W. Han et al. / Journal of Fluorine Chemistry 131 (2010) 698–703
699
In this contribution, we report a novel catalyst, K2O/AC
(activated carbon), for the decomposition of CHF3 into C2F4
(TFE) and C3F6 (HEP). Activated carbon is chosen because it is stable
in strongly acid and basic environments. Catalysts supported on
various silica and metal oxides are reportedly unstable because of
the degradation of supports in the presence of corrosive HF. The
catalytic reaction was carried out in a fixed-bed reactor and the
effect of temperature on the reaction, as well as catalyst stability,
were investigated.
2. Experimental
2.1. Catalyst preparation
Activated carbon (1.0–1.4 mm) used as catalyst support,
originated from coconut shell, was provided by Hainan Activated
Carbon Co., China, with BET surface area of 993 m2 gꢀ1 and pore
volume of 0.51 cm3 gꢀ1. Catalysts were prepared by traditional
impregnation methods with KNO3 (Aldrich, 99%) as precursor.
Prior to impregnation, activated carbon was treated in 30% HNO3
solution at 363 K for 5 h in order to eliminate ash content in the
carbon. The nominal K loading was 10 wt%. The decomposition
temperature of KNO3 is approximately 673 K.
Fig. 1. Conversion of CHF3, carbon balance and formation rate of products as a
function of time-on-stream over activated carbon at 1073 K and
4300 hꢀ1
a GHSV of
.
(GHSV) of 4300 hꢀ1 to investigate the effect of support. The
support has little influence on the reaction compared to K2O/AC
(shown in Section 3.2), in particular after several hours on stream.
CF4 is the dominant carbon containing product with C2F6 being a
minor product. C2F4 and C3F6 were detected only in trace amounts.
Fig. 1 shows a typical run of CHF3 pyrolysis at temperature of
1073 K. The rate of formation of CF4 was relatively high in the first
hour and dropped rapidly until it reached a stable value.
Consensus exists in the literature that the initial step of
homogeneous gas phase pyrolysis of CHF3 is the elimination of HF
at temperatures above 1023 K leading to formation of CF2, which
rapidly dimerises to C2F4 which is the major product of the reaction
[10,11].
2.2. Temperature-programmed desorption-mass spectrometry
(TPD-MS) experiment of activated carbon
TPD-MS experiment was carried out on AutoChem 2910
(Micromeritics Co.) attached to a QMS 200 (Omnistar) mass
spectrometer. A 50 mg of sample was heated to 373 K in the
sample tube and held that temperature for 0.5 h in flowing helium
gas to remove absorbed water and other impurities on the surface
of the sample. After cooling down to room temperature, the sample
was heated to 1273 K at a ramp rate of 10 K minꢀ1 in He with a flow
rate of 40 mL minꢀ1. The effluent gas was monitored by a thermal
conductivity detector and mass spectrometer detector.
CHF3 ! CF2 þ HF
(1)
2.3. Catalytic experiments
A tubular high purity (99.99%) alumina reactor (i.d. 7.0 mm)
was employed for all experiments. Flow rates of CHF3 (>98%, Core
Gas) and diluting gas N2 (BOC gases, 99.99%) were controlled by
mass flow controllers (Brooks) to give a total flow rate of
220 mmol hꢀ1, with CHF3 accounting for 10% of the total volume
flow. The catalytic pyrolysis of CHF3 was carried out at a reaction
During decomposition of CHF3 over activated carbon, however,
only trace amounts of C2F4 are detected. This indicates that the
decomposition of CHF3 over activated carbon follows a mechanism
which is different from the homogeneous mechanism. Recently,
Yang et al. [12–14] studied the pyrolysis of CHF3 over activated
carbon and in their experiments, C2F4 was not detected. They
suggest that the reactions leading to formation of CF4 and C2F6 is
likely to be via the steps as illustrated in Scheme 1. However, this
seems to contradict the results of their efforts to capture the
difluorocarbene intermediate with H2 and 2-methyl-2-butene,
where no CH2F2 or gem-difluorotrimethylcyclopropane was
captured. Furthermore, when CHClF2 was introduced instead of
CHF3, virtually no CF4 or C2F6 were found in the products [15].
CHClF2 is believed to form CF2 radicals more readily via
dehydrochlorination compared with the elimination of HF from
CHF3. Apparently, an increase of CF2 does not facilitate the
formation of CF4 and C2F6, and the reaction steps proposed in
Scheme 1 likely play only a relatively minor role in the overall
reaction.
temperature between 873 and 1173 K, space velocity of 4300 hꢀ1
,
and at atmospheric pressure. HF formed during reaction was
trapped by a caustic scrubber (NaOH solution) before the reactor
effluent reached an online micro gas chromatograph. Carbon
containing products were identified by a GC/MS (Shimadzu
QP5000) equipped with an AT-Q column, and quantified with a
micro GC (Varian CP-2003) equipped with molecular sieve 5A and
PoraPLOT Q columns. Relative molar response (RMR) factors of
fluorocarbons for TCD detection were experimentally obtained
from standard gas mixtures, and quantification of halogenated
hydrocarbons was performed with diluted halogenated hydro-
carbons in nitrogen. Quantification of other species was estimated
from published correlations [8–10].
3. Results and discussion
3.1.2. Effect of surface oxygen groups
For the purpose of destruction of chlorofluorocarbons (CFCs),
Burdeniuc and Crabtree [15] discovered that the reaction of
sodium oxalate (Na2C2O4) with CFCs enables the complete
conversion of these environmentally hazardous species at
temperatures as low as 543 K. It is important to note that the
existence of oxygen groups on the surface of activated carbon,
3.1. CHF3 pyrolysis over activated carbon
3.1.1. Decomposition of CHF3 over activated carbon
Pyrolysis of CHF3 was conducted over activated carbon at
temperature range of 873–1173 K and gas hourly space velocity