A. Śrębowata et al. / Catalysis Communications 57 (2014) 107–110
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red-C-NiSiBEA with formation of Ni ions that can migrate and incorpo-
rate into zeolite framework.
Fig. 3 and Table 1 show the results of hydrodechlorination of trichlo-
roethylene on parent BEA zeolites and nickel-containing BEA zeolites
with different Si/Al ratio. Red-C-SiBEA shows only a negligible activity
which is in agreement with our earlier study observed during conver-
sion of 1,2-dichloroethane [13]. Addition of 2 wt.% of nickel to
dealuminated BEA (SiBEA) leads to formation of the active catalyst in
hydrodechlorination of tichloroethylene. Time on stream behavior
shows the most spectacular changes of the total conversion of TCE dur-
ing the first two hours of reaction with red-C-NiSiBEA. After this time,
the activity is stabilized on the value characteristic for steady state con-
ditions (Fig. 3). For red-C-NiSiBEA the summary selectivity toward
unsaturated hydrocarbons (ethylene and propylene — the most impor-
tant starting products in the petrochemical industry, manufacturing of
plastics) is close to 55% and additionally 1,1-dichloroethylene (the com-
pound used for production of certain plastics, and also in semiconductor
device fabrication) as the main product is formed (Table 1). Red-C-
HAlBEA with Si/Al ratio of 17 shows small, but about 5 times higher con-
version than this obtained on red-C-SiBEA. Both, red-C-HAlBEA and red-
C-NiHAlBEA were deactivated as a function of time much stronger than
red-C-NiSiBEA. The difference in catalytic behavior of two parent red-C-
SiBEA and red-C-HAlBEA zeolites and nickel containing red-C-NiSiBEA
and red-C-NiHAlBEA zeolites could be related to the presence of acidic
sites and the ration between the amounts of Brønsted and Lewis acidic
sites, as it was reported earlier [12,13]. It seems that the presence of
big amounts of strong Brønsted acidic sites is responsible for the activity
of red-C-HAlBEA catalyst with more than 90% of selectivity toward eth-
ylene (desired product of HDC of TCE). The presence of small nickel
nanoparticles in red-C-NiHAlBEA leads to the formation of olefins (eth-
ylene and propylene) as the main products (Table 1) and additionally
1,1-dichloroethylene as the effect of the presence of Lewis acidic sites.
Our results are in agreement with the earlier studies of
hydrodechlorination of trichloroethane [12,14,15], where Lewis acidic
sites were suggested to be involved in the reaction leading to 1,1-
dichloroethylene as the major reaction product. For nickel containing
zeolites, the selectivity towards 1,1-dichloroethylene increased propor-
tionally to amounts of Lewis acidic sites. Maximally 45% of selectivity
was obtained for red-C-NiSiBEA with the most amounts of Lewis acidic
centers (Table 1).
Fig. 2. XRD patterns of red-C-NiSiBEA, spent-red-C-NiSiBEA, red-C-NiHAlBEA and spent-
red-C-NiHAlBEA.
these materials, as reported earlier [13]. Additional investigations of the
catalysts after kinetic run have shown that after hydrodechlorination of
TCE the crystal structure of BEA is still preserved. Furthermore, compar-
ison investigations of the zeolites catalysts after reduction and reaction
(Fig. 2) have shown that for catalyst based on NiHAlBEA only negligible
shift of the main diffraction peak is observed (from 2θ = 22.46 for red-
C-NiHAlBEA to 2θ = 22.47 for spent-red-C-NiHAlBEA). However, for the
catalyst prepared by two-step postsynthesis method significant shift of
the main diffraction peak is observed (from 2θ = 22.54 for red-C-
NiSiBEA to 2θ = 22.41 for spent-red-C-NiSiBEA). It suggests that proba-
bly upon reaction test the oxidation of nickel nanoparticles occurs on
From the practical point of view, very important is the separation of
the value added products of hydrodechlorination of TCE. From tradi-
tional methods of hydrocarbons separation particularly noteworthy is
low-temperature distillation. In the case of ethylene /propylene separa-
tion this method is integrated with cascaded ethylene/propylene refrig-
eration system or even cryogenic distillation [16]. Economically,
attractive method of separation is the chemical affinity based technolo-
gy like π-complexation of the silver and copper ions [17]. Additionally,
for separation of olefins from 1,1-dichloroethylene we can use rectifica-
tion column, and absorbers for trapping of HCl. All of the above solutions
can be used for separation of HDC TCE products.
It should be noted here that there are only few reports showing the
catalytic conversion of trichloroethylene in the gas phase at a rather low
reaction temperature — 503 K. Generally, hydrodechlorination of TCE
were carried out at the temperature range of 373–573 K [18], but the
desirable results were observed at higher temperatures [18,19]. For ex-
ample, Meshesha et al. [11] showed results of hydrodechlorination of
TCE at 573 K. During 270 min of reaction over Pd/NiMgAl mixed
oxide, strong deactivation was observed, and the selectivity to ethylene
for NiMgAl was maximally 55%. Reactions with Cu-hydrotalcite-derived
catalysts [20] and Pt/CeO2 [2] have shown very high activity of the cat-
alysts at 573 K. At the temperature of 473 K the conversion for 0.2% Pt/
CeO2 was about 5% and ethylene and ethane were obtained as the main
products [2]. In view of the literature data our results obtained for
hydrodechlorination of trichloroethylene in a relatively low reaction
temperature are satisfactory. It is worth noting here that rather rarely
Fig. 3. Time on stream behavior during hydrodechlorination of trichloroethene, TCE con-
version at the temperature of 503 K.