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Low-temperature catalytic combustion of methane over MnOx-CeO2 m...
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Low-temperature catalytic combustion of methane over MnOx-CeO2 mixed oxide catalysts: Effect of preparation method,Shi Limin,储伟,The effect of preparation method on MnOx-CeO2 mixed oxide catalysts for methane combustion at low temperature was investigated by means of BET, XRD, XPS, H2-TPR techniques and meth
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http://www.paper.edu.cn
-1-
Low-temperature catalytic combustion of methane over
MnO
x
-CeO
2
mixed oxide catalysts: Effect of preparation
method
1
Shi Limin
1
, Chu Wei
1
, Qu Fenfen
2
, LuoShizhong
1
1 School of Chemical Engineering, Sichuan University, Chengdu (610065)
2 Department of Environment, Sichuan University, Chengdu (610065)
E-mail:chuwei65@yahoo.com.cn
Abstract
The effect of preparation method on MnO
x
-CeO
2
mixed oxide catalysts for methane combustion at low
temperature was investigated by means of BET, XRD, XPS, H
2
-TPR techniques and methane oxidation
reaction. The catalysts were prepared by the conventional coprecipitation, plasma and modified
coprecipitation methods, respectively. It was found that the catalyst prepared by modified
coprecipitation was the most active, over which methane conversion reached 90% at a temperature as
low as 390℃. The XRD results showed the preparation methods had no effect on the solid solution
structure of MnO
x
-CeO
2
catalysts. More Mn
4+
and richer lattice oxygen were found on the surface of
the modified coprecipitation prepared catalyst with the help of XPS analysis, and its reduction and BET
surface area were remarkably promoted. These factors could be responsible for its higher activity for
methane combustion at low temperature.
Keywords: MnO
x
-CeO
2
mixed oxide; solid solution; methane combustion; low-temperature activity.
1. Introduction
For the environment and energy consideration, complete oxidation of methane into harmless
CO
2
and H
2
O has been paid much attention in catalytic combustion field. Among the
heterogeneous catalysts, the supported noble metal Pd-based catalysts show excellent activity at
low temperature [1-3]. The temperature corresponding to 90% methane conversion (T
90
) over
Pd/SnO
2
catalyst is 440 ℃ [2]. Pd/Sn
x
Zr
1-x
O
2
catalyst has been also reported to possess high
activity at low temperature for methane complete oxidation, over which T
90
is 378 ℃ [3]. However,
poor thermal stability and expensive cost of noble metals prevent the widespread application of
these catalysts. Recently, the transition metal mixed oxides are attractive due to the relatively low
price and as high as or slightly higher catalytic activity toward methane combustion at low
temperature than supported noble metals [4, 5].
Among the transition metal mixed oxides of interest for oxidation reactions, MnO
x
-bases
mixed oxide catalysts exhibit great potential. It is generally believed that MnO
x
are compounds
with a typical berthollide structure and contain labile lattice oxygen. Their catalytic properties are
attributed to the ability for manganese to form oxides with variable oxidation states (MnO
2
,
Mn
2
O
3
, Mn
3
O
4
, or MnO) and to their oxygen storage capacity in the crystalline lattice [6, 7]. For
methane oxidation reaction, the Mn
4
+
sites are stronger catalytic active sites than the Mn
3
+
sites [6,
8]. The active site on supported MnO
x
is mainly identified as being Mn
4+
of MnO
2
in other
oxidation processes [7, 9]. In addition, CeO
2
has been widely used as a promoter and an oxidation
catalyst owing to its unique redox properties and high oxygen storage capacity [10, 11]. Compared
with pure MnO
x
and CeO
2
, MnO
x
-CeO
2
mixed oxides showed higher catalytic activities because
manganese and cerium oxides formed solid solution in which oxygen reservoir of CeO
2
and the
mobility of oxygen species were greatly enhanced [12, 13].
The catalytic performance of MnO
x
-CeO
2
mixed oxides is notably affected by the preparation
1
This work was supported by the National Natural Science Foundation of China (205903603) and by the 973
project of the Ministry of Science and Technology of China (2005CB221406).
http://www.paper.edu.cn
-2-
methods and conditions.The MnO
x
-CeO
2
catalyst modified with Ag exhibited much higher activity
at low temperature for oxidation of formaldehyde because the content of lattice oxygen was
apparently increased [14]. Previous studies have proved that the modified coprecipitation prepared
MnO
x
-CeO
2
catalyst was more active than those prepared by coprecipitation and sol-gel methods
[13]. Considering the same catalytic mechanism (Mars-Van-Krevelen redox mechanism) as total
oxidation of formaldehyde, modified coprecipitation method was used to prepare MnO
x
-CeO
2
mixed oxide catalysts for methane combustion in this contribution. Meanwhile, as effective
molecule activation and surface modification approaches, the plasma technique was also
considered to prepare MnO
x
-CeO
2
catalysts in this work. It was reported that the plasma prepared
catalysts showed higher dispersion and enrichment on surface of active components, decrease of
reduction temperature, etc. [15-17]. Since these favorable effects, the low-temperature activities of
catalysts prepared by plasma method could be remarkably improved.
With the aforementioned background, the aim of the present work was to investigate the
effect of preparation method on the properties of MnO
x
-CeO
2
mixed oxide catalysts for methane
combustion at low temperature. MnO
x
-CeO
2
catalysts were prepared by coprecipitation, plasma
and modified coprecipitation methods, respectively, and were characterized with BET、XRD、XPS
and TPR techniques.
2. Experimental procedure
2.1. Catalyst preparation
MnO
x
-CeO
2
mixed oxides (Mn/ (Mn+Ce)=0.5,molar ratio) were prepared by three different
methods. (1) Coprecipitation method: 50 %Mn(NO
3
)
2
solution and (NH
4
)
2
Ce(NO
3
)
6
with a molar
ratio of 5:5 was mixed in dissolved distilled water. 2 M NaOH solution was added to the mixing
solution at 50℃ drop by drop until the pH value reached 10.5 with stirring. The mixtures were
further aged at 50℃ for 2 h in the mother liquid. After filtration and washing with distilled water,
the obtained solid was dried at 110℃ overnight and calcined at 500℃ for 6 h in air. The catalyst
was designed as CP. (2) Plasma method: the catalyst was prepared using the same process as the
above. Furthermore, the catalyst precursor was treated 90 min by glow discharge plasma before
calcination. The treatment approach was similar to that in Ref [15]. The precursor was put into the
discharging tube and decomposed in vacuum. The discharge parameters are as follows: frequency
13.56 MHz, discharge voltage 100V, anodic current 100 mA. The prepared catalyst was denoted
as PP. (3) Modified coprecipitation method: the coprecipitation procedure was the same as CP, but
the metal oxide precursors contained KMnO
4
. The molar ratio of Mn(NO
3
)
2
, KMnO
4
and
(NH
4
)
2
Ce(NO
3
)
6
was 1:4:5. The catalyst was nominated as MP. The precipitates were filtered and
washed with distilled water many times during the preparation as Ref [13]. There should be no or
considerable little potassium in the MP catalyst and the effect of traces of potassium on catalytic
activity was not considered in this work. For a comparison purpose, pure MnO
x
was prepared by
coprecipitation of Mn(NO
3
)
2
and KMnO
4
with the ratio of 1:4.
2.2. Catalyst characterization
The BET surface area of catalysts were determined by N
2
adsorption experiments at -196℃
on a micromeritics NOVA 1000e. Before each measurement, the sample was degassed in vacuum
at 300℃ for 3 h.
X-ray powder diffraction (XRD) patterns were recorded on the DX-2000 diffractometer using
Cu K
a
(l = 1.54056 Å) radiation between 10°and 80°. The voltage and anode current were 40 kV
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