Document 6weEwrrMeE6XpXQJ2rKXaM7Q3
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CEntrE Analytical Laboratories, Inc.
3048 Research Drive State Ca?ge,PA 16801
www.centrelab.com
(814) 231-8032
Fax: (814) 231-1253 or (814) 231-1580
Analytical Report
Fluorochemical Characterization of Drinking Water Samples Decatur, Alabama (Wl979)
Centre Analytical Laboratory Report No. 023-007B (Revision 1)
Revision Date 3/'20/01
Testing Laboratory Centre Analytical Laboratory, Inc.
3048 Research Drive State College, PA 16801
3M Environmental Laboratory Contact Kent R. Lindstrorri
Bldg. 2-3E-09
P.O. Box 33331 St. Paul, MN 55133-3331 Phone: (651) 778-5:352
Requester Kris J. Hansen, Ph.D. 3M Environmental Technology & Saifety Services
Bldg. 2-3E-09 P.O. Box 33331 St. Paul, MN 551334331
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1 Introduction
Results are reported for the analysis of a series of drinking water samples received by Centre Analytical Laboratories, Inc. (Centre) from the 3M EnvironmentalLaboratory. The samples were collectedfrom Decatur, Alabama. The Centre study number assignedto the project is 023-007. Specific fluorochemical characterization by liquid chromatography / tandem mass spectrometry (LCIMSRVIS)was requestedfor all samples. A total of 14 samples were received for analysis. The samples were prepared and analyzed by LC/MS/MS for the following list of fluorochemicals:
0 Table 1:Target Analysis Perfluorooctane Sulfonate Perfluorooctanoate The analytical method used was validated by Centre. The validation protocol and results are on file with Centre. Data presented here is the highest quality data available,atthis time.
2 Sample Receipt
The samples were submitted in individual plastic containers and were not preserved. Fourteen individual sample containers were received. Samples were received on 02/15/00. The sample collection dates were not supplied. Chain-of-custody information is presented in Attachment C. 3 Holding Times The analytical method used was validated against a maximum holding time of 14 days. The stability of the analytes of interest for longer periods hiaS not been determined. However, it should be noted that field fortifications in water and other matrices have shown acceptable recoveries at 100 and 1000 ng/Lfor periods longer than 14 days.
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4 Methods - Analytical and Preparatory
4.1
4.1.1
4.1.2
LC/MS/MS Sample Preparationfor LC/MS/MS Analysis
Samples were initially treated with 200 UL of 250 mc& sodium thiosulfate solution to remove residual chlorine. Solid phase extraction (SPE) was used to prepare the samples for LC/MS/MS analysis. A forty-milliliterportion of sample was transferredto a CIS SPE cartridge. The cartridge was first eluted with 5 m i of 40% methanol in water solution. The eluate was discarded and the SPE column was then eluted with 100% methanol. A 5 ml portion of methanol was collected for analysis by LC/MS/MS. This treatment resulted in an eight-fold concentration of the samples prior to analysis.
Sample Analysis by LC/MS/MS
In HPLC, an aliquot of extract is injected and passed through a liquid-phasechromatographic column. Based on the affinity of the analyte for the stationary phase in the column relative to the liquidmobile phase, the analyte is retained for a ch(aracteristicamount of time. Following HPLC separation, EWMS 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 quantitatedagainst standards.
A Hewlett-PackardHP1100 HPLC system coupledto a Micromass Ultima MS/MS was usedto analyze the sample extracts. Analysis was performed using selected reaction monitoring (SRM). Samples were extracted on 2/18/00 and analyzed by MS/MS between 2/16/00 and 2/19/00. The HPLC and MS/MS methods usedfor analysis and instrument parameterscan be found 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) The response of the quantitation ion versus the concentration was plotted for each point. Using linear regression with l/x weighting, the slope, y-intercept and
correlation coefficient (r) and coefficient of determination (P) were determined. A calibration curve is acceptable if r ~ 0 . 9 8 5(?2 0.970).
Calibration standards are preparedusing the same SPEZ procedureusedfor samples.
Calibration check standards were analyzed periodically (every three to five sample injections) throughout the analysis sequence. Compliance i:j obtained if the standard analyte concentrations are within +/-20% of the actual value.
For the results reportedhere, calibration criteria were met.
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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 calibrationstandard. 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 analyticalmethod.
5.4 Matrix Spikes
Matrix spikes were prepared for every sample at a concentration of 100 ngR using all compounds of interest. Matrix spike recoveries are giver1in Attachment 8. Field spikes were also prepared on several samples at a concentration of 100 ngR using all compounds of interest. Field spike recoveries are also given in Attachment B.
5.5 Duplicates
All samples were analyzed in duplicate. Results are given along with the sample results in Attachment A.
5.6 Laboratory Control Samples
Milliq water was spiked with all compound of interest at 25 and 250 ngR. Initial analysis of the
25 ng/L LCS showed low recovery for PFOS. The standard was reinjected and was found to
have acceptable recovery (70-130%). All other recoveries for all compounds were between 70130% in each LCS.
5.7 Sample Related Comments Field blank samples consisted of empty containers. Forty milliliters of type I water filtered
through a hypercarb cartridge was added to the empty container and analyzed in the same manner as the other samples.
6 Data Summary
Please see Attachment A for a detailed listing of the anailytical results.
7 DatdSample Retention
Samples are disposed of one month after the report is issued unless othetwise specified. All electronic data is archived on retrievable media and hard copy reports are stored in data folders maintained by Centre.
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8 Attachments
8.1 Attachment A: Results 8.2 Attachment 6:Matnx Spike Recoveries (Fieldand Laboratory Spikes) 8.3 Attachment C: Chain of Custody 8.4 Attachment D: LC/MS/MS Raw Analytical Data
9 Signatures
Kevin J Lloyd, Vice President
- 3/74
Date
-
$?fldeccl -0 1
Date
Other Lab Members Contributing to Data
Enaksha Wickremesinhe Karen Smith
4w\ Inc. Centre Analytical Laboratories.
3048 Research Drive, State College PA 16801 814-231-8032 FAX 814-231-1253
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Analytical Results W1979 Decatur, Alabama
3M Sample Identification
Sample Description
PFOS (nghL)
PFOSA (ng/L)
POAA (ng/L)
MC-215H MC-217H MC-220H MC-221H MC-223H MC-226H MC-228H MC-233H
Intake-PIN
ND
ND
ND
Intake-P/N duplicate
ND
ND
ND
Intake-FieldBlank Empty
ND
ND
ND
Outflo~-P/N
ND
NO
ND
Outflow-PIN duplicate
ND
ND
ND
Site 1 P/N
ND
NO
ND
Site 1 PIN duplicate
ND
NO
ND
Field Blank PIN Empty
ND
ND
ND
Limit of Detection (LOD) for the procedure is appoximately 2.5 ng/L for PFOS and PFOSA and 7.5 ng/L for P O W
Limit of Quantitation (LOQ) for the procedure is 25 ngIL for all compounds
ND - Compound not detected NQ - Compound detected at a level between the LOD and LOQ. Result is not quantifiable.
ND e LOD e NQ c LOQ
- - Please refer to the reverse side for our standard terms and conditions.
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Attachment B: LC/MS/MS Laboratory Spike Recovery
!Sample ID:
I
!SpikedAmount (ng/L): 1
MC-219H 100
POAA Lower Recovery Limit: Upper Recovery Limit:
Sample Concentration
(ng/L)
0 0 0
Matrix Spike Result (ng/L)
99.4 115 107
I
70
1
130
I
-Matrix Spike
- Result ("/. Recovery) 99.4
-
115.01 107.O
Criteria (Pass / Fail)
PASS PASS PASS
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Attachment B: LC/MS/MS Laboratory Spike Recovery
Sample ID:
I
Spiked Amount (ng/L): I
MC-225H I
~
~
100
PFOS PFOSA POAA
Lower Recovery Limit:
Upper Recovery Limit:
Sample Concentration
(m-)
0 0 0
Matrix Spike Result (ng/L)
105 113 109
70
1
1
130
1
- Matrix Spike
- Result (% Recovery) 105.0
-
113.0 109.0
Criteria (Pass / Fail)
PASS PASS PASS
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Attachment B: LC/MS/MS Laboratory Spike Flecovery
Sample ID:
I MC-230H I
Spiked Amount (ng/L): I
100
I
PFOS PFOSA POAA
Lower Recovery Limit:
Upper Recovery Limit:
L
Sample Concentration
(ng/L)
0 0 0
I
70
I
130
Matrix Spike Result (ng/L)
97.9 108 102
> I
Matrix Spike
-- Result (% Recovery)
97.9 108.0 102.0
I
Criteria (Pass / Fail)
PASS PASS PASS
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Attachment B: LC/MS/MS Field Spike Recovery
Sarnule ID:
I MC-218H 1
I
I
Spiked Amount (ng/L): I
100
I
PFOS PFOSA POAA
Sample Concentration
(ng/L)
0 0 0
Matrix Spike Result (ng/L)
100 78.4 115
- Matrix Spike
Result
-(% Recovery) 100.0
- 78.4 115.0
Upper Recovery Limit: I
130
I
Criteria (Pass / Fail)
PASS PASS PASS
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Attachment B: LC/MS/MS Field Spike Recovery
Sample ID:
I MC-224H 1
Spiked Amount (nglL): [
100
PFOS PFOSA POAA
Sample Concentration
0 0
0
Matrix Spike Result
(ng/L)
102 83.9
110
Lower Recovery Limit: I Upper Recovery Limit: I
70
130
I
-Matrix Spike
Result
-(Oh Recovery) 102.0
83.9
- 110.0
Criteria (Pass / Fail)
PASS PASS PASS
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Attachment B: LC/MS/MS Field Spike Recovery
Sample CD:
c MC-229H I
Spiked Amount (nglL): I
100
ILEA
Sample Concentration
(n!m
0 0 0
Matrix Spike Result
113 83.8 118
- Matrix Spike
- Result (% Recovery) 1 13.0
-
83.8 118.0
Criteria (Pass / Fail)
PASS PASS PASS
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