[eqn. (1)]. A mechanism involving the direct reaction of NO, O2
and NO2 could not exceed thermodynamic limits. Therefore, the
current model of the alkene-SCR reaction over alumina-based
catalysts needs to be re-evaluated.5–7
At least two alternative solutions could be proposed to
explain the formation of the high concentrations of NO2
observed. First, a mechanism involving consecutive steps could
occur in which a nitro or a nitrite compound, e.g. nitromethane
CH3NO2, is formed along with CO (or CO2) from the reaction
of propene, O2 and NO [eqn. (2-1)]. Organic nitro or nitrite
species have often been quoted as possible intermediates of
SCR reactions.8 The subsequent oxidation of this organo-NOx
species would yield NO2 [eqn. (2-2)]
3
C3H6 + 2 O2 + 2 NO ? 2 CH3NO2 + CO
(2-1)
(2-2)
7
3
CH3NO2 + 4 O2 ? NO2 + CO2 + 2 H2O
Overall, eqn. (2-1) and (2-2) combine to give:
Fig. 3 Selective catalytic reduction of NO using propene over g-Al2O3 at
813 K as a function of the W/F: NO2 to NO ratio (a) experimental (2) and
C3H6 + 5 O2 + 2 NO ? 2 NO2 + 2 CO2 + CO + 3 H2O (2-3)
1
(b) at the thermodynamic equilibrium of the reaction NO + O2 Ô NO2
2
This mechanism is supported by the fact that thermodynamic
calculations show that the reactions given by eqn. (2-1) and
(2-2) are strongly exergonic over the temperature range
investigated here (e.g. DG°813K = 2298 kJ mol21 and 2734 kJ
mol21, respectively). Regarding a second possible mechanism,
the oxygen needed to form the NO2 could be supplied by
another molecule of NO, i.e. in a disproportionation reaction,
and not by the O2. An example of mechanism of SCR of NO
involving a disproportionation of NO to N2 and NO2 was
proposed by Smits and Iwasawa .9 These authors suggested that
one of the roles of the hydrocarbon, NO and O2 was to form a
radical molecule R* (e.g. 1-nitro-sec-propyl) which in turn
could propagate the disproportionation reaction:
(---). Feed: 500 ppm NO + 500 ppm C3H6 + 2.5% O2 in Ar, 200 mg of
alumina.
W/Fs greater than 180 mg s cm23. The striking feature of Fig.
2 is the sharp rise in the production of NO2 [Fig. 2(c)] as soon
as the conversion of propene reaches 100%. At propene
conversions lower than 95%, the presence of NO2 was not
detected (i.e. < 2.5 ppm). Upon completion of the conversion of
propene, the NO2 yield reached a value of approximately 25%
(corresponding to 127 ppm of NO2). With further increase in the
values of W/F, the NO2 yield gradually decreased. The gradual
decrease in the concentration of NO2 was accompanied by a
similar increase in the concentration of NO (not shown in Fig.
2) while the concentrations of all the other products of reaction
were either steady (N2) or decreased (N2O and NH3). Inter-
estingly, Fig. 3 shows that in the region of 100% propene
conversion (W/F ! 180 mg s cm23), the experimental values of
the molar ratios of NO2/NO were greater than 1. Hence, these
values were more than 10 times greater than the value of the
thermodynamic equilibrium ratio of NO2/NO (i.e. 0.09) calcu-
lated at the same temperature. The same results were obtained
whether the W/F was varied with increasing or decreasing
values.
Further experiments carried out using the same reactant
concentrations, at constant W/F (60 mg s cm23) and varying
temperature also showed that, at the temperature of 100%
conversion of propene, there was a sharp increase in the yield of
NO2. At 843 K, propene conversion was not complete and NO2
was not detected; however, at 873 K propene was fully
converted and NO2 yields of 30% were obtained (this value
again being well in excess of levels obtained from equilibrium
calculations). The sharp increase in the NO2/NO ratio at the
temperature of 100% conversion of propene was the same
regardless of whether the reaction temperatures were increased
or decreased.
4 NO (+R*) Ô N2 + 2 NO2 (+R*)
(3)
The thermodynamics of the disproportionation reaction de-
scribed by eqn. (3) essentially favour the right hand-side of the
equation at temperatures below 600 °C (and are independent of
the concentration of O2) and therefore this mechanism could be
responsible for the high yields of NO2 observed. Hence, one of
the possible role of the alumina (a known mild oxidiser) during
alkene-SCR reactions would be to allow the formation of
organic-nitro or nitrite species [eqn. (2)] and/or the formation of
a hydrocarbon-based propagator [eqn. (3)]. Experiments using
N18O and 16O2 are planned and should give some evidence of
the origin of the oxygen in NO2 (i.e. by observing either
N18O18O or N18O16O) to determine which of the two models
proposed is the most likely.
The conclusion of this work is that the formation of NO2
during the propene-SCR of NO over alumina is not obtained by
direct oxidation of NO by O2 but that a more complex
mechanism has to be considered.
Part of this work was funded by the European Community,
through the Environment and Climate Programme, Contracts
E5V5-CT94 and ENV4-CT97-0658.
It is evident from the results of experiments described in this
paper that NO2 could not be observed when propene was
present in the product streams. This can be explained by the
work of a number of different authors,4,6,7 who have shown that
alumina is very active for the reduction of NO2 by propene to
form N2. However, upon complete combustion of the propene,
the NO2 could not be reduced and was therefore detected in the
reactor effluent. Fig. 2 and 3 show that the maximum NO2/NO
ratio occurred at a W/F value of 200 mg s cm23, and at higher
W/Fs the ratio decreased towards the equilibrium ratio. This was
probably due to the slow decomposition of the NO2 to NO and
O2 (in the absence of propene) which Fig. 1(c) shows can occur
over the alumina catalyst. Surprisingly, the catalytic data
reported on alumina in this paper and the corresponding
thermodynamic calculations show that most of the NO2
observed upon completion of propene conversion during the
SCR of NO did not arise from the direct oxidation of NO by O2
Notes and references
1 R. Burch and T. C. Watling, Catal. Lett., 1997, 43,19.
2 R. Burch, P. Fornasiero and T. C. Watling, J. Catal., 1998, 176, 204.
3 H. Hamada, Catal. Today, 1994, 22, 21.
4 J. Yan, M. C. Kung, W. M. H. Sachtler and H. H. Kung, J. Catal., 1997,
172, 178.
5 H. Hamada, Y Kintaichi, M. Sasaki and T. Ito, Appl. Catal., 1991, 70,
L15.
6 H. Hamada, Y. Kintaichi, M. Inaba, M. Tabata, T. Yoshinari and H.
Tsuchida, Catal. Today, 1996, 29, 53.
7 N. Okazaki, S. Osada and A. Tada, Appl. Surf. Sci., 1997, 121/122,
396.
8 C. Yokoyama and M. Misono, J. Catal., 1994, 150, 9.
9 R. H. H. Smits and Y. Iwasawa, Appl. Catal. B, 1995, 6, L201.
Communication 8/08465C
260
Chem. Commun., 1999, 259–260