Document KGarye2rR8v6Mn10rd7d1jZvQ
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CEntrE Analytical LaboratoriEs, Inc.
3048 Research Drive State College, PA 16801
www.centrelab.com
(814)231-8032
Fax: (814)231-1253 or (814)231-1 580
Analytical Report
Fluorochemical Characterization of Surface Water Samples Columbus, GA (W2336)
Centre Analytical Laboratory Report No. 023-014E (Revision 1)
Revision Date 3/22/01
Testing Laboratory Centre Analytical Laboratory, Inc.
3048 Research Drive State College, PA 1680'1
3M Environmental Laboratory Contact Kent R. Lindstrorri
Bldg. 2-3E-09
P.O.Box 33331
St. Paul, MN 55133-3331 Phone: (651) 778-5352
Requester Kris J. Hansen, Ph.lD. 3M Environmental Technology & Safety Services
Bldg. 2-3E-09 P.O. Box 33331 St. Paul, MN 55133-3331
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7 Introduction
Results are reported for the analysis of a series of sutface water samples received by Centre Analytical Laboratories, Inc. (Centre) from the 3M EnvironmentalLaboratory. The samples were collectedfrom Columbus, GA. The Centre study number assignedto the project is 023-014. Specific fluorochemicalcharacterization by liquid chromatography/ tandem mass spectrometry (LC/MS/MS) was requestedfor all samples. A total of 8 samples were receivedfor analysis. The samples were prepared and analyzed by LC/MS/MS for the following list of fluorochemicals:
Table 1: Target Analysis Compound Name Perfluorooctane Sulfonate Perfluorooctane Sulfonvlamide Perfluorooctanoate
The analytical method used was validated by Centre. The validation protocol and results are on file with Centre. Data presentedhere is the highest quality data available at this time.
2 Sample Receipt
The samples were submitted in individual plastic containers and were not preserved. Eight individualsample containers were received. Samples were received on 05/03/00. The sample collection dates were not supplied. Chain-of-custody inforniation is presented in Attachment C.
3 Holding Times
The analytical method used was validated against a niaximum holding time of 14 days. The stability of the analytes of interest for longer periods has; not been determined. However, it should be noted that field fortifications have shown acceptable recoveries at 100 and 1000 ng/L for periods longer than 14 days.
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4 Methods -Analytical and Preparatory
4.1 LCIMSIMS
4.1.1 Sample Preparation for LC/Ms/MS Analysis
Samples were initially treated with 200 ULof 250 m a 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 C18SPE cartridge. The cartridge was first eluted with 5 mL of 40% metlianlol in water solution. The eluate was discarded and the SPE column was then eluted with 100/o 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.
4.1.2 Sample Analysis by LC/MS/MS
In HPLC, an aliquot of extract is injected and passed thrlough 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 observedand quantitated against standards.
A Hewlett-PackardHP1100HPLC system coupledto a Nlicromass Ultima MSNS was usedto analyze the sample extracts. Analysis was performed using selected reaction monitoring (SRM). Samples were extracted on 5/18/00 and analyzed by MS/MS between 5/20/00 and 5/21/00. The HPLC and MS/MS methods used for analysis and instrument parameters can 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 ngR (ppt) The response of the quantitation ion versus the concentration was plotted for each point. Using linear regression with `I/x weighting, the slope, y-intercept and
correlation coefficient (r) and coefficient of determination (12) were determined. A calibration curve is acceptable if r 10.985(12 2 0.970).
Calibration standards are prepared using the same SF'E 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.
For the results reported here, 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-levelcalibration standard. For these samples, the extraction blanks were compliant.
Instrument blanks in the form of clean methanol solvent were also analyzed after every high-
level 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 cornpliant.
5.3 Surrogates
Surrogate spikes are not a component of the LC/MS/hAS ;analytical method.
5.4 Matrix Spikes
Matrix spikes were prepared for every field sample (excluding blanks) at a concentration of
100 ng/L using all compounds of interest. Matrix spike recoveries are given in Attachment B.
All compounds showed matrix spike recoveries between `70-130% in all samples.
Field spikes were prepared on sample MC-501H at a concentration of 100 n g R using all compounds of interest. The field spike is identilied as sample MC-504H. Field spike recoveries are also given in Attachment B. The field spike results showed low recovery for PFOSA. All other compounds showed matrix spike recovleries between 70-130%.
5.5 Duplicates
All samples (excluding blanks) were analyzed in duplicale. 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 215 and 250 ngR. 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 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 emlpty container and analyzed in the same manner as the other samples.
6 Datasummary
Please see Attachment A for a detailed listing of the analytical results.
7 DatdSample 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 Centre.
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8 Attachments
8.1 Attachment A: Resub
8.2 Attachment 6:Matrix Spike Recoveries(Fieldand Laboratory Spikes) 8.3 Attachment C: Chain of Custody
8.4 Attachment D: LC/MS/MS Raw Analytical Data
9 Signatures
- Operations Manager
-
Kevin J Lloyd, Vice President
Date
j 3 MA&%U a I
Date
Other Lab Members Contributing to Data
Enaksha Wickremesinhe Karen Smith David Bell
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3048 Research Drive, State College PA 16801 814-231-8032 FAX 814-231-1253
Analytical Results W2336 Columbus, GA
:3MSample Identification
Sample Description
PFOS (iig/L.)
PFOSA (ngL)
IWC-501 H IUC-503H MC-506H
NA MC-507H NA MC-508H MC-584H NA
Site 1 P/N Surface Water
63.8
NQ
Site 1 P/N Surface Water Duplicate
59.9
NQ
Site 2 P/N Surface Water
76.6
NQ
Site 2 PIN Surface Water Duplicate
83.3
NQ
Site 3 P/N Surface Water
55.4
NQ
Site 3 P/N Surface Water Duplicate
55.4
NQ
Field Blank-P/N Empty
ND
ND
Quiet Surface Water
ND
ND
Quiet Surface Water Duplicate
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 POAA
Limit of Quantitation (LOQ)for the procedure is 25 ng/L for all compounds
ND - Compound not detected
NQ - Compound detected at a level between the LOD and LOQ. Result is not quantifiable.
ND < LOD c NQ c LOQ
POAA (ng/L)
26.1 25.6 26.1 26.7 NQ NQ ND ND ND
-
- 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 MC-505H 1
!Spiked Amount (ng/L): I
~~
100
Lower Recovery Limit: IJpper Recovery Limit:
k
Sample Concentration
(ng/L)
63.8 11.7 26.1
Matrix Spike Result (ng/L)
164 107 121
I
70
I
[
130
-Matrix Spike
- Result (% Recovery)
100.2
- 95.3 94.9
Criteria (Pass / Fail)
PASS PASS PASS
Note: Sample results less than 25 ng/L are reported as NQ in the results section as they are below the limit of quantitation. Results are given in this table for recovery calculations only.
Also note that sample MC-505H is a laboratory spike of sample MC-501H
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Attachment B: LC/MS/MS Laboratory Spike Recovery
!Sample ID:
I MC-506H I
!SpikedAmount (ng/L): 1
100
I
1IPFOS
IPFOSA IPOAA
Sample Concentration
(ng/L)
76.6 16.5 26.1
Matrix Spike Result (ng/L)
162 114 124
-Matrix Spike
- Result (% Recovery) 85.4
-
97.5 97.9
Criteria (Pass / Fail)
PASS PASS PASS
IUpper Recovery Limit:
130
I
IVote: Sample results less than 25 ng/L are reported as NQ in the resullts section as they are Ibelow the limit of quantitation. Results are given in this table for recovery calculations only.
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Attachment B: LC/MS/MS Laboratory Spike Recovery
!Sample ID:
MC-507H 1
Sample
Matrix Spike
Concentration
Result
IIPFOS
IPFOSA IPOAA
(ng/L)
55.4 12.0 23.6
(ng/L)
159 117 125
Lower Recovery Limit: I
70
1
IJpper Recovery Limit: I
130
I
-Matrix Spike - Result
(% Recovery)
103.6 105.0 101.4
Criteria (Pass / Fail)
PASS PASS PASS
Note: Sample results less than 25 ng/L are reported as NQ in the results section as they are below the limit of quantitation. Results are given in this table for rectovery calculations only.
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Attachment B: LC/MS/MS Laboratory Spike Recovery
Sample ID:
I MC-584H I
Spiked Amount (ng/L): I
100
I
POAA Lower Recovery Limit: Upper Recovery Limit:
Sample Concentration
(ng/L)
0 0 0
Matrix Spike Result (ng/L)
79.9 94.5 103
I
70
1
1
130
I
-Matrix Spike
Result
(% Recovery)
9
79.9
94.5
103.0
9
Criteria (Pass / Fail)
PASS PASS PASS
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Attachment B: LC/MS/MS Field Spike Recovery
!Sample ID:
MC-504H I
Sample Concentration
Matrix Spike Result
-Matrix Spike
Result
69.0
26.1
124
97.9
Criteria (Pass / Fail)
PASS FAIL PASS
I-ower Recovery Limit: I
70
I
IJpper Recovery Limit: I
130
1
IVote: Sample results less than 25 ng/L are reported as NQ in the results section as they are Ibelow the limit of quantitation. Results are given in this table for recovery calculations only.
,Also note that sample MC-504H is a field spike of sample MC-501I-i
3M Environmental Laboratory
F M 3~8778 - PWO
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3MBldg 2-3E-09
Samplm Receiving: (651) 7784940
935 BushAvenue
Alternate: (651) 7716753
SI Paul.MN 55106
FAX: (651) 7784170
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Chain of Custody /Request for Laboratory Analytical 1 42 69
Project IDlProJect N a m e ~ f / L l ~ ~ / / ~ ~ ~ ~ ~ ~ R 4 LIp , flldj ,-I )~- hdf-~,lAy 4l
Template # Proiect Lead
I1FinaI Report Due Date Internal Due Date
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3M Env. Lab Project #
For Internal Use Only
wa=
lethod, lmit of detedlMI.reporlng u n l s . etc )
Client Sample Identification
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3M LIMS#
Sam led
Time Sam led
lh
Matrix/ Media
L4-J ti4
Analysis Requested:
I I.
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ICollector's signature: 0IA
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sample Condition Upon Receipt:
dAcceptable 0 Other:
remperature:
'C
d e c e i v e d on Ice
IWAssoualedCoCI 1 4 3 ~,3\ ~ a c o l p , \ ~ a ~ ~ ,
'-kab%\L, ta 70
Oriiinal -AccompanyingSamples
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Comments
Last Paga - Originator
See Reverse Side fw Inslructions
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