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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 Characterizationof POTW Effluent Columbus, Georgia (W2336)
Centre Analytical Laboratory Report No. 023-014M (Revision 1)
Revision Date 3/27/01
Testing Laboratory Centre Analytical Laboratory, Inc.
3048 Research Drive State College, PA 16801
3M Environmental Laboratory Contact Kent R. Lindstrom
Bldg. 2-3E-09
P.O. Box 33331 St. Paul, MN 55133-3331 Phone: (651) 778-5352
Requester Kris J. Hansen, Ph.D. 3M Environmental Technology & Safety Services
Bldg. 2-3E-09 P.O. Box 33331 St. Paul, MN 55133-3331
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1 Introduction
Results are reportedfor the analysis of a series of P O W effluent samples received by Centre Analytical Laboratories, lnc. (Centre)from the 3M Environmental Laboratory. The samples were collected from Columbus, Georgia. The Centre study number assigned to the project is 023014.
Specific fluorochemical characterization by liquid chromatography / tandem mass spectrometry (LC/MS/MS) was requestedfor all samples. A total of 4 samples were received for analysis.
The samples were prepared and analyzed by LC/MS/MS for the following list of fluorochemicals:
Table 1:Target Analysis
ComDound Name Perfluorooctane Sulfonate Perfluorooctane Sulfonvlamide Perfluorooctanoate
PFOSA POAA
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 at this time.
2 Sample Receipt
The samples were submitted in individual plastic containers and were not preserved. Four individual sample containers were received. Samples were received on 6/6/00. The sample collection dates were not supplied. Chain-of-custody informationis presentedin 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 has 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/L for periods longer than 14 days.
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 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 forty-milliliter portion of sample was transferred to a CIS SPE cartridge.
The cartridge was first eluted with 5 mL of 40% methanol in water solution. The eluate was
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4.1.2
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 injectedand passed through a liquid-phasechromatographic 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 fluorochemicalsare observed and quantitated against standards.
A Hewlett-PackardHP1100 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 initially extracted on 6/12/00 and analyzed by MS/MS on 6/15/00. The initial run was rejected because of control sample recoveries outside of acceptable ranges. The samples were re-extracted on 6/28/00 and re-analyzed by MS/MS between 6/28/00 and 6/29/00. Both sets of raw data are included for informational purposes. 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 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 (?) were determined. A calibration
curve is acceptable if r 20.985 (?2 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.
For the results reported here, calibration criteria were met.
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-levelcalibrationstandard. 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 presentedhere the instrument blanks are compliant.
5.3 Surrogates
Surrogate spikes are not a component of the LC/MS/MS analytical method.
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5.4 Matrix Spikes
Matrix spikes were prepared for every sample at a concentration of 1000 ngR using all compounds of interest. Matrix spike recoveries are given in Attachment B. All recoveries were between70-130%. Field spikes were also prepared at a concentration of 1000 ngR. However, the results would indicate that a 100 ngR concentration was spiked instead of the 1000 ng/L given on the field data sheets. Spike recoveries were calculated based on the 100 ng/L spiking level. 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 ng/L. All recoveries for all compounds were between 70-130% 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 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 maintainedby Centre.
8 Attachments
8.1 Attachment A: Results 8.2 Attachment B: Matrix Spike Recoveries (Field and Laboratory Spikes) 8.3 Attachment C: Chain of Custody 8.4 Attachment D: LC/MS/MS Raw Analytical Data
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9 Signatures
Kevin J Lloyd, Vice President Other Lab Members Contributingto Data Enaksha Wickremesinhe Karen Smith
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Date
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a\Laboratories. Inc. CEntre Analytical
3048 Research Drive, State College PA 16801 8 14-231-8032 FAX 8 - 14-231 1253
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Analytical Results W2336 Columbus, Georgia
3M Sample Identification
MC-539HP O W Effluent NA Duplicate P O W Effluent MC-543H
Sample Description
P/N Ion Pair PIN Ion Pair Duplicate Field Blank P/N Empty
PFOS (ng/L)
437 416 ND
PFOSA (ng/L)
05.3 84.8 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 betweenthe LOD and LOQ. Result is not quantifiable.
ND c LOD < NQ < LOQ
POAA (ng/L)
139 147 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-542H 1
Spiked Amount (ng/L): I
1000
1
PFOS PFOSA POAA
Lower Recovery Limit:
Upper Recovery Limit:
Sample Concentration
(ng/L)
437 85.3 139
I
70
1
130
Matrix Spike Result (ng/L) 1720 1102 1055
I
Matrix Spike Result
(% Recovery)
128.3 101.7 91 ..6
I Criteria (Pass / Fail)
I PASS PASS PASS
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Attachment B: LC/MS/MS Field Spike Recovery
Sample ID:
MC-541H 1
PFOS PFOSA POAA
Lower Recovery Limit:
Upper Recovery Limit:
Sample Concentration
(ng/L)
437 85.3 139
I
70
1
130
Matrix Spike Result (ng/L) 530 200 252
I
Matrix Spike Result
(% Recovery)
93.0 1 14.7 113.0
I I Criteria (Pass / Fail)
PASS PASS PASS
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