9
94
Chemistry Letters Vol.36, No.8 (2007)
Palladium–Copper/Hydrophobic Active Carbon as a Highly Active
and Selective Catalyst for Hydrogenation of Nitrate in Water
1
1
2
1
ꢀ1
Yi Wang, Tomohiro Kasuga, Ikkou Mikami, Yuichi Kamiya, and Toshio Okuhara
1
Graduate School of Environmental Science, Hokkaido University, Sapporo 060-0810
2
Japan Science and Technology Agency, 4-1-8 Honcho, Kawaguchi 332-0012
(Received May 1, 2007; CL-070464; E-mail: oku@ees.hokudai.ac.jp)
Cu–Pd supported on active carbon (AC), in which Cu/Pd
ratio is strictly controlled, is an excellent catalyst for selective
hydrogenation of NO3 to harmless products in the presence
pressure H2 (0.05 atm) is used. To the best of our knowledge, this
is the first report of catalytic hydrogenation of nitrate under such
reaction conditions.
ꢁ
of H2 at low partial pressure. 3.6 wt % Cu; 2.0 wt % Pd/AC,
coupled with another Pd/AC catalyst, showed high selectivity
to N2 (98% at 298 K), while suppressing NH3 production (2%
ꢁ
ꢁ
2
NO3 þ 5H2 ! N2 þ 2OH þ 4H2O
ð1Þ
ð2Þ
ꢁ
ꢁ
NO3 þ 4H2 ! NH3 þ OH þ 2H2O
ꢁ
selectivity, 0.5 from 100 ppm of NO3 ). Modification of the
Cu–Pd/active carbon catalysts were prepared by an impreg-
nation method using PdCl2 and Cu(NO3)2 from Wako Pure
Chem. Co. The four types of active carbon (AC) listed in
Table 1 were used as supports. An aqueous solution of
Cu–Pd/AC catalyst with PTFE results in further enhancement;
the activity more than tripled, while suppression of NH3 produc-
tion was retained.
ꢁ
1
ꢁ3
PdCl2 (1:13 ꢂ 10 mol dm ) was added to AC and stirred
for 30 min at room temperature. After filtration and drying at
373 K for 12 h, an aqueous solution of Cu(NO3)2 (1:66 ꢂ
The pollution of groundwater by harmful nitrogen-contain-
ing compounds such as nitrate is an increasing problem through-
out the world. The use of drinking water containing high concen-
trations of nitrate causes various diseases, including blue baby
syndrome and diabetes. Thus, the reduction of nitrate in polluted
groundwater to an allowable level (25 ppm recommended by
WHO) is absolutely necessary for the provision of safe drinking
water.
ꢁ1
ꢁ3
10 mol dm ) was introduced to the solid at room temperature.
The resulting wet solid was dried at 373 K for 12 h, followed by
calcination at 523 K for 3 h. The catalysts were reduced using
NaBH4 before the reaction. As a reference, Cu–Pd/Al2O3
(JRC-ALO-4) was prepared.
The reduction of nitrate with H2 was performed using a gas–
ꢁ
3
liquid flow reactor (Pyrex tube, 10 mm i.d.) at 298 K. NO3 ,
prepared from NaNO3 (Wako Pure Chem Co.) (100 ppm,
The hydrogenation of nitrate with H2 to form N2 (eq 1)
over a solid catalyst has attracted much attention in the area of
purification of polluted water. In the catalytic hydrogenation,
the formation of NH3 (eq 2) is a critical problem; the allowable
level of NH3 in drinking water is 0.5 ppm. Many studies have
been carried out on the catalytic hydrogenation of nitrate using
ꢁ
3
3.22 mmol dm ), and gas (H2:CO2:He = 5:50:45 and 50:50:0
for low- and high-partial-pressure H2, respectively; flow
rate 80 cm h ) were fed into a reactor under atmospheric
pressure. The gas at the outlet of the reactor was analyzed by
TCD-GC (Shimadzu GC-8A), with a molecular sieve 5A column
for N2 and O2 and a Porapak Q column for N2O. Concentrations
3
ꢁ1
1
Cu–Pd bimetallic catalysts since the discovery of Cu–Pd/Al2O3
2
ꢁ
ꢁ
as an active and selective catalyst by Vorlop and colleagues.
of NO3 , NO2 , and NH3 in the aqueous phase were measured
using a flow injection analysis (FIA) system.
However, few catalysts with acceptable activity, stability, and
selectivity have been developed. Herein, we report the develop-
ment of a catalyst consisting of Cu–Pd/active carbon, in which
the Cu/Pd ratio has been controlled and a hydrophobic active
carbon selected, as a highly active, selective, and stable catalyst
for hydrogenation of nitrate in water. In this study, with a view to
profitable and practical use of the reaction system, low-partial-
ꢁ
Table 1 summarizes the activity (removal rate of NO3 ) and
selectivity and the AC surface areas of catalysts in which the
amounts of Cu and Pd were adjusted to 3.6 and 2.0 wt %, respec-
tively. The data for Cu–Pd/Al2O3 are also listed. In this Table,
selectivities were evaluated at near 100% conversion. The
AC-supported Cu–Pd catalysts showed relatively high activities
Table 1. Hydrogenation of nitrate with H2 over various Cu–Pd catalystsa
PH d
SA
2
e
Activity
f
Selectivity /%
ꢁ
Catalystb,c
2
ꢁ1
ꢁ1 ꢁ1
/atm
/m g
/mmol h
g
N2
N O
2
NO2
NH3
(NH ppm)
3
Cu–Pd/AC (coconut shell, Wako)
Cu–Pd/AC (coal, Kuraray)
Cu–Pd/AC (coconut shell, Kuraray)
Cu–Pd/AC (wood chip, Wako)
Cu–Pd/Al2O3
0.05
1022
1041
934
1393
166
—
0.12
0.10
0.09
0.04
0.06
0.27
0.53
93
84
65
70
34
41
1
0
0
23
16
58
0
0
0
0
0
0
0
0
7
16
12
14
7
55
24
b
1.8
4.5
4.0
3.9
1.8
15.1
6.4
Cu–Pd/AC (coconut shell, Wako)
Cu–Pd/Al2O3
0.50
—
75
a
ꢁ1
ꢁ
Reaction conditions: Temperature, 298 K; nitrate, 100 ppm (from NaNO3); WHSV = 54–102 h ; H2/NO3 = 9. Loading amounts
c
of Cu and Pd were 3.6 and 2.0 wt %, respectively. Information in parentheses is the type of active carbon used and the manufacturer.
e
d
f
Partial pressure of hydrogen. Surface area. Selectivity on the basis of N atom at near 100% conversion.
Copyright Ó 2007 The Chemical Society of Japan