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the reduction of N2O by CH4, and may play an important role
in the activation/oxidation of CH4. Zhu et al. [20] indicated
that the activity of Cu- or Co-loaded activated carbon in N2O
conversion was higher than that of Cu/ZSM-5 or Co/ZSM-5,
respectively. They [22,23] also investigated the role of O2 in
NO– and N2O–carbon reactions and reported that the pres-
ence of O2 greatly enhanced the NO–carbon reaction while it
suppressed the N2O–carbon reaction. However, little funda-
mental study has been concluded pertaining to the reduction
of N2O by carbon species including reaction intermediates
in the presence of O2 over metal-loaded zeolites.
Several research groups have reported the nature and the
role of oxygen species in the oxidation of hydrocarbons over
metal-exchanged zeolites, Li and Armor [29] studied Pd-
exchanged zeolites (ZSM-5, mordenite, and ferrierite) cat-
alysts for CH4 oxidation. They reported that Pd supported on
these zeolites showed much higher activities than Pd/Al2O3
and suggested that extra-lattice oxygen atoms could be very
active in the complete oxidation of CH4 at low temperature.
Panov et al. [30] proposed that a surface oxygen species,
dant (O2, N2O) has been also investigated to elucidate the
role of O2 in the oxidation of carbonaceous deposits.
2. Experimental
2.1. Catalyst preparation
Fe-ZSM-5 catalysts were prepared by a conventional ion-
exchange method using Na-ZSM-5 (SiO2/Al2O3 = 23.8) sup-
plied from Tosoh Co. Ltd. Na-ZSM-5 (4 g) was added to
3
−2
100 cm of FeSO4·7H2O aqueous solution of 2.45 × 10
M
and the resulting mixture was then stirred at 343 K for 12 h.
After filtration, the metal-supported zeolites were washed
with distilled water, dried at 383 K for 24 h, and calcined
in air at 773 K for 3 h. The content of Fe loaded was fixed at
3.4 wt.%, corresponding to 100% ion-exchangeable level.
2.2. N2O reduction
␣
-oxygen, generated in Fe-ZSM-5 under N2O decomposi-
The reaction was carried out in a conventional flow re-
−
3
tion exhibited high reactivity in oxidation of methane, ben-
zene and CO. They concluded that (1) ␣-oxygen was formed
on Fe-ZSM-5 but not on the other iron catalysts and that
actor at a W/F of 0.06 g s cm and at 598 K. The reactor
was made of 9 mm diameter Pyrex glass tubing in which a
catalyst sample of 0.05 g was mounted on loosely packed
quartz wool. Prior to the runs, the catalyst was treated in
a stream of He at 773 K for 2 h and cooled to the reaction
temperature.
(2) it was produced upon N2O decomposition but not upon
O2 adsorption. Sachtler et al. [31] identified the oxygen de-
posited by N2O decomposition on Fe/MFI by means of iso-
topic exchange technique. They suggested that [Fe2O2]2+
type ions should be considered in addition to the mononu-
clear [Fe O]2 ion as the oxo-species of dissociative N2O
adsorption on iron ions in partially pre-reduced and dehy-
drated Fe/MFI. However, little fundamental study has been
made concerning the nature and the role of surface oxygen
in the oxidation of hydrocarbons over Fe-zeolite catalysts.
Recently [32], we have reported that two types of carbona-
ceous deposits (C␣, C) are formed on Fe-ZSM-5 catalysts
during the N2O reduction by C2H4 in the absence of O2,
and the catalytic activity decreases with an increase in the
amount of C␣ formed. The C␣ species may be formed on the
Fe sites. It was found that the catalytic reduction of N2O by
C2H4 is promoted by O2, which prevents the accumulation
of carbonaceous deposits on Fe sites. These carbonaceous
deposits were scarcely accumulated by supplying only C2H4
over Fe-ZSM-5 or N2O–C2H4 mixture over Na-ZSM-5 par-
ent zeolite; therefore, these carbonaceous deposits are formed
through the reaction between N2O and C2H4 over Fe sites.
In the present study, the reduction of N2O by various hydro-
The reactant gases used were N2O and a hydrocarbon of
CH4, C2H4, C2H , C3H , or C3H8 diluted by He. The con-
6
6
+
centration used for CH4, C2H4, C2H , C3H , C3H8, and N2O
6
6
was 3000, 2000, 2000, 1300, 1300, and 2000 ppm, respec-
tively. In our previous work [32], a 2000 ppm concentration
of C2H4 was used. One mole of C2H4 is equivalent to six
moles of O atoms if the following stoichiometry is assumed:
C + 2O → CO2 and H2 + O → H2O. The concentration of the
other hydrocarbons was also adjusted to approximately have
the same equivalent number of reducing C and H atoms. To
examine the influence of O2, it was introduced into the feed
gas in different quantities up to 5%. The concentrations of
N2O, N2, O2, CO, CO2, and hydrocarbons in the outflow gas
were determined using gas chromatographs (Hitachi 663-50
and 063) with porapak Q and molecular sieve 5A columns.
The concentration of NO2 was monitored using a UV–vis
spectrophotometer (Hitachi Model 100-10). Because of low
concentrations of N2O and hydrocarbons used, the total flow
rate was practically constant throughout the catalyst bed.
carbons (CH4, C2H , C3H , C3H8) in addition to C2H4 in
2.3. Catalyst characterization
6
6
the presence and absence of O2 has been studied over Fe-
ZSM-5. The reducing ability of the hydrocarbons has been
discussed in terms of the accumulation of carbonaceous de-
posits on the catalyst. The nature and the structure of the
carbonaceous deposits have been investigated by means of
temperature-programmed oxidation (TPO) and X-ray photo-
electron spectroscopy (XPS) analysis. The reactivity of the
carbonaceous deposits and gaseous product (CO) with oxi-
Temperature programmed oxidation experiments were
carried out in the same reactor as used for the N2O reduction.
After the reaction, the reactor was cooled to room tempera-
ture, the stream of reactants was switched to He, and it was
allowed to flow through for 60 min, and then programmed
heating was started from room temperature to 773 K at a
−
1
rate of 5 K min in the stream of 5000 ppm O2 in He. The