Document jBDR81JxmdONwqB6EaKBvMD1y
Precise Research. Proven Resulte.
Analytical Report
Fluorochemical Characterization of Aqueous Samples Decatur Outfall 001 FC Monitoring (E04-0045)
Exygen Research Laboratory Report No. L0001718
Testing Laboratory Exygen Research
3058 Research Drive State College, PA 16801
Project Lead Jess Eldridge 3M Environmental Technology and Safety Services 935 Bush Avenue Building 0002-03-E-09 PO Box 33331 St. Paul, MN 55133-3331
3058 Research Drive m State College, PA 16801, USA
T: 800.281.3219 k. F: 814.272.1019
exygen.com
1 Introduction
Results are reported for the analysis of aqueous samples received by Exygen Research (Exygen) from PACE Analytical. The Exygen study number assigned to the project is L0001265.
Specific fluorochemical characterization by liquid chromatography / tandem mass spectrometry (LC/MS/MS) was requested for all samples. A total of 8 samples (including field duplicates, blanks, and spikes) were received for analysis.
The samples were prepared and analyzed by LC/MS/MS for the following list of fluorochemicals:
Table 1: Target Analysis
Compound Name Perfluorobutanesulfonate (PFBS) Perfluorohexanesulfonate (PFHS) Perfluorooctanesulfonate (PFOS) Perfluorobutvric Acid Perfluorooentanoic Acid Perfluorohexanoic Acid Perfluoroheptanoic Acid Perfluorooctanoic Acid Perfluorononanoic Acid Perfluorodecanoic Acid Perfluoroundecanoic Acid Perfluorododecanoic Acid Perfluorobutanesulfonamide (PFB Amide) Perfluorooctanesulfonamide 2-(N-methvlperiuorobutanesulfonamido)ethvl alcohol
Acronym C4 Sulfonate C6 Sulfonate C8 Sulfonate C4 Acid C5 Acid C6 Acid C7 Acid C8 Acid C9 Acid C10 Acid C11 Acid C12 Acid FBSA FOSA Me-FBSE-OH
The analytical methods used were originally developed for groundwater samples and were validated by Exygen. The validation protocol and results are on file with Exygen. Only the C8 Sulfonate, FOSA, and C8 Acid were included in the original method validation. It should be noted that the quality control elements included in this analysis demonstrate the applicability of the method to the additional analytes.
2 Sample Receipt
The water samples were submitted in plastic containers. Samples were received at ambient temperature. Samples were stored at 4C from receipt until analysis. Eight individual containers were received. Field samples were collected on 1/27/04 and 1/28/04. Samples were received on 1/29/04. Chain-of-custody information is presented in Attachment C.
PAGE 2 OF 5
3 Holding Times
Field and laboratory spikes of these fluorochemlcals have shown stability for periods greater than 90 days. Samples were analyzed within 60 days of collection.
4 Methods - Analytical and Preparatory
4.1 LC/MS/MS
4.1.1 Sample Preparation for LC/MS/MS Analysis
Water samples were initially treated with 200 uL of 250 mg/L sodium thiosulfate solution to remove residual chlorine. Solid phase extraction (SPE) was used to prepare the samples for LC/MS/MS analysis. A portion of sample was diluted to forty-milliliters with Type I water. The dilution was performed prior to extraction in order to lessen the effects of matrix enhancement. This matrix enhancement was observed in earlier samples from this location and from screening runs performed on these samples. The diluted samples were transferred to a C18 SPE cartridge. The cartridge was eluted with 5 mL of 100% methanol. This treatment resulted in an eight-fold concentration of the diluted samples prior to analysis.
4.1.2 Sample Analysis by LC/MS/MS
In HPLC, an aliquot of extract is injected and passed through a liquid-phase chromatographic column. Based on the affinity of the analyte for the stationary phase in the column relative to the liquid mobile phase, the analyte is retained for a characteristic amount of time. Following HPLC separation, ES/MS provides a rapid and accurate means for analyzing a wide range of organic compounds, including fluorochemicals. Electrospray is generally operated at relatively mild temperatures; molecules are ionized, fragmented, and detected. Ions characteristic of known fluorochemicals are observed and quantitated against standards.
A Hewlett-Packard HP1100 HPLC system coupled to a Micromass Ultima MS/MS was used to analyze the sample extracts. Analysis was performed using selected reaction monitoring
(SRM ). Samples were extracted on 2/20/04. Samples were analyzed between 2/24/04 and
3/3/04. Raw analytical data is provided in Attachment D.
5 Analysis
5.1 Calibration
A 7-point calibration curve was analyzed at the beginning and end of the analytical sequence for the compounds of interest. The calibration points were prepared at 0, 25, 50, 100, 250, 500, and 1000 ng/L (ppt) for LC/MS/MS analysis. The instrument response versus the concentration was plotted for each point. Using linear regression with 1/x weighting, the slope, y-intercept and correlation coefficient (r) and coefficient of determination (r2) were determined. A calibration curve is acceptable if r >.0.985 (r2 > 0.970).
Calibration standards are prepared using the same SPE procedure used for samples.
Calibration check standards were analyzed periodically (every three to five sample injections) throughout the analysis sequence. Compliance is obtained if the standard analyte concentrations are within +/-20% of the actual value.
PAGE3 OF5
All calibration criteria were met for this analysis.
5.2 Blanks
Extraction blanks were prepared and analyzed with every extraction batch of samples. The extraction blanks should not have any target analytes present at or above the concentration of the low-level calibration standard. For these samples, the extraction blanks were compliant.
Instrument blanks in the form of clean methanol solvent were also analyzed after every highlevel calibration standard, and after known high-level samples. Again, the blanks should not have any target analytes present at or above the low-level calibration standard. For the samples presented here the instrument blanks are compliant.
5.3 Surrogates
Surrogate spikes are not a component of the LC/MS/MS analytical methods.
5.4 Matrix Spikes
Field and laboratory spikes were prepared using all compounds of interest. Field spikes were prepared by adding a measured volume of field sample to a container spiked with the target analytes by the laboratory prior to shipping containers for sample collection. Laboratory spikes consisted of aliquots of un-spiked field samples that were fortified at the laboratory at the time of extraction. Field blank spikes consisted of laboratory water fortified at the laboratory and shipped with the sample containers to the field and back to the laboratory for analysis. Laboratory control spikes (see section 5.6) are samples of laboratory water spiked at the time of extraction. Each type of spike provides information needed to assess analyte stability, extraction efficiency, and matrix effects that may impact analytical results. Matrix spike recoveries are given in Attachment B. Please see Section 5.7 for additional discussion of matrix spike recoveries.
5.5 Duplicates
Field and laboratory duplicates were prepared for each field sample. Duplicate results are given along with the sample results in Attachment A.
5.6 Laboratory Control Samples
For L C /M S /M S analyses, Milliq water was spiked with all compounds of interest at 100 and
500 ng/mL during each extraction set. All recoveries for all compounds were between 70 130% in each LCS. Results are given along with the raw data in Attachment D.
5.7 Statement of Accuracy
Based on results of field spikes, laboratory fortified field samples, field blank spikes, and laboratory control spikes, the analytical accuracy of all analytes is 30% for all compounds with the following exceptions. No data is being reported for the C4 acid because of multiple QC failures. Results for the C5 Acid, C7 Acid, and C4 Sulfonate should be used as screening data only. These three analytes showed one or more spike recoveries outside of the acceptable ranges. The statement of accuracy is based on recoveries of field and laboratory spikes,
5.8 Data Summary
Please see Attachment A for a detailed listing of the analytical results. Results are reported in parts per billion (ppb) (ng/mL). Please note that the limit of quantitation is 1.0 ng/mL for all compounds except MeFBSE-OH, which has a quantitation limit of 4.0 ng/mL.
PAGE4 OF5
6 Data/Sample Retention
Samples are disposed of one month after the report is issued unless otherwise specified. All electronic data is archived on retrievable media and hard copy reports are stored in data folders maintained by Exygen.
7 Attachments
7.1 Attachment A: Results 7.2 Attachment B: Matrix Spike Recoveries 8.3 Attachment C: Chain of Custody 8.4 Attachment D: Raw Analytical Data
9 Signatures
Other Lab Members Contributing to Data Emily Decker Karen Smith
PAGE 5 OF5
SECTION A
ReportAnalytical Y'
Sum m ary of Fluorochemical Residues in Outfall 001 Effluent
Sample ID
Outfall 001 Effluent-Composite Outfall 001 Effluent-Composite* Outfall 001 Effluent-Composite Dup
Field Control/Travel Blank Equipment Blank
C5 Acid*
Perfluoropentanoic Acid
5.02 4.89 4.91 ND ND
Analyte Found (ng/mL) C6 Acid
Perfluorohexanoic Acid
10.5 10.2 9.88 ND ND
C7 Acid*
Perfluoroheptanoic Acid
2.23 1.78 1.71 ND ND
Sample ID
Outfall 001 Effluent-Composite Outfall 001 Effluent-Composite* Outfall 001 Effluent-Composite Dup
Field Control/Travel Blank Equipment Blank
C8 Acid
Perfluorooctanoic Acid
427 408 396 ND ND
Analyte Found (ng/mL)
C9 Acid
C10 Acid
Perfluorononanoic Acid
Peril uorodecanoic Acid
ND ND
ND ND
ND ND
ND ND
ND ND
C11 Acid
Perfluoroundecanoic Acid
ND ND ND ND ND
Sample ID
C12 Acid
Perfluorododecanoic Acid
Outfall 001 Effluent-Composite Outfall 001 Effluent-Composite* Outfall 001 Effluent-Composite Dup
ND ND ND
Field Control/Travel Blank Equipment Blank
ND ND
Analyte Found (ng/mL)
C4 Sulfonate*
C6 Sulfonate
Perfluorobutanesulfonate Perfluorohexanesulfonate
29.1 28.6 30.5
1.60 1.56 1.57
ND ND
ND ND
C8 Sulfonate
Perfluorooctanesulfonate
28.6 27.1 28.6 ND ND
Analyte Found (ng/mL)
S a m p le ID
Outfall 001 Effluent-Composite Outfall 001 Effluent-Composite* Outfall 001 Effluent-Composite Dup
Field Control/Travel Blank Equipment Blank
FBSA
78.1 75.5 67.8 ND ND
FO SA
3.60 3.33 3.68 ND ND
M e-F B S E -O H **
ND ND ND ND ND
ND = Not detected = Response between 0 and 1 ng/mL. **ND = Not detected = Response between 0 and 4 ng/mL. AData is to be used for screening purposes only. 'Laboratory Duplicate
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SECTION B
Proven Results.
Recovery Summary of Fluorochemical Residues in Outfall 001 Effluent
Sample Description Outfall 0 0 1
Low Field Spike
Amount Spiked (ng/mL)
Amt Found in Sample
(ng/mL)
C5 Acid_________________________ C6 Acid_________________________ C7 Acid
Amount
Amt Found Amount
Amt Found Amount
Recovered Recovery in Sample Recovered Recovery in Sample Recovered Recovery
(ng/mL)
(%)
(ng/ml.) (ng/rnL)
<%)
(ng/mL) (ng/mL)_____ (%)
5.02 9.06 **
10.5 12.8
2.23 5.92 369
Outfall 001
H igh Field Spike
500
5.02
2020
403
10.5
692 136 2.23
516 103
Outfall 0 0 1 Spk C
Low Lab Spike
Outfall 0 0 1 Spk D
High Lab Spike
10 250
5.02 5.02
38.4 334
756 \
300
10.5 10.5
21.9 114 240 92
2.23 2.23
12.7 105 185 73
Field Blank
Low Field Spike
Field Blank
High Field Spike
10 250
ND ND
9.33 93 315 126
ND ND
9.45 95 276 110
ND ND
14.7 147 779 312
Sample Description Outfall 0 0 1
Low Field Spike
Amount Spiked (ng/mL)
C8 Acid
C9 Acid
C10 Acid
C11 Acid
Amt Found Amount
Amt Found Amount
Amt Found Amount
Amt Found Amount
in Sample Recovered Recovery in Sample Recovered Recovery in Sample Recovered Recovery in Sample Recovered Recovery
(ing/mL) (ng/mL)
(%)
(nq/mL.) (nq/mL)
(%)
(ng/mL) (ng/mL)
(%)
(ng/mL) (ng/mL)
{%)
1
427.0
422.0
ND
0.823
82
ND
0.929
93
ND
0.984
98
Outfall 0 0 1
H igh Field Spike
500
427.0
848
84
ND
600 120
ND
587 117
ND
538 108
Outfall 0 0 1 Spk C
Low Lab Spike
10
427.0
447
**
ND 9.62 96 ND 10.6 106 ND 11.7 117
Outfall 001 Spk D
H igh L ab S p ike
250 427.0
655
91
ND
242 97
ND
239 96
ND
272 109
Field Blank
Low Field Spike
10
ND
10.6 106
ND
11.0 110
ND
10.9 109
ND
11.2 112
Field Blank
High Field Spike
250
ND
246 98
ND
276 110
ND
261 104
ND
249 100
ND = Not detected = Response between 0 and 1 ng/mL. *ND = Not detected = Response between 0 and 4 ng/mL. "Sample residue exceeded the spiking level by more than 4 times; therefore an accurate recovery cannot be calculated.
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Proven Results.
Recovery Summary of Fluorochemical Residues in Outfall 001 Effluent Continued
Sample Description Outfall 001 Low Field Spike
Outfall 001 High Field Spike
Amount Spiked (ng/mL)
C12 Acid
C4 Sulfonate
C6 Sulfonate
C8 Sulfonate
Amt Found Amount
Amt Found Amount
Amt Found Amount
Amt Found Amount
in Sample Recovered Recovery in Sample Recovered Recovery in Sample Recovered Recovery in Sample Recovered Recovery
(ng/mL) (ng/mL)_____ (%]___ (ng/mL) (ng/mL)
(%)
(ng/mL) (ng/mL)
(%)
(ng/mL) (ng/mL)
(%)
1
ND \
1.20
120
29.1
324
**
1.60 2.88 128 28.6 29.6 **
500 ND
615 123 29.1
1400
274
1.60
601 120 28.6
512
97
Outfall 001 Spk C
Low Lab Spike
10
ND
13:0 130
29.1
57.7
**
1.60
12.2 106
28.6
37.7 91
Outfall 001 Spk D High Lab Spike
250
ND
315 126 29.1
554 210
1.60
223
89
28.6
287 103
Field Blank
Low Field Spike
10
ND
11.7 117
ND
8.59 86
ND
10.3 103
ND
10.7 107
Field Blank
High Field Spike
250
ND
252 101
ND
270 108
ND
244 98
ND
264 106
Sample Description Outfall 0 0 1
Low Field Spike
Amount Spiked (ng/mL)
Amt Found in Sample
(ng/mL)
FBSA
Amount
Amt Found
Recovered Recovery in Sample
(ng/mL)
(%)
(ng/mIL)
FOSA
Me-FBSE-OH*
Amount
Amt Found Amount
Recovered Recovery in Sample Recovered Recovery
(ng/mL)
(%)
(nq/mL) (ng/mL)
(%)
1 78.1 72.9 ** 3.60 4.65 105 ND ND -
Outfall 0 0 1
H igh Field Spike
500
78.1
668 118 3.60 . 832 166
ND
508 102
Outfall 0 0 1 Spk C
Low Lab Spike
Outfall 0 0 1 S p k D
H igh Lab Spike
10 250
78.1 78.1
84.3 ** 317 96
3.60 19.5 159 ND 3.60 265 105 ND
9.68 97 240 96
Field Blank
Low Field Spike
10
ND
10.9 109
ND
11.7 117
ND
10.7 107
Field Blank
H igh Field Spike
250
ND
263 105
ND
252 101
ND
194 78
ND = Not detected = Response between 0 and 1 ng/mL. *ND = Not detected = Response between 0 and 4 ng/mL. "Sample residue exceeded the spiking level by more than 4 times; therefore an accurate recovery cannot be calculated.
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SECTION C
3058 Research Drive State College, PA 16801 RESEARCH
Phone: 814-272-1039 Fax: 814-231-1580
Login G rou p: L 0001718
Login#: Project:
1828 P0000689
Company Name: 3M
Submitted By: Jess Eldridge
Login Type:
Immediate Receipt of Samples
Started: Date Start:
T 01/29/2004
Due Date:
02/12/2004
Received Date: 01/29/2004
Received By:
AMMERMAN, MARK
Spread Sample:
Label:
Project Title/Type: Decatur Outfall 001 FC Monitoring / ROUTINE
Exygen SD/PI: RISHA, KAREN
Login Notes:
Conform Notes:
Conform COC Sample: Conform COC: Conform Sample: Conform Request:
True True True True
Package PK0002310
C a rto n
Packages / Containers
M ail Date / Condition
S h ip p er / ID
1/29/2004 1:10:22PM Package & Contents Uncompromised
FEDEX 8449572183000200
Tem p. C ontrol/Tem p.
None 12.1
D irection / Handled By
RECEIVED AMMERMAN, MARK
Container # C0026419 C0026420 C0026421 C0026422 C0026423 C0026424 C0026425 C0026426
Gross Weight pH
Container Type
608.8 g 262.5 g 270.7 g 612.1 g 278.3 g 255.5 g 254.6 g 612.7 g
500 ml Clear Plastic Narrow
500 ml Clear Plastic Narrow
500 ml Clear Plastic Narrow
500 ml Clear Plastic Narrow
500 ml Clear Plastic Narrow
500 ml Clear Plastic Narrow
500 ml Clear Plastic Narrow
500 ml Clear Plastic Narrow
Preservative NONE NONE NONE NONE NONE NONE NONE NONE
Mfg. Lot
Mfg. ID
3/3/2004 Login.rpt
Report Version: Feb 20 2004 11:35AM Page 1 of 2
Instance:
R0089128
R0089128
Sample ID L0001718-0001 L0001718-0002
L0001718-0003
L0001718-0004 L0001718-0005 L0001718-0006 L0001718-0007 L0001718-0008
Container C0026419
C0026420
C0026421 C0026422 C0026423 C0026424 C0026425 C0026426
Matrix LIQUID LIQUID
LIQUID
LIQUID LIQUID LIQUID LIQUID LIQUID
ogin
Fraction Water
Samples
Sample Outfall 001 Effluent-Composite
Date Sampled Date Received Date Due
01/28/2004 01/29/2004
02/12/2004
Water
Outfall 001 Effluent-Composite Low Spk 10 ppb
01/28/2004 01/29/2004
02/12/2004
Water
Outfall 001 Effluent-Composite High Spk 250 01/28/2004 01/29/2004 ppb
02/12/2004
Water
Outfall 001 Effluent-Composite Duplicate
01/28/2004 01/29/2004 02/12/2004
Water
Field Control / Travel Blank
01/29/2004 02/12/2004
Water
Field Control / Travel Blank Low Spk 10 ppb
01/29/2004
02/12/2004
Water
Field Control / Travel Blank High Spk 250 ppb
01/29/2004 02/12/2004
Water
Equipment Blank
01/27/2004 01/29/2004 02/12/2004
3/3/2004 Login.rpt
Report Version: Feb 20 2004 11:35AM Page 2 of 2
Instance:
R0089128
R0089128
raceAnalytical"
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Q uotation#:
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PROJECT REQUIREMENTS Results Deadline:
Laboratory Report Options: I I Sample results only I I Add case narrative I I Add quality control summary I I Add calibration summary I I Add raw data Other_________
REV. 3-02
[John Quiitn r~E04-D045 O^catur'1TW
FagSTj
1/14/2004 Project: E04-0046
3M ENVIRONMENTAL LABORATORY P re llm lna ry /U n a uthorlz e c Fe p ort
Requester: Schnobrich, Dana M (223-1N-0S) Department: 530711 Project Number: 0022674449 Date Received: 1/14/2004 Project Description: Decatur Outfall 001 FC Monitoring Quarterly Comments:
Completion Date: Project Lead: Jess S. Eldridge Phone Number: 651-778-5233 Email Address: jseldridge@mmm.com
1 of 2
Project Results/Actlvlty Pace Field Sampling Event
3M SampleNumber
SampledDate
E04-004S-65674
1/27/2004
LAB EXYGEN
Analytical Mathod LCMS
E04-0045-6S676
1/27/2004
LAB EXYGEN
Analytical Method LCMS
E04-0046-65676
1/27/2004
Sample Description Outfall 001 Effluent - Composite
Components , PFOS PFHS PFBS
Result
FOSA
PFBAmide MeFBSE-OH
C4 acid CS acid
C6 acid
C7 acid
PFOA
C9 acid
CIO acid
C ll acid
0 2 acid
Outfall 001 Effluent - CompositeDuplicate
Components PFOS
PFHS PFBS FOSA
.
PFBAmide MeFBSE-OH C4 acid
CS acid C6 acid C7 acid
PFOA C9 acid CIO acid
C ll acid C12 acid
Field Control/Travel Blank
Result
R L Qualifier R L Qualifier
4 '_________. ;'___ '_____ ' _________ ________
John Qualtieri - E04-0045 Decatur 1Q04 NPDES FC LR.pdf
Page 2 1
1/14/2004
3M ENVIRONMENTAL LABORATORY Preliminary/UnauthorizetReport
Project: E04-0045 (cont)
3M SampleNumber
SampledDate
E04-004S-65676 (cont.) 1/27/2004
LAB EXYGEN
Analytical Method LCMS
' E04-0045-65677
' 1/27/2004
LAB EXYGEN
Analytical Method LCMS
Sample Description Field Control/Travel Blank
Components PFOS PFHS PFBS FOSA PFBAmide MeFBSE-OH C4 acid C5 acid C6 acid C7 acid PFOA C9 acid CIO acid C11 acid C12 acid
EquipmentBlank
:
Component PFOS PFHS PFBS FOSA PFBAmide MeFBSE-OH C4 acid C5 acid C6 acid C7 acid PFOA C9 acid CIO acid CU acid C l 2 acid
.
Result
Result .
2 of 2 RL Qualifier
RL Qualifier
4
PJbttn Qualterf^e>3045 qJrVfllfe DecaHr 1Q04 .xls
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