOS (499)
Exact Copy 'T !i> -C Y L .
Initiai Onte
001837
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudej r .i\D02062B.b\DUDE0076.D Page 1 Report Date: 09-Dec-2002 13:08
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\DO2O620 .b\DUDE0076 .D
Lab Smp Id SL-3. LM-1-3
Inj Date 29-JN-2002 05:32
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020628.b\D020628 .m
Meth Date 09-Dec-2002 13:01 dudejr.i Quant Type: ESTD
Cal Date 29-JUN-2002 00:48
Cal File: DUDE0050.D
Als bottle 42
Dil Factor 1 .0 0 00 0
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
pound 18 pros (299)
20 FFHS (399) 21 PFOA (413) 22 POSA (9) 23 PFOS (499)
QUANT Sia NASS
299 299 299 399 399 413 498 499 499
CONCENTRATIONS
OM-COLUMN RT EXP RT DLT RT RESPONSE (ng/L)
FINAL (ng/mL)
3.388 3.189 3.764 3.805 3.559 3.996 4.899 4.174 4.611
3.388 3.388 3.388 3.798 3.798 3.997 4.769 4.174 4.174
0.000 -0.199
0.376 0.007 -0.239 -0.001 0.130
0.000 0.437
17998 3724 1636
16875 3229
60835 78316 716542 12921
569.414 569.966 570.039 0.08359 786.407 0.95299 0.02433 1637.71 1659.94
569 570 570 0.0836 786 0.953(H) 0.0243(H) 1640 1660
QC Flag Legend M - Compound response manually integrated.
Exact Copy of Origina1 Data
001838
Report E02-0443
le t* F ile* SSEt*t*Pe*tSt*rtt\ch*i%\dud*jr.lS228.bSBUDE007i.D
Tenn. River Valley Samples Pa* 2
ExactCopyo: Originai
initial
Ls/ib Jj j . Cou-
01U 39
Report E02-0443
D a ti F l i t : SSEtstarctStar(*tSehn\dud*Jr. 1SD020628.bSDUDE0076D
21 PFOA (413>
Tenn. River Valley Samples Pag 3
22 FOSA (498>
ExactCopvr ' Onrn
nL_ t /to
initial ote
001840
Report E02-0443
Tenn. River Valley Samples
Data File: \\ Et st ar get\targe~\chem\dudej r .i \ D 0 20 62 8.b \ D D E 0 0 8 9 .D Page 1 Report Date: 09-Dec-2002 13:08
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020628.b\DUDE0089.D
Lab Smp Id SL-3. LM-4-3
Inj Date 29-JUN-2002 07:55
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020628.b\D020628.m
Meth Date 09-Dec-200213:01 dudejr.i Quant Type: ESTD
Cal Date 29-JUN-2002 00:48
Cal File: DUDE0050.D
Als bottle 52
Dil Factor 1 .0 0 0 0 0
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compounds
18 PFBS (as9)
20 PFHS (3991
21 PPOA (4X3) 22 FOSA (498) 23 PFOS (4991
QUANT Sin HASS
299 299 299 399 399 413 498 499 499
CONCENTRATIONS
ON-COLUMN FINAL
FT EXP FT DLT RT RESPONSE
ing/mL)
ing/mL)
3.395 3.190 3.757 3.805 3.552 4.003 4.769 4.174 4.605
3.368 3.388 3.388 3.798 3.798 3.997 4.769 4.174 4.174
0.007 '0.198
0.369 0.007 -0.246 0.006 0.000 0.000 0.431
12936 3732 1991 7393 2451
24746 64726 1029061 18761
569.610 569.966 570.033 786.298 786.427 115.313 . 1885.89 1627.64 1659.75
570 570 570 786 786 8L5 (M) 1880 1630 1660
QC F la g L e g e n d
M - Compound response manually integrated.
Exact Copy of Ordina?
U U lo /o x -
rnitiai
Oat
001S41
Report E02-0443
Tenn. River Valley Samples
18 PFBS <299> 20 PFHS (399>
Exact Copy of Origina! 001^42
Report E02-0443
Dt Filet S\Et*t*rttSUrt*tSehS*KlJr.iM20628.bM)UDE0089.D 21 PFOA (4 13)
Tenn. River Valley Samples pn 3
2 3 PFOS <499>
Copy of Original '-n,lia{ Date
O I8 4 3
Report E02-0443
Tenn. River Valley Samples
Data File: \ \ E t st ar ge t\ tar ge t\ ch em \d ude jr.i\D020628.b\DDE0102.D Page 1 Report Date: 09-Dec-202 13:08
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020628,b\DUDE0102.D
Lab Smp Id: SL-3. LM-7-2
Inj Date : 29-JUN-2002 10:18
Operator : mla
Inst ID: dudejr.i
Smp Info : Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info :
Comment :
Method : \\Etstarget\target\chem\dudejr.i\D020628.b\D020628.m
Meth Date : 09-Dec-2002 13:01 dudejr.i Quant Type: ESTD
Cal Date : 29-JUN-2002 00:48
Cal File: DUDE0050.D
Als bottle: 62
Dil Factor: 1 .0 0 0 0 0
Integrator : Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compounds 18 P7BS 1299)
20 PPHS (399) 21 PFOA (413) 22 POSA (499) 23 PPOS (499)
q o a k t sia NASS
299 299 299 399 413 498 498 499 499
CONCENTRATIONS
QM-corow PINAL
RT EXP RT DLT RT RESPONSE
(ng/mM
[ng/aL)
3.388 3.176 3.757 3.799 3.997 4.769 4.441 4.175 4.598
3.388 3.3BB 3.388 3.798 3.997 4.769 4.769 4.174 4.174
0.000 -0.212
0.369 0.001 0.000 0.000 -0.328 0.001 0.424
24706 1376 1023 9487
62864 23637
779 906705
29289
569.154 570.057 570.071
786.244 1.06124 1887.28 1888.05 1631.60 1659.43
569 570 570 786 <H) 1.06 18 90 1890 1630 1660
QC Flag Legend M - Compound response manually integrated.
SraciCopyc.` Oricirur-
Me
001S44
Report E02-0443 Data Fila: S\Etstai^atStargatScheiXdudaJr.i\I20i2a.b\Din)E0102.D
Tenn. River Valley Samples Paga 2
Exact Copy of Original CJn ( / p / z o / Cr*.
Initial Data
001845
Report E02-0443
Sat* F ilt VsEtit*rt*tSt*rs*tSehMiSdud*Jr.lMK20628.bM)USE0102,D
21 PFQft <413)
Tenn. River Valley Samples
22 FOSA <498)
23 PFOS <499)
3M Environmental Laboratory
Exact Copy of Origin'-.:
C iv it a d l l< n -
initial
O aio
001846
Page 97 of 276
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\tar ge t\ ch em \d ude jr.i\D020628.b\DUDE0104.D Page 1 Report Date: 09-Dec-2002 13:08
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020628.b\DUDE0104.D
Lab Inj
Smp Id: Date :
SL-3. SM-1-1 29-JUN-2002 10:40
Operator : mla
Inst ID: dudejr.i
Smp Info : Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info :
Comment :
Method : \\Etstarget\target\chem\dudejr.i\D020628.b\D020628.m
Meth Date : 09-Dec-2002 13:01 dudejr.i Quant Type: ESTD
Cal Date : 29-JUN-2002 00:48
Cal File: DUDE0050.D
Als bottle: 6 5
Dil Factor: 1 .0 0 0 0 0
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compounds 18 PPBS (299)
20 PFHS (399)
21 PFOA (4X3) 22 F0SA (498) 23 FPOS (499)
QUANT SIG MASS
299 299 299 399 399 399 13 498 499 499
CONCENTRATIONS
ON-COLUMN RT EXP RT DUT RT RESPONSE (ng/mL)
FINAL tng/mL)
3.368 3.190 3.757 3.812 3.566 4.174 3.996 4.769 4.174 4 .60S
3.388 3.388 3.388 3.798 3.798 3.798 3.997
4.769 :i74 4.194
0.000 -*0.198
0.369 0.014 -0.232 0.376 -0.001
0.000 0.000 0.411
10955 2138 1256
11252 5688
975 55673
41082 429027
15*11
569.686 510.027 570.062 786.197 786.343 786.466 0.67774
1886.69 1646.86 1659.05
570 570 570
786 786 786 0.678(H)
1890(H) 1650 1660
QC Flag Legend M - Compound response manually integrated.
Exact Copy c f Original
Initlal
Data
P ew rcN nm A nlal I
01 47
n...An.fM*f/
Report E02-0443 Data Fila: S\Et*tarsatStargatScha\dudajp.iSD020628.b\DUDE0104.D
Tenn. River Valley Samples
Paje 2
18 PFBS (299>
Exact Copy o f Origina
L!rs*iiia(! r i /O^a/tea
0Qlt48
Report E02-0443
D ata F i 1*5 S S E tsta r^vtS tarca tS chm S du daJr, iSD,>20428.bSDUDE0104.D 21 PFOA <413)
Tenn. River Valley Samples
23 PFOS <499)
E 'c sc i C op y o f Original
.Chn? .. *J1joJj p _.
initiai
Ogin
001849
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020628.b\DUDE0105.D Page 1 Report Date: 09-Dec-2002 13:08
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file : \\Etstarget\targst\chem\dudejr.i\D020628.b\DUDE0105.D
Lab Smp Id: SL-3. SM-1-2
Inj Date : 29-JUN-2002 10:51
Operator mla
Inst ID: dudejr.i
Smp Info : Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info :
Comment
Method : \\Etstarget\target\chem\dudejr.i\D020628.b\D020628.m
Meth Date : 09-Dec-2002 13:01 dudejr.i Quant Type: ESTD
Cal Date 29-JUN-2002 00:48
Cal File: DUDE0050.D
Als bottle: 66
Dil Factor: 1 .0 0 00 0
Integrator : Falcon
Compound Sublist:all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compounds
U18 PFBS 99)
20 PFHS (399)
21 PFOA (413) 22 POSA (498) 23 pros (499)
QUANT Sia HASS --
299 299 299 399 399 399 413
498 499 49
RT
- 3.388 3.182 3.764 3.82S 3.S52 4.194 3.996
4.769 4.174 4.408
BXP RT
3.388 3.388 3.388 3.798 3.798 3.798 3.997 4.769 4.174 4 .1 7 4
DLT RT
0.000 >0.206
0.376 0.027 -0.246 0.396 -0 .0 0 1 0.000 0 .0 0 0 O.4 3 1
RESPONSB
11225 1896 1US
12780 6122 930
52802 40143 469574 1424
CONCENTRATIONS
ON-COLUMN PINAL
(ng/mb)
<ng/iaL)
569.676 570.037
570.067 786.158 786.331 786.467 0.52474
1886.72 164S.S8 1649.8
570 570
570 786 786 786 0.525(H)
1890(H) 1640 1660
QC Flag Legend M - Compound response manually integrated.
Exact Copy origin al
C U iL - U L i P -
inSial
Data
i>18S0
Report E02-0443
Data Fi la: s\Et*tar|tStrs*t\eh*iVdud*jr.iMW20628.bSDUlJeoiO5.D
Tenn. River Valley Samples
Pit* 2
18 PFBS <299)
xt Cupv of Original
ritla l
Data
001851
Report E02-0443
Hat F ila : SSEtstars*tStar(*tSe>wSdud*Jp.lSDSe28.bS0UDE010S.I) 21 PFOA <413)
Tenn. River Valley Samples P ,. 3
2 3 PFOS <499>
Exact Copy of Origins}
U ia l-- initial
Date
001852
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr .i\D020628.b\DUDE0108.D Page 1 Report Date: 09-Dec-2002 13:08
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020628.b\DUDE0108.D
Lab Smp Id SL-3. SM-1-3
Inj Date 29-JUN-2002 11:25
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Misc Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020S28,b\D020628.m
Meth Date 09-Dec-2002 13:01 dudejr.i Quant Type: ESTD
Cal Date 29-JUN-2002 00:48
Cal File: DUDE0050.D
Als bottle 67
Dil Factor 1 .0 0 00 0
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compounds
1 FFBS <399)
30 PFHS (399) 21 PFOA (413) 22 FOSA (498) 23 PFOS (499)
QUANT SIG MASS
299 299 299 399 413 499 499 499
CONCENTRATIONS
ON-COLUMN FINAL
AT EXP AT DLT RT RESPONSE
(ng/raL)
ng/mL)
3.368 3.183 3.764 3.798 3.996 4.762 4.174 4 .598
3.389 3.388 3.388 3.798 3.997 4.769 4.174 4.174
0.000 -0.205
0.376 0.000 -0.001 -0.007 0.000 0.424
16091 2727 1588
13195 S4265 44388 458983 15684
569.488 570.005 570.049 786.147 0.60270 1886.57 1645.91 1659.85
569 570 570 786 <M) 0.603 (M) 1890 (Ml 1640 1660
QC Flag Legend M - Compound response manually integrated.
Exact Copy of Origina!
L iti/ ._ 2 //o /o ^
Initial Date
IL4 M Cl mi
01ZS3
Report E02-0443
Bt F ile: SSEtstrtetSUrt*tScheeSdudejp.lSl20t28.bSBUXC0108.D
Tenn. River Valley Samples
Pat* 2
E x sc l C opy of Odoifui
L 2//o /c.
initiai
o ift"
001854
Report E02-0443
Dt* Filet SSEt*tr*tStrttSch*>S<ludejr.lM20628.bM)UllE0108.D
21 PFOft <413)
Tenn. River Valley Samples P ift 3
23 PFOS <499)
Exact Copy or Original f - i +j( n h o f x
initia] Dato
^ O lS S S
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D0206~29 ,b\DUDE089 .D Page l Report Date: 27-Aug-2Q02 10:06
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0089.D
Lab Smp Id SL-1. WB-1
Inj Date 01-JUL-2002 04:25
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info
Comment
Method
\\Etstarget\target\chem\dudejr .i\D020629,b\D020629 .m
Meth Date 27-Aug-2002 09:59 dudejr.i Quant Type: ESTD
Cal Date 30-JUN-2002 22 :4o
Cal File: DUDE0058.D
Als bottle 47
Dil Factor 1 .0 0 0 0 0
Integrator Falcon
Confound Sublist:all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
.-i
1
Compound
is PPBS (2 9 1 ) 1 20 PPKS <299)
21 PPOA (4 1 2 ) i 22 POSA (9)
23 ppoa (499) ,,,,*i
QUANT SIG MASS
209 299 299 399 413 490 499 499
CONCENTRATIONS
ON-COLUMN PINAL
RT KXP RT DLT RT RESPONSE (ng/nL)
(ng/L)
3.313 2.944 3.1 3.790 4.004 4.770 4.100 4.005
3.3B1 3.301 3.301 3.792 3.990 4.750 4.1(0 4.100
-0.000 -0.437 -0.210
0.000 0.014 0.020 0.020 0.437
23S77 470
2901 0170 10932 7049 90922 22025
1223.22 1224.54 1224.39 0.10435 019.144 2744.00 1274.91 1277.09
1220 1220 1220 0.104
19 2740 1270 1200
Exact Co# oJ'ting
fmOiia!L . o*t>:\fo?--
001856
Report E02-0443
Data F ila: S\EtstarcatSUr(atSchan\dudajr.iSD020629.bSDUK0089.D
Tenn. River Valley Samples P aja 2
3.9-; 3.6^ 3*3^ 3. 0: 2.?-:
Ion 299.00
frvprS.
v 1.*8--:
" 1.8-, 1
n2 k
^0. 9:
7
1
./LIJ\ *-
V^. _
--
3.00 3.20 3.40 3.60 3 .BO
________________ Hin_________________
20 PFHS (399)
tact Ccpy j ; 'j.lcii:.' tZ /Jc/a i-
feiitial Oa&
001S57
Report E02-0443
BU F ile t SStitri*tStrc*tSchSdudJr. I\D020629.b\DUDE0089.D 21 PFQA <413>
Tenn. River Valley Samples
22 FOSA <496>
Beaci Copy or Origina!
C'l'iijt2ia.lL . li JD/aoto/qi--
U01bS8
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0127.D Page l Report Date: 27-Aug-2002 10:07
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0l27 .D
Leib Smp Id SL-2. WB-1
Inj Date 01-JUL-2002 11:23
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 03
Mise Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020629.b\D020629.m
Meth Date 27-Aug-2002 09:59 dudejr.i Quant Type: ESTD
Cal Date 30-JUN-2002 22:46
Cal File: DUDE0058.D
Als bottle 76
Dil Factor 1 .0 0 0 0 0
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compound* 1 PFBS(a> ao PPH(3*1) PPOAa i (413) POSAaa (4 **) PPOS(4*1)aa
QUMANASTSSIO RT SXPRT DLTRTRUFONSBON(nC-COgOM/tLCtULRMN)TNRATX(OnPNIgNa/A*LL)
399
3.319 3.391 -0 .0 4 3
31973
1 3 3 3 .3 2
1220
399
3.17 3.391 -0 .3 0 5
3794
1 2 2 4 .3 5
1330
399
3.791 3.79a -0 .0 0 1
3414
0.03479
0 .0 3 4 9
399
3.913 3.793 0.190
1931
7 9 7 .1 4 9
797
413
3.99 3 .9 9 0 0.004
13991
9 1 9 .0 3 5
919
49S
4.774 4 .7 5 4 o.oao
3433
2 7 4 4 .1 9
2740
499
4.119 4 .1 4 9 0.030
94974
1 2 7 5 .3 0
1290
499
4.599 4 .1 4 9 0.430
12403
1 3 7 7 .4 0
1240
Cjn rci Cop]. '<' Original t p / f / .z--
iii a j
Oafs
001.8S9
Report E02-0443 Data F lla : \\E t*ta rta t\ta r* tS c h a *S d u d jr.iS D 0 2 0 6 2 9 .b \D llD E 0 1 2 7 .D
Tenn. River Valley Samples
Pata 2
20 PFHS (3 99)
:T,Vi ' 2 / / 'j /o?
qo l $60
Report E02-0443
Data F llat SSEtstarcat\tarc*tSchanSdudaJr.l\D0206294bM)UDE0127.D 21 PFOA <413)
Tenn. River Valley Samples
22 FOSA <498) 23 PFOS <499)
"V jt ^ -v, 1Oi'.'giii:
S-klOC. -il/to/i-
ilaJ
D f
001861
Report E02-0443
Tenn. River Valley Samples
Data File: DUDE0089.D Report Date: 27-Aug-2002 11:06
Page 1
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file Lab Smp Id
\S\LE-t3s. taWrBg-e1t\target\chem\dudejr.i\D020702 (D20702).b\DUDE0089.D
Inj Date 03-JUL-2002 07:02
Operator mla
Inst ID: dudejr.i
Sng? Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020702(D20702),b\D020702.m
Meth Date 27-Aug-2002 11:01 dudejr.i Quant Type: ESTD
Cal Date 03-JUL-2002 01:21
Cal File: DUDE0058.D
Als bottle 72
Dil Factor 1 .0 0 00 0
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Confound Variable
Compound
ia PPBS (3>
30 W H S (3) 21 PPOA (13 aa FOSA (43*) 23 PPO* (433)
QUANT SIS MASS
290 299 299 399 399 413 49* 499 499
C0HCBMTIUXI3NS
ON-COLONS FINAL
RT BXP RT DLT RT RBSP0MS8
(ng/nL)
(rjg/mL)
3.324 3.113 3.777 3.025 3.545 4.010
4.003 4.194 4.591
3.307 3.307
3.307 3.791 3.791 3.909
4.740 4.147 4.147
-0.041 -0.204
0.390 0.034 -0.244 0.021
0.055 0.027 0.414
25327 3225 490 7077 937
14443
5535 02445 22937
1219.50 1220.47 1220.50 0.25045 0.12420 795.103
2054.35 1323.02 1324.24
1230 1220
1220 0.25ft 0.124
7.8(11)
2150(H) 1320 1220
QC Flag Legend M - Compound response manually integrated.
Exact Copy of Grig:r..v
P in t Enttiai
Dato
001862
Report E02-0443
Tenn. River Valley Samples
ta t* F ilas SSEt*tart*tStarc*tSohSdud*jr. 1SD020702<S20702>.bSIHJDE0089.D
PC 2
20 PFHS (399>
Exact Copy of Criginal
Initiai ;3te
001S63
Report E02-0443
Tenn. River Valley Samples
Data F ila: SSEtatvt*tStars*tSeh*nSdud*Jr.iMK>20702(020702>.bSDU])EO89.D 21 PFOA <413>
22 FOSA <490) 23 PFOS <499)
cicict Cupy of Origmai % < - . L 2 /o x -
001864
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0064.D Page 1 Report Date: 27-Aug-2002 10:05
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0064.D
Lab Smp Id: SL-1. C-l-3
Inj Date : 30-JUN-2002 23:51
Operator mla
Inst ID: dudejr.i
Smp Info : Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info :
Comment :
Method : \\Etstarget\target\chem\dudejr.i\D020629.b\D020629.m
Meth Date : 27-Aug-200209:59 dudejr.i Quant Type: ESTD
Cal Date : 30-JUN-2002 22:45
Cal File: DUDE0058.D
Als bottle: 28
Dii Factor: 1 .0 0 0 0 0
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
C o n c e n t r a t io n F o rm u la : A m t * D F * C p n d V a r ia b le
Cpnd Variable
Local Compound Variable
Conpoundo
IB PFBS (299)
20 PFH8 (299) 21 PPOA (413) 22 POSA (491) 23 ppoa (499)
QUANT a m HASS
299 299 299 399 413 49B 499 499 499
CONCENTRAT] ONS
ON-COLUMN PINAL
RT KXP RT DLT RT R85POK5R
(ng/mL)
(ng/oL)
3.3BB 3.17 3.7S1 3.79B 3.997 4.754
4.175 4.434 4.409
3.311 3.3B1 3.3B1 3.792 3.990 4.75C
4.145 4.1*4 4.149
0.007 -0.305
0.370 0.004 0.007 0.000
0.007 0.2CC 0.437
12710 3939 2S5S 71B2 23937
140C25 4&0BC4
4774 19939
1333.84 1224.34 1224.42 0.13435 0.3B2S9 5.2038B
10.0242 1277.40 1177.17
1220 1220 1220 0.134(H) 0.343 (N) 5.30 (N)
10.0 12 BQ 1190
QC Flag Legend M - Compound response manually integrated.
Eact Copy or Odern;: & L C . IZ U & lo i-
feirsaj
00186S
Report E02-0443
Data F ilas NSEt*UrjatStartatSchaSludajr.iSD02<S2S.bSDUDE006*.D
Tenn. River Valley Samples
Paca 2
20 PFHS (3 9 9 )
Bacttte#
-?WC
if?iaj
L l/lo fb X -- 'MV:.
01866
Report E02-0443
Data Filai SSEt*targat\tarf*tSch*Sdu6jr.i\D020629 .b\BUDE0C64,D
21 PFOft <413)
Tenn. River Valley Samples ps, 3
22 POSA <498) 23 PFOS <499)
0 00 C o.O ,i: r _ J 2 -/io / o2s
fcit'ai rjofc
001S67
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0065.D Page 1 Report Date: 27-Aug-2002 10:05
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0065.D
Lab Smp Id SL-1. C-2-1
Inj Date 01-JUL-2002 00:02
Operator mla
Inst ID: dudejr.i
Snip Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Misc Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020629.b\D020629 .m
Meth Date 27-Aug-2002 09:59 dudejr.i Quant Type: ESTD
Cal Date 30-JUN-2002 22:46
Cal File: DDE0058.D
Als bottle 29
Dil Factor 1 .0 0 0 0 0
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compound IB m s (a>)
30 FFHS (3>>
31 pro* (413) SB POSA (4M) 33 pros <499)
QUANT SIG NASS
299 299 299 299 299 299 413 493 4 93 499 499
CONCENTRATIONS
ON-COLUMN FINAL
RT BXP RT DLT RT RISFOM8B
(ng/nli)
(ng/L)
3.3BB 3-1
3.751 3.791 3.402 3.531
3.997 4.7S3 4.171 3.792 4.COS
3.331 3.331 3.331 3.793 3.792 3.792
3.990 4.751 4.144
4.151 4.lit
0.007 -0.212
0.370 0.005 -0.390 -0.253
0.007 0.007 0.007 -0.375 0.437
13C24 2305
1(21 10531
1005 2533
25775 122304 473QS7
2335 21371
1223.79 1224.40
1224.47 0.23151 797.194 0.00404 0.54153 4.44735 9.74111
1377.70 1277.14
1220 1220 1220 0.232
797 0.00404
0.542(N> 4.45 9.74 1210 1230
QC Flag Legend M - Compound response manually integrated.
Dat.3
001868
Report E02-0443
Tenn. River Valley Samples
Data F ila: SSElstar*atStartatSehSdudJr.l\D020629.bSDUDE005.I) SSEtstartatSbarctSchanSdudajr.iS0020&29.bSIlUI00S.D
Pa( 2
18 PFBS <299) 20 PFHS <399)
Exact Ccpy of Originai
y*i< 17-1/o f ai.
Initiai Date
0169
Report E02-0443
Data F il t S\EUtar*at\taritSch\*jdajr.iSD020629.bSIIUl>E0C68.]) 21 PfOA (413)
Tenn. River Valley Samples
Pa 3
22 FDSft <498) 23 PFOS (499)
Exa c tC c jy a :'! ,4dni_ jlc*
initia} 0i6
Q1670
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE007L.D Page 1 Report Date: 27-Aug-2002 10:05
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE007l.D
Led> Smp Id SL-1. C-3-2
Inj Date 01-JUL-2002 01:08
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Misc Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020S29.b\D020629.m
Meth Date 27-Aug-2002 09:59 dudejr.i Quant Type: BSTD
Cal Date 30-JDN-2002 22:46
Cal File: DUDE0058.D
Als bottle 34
Dil Factor 1.00000
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Coapoundi
14 P P M Us)
i t 30 r a s U>
31 n oA (413)
*
32 roSA (4SI)
1
<4 23 r o s (4SS)
QUANT sia
hass
299 299 299 399 413 499 491 499
499
CONCENTRATIONS
OH-COLOHN 92MAL
sa SX RT DLT RT RESPONSI (ng/m L )
(ng/mL)
3.394
3.174 3.750 3.794
3.997
4.752
S. 009
4.174
a.es
3.341 3.341 3.341 3.792 3.990 4.754 4.75 4.144
4 .1 4
0.007 -0.205
0.349 0.004 0.007 0.004
0.253
0.005 0.437
1530S 2054 1430
12444 20244 145959
9741 742237
0017
1233.49 1224.45 1234.44 0.34719 0.17434 7.07743 2743.92 17.9441
1277.17
1220 1220 1220
0.2.7IM) 0.17SIM)
7.04 2740 17.9
120
QC Flag Legend M - Compound response manually integrated.
'S cxaciCopyofi
L ta lL -- /2 / j o / r > i ,
Initiai Dais
00X87X
Report E02-0443 Sata F i t a : S S E ts ta ria tS ta r{ t\c h a n S d iid a jr.l>vS020S29.bSIUDE0071.B
Tenn. River Valley Samples Paa 2
20 PFHS (399>
Sect Copy
nfiaj
bfU:
001872
Report E02-0443
Data Fila: SSEttartMarttSch*Sdudjr.lM20629.bM)UDE0071.D
21 PFOA (413)
Tenn. River Valley Samples
Paca 3
22 FOSA (496) 23 PFOS (499)
ilC Copy... OcjiiTcl
fniSaJ {feta 2 U d g L -
OOI073
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0076.D Page 1 Report Date: 27-Aug-2002 10:06
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0076.D
Lab Smp Id SL-1. C-4-2
Inj Date 01-JUL-2002 02:03
Operator mla
Inst ID: dudejr.i
Snip Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Misc Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020629.b\D020629.m
Meth Date 27-Aug-2002 09:59 dudejr.i Quant Type: ESTD
Cal Date 30-JN-2002 22:46
Cal File: DUDE0058.D
Als bottle 37
Dil Factor 1.00000
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula.- Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compounds
11 PFBS (2>
20 m U )
posa21 proA (413)
22 (4M) 22 9900 (49)
qu a k t aia HASS
299 299 299 299 413 49t 499 499 41* 499
CONCENTRATIONS
ON-COLUMN FINAL
RT EXP RT DLT RT RESPONSI
(ng/L)
(r.g/*L)
3 .311 3.391 3.224 3.311
3.750 3.3ftl 3.792 3.792
3.997 3.990 4.749 4.754
3.71S4.174 4.149 4.149 4.434 4.100 4.COC 4.159
0.000 -0.1S7
0.359 0.000 0.007 0.013 0.005 -0.393 0.200 0.437
13243 2*13 429 5712
11747 103537 594549
514 11440 20929
1223.91 1224.40
1234.53 0.09444 919.097 3.47245 14.1974
1277.75 1277.43 1277.15
1220 1220 1220 0.0944<M)
19(H) 2.57 14.2 1290 1290 1290
QC Flag Legend M - Compound response manually integrated.
CM C lO -lio / t-
initial
001874
S iS T o o
C.
Report E02-0443
Data Fil; SSEtstarttStare*tSchmSdud*Jr.i\l)02629.bSIIUOE0076.D
21 PFOft <413)
Tenn. River Valley Samples Pag 3
22 FOSA <4 9 8)
23 PFOS (499)
E ra# Cop., Q n _
is m
U 0X87G
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0097.D Page l Report Date: 27-Aug-2002 10:06
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0097.D
Leib Smp Id SL-2. C-l-3
Inj Date 01-JUL-2002 05:53
Operator mia
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020629.b\D020629.m
Meth Date 27-Aug-2002 09:59 dudejr.i Quant Type: ESTD
Cal Date 30-JUN-2002 22:46
Cal File: DUDE0058.D
Als bottle 54
Dil Factor 1.00000
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
10*
o1
Compounds is m s (
099)
21 PPOA (411) aa s o s a <) 23 proa (4>
quant a io
HASS
299 299 299 399 399 399 399 413 4M 499 499
CONCBRKATIONS
OH-COLUMN PINAL
RT HXP XT DLT RT RB8PORSI
(ng/.L)
(ng/mL)
3.3S7 3.119 3*750 3.79S 3.394 3.SSS
3.952 3 *994 4.7M 4.110 4.11
3.311 3.311 3.311 3.792 3.792 3.792 3.792 3.990 4.71 4.1! 4.ICO
0.00 *0.212
0.319 0.001 *0.391 -0.234
0.190 0.001 0.00 0.012 0.443
1134$ 2159 1134 3192 1197 till
1579 12700 14*14 121153 113C1
1223.92 1224.44 1224.50 0.03700
797.111 0.17119
797.119 19.045 o.oaaoi 1374.02 1277.43
1220 1220 1220 0.0370
797 0.177
797 1 9 (N) o.oaio(K) 1270 1210
QC Flag Legend M - Compound response manually integrated.
Exact Copy r.:
4~- laj'e/ai.
001877
Report E02-0443
Tenn. River Valley Samples
Data Fila: SSEtstargat\targatSchanSdudajr.i\D020629.bM)UDE0097.D
S\Et*tart*tVtrtatSchai*SdudaJr. iMK>20i29.b\DUDeo097,D
Paca 2
18 PFBS <299) 2 PFHS <399)
BxzCor.- - - .. /mXfff ~2--
,p;'73
0 0 *5 7 8
Report E02-0443
Data Filai S\Ettar*atStar*at\ehiSdudajr.i\B020629,bSDUDE0097.D
21 PFOA <413)
Tenn. River Valley Samples
Paj* 3
22 FOSA <498) 23 PFOS <499)
tacf Copy o f Original Oste
001879
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0105.D Page 1 Report Date: 27-Aug-2002 10:06
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0105.D
Lab Smp Id SL-2. C-3-2
Inj Date 01-JUL-2002 07:21
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020629.b\D020629 .m
Meth Date 27-Aug-2002 09:59 dudejr.i Quant Type: ESTD
Cal Date 30-JUN-2002 22:46
Cal File: DUDE0058.D
Als bottle 60
Dil Factor 1.00000
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
(a>Compounds 1ft PFBS
ao PFHS (3S)
31 PPOA (413) 33 POSA (*) 23 PFOfl (4)
G U M R 31G MASS
299 39ft 299 399 399 399 413 49ft 49ft 499 49 499
ot-couamG0NCSNTRAT1ON8 PIMM.
RT EXP RT DLT RT RSSPONSB (ng/mL)
(ng/mL)
3.3ftft 3.1(2 3.7S0 3.79ft 3.S4S 3.97ft 3.99 4.7C9 4.437 4.174
4.434 4.SOS
3.3ft! 3.391 3.311 3.792 3.792 3.792 3.990 4.75ft 4.7SS 4.14ft
4.1ft 4.14ft
0.007 -0.219
0.349 0.004 -0.247 0.1*4 0.004 0.013 -0.329 0.004
0.244 0.437
923ft 149 243 329 4903 3370 771 20521 14C4 179402
5700 19533
1224.04 1224.47 1224.41 0.02579 0.07143 0.02704 919.244 0.25210 3744.34 0.99442 1375.24 1277.19
1220 1220 1220 0.025ft 0.0714
w0.027ft 1 0.252 2740 0.9B7
1290 1200
QC Flag Legend M - Compound response manually integrated.
Exact Copy oiO t'c'rt-
.C k L - S j/ fo L -
initiai Of-tr.
^ v > iS g o
Report E02-0443
Bat F lit !
t*tSt*rt*tSchSdud*Jr. i SD020629.bSDUBE01.05. B
Tenn. River Valley Samples P *t 2
20 PFHS <3 9 9)
, f c t Cop;
Oaii
001881
Report E02-0443
Data Fila: YsEtatartatStarft\cha\dud*Jr.iM>020629.bSDUDE0105.D 2 t PFOA <413>
Tenn. River Valley Samples P a ja 3
22 FOSA <49S> 23 PF08 <499>
&actCcpj/j-.:.. .,sl
U ltP h u
U 01bS 2
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0ll7.D Page 1 Report Date: 27-Aug-2002 10:07
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020629.b\DUDE0117.D
Lab Smp Id SL-2. C-6-1
Inj Date 01-JUL-2002 09:33
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info
Comment
Method Meth Date Cal Date
\\Etstarget\target\chem\dudejr.i\D020629.b\D020629 .m
27-Aug-2002 09:59 dudejr.i Quant Type: ESTD
30-JUN-2002 22:46
Cal File: DUDE0058.D
Als bottle 69
Dil Factor 1.00000
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compound
li PPBS (29)
20 PPKfl () 21 PPOA <13> 22 POSA (> 23 ppoa <>
QUANT SIG NASS
299 299 299 399 413 490 499 499
CONCENTRATIONS
ON-COLUMN PINAL
RT BXP RT DXiT RT RESPONSO
(ng/mL)
<ng/mL)
3.301 3.170 3.7S0 3.790 3.990 4.709 4.101 4. COB
3.301 3.301 3.301 3.792 3.990 4.750 4.100 4.100
0.007 -0.205
0.309 0.000 0.000 0.013 0.013 0.437
9473 141B
545 2433 100 32417 221203 22005
1224.03 1224.41 1224.53 0.00120 19.302 0.33013 2.2003S 1277.10
1220 1220 1220 0.00120(H)
1(H) 0.330
2.20 1200
QC Flag Legend M - Compound response manually integrated.
& a ct Copy or Gr.~?n::
C JlIL. IlkLijl--
iiiat
Ost;-
001 3
Report E02-0443
Bat Filet SS E lt*rj t\t -t# t'sch N *Jd *4 r.iM )0 2 0 i2 9 .b M )U D E 0 1 1 7 ,D
Tenn. River Valley Samples
Pace 2
20 PFHS (399>
Exact Copy of Original
Clt2C- iJ//tn Ort.
U014
Report E02-0443
Data Fila: \\EtitarcatStartat\eh**\dudajr.iSD020629.bSDUDE117.D
21 PFOA (413)
Tenn. River Valley Samples
22 FOSA (49S>
23 PFOS <499)
.~ct Copy ( ; Ctiginni
i & C l2.Ulo2-
Qstf;
0188S
Report E02-0443
Tenn. River Valley Samples
Data File: DUDE0066.D Report Date: 27-Aug-2002 11:05
Page 1
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020702(D20702).b\DUDE0066.E
Lab Smp Id SL-3. C-2-2 Inj Date 03-JUL-2002 02:49
Operator rala
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Misc Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020702(D20702).b\D020702.m
Meth Date 27-Aug-2002 11:01 dudejr.i Quant Type: ESTD
Cal Date 03-JUL-2002 01:21
Cal File: DUDE0058.D
Als bottle 55
Dil Factor 1.00000
Integrator Falcon
Compound Sublist:all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compound
1* PRBS (2M>
20 PPHS (1) 21 PROA Mil) 22 ROSA (4M) 23 PROS (4M)
QUANT SIG HASS
ass 399 ass ass 413 4SB 4SS 4SS
CONCENTRATIONS
ON-COLUMN PINAL
RT EXP RT DLT RT RBSPOKS8
(ng/mL)
(ng/uL)
a.ass 3.113 3.75? a.ais 4.003 4.003 4.Ill 4.SSI
3.307 3.3*7 3.3*7 3.7S1 3.S*S 4.74* 4.147 4.1*7
0.00* 0.204
0.370 o.oa* 0.014 0.055 0.014 0.424
14173 3040 aaac soss
2254 2313* 1*3*14 23954
1220.00 1220.4* 1230.51 0.30394 0.37074 0.4310* 1.14537 1324.22
1320 1320 1220 0.204(H) 0.271(H) 0.431 1.14 1320
QC Flag Legend M - Compound response manually integrated.
"-XM CopyofOriginal
C i& ~ mtiv
Date
001886
Report E02-0443
Tenn. River Valley Samples
Data F l U i SSEtstarfatStartatl>ha*Vluda<jr.lM)020?02<D20702.bMXJDE0066.D
Paca 2
20 PFHS (399>
Exact Copy of Origina1
Ul U I p
initial
Oatr-
t0 lS S 7
Report E02-0443
Tenn. River Valley Samples
Data Flit: \SEtUrtttStrttSchaiSdudJr.iS0020702<H20702) .bMXOEEOOi.D
21 PFOA <413)
Pat# 3
23 PFOS <499)
Exact Copy of Original
CiiL_ l2-//dfL.
'nffiai
ox,-.
0Q88S
Report E02-0443
Tenn. River Valley Samples
Data Pile: DUDE0076.D Report Date: 27-Aug-2002 11:06
Paqe 1 a
3M Environmental Laboratory
B02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020702 (D20702).b\DUDE0076.D
Leib Smp Id SL-3. C-4-2
Inj Date 03-JUL-2002 04:39
Operator tnla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info
Comment
Method
\\Btstarget\target\chem\dudejr.i\D020702 (D20702).b\D020702.m
Meth Date 27-Aug-2002 11:01 dudejr.i Quant Type: ESTD
Cal Date 03-JL-2002 01:21
Cal File: DUDE0058 .D
Als bottle 62
Dil Factor 1.00000
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compound* it PPBS (2)
20 FFHS tt)
21 PFOA (4131 22 POSA (4M) 23 rros <499*
QUANT SIQ MASS
29 299 299 399 399 399 413 49 499 499 499
CONCENTRATIONS
OH-COLUMN FINAL
RT BXF RT DLT RT RESPONSE
(ng/oL)
(ng/*L)
3.394 3.112
3.770 3.25 3.572 4.01O 4.010 4.749 4.147 3.911 4.591
3.347 3.347 3.347 3.791 3.711 3.791 3.949 4.74 4.147 4.1C7 4.147
0.007 -0.205 0.343 0.034 -0.219 0.219 0.031
0.031 0.030 -0.35
0.434
21375 2047 1244 39C5 331* 3391
9130 20947 307947
1347 20341
1219.74 1220.52 1220.55 0.14177 0.14954 0.15973 795.310 0.35235 3.40(47 1324.54 1324.29
1220 1220 1220 0.143
0.170 0.170
7*5 (N) 0.352
3.41 1320
1320
QC Flag Legend M - Compound response manually integrated.
Bract Copy of Origina! /3 -//o fp i-
0018S9
Report E02-0443
Tenn. River Valley Samples
Dt* Fllt SSEtsUrs*t\tarsttSchnNdud*Jr.lSD020702<S20702>.bSOUI007e.S
PHI 2
20 PFHS (399)
Exact Copy of Original
.CJ}*- iZ(</i-
initia!
Dair.
001C90
Report E02-0443
Tenn. River Valley Samples
S*ta F ila i SSEtstartkStart*tSch*aSdudjp. i\IK>20702<B20702>. b\DUDEOO?6. D a PF (413)
3
22 FOSA <496)
23 PFOS <499)
i Copy o f Original
OnC._ la ftc J l-
Osta
001891
Report EQ2-Q443
Tenn. River Valley Samples
Data File: DUDE0083.D Report Date: 27-Aug-2002 11:06
Page 1
3M Environmental Laboratory
E02-0443, Term. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020702(D20702).b\DUDE0083.D
Lab Smp Id SL-3. C-6-1
Inj Date 03-JUL-2002 05:56
Operator mla
Inst ID: dudejr.i
Smp Info Tenn. River Valley Fish. Prep-17 Jun 02. CMC/MLA. 20 Jun 02
Mise Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020702(D20702).b\D020702.m
Meth Date 27-Aug-2002 11:01 dudejr.i Quant Type: ESTD
Cal Date 03-JUL-2002 01:21
Cal File: DUDE0058.D
Als bottle 68
Dil Factor 1.00000
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Concentration Formula: Amt * DF * CpndVariable
Cpnd Variable
Local Compound Variable
Compound*
It m s (399) 20 m a <359) 21 PPOA (413) 22 POSA (495) 22 ppoa (499)
QUANT3ia
NASS
299 3) 413 491 499
CONCSNTRATIOKS ON-COLUMN PINAL RT BXP RT DLT AT RBSPOKS (ng/mL) (ng/L>
Compound Hob Detected Compound Not Dotocbftd. Cowpound Hob Dotectod Compound Hob Detected. Compound Nob Detected,
Copy of Original
C i n e ^//a/rj.2Dste
001892
Report E02-0443
Tenn. River Valley Samples
Sata F ilt \SEt*tars*tStartt\ch*n\dudaJr.AD020702<D20702>.bMXJX0083.D
p* 2
fl
20 PFHS <399) (Unctotaotad)
Exact Copy of Origina!
C m... la-J j d p -ju
001893
Report E02-0443
Tenn. River Valley Samples
ta ta F lU t S S E ts ta rc *tS ta re tS e h *n S d U d *J r. iS D 020702(D 20702) .b S K fl)E 0 0 83 .D
2 t PFOA (413> (UncMmtwl)
Pe* 3
22 FOSA (498) <Uhd*taetad)
23 PFOS (499> < U n d *te c t*d >
:\ 'u Copy o Crfgfna!
C W L . I2jc&-
`niL!ai
Oats
001894
Report E02-0443
Tenn. River Valley Samples
Data Pile: \\Etstarget\target\chem\dudejr.i\D02082A.b\DUDE0065.D Page l Report Date: 27-Aug-2002 14:11
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr. i\D020812A.b\DUDE0065.D
Lab Smp Id: Water Blank-1
Inj Date : 12-AUG-2002 23:11
Operator : mla
Inst ID: dudejr.i
Smp Info : E02-0443 Water Blank Water Samples; non-GLP; 6/20/02; OK
Misc Info :
Comment :
Method : \\Etstarget\target\chem\dudejr.i\D020812A.b\D020812A.m
Meth Date : 27-Aug-2002 14:06 dudejr.i Quant Type: ESTD
Cal Als
Date : bottle:
2102-AUG-2002
16:13
Cal Pile: DUDE0027.D
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist:all.sub
Target Version: 4.12
<o
1
Compound 1 (J9S)
2 PFH3 (MS)
3 PPOX (413)
s4 YOOA (4SI) pros (4>)
q u a n t aia HABS
299 299 299 399 399 413 496 499
C0NCEWTRATZ0M8
OM-COLUXM PINAS
RT BXP RT DLT RT RR8PONSB (ng/mL)
(ng/aL)
3.353 3.10 4.301 3.04 3.565 4.016 4.609 4.301
3.394 1.394 3.394 3.791 3,791 3.963 4.766 4.160
0.041 Q.145
0.607 0.013 -0.326 0.034 0.041 0.041
29174 5546 1904 S192 1012 9179 3390
34010
0.54141 501.660 503.766 0.1546 0.02703 0.04921 6.10649 0.16996
0.541 504 504
0.155 0.0270 0.0492
0.105 0.170
Eiaci Co;j orOrg-iiw:
A.' IrJUa!
Date
001S95
Report E02-0443
to ta F ila : SSt*tartt\tapet\chnSdudjr. lM1020fll2A.bSDUDE006S.D
Tenn. River Valley Samples
P**a i
Exact Copy o: C r.--.
-C&t t'lj/d i-- tflltfal Or.t
001836
Report E02-0443
Dit* F il; SSEttar{tNtrgtt\chiiSdudjr.l\D0208i2fl,b\DUE0065.D 3 P F <413>
Tenn. River Valley Samples
4 FOM <498>
B PFOS (499>
ECt Copy o; iJrfn
i2u
initiaj
Date
001S97
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D02082A.b\DUDE0066.D Page 1 Report Date: 27-Aug-2002 14:11
3M Environmental Laboratory
E02-0443, Term. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020812A.b\DUDE0066.D
Lab Stop Id: Water Blank-2
Inj Date : 1 2 -AUG-2002 23:22
Operator : mla
Inst ID: dudejr.i
Smp Info : E02-0443 Water Blank Water Samples; non-GLP; 7/17/02; OK
Misc Info :
Comment
Method : \\Etstarget\target\chem\dudejr.i\D0208l2A.b\D0208l2A.m
Meth Date : 27-Aug-2002 14:06 dudejr.i Quant Typej ESTD
Cal Date : 12-AUG-2002 16:13
Cal File: DUDE0027.D
Als bottle: 21
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Compounds 1PFBS<2>
23PPPFOHSA((34131) 45PPOROSAS((443))
QUNAANSTSSIC RT BNPNT DLTRTRfiSPONSBONInG-CgOO/NaLCULBM)INTJUTXInPagNIN/SmALL)
299
299
299
299
2444411399339
333344444.......3..37103351491500140350150 333333344.........333399771999898988444343180--000000000.........01038003048440137404291471 511340133134158734183011740785110987890 154500005.00....0041121313332105...34.944477787978221828887703 0Q001....11124.555420510000355732454
c t C opy o f ergi:*;
fnifiai
2-
QZf
001S98
Report E02-0443
ta t F il : S\Etstr(tStargtSchSdudtJr. i\D02O8i2ft,b\DUDEOOM.D
Tenn. River Valley Samples
Pt 2
ExactCcpy Jt
J o [ X
Data
001S99
Report E02-0443
Data F ila: S\EfcatarcatStarsatSchMSdudajr.iSl)020ei2A.bMIUI)E0066.9 3 PFtM (413)
Tenn. River Valley Samples
Pata 3
4 FOSA <498> B PFOS (499)
'S .. W (
001900
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D02082A.b\DUDE0076.D Page 1 Report Date: 27-Aug-2002 14:11
3M Environmental Laboratory
E02-0443 Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudej r .i\D020812A.b\DUDE0076.D
Lab Smp Id: 38032
Inj Date 13-AUG-2002 01:12
Operator : mia
Inst ID: dudejr.i
Smp Info : E02-0443-38032; Water Samples; non-GLP; 6/20/02; OK
Misc Info :
Comment
Method : \\Etstarget\target\chem\dudejr.i\D0208l2A.b\D0208l2A.m
Meth Date : 27-Aug-2002 14:06 dudejr.i Queuit Type: ESTD
Cal Date : 12-AUG-2002 16:13
Cal File: DUDE0027.D
Als bottle: 26
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Coapound 1 FTBS
2 PTHfl (39J)
2 4
FVOX POSA
l(U90)
()
iM
QUANT SIS NASS 299 29 2 a2 2399 444199390
RT 2XF RT OUT RT RESPONSE
3.401 2.540
33..339944
0.007 -0.054
3.203 3.394 -0.191
34..004140 33..339944 00..442540
34,,021055
33..379941
0.021 0.014
444,.,71000031 434...197055200 0.0...00a22x11'
19351 147211
195 2975503 157279770 04190 130473 190157
CONCRNTRATCCMS
ON-COLUMN (ng/mL)
PINAL (ng/ab)
a
0.19454 0.197
4.72522 4.73
303.706
504
550033..705219
550044
540.035.003070
45.0054
44..9544495220
44..9547
5.10901 5.19
Exact Copy n.! O-ip:;
Uni. Urjih-
Lnitia!
0*V:
001901
Report E02-0443 Dt* Filet 'sNEtitrt;tSUrttSchiSdu<iJr.SB020812.bVtlBE007t.D
Tenn. River Valley Samples P *t Z
Z PFHS <399)
Exact Copy of Origina!
CimC M -f/oloi-
initial
Date
0 0 1 .9 0 2
Report E02-0443
Data m a : \\EtttartatStartat\cha*Sduel9jr.i'J20eia).bSDUDE0076.D
3 PFOfi <413)
Tenn. River Valley Samples P *(t 3
4 POSA <498) B PFOS <499)
fc.tacCopy,-0Vf/:.^ ijx/o'i-
001903
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D02082A.b\DUDE0073.D Page l Report Date: 27-Aug-2002 14:11
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020812A.b\DUDE0073.D
Lab Smp Id 38029
Inj Date 13-AUG-2002 00:39
Operator mla
Inst ID: dudejr.i
Smp Info E02-0443-38029; Water Samples; non-GLP; 6/20/02; OK
.Misc Info
Comment
Method Meth Date Cal Date
\\Etstarget\target\chem\dudejr.i\D020812A.b\D020812A.m
27-Aug-2002 14:06 dudejr.i Quant Type: ESTD
12-AUG-2002 16:13
-C-a-l -F-ile: DUDE0027.D
Als bottle 25
Dil Factor 1.00000
Integrator Falcon
Compound Sublist : all.sub
Target Version: 4.12
Compounde
a 1 CPU (JJ>
a PFHS (1*9) 3 PPA (413) 4 POSA (4*0 s proa (4)
1 i
QOAMT 91 MAAS
399 39* 413 499 499 499
RT ax? RT
3.40* 3.111 4.00 4.19 4.197 4.447
3.394 3.791 3.943 4.74* 4.140 4.140
DLT RT RBSPORflB
0.014 0.030 0.037 0.034 0.037 0.307
19093 353177 3301*1
34000 31300 131570
c o N c n m u s io iu ON-COLON* FINAL
(ng/L) (ng/aL)
3.45491 7.05310 31.0431 1.11439 30.1041 3.3904
a.c(N)
7.05 31.0
1.11 (M) 30.3 3.39
QC Flag Legend M - Compound response manually integrated.
B o c i Cop/ of O rirJrr
l/o/ km
U01S04
Report E02-0443
Date F ile t Vtstar{tSt4rs*tSch*ASduc(*4rtMtt20812A.bM)UK0073,!l
Tenn. River Valley Samples
Pf* 2
2 PFHS <399)
E e c t C o p y r .f -'.
M l C. Il !/*{&-
Initiai
.
001905
Report E02-0443
Bata Filas \SEtstartetStarjat\cheiSdudaJi-,i\D020812ft.bMIUZ)E0073.I> 3 PFOA <4131
Tenn. River Vaitey Samples Pas 3
4 FOSA (498) B FFOS <4991
Exact Copy of Cn'!)'!
l 'i l l o i -
initial Date
001906
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D02O8'2B.b\DUDE0l30.D Page l Report Date: 29-Aug-2002 07:12
3M Environmental Laboratory
E02-0443, Term. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020812B.b\DUDE0130.D
Lab Snip Id: 38030
Inj Date : 13-AUG-2002 11:08
Operator : mla
Inst ID: dudejr.i
Smp Info : E02-0443-3&030; Water Samples; non-GLP; 7/17/02; OK
Misc Info :
Comment :
Method : \\Etstarget\target\chem\dudejr.i\D020812B.b\D020812B.m Meth Date : 29-Aug-2002 07:08 dudejr.i Quant Type: ESTD
Cal Date : 13-AUG-2002 06:44
Cal File: DUDE0106.D
Als bottle: 42
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Compounds
i PBS (a>
2 ras (3>
3 ?roA (411) 4 POSA (4*1) S PFOS (441)
QUANT Slfr NASS
39 39 29 29 399 413 49 49
CONCENTRATIONS
OM-CQliUKN PINAL
RT RXP RT DLT RT R85P0NSK (ng/mL)
(ng/ali)
3.3? 2.49 3.303 3.777 3.777 3.941 4.741 4.13
3.394 3.394 3.394 3.394 3.791 3.992 4.7 4.ICO
0.007 0.994 0.191
0.393 0.014 0.014 0.027 -0.021
197441 1231 2244
112C9 307299 4152125 7940357 991442
3934.50 2935.44 2935.42 2935.20 424.445 427.440 300.224 423.473
2930 2940 2940 2940
425 42 300 424
i
Exact Copy a - G ri^ ir;
UJjjrfamitlal Dsta'
001907
Report E02-0443
Hat F ilar \\EUUrs*tStare*tSchMSdud*jr.lM>020812B.bSIIUIIE0130.0
Tenn. River Valley Samples P j* 2
2 FFHS <399)
East Copy
001908
Report E02-0443
D a ta F iU : S S E ts ta ri t\U r* l\c h tia \d u d * 1ir.iS D 020812B .bS IIU D E 130.II 3 PFOA <413)
Tenn. River Valley Samples
4 FOSA <496) B PFOS <499)
Exact Copy Or`r;.v . U o |s G 9
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D02082A.b\DUDE0092.D Page 1 Report Date: 27-Aug-2002 14:12
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020812A.b\DUDE0092.D
Lab Smp Id 38043
Inj Date 13-AUG-2002 04:09
Operator mla
Inst ID: dudejr.i
Smp Info E02-0443-38043; Water Samples; non-GLP; 6/20/02; OK
Mise Info
Comment
Method Meth Date Cal Date
\\Etstarget\target\chem\dudejr.i\D020812A.b\D020812A.m
27-Aug-2002 14:OS dudejr.i Quant Type: ESTD
12-AUG-2002 16:13
Cal File: DUDE0027.D
Als bottle 34
Dii Factor 1.00000 Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Ooapeund* 1 p p b s (21)
3 m a (211) 3 PFOA (413) 4 POSA (4M) 5 proa (4M)
QUANT S2Q MASS
299 299 299 299 299 299
413 4M 4M
CONCENTRATIOMS
OW-COLONN PXNAXi
RT EXP RT DLT RT RESPONSE
(ng/aL)
(ng/aL)
3.354 a.4SI 3 .210 3 .IS 4.037 3.M3 4.010 4.7*5 4.195
3.3*4 3.3*4 3.3*4 3.3*4 3.3*4 3.791 3. a 4.75 4. ISO
*0.040 -0.943 *0.1*4
0.424 0.443 0.171 0.020
o.oaa
0.035
3214 739
C2 1344 1953 15543 *4*1 5471 30*51
0.57051 503.29 503.534 503.511 503.7*5 0.S0173 0.0406a 0.2049 0.07297
0.571 504 504 504 504
0.502 0.05*7
0.207 0.0720
;rracfCcpyofOr^ir-'
Initiai n-j.. '
001910
Report E02-0443
Sata F ila: SSEtitartatStarjat\ehaSdudajr. iND020812A. b\DUDE0C92. D
Tenn. River Valley Samples Paca 2
Io n 299.00
6 .0 < 8 .8 -j
r 5ri
8.0-1
4.8-1
4.0 -!
? 3 .8 ) 1 3 .0 j 2 .8 -i
o
* M
Al
A
o. b-A /L -- lJ J -
US
s "
*k. .^J
_____2_._4___2_._8__B3.i2n. 3.4 4.0
2 PFHS <399)
-f -r'Original
CMJL / io/o^ 'i'rai Daa
00X311
Report E02-0443
Data F ila: \SEtstarcatStarsatSchmSdud*Jr.iM)020912A>bM)U])E0092>D 3 PFOA (413)
Tenn. River Valley Samples
4 FOSA (4W>
B PFOS (4 9 9 )
001912
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D02082A.b\DUDE0067.D Page 1
Report Date: 27-Aug-2002 14:11
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020812A.b\DUDB0067.D
Lab Smp Id: 38025
Inj Date : 12-AUG-2002 23:33
Operator : mla
Inst ID: dudejr.i
Smp Info : E02-0443-38025; Water Sandies; non-GLP; 6/20/02; OK
Misc Info :
Comment :
Method : \\Etstarget\target\chem\dudejr.i\D020812A.b\D020812A.m
Meth Date : 27-Aug-2002 14:06 dudejr.i Quant Type: ESTD
Cal Date : 12-AUG-2002 16:13
Cal File: DUDE0027.D
AlS bottle: 22
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Compounds
a1 a
ms PFHS PROA,
Um )
O
(*!*)
4 POSA (4M)
S PPOS (4M)
QCANT SIO NASS
399 399 413 494 49 499
CONCENTRATIONS
OH-COLOHM PINAL
RT EXP RT DLT RT RBSPORSI (ng/mL)
tng/L)
3.401 3. aia 4.003 4.794 4.141 4.464
3.394 3.791 3.931 4.764 4.160 4.160
0.007 0.031 Q.031 0.014 0.031 0.304
9453 247750 33164
39344 643(51 135043
3.99306 7.71X34 31.319 0.96234 14.4924 3.40254
3 . M (N) 7.71 31.3 S.M2M) 14. S 3.40
QC Flag Legend M - Compound response manually integrated.
EiaciCopv C-
D L . U/y
fe iia i
001913
Report E02-0443
Data F ilt S\EttarttStartt\eha*SdudJr.i\D020812A.b\IWIIE0067.D
Tenn. River Valley Samples
Pat a
2 PFHS <399)
WoO\
001914
Report E02-0443
Data Fi lat SSEtstartatStar*lScha\du<ra,Jr.i\D020812A.bMIUDE0067,D 3 PFOA C4t3>
Tenn. River Valley Samples
ptgt 3
4 FOSA <498) 8 PFOS <49>
C-0 1 9 1 5
Report E02-0443
Tenn. Rivet Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D02082A.b\DUDE0069.D Page 1 Report Date: 27-Aug-2002 14:11
3M Environmental Laboratory-
B02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudejr.i\D020812A.b\DUDE0069.D
Lab Smp Id 38026
Inj Date 12-ADG-2002 23:55
Operator mla
Inst ID: dudejr.i
Smp Info E02-0443-38026; Water Samples; non-GLP; 7/17/02; OK
Misc Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020812A.b\D0208l2A.m
Meth Date 27-Aug-2002 14:06 dudejr.i Quant Type: ESTD
Cal Date 12-AUG-2002 16:13
Cal File: DUDE0027.D
Als bottle 23
Dil Factor 1.00000
Integrator Falcon
Compound Sublist : all.sub
Target Version: 4.12
1 i
i CONCSNTRATXONS
QUANT SXG
ON-COLUMN PINAL
Qmapounds
NAJS
m r t DLT RT RBSPOMS8 (ng/aL)
(ng/aL)
1 PFBB 2 PPKfl 3 PPOA 4 POSA 5 PPOS
(299) <299) (413) (494) (499)
299
3.401 3.394 0.007
114547 3.70420
3.70{lt)
399
3.411 3.791 0.020
2S5IC4 7.94944
7.97
M
4.003 3.942 0.031
340041 22.4S24
22.4
49t
4.749 4.744 0.021
31142 1.02079
1.0i (H)
99
4.140 4.140 0.020
444455 20.7904
20.4
499
4.497 4.140 0.307
140144 3.54101
3.57
QC Flag Legend M - Compound response manually integrated.
Cos, Ci/ic i j j /0{ i_
00916
Report E02-0443
Tenn. River Valley Samples
i PFBS <299 2 PFHS <399)
00191?
Report E02-0443
Hat F ila t S\EtstargatStarcatSchaMSdudaJr.i'a>O2OB12fl.bsgUIE009.D 3 PPM <413>
Tenn. River Valley Samples
Paca 3
4 FOSA <498> S PFOS <499>
^Ca^ya;Cr!:in.y M L u U (* /n -
0 0 9 1 S
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D02082A.b\DUDE0071.D Page 1 Report Date: 27-Aug-2002 14:11
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020812A.b\DUDE0071.D
Lab Smp Id: 38027
Inj Date : 13-AUG-2002 00:17
Operator : mla
Inst ID: dudejr.i
Stnp Info : E02-0443-38027; Water Samples; non-GLP; 7/17/02; OK
Mise Info :
Comment :
Method
\\Etstarget\target\chem\dudejr.i\D0208l2A.b\D0208l2A.m
Meth Date : 27-Aug-2002 14:06 dudejr.i Quant Type: ESTD
Cal Date : 12-AUG-2002 16:13
Cal File: DUDE0027.D
Als bottle: 24
Dii Factor: 1.00000
Integrator: Falcon
Compound. Sublist : all.sub
Target Version: 4.12
Compound*
1 PVBS U s s )
2 PFHS (is >
3 PPOA (413) 4 POSA (4SI) 5 p ro s (4SI)
QUANT 8Xa NASa
139 399 413 49 499 499 499
COWCBmUZIOHS
ON-COLUMN PINAL
RT EXP RT DUT XT RESPONSE
(ng/mL)
(ng/aL)
3.401 3.911 4.002 4.794 4.190 3.944 4.447
3.394 3.791 3.993 4.749 4.140 4.140 4.140
0.007 0.020 0.020 0.02 0.020 -0.294 0.307
102929 405593 412129 121332 909339
410 S093
3.14444 12.7977 27.9472 4.0011S 24.5743 379.797 1.79743
3*1. (It) 12.9 29.0 4.00 24.4
390 l.0
QC Flag Legend M - Compound response manually integrated.
<
0Q1919
Report E02-0443
Oats F ilet \\Ett*rtt\tarj*t\ehw\dudjr,lM020812A.b\DUDE0071.D
Tenn. River Valley Samples
Fit 2
2 PFHS <399)
'^COC;
,CMr_ ii'a;"
w/il
001920
Report E02-0443
Data Fil! SSEtstarjatNtarj*t\eh*a\dud#jr, iSD020812A. b\DUBE0071. D
3 PFCK < 413)
Tenn. River Valley Samples
4 FOSA <496) B PFOS <499)
Chy /xht/oi. 001921
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D02082A.b\DDE0078.D Page 1 Report Date: 27-Aug-2002 14:11
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020812A.b\DUDE0078.D
Lab Smp Id: 38033
Inj Date : 13-AUG-2002 01:34
Operator : mla
Inst ID: dudejr.i
Smp Info E02-0443-38033; Water Samples; non-GLP; 6/20/02; OK
Mise Info :
Comment :
Method : \\Etstarget\target\chem\dudejr.i\D020812A.b\D020812A.m
Meth Date : 27-Aug-2002 14:05 dudejr.i Quant Type: ESTD
Cal Date : 12-AUG-2002 16:13
Cal File: DUDE0027.D
Als bottle: 27
Dii Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Compounds 1 m a (3)
a PIHS (3*) a PPOA (413) 4 POSA (4**) s PPOS (43)
QUANT SZG MASS
299 295 29 299 39 399 413 49ft 499
CONCSNTKATJOtKi
ON-COLUMN PINAL
RT BXF RT DLT RT RB5F0MS8 (ng/*L)
(ng/nlj)
3.3CO a.aio 3.10 4.OSS 3.412 3.969 4.010 4.796 4.194
3.394 3.394 3.394 3.394 3.791 3.791 3.992 4.76 4.160
-0.034 -0.14 0.424 0.664
0.021 0.17 0.02 0.02 0.034
26600 4236 1671 634 S6S 5436
11637 5467
S0it
0.45093 503.706 503.796 503.632 0.16974 0.16313 0.20126 0.17456 0.20349
0.451 504 504 504
0.170 0.162 0.201 0.174 0.203
t
001922
Report E02-0443
D*U F i l e SSEtstr(tStar(tNchmSdud*jri SD020B12A. bMUDE0078. S
Tenn. River Valley Samples
<*n* 2
2 PFHS <3S9>
..CiiiC J ii /o k .
001923
Report E02-0443
Data F ilt \\Ettar*t\t*rxtSchw\dudjr.iSI02ei2A.bSDUDE0<>78.D
3 P FM (413>
Tenn. River Valley Samples
Pjp 3
B PFOS <499>
Ciyu"Ju, l^l//2001924
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr .i\D020812A.b\DUDEQ080.D Pacre 1
Report Date: 27-Aug-2002 14:11
a
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file \\Etstarget\target\chem\dudej r .i\D020812A .b\DUDE0080.D
Lab Smp Id 38034
Inj Date 13-AUG-2002 01:57
Operator mla
Inst ID: dudejr.i
Smp Info E02-0443-38034; Water Samples; non-GLP; 6/20/02; OK
Mise Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020812A.b\D020812A.m
Meth Date 27-Aug-2002 14:06 dudejr.i Quant Type: ESTD
Cal Date 12-AUG-2002 16:13
Cal File: DDE0027.D
Als bottle 28
Dil Factor 1.00000
Integrator Falcon
Compound Sublist : all.sub
Target Version: 4.12
Compound
1 PPBS (a> a PPHS (3l 3 SPOA U V D 4 POSA (4M)
5 p ros (4M)
QUANT SIO HASS
299 399 413 492 492 499
COMCBHTftATIOHS
ON-COLUMN PINAL
RT BXP RT DLT RT RESPONSI
(ng/mL)
(ng/aL)
3.401 3.212 4.010 4.79 5.090 4.194
3.394 3.791 3.922 4.752 4.742 4.150
0.007 0.021 0.022 0.022 0.322 0.034
21015 2573
17031 5747 275
51049
0.50070 0.25104 0.55503 0.21507 0.00294 0.71127
0.501(M) 0.251 0.555 0.215 0.00294 0.711
QC Flag Legend M - Compound response manually integrated.
J
On' / j / , a/ c.
*> 0 1 9 2 5
Report E02-0443
Data F lla: SSEtatarc*tStar(tSehmSdiidaJr.:SD020S12A.bMIUDE0ee.D
Tenn. River Valley Samples
Paj 2
2 PFHS <399>
UJJtiC\ k '& a i
L2lteJ.2Jrcw.u-
i9 2 e
Report E02-Q443
B a t* F l U t \S E ts ta rt t\ta rt tS c h m S d u d J r. L\D 02 0 8 i2 .b \D U D E 0 O e o .r 3 PFOA <413)
Tenn. River Valley Samples
4 FOSA <498) 8 PFOS (4 9 9 )
r x i c i iJc^y ; Original
feiraJ
Date
001927
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D020812A.b\DUDE0084.D Page 1 Report Date: 27-Aug-2002 14:11
3M Environmental Laboratory
E02-0443, Terni. River Valley Samples
Data file : \\Etstarget\target\chem\dudej r .i\D020812A.b\DDE0084.D
Lab Smp Id: 38037
Znj Date : 13-AUG-2002 02:41
Operator : mia
Inst ID: dudejr.i
Smp Info E02-0443-38037; Water Samples; non-GLP; 6/20/02; OK
Mise Info :
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020812A.b\D020812A.m
Meth Date : 27-Aug-2002 14:06 dudejr.i Quant Type: ESTD
Cal Date : 12-AUG-2002 16:13
Cal File: DUDE0027.D
Als bottle: 30
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Coapoundfl
1 m s > 2 PVHS <34) 3 PPQA <413) 4 POSA <44) S vos (449)
QUANT 81G NASS
299 399 413 499 499
CONCENTRATIONS
ON-COLOHM VINAI*
RT KXP RT DLT RT R8SPOMSB
(ng/L)
tng/aL)
3.3S3 3.90S 4.010 4.79C 4.199
3.394 3.791 3.992 4.769 4.160
-0.041 0.014 0.029 0.029 0.029
32546 12979 14081
6547 43CS1
0.65999 0.39267 0.36547 0.20949 0.47606
0.660(N> 0.393 0.365 0.209 0.476
QC Flag Legend M - Compound response manually integrated.
001928
Report E02-0443
D a ta F i la t S S E tsta rja tS ta rja tS ch a S d u d a Jr.iS D 0 2 4 8 1 2 ft.b \D U D E O O S 4 .B
Tenn. River Valley Samples P a ja 2
2 PFHS <399)
`^^yofO iigfnai C1 3t3
001929
Report E02-0443
D a ta F ila S \E U ta r t t\ta r fr tS e h M \* jd a J r . iS B 0 8 1 2 fl.b M U B E 0 0 8 4 .a
3 PFOA <413>
Tenn. River Valley Samples
Pe 3
4 FOSA (4 9 8 )
B PFOS (499)
001930
Report E02-0443
' Tenn. River Valley Samples
Data File-. \\Etstarget\target\chem\dudejr.i\D020812A.b\DUDE0086.D Page 1 Report Date: 27-Aug-2002 14:12
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file : \\Btstarget\target\chem\dudejr.i\D0208l2A.b\DUDE0086.D
Lab Stnp Id 38038
Inj Date 13-AUG-2002 03:03
Operator Smp Info
mia Inst ID: dudejr.i E02-0443-38038; Water Samples; non-GLP; 6/20/02? OK
Mise Info
Comment
Method
\\Etstarget\target\chem\dudejr.i\D020812A.b\D020812A.m
Meth Date 27-Aug-2002 14:06 dudejr.i Quant Type: ESTO
Cal Date 12-AUG-2002 16:13
Cal File: DUDE0027.D
Als bottle 31
Dil Factor 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Compound*
1 PFBS (2M> 2 pphs (IS 2 PTC* (41 4 POSA (4M) % pros (4M)
QUART SII MASS
299 39* 413 49 4
OOHCBHTRArtOtB
OM-COLUNN PINAL
KT BXP RT DLT RT RESPONSI
(ng/nL)
(ng/L)
3.353 3.12 4.003 4.794 4.111
3.394 3,791 3.992 4.74 4.140
>0.041 0.021 0.021 0.02 0.02
34994 214
1S139 3453
44194
0.74244 0.24701 0.43379 0.10754 0.4933
0.743(H) 0.247 0.434 0.10 0.493
QC Flag Legend M - Compound response manually integrated.
<act Copy of 0ri3,,,a! ''i (
Date
001931
Report E02-0443
Data F ila i S\EttarttStartt\chSduci*jr. lSD020ei2A.bMJUDE0084.fl
Tenn. River Valley Samples
Pa( 2
2 PFHS <3OT>
fmcoi'PyofOrigin# CsL
tm T '--'niS
0X332 \
Report 02-0443
F il*: \SEtstarg*t\t*rttSc)wSdtid*,ir.iM)OZO812A.bMUl)E0O86.9 3 PFOA <413)
Tenn. River Valley Samples
Pat* 3
4 FOSA (498) B PFCS <499)
ftn c i Copy o; Origyihn,ci
n ( LllLiT-
Fn;t!a!
iteto
001933
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D0208l2B.b\DUDE0l27.D Page l Report Date: 29-Aug-2002 07:12
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file : \\Btstarget\target\chem\dudejr.i\D020812B.b\DUDE0127.D
Lab Smp Id: 38028
Inj Date : 13-AUG-2002 10:35
Operator : cmc
Inst ID: dudejr.i
Smp Info : E02-0443-38028; Water Samples; non-GLP; 7/17/02; OK
Misc Info :
Comment :
Method : \\Etstarget\target\chem\dudejr.i\D020812B.b\D020812B.m
Meth Date : 29-Aug-2002 07:08 dudejr.i Quant Type: ESTD
Cal Date : 13-AUG-2002 06:44
Cal File: DUDE0106.D
Als bottle: 41
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Ooapoundi 1 SPSS <i>
2 PPH3 (]>*) 3 p f o a (411) 4 POSA (4*1) S pros (4*1)
QUANT SIO NASS
299 299 299 299 299 299 299 413 494 499
CONCENTRATIONS
QN-COLUMN PXNAb
RT BXP RT DLT RT R8SMNSI
(ng/aL)
(ng/aL)
3.31 2.497 3.073 3.777 4. OIS 4.249 3.777 3.942 4.741 4.140
3.394 3.394 3.394 3.394 3.394 3.394 3.791 3.9S2 4.744 4.140
-0.004 -0.497 -0.321
0.3S3 0.491 0.454 -0.014 -0.020 -0.027 -0.020
195304 943
9274 1440
402 439 7474701 34 4 43 02 4025349 7427444
2924.40 2934.44 2935.29 3935.33 2935.49 2935.70 392.549 314.424 302.105 341.743
3930 2940 2940 2940 2940 2940
392 344 302 342
!:>FIGVCti
c#*
001934
Report E02-0443
Data F ila: SSEfcfcar{t\tarjt\ch*Sdudjr.l\D020812B.bMUDE0127,D
Tenn. River Valley Samples
Paja 2
2 FFHS (399)
-.aut Cos j o; CiiginaJ
Date
0193S
Report E02-0443
Data F ila : S\Ettare#t\tarcttSchaaNdudtjr. 1SD020812B. b\DUDE0127. S 3 PFOft <4131
Tenn. River Valley Samples
Pact 3
4 FOSA <4901 B FFOS <499)
.'.VaICt LOfjy ;17Oriofngl
fa/io/?--
00X93G
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudej r .i\D02082B.b\DUDE0133.D Page 1 Report Date: 29-Aug-2002 07:12
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020812B.b\DUDE0133.D
Lab Smp Id: 38036
Inj Date : 13-AU6-2002 11:41
Operator Smp Info
: :
mla E02-0443-38036;
Water
Inst ID: dudejr.i Samples; non-GLP; 6/20/02;
OK
Mise Info :
Comment :
Method : \\Etstarget\target\chem\dudejr.i\D020Sl2B.b\D0203l2B.m
Meth Date : 29-Aug-2002 07:08 dudejr.i Quant Type.- ESTD
Cal Date 13-AUG-2002 06:44
Cal File: DUDE0106.D
Al s bottle: 43
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Cofound 1 m a (a>
2 anta (>) 2 PFQA (413) 4 POSA <> 5 p r o s (.)
QUANT 813 HASS
399 299 399 399 399 399 413 499 499 499
CONC8NTRATXON8
ON-COLUMN FINAL
AT SXP RT DLT RT HRSPONS8
(ng/aL)
(ng/mL)
3.399 3.073 3.777 4 095 4.342 3.771 3.9C3 4.735 4.133 3.932
3.394 3.394 3.394 3.394 3.394 3.791 3.993 4.799 4.190 4.190
>0.009 -0.321 0.393
0.991 0.949 -0.020 -0.020 -0.033 -0.027 -0.339
302053 19005 9501 930 917
9071912 3927039 9559553 71*0357
909
2929.29 2934.99 2935.39 2935.99 2935.99 404.170 399.497 324.535 395.295 3071.35
2930 2930 2940 2940 2940
405 399 324 395 3070
Braci Copy or C 'jir-..
.XJLC
initial
001937
Report E02-0443
Qt* F il : \\Ettar-t*tSt*rt*lSch**\du<iJr.iMW20812S.bM)UDE0133.D
Tenn. River Valley Samples
P*C*Z
1 PFBS (299> 2 PFHS <3>
B cbctCopy of Orfclna'
! L LOi/joJfru
001938
Report E02-0443
Bata F it: S\EUtar*atVtarjtSc*aa\dudajr.iVJ>030812B.b\DUI>e0133.D 3 PFOA (413)
Tenn. River Valley Samples
B PFOS (499)
CuiL. /^((isu .W;
001939
Report E02-O443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\dudejr.i\D02082B.b\DUDE0136.D Page 1
Report Date: 29-Aug-2002 07:12
3M Environmental Laboratory
E02-0443, Tenn. River Valley Samples
Data file : \\Etstarget\target\chem\dudejr.i\D020812B.b\DUDE0l3S.D
Lab Smp Id: 38040
I.nj Date : 13-AUG-2002 12:14
Operator Smp Info
: :
mla E02-0443-38040;
Water
Inst ID: dudejr.i Samples; non-GLP; 6/20/02;
OK
Mise Info :
Comment :
Method : \\Etstarget\tarcet\chem\dudejr.i\D020812B.b\D020812B.m
Meth Date Cal Date
: :
29-Aug-2002 13-AUG-2002
07:C8 06:44
dudejr.i
Quant Type: ESTD Cal File: DUDE0106.D
Als bottle: 44
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist:all.sub
Target Version: 4.12
Compound* 1 PFBfl Iasi)
2 FFH9 (3) 3 PPOA (411) 4 POSA (4SI) 5 pros (4*4)
QUART 9H3 MA99
399 299 299 299 299 299 413 499 499
C0NCRNTRATX0M9
OR-COLORI* FINAL
XT KXP RT DXiT RT R U PORSI
(ng/aL)
(ng/aL)
3.297 3.936 3.073 3.932 4.023 3.777 3.991 4.741 4.132
3.394 3.394 3.394 3.394 3.394 3.791 3.9ta 4.74 4.140
-0.007 -0.454 -0.331
0.434 0.439 -0.014 -0.021 -0.037 0.024
200230 5435
13145 10649
44$ 4244279 3997S4S 795SS92 776002S
2926.37 2936.47 2935.11 2935.33 2935.70 416.475 407.549 299.205 354.040
2930 2940 2940 2940 2940
416 404 299 354
issaci- Ccpy of Origina.'
fox* fcs]
Oato
0019^
Report E02-0443
D*ta F lit: SSEttarcttSttrcttSehtnSdudtlJr.lS0020812B*bSDUlOt36D
Tenn. River Valley Samples
p*gv 2
i 1t
i
ii
t
1 PFBS <299)
'J;2CU/p vilgii^ teaj jai.-
001941
Report E02-0443
Seta F il t SSEtstarsetStarfat\ehe*SdudaJriSD024812BbSDUDE0136.D 3 PFOA (413)
Tenn. River Valley Samples
Pag 3
4 FOSA (498)
8 PFOS (499)
BaciCo,'-;-.-.: f:-;-
001942
Report E02-0443
: ^ Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\itchy.i\l021112.b\ITCHY034.D Page l Report Date: 19-Nov-2002 14:49
3M Environmental Laboratory
Data file : \\Etstarget\target\chem\itchy.i\1021112.b\ITCHY034 ,D
Lab Smp Id: 0443-WB-l
Inj Date : 12-NOV-2002 13:40
Operator Smp Info
: mla : E02-0443-WB-l;
Water
Blank;
Inst ID: itchy.i MeOH Extract; 21 Oct
02;
MLA.
Misc Info :
Comment :
Method : \\Etstarget\targBt\chem\itchy.i\I021ll2.b\I0211l2.m
Meth Date : 13-NOV-2002 09:IS itchy.i Quant Type: ESTD
Cal Date 12-NOV-2002 12:14
Cal File: ITCHY026.D
Als bottle: 21
Dil Factor: 1.00000
.Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Compound*
i 1 pros U*J
2 PFH8 <3> 3 PPOA (411)
4 TOSA (>> S PPOS (4)
Q vw r axe HASS
39 399 399 399 413 413 49 499
GOMCmZIUiTZONS OM-OOUJMM fimi RT RXP RT DLT RT RESPONSI ing/mh) (ng/mL)
3.421 3.353 4.129 3.940 4.039 4.341 4.157 4.209
3.422 3.422 3.422 3.130 4.020 4.020 4.157 4.199
-0.001 -0.170
0.707 0.010 0.019 0.320 0.000 0.010
37974 7025 7365 2S41
13412 10374
1927 70922
0.55035 932.500 933.490 0.13306 744.74 745.050 0.17215 1.09119
0.560 933 933
0.133 746 745
0.172 1.09
~T/r
ClttL jj/tnSfia]
001943
Report E02-0443 Data Fila: \\Efc*tarct\tarefc\ch'atchy.M021112.h\ITCHY034,D
Tenn. River Valley Samples
2 PFHS <399>
Ion 399,00
i 1.00
I/rl l
"1A 0 .9 0
11 /
g .SO
%$F0,70 ( \ a /
> 0.60
// ^
0 .5 0
-3-.4-0---3-.6-0 Hi3n_.80__4.0_0__4.20---
wacrcupy:;.- _j;
is ir V *f '
01(1944
Report E02-0443
Sa ta F ila i S\E ttariatStarcatSehai\lte*m ,i\IM 1112.bSITCH Y034.D
3 PFOA (413)
Tenn. River Valley Samples Pag 3
4 FOSA (499)
B PFOS (4 9 9 )
4 . ^ lief6101*4345
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\itchy.i\1021112.b\ITCHY035.D Page 1 Report Date: 19-Nov-2002 14:49
3M Environmental Laboratory
Data file \\Etstarget\target\chem\itchy.i\l02iii2.b\ITCHY035.D
Lab Smp Id 0443-WB-2
Inj Date 12-NOV-2002 13:51
Operator mla
Inst ID: itchy.i
Smp Info E02-0443-WB-2; Water Blank; MeOH Extract; 21 Oct 02; MLA.
Misc Info
Comment
Method
\\Etstarget\target\chem\itchy.i\I021ll2.b\I021112.m
Meth Date 1 3 -Nov-2002 09:16 itchy.i Quant Type: ESTD
Cal Date 12-NOV-2002 12:14
Cal File: ITCHY026.D
Als bottle 22
Dil Factor 1.00000
Integrator Falcon
Compound Sublist: all,sub
Target Version: 4.12
Cowpound* 1 ? n a la)
a PPHS <> a PPGA (413) 4 POSA (491) S PPOS (499)
q u a n t sicNASS
39 39 399 399 39 413 413 49 49
coN cnm urxoM S
O N -counuf FINAL
RT RXP RT DLT RT RESPONSI
(ng/nL)
(ng/mL)
3.411 3 .353 4.119 3.930 3.491 4.039 4.34 4 .47 4.319
3.433 3.433 3.423 3.930 3.930 4.030 4.020
4.997 4.199
-0.011 -0.170 0.997 0.000 -0.33 0.009 0.32
0.000 0.020
-32544 5959 3295 3529 1344
14593 12055
3453 42341
0.39735 933.530 933.507 0.15642 0.10734 0.04324 744.949 0.19434 0.23530
0.397 934 934
0.155 0.107 0.0432
745
0.194 0.236
001946
Report E02-0443
Data F ila t \ \E ttarja tS tar*atSch aa SI tehy. 1S1021112.bSITCHY03S. D
Tenn. River Valley Samples
Paca 2
2 PFHS <399)
& a ci Copy x Odgi
J
t
001947
Report E02-0443
Data F ila : S \ E t * t * r tchy, iSI021112.bSITCHY03B.D 3 PFOA (413>
Tenn. River Valley Samples
Pat* 3
4 FOSA <496>
H<acf Copy of Original
001948
Report E02-0443
Tenn. River Valley Samples
Data Pile: \\Etstarget\target\chem\itchy.i\I021l2.b\ITCHY038.D Page 1 Report Date: 19-Nov-2002 14:49
3M Environmental Laboratory
Data file : \\Etstarget\target\chem\itchy.i\l021112.b\lTCHY038 .D
Lab Smp Id: 0443-38044-1
Inj Date 12- NOV-2002 14:23
Operator : mla
Inst ID: itchy.i
Smp Info : E02-0443-38044-1; SL-1; MeOH Extract; 21 Oct 02; MLA
Mise Info :
Comment :
Method
\\Etstarget\target\chem\itchy.i\l02lll2 .b\I021H2 ,m
Meth Date : 13-Nov-2002 09:16 itchy.i Quant Type: ESTD
Cal Date : 12-NOV-2002 12:14
Cal File: ITCHY026.D
Als bottle: 25
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
v** Target Version: 4.12
Compound* 3
t
1 m a (299)
2 PPHfl (399)
3 PPOA (413)
4 POSA (494) 5 PPOS (499)
QOJU9T 813
NWB
299 299 299 399 399 413 413 491 499
a a
1
a a
a
a a
!1 a> 1 ; a
RT BXP RT DLT RT RiaPOMSR
a
a a
:
a
11
a a
3.511 3.970 4.309 3.940 3.432 4.040 3.701 4.997 4.219
3.422 3.422 3.422 3.930 3.430 4.020 4.020 4.4C7 4.199
0.049 0.544 0.447 0.010 -0.394 0.020 -0.319 0.020 0.020
313459 2S93 4144
132C3S 14909
295590 4211
1250415 2745277
COMCSMIMTIONB N-C01HN PINAL
(ng/aL) (ns/b)
.......
10.5974 933.427 932.592 2.71999 0.49492 14.1949 745.144
10.4 934 934
2.73 0.445
14.2 745
29.4711 47.4542
29.7(1*) 47.4(H)
QC Flag Legend
M - C o m p o u n d re s p o n s e m a n u a lly in t e g r a t e d .
B a c i Copy or Original
001949
Report E02-0443 Sata Fil*; S\Et*fcarffcSfcart*tXeh\itchy,l'\lG2111.2.bMTCHY038,D
Tenn. River Valley Samples
Pat* 2
1 PFBS <299) 2 PFHS <399)
wtOWKOrsi
001950
Report E02-0443 lu t * Pi U t SSEt*t*rt*tSt*rtt\ch*nSi teTia.iSI*2H12.b\ITCHY038.D
Tenn. River Valley Samples P l{ 3
4 FOSA (4 9 8 )
B PFOS (499)
oeci Ccay of Orig na*
C `'mna-:j x 'M--j:.;- p -'
U01S51
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\itchy.i\l021ll2.b\ITCHY040.D Page 1 Report Date: 19-Nov-2002 14:49
3M Environmental Laboratory
Data file : \\Etstarget\target\chem\itchy.i\l02lll2.b\ITCHY040 .D
Lab Smp Id: 0443-38044-2
Inj Date : 12-NOV-2002 14:45
Operator : mia
Inst ID: itchy.i
Smp Info : E02-0443-38044-2; SL-1; MeOH Extract; 21 Oct 02; MIA
Mise Info :
Comment :
Method : \\Etstarget\target\chem\itchy.i\I021112.b\l021112.m
Meth Date : 13-Nov-2002 09:16 itchy.i Quant Type: ESTD
Cal Date : 12-NOV-2002 12:14
Cal File: ITCHY026.D
Als bottle: 26
Dii Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
4II Target Version: 4.12
COtKBRMTIOMS
QOAMT SZG
OM-COLONM PIMM.
Compound
MASS
K t BXP RT DLT RT RSSFOS08 (ng/ab) (ng/aL)
l pros <2l
2 PFHS (3M>
3 p p o a (413) 4 POSA (4M) S PPOS (4M)
299
3.432 3.422 0.010
393409 10,5904
10.4
299
3.970 3.432 0.549
1970 933.945
934
299
4.309 3.422 0.447
<2491 1.29471
1.27
399
3.940 3.930 0.010
111901 2.93937
2.94
399
3.432 3.430 -0.394
13479 0.37475
0.377
413
4.040 4.020 0.030
290003 14.1091
14.1
413
3.711 4.020 -0.309
9504 745.093
745
494
4.9S7 4.497 0.020 1341450 32.3550
32.4
499
4.219 4.199 0.020 2445124 70.2517
70.2(H)
QC Flag Legend
3 M - Compound response manually integrated. 43
../icfiru
001952
Report E02-0443 Dt F i U s SSEt*fcarstNfciri*fc\ch*Mtehy.l\I02ill2.bMTCHV040.J)
Tenn. River Valley Samples
PH 2
2 PFHS <399)
Exact Copy o; Origini.
> fffifeaJ
fe T
001953
Report E02-0443
D a ta F ila : S S ts ta rc a tS ta rta tS c h a a M te h y .lS I0 2 1 1 1 2 .b M T C H Y 0 4 0 .D 3 PFOft <413
Tenn. River Valley Samples Pac* 3
4 FOSA <498 B PFOS (4 9 9 )
' i-V v ;>? Orfgna
C M C ljiU u
0019jp4
Report EQ2-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\itchy.i\I021ll2.b\ITCHY042.D Page 1 Report Date: 19-NOV-2002 14:49
3M Environmental Laboratory
Data file : \\Etstarget\target\chem\itchy.i\I02ili2.b\lTCHY042.D
Lab Smp Id: 0443-38044-3
Inj Date : 12- NOV-2002 15:07
Operator : mla
Inst ID: itchy.i
Smp Info : E02-0443-38044-3; SL-1; MeOH Extract; 21 Oct 02; MLA
Mise Info :
Comment :
Method : \\Etstarget\target\chem\itchy. i\I02H12.b\I021H2 .m
Meth Date Cal Date
: 13-NOV-2002 : 12-NOV-2002
09:16 12:14
itchy.i
Quant Type: ESTD C-al- File: ITCHY026.D
Als bottle: 27
Dii Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
i
t
A
Oompounda
1 m a (3)
2 FFHS ( 3 * 9 )
3 n o A (4X3)
4 POSA (4 9 ) 1 5 ppoa (499)
QUANT IO MAS
3
299 399 399 413 413 494 499
CONCBMmXXONS
oH -counm
RT BXP XT DXiT XT KX S90N 8I
(ng/*L)
v in a l
(ng/.L)
3 .5 3 1 4 .2 3 .5 4 0 3 .4 3 2 4 .0 4 0 3 .7 0 1 4 .5 5 7 4 .2 1
3 .4 2 2 3 .4 2 2 3 .5 3 0 3 .5 3 0 4 .0 2 0 4 .0 2 0 4 .5 7 4 .1 9
0 .1 0 9 Q .577 0 .0 1 0 -0 .3 9 5 0 .0 2 0 -0 .3 1 0 .0 2 0 0 .0 2 0
452034 50024
111724 19590
253343 5515
1033771 2109105
13.4994 0.59957 2.45445 0 .4 9 9 5 7 13.7201 7 4 5 .1 4 9 34.4535 50.3521
13.S 0 .9 0 0
2 .4 5 0 .5 0 0
1 3 .7 745
24.9(H ) 5 0 .4
QC Flag Legend M - Compound response manually integrated.
feast &jpv ::: u*rOii-.
Cvnc /j/./.fu
0019S
1
Report E02-0443 Sat* Fila: SSEtt*rjt\t*rjet\oh*nSitchy.lSI021112.bSlTCHY042.D
Tenn. River Valley Samples PH Z
2 PFH8 <399>
^ O ricin a]
L m ( ll/jAJt*
0019(16
Report E02-0443
Data F ile : V \ E t*t` t*tStr{tSch*\ltcha.l''I02 1il2 .b M ;T C H Y O 4 2.I>
3 PFOA <413)
Tenn. River Valley Samples
4 POSO <49B>
B PFOS <499)
; '.* V.'lw'lli,
n c ^ IS-J&lsi* t;ll :?*!
001957
Report E02-0443
Tenn. River Valley Samples
Data Pile: \\Etstarget\target\chem\itchy.i\I021l2.b\ITCHY046.D Page 1 Report Date: 19-Nov-2002 14:49
3M Environmental Laboratory
Data file : \\Etstarget\target\chem\itchy.i\l021ll2.b\lTCHY046.D
Lab Sirro Id: 0453-38045-1
Inj Date : 12-NOV-2002 15:50
Operator : mla
Inat ID: itchy.i
Smp Info : E02-0443-38045-1; SL-3; MeOH Extract; 21 Oct 02; MLA
Misc Info :
Comment
Method
\\Etstarget\target\chem\itchy.i\l0211l2.b\l02ili2.m
Meth Date 13-Nov-2002 09:16 itchy.i Quant Type: ESTD
Cal Date 12-NOV-2002 12:14
Cal File: ITCHY026.D
Als bottle 31
Dii Factor 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
1 PPBS *>
2 PPHS (3> 3 PPOA (413)
4 P O M (4M) 5 PP09 (433)
QOMfT SIG NASA
39 39 399 39 39 413 413 413 499 49ft 499 49
CONCBNIMSlOm
OH-COLOMM PINAL
RT BXP RT OUT RT RtSPOtlH (ng/aU
(ng/*M
3.413 3.950
4.30 3.940 3.443 4.040 3.711 4.37 4.ft>7 4.59ft 4.31 4 569
3.433 3.422 3.422 3.030 3.930 4.020 4.020 4.020 4.947 4.967 4.199 4.199
>0.010 0.529 0.997 0.010
>0.399 0.020 -0.309
0.359 0.020 -0.26 0.020 0.369
325254 2272
17131 13341
750 49049
9113 7941 49310 5113 4194S4 11902
9.99037 933.634 933.210 0.36520 0.26651 1.92935 745.115 745.191 1.24672 0.24754 9.07917 1354.25
9.ft 934 933
0.365 0.266
1.93 745 745
1.25 0.249
9.09 13S0
Gre. llltl--
,.:a T fe o
001958
Report E02-0443
Data F ila i SSEfctarcatStartatSehai\itchy,iM02U2.bM.TCHY046,I>
Tenn. River Valley Samples
Paca 2
2 PFHS <399)
an" -^nsl ) 001959
Report E02-0443
Hat F lU t V sE tlw ttS trtt\ ch **Slte h a.lM 0 2 1 il2 .b SIT C H Y 0 4 t.B
Tenn. River Valley Samples
P l( 3
4 F08A (498> S PFOS (499>
SZ2
j-ir;
n,
001960
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\itchy.i\I021112.b\lTCHY048.D Page 1 Report Date: 19-NOV-2002 14:49
3M Environmental Laboratory
Data file \\Etstarget\target\chem\itchy.i\I021112.b\ITCHY048.D
Lab Smp Id 0453-38045-2
Inj Date 12- NOV-2002 16:12
Operator mla
Inst ID: itchy.i
Smp Info E02-0443-38045-2; SL-3; MeOH Extract; 21 Oct 02; MLA
Misc Info
Comment
Method
\\Etstarget\target\chem\itchy.i\l021112.b\I021112 .m
Meth Date 13- Nov-2002 09:16 itchy.i Quant Type: ESTD
Cad. Date 12-NOV-2002 12:14
Cal File: ITCHY026.D
Als bottle 32
Dil Factor 1.00000
integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Compounds 1 PFBS (2*1)
2 PFHS **)
3 PPOA (411) 4 POSA (41) s p ro s (411)
QUANT SXQ NASS
399 399 399 399 399 399 413 413
493 499 499
cohcbwiraxxons
ON-COUMN FINAL
RT EXP RT DOT RT RBSFONS8
(ng/L)
(ng/aL)
3.431 3.940
4.31 3.940 3.441 4.039 4.049 3.710 4.334 4.417 4.339 4.543
3.433 3.433 3.433 3.330 3.930 3.930 4.030 4.030 4.447 4.367 4.199 4.199
0.001 0.633 0.396 0.010
0.399 0.199 0.039
-0.310 0.019
0.350 0.030 0.369
305101 7199
12339 11469 19109 10665 60331
754 44173 4067 323943
6925
9.29129 933.495 933.333 0.33496 0.46773 0.30767 2.61356 745.135 1.19716 0.22171 6.94S39 1354.37
9.29 933 933
0.335 0.469 0.309
3.62 745
1.30 0.322
6.34 1350
UQ1961
Report E02-0443
Data Fllaj SNEtatar|atStartat\ehMSitchy.lM021112.bSITCHV048.9
Tenn. River Valley Samples
Pt2
2 PFHS <399)
CM .
liHH j
001962
Report E02-0443
Data Fil.! S\Etit*ret\UrttSchnMtcha.iM021112.bSITCHV048.D
3 PFOA (413)
Tenn. River Valley Samples
3
4 FOSfl (49S) C PFOS (499)
C Jt
'/cfi
001963
Report E02-0443
Tenn. River Valley Samples
Data Pile: \\Btstarget\target\chera\itchy.i\I02lll2.b\lTCHY05l.D Page 1 Report Date: 19-Nov-2002 14:49
3M Environmental Laboratory
Data file : \\Etstarget\target\chem\itchy.i\l02lll2.b\ITCHY05l.D
Lab Snip Id: 0453-38045-3
Inj Date : 12-NOV-2002 16:44
Operator : mla
Inst ID: itchy, i
Strip Info : E02-0443-38045-3; SL-3; MeOH Extract; 21 Oct 02; MLA
Misc Info :
Comment
Method : \\Etstarget\target\chem\itchy.i\I0211l2.b\I02lll2.m
Meth Date : 13-NOV-200209:16 itchy.i Quant Type: ESTD
Cal Date : 12-NOV-2002 12:14
CalFile:ITCHY026.D
AlS bottle: 33
Dil Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Oowpomid* 1 PPB3 ttll)
a p p H s (31*)
3 PPQA (33)
4 POSA (4*1) 5 PP03 (**)
QUANT SID
NASS --
239 239 299 399 399 399 413 413 413 499 499 499 499
11
81aa
1 1
11t
RT -- 3.402 3.950 4.309 3.720 3.431 4.039 4.049 3.711 4.319 4.997 4.599 4.229 3.930
BXF NT
3.422 3.423 3.422 3.130 3.930 3.930 4.020 4.020 4.020 4.967 4.967 4.199 4.199
OLT ST
-0.020 0.529 0.997
-0.110 -0.299
0.209 0.029 -0.309 0.3S9 0.030 -0.279 0.030 -0.2C9
RESPONSE
........
364599 2069
19956 12125
2424 11470 54999 12405 12569 65769
4044 420495
4S04
C0MC8MTRATI0N9
ON*COLUMN PINAL
(ng/aL)
(ng/aL)
as s
.......
10.0353
10.0
933.642 0.00434
934 0.00434
0.33906
0.339
0.13055
0.130
0.32499
0.32S
2.32242 744.930
2.32 74S
744.915 1.65159
745 1.65
0.22117 9.12623 1354.43
0.221 9.13 1350
i Jr:
001964
Report E02-0443 Data Filai S\EttarcatStarcptSch*MMtchy.iSI021112.bSITCHY061.D
Tenn. River Valley Samples
P*C 2
2 PFHS <3995
'/-/h / t u __
001965
Report E02-0443
Data Filt SSEtstarc*tStarc*tSehMSitcy.iSI021112.bSiyCHY081.D 3 FFOA <413)
Tenn. River Valley Samples
4 POSA <498> 8 PFOS <499)
Q01966
Report E02-0443
Tenn. Rive'Valley Samples
Data Pile: \\Etstarget\target\chem\itchy.i\I02lll2.b\ITCHY053.D Page l Report Date: 19-Nov-2002 14:49
3M Environmental Laboratory
Data file : \\Etstarget\target\chem\itchy.i\l02lll2.b\lTCHY053.D
Lab Smp Id: 0453-38045-MS(3)
Inj Date : 12-NOV-2002 17:05
Operator : mla
Inst ID: itchy.i
Smp Info E02-0443-38045-MS(3); SL-3; MeOH Extract; 21 Oct 02; MLA
Mise Info :
Comment
Method
\\Etstarget\target\chem\itchy.i\l021112.b\I021112 .m
Meth Date 13-Nov-2002 09:15 itchy.i Quant Type: ESTD
Cal Date 12-NOV-2002 12:14
Cal Pile: ITCHY026.D
Als bottle 34
Dii Factor 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
Compounds
1 P P M (299)
2 PPHS (399) 3 PPOA (413) 4 POSA (49) 5 PROS (499)
QUANT 310
NASS
299 299 299 399 413 413 499 499 499
CONCENTRATIONS
ON-COLUNN PINAL
RT EXP RT OIiT RT RESPONSE
(ng/uL)
(ng/aiL)
3.422 3.940 4.299 3.920 4.020 3.991 4.947 4.199 3.920
3.422 3.422 3.422 3.930 4.020 4.020 4.997 4.199 4.199
H
Ml
e
0.000
0.997 -0.010
0.000 -0.329
0.000 0.000 -0.279
1540799 9713
119799 1995S5A
991399 9719
1092919 1295395
2917
45.9349 933.509 2.99093 37.9097 40.2752 745.250 25.9793 29.9191 1354.45
45.9 934
2.95
37. 40.3
745 25.9 29.9 1350
001967
Report E02-0443
SaU F il : NNEtatarjtStartt\chSitchy, iS 1021112.b\lTCH053. B
Tenn. River Valley Samples P a (* 2
2 PFHS <3W >
' ''" `k O C
Oriain!
001$68
Report E02-0443
Data Fila$ SSEtstarc*tStiPt*tSchMMtehy.iM021112.bSITCHY0S3.D
3 PFOft (413)
Tenn. River Valley Samples Pag* 3
9 PFOS < 4 >
001969
Report E02-0443
Tenn. River Valley Samples
Data File: \\Etstarget\target\chem\itchy.i\I021112.b\lTCHY05S.D Page l Report Date: 19-Nov-2002 14:50
3M Environmental Laboratory
Data file : \\Etstarget\target\chem\itchy.i\l021112.b\ITCHY055.D
Lab Smp d: 0463-38046-1
Inj Date : 12- NOV-2002 17:28
Operator : mla
Inst ID: itchy.i
Smp Info E02-0443-38046-1; SL-2; MeOH Extract; 21 Oct 02; MLA
Mise Info :
Comment :
Method : \\Etstarget\target\chem\ itchy.i\I021H2 .b\I021H2 .m
Meth Date : 13- Nov-2002 09:16 itchy.i Quant Type: ESTD
Cal Date : 12-NOV-2002 12:14
Cal File: ITCHY026.D
Al s bottle: 41
Dii Factor: 1.00000
Integrator: Falcon
Compound Sublist: all.sub
Target Version: 4.12
R11
I
Compounds
i pros (39)
2 pros (399)
2 PPQA (413) 4 POSA <49) 5 PPOS (499)
QfOHr SIG HASS
293 299 299
799
299 413 413 411 49 49
. H. .T.
3.S31 4.01 4.319
3. 40 3.423 4.040 3.711 4.97 4.219 3.930
HXP KT
3.422 3.422 3.422 3.930 3.930 4.029 4.020 4.997 4.199 4.19
DLT HT
0.109 0.CS7 0.997 0.010 -0.409 Q.Q2Q -0.309 0.020 0.020 -0.299
RSSPOtfSB
327390 SO09 043
173S3 14192 5337S
72S9 120497 417239
11992
C O M C BN T O A rXO N S
OM-C0L0HN PINAL
Ing/mL)
Ing/mL)
9.9425 933.959 33.471
0.4514 0.39350 2.23055 745.219 2.92155 9.04935 1354.25
9.94 934 933
0.451 0.393
2.23 74S
2.92 9.05 1350
001970
4
0}
Report E02-0443
Data F il; \\EttaritStart*t\ohiSitcha.iM21112.b\lTCHY058.D
Tenn. River Valley Samples
Paca 2
J i r
001971
Report E02-0443
lUt* FU *t VsEtst*rt*t\tM>ttSohM>Sitehy.tsI021112.bSITaQe.S 3 PFQft (413)
Tenn. River Valley Samples
P** 3
4 FOSA <498) B PFCS (499)
?%' WO
001972
Report E02-0443
Tenn. River Valley Samples
Data File: \\Btstarget\target\chem\itchy.i\I021112.b\lTCHY057.D Page 1 Report Date: 19-Nov-2002 14-.50
3M Environmental Laboratory
Data file \\Etstarget\target\chem\itchy.i\I021112.b\ITCHY057.D
Lab Strip Id 0463-38046-2
Inj Date 12- NOV-2002 17:50
Operator mla
Inst ID: itchy.i
Smp Info E02-0443-38046-2; SL-2; MeOH Extract; 21 Oct 02; MLA
Misc Info
Comment
Method
\\Etstarget\target\chem\itchy.i\l0211l2.b\I02lll2.m
Meth Date 13-Nov-2002 09:16 itchy.i Quant Type: ESTD
Cal Date 12-NOV-2002 12:14
Cal File: ITCHY026.D
Als bottle 42
Dil Factor 1.00000
Integrator Falcon
Compound Sublist: all.sub
Target Version: 4.12
Coapounds i w na (
3 WHa (3**) 3 PPOA (413)
4 FOflA (4M) 5 w o a (4>
QOJun s i a
Musa
39 299 299 299 399 399 413 413 413 494 499 499
CONCENTRATIONS
ON-COLUMN fin a l
RT XXP XT DLT RT X B S N M a i
(ng/aL)
(ng/t)
3.511 3.940 4.019
4.319 3.440 3.432 4.040 3.711 4.349 4.447 4.229 3.930
3.422 3.422 3.422 3.423 3.430 3.430 4.020 4.020 4.020 4.447 4.19 4.199
0.049 0.534 0.447 0.497 0.010 -0.394 0.020 -0.309 0.349 0.020 0.030 -0.249
232749 2454 S27Q 7437
14434 10544 35197
7429 12091 103403 393450 12974
4.14254 933.425 933.550 933.444 0.47471 0.30507 1.20373 745.199 744.944 3.52745 4.49144 1354.23
4.14 34 934 933
0.47S 0.305
1.30 745 74S
a . 53(H) 4.49 1350
QC Flag Legend M - Compound response manually integrated.
o.
V |jf .
' J '"f v r/giriai
Ja&
001973
Report E 02-0443
Sata F ilt SSEtstargatNtargatSchaaSitchy.iM421112.bMTCHY057'B
Tenn. River V alley Samples
Pa 2
C n i 001974
Report E 02-0443
Bata F ila : SSEtstargatStar(atSchmSit6hy.iM021112.bMTCHY0S7.D 3 PFOft (413)
Tenn. River Valley Sam ples
Pag 3
4 FOSA C498)
B PFOS (499)
'vCiCWoiOr}3ina! 0019^5
Report E 02-0443
Tenn. River Valley Sam ples
Data File: \\Etstarget\target\chera\itchy.i\I02lll2.b\rrCHY059.D Page 1 Report Date: 19-NOV-2002 14:50
3M Environmental Laboratory
Data file \\Etstarget\target\chem\itchy.i\I021ll2.b\ITCHY059 .D
Lab Strip Id 0463-38046-3
Inj Date 12- NOV-2002 18:12
Operator mla
Inst ID: itchy.i
Smp Info E02-0443-38046-3; SL-2; MeOH Extract; 21 Oct 02; MLA
Misc Info
Comment
Method
\\Etstarget\target\chem\itchy.i\I021ll2.b\I021ll2.m
Meth Date 13- NOV-2002 09:16 itchy.i Quant Type: ESTD
Cal Date 12-NOV-2002 12:14
Cal File: ITCHY026.D
Als bottle 43
Dil Factor 1.00000
Integrator Falcon
Compound Sublist:all.sub
Target Version: 4.12
Compound 1 m s US
3 PFHS U s > 3 PFA (413)
4 POSA (4M) s p r o s (4SS)
QUANT SZ6 HASS
39 399 399 399 399 413 413 413 490 499 49
coM cra nuT ione
ON-COLUMN PINAL
RT EXP RT DLT RT RESPONSE
(ng/aL)
(ng/aL)
3.541 4.090 4.319 3.050 3.433 4.040 3.711 4.369 4.007 4.339 3.930
3.433 3.423 3.423 3.030 3.030 4.030 4.020 4.030 4.067 4.199 4.199
0.119 0.660 0.097 0.030 >0.390
0.020 -0.309
0.349 0.020 0.030 -0.26
420079 6904
11502 25494 17014 40917 ' 0500 11004 133252 470507 14760
11.6624 933.503 933.369 0.62654 0.44417 1.52653 745.145 744.964 3.21070 10.5037 1354.1
11.7 934 933
0.626 0.444
1.53 745 745
3.22 10.5 13S0
B ract Copy x w . --.;
mL
Dfssu
00^976
Report E02-0443
Data F ila : S\EtstarcatStartatSchaaSitehy,iM0211t2.bSITCHY059,D
Tenn. River Valley Samples
Pa(t 2
2 PFHS <399)
t 001977
Report E02-0443
Tenn. River Valley Samples
IUU F ilt SSEUtar?at\tarstSchmSltchu.tSI0ailia.bSITCHY0S9.S 3 PFOA (413)
pe 3
4 FOSA <496>
8 PFOS <499>
1' (ki',y f; Orioii1?'
001978
Report E02-0443
Tenn. River Valtey Sam ples
Attachment D: Sample Prep Sheets, Test Substance, and Test System Information
001979
Report E02-0443
Tenn. River Valley Samples
coi s tid/i 7
_l j / y H3- gy^C
Ter,:Cvntrifuo* >0:
RCF/PRM Readouti3coo
3 ---
Temp " C A Z L
c o n T/Q ji? .3 o < w i (a i l Y i t d - C t t t
Col 7 Spiking Standard 1 0 *
~~l7 _
Approxim ate Cone. 1 p jd rv * Am ount added ^ 0 C.
T/ori n - o a . t m
(p / H ; /t f k i : w
Col i ' T hi*-Mbs'
^ l ^ J a U sio9' a ^ c
G e B^RM Readout ^ 0 .*^ Minute IT S _______Temp *C /Q O
coin
i? n? /{fl-CW l l
coi iaTmnlf.giki. It nX i o i f j vtc WaterID M ill. -fr^ W ^lll?
001980
Col 13 T/DP
I n ICi
ColH T/DPO.AT/W. fa I lOl
.
MeOH10: TN-A 4 5 3 f t \fil
^n f
iff?
Q Tf.flmi/*i-'y/f> jrr.-Ttr+JrJ cil`1
Page 1ote'(y^.1l>Anr C-itT'
-*1W- !!<>*>&) . /*
. (LiD'fM ` ** IlfttPi *'''V
Report E02-0443
Tenn. River Valley Samples
Lab Request i
Tennessee River Valley Samples Sample Location 1, Catfish
VI.
MaMKlige at SOMrcf1er
9
I
1 SL-1. C-1-1 SL-1. C-1-2 S l-1 . C-1-3
n
I 1
i X
I k
s1
5 . 5 /V --
7
5 T 3 ii 1
!
illl i j
li 3
7L A
_r _
i Is
I ill| i i l
7 j i ii
i
1__!S _ A
is
/t r / / -
L
r
r_
I
is
ii 14 \ ,1 $
Hs
SL-1.C-2-1 $ , < p s r
SL-1. C-2-2 SL-1, C-2-3 SL-1. C-2-MS
L
--
n u
.. , a
SL-1. C-3-1
A.
S L-1.C -U T 3
\ ES 1
H
S L -1 ,C -3 -y \ S L-1.C -4-7 SL-1. CM -J
-- iZ 1 "1
J .O D .'i -S c B 1
_s: H ir
N _
SL-1, C-4 ~ t .____. S L-1.C M -M S
SL-1. C-S-1 > d ? 3 0
fe ! i
V X ^3
Ki "<
SL-1. C-5-2
_ V
SL-1. C-5-3
--
~V
53
.3
SL-1. CM-1
li
r
1
11 l . l_ > m
Wt _
> A
s. 2 VJ \
4 " 53 . 2 " T . ^.
.1
d/ 5 z X
rv V
4:
s [C
4
" --s
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3: -L S
T]
. Z _w
^3 O V
_ a i. 1 3 _. 1 1 .
IEL / M/
. 5 . __5
___ !9
SL-1, C-8-2 SL-1. C-6-3 SL-1. C-e-MS SL-1. WB-1 SL-1. WB-2 SL-1, SB-1 SL-1. SB-2
I j
--- --
n.-- ,
n 7--
3 2 . J )- s IZ--
t
Lia
i2A i-
NL
--
~
t \U -
0 ---
___ j
'.A
r~ '
"3
^e
r r [n 1
----
r~ r --
V -
r-- ~
_
-
IlZ -
-
50*coi2Tfl
m
n
lOoo >fi*i./*T**-.n*!f l i . j . ,,
Vji>rCiA\A '
.
Balance ID t t 9 / H Tube tvoe/slza f V y f r y /
<-
C ol Shaker ID J X L S L C _______
Equj Start
I/ J f r ^ L ^ C
cd 3T/tmp'.^ffyvr. /a 11 iO-LAA-C
Equil Stop T r t M jllS a r liia ' fm t
11
* i
W ater ID M U V . - f o T f i C ^ i A
col 4 ___von l-.l'pmh ttl SX. ( f h --wHmL Cois nonT to . > I f t en. CMC.
Centrifuge 10:,
3RCF/PRM Readout ccd
Col non*?.' V/Vrv ( a l i i iC D r.t '~ 'c
Tno*C f~7
C o l7 n n iw in ^a ie n rt.n lm e r~VJ6 3 ~ 7 7
Approximate Clone f ^
Amount added__ICOy L ,
non n.ocn-v la ; /T )
C o l? : T M A -W ^ S '
SM Environmental laboratory
Col to non
h n r lO.a-rnng.
CenklkiaeIpT T "Q ~ 2 -__________
0^PR M R6doul3 C fil^ I i _____ __Temp c 5 3
co in n o n (j >iy >^ y rC. co tnnontMip.vx, h in 2 (_
waterIDIU'iU i-pi T H wAift
Col 13 T lD flMO|'i<n f r r l cl iC X -O ^
cot14nonl',to^iv IcAc\ il,
001981
MeOHID: TN-A, 4 3 - 0 Mi! O u d - ^ n"(U
//J(J^) L i t t rr7ry-/i(fJ.'J f t i ft ! Y "+'L < *r - * 0 4 - 0 1 O tt 0 1
Page 20160) A f ' 7*1,1r, V V } -/* 'X
, < \ _ . T r . '_ t A * , , .
V H f t t t y !/ ;/ t * -
V "W
y v ;* ft
Report E02-0443
Tenn. River Valley Samples
Lab Request:
Tennessee River Valley Samples Sample Location 2- Large Mouth & Location 3-Small Mouth
9
!
1 SL-2. LM-1-1 SL-2. LM-1-2 SL-2. LM-1-3
w
I
t
1 i
i 1 *,
\
J i. . l i 1
2
9 4s
W `` J
A *
"7q
r MS
-------- .
!fi li 1
Jl
y
V
il
il
1r 1 %1
s
II
9 ]B T II S f
li
i l li J ii l i 1
i
10 11 12 19
14
t _J_ vr " 7 ~
r v /<
i
.!
19
SL-2. LM-2-1 J i g V h }
I J
SL-2. LM-2-2
_
__ 1 _
!
SL-2. LM-2-3 SL-2. LM-2-MS
__
-- si
i
3 ._ 4 r? _
.3 .X
_J
SL-2. LM-3-1 J a t J T j
SL-2, LM-3-72 SL-2. LM-3-/J --
SL-2, LM-1-1 C. OTtfo7
SL-2. LM-4 -2
rv.
s
n
SL-2, LM-4 - SL-2. LM-4-MS
--
-- -
/oUHc1SL-3?&?1-1
SL-3?Jhft-2
__
a JC
-
c"
i
~
1
\3
tv
"
_
vV
7<t3 1--
S'S, ",," s 0 J
oV
l ^5
T\** _ i . 1 5
2 z
V
3
Tn
_ ~ 313 33
%' "3 3
_*S_ 0 . o I P I >5
-aJX
t- -S
TZ IE I
'
3
O
I
j V . m i . 1 ?
~_s - L S
~
m m
i i
L
3
'S
t,
s^!
SL-3,^M ^-3
rS L-3.^lt-M S
__ ----.
SP L iL
d L Irp
L
HT
!
\
l> L 3 P 3
Z3M
y.
V 'r5TM f
*\fS*i7j* yc
L <
C o l2 T / D
/ l fa / n / G - ir X f
Col 9 Shaker ID O S T --
Balance ID ^ lO O __________ Tube tvne/tee \tn \l -Vi | 5?s. L
EquM Start T/O /l IK U fr, lb / f r T X l x A
C ol 3 T im U M d /h v f t l 1 1 I O X C/ r l
WaterID H ; 'ii; - a T h e B u s
Equil S lop T/DA/ r cU vw L / IV / > fl-L > v J C ol 10 T/D /l iJ lS s jh ^ t i H ^ I h Q ftV C .
c o la t /d /i ft'.O Q ^ Irv U / O fS l * rJ I^ M d /M llln a ^ 0
CentnfuoelO: 1 t 2 - .
c o i s Tim 7 - l a i l X i D 3 ct v \(
rfCF/^RM ReadoutA D Minuta L Q
Tamo *C 3 o t
Centrifuga ID: | C l
C o in T/D /i k?` s
te / I t \ X Ch rC
RCF/PRM Readout:
Ulnute 0?._______ Temp *C / 7
C ol 12 T /D /l
t i r I 2 / f iA
C ol 6 T/D /l 9 .` 3 0 tte n ( i ! i K l tT)- CK* <
W ater ID H \ U >
T r r ^ lu &
Col 7 Spiking Standard ID # 0 . 3 l ) ^ . i - 7 1
C ol ? T/D /l l l g L / / a J C - / / 4 w
Approxim ate Cone.
Am ount added; t*3L)<A -L-
Col fp TM ,
/! / f 9 r a _ M r A * i4
T/D/l
is /I ST / flL - C lK / 1
Cr-LC tf/n/oi
l T T W A - W i f `'a/tnn L/t XO)-
3M Environm ental Laboratory
M eO H ID : TN-A A p ' - I j L ' , . / j ^ C ^ Q O
( P L v A iiT ry^ ^ t | | /t f J y / ^ l/ i
/IH- (flUfiBX (^J ) L j f t t* T yyt, r~p d tttb j 9h4ofl^1! *('' ,(<Mr rt "-
^ .3 *0 0 * 1 /.^
S fv ?
tv
Report E02-0443
Tenn. River Valley Samples
LabRoquoU:
M
Tennessee River Valley Samples
S a m p la L o c a tio n 2 , C a tfis h
fi
i
t SL-Z 0 1 -1 SL-2. C-1-2 SL-2. 0 1 -3
I
5T 1
1 1
1
1
li
i ili 7I li 23
li 41
li .1
3 o * 3 -fc >
-A
- V 1
--
SL-2. C-2-1 3 e & T j
SL-2, C-2-2
SL-2. 0 2 -3
--
SL-2. 02-M S -- --
1
SL-2. 0 3-1 i f l l l l q C -
SL-2. C - l- r j SL-2. C -3 -/
-- --
Ve_ IN.
S L -2.C -4 -/ A o m SL-2. C -4-J -- SL-2.C-4 -1 ------ SL-2. C-4-US --
^_ .
7" '-
-
\
^-- V. \
X
SL-2. 05-1 SL-2. C-5-2
co tti -------- d
'5
V .^ N s.
SL-2. C-5-3
--
_v _ : > a '^ 5 '
SL-2. C-S-1 J S W f'
SL-2. 0 6 -2
v< "
SL-Z 0 8 -3 SL-2. C-6-MS
----
F -I I v ~
-4 -
. il
SL-2, 07-1 U 1 T S L
.
1 w
A t l: jH K 3E
_ ~__- i.
V. p
3 0
SL-Z 0 7 -2 SL-Z 0 7 -3 SL-ZW B-1 SL-Z WB-2 SL-2. SB-1 SL-2. S8-2
-----a
--------
-- /V O r-- ti
ir T JI
" "1
13
-- ~t
EVL T
i
1
1 ?1 li
l IliI I
i l Wl
i
a ta
T HI
ti *
12 13
14
rA 1 *
1 t
. --{ -
e
Iy
* fR f S is 5
r
q ~T
I s '3
.1 2
M 1
S _
-q / l( . . 2
'N
HI
J S i1
-o
1 - :
j
s _ ._ a 3 %
!1 7
HJ -1
~n
X_ r "
s IF
. 5 T j '
L" X
1 P> '_____ > ~ L
v "1
il
A
\_ A \__ NP
---- ^
. 1 3 5,__r
*
~" ,, ~
T i
P
1T
i
C o U T flM
.U-iD-f& .C&'K
C ol ShakarIP O S ~ ~ J _______
!
12
Satanca ID P C D ________ Tub *
Equi Start T/DB U ` W n / It T / - O - X ,
c o t s t /o/i jy ^ Q p n n [ f i h i C iX C K ^ -
W aterID
~G -T C C ^ - l^
Col 4 T /O /ljfC P ^ V rt 1 0 / H / C kO ^S Q aadH aiH na ( j
Col 5 T/OB
i ( V i C O - C**-C.
Equi Stop T/O BlfATfr , Ip i li7f i ) - 0 \.l Otrv.b-nw.
c o n o t/db II iS jv n j f u fi; m i C iW
CanUUuoi IH; \ f\~Z--___________
(bCjVrMRaadoutSCCO Mtaaaa\Q _Tamp *C,
CarrtrAjoaID
RCF/PRM B m a *
>2________
Mirm laa
_______ Tamp *C
c o in t /db f P fV W / IK~< IS ^ - C n n C
CO112 T/O/l I V O
6 l/T l 0 1
A
*
ili
u*it .
*
's1 j "?e ^ > c N^ J
4 -1 "
V* *r-b7t* VO
_'r>ITja?^S jS1i ^X <5^3
C o l# T IP tf t . X W ( d l l X l f r ' l - Lj * ~ _
Col 7 Spiking Standard 10 f
" 77
Approximata Cone 1 ^ 1 I V t Amount addad IC O
T/O/I U .lP A + i f t '
Col5: TA/yt-^-r V: 3i-\Tvt b h t u iv-c^c
3M Enwonmerwat laboratory
.
v o ta r ID K x V V \ - f a T C l I ^ V jS
Col 13 T/DB
- ) 0 r ^ .. I f / y> *1
00*983
Col 14 T/DB > j 5 f -
< !j,. 1 v y fH
MaOH IO: TH -A c4 5 ~ c ? t^
V i i Q t -3 ^ - `" 'r' J
(T ) L t / ^ t< y. /fl>Ol aJJUr
JhJrJhisp^ (idilli? X--) - MIr/ . Y&Sl
^
Ji'L
Report E02-0443
Tenn. River Valley Samples
Lab Request ,
Tennessee River Valley Samples Sample Location 3, Large Mouth
lu ip ItB
1
!1
1L
1 S9
SL-3, LM-1-1 SL-3, LM-1-2 SL-3. LM-1-3 SL-3. LM-2-1 SL-3. LM-2-2
lJlc 1 V --r
Aonu
~ "T 1
SL-3, LM-2-3 ---- .
SL-3. LM-2-MS --
SL-3. LM-3-1
0
i 17 i l
j !
i| !
il! ! i
48
8
7
hi
._ L
i
SL-3, LM-3-1
SL-3, LM-3-1 SL-3. LM-4 SL-3.LM-4 SL-3. LM-4
SL-3, LM-4-MS SL-3, LM-5-1 SL-3. LM-S-2 SL-3. IM-5-3 SL-3. LM-S-1
-- -_r
OWlo
1 --q -
""
n i > .1 .
-->
V
L--
^T "
S. n.
ientfio \
N. --a 3 N
o
--
h/.< ? %
U
SL-3. LM-6-2
SL-3. LM--3
--j
SL-3, LM-6-MS
--
VJ
\ <S s *; a
IJ
p4
^3 >3
c
SL-3. IM-7-1 > 0 1 ^
SL-3. LM-7-2 SL-3. LM-7-3
--
- A - J f --N
L' Ni '
i
1
jl
P
i I
as !i
!
il ili l a i
i\ S h
Ui ! i
il!
ii
B 8 10 i
12
.JL_ Z / k ..JJLL
\13 U / i\ 1
r>
. -4 - .
5. rA
rj k -O l
-X.
JL
JS .3 \
! s.
V0
cJ
N 'V
4
1' 'S
s n " tw
S
i
\ \
J
V
S
\
\
1 i
1 i 1
'1 '
L > t! -L-
.J l
Col 2
1Ip i n 0 ,3 C U C
C ol 9 Shaker ID 03L3.U
^iD bBalance ID
________ Tube type/sizej)
Equ Start T/Q /l If
{, I l Y l h ) /h q t
, 11
c o i j t /d/i
( ill i O - L ^
Equil Stop TMfrx b iV v t i / Y fi 6 l - i f f d
w a te r ID t u ; i r . - & T t t : M u s
C ol 10 T/Pfl /WS^kM /p / ItC I P X O V iC
C o te t / d / i T o ti* ia ;/ V / O'L Q l'Z L tc a n o t/>
Col s von T.JStV* (o i l l r i (12 O n . c
Cantrtbg ___
Centrifuge ID: | C \~2~
jic )/P R M Readaufc ^ C filN Minute / P
Tem o*C^ - 3
C o in von
t / Hr/ 03-CtviC
RCF/PRM Readout I d M Minute X L C o l* T /D /l9 '? tV n i n I I f f I ffXC ol 7 S p ikin g Standard 10 i f t
Tamp "Cj [ f i
C ol 12T/O/l / ?/S _____ _/_Z/ 0 -3
Water IP M U k-ft 7PC P/o-->
C ol 13 T/D/t ) 5 i O I 9 , J * V t 'J s u t
001984
Approxim ate Cone. I
Amount added
T/D /l \ V.
Iv / 1^
C d Uq- ^DWv b/t'ifcn- rwv_ 3M Environmental Laboratory
C ol 14 T/D/I
/y /X n /^ X ^
vvoA m
-m * -
d ) C l "- r t S *
wer* ip'.lff ii S f p
f t V - 1 ?t
(2) ~
\,7.n-/
f>7rykhu-~i1
wr/-f W~ H ht
!l
kJ Trr-- hi'/r`u7?
Page Sois
Report E02-0443
Tenn. River Valley Samples
Lab Request ;
Tennessee River Valley Samples Sample Location 3, Catfish
a
1
1 SL-3. C-1-1 SL-3, C-1-2 SL-3, C-1-3
f 1 2 l.'W lo
3
1
w
!i
1?
3
k1 i l l i
3 4$
A _ k ,i.
I
/
if P i72a j l i
il II
ilii l I
l i i i l i 11
il
y i t 10 11 12 13 14
_ L 7 7 k " r / s.
7 \ feLe s rtu . 0<
zZ __ n
SL-3. C-2-1 'TirSVf 1
SL-3. C-2-2
I
SL-3.C-2-3 -- SL-3. C-2-MS --
1
1y
I
SL-3, C-3-1 SL-3.C-3-1 SL-3. C-3-1 sua.c-4 SL-3.C-4 SL-3. C-4 SL-3, C-4-MS Sc-3. C-5-1 SL-3. C-S-2 SL-3, C-5-3 SL-3. C-S-t SL-3, C-S-2 SL-3, C-6-3
/.W /r &
----
__ J s
--
i
\ .A . l_
mVlAi
.
4
-VA _ j
- X .- S - I S
Se
-- aiM W ij
*r
x "S
` '
"
t" 1I
_J
v! A O
w
X ~>5
7*
*3
jla
1--
* _
-3
'.Kola
___ 7
- ..3
---
~~
s.
~ 1-- . 3 _c 3
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;
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rA i
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!_ Ti
L- i 7]
_ c .s !_ " " TS .Io
__ :- 1 - 4 777
>v -- 7J
SL-3. C-6-MS ----- .
SL-3, WB-1 -- SL-3.WB-2 -- 5 y |u 2 1 3
r>r vD
SL-3, SB-1 SL-3. SB-2
""
__ i i i
i 1
L L !__ > [ 711
rJ__n__ ____
I
"i
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iE
2
1,
> XT'
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( / i 11 IO O C
C o is Shaker ID _ - o a & L
Balancs ID ^ lO Q ________Tuba typelsizaj
E qui Start T/D41l ' J c fta ( j //& / (S > -f IW C
! 10
.
Col 3 T/DIt I 3 & 0 f i ( { / |1 l O --
M lWater ID
111
T C H mS
c o i4 t/d h T .O Q v * fc
L>
EquIIStop T/Dfl I I ' W f . / t ^ r f L C - ^
C o lio TIDft? .U J p *i
/ f i 0 > 4*1 ( -
CenlrihKM IP: Ig t8*_______
Col S T/Ofl
l i t I OX-c* - c.
( r CF^RM RaeflouL 3 tp Q Mtaul. ( A
Te m e *C _ 3 5 --
CantritUo*10:. < T c . t ~
C o lli T/DO J c y u (g / I t i c o _ g ^ . e
RCFJPRMRaadout^ O U ^ Minuta z-3--
Tu li *C. Q - Q
C o l* TIPif l '
t f l i t I f i A - C tV -C
Col 12Tm o/ ? l9 a
! T l3vl 0 J
WWater ID ri;!h 0 P/,,K Toc a
001985
Col 7 Spiking Standard ID #
*1 ^
Approximate Cone.. ) p p W * \ Amount rid* n \ l l l
T/O/lU a i ^ x _ U . / J L 6 1 K
3U E nw ranm tnui Laboratory
Col 13 TIPO Col 14 T ID I0 9 & 0 ) 6 l 7 * ' ' l M
S ix
9
fl'
MeOH IO: TN-A
5 ^ 7) / V j Us ti) } " i^ lP c ,0 i
Q U & oitiyW- Wton
**? p/f/rv* - /**n 'tK/i7'! V
PlQaSoft 5 c V y ' - / V i - ' s - y - s
jy , . S ty ?
f. .. fi
986T00
Tenn. River Valley Sample
mmausimsomiuo u'**Q*uSo3c-a1n1p3o9u-tHi3-trcH0a064ntVWI ww oootj 301 iwanpaid '1-0OC6 =P1
H i 1 i"ft**
--CIIPM*Mi8<uuttlie3 JWWOPmUa
01**0
*1Tivilursml"t'm*a*uu'm*ynefmA*mU"u"iUT'Tv1OoouOUoouWOocO*WoenoOoOmosO*LWftiilnlUun'ImtsIfo6sHMOr-iu6nanH+O0QaoomOOar13riIrirfufwH1ktwMHna8OooMo0oMOamsM*1ts-4w'aOM0aail>tslB^hin-MKM>mMe'uiI1illi133sMT*3KK3XennnWninIMmuMuruMuSsssSSssSs!
1 1
n T f / O O t l (J)*1*L|03
hJfUi9fTH--fI7'`0v,VfgPlfwAwiuJ-uitfilwernaiu.al
-tiwjfy'f/'PUit.T"7f";"*,~S<>',,.w/i;io V/~4>y<W2VM"Lti'?"Jj)'Ht.Un'ryV3I1Huiu~MIswiao
-
n !
\
lix im
b ^ V)S0V'*VrC/Vitf vati
*0" -- '""fKfe'HfWfg2wf>t0o* aw=pBMm*n3*g
t j * yssA--S-A"Aanm-'1tan'n%>T9*niismnU>ni**tv^`KaS-S/S^SArSS/AsC**T99/7ttLT2'*T77/)^ct^x--i****'7*970-7*>9at7~SssffSASAusSfft~7fLAA*l*lt/tAiLllw*l7">T
Ij 1 !** f
S
l l1 rl
f l i ' i t * I t i ' u >f / i A F'/ ra a ^ w o
'Kj<...V'OTT/'"117 anun lim/Kr iKiJVJStl'm.
4ot- /WJ*utvMiiywn s*j*M/?tc|)W/-7"ysf-Q-XimiWfiYMipotapuuo*Q**pMvWpmVs
u*Wgr ^^Wi'H^VSH-rta wu.
fl
f1l
sA
ffASlnlTt *1ASfSffAAfHSSfllll*il
n
If
li
s\
A
*ffAAS/Sl1lt\1
AffSsll
----AA5flTl----A
ti*
%1
i
f.'l'9/ *"? 1SAfASfAAfnSftAAAsAAslli.ll. j i
""A~AfffAsATf/ASSA7ff>Sl/nlltlll-ri~-"l"TSrsSfAAAfAAAAnff1AfAi.i1?Al.llll't*rrWTiTfU<SIhJ>PiTiffref&r(*ITrrl<fiAr!T"f3kr:7VifA--fn~m*i}ifhTUlu?mlle.3-7-----T---i-J5Tt-cBinTuTr>AiLiW7TMfnCmY7w--sKt1FiTff--A^3TtlMwgt*i*.ft3u->TTWTiT"-r<-'H'T'JJrJiJT?TfJP?fTWttiT-t-
tMSSS'wVPHNVMiiWWMPu>ItmmMiulmHIwiUUUOiiuUWUuiCMdoHu8WnuMBWswMMNnacsVpIFipZnPPifpPWuwMMioMHAliS*Wm*po*ugg'lSSnNU9SuASSoA'*T''A8AAAAaAMAoA'0AAAAo'AAaTA3oHHWn~HHTMUMuHIMoI*iu9Vlr)Mr*I*'''i''TA1111iiliil1ll1iliiimIWB`WmetZM-HnCMntfiiLt*i--^Hincimw>-iMo-mMMpsOrt*Mr-swwt-WaoO3o-fOtoWaOOmwotOtio1lwa>vIeeMKtAtHtn-tTCCC-tceAvcr-ecWwtKm-L-Ct-*W<--CtcMwcmtocCt-zCcCmtw--^wm*ttwwoM>tLM>ocMOt>OuwoW0oK0-0Lowoocw-pooh0-OzZ-->^f-c8-ZO-aCnCZOt8zrtZ0oc^oioWooDoo000l0osmo0n003a3a338a3a3aa3333a33a3i i
r6
^'>1 :pnuum(O3|0PdAi
u&|^ij)X3 dos
ttW K03 _Mqiun(4*P"IS
O -P O -S l ~:pcy*l9PQ
Report E02-0443
Raport E02-0443
'8
1 i
C O 33 O
i U1l
1 to
1
'}
i
6
1 1 >1
I fi
19
B 0
Tann. River VaHey Samples
1 '<*.h33
**
1
"V
Report E02-0443
Tenn. River Valley Samples
Balana ID 900
C ol J TOM (? & >
_ Tuba type/alze. Z )l7 . U (S i M tl
fq d il S tart TOM fd tfil S lop TOM
J i lX ./iU -# h. J I I . V A /> */
^ 0* fJ lV S ^ , {V P ? '
W ater ID A : l l i ' U T0\ C o l4 TOM ( ? V S S
P /u \_________
ff
(fit 7S petd/uttinfl
C ol ST/Dfl IQOQ M
___
C ol 10 T/D /l
l l T ^ l X / l tTh
Centrifuga ID: T 4
(^C{>PRM Readout: ^ 0 0 0 Mlnirtaa /iO
'" ^ yS ^ Tamo *C
Cantrifuga IP: O o t l / % ~ S' ^
C ol 11 TOM / 5 V 3 j / / J a /
y?
-- tR CF/^R SR .adoutK t *
C ol 6 TOM l / O O /)
Minula >.01" r f lA-
Tamp c_ A ,< t O t i )
C ol 1J TOM f."*a^e> '
W ater ID
3 / /J ^ ' l (S iV fH T Q P )^ J
C ol 7 S p ikin g S tandard ID O l O P ' O 1 4 f O i C 1 J
h/'
Approxim ate Cone. V _ _ _ _ A m o u n t added___________
Q l 0 0*1 0 > J O S i , C 5 V " O S S
TOM / H O
)) 1 7 .-i / & "
0
( j ( Z 1 / b / J /JH L - iL / -V iH S L t T 4 (,v id , tv - 4 * / lt 6$ -
3M Erwanmotal laborMory
COM3 TOM
J > lX a f
`'I
C ol 14 TOM
M eO H ID : TN.A / ) 6 t ) 0 6 / V '. '/ l/ 'p J O " ^
d.J
Pagatoli 001988
Report E02-0443
Tenn. River Valley Samples
Prep Date: Analysts initials:
Non GLP SPE Columns Extraction Worksheet
6/20/2002 OK
Method Revision: Study Number
Q
ETS 8Afrfcfr 4 0 1*14-Ititi Vi
E02-0443
Volume of Sample Number sample
or description filtered
water blank E02-0443-38025 E02-0443-38026 E02-0443-38027 E02-0443-38028 E02-0443-38029 E02-0443-38030 E02-0443-38032 E02-0443-38033 E02-0443-38034 E02-0443-38035 E02-0443-38036 E02-0443-38037 E02-0443-38038 E02-0443-38039 E02-0443-38040 E02-0443-38041 E02-0443-38042 E02-0443-38043 E02-0443-38047
40 ml 40 ml 40 ml 40 ml 40 mi 40 ml 40 ml 40 ml 40 ml 40 ml 40 ml 40 ml 40 ml 40 ml 40 ml 40 ml 40 ml 40 ml 40 ml 40 ml
Type of cotumn used
1g, 6 m l, C1B lo t 2057B2
1g, 6m l, C 18 W 2057B2
1g, 6 m l, C 18 to t 20S7B2 1g, 6m l, C1B kX2057B2 1g, 6m l, C 18 Io t2 0 5 7 8 2 1g, 6 m l,C 1 8 lo t 2057B2 1g, 8m l, C 18 lo t 2057B2 1g, 6 m l, C 18 lo t 205782 1 g .6 m l.C 1 8 to t 205782 1g, 6m l, C 18 to t 205782 1g, 6m l. C 18 lo t 205782 1g, 6 m l, C18 lo t 205782 1g, 6m l, C a M 2057B2 1g, 6 m l, C 18 lo t 205782 1g, 6 m l, C18 M 2057B2 1 g .6 m l.C 1 8 to t 2057B2 1g, 6 m l, C 18 lo t 205782 1g .6m l,C ia lo t 2057B2 1g, Bm l, C 18 k it 205782 1g, 6m l, C 18 lo t 2057B2
-- 14- ! t
Amount and Elution solvent and
spike mix used
volume
NA M oOH T N -A -6116 2m l
N A M oOH T N -A -6116 2m l
NA M oOH T N -A -6116 2m l
NA M oO H T N -A -6116 2m l
N A M oOH T N -A -6116 2m l
NA MoOH T N A - 6116 2m l
NA MoOH T N -A -8116 2m l
NA MoOH T N -A -6116 2m l
NA MeOH T N -A -6116 2m l
NA MoOH T N A - 8116 2m l
NA M eOH TN -A -6116 2m l
N A M eOH T N -A -6116 2m l
NA MeOH T N A -6118 2m l
MeOH T N -A -6116 NA
2m l
NA
M eOH T N -A -6116 2m l
M oOH T N -A -6116 NA
2m l
M eOH T N -A -6116 NA
2m l
NA
MeOH T N A -6 11 6 2m l
MeOH T N A -6 11 6 NA
2m l
NA MeOH T N A -6 11 6 2m l
Comments
Extraction Steps (initial when/if done):
C*i,' condition column with MeOH;
wash with milliq;
filter sample;
r K . vacuum dry the column; c K elute column with solvent; o K transfer extract into an autovial
Additional comments:
-If! ,Uc,'f ofe'C - P .cp t iy&czfj
vT-v/ii-j ,>@ 6
b t * r j = n ,'1 < ~ r 'i
b '1 .1
cv .o j y u i , J
$ ,fA'
GtCop'J jD k -
Report E02-0443
Tenn. River Valley Samples
Non GLP SPE Columns Extraction W orksheet
Prep Date:
7/17/2002
Analysts initials: OK
Method Revision: BFS*r15rO- <> .\a litr/t,
Study Number E02-0443
volume ot Sample Number sample
or description filtered
water blank E02-0443-38026 E02-0443-38027 E02-0443-38028 E02-0443-38030
40 ml 40 ml 40 ml 40 ml 40 ml
V
Type of column used
Ig , 6 m l. C16 lo t 2057B2 Ig , 6 m l, C 18 lo t 2057B2
1g, 6 m l, C 18 lo t 2057B2 Ig , 6 m l, C18 lo t 2057B2 Ig , 6 m l, C IS lo t 2057B2
Amount and Elution solvent and
spike mix used
volume
2NA M eO H T N -A -fiM O tC ml {
2NA M e O H T N -A - ttfl 1 ml I
2NA M e O H T H A -S H fl ml
2NA M eOH T N -A -.6 4 ml
2NA M eOH T N -A -U M . ml
Comments
' S s s ''v
\
\
Extraction Steps (initial when/if done):
:ondition column with MeOH; CM wash with milliq: p ^ filter sample; vacuum dry the column; /P K elute column with solvent; pK . transfer extract into an autovial
Additional comments:
g g ) TXi-fw-eao?
r e -`& c h cK ? b 'c tA
._
___
7 ^02.
S>.
E-octCopyc'Ci: / r _ J 2 & l
Initial nL/ui<3
Q ^ fr.ct,^ Wi
1 ** ^ T5
M I** ^ ' / ^ J * '
001990
Report E02-0443
D escrip tion : Date Prepared:
Prepared By:
I
La I ( , * j<
<m__________
_____________
Storage Location: Expiration Date:
3,
f& i
M U LTI-LEVEL PREPARATION LOG
Book No. 02 003
________ _____ Solvent: / I t f i HPa_g_e_N_o_.______5_2
,f jU Ci } 3M Trace f t r3>
Standard ID #
02003-12-1 lu O D M M 02003424 02003434 02003-52-8 02083-824 0200342-7 02003424
Description Cp f O
Component Standard*
D escription V e - 5/:i A lt
ID # Cone ' rJ T C O iio ^ V it. . V f-
E x p ira tio n Date
li/J l/o i
lOOnatK ft',1 ft / f / r
tu e
IQ O fft
k /O i --
1 1 3 .S
Std 1 3 J-- --
Std 2
-- --
S 0 S 5> Am ount o f Com ponent Standard Added
6 0
dse
S td 3 i& u . --
--
Std 4 3 0 1 /L
--
--
Std 5 SOctL --
--
Std 6 IC & U
--
--
Std 7
_
3 , --
Sid 8
--
Sj L
Final Vbltne 6 * ^ Final Coneartntk
I 0 .S s
3 a.
So1 0 3 5
i _ 5 0
D escription
Standard ID #
Description Component Standards
ID # Core
fffk )
E x p ira tio n Date
02003424 0208343-10 0200342-11 020034242 0200342-13 020034244 0200342-18 0200342-18
<00 7 5 l e v a
0.
--
------
Am ount o f Com ponent Standard Added
Std 9 Std 10 Std 11 S td 12 Std 13 Std 14 Std 15 Std 16
IO O .,,t, % ;i. M l/
O io iW i
lh *
A Vo --
1 0 t. --
S x /C --
^ 0uL --
---- ----
-- -- ----
--
--
--
------
--
-- ----
-- ----
Final Volane (n 0 Final ConcatMien ( f f i)
D 5C 0
0
* tooo
0
-- -> -- ----
"l^A^ir.*Cift/j*-
Ravfewod
itfLlOO
SigntureJ
DaiirJ61
Dai
Tenn. River Valley Samples
001991
Report E02-0443
ascription:
Cot K i i (tw r
Storage Location:
M ULTI-LEVEL PREPARATION LOO
Book No. 02 003
Paga No.
54
S o lva n t s J r M
Standard ID #
020QM4.1 02003-64-2 02003-044 0200144-4 02003444 2003444 0200344-7 02003444
Description
Description Component Standards
ID # Cono
(ffi
Expiration Date
I
Std 1
Std 2
5 Jo 2 5 5 o
Amount ot Component Standard Added
Std 3 Std 4 Std 5 Std 6
loo
Std 7
So
Std B
Irtan ^tr^> MlY l M t 0 H Vati-r& t 1I f *
1o o f r
Mir;-, iOH W Q -O tt iOOfmn
--
"/u / 4 /li/c A --
3t/ --
-
5oL
--
--
fBoi >vt --
----
S0vL
--
-
lkit --
-- >1 --
o t-
--
FM Votum 6 L-)
i
o)
i
*
FlraiConontratton {*$^0
I
3 .S
5 l
<35
SO J
<3J
Standen! ID #
D escription
Description Component Standards
ID # Cono
E xp ira tio n Date
lO O jpn lr f lif t M 'O t
0 0 M * Tr
'/)/* >
--
o o o fo o o -- --2003444 0200344-16 0200144-11 0200344-12 0200344-13 0200944-14 0034445 00344-1
S ?5
Q
--
Am ount o f Component Standard Added
Std 9 & u L
--
Std 10 IS ^ L
--
Std 11
--
S U 12 Q uL
--------
SU 13
----
--SU 14 --
--SU 15 --
SU 16 ---
--
--
--
-- ------
-- ----
----
FWaiVolume FndCorrartrattanl ^ 0
Tvon-LuS" uM. j[y|
"i i m.
/Ooo o
lOiSf OtiB
2
Reviewed
---- ----
\'sWJlU
--
------
-------
Rhs-<kOK-_
Vr " *` VR~~
. . Term. River Valley Samples
001992
Report E02-0443
D escription: 'F is*
Storage Location:
M U LTILE V E L PREPARATION LOG
Book No. 02 003
Page No.
SO
Solvent: M e o H
Stnden! ID #
0200340-1 02003404 02003404 82003404 02003404 2003404 0200340-7 02001404
Com ponent Standards
D escription
_________<&)Ju i
ID # Cone
n io > -TR n a rm a -T l lo O y r* A - ---------------
E xp ira tio n Date
iirs lo v
/ fe v
Std 1 IO ,u L .
--------
j- s x tb J s . ~ u
^ > e ^
Am ount o f Com ponent Standard Added
S td 2 5 ^ L
--
Std 3 S O jtL
--
Std 4
--tO O juL
Std 5
Std 6
-- --SSOm U 5 c o > u
Std 7 lOfiL-
--Std 8
JS >L
p m vouma Final Concantnton o n U
_ L j2___ a s -
go
----- V
i sIO s o ID O a r o
D escription
Standard ID #
Description Com oonent Standards
ID # Cone
E xp ira tio n Date
o a o j a - i A - l i t s : __ / V U 3 . OJoaa-33
Fral Vokm FinalConantrmon. o n io
s;82003404 0200340*10 0200340-11 0208340-12 0200340-13 B20034D-U 0200340-19 0200340-19 -7 S & * k
18
C
Am ount o f C< m txw ent Standard Added
\
-- -- --Std 9
S td 10 Std 11 S t
5Cy*<- i 5 * l IOOm L
ISO300
->
\S&Qr
S W l3
Std 14
** S _ -------
/Std 15 Std 16I _4
______ 3
_____ i r
u
BactCopyof Original
S M &iD"91
M U Data
R*viwedbyv Signatur,
. _ Tenn. River Valley Samples
001993
Exact concentration of every point of every analyte
Prao data: f Q T , vui____________
A nalyst F/WC
SoFlivneanlVt &olTumOeAof:eMachr
*
p
\K
o in
t
TNA
-_______f_\______________________
Target analytes: frp iAS. FOSA.
_______________________________________
PBaoooek NNoo::
oaoo]
50
Report E02-0443
Tenn. River Valley Samples
SectCopyof Original
AtA- ONPita
total otoi
*3t
Revtaradby:
Signatur,
01994
Report E02-0443
Tenn. River Valley Samples
r*
I
SINGLE COMPONENT PREPARATION LOG
Date: 1 ) O t l I / O ______ Analyst: / v} i , 1 ____________ _
Book No. 02 050 Page No. 34
IDescription:
A v ,Vt lJ ilts ; P i'ir 'i, Fo>4j p m . fpoj r* pPd s
Stock Number,
n
Weight or Volume Used:
Concentration or Purity:
Corrected Weight
F in a l V o lu m e :
1 , 0 "?,C
Storage Location:
Balance ID:
A/A
Other Correction Factors:
Solvent and TN-A Number. d S T / f /v w i U i / T f r -
( M M r Q . TOC
Final Concentration:
I
Expiration Date:_
I
ExactCopyofOriginal
Initial Caia
Reviewed by:
Signature, /
k / L / k J ' IIA / ^ _
Date
001995
Report E02-0443
Tenn. River Valley Sam ples
Description: Y t f'U . -So? E g
Date Preoared: > ( \ K \ ' i --
Prepared By:_ C M C ___________
Storage Location:_
Expiration Date:
il / ,3 .3 ) 3--*
_MULTI-COMPONENT PREPARATION LOG Book No. 02 002 Page No. 33
Solvent' 3MTrace It. TN-A- fMiw
Description
P F dp. PPSS
Standard ID *
02 002-33
H
Component Standard
ID#
Cone, or Purity
Expiration Weightor
Corrected Weight
Final Concentration
Date Volume Balance ID
O^CCI - n o a c c *-i^
3na P frv'
471#
V i lo - K V -
53/^
'/lt> )t> 3
Nft
?xsx*
IO .0p |Q ^v\
osh.d i- o s 'S' 3 \ 1 3 L
l\ x -U
n m&2o pp*
03LOOI-&M 3 3 c t \
\ V > - .
pprv a j j S '/
\
1 06 ^ pp/Vn
`m s ;
\V ^ 9 .1 M pprrt
___ 1
tl
..... ^
Final Volume
Exact Copy of Original
/H/c
Initial
Dato
Reviewed m
Approximate Concentrationof the irix 1C x ) p p iV \
Signature.
0 0 1/9/ 3 8J u n 0 0
Report E02-0443
Tenn. River Valley Samples
Date:
Analyst
fMl
SINGLE COMPONENTPREPARATION LOG ____
Book No. 02022 Page No. 77
Description: I /vs S ii lL. M f X _______
StockNumber, m r ^ / l ~ 3=^--------------------
Weight orVolume
Used:
Concentration or Purity:
CorrectedWeight
S S O ^l
M 'j'
i f*', k w *
ce ID:
1 - > >
{ /
lD p p n rs_ *? *'' 1^
li tt
M r 11 i~Q T r l uSolventamnd TN-A Number
CL,V
Final Volume:_ r S / n \ ~
Final Concentration:
-ftpm.
Storaga Location:
ExpirationDate: Il j H f O l* -*
Exact Copy ofOrigbid
Ma ^MAM-i
Cats
Reviewed by: Signatura,
Oata
001997
Report E02-0443
Tenn. River Valley Samples
Date;
SINGLE COMPONENT PREPARATION LOG I I S f p j 0 ^ ______
BookNo. 02 040 Pipe No. 80
Description: / %
A r a i r e A a J h / l u b - Q ________
Stock Number
( Z Q & r n V T M 'J - lt l-
Weight orVolume Usetfc__
Concentrationor Purity:_
<n
Balance ID:
A /A -
OtherCorrection Factors:
.
sisA t
CorrectedWeight _
//A
. " " S T M - J } T o e p /u ^ _
Final Volume:_
1)
Final Concentration:
i^
Storage Locatkm:_
y ^ F f r frrp___
ExpirationDate: G ty ) A / A ls f j
& r
Reviewed
001998
Report E02-0443
Tenn. River Valley Samples
Date:
SINGLE COMPONENT PREPARATION LOG
| fOO_________
Analyst:________ OKJ______________
BooKNo. 02 001 PageNo. 17
Description:
7*4 H S
Stock Number
` 0^>G
WeightorVolume Used:
Concentration or Purity:
Corrected Weight:
BalanceID: _____ ^ IM
OtherCorrection Factors:
iJA
Solvent andTN-A
Number H e O H W -A
Final Volume:
Storage Location:
t L c t ja?l
Final Concentration:
7 *5 fp A xj
Expiration Date:______ f-JO-t? 3
ReportE02-0443
Tenn. River Valley Samples
! m 0
i Im
\
a im
Data:______ 1 - fO 'O S
Analyst
06
Description:
SINGLE COMPONENT PREPARATION LOG
Book No. 02 001 Page No. 19
Stock Number
-2 D o a q
Weight orVolume
Used: (p . / / 7 ? cl ---------------------- z r
Concentration or Purity:__
M p a i.
Corrected Weight
M _____________
Balance ID:
Other Correction Factors:
Solvent and TN-A Number
H e O n /m 'A - e s ^ - ^
Final Volume:
cf c 5 u A .
StorageLocatk>n:_
d u d jfcPC
Final Concentration:_______t*-t-
Expiratlon Date:
//fr 0 3
002000
Report E02-0443
Tenn. River Valley Samples
SINGLE COMPONENT PREPARATION LOG
Analyst /j t/F_ _ _ _ _ _ _ _ _ FC K ?FQ5>Description:
Book No. 02001 Page No. 84
Stock Number:_J M M
jd --
w < w " v?r
0 ,. m
Concentration or Purity:
CorrectedWelght:_
^ 5*7FinalVolume:
C
Storage Location:
Other Correction Factors:
Solvent and TN-A\ * t J Number
f P f l i f I* 61
Final Concentration:
0 e/ ^
3 0 3>Expiration Date:
fe b
Exact Copy of Original
/ WU U- Di a/tka i n
Reviewed
t / '/ o .I
003001
Report E02-0443
Tenn. River Valley Samples
a SINGLE COMPONENT PREPARATION LOG
Date:
BookNo. 02001
4 Page No. 85
Analyst_ / V A
________V C - mDescription:_
jP T O A
'Hay*-mi
S tock N um ber^
g>
" w * " vs s ; 0 . 5 7 { 9-
a Concentration or
Purity:
IS 3 &
Corrected W eight
Balance ID:
m.
Other Correction
Factors:
/I O M } 7A/'ASolventand TN-A Number
p
~
7~
Final Volume: .~? . h n L
Final Concentration:_____
S to ra g e L o c a tio n :
D f-
Expiration Date: ,J?S?
Exact Copy of Original
A M - & 0 ib e c i # * -
biitial Date
Reviewed by:
j [ x j-
002002
Report E02-0443
Tenn. River Valley Samples
SINGLE COMPONENT PREPARATION LOG
_ _ _ _ _1/4Analyst / t y
Book N a 02022
Pig* No. 66
Description:
/ I. - T O t t . L s r Z
(C
s s ,< c O
StockNumber. 7C.Q-Mf-}-e>?l / TCK - i i l CMew)
WWghtorVotums
Ueed:
- _^
.5 > % 5 *
Concentrationor Purilv:
n --> o /
y 7 .5 / 0
(7).^CorrectedWeight_____
f
Final Volume:
.Storage Location:
V PI,
Balance ID;
Other Correction Factors;
Solvent andTN-A
m-
Final Concentration:
I1 ; ? f J
Expiration Date:
A 'f r J < 0 3
m
Reviewed uy SignuM^uraJy'tL! P&JsA J' ?Oiatn*J7'L->
002003
Report E02-0443
Tenn. River Valley Samples
Oat: Analyst
SIN G LE C O M PO NENT PR EPARA TIO N LO G
V T tj r\& C~ C M C ___________
BookNo. 02022
PageNo. 79
Description: X ~ C . ( v \ 'v . ( p p y v \ _____ _______________________ __
Stock Number
( g p "O ie > e X - M * . i 0 J
WeightorVolume Used:_____ lO a --
Concentration or Purity:
p p ^
Corrected Weight
Balance ID: W f i
OtherCorrection Factors:
Solvent andTN-A Number V-V OH . T N f l ~ 4 S J O
Final Volume:
ItV rL
Storage Location:
Final Concentratione:-----! ^ J 3 0 Expiration Date:
Reviewed by. Signatura,
0X
Data
002004
Report E 02-0443
Tenn. River Valley Samples
TCR Receipt & General Information
rcR#
TCR-S3
Substance trade name or T B i
reference*:
Substance/chemlcal name: Parfluorohexancsulfonate Primary
std
Lot/batch *:
Location of synthesis,
fabrication, or derivation -acorda:
Molecular Formula:
C6F13S03-K+
Condition:
white powder
Expiration date:
10/18/3000
TCR Substance *
SE038
Received from:
George Moore
Date Received:
09/03/1999
Amount received (wt orvol): 154 0,277.38 g gross w t
Number/size of containers: Shipper MSOS (y/n)
1/150 mL glass container
Courier
Y <J N
Purity:
98.6% LAC 01/17/01
3M # Entered by (Initials) LAC Std Location/Storage
N B 120067-89 Date Entered 09/03/1999
Initials
Records received:
Checked By Date
MSDS, NMR Characterization Request*69085 Interim final report bom Centra and Certificate of Analysis. LAC 04/26/01
Date
Checked by (Initial/Dale)
F19, Frozen Amount of Retain
0.3610 g
Initials
Date 10/19/1999
Checked by (Initial/Date)
Comments
Standard has been moved to Freezer 19 in room 347 KJD 06/08/00 Sent to Centre Analytical for Certificate of Analysis
Analysis on 07/06/00 LAC 07/31/00 Standard was stored at room temperature prior to 06/06/00. LAC 12/19/00 Shipping Codes: 41-2600-9459-8. LAC 06/14/01 Original label - 8/4/99 RWW-11/2/01
Initials
Shipping com m ents: NOT REGULATED, 311 shipping ID
41-2700-4647-3.
LAC 01/104)2
Attachments
Date
Checked By Date
ase036m sds.pdf se036nmrreq59085. pd
E00-1878-COA-SE036-PFHS-R "O Archlved/Substance Not Avajlablej
002005
Report E02-0443
Tenn. River Valley Samples
rcR*
Substance trade name or reference #: Substance/chemical name:
lo t/b atch * Location of synthesis, fabrication, orderivation records: Molecular Formula: Condition: Expiration date:
Purity:
3M # Entered by (Initials) LAC Std Location/Storage F19, Frozen Amount of Retain 0.2233g
TCR-29 PFOSA
TCR Receipt & General Information
TCR Substance #
mi
Perfluorooctane sulfonyl amide or Perfluorooctanesulfonamlda AC KJD 7/24/00 L-15709
Building 236
Received from:
R. Buckanin
Date Received:
04/20/1999
Amount received (w t or vol): 124.98g
gross w t
C0F17SO2NH2
Number/size of containers:
light yellow waxy solid MCH 07/22/99 Shipper.
10/31/2006
MSDS (y/n)
TBD, KJD 06/05/00
Records received:
NA Data Entered
Checked By
1/100 mLglass container Road Runner yon MSDS, summary page of FID analysis 57915
Date
Initials
Data
Checked by (Inkial/Date)
Initials
Date 10/18/1999
Checked by (Initial/Date)
Comments
Initials
Gross weight difference due to removal of parafilm LAC 04/28/99 Standard has been moved to Freezer 19 In room 347
KJD 06/06/00 Standard was stored at room temperature prior to
06/06/00. LAC 12/19/00 The expiration date was assigned based on hydrolysis study EL-1132 and photolysis study W2783 which showed this compound to be stable. LAC 10/31/01 Original label dated 3/18/97 - RWW 10/25/01 Shipping Comments: NOT REGULATED, shipping code
-LB-I000-1S70-S. L-15709. LAC01/08/02
Attachments
Date
Checked By Date
sd029msds.pd sd029fid57915.p
;Ci rchlved/Substance NotAvailable
002006 /
Report E02-0443
Tenn. River Valley Samples
rcR#
Substance trade name or reference#: Substance/chemical name:
Lot/bateh#: Location of synthesis, fabrication, or derivation records: Molecular Formula: Condition: Expiration date:
Purity:
3M# Entered by (Initials) KJD Std Location/Storage F19, Frozen Amount of Retain 0.2737 g
TCR Receipt & General Information
TCR-123 PFOA (POAA)
TCR Substance #
TCR-ifigd-oSa
FC-143 Ammonium Perfluorooctanoate (Primary Std) 332
3M
Received from:
N/A
Date Received:
02/02/2000
Amount received (wL or vol): 278.20 g gross wL
C7F15COO-NH4+ White powder KJD-2/2/00 10/31/2008 95.0% LAC 01/17/01
N/A Date Entered
Initials
Initials
Number/size of containers: Shipper USDS (y/n)
Records received:
1/ -200 mL glass bottle
Unknown Y( )N
MSDS Interim final report from Centre and Certificate of Analysis. LAC 04/26/01
Checked By
Date
Date
Checked by (Initial/Data)
Date 02/17/2000
Checked by (Initial/Date)
Comments
Initials
Was originally TN-A-2143, KJO 2121/00 Standard has been moved to Freezer 19 In room 347
KJD 6/6/00 standard was weighed on 9/28/00. Standard was
stored frozen at -20C+/-10C until shipment on
10/03/OO.LAC 10/03/00 Shipping Codes: 98-02114)891-9/FC-S000-0192-0(00 g on dry Ice) LAC 08/14/01
Standard stored at room temperature prior to 6/6/00
LLAabCe-l1-2r/2e8c/o0r0ded-10/98 RVWV-11/8/01
Shipping comments: REGULATED-TOXIC Dangerous goods In excepted quantity of Class 8, UN2811.3M Shipping ID: 98-0211-7394-7, (4 lb. carton) fully regulated. LAC 01/09/02_________________________
Attachments
Date
Checked By Date
tcr99030-30msds.pdf
*
EOO-1763-COA-99030-30-P FOA-R
Archived/Substaiice Not Available |
002007
Report E02-0443
Tenn. River Valley Samples
rcR*
Substance trade name or
reference #:
Substance/chemlcal name:
Lot/batch #:
-ocatlon of synthesis, fabrication, or derivation records: Molecular Formula: Condition: Expiration date:
Purity: 3M *
Entered by (Initials) KJD
Std Location/Storage F19, Frozen
Amount of Retain 0.18670
TCR Receipt & General information
TCR-129 PFOS
TCR Substance#
TCR-fiOSJ-Od
FC-98
Received from:
Potassium perfluorooctansultanato
N/A
AC KJD 7/24/00
215
Date Received:
02/02/2000
N/A Amount received (w l or voi): 40.1441 g gross wL
C8F17S03-K+ whit powder 12101(2010 TBD.KJD Sismo N/A
Data Entered
Initiate
Initiate
Number/size of containers: Shipper MSOS (y/n)
Records received:
1/ 80ml nalgene bottle N/A yU n
MSDS
Checked By
Date
Date
Checked by (Initial/Oate)
Date 02/17/2000
Checked by (Initial/Date)
Comments
initials
Was originally TN-A-2144, KJD 201/00 Standard has been moved to Freezer 19 In room 347 KJD 6/6/00 Shipping Codes: FC-SOOO-0185-6(<30 g on dry Ice) LAC 96/14/01 Standard wae stored at room temperature prior to 8/6/00 LAC 12/26/00 Received 5/96 RWW11/8/01 Shipping Comments: Dangerous goods in excepted quantity of Claes 6, UN2B11. REGULATED-TOXIC 98-0211-0808-6 (>30 g (1 oz
tempi)) Not on dry lea. LAC 01/08/02
Mtachments
Date
Checked By Date
tcr99030-36msds. pdf ,0 Archived/Substance NotAvailable j
002008
Report E02-0443
Tenn. River Valley Samples
rcR#
Substance trade name or rfrence#: Subetance/ehamical name:
Lot/batch #: Location of synthesis, Fabrication, or derivation records: Molecular Formula: Condition: Expiration date:
Purity:
3M # Entered by (Initials) KJD Std Locatkm/Storage Freezer F-19, frozen Amount of Retain 0.282 g
TCR-ffiJ PFB3
TCR Receipt & General Information
TCR Substance *
TCR-00017-071
Potassium perfluorobutane sultanate 2
Wildlife
Received from:
Wildlife
Data Received:
06/30/2000
Amount received (wt or vol): -100 g, 121.6288 g gross w t
C4F9S03-K*
good/ fluffy white crystals
01/17/2007 97.3% LAC 04/26/01
L-7038 LAC 01/03/01 Date Entered
Initials
Initials
Number/siza of containers: Shipper MSOS (y/n)
Records received:
1/ -100 mL plastic container unknown vO n
MSDS Intarim final report from Centre and Certificate of Analysis. LAC 04/26/01
Checked By
Date
Date
Checked by (Initial/Date)
Data 06/30/2000
Checked by (InWal/Oatel
Comments
Wildlife International Number 8292 KJD 6/30/00 Standard is being stored In Freezer F-19 at -20C KJD 7/17/00 Formula added on 07/24/00 by KJD Sent to Centra Analytical for Certificate of Analysis Analysis on 07/08/00 LAC 07/31/00 By F-11926 process LAC 01/03/01
Shipping comments: NOT REGULATED, (based on shipping code of LB-1000-0703-8). LAC 01/10/02 A ttachm ents
Initials
Date
Checked By Date
tcr00017-71msds.pdf tcr00017-71Iotinfo.
E00-1877-COA-00017-71-PFBS-R i^O' re h iw ^ u ^ n ' Ncrt.
03$
0QS009
Report E02-0443
E N T- R
O l- O th l
S M fV j
n -i
Atlanta Goleta Wihninton
Boston
H ouston
_
D ates Okemos Walnut Creek
Dearborn Olympia
East Greenwich Sacramento
Edmond Tacoma
CHAIN OF CUSTODY AND ANALYTICAL REQUEST RECORD
Page -
Gig Harbor Ventura
------------ " *----- Jw rjtant:
_________ & * * 1 ------------------- - --y ------- ,--------------
ProtectKlo. I 7 Q 0 \
t w a l y t i o l V q u e s t ____________________ 1
Sample ID
M .Q & W r
Akbfll No
''Pi
Data
Time
Comp Grab
No. of Con
Sample / 1 i i r l
Meda / v j V / /
i
/
li / / / / / /
//// I / i /
Commenta
* bW O\
v jo i --0w 0 V s W O I- L ol/ A
S W fll -M e ri P S C l -- Lid P S C o i-fja d 'fib
rp v ii
Sv o3a
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X i W^i' *
fi i
fi i
Xi Xi
11 M
.
I L|3>C \\ II
X i V/ yX/ j-- r . i
i & r
i VeA
fio o
X
Total NumberofContainers
\
V
'ig o z s i*o z & l& o x i3&Zg iK o z I 1XQ 2&
3SO 1
3 *0 3 2
t e r buyj viWHn ^ bhf
Reinquiahed By
Data Tima _ /
RecabadBy *"***** *****
Dale Time
w / (n
_____________ -
iSa
ftJ + J
'C T ^ r - f n m
-r- r \
., V
? ..
i ficto.
FO R M * CNT-1S1
. _ Tenn. River Valley Samples
002010
Report E02-0443
Atlanta
G Goleta Wilminton
Boston n Houston
Dallas Okemoa Walnut Creak
i-- , S f M p J S ItsJ
0 2 - C 'V ' t 3
- Dearborn
Olympia
, East Greenwich Sacramento
Edmond Tacoma
K V.aie
Gig Harbor Ventura
C H A IN O F C U S T O D Y A N D A N A L Y T IC A L R E Q U E S T R E C O R D
S r ^
fatm-
j e . " 5 e i* L i 4 l Enti4.r^nMi-% u>rr-r
ra i *
ProiecINo. I " 7 ^ ^ 0 )
$ E 2 $ T L W , U M , \ iW
Airbill No
ANALYTICAL REQUEST
WTTTTTTTT7*'1 3 'I*jotr 7s?/
Sample ID
O at*
Time
Comp Grab
No. o l Sample / ( J J C ent Media / s / j
//
Comments
V J 03- D t.p
s i " 0200
X 1 Weir C
7goy~t
C , v J 01 " Loi~>
$ W o l* M eJ
Q moI l
v /i/o a
u
i l>
>030
X1 X1 X1
7to !> 3 o i y io z q -
S w o 3 - u O
1
X1
os O s7
O ol - 1-0 uJ
%l
ZZO 'l*!
S W o 'J -N ftJ F S C 0 3 - Lou
*\ 1
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'ito H -o 7&o<r>
/ - S C 0 ol " MccJ "Tr ; ^ t I^h K ^ )
n| /
* 1/
X\
1 'A' \y
3 yo tfx
Total Number o f Container 10
TU M
Relinquished By
FORM I ENT*131
Data Time
I3oo
fktr-JL-
Received By
C .'3 ^ *r' 3r~>
. * ' ' i.'.
.-rt
Date
Time
ty/iln. ucl a .
. _ Tenn. River Valley Samples
002011
Report E02-0+43
Atlanta Goleta Wilmlnton
Boston
Dallas
Houston
Okemos
______ Walnut Creek
. 0 2 - 0 r t 3
Dearborn Olympia
East Greenwich Sacramento
Edmond Tacoma
Gig Harbor Ventura
_ Tenn. R iver Valley Samples
FOPM * E*fT>l9Y
00C 012
Report E02-0443
E OX-Oi^
Atlanta Golata Wilminton
Boston
H ouston
_
a lia s Okamos W alnut C reek
Dearborn Olympia
East Greenwich Sacramento
Edmond Tacoma
CHAIN OF CUSTODY AND ANALYTICAL REQUEST RECORD
Paga
Q G ig Harbor Ventura
_j
-o t_ 2 L
-r O ta r
ry
"3 ^
,
A, )
O
Protect No. Alm a NO
T S -tn -in #
A N A L Y T IC A L R E Q U E S T
1 , \v/ l/ l / / l l / l I l I lI l I l I l I l / v///////////
Sample ID
j S L o i- i- M o a
J y S L O I-L in c i j SLC1 - l ^ O b
Date ll
Time
Comp Grab X
No. of Sample I J jY /
C ant Media / k / /
1 T r .
1.
\
h *pj
/' / '/
/// //
/ /
i
1
1
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Comments
p a 4 K W J ) >1. <5ev
3?
2 3 *1 1 I t l? C tt 3 :hu j M b 5 C -
n
ic
4 4 S ' n -ivi
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12; . S . .u . } I ^ 1S
C .I I - C A T o \ cA To&
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x
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.
.
1
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\y
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? '4 / G A- #
20
'i f
rs^ d Z f'.n , p . /t. / i l f l i . 6 / / '. j 3 a y 1 1 4 - u ., p , ib . si-.
Relinquished By
Date
Time
^ / Received By
Date
Time
7 7 /'7/<q |3 V 0
^ /z c / i / a
t y lo h \7 '.& V
FOWU t E JfT -U I
Term. River Valley Samples
002013
Report E02-0443
J
Atlanta Goleta G Wibninton
E . Il I K
ox- O
Boston
D allas
Houston
Okamos
______ Walnut Creek
G Dearborn
Olympia '
East Greenwich Sacramento
Edmond Tacoma
Gig Harbor Ventura
CHAIN OF CUSTODY AND ANALYTICAL REQUEST RECORD
p^. 3 ^ 3
l`
Tenn. R iver Valley Samples
002014
Atlanta Goteta Wilminton
Boston Houston
Dallas Okemos Wlnut Creek
1i i .
rt Dearborn
Olympia
t0 Z '0 'j> tf-n
East Greenwich Sacramento
/
Edmond Tacoma
Gig Harbor Ventura
CHAIN OF CUSTODY AND ANALYTICAL REQUEST RECORD '
p*ge_L-e<-i.
Term. River Valley Samples
>>
002015
Atlanta Goleta Wilminton
N >r -R
Boston
n Houston
Dallas Okemos P I Walnut Creek
Dearborn Olympia
East Greenwich Sacramento
Edmond Tacoma
C H A IN O F C U S TO D Y A N D A N A L Y T IC A L R E Q U E S T R E C O R D
Pag
Gig Harbor Ventura
m S
i'
Tenn. River Valley Samples
qO & 0 ( &
- E - N - ~ R ~ -
1 - 0 3 (f
Atlanta Goleta WHminton
Boston Houston _____
Dallas Otemos Walnut Creek
Dearborn Olympia
Q East Greenwich Q Edmond
Sacramento
Tacoma
Gig Harbor Ventura
C H A IN O F C U S T O D Y A N D A N A L Y T IC A L R E Q U E S T R E C O R D
P age___!___ o t-- kX .
I
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I
Tenn. River Valley Samples
U0 2 0 1 7
Atlanta Golata Wilmlnton
r - ' N V-T: R'
boz-olu 7
D Boston
Dallas
Houston
Okemos
______ Walnut Creek
Dearborn Olympia'
East Greenwich Sacram ento
Edmond Tacoma
Q G ig H arbor Ventura
C H A IN O F C U S T O D Y A N D A N A L Y T IC A L R E Q U E S T R E C O R D
PllB. 3 ,, ^
Tenn. River Valley Samples
1 (0 2 0 1 8
Report E02-0443
Attachment E: Notes to File
Tenn. River Valley Samples
002019
Report E02-0443
Tenn. RK/er Valley Samples
3M ENVIRONMENTAL LABORATORY
Note to File
Project or Study Number: E02-0443 LIM S Number: NA________ ________________________________________ Affected Data: D020626Extracted, D020628, D020629, and D020702 (Fish Tissue)
T1.he following samples were mislabeled in their respective sequences. They were all labeled as "-1-1" when they should have been labeled as "-1-2". The list is as follows: D020626Extracted: DUDE0055, D020628: DUDE0056 and DUDE0075, D020629: DUDE0063 andDUDE0096, and D020702: DUDE0062.
2A.ll o f the fish tissue sample preparation was done at the same time; therefore, Water Blanks (WB) and Solvent Blanks (SB) were done with each Sample Location, not with each different type of fish from each location. This was done since the WBs and SBs are for examining the sample preparation process and are independent of the species of fish being analyzed. The WBs and SBs were analyzed with the Catfish samples. For this reason, there are not any WB or SB data contained within the Large Mouth or Small Mouth analytical sequences. 3. Tcohnetafiisnherti(sCsuoelusmamn p2l)e,shwaderweaatnearlaydzdeeddin(Ctroilpulmicante3.),Eaancdhthfiesnhhtiosmsuoegpeanrieznedt s(aCmoplulemwna4s)fbiresftowreeiitgwheads oseupt ainratotead into triplicates. The weight are recorded in the "-1" rows of the Fish Tissue prep sheets. It is not until Column 6 that the triplicates are generated from the homogenate (MSs are also generated at this time). The samples that were labeled with "-MS" were spiked with the spike solution in Column 7. 4T.he fish tissue that was used in the extracted fish curves was from the fish tissue sample with the lowest amount o f endogenous analyte concentration. This was determined during a preliminary range-finding experiment. 5. The extracted fish tissue standard curves had a 0 ppb curve point. This point was part of the calibration curve and was "Enabled" in the quantitation software, but it was not calculated as part of the curve.
T6.he 10 ng/mL standard curve point in the Extracted Large Mouth Standard Curve had 21% and 22% deviations, exceeding the criteria by 1% and 2%. These points were not excluded from the curves and their inclusion had no negative effect on the data quality due to the point being surrounded by at least two passing calibration points on
both sides.
002020
Date:
Page i_ of fx-
Report E02-0443
Tenn. River Valley Samples
3M ENVIRONMENTAL LABORATORY
Note to File
Project or Study Number; E02-Q443 LIM S Number: NA_____________________ Affected Data: 1021112/River Sediments
L1.ab Control Samples (LCS) were performed for the River Sediments. However, the information was not used because the data suggested it was impossible to recover spiked analytes from acidified water when river sediment was not present 2T.he injection files from the sequence 1021112 that are after file Itchy062 are not part o f the reportable analyses. These samples were method development only.
Recorded
Date:
002021
Pave<D of
Report E02-0443
Tenn. Rn/erVatey Samples
3M ENVIRONMENTAL LABORATORY
Note to File
Project or Study Number: E02-0443________________ __________ LIM S Number; NA_______________________
Affected Data: D020812A and D020812B.
A1.ll data that is in D020812A and D020812B are from one original sequence: D020812. The D020812 parent sequence is made up o f 161 injections/files. Files DUDE0001 to DUDE0096 are found in the sub-sequence D020812A. Files DUDE0097 to DUDE 0161 are in sub-sequence D020812B. The parent sequence was broken up into two separate sub-sequences after LC/MS analysis to simplify data analysis. Low concentration samples that fall in the bottom end o f the standard calibration curve (0.1 ng/mL to SO ng/mL) are in sub-sequence D020812A. Very high concentration samples that required small injection volumes that fall in the top end of the curve (S ng/mL to 1000 ng/mL) are in sub-sequence D020812B. There are not any files that are contained in both sub-sequences.
2
There are two different extraction dates for the samples: 20 Jun 02 and 17 Jul 02. This is due to a re-extraction o f 5 samples whose results were questionable.
3.
The following are the LIMS numbers and the sample names of the samples and their associated duplicates and
matrix spikes:
38025 SW01 38026 SWOl-Dup 38027 SW01-Low
SFWSC==SFaimelpdleSaWmaptleer(CSoamntprolel Location) FB= Field Blank
38028 SW01-Med
Low=Low Field Spike
3388002390
F S C 0 1-Low
FSCOl-Med
Med=Medium Field Spike
38032 FB02
38033 SW03
38034 SW03-Dup
38035 SW03-Low
38036 SW03-Med
38037 SW02
38038 SW02-Dup
38039 SW02-LOW
38340 SW02-Med
38041 FCS02-LOW
38042 FCS02-Med
38043 Trip Blank #1 and 38047 Trip Blank #2
002022
Recorded Bv:
Date:
Report E02-0443
Tenn. River Valley Samples
3M ENVIRONMENTAL LABORATORY
Note to File
Project or Study Number: E02-0443 LIMS Number: NA Affected Data: D020626Extracted
I1n. the D020626Extracted sequence there were not any Extracted CCV curve points run. All subsequent Fish Tissue sequences had extracted CCVs included. The unextracted CCVs were quantitated against the unextracted fish curve, 02003-050, using an Excel spreadsheet. All of the unextracted CCVs passed and the results are found in Appendix B: Data Summary Tables.
Recorded By:
Date:
002023
M AT>____ - f
Report E02-O443
Tenn. River Valley Samples
3M ENVIRONMENTAL LABORATORY
Note to File
Project or Study Number: E02-0443 LIMS Number; NA Affected Data: All Data
Note: This is to explain how the quantitation wasperformed on the data. T1.he entire calibration curve was entered into the quantitation software and the curve was then analyzed. In many cases, high level curve points were "Disabled" in the software and were removed from the curve calculation. In all instances in which this was done, the disabled curve points show a recovery o f 0%. Low end curve points that had % Recoveries that exceeded the criteria or were <2X the solvent blanks levels were not used. These points were still included in the calibration curve calculations, however, they were not used in the determination of the LOQ. 2In. the raw data that comes from the Target software, concentrations that would normally be quantitated as a very alobwnoorrmaalnleyglaatrigvee vvaalluueesaarleoansgsiwgintehdvaenryexsmtreamll earpeoascitoivuentvs.aluTeh.esTehveasleuvesa,luaelosnagreweiathsilvyalnuoetsictehdatdaureetboetlhoewirthe limit o f quantitation, are changed to "BLOQ" to eliminate any possible confusion.
Recorded By:
Date:
0 OC0 2 4
SPase of .
Report E02-0443
Tenn. River Valley Samples
3M ENVIRONMENTAL LABORATORY
Note to File
Project or Study Number: E02-0443 __________ LIM S Number: NA_______
Affected Data: Fish Tissue
I1n. die sample preparation process o f the fish tissue, after the homogenization process (Step 4), the homogenate is centrifuged for a short time and then shaken (Step S). The centrifugation was done to eliminate the foam that developed during the homogenization process. The homogenate was then shaken/vortexed to make the solution homogenous again.
OOC025
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