Document DMpkYmD1bM21oKeo2yVeEwN05
entreAnalyticLaalboratorieIsn,c,.
048ResearcDhrive StateCollege,PA 16801
wwwcentrelab.com
hone:(814)231-8032
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AnaWcal Report
Fluorochemic,@51 *Characterization of Water and Sediment Samples
Port St.Lucie Resamp!ing (EOO-2003) Centre AnalyticalLaboratory Report No. 023-014P
Testing Laboratory CentreAnalyticaLlaboratoryI,nc.
3048 Research Ddve 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 Dale Bacon Ph.D. 3M Environmental Technology & SafetyServices
Bldg. 2-3E-09 P.O. Box 33331 St.Paul,MN 55133-3331
PAW I OF5
Introduction
Resultasrereportefdbrtheanalysiosfa serieosfwaterand sedimentsamplesreceivebdy Centre AnalyticaLlaboratoriesI,nc.(Centre)from the 3M EnvironmentalLaboratory.The samples were collectedfrom PortSt.Lucie,Floridaand are partof3M ProjectEOO-2003. The' Centre studynumber assigned to the projectis023-014.
Specificfluorochemicaclharacterizatiobny liquidchromatography /tandem mass spectrometry (LCIMS/MS) and ion chromatographywas requestedforallsamples. A totalof 45 samples were receivedforanalysis.
The samples were prepared and analyzed by LC/MS/MS forthefollowinglisotffluorochemicals:
Table 1:Target Analysis
Comoound Name PerfluorooctaneSutfonate -PerfluorooctanSeulfonvlamide Perfluorooctanoate
Acronvm PFOS PFOSA POAA
The analyticamlethods used forwater samples were validatedby Centre.The validatiopnrotocol and resultsare on filewith Centre. The methods were modifiedforthe sediment samples, however theprocedureshave not been fullvyalidatedforthismatrix.Data presentedhere isthe highestqualitydata availableat thistime.
2 Sample Receipt
The samples were submided inindividuapllasticontainersand were not preserved. Forty-five individuaslample containerswere received.Samples were receivedon 7/25/00.The samples were collectedbetween 7/18/00 and 7/19/00.Chain-of-custodiynformatonis presented in Attachment A.
3 Holding Times
The analyticamlethod used was validatedagainsta maximum holdingtime of 14 days. Stability afterthistimeperiodhas not been validatedh,owever itshouldbe noted thatfielfdortifications have shown acceptablerecoveriesat the 100 ng/L forperiodslongerthan 14 days.
PAGE20FS
4 Methods-Analyticanld Preparatory
4.1 LC/MS/MS
4.1.1 Sample Preparation forLC/MS/MS Analysis
Water samples were initialtlryeatedwith 200 uL of 250 mg/L sodium thiosulfatseolubon to remove residualchlorineS.olidphase extracbon(SPE) was used topreparethe samples for. LC/MS/MS analysis.A forty-milliploirtteironofsample was transferretdoa CiaSPE cartridge. The cartridgvem'-s@rit-elutewdith5 mL of40% methanol inwater solution.The eluatewas discardedand the SPE column was then elutedwith 100% methanol. A 5 mL portionof methanolwas collectefdoranalysisby LC/MS/MS. Thistreatmentresultedinan eight-fold concentrationfthesamples priotroanalysis.'
For the sedimentand sludgesamples,a representatipvoertionofsample (5 grams) was first extracteidnto5 mi ofmethanol.The extractswere filteraendd dilutetdoa finavlolume of40 mL withType Iwater.The diluteedxtractwsere thentreatedinthesame manner as thewater samples,beginningwiththesolidphase extraction.
4.1.2 Sample Analysis by LC/MSIMS
InHPLC, an aliquotofextractisinjectedand passed througha liquid-phascehromatographic column. Based on theaffiniotfytheanalyteforthestationarpyhase inthecolumn relativteo theliquimdobile phase,the analyteis-retainefdora charactedstcamount ofUme. Following HPLC separabon,ES/MS providesa rapidand accuratemeans foranalyzinga vade rangeof organiccompounds, includinfgluorochemicalsE.lectrospraiysgeneralloyperatedatrelatively mildtemperaturesm;oleculesare ionizedf,ragmented,and detected.Ionscharacteristoifc known fluorochemicalasreobserved and quantitateadgainststandards.
A Hewlett-PackardHPI.100HPLC system coupledtoa Micromass Ultma MS/MS was used to analyzethe sample extractsA.nalysiswas performedusingselectedreactionmonitoring (SRM). Water samples were extractedbetween 8115100and 8/17/00and analyzedby MS/MS between 8/18/00and 8/23/00.Sediment and sludgesamples were extractedon 8/18/00and were analyzedby MS/MS on 8121/00.The HPLC and MS/MS methods used foranalysisand instrumentparameterscan be found inAttachmentsD and E.
5 Analysis
5.1 Calibration A 7-pointcalibraboncurvewas analyzedatthe beginningand end ofthe analyticaslequence forthecompounds of interesTth.e calibratipoonintswere preparedat 0, 25,50, 100,250, 500, and 1000 ng/L (ppt)for LC/MS/MS analysisT.he instrumentresponseversusthe concentratiownas plottefdoreach point.Usinglinearegressiownith1/xweightingt,he slope, y-interceapntd correlaticoonefficie(nrt)and coefficieonftdeterminatio(n@)were determined. A calibrabocnurveisacceptableI r> 0.985(r,>20.970).
Calibrabonstandardsarepreparedusingthesame S.PE procedureused forsamples.
PAGE30FS
Calibratiocnheck standardswere analyzed periodical(leyverythreetofivesample injections) throughoutthe analysissequence. Compliance is obtained ff the standard analyte concentrationasre within+/-20% ofthe actualvalue.
For theresultsreportedhere,calibratiocnriteriwaere met.
5.2 Blanks
Extracfiobnlanks were prepared and analyzed withevery extractiobnatch of samples. The extractiobnlanksshouldnothave any targetanalytespresentator above theconcentrationof the low-leveclalibratiosntandard.For these samples, the extractiobnlankswere complia6t.
Instrumentblanks-int.tleform ofcleanmethanol solventwere alsoanalyzed aftereveryhighlevelcalibratiosnianda@d,and afterknown high-leveslamples. Again,the blanksshould not have any targetanalytespresentat or above the low-levelcalib-rabosnt.andard. For the samples presentedhere the instrumentblanks are compliant.
5.3 Surrogates
Surrogatespikesare not a component of the LC/MS/MS analyticamlethods.
5.4 MatrixSpikes
Matrixspikeswere preparedforevery fieldsample usingallcompounds of interestMatrix spikerecoveriesare giveninAttachment C.
Fieldspikeswere submittedwiththewater samples. Fieldspikerecoveriesare alsoincluded inAttachmentC. The resultfsrom the200 pptfielsdpikeforsample QSW Palm City-C-FMS200pptA indicattehatthissample was spikedat1000 pptratherthan200 ppt. The resultfsor QSW Palm-City-C-FMS-200pptB indicatea 200 ppt spikingconcentrafion.
5.5 Duplicates
Allfielsdamples were analyzed induplicate.Resultsare givenalong withthe sample results inAttachment B.
5.6 LaboratoryControlSamples
For LC/MS/MS analyses,Milliwqater was spiked withallcompounds of interesatt 25 and 250 ng/L duringeach extractiosnet. Allrecoveriesforallcompounds were between 70-130% in each LCS. Resultsare given along withthe raw data inAttachments D and E.
5.7 Sample RelatedComments
There are no othersample relatedcomments forthisdata seL
6 Data Summary
Please see Attachment B fora detailedlistinogf the analyticarlesults.Surface water results are reportedinpartsper trilli(opnpt)(ngIL).Sediment and sludgesample resultsare reported inpartsperbillio(nppb)(ng/g)on both an as-receivedand dry-weightbasis.
PAG64OFS
7 DatalSample Retention
SamplesaredisposeodfonemonthaftetrhereporitsissueudnlesostherwisspeecifieAdJ.I electronidcata isarchivedon retrievablmedia and hard copy reportsare storedin data foldersmaintainedby Centre.
8 Attachments
8.1 AttachmentA-Chah-of-Custody 8.2 Attachment B: Results. 8.3 AttachmentC: MatrixSpikeRecoveries 8.4 AttachmentD: LC/MS/MS Raw AnalyticaDlata (SurfaceWater Samples) 8.5 AttachmentE: LC/MSIMS Raw AnalyticaDlata (Sedimentand SludgeSamples)
9 Signatures
l@7
ohn M. Flaherty, a O0perafionsManager
Date
KevinJ Uoyd, Vice President
Date
OtherLab Members ContributintgoData Karen Smith
PAGESOF5
ANALYTICARLEPORT771
Centre Analytical
Laboratoric=sI,nc.
3048 Research Drive,State CollegePA 16801 814-231-8032 FAX 814-231-1253
AnalyticalResults EOO-2003 PortSt.Lucie,FL Resampling (watersamples)
3M Sample Identification
MDWPIN-R-0-C
MDWPIN-R-0-C dup
MDWPIN-Lime-C
MDWPIN-Lime-C dup
MDWPOut -C
MDWPOut-C dup
NPWWTPEff -C
NPWWTPEff-C dup
NPWWTPCC-C
NPWWTPCC-C
dup
PSLF Leach-C
PSLF Leach-C dup
TW#2 FireDept-C
TW#2 FireDept-C dup
SW#3 SH-C
SW#3 SH-C dup
TW#3 Penpark-C
TW#3 Penpark-C dup
SW#l Penpark-C
SW#l Penpark-C dup
TW#l HolidayInn-C
TW#l Holiday Inn-C dup
SW#2 MCM-C
SW#2 MCM-C dup
OSW Palm City-C
QSW Palm City-Cdup
BlindDup Cl
BlindDup Cl dup
BlindDup C2
Blind Dup C2 dup
PFOS (ng/L)
<25 < 25 < 25 -c2.5 <25 <25
14.7 J 16.6 J
85.5 78.8 429 425 < 25 < 25 7.8 J 5.4 J < 25 < 25 5.2 J 4.1 J <25 <25 7.7 J 9.3 J 2930 2850 <25 < 25 8.0 J 9.8 J
PFOSA (ng/L)
or
< 25 < 25 < 25 < 25 < 25 < 25 < 25
4.4 J 3.5 J 7.0 1 8.0 J < 25 < 25 < 25 < 25 < 25 < 25 < 25 < 25 < 25 < 25 < 25 < 25 30.0 27.5 < 25 < 25 < 25 < 25
POAA (ng/L)
< 25 < 25 < 25 < 25 < 25 < 25
15.11 14.1 J
42.9 40.2 1030 1020 < 25 < 25 < 25 < 25 < 25 < 25 < 25 < 25 <25 < 25 < 25 < 25 96.9 97.1 < 25 < 25 < 25 < 25
J - Compound ispresent,but below the reportinglimitof 25 ng/L. The resultisan estimated value. Method Detection Limitsare approximately 2.5 ng/L forPFOS and PFOSA and 7.5 ng/L forPOAA.
pl@assrefertoft reveme sideforourstandardtonnsand conditions. jot"
ANALYTICALREPORT,;,@@,
Centrc=.Analytical ao\k\W@ Laboratoric=s,Inc.
3048 Research Drive,State College PA 16801 814-231-8032 FAX 814-231-1253
AnalyticalResults EOO-2003 Port St.Lucie,FL Resampling (solids)
3M Sample Identification
NPWWTP Sludge-C NPWWTP Sludge-C dup SED #3 SH-C SED #3 SH-C dup SED#L Penpark-C SED#L Penpark-C dup SED#2 MCM-C SED#2 MCM-C dup
PFOS (ug/Kg) (as received)
1.36 1.30 < 0.200 < 0.200 < 0.200 < 0.200 < 0.200 < 0.200
PFOSA (ug/Kg) (asreceived)
< 0.200' < 0.200 < 0.200 < 0.200 < 0.200 < 0.200 < 0.200 < 0.200
POAA (ug/Kg) (as received)
< 0.200 < 0.200 < 0.200 < 0.200 < 0.200 < 0.200 < 0.200 < 0.200
3M Sample Identification
NPWWTP Sludge-C NPWWTP Sludge-C dup SED #3 SH-C SED #3 SH-C dup SED#L Penpark-C SED#L Penpark-C dup SED#2 MCM-C SED#2 MCM-C dup.
PFOS (ug/Kg) (dryweight)
62.9 60.2 < 0.261 < 0.261 < 0.263 < 0.263 < 0.304 < 0.304
PFOSA (ug/Kg) (dryweight)
< 9.3 < 9.3 < 0.261 < 0.261 < 0.263 < 0.263 < 0.304 < 0.304
POAA (ug/Kg) (dryweight)
< 9.3 < 9.3 < 0.261 < 0.261 < 0.263 < 0.263 < 0.304 < 0.304
J - Compound ispresent,but below the reportinglimit.The resultisan estimated value.
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pleaserefertothervversesideforourstandardtermsand conditions.
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