Document 8RLeMgdv2d63O9o6YD7Rn9qok
T W RESEARCH
Precise Research. Proven Results.
Analytical Report
Fluorochemical Characterization of Aqueous Samples Decatur Outfall 001 FC Monitoring (E05-0368)
Exygen Research Laboratory Report No. L0005336
Testing Laboratory Exygen Research
3058 Research Drive State College, PA 16801
Requester Gary A, Hohenstein Environmental Manager, Special Projects, EHS Operations 3M Bldg, 42-2E-27 St. Paul, MN 55133
.3058 Research Drive i State College, PA 16801, USA
if: 800.281.3219
kF: 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 L0005336.
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) Perfiuorooctanesulfonate (PFOS) Perfluorobutvric Acid Perfluorooentanoic Acid Perfluorohexanoic Acid Perfluoroheotanoic Acid Perfluorooctanoic Acid Perfluorononanoic Acid Perfluorodecanoic Acid Perfluoroundecanoic Acid Perfluorododecanoic Acid Perfluorobutanesulfonamide (PFB Amide) Perfluorooctanesulfonamide 2-(N-methvlperluorobutanesulfonamido)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 5/24/05 and 5/25/05. Samples were received on 5/26/05. Chain-of-custody information is presented in Attachment C.
PAGE 2 O F5
3 Holding Times
Field and laboratory spikes of these fluorochemicals 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 40 mL portion of sample was 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 PE Sciex API 4000 MS/MS was used to analyze the sample extracts. Analysis was performed using selected reaction monitoring (SRM). Samples were extracted on 6/2/05. Samples were analyzed on 6/2/05 and 6/3/05. Raw analytical data is provided in Attachment D.
5 Analysis
5.1 Calibration
A 9-level calibration curve was analyzed at the beginning and throughout the analytical sequence for the compounds of interest. The calibration points were prepared at 0, 25, 50, 100, 250, 500, 1000, 2500, and 5000 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.
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.
PAGE 3 OF5
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 LC/MS/MS 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. Results for C4 Sulfonate, 4 Acid and C5 Acid should be considered as screening quality because of high and variable field and laboratory matrix spike recoveries. The statements of accuracy are based on an overall evaluation of recoveries of field and laboratory spikes, field blank spikes and laboratory control 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 and C4 Acid, which have a quantitation limit of 4.0 ng/mL.
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.
PAGE 4 OF 5
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 Karen Risha
PAGE 5 OF 5
Section A
Summary of Fluorochemical Residues in Outfall 001 Effluent for E05-0368
Sample ID
Outfall 001 Effluent Outfall 001 Effluent* Outfall 001 Effluent Dup Field Control/Travel Blank
.
C4 Acid**
Perfluorobutyric Acid
22.3 25.2 21.1 ND
Analyte Found (ng/mL)
C5 Acid
C6 Acid
Perfluoropentanoic Acid Perfluorohexanoic Acid
2.59
6.02
2.54
5.65
2.37
6.21
ND ND
C7 Acid
Perfluoroheptanoic Acid
1.32 1.30 1.30 ND
Sample ID
Outfall 001 Effluent Outfall 001 Effluent* Outfall 001 Effluent Dup Field Control/Travel Blank
C8 Acid
Perfluorooctanoic Acid
8.33 8.38 8.77 ND
Analyte Found (ng/mL)
C9 Acid
C10 Acid
Perfluorononanoic Acid
Perfluorodecanoic Acid
ND ND
ND ND
ND ND
ND ND
C11 Acid
Perfluoroundecanolc Acid
ND ND ND ND
Sample ID Outfall 001 Effluent Outfall 001 Effluent* Outfall 001 Effluent Dup Field Control/Travel Blank
C12 Acid
Perfluorododecanolc Acid
ND ND ND ND
Analyte Found (ng/mL)
C4 Sulfonate
C6 Sulfonate
Perfluorobutanesulfonate Perfluorohexanesulfonate
26.2
1.05
26.1 26.9 ND
1.03 0.966
ND
C8 Sulfonate
Perfluorooctanesulfonate
16.3 16.0 16.3 ND
Analyte Found (ng/mL)
Sample ID
Outfall 001 Effluent Outfall 001 Effluent* Outfall 001 Effluent Dup Field Control/Travel Blank
FBSA 9.24 9.16 9.54 ND
FOSA
. 2.51 2.46 2.55 ND
Me-FBSE-OH**
ND ND ND ND
ND = Not detected = Response between 0 and 1 ng/mL. **ND = Not detected = Response between 0 and 4 ng/mL.
'Laboratory Duplicate
0006
\ TJ^30.350E58 Research Drive
> # m s tSatatte College, PA 16801, USA
J: 814.272.1039 F: 814.231.1580 exygen.com
Section B
CH
Recovery Summary of Fluorochemical Residues in Outfall 001 Effluent for E05-0368
Sample Description
Outfall 001
Low Field Spike
C4 Acid*____________________ C5 Acid______________________ CBAcid______________________C7 Acid
Amount Amt Found Amount
Amt Found Amount
Amt Found Amount
Amt Found Amount
Spiked 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) (%)
(no/mL) (ng/mL) (%)
(ng/mL) (ng/mL) (%)
10
22.3
40.1 178 2.59
30.4 278
6.02
13.3 73
1.32 11.0 97
Outfall 001
High Field Spike
250
22.3
,402
152
2.59
513 204 6.02
180 70
1.32
187 74
Outfall 001 Spk C Low Lab Spike 1 22.3 26> ** 2.59 6.00 341 6.02 7.69 167 1.32 2.81 149
Outfall 001 Spk D
High Lab Spike
500
22.3
2080
412
2.59
1620
324
6.02
674 134
1.32
514 103
Field Blank
Low Field Spike
10
ND
11.8 1.18 ND 8.71 87
ND
ic i 111 ND 9.27 93
Field Blank
High Field Spike
250
ND
295
118 .
ND
94.6 38
ND
254 102
ND
230 92
Sample Description Outfall 001
Low Field Spike
CS Acid
C9 Acid
CIOAcid
C11 Acid
Amount Amt Found Amount
Amt Found Amount
Amt Found Amount
Amt Found Amount
Spiked 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) (ng/mL) (%)
10 8.33 16.4 81
ND 9.15 92
ND 9.25 93
ND 7.64 76
Outfall 001
High Field Spike
250
8.33
197 75
ND
203 81
ND
214 86
ND
183 73
Outfall 001 Spk C
Low Lab Spike
1
8.33
9.85
**
ND 1.19 119 ND
1.06 106 ND 1.01 101
Outfall 001 S p k D
High Lab Spike
500
8.33
531 105
ND
481 , 96
ND
490 98
ND
497 99
Field Blank
Low Field Spike
10
ND
10.0 100
ND
10.1 ,101
ND
10.7 107
ND
11.4 114
Field Blank
High Field Spike
250
ND
235 94
ND
247 99 , ND
252 101
ND
243 97
ND = Not detected = Response between 0 and 1 ng/mL. *ND = Not detected = Response between 0 and 4 ng/mL.
0007
J& 3300558 Research Drive -/Tm StSata)te College, PA 16801, USA
VT: 800.281.3219 F: 814.272.1019 exygen.com
CH
Recovery Summary of Fluorochemical Residues in Outfall 001 Effluent for E05-0368 Continued
Sample Description Outfall 001
Low Fiald Spika
C12 Acid
C4 Sulfonate
C6 Sulfonate
CS Sulfonate
Amount Amt Found Amount
Amt Found Amount
Amt Found Amount
Amt Found Amount
Spiked in Sample Recovered Recovery In Sample Recovered Recovery in Sample Recovered Recovery in Sample Recovered Recovery
(ng/mL) (ng/mU (ng/mL) (%)
(ng/mL) (ng/mL) (%)
(ng/mL) (ng/mL) (%)
(ng/mL) (ng/mL) (%)
10
ND . 7 .1 3
71
2 6 .2
4 7.3
211
1 .0 5
1 1 .6
106
1 6 .3
2 5 .5
92
Outfall 001
High Fiald Spiks
250
ND
222 89
2 6 .2
500 190
1 .0 5
246
98
1 6 .3
243 91
Outfall 001 Spk C
Low Lab Spika
1
ND
1 .2 9
129
2 6 .2
2 9.2
"
1 .0 5
2 .3 4
129
1 6 .3
1 8 .2
"
Outfall 001 Spk D
High Lab Spika
500
ND
640 , 128
2 6.2
936 182
1 .0 5
510 102 16.3
544 106
Field Blank
Low Fiald Spika
10
ND
1 7 .2
172
ND
1 2 .8
128
ND
1 0 .8
108
ND
1 0 .5
105
Field Blank
High Fiald Spika
250
ND
213 85
ND
182 73
ND
241 96
ND
238 95
Sample Description
Outfall 001 LowFialdSpika
FBSA
FOSA
Me-FBSE-OH*
Amount Amt Found Amount
Amt Found Amount
Amt Found Amount
Spiked in Sample Recovered Recovery in Sample Recovered Recovery In Sample Recovered Recovery
(ng/mL) (ng/mL) (ng/mL) (%)
(ng/niL) (ng/mL) (V.)
(ng/mL) (ng/mL) (*/.)
10
9 .2 4
1 9 .7
105
2.51 ,
13.1
106 0 .9 7 3
1 5 .7
147
Outfall 001
HighFialdSpika
250
9 .2 4
257
99
2.51
,2 5 1
99 0.973 244
98
Outfall 001 Spk C LowLabSpika
Outfall 001 Spk D HighLabSpika
1 500
9 .2 4 9 .2 4
1 1 .3 561
-
110
2.51 2.51
3.58 107 0 .9 7 3 532 106 0 .9 7 3
1 .7 6 532
79 106
Field Blank
LowFialdSpika
10
ND
9 .6 2
96
ND
1 0 .6
106
ND
1 1 .3
113
Field Blank HighFialdSpika
250
ND
259 104
ND
266 106
ND
393 157
ND = Not detected = Response between 0 and 1 ng/mL.
*ND a Not detected * Response between 0 and 4 ng/mL.
.
"S am ple residue exceeded the spiking level by more than 4 times; therefore an accurate recovery cannot be calculated.
J&30,3505E8 Research Drive jr m s tSatatte College, PA 16801, USA
V,T: 800.281.3219 F: 814.272.1019 exygen.com
Section C
3058 Research Drive State College, PA 16801
Phone:814-272-1039 Fax: 814-231-1580
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Login #: Project:
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Water
Outfall 001 Effluent 10 ppb Spk
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Outfall 001 Effluent 250 ppb Spk
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Field Control/Travel Blank
Water
Field Control/Travel Blank 10 ppb Spk
Water
Field Control/Travel Blank 250 ppb Spk
Date Sampled 05/25/2005
05/25/2005
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05/25/2005
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5/18/2005 Project: E05-0368
3M ENVIRONMENTAL LABORATORY Preliminary/Unauthorized Report
Page 1o f2
Requester: Schnobrich, Dana M (223-1N-08) Department: 530711 Project Number: 0022674449 Date Received: 5/17/2005 Project Description: Decatur Outfall 001 FC Monitoring Quarterly Comments:
Completion Date: Project Lead: Kent Lindstrom Phone Number: 651-778-5352 Email Address: krlindstrom@mmm.com
Statement of Accuracy:____________________________________________
ProjePcatcRe eFsiuelldts/SAacmtipvliitnvg Event
3M Sample Number______Sampled Date______Sample Description____________
E05-0368-82837
5/24/2005
Outfall 001 Effluent - Composite
LAB EXYGEN
Analytical Method LCMS
Components PFOS PFHS PFBS FOSA PFBAmide MeFBSE-OH C4 acid C5 acid C6 acid C7 acid PFOA C9 acid CIO acid Cll acid C12 acid
Result
E05-0368-82838
5/24/2005
Outfall 001 Effluent - Composite Duplicate
LAB Analytical Method EXYGEN LCMS
Components PFOS PFHS
Result
PFBS FOSA PFBAmide MeFBSE-OH C4 acid C5 acid
C6 acid C7 acid PFOA
C9 acid
CIO acid Cll acid
C12 acid
RL Qualifier RL Qualifier
2
f in
5/18/2005
3M ENVIRONMENTAL LABORATORY Preliminary/Unauthorized Report
Project: E05-0368 (cont.) 3M Sample Number______Sampled Date______ Sample Description_______
E05-0368-82839
5/24/2005
Field Control/Travel Blank
LAB EXYGEN
Analytical Method LCMS
Components PFOS PFHS PFBS FOSA PFBAmide MeFBSE-OH C4 acid C5 acid C6 acid C7 acid PFOA C9 acid CIO acid Cil acid C12 acid
E05-0368-82840
5/24/2005
Equipment Blank
LAB Analytical Method EXYGEN LCMS
Components PFOS PFHS PFBS FOSA PFBAmide MeFBSE-OH C4 acid C5 acid C6 acid C7 acid PFOA C9 acid CIO acid Cil acid
Result Result
Page 2 o f2 RL Qualifier
RL Qualifier
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S e c tio n D
Required Client Information:
S A M P L E ID
One character per box. (A-Z, 0-9 /
Scim ple IDs M U S T BE U N IQ U E
0 m T - p A t L. o
J f Um
X t A U _k_ c nat L_ i f L .e<A V
Valid MatrixCodes
MATRIX
CODE
DRINKING WATER DW
GROUNDWATER GW
SURFACEWATER SW
WASTEWATER WW
PRODUCT
P
SOIL SL
OIL OL
WIPE
WP
AIR AR
OTHER
OT
0 f
3"
% >os lC
<2 U ml . (
3
iW C _L
J E i Co p \ a \
A rt IL _
X 2 `S3
START
COLLECTED
END
DATE TIME DATE TIME
/ / 5 3 S b s fo i I l S b
// ' F i sb sb s f!S 3 --------------- .
1! : S i
MATRIX CODE SAMPLE TYPE G=GRAB C=COMP. SAMPLE TEMP AT COLLECTION Unpreserved NaOH Methanol Other
Preservatives
D /< r /r Y ' / " Y v 13
Tt 0CCOM
CO
O Z
o
1 XX
l
1 i
CO OC\J CCCOOM z
//f//////
---- -- ....
--- --
r%
_ _
IT E L O C A T IO N
N C ~ SC GA Other_________
NPDES UST
REGULATORY AGENCY
G RO UND WATER DRINKING WATER
RCRA
Other.
SAMPLE CONDITION
SAMPLE NOTES
Temp in C Received on Ice Y/N
A / otF : Effuip
C o//ft+c4
yo
Sealed Cooler Y/N
Sam ples Intact Y/N Additional Comments:
2
.. ,
M.Al c(\ lourde. -- YTUjf^L
(n i+ i A L- o ^ T a Lu oo \
O *I3
COrApo&rti OU^^L1 ooK Fi iACt.t ouf LL o p t
---------------
RELIN Q U ISH ED BY / AFFILIATION j a : j
____ / f o t f*
-
il* --
------------------------- -- A F F IL IA T IO N
/ -----------------------
DATE TIME V '/ ^ f / C ? -
SA M PLER NAME AND S 'G NATURE PRINT Name
SEE
CUr4_
DATE Signed: (MM / DD / YY)
j '/J S -/O S
: SIDE FOR INSTRUCTIONS
Form COC01 Rev. 0304
F ace Analytical
/ www.pacalaks.coni
Required Client Information:
Section A
Required Client Information:
CHAIN-OF-CUSTODY / Analytical Request Document
The Chain-of-Custody is a LEGAL DOCUMENT. All relevant fields must be completed accurately.
Section B
8570S6
To Be Completed by Pace Analytical and Client
Section C
NC SC . GA Other_________
NPDES G RO UND WATER DRINKING WATER
UST
RCRA
Other.
SAMPLE CONDITION
SAMPLE NOTES
Temp in C Received on Ice Y/N
a Jt? :
Ce//ft4cef
Sealed Cooler Y/N
Samples Intact Y/N Additional Comments:
3
'Total.
i A,+ I A L
irvuu c?o \
C^posrt en1 oov
OUif*Lt- 00{
-- rrwj/-_ G `I2
R ELIN Q U ISH ED B Y / AFFILIATION DATE TIME
ACCEPTED BY / AFFILIATION
jh
^4^
A " -------- ----------- _ / 7 -
DATE TIM E
SA M PLER NAME AND SIG N A TU R E
PRINT Name o f SAMI
m
, /^ ;
uTa
DATE Signed: (MM / DD / YY)
SEE
SIDE FOR INSTRUCTIONS
Form COC01 Rev. 0304
CHAIN-OF-CUSTODY / Analytical Request Document
'aceA nalytical*
www.pacelahs.eom
Required Client Information:
Company
3 jr ) e
Address
Section A r i, s s
Q 7IS-
The Chain-of-Custody is a LEGAL DOCUMENT. A ll relevant fields must be completed accurately.
Required Client Information:
Report To:
ffif.
Copy<TTVov:
S.
Section B E l d r tcktg,
I
_______ ___________ Page: / of /
857096
To Be Completed by Pace Analytical and Client Quote Reference:
Client Information (Check quote/contract):
Invoice To:
Requested Due Date:
*TAT:
Project Manager: " .
LAP.O.
'T u rn around time less than 14 days subject to
Project #:
Project Name:
O u if A U t- o o |
laboratory and contractual obligations and may result in a Rush Turnaround Surcharge.
Turn Around Time (TAT) in calendar days.
Profile #:
Project Number:
T
Section C
Section D
Required Client Information:
SAMPLE ID
Valid Matrix Codes MATRIX DRINKING WATER GROUNDWATER SURFACE WATER WASTE WATER
CODE DW GW SW WW
CL
clO >o UJOh
Preservatives
O ne character per box. (A-Z, 0-9 / . - )
Sam ple IDs M U S T BE U N IQ U E
PRODUCT SOIL OIL WIPE AIR OTHER
P SL OL WP AR OT
Jm
5;-<c0c
*h o
5l e
Sa 3 H .r -
ALL
C<>i l
Sl* ik // S3 Shs!o$
< * i t I
i l ii&
Q jj.
A I L i
oo
VB t*
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ajj
Sk,f tt.o i
//
Si
sfa bs U-
< 1e
Ft Co A
Q ' B \AA
^ /c
Remarks / U b >01
NC SC ,] GA Other_________
NPDES GROUND WATER
UST
RCRA
SAMPLE CONDITION
SAMPLE NOTES
DRINKING WATER O th er.__________
Temp in C Received on Ice Y/N
;I C e l/ftM
AfbT
Sealed Cooler Y/N
Samples Intact Y/N Additional Comments:
4
Torni-
I c(tlorndE --
In ,4 1a L. ow* Fp Lu oo t
O i <?
Cnvnpotrtf O iA 1 1*1.1 o o (
t i t O tol
!
y*
S A M P LE R NAME AND PiG N A TU R E PRINT Name o f SAM]
SIGNATURE
rn L L
f
DATE Signed: (MM / DD / YY)
S /J trjo s
eliSEE
ERSE SIDE FOR INSTRUCTIONS
Form COC01 Rev. 0304