CHEMCATCHEM
COMMUNICATIONS
DOI: 10.1002/cctc.201300777
A Highly Distributed Cu Au -Deposited Nanotube Carbon
x
y
for Selective Reduction of NO in the Presence of NH at
3
Very Low Temperature
Rachid Amrousse* and Said El Moumni
[a]
[b]
Cu Au Deposited on carbon nanotubes prepared by solution
higher activities in SCR of NO with NH , H , CO, and hydrocar-
3 2
x
y
plasma sputtering was used for first time as a catalyst for selec-
bons.
tive reduction of NO, in the presence of NH , at low tempera-
The aim of this work is to study SCR of NO with NH over
3
3
ture. N and H O are desirable during the NO reduction pro-
novel Cu Au /CNTs catalysts synthesized by solution plasma
2
2
x
y
cess; however, N O is totally absent from the obtained prod-
sputtering (SPS) process and the detailed preparation condi-
tions and characterization results are given in the Supporting
Information.
2
ucts.
Moreover, the measurements of the SCR activity were per-
[15]
Selective catalytic reduction (SCR) is considered to be the most
formed in a self-designed SCR reactor.
Four gas steams,
efficient technology for reducing NO emissions from station-
700 ppm of NO, 4% of O and 10% of H O steam and with He
x
2
2
ary sources. The reaction can be achieved efficiently by con-
in balance were used to simulate the flue gas. Mass flow con-
troller was used to control NO, and gas rotameters were used
to control the stream of NH and O . In all the runs, the total
[
1]
ventional catalysts such as V O -WO /TiO [Eq. (1)]:
2
5
3
2
3
2
ꢀ
1
2
NO þ 2 NH þ 1=2 O ! 2 N þ 3 H O
ð1Þ
3
2
2
2
gas flow rate was maintained at 300 mLmin over 1 g of cata-
ꢀ3
ꢀ1
lyst to adjust W/F as 3.2ꢀ10 g/(mLmin ), where W denotes
the weight of catalyst and F denotes the flue of the feed
gases. The feed gases were mixed in a chamber and then pre-
heated before entering the reactor. Catalytic activity data was
collected at low temperature range of about 30–658C. The NO
concentrations at the inlet and outlet of the reactor were
monitored by using an on-line Flue Gas Analyzer KM900
equipped with NO sensor. To avoid the effect of the adsorption
characters, the catalysts were purged with reaction gas for 2 h
at first.
The most effective reaction temperature for this process is
[
2,3]
known to be in the range of 300–4008C.
However, many
studies have been performed to develop new low temperature
SCR catalysts that can work well around 2508C or even below.
In this case the SCR unit could be placed behind the electric
precipitation and desulfurizer in a power plant to efficiently
remove NO over a wider temperature range and for NO con-
x
x
[
4]
trol in diesel engines. According to our literature overview,
[
5]
many catalysts, e.g., modified carbon fibers and metal-acti-
[
6]
vated carbon, have been tested for the SCR of NO at low
temperatures (<2508C), however, such catalysts exhibited
lower catalytic activity for a commercial process. On the other
hand, catalysts containing transition metals such as Mn, V, Fe,
Here we report a rare example of SCR of NO using Cu Au /
x
y
CNTs catalysts. Figure 1 shows the catalytic activities of Cu Au /
x
y
[
7–10]
and Rh-Sn
exhibited good low-temperature SCR activity.
Among them, the nano-MnO catalyst has been studied exten-
x
sively, as it contains various types of labile oxygen species re-
[
4,11]
quired for low-temperature SCR.
Several accounts have
been reported for the SCR of NO conversion; Cu/CeO , Cu-Fe
2
[
12–14]
and Au/MgO, Au/SiO , and Au/Al O
3
catalysts display
2
2
[a] Dr. R. Amrousse
Japan Aerospace Exploration Agency (JAXA)
Chemical Engineering
3
-1-1 Yoshinodai Chuo-ku, Sagamihara 252-5210 Kanagawa (Japan)
Fax: (+81)42-759-8284
E-mail: rachid.amrousse@jaxa.jp
[b] S. E. Moumni
University of Chouaib Doukkali
Department of Chemistry
2
4000 El Jadida (Morocco)
Figure 1. Catalytic activity of Cu
x y
Au /CNTs catalysts calcined at different tem-
Supporting information for this article is available on the WWW under
http://dx.doi.org/10.1002/cctc.201300777.
peratures. Reaction conditions: 700 ppm of NO, 750 ppm of NH
3
, 4% of O
2
ꢀ3
ꢀ1
and 10% of H
2
O steam, He to balance, W/F=3.2ꢀ10 g/(mLmin ).
ꢁ
2014 Wiley-VCH Verlag GmbH & Co. KGaA, Weinheim
ChemCatChem 2014, 6, 119 – 122 119