International Journal of Scientific & Engineering Research, Volume 7, Issue 10, October-2016 1730
ISSN 2229-5518
IJSER © 2016
http://www.ijser.org
Total oxidation of CO by CuMnOx catalyst at a
low temperature
Subhashish Dey
1
, Ganesh Chand Dhal
1
, Ram Prasad
2
, Devendra Mohan
1
1
Department of Civil Engineering, IIT (BHU), Varanasi, India
2
Department of Chemical Engineering and Technology, IIT (BHU), Varanasi, India
Abstract— The copper manganese oxides catalyst was synthesized by using co-precipitation method with different Cu:Mn ratio for carbon
monoxide oxidation. The drying of the precursor at 120
o
C temperatures for 12 h in an oven and calcinations at 300
o
C in stagnant air, flowing air
and in a reactive gas mixture of 4.5% CO in the air known as reactive calcination (RC). The CuMnOx catalyst is prepared into different molar
ratio like (Cu:Mn=2:1), (Cu:Mn=1:1) and (Cu:Mn=1:2) for oxidation of CO. The activity of the catalysts was evaluated in a tubular reactor under
the following conditions: 100 mg catalyst, 2.5% CO in air, total flow rate 60 mL/min and temperature varying from ambient to a higher value, at
which complete oxidation of CO was achieved. The decomposition of mixed copper and manganese nitrate in controlled conditions therefore
produced CuMnOx catalyst and it depending on the oxygen concentration and flow conditions of gases during the heat treatment. The
prepared catalysts were characterized by XRD, FTIR, SEM-EDX, XPS and BET techniques. The ability to oxidation state and phase
composition of CuMnOx catalysts is a key preparation parameter for controlling the CO oxidation.
Index Terms— Carbon monoxide, Catalytic oxidation, Ambient temperature, Hopcalite catalysts, Co-precipitation, Reactive Calcination.
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1 INTRODUCTION
Air pollution has become a major concern in most of the
countries in the world. It is responsible for causing respiratory
diseases, cancers and serious other illness. In addition of the
health effects, air pollution also contributes to high economic
losses. The transportation sector i.e. the vehicles (particularly
cars, trucks and buses) which run by petrol and diesel are one of
the greatest contributors to air pollution. It was expected that
motor vehicles emissions contribute to the global emissions, an
amount of 21% for carbon dioxide (CO
2
), 37% for nitrogen
oxides (NOx), 19% for volatile organic compounds, 18% for
carbon monoxide (CO) and 14% for black carbon (1).
Carbon monoxide with the chemical formula of CO is a
colorless, odorless and tasteless, it is highly toxic and it emitted
from vehicle exhaust. It is produced from the partial oxidation
of carbon-containing materials. It converted in to the more usual
carbon dioxide (CO
2
) when there is a reduced availability of
oxygen, such as when operating an internal combustion engine
in an enclosed space Carbon monoxide (CO) and carbon
dioxide (CO
2
) from diesel engines are relatively low. The CO
emissions are more significant in the spark ignition engines as
the fuel/air ratio is often close to stoichiometric at a part of the
load and more at full load (2).
A catalytic converter is an automobile emissions control device
that converts toxic pollutants in the exhaust gas into less
poisonous gas by catalyzing a redox reaction (oxidation or
reduction). Catalytic converters are used in internal ignition
engines fueled by either gasoline or diesel-including lean burn
engines. For the catalyst design, it is essential to explain the
catalyst performance parameters into a physical picture of the
catalyst structure (3). In the beginning more interest has been
focused on catalytic control of CO emissions from automobile
exhaust because it is dangerous for the environment. On start-
up car exhaust catalysts take a little time to become effective
and this primarily due to the time required to heat the catalyst
using the exothermicity of the combustion reactions. If the
catalyst could be added that was very efficient for CO
oxidations at lower temperatures then this initial warm-up
period could be shortened and the cold start problem can be
solved (4). In the last 35 years, the catalytic converters have been
installed on more than 1000 million vehicles around the world.
The choice of the appropriate catalyst is an important step for
improving the environment.
The most effective catalysts for CO oxidation at low a
temperature in many years are known as hopcalite catalyst
(CuMnOx), which is a mixture of copper manganese oxide (5).
The catalytic properties of such a system called hopcalite were
confirmed by Jones and Taylor in the year 1923; since that time
hopcalite has become a well-known oxidation catalyst at room
temperature. A literature study reveals that CuMnOx catalyst is
extremely active in the amorphous state even at room
temperature but it has observed that the CuMnOx catalyst lose
his activity after exposition at temperatures above 773K where
crystallization of the spinel CuMn
2
O
4
. However, crystalline
Cu
2
MnO
4
has also been reported by Schwab and Kanungo (6)
to be active.
Recently, the low temperature oxidation of carbon monoxide
has seen a renaissance in its interest to the catalytic community.
Ever since that time, hopcalite catalysts have been employed to
oxidize a range of environmentally damaging gasses at low
temperatures. A lot of attention has been given to modification
of the CuMnOx catalyst in order to remove its faults of moisture
for deactivation and low activity. The preparation of the catalyst
by other non-conventional methods including synthesis of
nano-crystalline copper manganese oxide catalysts by using the
supercritical anti-solvent precipitation method (7), copper
manganese oxide from sol-gel (8) were reported to give better
conversion than commercial hopcalite.
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