Document om2YEDV19xV6BJbK6VR8MqzpE
2-A7 KV. ).:-7S
AR226-3332
isra'uSticua;
E. I. DU PONT DE NEMOURS S COMPANY INCORPMATEO P. 0. Box 1217 PARKERSBURG, W. VA. 26101
PLASTIC PRODUCTS AND RESINS DEPARTMENT
TO; FROM
J.
P.
YUK
.
TEXTILE FIBERS DEPARTMENT
SPRUANCE PLANT
S. COPE
PP&R DEPARTMENT WASHINGTON LABORATORY
CC: E. D. Champney, D131S8
H. B. Voigt, Wilm A. A. Wright, T.F. Dept, Wilm M.-A. Forte, T.F. Dept, Spruance P. Thistleton, WW
R. E. Putnam, WL R. G. Brown, WL S. V. Gangal, WL
File; 8-5
September 25, 1979
CONCENTRATION LEVEL OF C-8 FLUOROSURFACTANT IM
PE-3311 DISPERSION
INTRODUCTION
We spoke by telephone about two weeks ago concerning
the level of C-8 fluorosurfactant present in TE-3311 dispersion transferred from our Department to yours for use in making^Hf|| fibers by the viscose process. At about the same time, I sfso had telephone discussions with A. A. Wright and M. A. Forte of your Department on the same subject. My understanding from these dis cussions is as follows:
Analyses at Spruance of the measurable C-8 levels in
TE-3311, primarily by extraction followed by esterification and
G. C. analysis, have shown about 200 ppm (100-300 ppm range) to be
present.
it
Since the level of C-8 used in the recipe for preparing
TE-3311 would lead us to expect about 1200 ppm to be present,
has been concluded that the unaccounted-for portion of the C-8 is
inaccessibly held ("trapped") within the PTFE polymer itself.
Attempts at Spruance to locate the "missing" C-8 elsewhere in the
spinning process or on the final product have been unsuccessful.
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These findings were not in accord with our general ex perience with regard to C-8 in PTFE dispersions, although no specific data were available along these lines for TE-3311 in particular. Accordingly, I set about determining the level of C-8 in TE-3311, using analytical techniques we have applied and found reliable in the past.
DISCUSSION
The TE-3311 sampleused-in the following analyses was from a recent lot,--------------------
Analytical Procedures
None of the methods of C-8 assay available to us can be
applied directly to "Triton" - stabilized PTFE dispersions. It is
first necessary to separate the C-8, for which purpose the technique
of adding a strong, non-volatile acid (phosphoric acid) and water
to the dispersion and distilling over the volatile C-8 acid (with
water) was employed. A detailed description of this procedure is appended.
The distillate fractions, containing successively lower concentrations of C-8 until essentially no further carry-over of
C-8 was taking place, were analyzed by a variety of complementary
methods:
NaOH titration
Chloroform/methylene blue analysis
Cetyltrimethylanmionium bromide titration.
HaOH Titration r,
Titrafcion with NaOH (0.1 N) to a phenolphthalein pink end-point gives results, when expressed as equivalent C-8 APFC (eq. wt. = 431), which are known to be high by this method, pre sumably because of the presence of small amounts of other volatile
acids carried over in the distillation.
Chloroform/Methylene Blue Analysis
It The chloroform/methylene blue analysis, regarded as the
preferred method of assay in this case, is based on formation of a
neutral complex between the cation of methylene blue hydrochloride
and the C-8 anion. The blue-colored complex is then partitioned
between fixed amounts of water and chloroform. The greater the
level of C-8 present, the more intense the blue coloration in the
chloroform layer. Measurement of the absorbance maximum at about
633 nm in the visible region by spectrophotometer serves as a
measure of C-8 assay, the relationship between absorbance and con
centration being established by measurement of prepared standard
solutions of known C-8 APFC concentration.
has-been demonstrated
that "Triton" X-100 and citric acid (used at low levels in TE-3311
for chelafcion of any iron adventitiously present) do not interfere
in the analysis of distillate samples by this method. A description
of the chlorofonn/methylene blue method is appended.
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(Incidentally, as you are no doubt aware, chloroform is now designated as a Suspect Carcinogen, and we would therefore prefer to avoid its use. However, a brief study of methylene chloride and "Freon" 113 as possible substitutes indicated that neither was suitable.)
Cetyltriinethylammonium Bromide Titration
The titration analysis using cetyltriniethylainnionium
bromide (CTMAB) solution (0.100% w/v) is based on the finding in
this Department that the cation of CTMAB forms a neutral 1;1 molar
comple^withthe C-8 anion." This
Hence,------------jrawdispersion may
complex be used
is
as
not surface-active. an "indicator" for
the titration; when the equivalence point is needed, the C-8 is no
longer effective as a surface-active agent to keep the polymer
particles dispersed, and they settle out^as a flocculent gel, leaving
the aqueous phase clear. Actually, rawM------|JFEP dispersion
(HFP/TFE copolymer) is preferred as indicator, since it contains
less C-8 to begin with and also happens to give a perfectly clear
aqueous supernate when the equivalence point is reached.
The CTMAB method, like the chloroform/methylene blue
method, is relatively specific for C-8, though "Triton" X-100, if
present, would certainly be expected to interfere. A disadvantage
of the CTMAB method, insofar as your possible use of it would be
concerned, is that raw FEP dispersion has a short shelf-life and is difficult to ship without coagulation occurring. A description
of the CTMAB method is appended.
Analytical Results
A summary of our analytical results on the TE-3311 sample
tested is given in Table I. Expressed as equivalent C-8 APFC, the
results obtained are:
Method used
NaOH Titration
CHCl3/Me Blue
CTMAB Titration
ppm C-8
(based on total
1950
1140
960
dispersion)
Recognizing that the NaOH titration results were expected to be high, the agreement -among the different results is considered
good. The indicated concentration of C-8 is at the level expected from our previous general experience, and several-fold higher than that obtained by extraction/GC analysis. We conclude that the C-8
present can be recovered and accounted for, and that little or no .
C-8 is located within the PTFE particles themselves, which, inci-, dentally, are known to be solid and very highly crystalline. We
do know that there is an equilibrium between C-8 adsorbed on the surface of the particles and C-8 dissolved in the aqueous phase... . At room temperature, the majority of the C-8 is adsorbed.
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Note the high sensitivity of the CHCl3/methylene blue
c
method, which permits reliable determination of C-8 in amounts as
low as 10 micrograms. For this reason, dilution of distillate
samples (typically by 20-fold) was required prior to C-8 assay by
this method.
..
One of the main attractions of the analytical procedures just described is that they should be applicable as well to deter-
Lnation of residual C-8 in the PTFE fiber products you produce a-t
One point we should like to emphasize with respect.to the C-8 analysis is that, although we have now apparently succeeded in accounting for the C-8 expected to be present, the result does not directly answer the question as to how accessible this C-8 is in terms of contact by personnel, e.g., by skin contact, or by in halation of vapors evolved on heating during fabrication operations.
Information on this subject could come only through more extensive testing of a more direct nature.
Program
I hope in the near future to "close the balance" on C-8
in the production of TE-3311 dispersion by measuring, using the
c
same methods given here, the C-8 concentration in the supernatant layer which is produced (and discarded) during the thermal concen
tration step in which raw dispersion (45% solids, known C-8 content)
is treated with "Triton" X-100 and raised to the 60% solids content.
of TE-3311. When these results are in hand, I shall let you know.
CSCope/ldl
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Attachments: 1 Table
\
3 Analytical Methods (Spruance copies only).
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