R.K. Belter et al. / Journal of Fluorine Chemistry 127 (2006) 816–820
817
bed occurs readily under such conditions. Water generation also
has the disadvantage of removing the protective metal fluoride
layer from the inside of the reactor and accompanying fittings.
Corrosion and erosion result and damage to the equipment can
be extensive. As such, equipment must be replaced more
frequently, adversely affecting the economics of the process.
Selectivity and reactivity are reduced and eventually the
operation must be shut down and refurbished.
exchange occurs. Samples were drawn at 15 min intervals
and analyzed by GC.
2.1. Fluorination reactions with oxygen (O2)
For comparison purposes, reactions were run on R-30, R-
23 and R-133a over chromium-based catalyst with 1–2 mol%
O as a co-feed. Catalyst beds of chromium oxide-on-carbon
1
2
Alternative oxidants have been used to replace O and its
2
were preconditioned under a stream of HF vapor diluted in
nitrogen. A period of oxygen co-feed at or above the anticipated
reaction temperature preceded the initiation of reagent feeds.
Conditions were adjusted so as to be able to maintain a constant
and acceptable level of conversion, that is to say, catalyst
activity. Conversions averaged 70%, 55% and 40% respec-
tively.
accompanying water generation problem. Chlorine has been
used as a co-feed in the manufacture of R-32 [5,6] and R-134a
[
chlorinated by-products of the R-20 series (CHCl , CHFCl ,
3]. The main impurities reported for the R-32 process are
3
2
CHF Cl) and R-110 series (CFCl -CFCl , CF Cl–CFCl ). For
2
2
2
2
2
the R-134a process, the nature and level of by-products are not
disclosed.
Fluorine (F ) has wisely not been pursued as an alternative
2
oxidant due to its high reactivity and dangerous nature.
Chlorine fluoride (ClF) or chlorine trifluoride (ClF ) likely
2.2. Fluorination reactions with nitrogen trifluoride (NF3)
3
would also be problematic, if not dangerous, co-feeds [7]. As
such, we struck upon the idea of applying the high temperature
reactivity of nitrogen trifluoride (NF ) to our advantage and
To test the efficacy of NF as a catalyst activity stabilizer,
3
reactions were run on R-30, R-123 and R-133a over chromium
oxide-on-carbon catalyst beds prepared as above. HF and the
appropriate chlorinated compound were passed over the
3
sought to use NF as an oxidative co-feed in fluorine-for-
3
chlorine exchange reactions. While NF3 may seem an
expensive choice as an O substitute, there are fluorochemical
catalyst bed and a co-feed of NF was maintained during this
3
period. As anticipated, the activity of the catalyst was
maintained at a constant level. Conversions were closely
comparable to those observed during O co-feed. Conversion to
2
production facilities around the world where fluorination
processes and inexpensive NF streams are in close proximity.
3
2
R-32 averaged 69%, conversion to R-125 averaged 58%, and
conversion to R-134a averaged 34%. Most importantly, catalyst
activity during NF co-feed was maintained at levels parallel to
2
. Results and discussion
3
that of O co-feed.
2
We have now discovered that NF can be an alternative co-
3
Under the oxidant rich conditions that we chose to maintain
for our experiments, some oxidation by-products were formed.
Interestingly, the level and nature of by-products generated by
O co-feed and NF co-feed were similar. That is, while NF is
reagent for maintaining the activity of fluorination catalysts.
Three fluorine-for-chlorine exchange reactions were used to
evaluate the efficacy of this procedure. Dichloromethane was
converted to R-32. R-123 was converted to R-125, and R-133a
was converted to R-134a (see Scheme 1). Besides conversion
rates, particular attention was given the condition of the catalyst
after recovery from the reaction.
2
3
3
acting as an oxidant, it does not act as a fluorinating agent, even
at temperatures as high as 500 8C. Rather, for both reagents,
chlorine addition products were observed at slowly increasing
levels. For the fluorination of CH Cl with oxygen co-feed, R-
2
2
Vapor phase reactions were performed in an electrically
heated tubular reactor packed with active carbon supported
chromium oxide pellets. Reagents were vaporized and passed
over the heated catalyst bed where fluorine-for-chlorine
22 (CHF Cl) and R-23 (CHF ), at the 1% level, were indicative
2 3
of oxidation (see Graph 1). For the fluorination of CH Cl with
2
2
NF , R-22 and R-23 were observed at similar levels along with
3
some R-12 (CF Cl ). For the fluorination of R-123 with oxygen
2
2
co-feed, R-113a (CF -CCl ) was observed on G.C. at 1–1.5%
3
3
(see Graph 2). For the fluorination of R-123 with NF co-feed,
3
the level of R-133a was also about 1.5%. A closer look at both
product streams with GC/MS showed lesser amounts of R-114
(CF –CFCl ), R-115 (CF –CF Cl), R-13 (CF Cl) and CF –
CHCl–CHCl–CF . For the fluorination of R-133a, oxidation is,
3 2 3 2 3 3
3
as mentioned in the introductory reference, more prevalent.
Both R-123 and R-124 were observed, with oxygen co-feed
generating about 9% of combined oxidation products and NF3
co-feed generating 10% (see Graph 3). Clearly, just as O reacts
2
with HCl to form Cl in a Deacon reaction [8,9], NF was also
2
3
oxidizing HCl to Cl . This was supported by the plainly
2
detectable odor of chlorine observed at the reactor outlet (after
scrubbing with water).
Scheme 1.