Document 71MX9kO44B1ZJxZyovQVL25ve
A W IG -o o sn
fc-i
WATER SOLUBILITY
TEST SUBSTANCE
Identity: Perfluorooctanesulfonate; may also be referred to as PFOS or FC-95. (1-Octanesulfonic acid, 1,1,2,2,3,3,4,4,5,5,6,6,7,7,8,8,8heptadecafluoro-, potassium salt, CAS # 2795-39-3)
Remarks: The test substance is a white powder. Sample was taken from 3M lot number 217. Sample was stored under ambient conditions prior to testing. Purity determined to be 90.49% by LC/MS, 1FI-HMR, 19FNMR and elemental analyses techniques.
METHOD
Method: OECD 105, OPPTS 830.7840, and 40 CFR 796.1840. GLP (Y/N): Yes Year completed: Study completed 1999. Report completed 2000
Remarks: The definitive test consisted of equilibration of an excess amount of test substance with NANOpure water at 30C followed by equilibration at 20C and analyzing subsamples by high performance liquid chromatography with mass spectrometric detection (LCMS).
NANOpure water is equivalent to ASTM Type II Designation D1193-91.
RESULTS
Value (mg/L) at temperature C: 519 mg/L at 20 0.5C. Description of solubility: Slightly soluble.
Remarks: Triplicate subsamples were removed from the appropriate bottles after one, two and three days of shaking in a water bath maintained at 30 1,0C and following one day of a 20 0.5C equilibration period. Analysis of aqueous subsamples after one day had a mean analytical result of 459 mg/L (SD = 8.96, CV = 1.95%). For subsamples collected after two and three days, the mean concentration were 537 mg/L (SD = 27.6, CV = 5.14%) and 501 mg/L (SD = 64.2, CV = 12.8%), respectively.
000150
CONCLUSIONS The Day 2 and Day 3 mean solubility concentration were within 15% of each other and were averaged to obtain the overall mean solubility concentration. The overall mean solubility concentration of the test substance in NANOpure water was 519 mg/L (SD = 48.3; CV = 9.31%; N = 6). Submitter: 3M Company, Environmental Laboratory, P.O. Box 33331, St. Paul, Minnesota, 55133 DATA QUALITY Reliability: Klimisch ranking 1. REFERENCES Study conducted at the request of 3M Company by Wildlife International, Ltd. of Easton, Maryland. OTHER Last changed: 5/3/00
000151
WATER SOLUBILITY
TEST SUBSTANCE
Identity: Perfluorooctanesulfonate; may also be referred to as PFOS or FC-95. (1-Octanesulfonic acid, 1,1,2,2,3,3,4,4,5,5,6,6,7,7,8,8,8heptadecafluoro-, potassium salt, CAS # 2795-39-3)
Remarks field: The test substance is a white powder (3M Lot 583) of uncharacterized purity.
The following summary is abbreviated due to the fact that this study has been superceded by a more recent test.
METHOD____________________________________ ____________________
Method: Procedure developed by M. T. Pike and E. A. Reiner of 3M Company
GLP (Y/N): No Year (study performed): 1980 Remarks field: Test was done in deionized water.
RESULTS___________________________________________________
Value at temperature C: 1.08 g/L at 22.5C
Description of solubility (e.g., miscible to soluble to not soluble): Slightly soluble.
DATA QUALITY_________________________________________________
Reliability: Klimisch ranking = 2. This study satisfied criteria for quality testing at the time performed, but actual concentrations were not measured. The value was determined by indirect measurement. Additionally, this study lacks sufficient characterization of the test substance purity.
REFERENCES_________________________________________________
This study was conducted by the 3M Company, Environmental Laboratory, 1980.
O T H E R ________________________________________________________
Submitter: 3M Company, Environmental Laboratory, P.O. Box 33331, St. Paul, Minnesota, 55133
Last changed: 5/3/00
000152
Comments on
"Solubility Measurements on FC-95" E. A. Reiner, W. A. Scheil Project 9970012600 Commercial Chemicals Division, Report No. 49, Feb 6. 1961.
G eneral Preface: It has been indicated by 3M personnel that the fluorochemical products produced are invariably mixtures o f compounds with somewhat variable chain lengths and positional isomerism. Given this, the definition o f "solubility" o f a particular product has little meaning except in an operational sense. That is, one can say (assuming that adequate experimental procedures are followed and that appropriate analytical tools are at hand) that the total amount o f fluorocarbon substance dissolving in water from a particular batch is a certain value. That value o f solubility is probably not pertinent to another batch unless the chemical composition o f the second batch is identical to the first. This is particularly im portant in die case o f determining solubility of surface active substances because anionic surfactants which may be near their K rafft points in a particular solubility experiment w ill show substantial changes in solubility w ith tem perature, chain length, isomeric structure, and counter-ion (e .g ., lithium , sodium or potassium).
The procedures used in the current report are really not adequate for solubility determination. In general, a number o f solutions o f differing concentrations should be prepared and analyzed after equilibration. The approach to equilibrium should be done in both directions, i.e ., from lower and higher temperatures to the temperature o f interest.
The solubility result from this report is in agreement with the result (1 .0 8 g/1) for FC-95 from Env. Lab. Request No. 5372S o f Dec. 2, 1980. However, no higher concentration mixtures o f FC-95 ( than 0.25% ) with water were attempted and this is a defect o f the report. There is a disturbing suggestion in the report that the "solubility" may be a function o f the quantity o f FC-95 mixed w ith water (see p. 2, Introduction, text following "The Commercial C hem icals. . . " . If solubility is to mean anything, one should get the same value with differing amounts o f solid phase present.
Edwin E. Tucker, Ph. D. 1805 Aladdin St. Norman, OK 73072 M arch 1, 1993
000153
Fo rm 6747-11 -
TECHNICAL REPORT SUMMARY
Oate
2- 6-81
TO : T E C H N IC A L C O M M U N IC A T IO N S C EN TER - 201-2CN
(Im p o rtan t -- I f report is printed on both sides o f paper, send two copies to TCCJ
D iv is io n
P ro ja c t
Environmental Laboratory (EE & PC)
Commercial Chemicals Division
R eport Title
To Solubilitv Measurements on FC-95
ept Number
0535
Project N um bar
9970012600
Report Number
049 ------------------------------------- ---------------
Don Ricker ,,
A u th o r(s )
r
E. A. Reiher,
N otebook Rafaranca
None See Env.
'
,,
W. A. Scheil
Lab Request No.
5372S
Em ployee NumberU)
47816 214128
No. o f Pages In clu dingC o vershe et
5
SECURITY
: Open (Company Confidential)
Closed (Special Authorization)
3M CHEMICAL w REGISTRY ~
New Chemicals Reported
Yes
03 No
KEYWORDS: (Select terms from 3M Thesaurus. Suggest other applicable terms.)
CURRENT OBJECTIVE:
To measure the water solubility of Commercial FC-95.
Carcraercial Chemical; >
Environmental Lab
EE & PC Solubility
______________________________________________________ _____________
REPORT ABSTRACT: (200-250 words) This abstract information is distributed by the Technical Communications Center to alert 3M 'ers to Company R&O. '
Replicate laboratory measurements showed, the water solubility of FC-95, Lot 583, to be 1.08 g/1 at 22.5C. The procedure for determining this solubility involves stirring 2.5 grams of -FC-95 in deionized water for 24 hours, settling for 1 hour, and filtering through a 0.45 ul membrane filter or filtering through a 0.7 ul glass-fiber filter or centrifuging at 12,000 x G for 10 minutes. TOC measurements on the saturated solutions developed by all 3 of the above procedures varied from each other by <1%. The complete solubility of FC-95 at 0.25 g/1 demonstrated that saturation and not the presence of insoluble components caused the incomplete dissolution of FC-95 with 2.5 g/1 mixtures.
Information Liaison
W\c1
000154
Solu. Meas. FC-95 - EAR/WAS Page 2 February 16, 1981
INTRODUCTION
This project, to measure the water solubility of commercial
FC-95, was undertaken because of large discrepancies that existed
between measurements made by the Environmental Laboratory and by
Commercial Chemicals Laboratory. The Environmental Laboratory
had used the Veith techniqued) for saturating water with organic
materials. The saturation procedure utilized radio-labeled FC-95
and saturated the solution by recycling water through an FC-95
coated column for 48 hours prior to determining a concentration
of 286 mg/1 b y scintillation counting(2). The Commercial
Chemicals reported solubility value for FC-95 is 1 gram per 100
grams of distilled water, which is 35 times the previous
Environmental Laboratory's measured concentration. CCD's
procedure, however, involved mixing very large quantities of the
Commercial FC-95 with water and may have selectively dissolved
very soluble components of FC-95.
\
The present study measures the water solubility of FC-95 using water-product mixture levels that are near the saturation level, and thus should eliminate the possible error in the Commercial Chemicals' technique.
METHODS AND MATERIALS
The measurements utilized FC-95, Lot 583.
Test mixture concentrations were 2.5 grams and 0.25 grams per liter. Mixing took place in a 20+lC incubator, using 1 1/2" Teflon-coated magnetic stirring bars and magnetic stirrers. Styrofoam sheeting separated and insulated the bottles' containing the test mixtures from the heat generated by the magnetic stirring boxes.
At the end of the stirring period (24 hours), the temperature of the test solutions were 22.6C for the 2.5 g/1 mixture and 23.2C for the 0.25 g/1 mixture, indicating incomplete insulation. Following mixing, the mixtures settled for 1 hour prior to pipetting off the supernatants and their division into 3 aliquots. Three separate procedures, performed in parallel, insured complete clarification of the supernatant. These included: 1) filtration of one of the 3 aliquots from each mixture through a 0.7 urn glass-fiber filter, 2) filtration through a .45 um millipore membrane filter Type HA, and 3) centri fugation at 10,000 rpm (approx. 12,000 x G) at 20C for 10 minutes
Solub. Meas. FC-95 - EAR/WAS Page 3 February 16, 1981
TOC measurement provided the data for the calculation of the FC-95 concentrations in the filtrates and supernatants. Boiling the millipore filters 3 times for 1 hour and washing the glass-fiber filters thoroughly with distilled water before filtering insured that the filters did not add organic material (TOC) to the filtrate. The calculation of the FC-95 concentrations assumed a TOC of 17.8%. This is the theoretical TOC and is also the TOC we have measured in our laboratory analysis of FC-95.
RESULTS AND DISCUSSION
Table 1 shows the results of the dissolved TOC (DOC) measurements and the corresponding FC-95 concentrations. The data shows that at .25 g/1, FC-95 is completed dissolved. This indicates that there are no very insoluble components of FC-95. At 2.5 g/1, only approximately 1 g/1 is dissolved. This identical result was obtained using all three clarification procedures. In addition, as a quality assurance test, TOC measurements were made on potassium hydrogen phthalate solutions of known concentration (Table 2). These controls demonstrated the accuracy of our TOC procedure.
REFERENCES
(1) G. D. Veith and V. M. Comstock, J. Fish. Res. Board Can. 3 2 , 1848 (1975).
(2) Art Mendel, Analytical Methodology and Support, Dept. 0535, Project 9970612643, Report 008, 1/17/79.
EAR/cel Attachments:
Table 1 and 2
000156
TABLE 1
DISSOLVED TOTAL ORGANIC CAHBCN (DOC) AND CALCULATED SOLUBLE CONCENTRATION OF FC-95
Initial Concentration of FC-95 Water Mixture
250 mg/1
2,500 mg/1
SOLIDS REMOVAL PROCEDURE
Filtration
(0.45 um IVF)^ DOC Cone.
US/1
m/1
43.2
243
Filtration
(0.7 um GF/F)2
DOC Cone.
mg/1
mg/1
43.6
245
Centrifugation
(10 min. @ 1200 x G
DOC Cone.
mg/1
mg/1
45.2 45.43 44.53
253*
192.0 192.63
1,080*
191.6 192.63
1,080* 193.4 . 193.23
1,090*
Footnotes:
0.45 urn membrane filter 0.7 um glass-fiber filter Replicate analysis Solubility is calculated from average DOC.
V
000157
TABLE 2
DOC MEASUREMENTS AND CALCULATED CONCENTRATIONS OF STANDARD SOLUTIONS
Concentration of Potassium Hydrogen Phthalate (KHP) Standard
382.5 mg/1
Theoretical DOC
180.0
150 mg/1
70.6
Measured DOC
181.2 179.51 178.91
72.0 71.ll 70.61
Footnotes: 1 Replicate analysis 2 Solubility is calculated from average DOC.
t
\
KHP Concentration Calculated from DOC
382.32
1512
000158
Form 10620*0 PWO
Request For Laboratory Work Environmental Lab-EE & PC Bldg. 2-3E (9)
u
B d lC R B M ER
D e p t. Charge
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0222
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Requester 0535
Request O at*
P ro je ct N o.
P roblam No.
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D escription
F t-ir
R equirad T u rn -a ro u n d
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Purpose o f Data
Agency O Internal
C om m antt _
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C ontract Lab
Estim ated Lab H rs.
E xpected C o m p le tio n D ate
Hours (E L I
to
Date Completed
/2 - 0 2 -Bo
C ost (CL)
Sample N o. Code D ate D escrip tion
^7
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2
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34 5 V* "l ?
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Samples w ill be d isca rd e d 3 0 d ays a fte r c o m p le tio n o f analysis unless o th e rw is e n o te d
Da wApproved By U S -g o
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/A 4 -
000159
/l.CEC: 0535 A ti
REGUEST FOR LABORATORY WORK FINAL REPORT
LAB REQUEST NO. 5372S
RECUESTCR-- EIRE: ear
FFCJEC1 NC. 5970012600 CISC: EC 55 LOT 583
-- LAB PERSONNEL
DA1E RECEIVED: 2/01/1980
ANALYST: WAS
DATE COMPLETED: 12/02/1980
HRS SPENT: 10
ICTICA' DATE
11/24/198C
12/02/1980
CCCfa CITE JIC.CEC.
TEST SCLIEIl ITV ICC TCC ICC
COCE CITE ICC-DEC.
TEST SGLUBIlm TCC ICC TCC
0.025* 0.45UM M/F 01 43.2 MC/L
0.25* 0.45UM M/F 05 1080 MG/L 192.0 MG/L 192.6 MG/L
0.025* C.7UM CF/F 02 43.6 MG/L
0.025*
CENTRIFUGE
03 r, t
45.2 NG/L 45.4 MG/L 44.5 MC/L
\U o ^ STD #35
04
72.0 MG/L 7 71.1 MG/L ( 7* 70.6 MG/L
0.25*
0.7UM GF/F
06 1C80 MG/L 151.6 MG/L 152.6 MG/L
0.2b*
CENTRIFUGE
07 1090 MG/L 192.4 MG/L 193.2 MG/L
CA T V - MSOrvyf. ^ STD #431
08
181.2 MG/L ) - 179.5 MG/L ?
178.9 MG/L)
*********** ***********************
* SAPPLE DISCARD DATE 1/01/1981 *
**
**********************************
000160
Internal Correspondence
ce: D. R. Ricker - 53-4 D. L. Bacon/R. L . B o h o n - ;21-BW (63)
\aJ a b
To: M. T. PIK E - COMMERCIAL CHEMICALS DIVISION - 236-2A01 P'om E. A. R E I N E R - ENVIRONMENTAL LABORATORY (EE&PC) - 2I-BW (63) Subieci S O L U B I L I T Y DETERMINATION ON FC-95 Da J A N U A R Y 30, 1980
The following is technique we agreed to in our phone conversation of 1/30/80 to measure the solubility in water of PC-95:
1. Prepare 0.25% and 0.025% mixtures of FC-95 in deionized water.
2. Mix for 24 h o u r s ,4using a magnetic stirrer, s *
I K * -- - t v . , -- r<-- i --
r r ' t r V\
3. Le t settle for approximately 1 hour.
4. Pipette off the supernatants and divide the supernatants into 3 aliquots.
5. Filter one of the aliquots from each initial concentration ^ through a .7 >um glass fiber filter*. s,Va *'<'
6.
7. Coy i 0 * , ^
Filter the second aliquots through a . 4 5 /im millipore
0 c
Let the remaining (third) aliquots/! se*rtle fui 24- hours and-- remove a sample of the supernatants by pipette.
8. Do a TO C a n a lysis of the filtrates from Steps 5 and 6, and the supernatants from Step 7.
9. C a lculate the concentration of FC-95 by assuming a TOC of ' 17.8%. This is the theoretical TOC and also the TOC we have measured in our laboratory analysis of FC-95.
The filters used will be boiled 3 times for 1 hour using fresh Dl water to prevent filters from adding TOC to the filtrate.
000161
I
We estimate that this procedure, modified per our phone call, will take approximately 12 hours of technician time, zt will take longer than the 8 hrs. estimated in our original proposal because 6 rather than 3 samples will have to be prepared and analyzed. Our current recharge rate will cost approximately $375.00. If you have any further questions or comments, please feel free to contact me on 778-5079.
N
EAU/cel
000162
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WATER SOLUBILITY (BY ANALYSIS OF TOC)
TEST SUBSTANCE
Identity: Perfluorooctanesulfonate; may also be referred to as PFOS or FC-95. (1-Octanesulfonic acid, 1,1,2,2,3,3,4,4,5,5,6,6,7,7,8,8,8heptadecafluoro-, potassium salt, CAS # 2795-39-3)
Remarks field: The test substance is a white powder (3M Lot 583) of uncharacterized purity.
The following is abbreviated due to the fact that this study has been superceded by a more recent test.
METHOD
Method: Procedure developed by 3M Company GLP (Y/N): No Year (study performed): 1982 Remarks field: The two samples submitted for testing were duplicate filtrates of a mixture of the test substance dispersed in water at a concentration of 0.25%. Undissolved material was noted in the mixtures. The mixtures were stored in an incubator at 20 + 1C from 11 -24-80 until filtered through a Whatman glass fiber filter prior to TOC analysis on 6/16/82.
RESULTS
Values using the TOC Analyzer DC-80: Sample 1: 9ppm TC Sample 2: 9ppm TC
Values using the TOC Analyzer DC-52 High Temperature (800C) method:
Sample 1: 195 ppm TC Sample 2: 195 ppm TC
Remarks: Results for the DC-80 UV-Persulfate Analyzer indicated there was no breakdown of the C-F bond, so it was determined that this was an unacceptable method. It is noted that the test author felt the DC52 analysis was accurate. Therefore using the molecular weight of Perfluorooctanesulfonate (538), a solubility of 1090 mg/L can be calculated.
Description of solubility (e.g., miscible to soluble to not soluble): Slightly soluble.
000167
DATA QUALITY Reliability: Klimisch ranking = 3. This study does not meet criteria for quality testing. Actual concentrations were not measured. The value was determined by indirect measurement. Additionally, this study lacks sufficient characterization of the test substance purity. REFERENCES This study was conducted by XERTEX, Dohrmann Division of Santa Clara, California, 1980 on the request of 3M Company. OTHER Submitter: 3M Company, Environmental Laboratory, P.O. Box 33331, St. Paul, Minnesota, 55133 Last changed: 5/3/00
000168
DOHRMANN DIVISION
3M24"*0v SCv Ou Ti Ti DBOWUbLcEvVnAnRuDi, SANT1 A WCLLA/Rv Ai a, \Cj iALIFORNIA 9 6 050 TELEPHONE (408) 727-8000 TELEX 3 4 6395
June 29, 1982
Wade Schell 3M/Environmental Lab Box 33331, Bldg. 2-3E-09 St. Paul, MN 55133
Bear Mr. Schell: We have completed thf analysis of your samples, Project No. 1653. The
results are summarized In the attached Application Report. As we discussed over the telephone, your perfluoronated organic samples
were analyzed for Total Carbon using two TOC methods: the DC-80 UV-Persulfate Analyzer and the DC-52 High Temperature Analyzer. It is apparent from the results that the UV-Persulfate Oxidation does' not breakdown the C-F bond so it is not an acceptable method. Since you already have a DC-52 but need to analyze for trace carbon, I suggest that you push it to its lowest detection limit possible by using the TC mode and keeping the system very clean.
If you have any questions concerning these results, please feel free to contact us directly.
Sincerely,
John T. Martin Applications Group Leader JTM/rad cc: Phil Brown
Fred Harper
O O O iG D
XERTEX
DOHRMANN DIVISION
3240 SCOTT BOULEVARD, SANTA CLARA, CALIFORNIA 95050 TELEPHONE (408) 727-6000 TELEX 346395
APPLICATION PROJECT REPORT REPORT NO. 1653
SYSTEM USED: Total Organic Carton Analyzer DC-80
INSTRUMENTAL CONDITIONS: As per equipment manual
SAMPLE TREATMENT: The two samples were analyzed for total carbon by injecting 20Oul aliquots.
DATA:
1653-1 1653-2
9ppm TC 9ppm TC
COMMENTS: Your perfluoronated organic was not completely oxidized by the UV-
persulfate reactor. The real TC in both samples as analyzed by the high temp
erature (800C) method on the PC-52 is 195ppmC.--- ,, f~ ~
l-S - t ^ 3 ^
/ f" -.s C*"1" 1^ *
RECOMMENDATIONS: Unfortunely the DC-80 TOC Analyzer can not be used to analyze
perfluoronated organics.
f*
EQUIPMENT REQUIRED FOR THIS ANALYSIS Instrumentation: Total Organic Carbon Analyzer DC-80
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