1. Introduction
Glycerol carbonate (GC) is a significant cyclic carbonate with excellent properties and broad use. GC is a nontoxic, readily biodegradable, water-soluble, not flammable (fp 165.9
oC), and viscous liquid, which can be used as a polar high boiling solvent, a surfactant component, an intermediate for many kinds of polymers. In addition, GC also can be utilized as components for gas separation membranes [
1,
2,
3,
4]. GC can be synthesized from the reaction of the biological glycerol (GL), a by-product of biodiesel, and various substances with carbonyl, such as dimethyl carbonate (DMC), or urea, or carbon dioxide. As the by-product of biodiesel manufacture, the biological GL is produced in huge amounts for the production of biodiesel is increased rapidly year by year [
5,
6,
7]. Therefore, the synthesis of high value-added GC from the surplus and cheap GL has attracted more and more attentions, which is one of the main topics of biomass valorization [
8,
9,
10]. Among the synthesis methods of GC, the reactions of GL with DMC or urea suffer some drawbacks, such as expensive reactant for DMC route [
11,
12,
13], or generating an environmentally harmful by-product (NH
3) for urea route [
14,
15,
16,
17]. Compared with the above methods, the synthesis of GC by the carbonylation of GL with CO
2 is more interesting and its atom utilization is as high as 87%. Moreover, this reaction is regarded as a green process in which two wastes, GL, a by-product of biodiesel, and CO
2, a primary greenhouse gas, are converted into a value-added chemical, GC [
18,
19,
20,
21,
22,
23,
24,
25].
Up to now, a series of homogeneous and heterogeneous catalysts have been developed and used for the reaction of GL with CO
2. Unfortunately, however, the GL conversion and GC yield are still far from satisfactory because this reaction is severely limited by thermodynamics [
20,
26,
27,
28,
29]. Dibenedetto et al. used CeO
2/Al
2O
3 or CeO
2/Nb
2O
5 as a catalyst for the reaction of GL with CO
2 in the presence of tetraglycol dimethyl ether and found that the GL conversion only reached to 2.5% under pressure of 5.0 MPa and reaction time of 15 h [
28]. In order to break the thermodynamic limit to increase the GL conversion, the dehydrants were used in the reaction to pull out of water produced as a by-product during the reaction to shift the chemical equilibrium to product side. George et al. used the 13X zeolite as a dehydrant for the reaction of GL and CO
2 with
nBu
2SnO as a catalyst and obtained GC yield of 35% (13.8 MPa, 393 K, 4 h) [
21]. The acetonitrile also was used as a dehydrant for the reaction of GL and CO
2 by using Cu/La
2O
3 [
19,
30], or Zn/Al/La/M(M=Li, Mg, Zr) [
31], or La
2O
2CO
3-ZnO as a catalyst [
32,
33], and the GC yield reached to 15.2%, or 18.7%, or 14.3%, respectively. Recently, He et al. used 2-cyanopyridine as a dehydrant and CeO
2 as a catalyst for the reaction of GL and CO
2. Although a higher GC yield of 78.9% was obtained in this process, the catalyst amount was too higher (187 wt% based on GL weight) to the industrial production of GC [
18]. These results indicate that the GL conversion and GC yield increase assuredly due to introduction of the dehydrant for the reaction of GL and CO
2. Compared with acetonitrile and 13X zeolite, 2-cyanopyridine is more suitable for the reaction of GL with CO
2 because a higher GC selectivity and a fewer side reaction would be obtained; moreover, Zhao et al. found that 2-cyanopridine not only acts as the dehydrant, but also actives the carbonyl bond of CO
2 [
35]. However, in spite of these progresses, the GC yield is still not enough high for the industrial production and it is also urgently requisite to develop new more effective catalyst for the synthesis of GC from GL and CO
2.
The supported CuO-based nanocatalysts were used in various applications such as the low-temperature water-gas shift reaction, oxidation of various amounts of SO
2, oxidation of volatile organic compounds (VOCs), oxidation of methane, epoxidation of alkenes through oxygen activation, catalyst-sorbent suitable for simultaneous SO
2 and NOx removal from flue gases, etc [
36,
37,
38,
39,
40]. However, to the best of our knowledge, there are few reports on the synthesis of GC from GL and CO
2 by means of using supported CuO-based nanoparticle as a catalyst. In the present work, a series of CuO-based catalysts were prepared and used for the synthesis of GC by the carbonylation of GL and CO
2 in the presence of 2-cyanopyridine as a dehydrant and DMF as a solvent (
Scheme 1). XRD, FTIR, SEM, BET method, and CO
2-TPD were used to scrutinize physicochemical properties of the prepared catalysts. The effects of supports (activated alumina, silicon dioxide, graphene oxide, graphene, and activated carbone), CuO loading amount, calcination temperature, and reaction parameters (CO
2 pressure, reaction temperature, time, and catalyst amount) on the catalytic activity of catalyst were investigated in detail. Finally, based on the experiment results and FTIR characterization, a possible reaction mechanism for the carbonylation of GL and CO
2 was proposed.
3. Materials and Methods
3.1. Chemicals
Copper nitrate [(Cu(NO3)2▪3H2O] (99% purity), activated alumina (Al2O3), silicon dioxide (SiO2), activated carbone (AC), graphite, GL (99% purity), and methanol (99.5% purity) were bought from Sinopharm Chemical Reagent Co. Ltd., Beijing, China. 2-cyanopyridine (98% purity), tetraethylene glycol (99% purity), and 2-picolinamide (>98% purity) were purchased from Aladdin Industrial Corporation, Shanghai, China. Carbon dioxide (99.9% purity) was supplied by Wuhan Minghui Gas Technology Co. Ltd., Wuhan, China. GC (Tokyo Chemical Industry Co., Ltd., Tokyo, Japan) was of over 90% purity. N, N-dimethyl formamide (DMF) (99.5% purity) was purchased from Chinasun Speciality Products Co. Ltd., Jiangsu, China. All these chemicals were used without further purification.
3.2. Supported CuO-based nanoparticle catalyst preparation
The Al2O3, SiO2, AC, graphene oxide (GO), and graphene (GE) were used as supports to prepare the supported CuO-based nanoparticle catalysts. The CuO/Al2O3 catalysts were prepared by the impregnation method using aqueous solution of Cu(NO3)2▪3H2O and activated alumina powder. Firstly, the activated alumina powder was dried under vacuum at 60 oC for 2 h to remove physisorbed water. Then, a certain amount of activated alumina (such as 7 g) was mixed with an aqueous solution of Cu(NO3)2▪3H2O (for example, 100 mL and the amount of Cu(NO3)2▪3H2O of 9.08g) in a glass flask. After strring for 15 min, the mixture was set for 24 h at room temperature and then dried at 100 oC for 1 h to remove water through evaporation. Subsequently, the solid mixture was grinded and sieved using the standard sieve with 100 mesh. The obtained solid powder was calcined at specified temperature (for example, 700 oC) for 5 h under static air. A heating ramp of 5 oC/min was employed in this step. Finally, the obtained catalyst was used in the reaction of GL and CO2. All the prepared catalysts are denoted as CuO/Al2O3(n%, m), where n% is the weight percentage of CuO loaded on Al2O3 and m is the calcination temperature. The CuO/SiO2(30%, 500) catalyst and CuO/AC(30%, 500) were prepared by the same method with CuO/Al2O3(30%, 500) using SiO2 and AC as supports instead of Al2O3, respectively.
CuO/GO(30%, 500) was prepared by the procedure shown below. Firstly, the GO was obtained by the modified Hummers method. Briefly, 100 mL of the concentrated H2SO4 and 10 mL of the concentrated H3PO4 were poured into a beaker, and then, 2 g of graphite was added. The beaker was put in an ultrasonic cleaner for 1 h at 20 °C and 200 W. Subsequently, 0.75 g of KMnO4 was added into the beaker, which was further treated by ultrasonic for another 2 h. Afterwards, the additional 3 g of KMnO4 was added and the solution was stirred at 60 oC for 3 h. Then, the mixture was poured into a large beaker with 190 mL of ice water, and then, 7.5 mL of H2O2 was added to give the graphite oxide. The sample was washed by centrifugation to be neutral and treated by ultrasonic dispersion at 200 W for 1h, and then, dried at 60 oC to give GO. The CuO/GO(30%, 500) was prepared by the same procedure with CuO/Al2O3(30%, 500) using GO as the support instead of Al2O3.
CuO/GE(30%, 500) was obtained by the following method: firstly, the GE was fabricated via a thermal exfoliation method. During the process, the dried GO was thermally exfoliated at 300 oC for 3 min in air and subsequently the sample was further treated at 900 oC for 3 h in air to give GE. The CuO/GE(30%, 500) was prepared by the same procedure with CuO/Al2O3(30%, 500) using GE as the support instead of Al2O3.
3.3. Catalyst characterization
X-ray diffraction (XRD) patterns of the catalysts were measured on a X’Pert PRO using Cu Kα radiation at 30 kV and 15 mA, over a 2θ range of 5o ~ 90o with a step size of 0.0167o at a scanning speed of 8 min-1. A Bruker VERTEX 70 FT-IR spectrometer was used to obtain the FT-IR spectra of samples using KBr pellet technique, with 2 cm-1 resolution over the wavenumber range 4000-400 cm-1. The morphology of the particles was observed by use of a scanning electron microscope (SEM, TESCAN VEGA3) with 20.0 kV of an accelerating voltage. Nitrogen adsorption-desorption isotherms were determined by a volumetric adsorption apparatus (Micromeritics ASAP 2420) at 77 K. The surface areas of samples were calculated by using the Brunauer-Emmett-Teller (BET) method. The pore volume was given at p/p0 =0.99. The pore size distribution was calculated by the Barrett-Joyner-Halenda (BJH) method.
The basicity studies of the prepared catalysts were conducted with temperature-programmed desorption of CO2 as probe molecule (CO2-TPD) using Huasi DAS-7000 apparatus equipped with thermal conductivity detector (TCD). The analysis was performed by heating 100 mg of the catalyst sample under a He flow from room temperature to 800 oC for 2 h (10 oC/min, 50 mL/min). Then, the temperature was decreased to 90 oC, and a flow of pure CO2 (50 mL/min) was subsequently introduced into the reactor during 1 h. After the catalyst was swept with He for 1 h to remove the physisorbed CO2 from catalyst surface, the TPD of CO2 was carried out between 90 oC and 900 oC under a He flow (10 oC/min, 30 mL/min), and the detection of the desorbed CO2 was performed by an on-line gas chromatograph provided with a TCD.
3.4. Reaction procedure
The tests of the catalytic activities of the metal oxide nanoparticle catalysts were carried out in a stainless-steel autoclave reactor of an inner volume of 250 mL equipped with thermostat, an electric heating jacket, pressure gauge, thermocouple, and agitator. After ascertaining the validity of the autoclave reactor, the typical procedure is as follows: 2.30 g of GL, 1.0 g of catalyst, 19.0 g of DMF, and 6.32 g of 2-cyanopyridine were put into the reactor together, and then, the reactor was sealed and purged with CO2 for 3 times, and pressurized with CO2 to 4 MPa. Subsequently, the reactor was heated to the reaction temperature (150 oC) and maintained for certain reaction time (5 h) under vigorous stirring (600 rpm). After reaction, the reactor was cooled to room temperature and depressurized. Then, all the product mixture was taken out from the autoclave reactor and the solid catalyst was separated by centrifugation from the liquid mixture. The collected catalyst was washed with methanol three times and then used in the recycle experiment. All of the liquid products were sampled for analysis. All the components were analyzed by the gas chromatograph (Fuli 9790-II) equipped with a flame ionization detector (FID) and a capillary column KB-WAX (30 m long, 0.25 mm i.d.). The internal standard method was used. The temperatures of the injector and the detector are 250 oC and 270 oC, respectively. The temperature of the column was programmed to have a 2-min initial hold at 70 oC, a 15 oC/min ramp from 70 oC to 250 oC and then a 15 min hold at 250 oC.
The conversion of GL,
, the yield of GC,
, and the selectivity to GC,
were calculated according to the following equations:
where
is the initial mole number (mol) of GL while
and
are the mole numbers (mol) of GL and GC in the residual reaction mixture after reaction, respectively.
Scheme 1.
The synthesis of GC from the reaction of GL with CO2.
Scheme 1.
The synthesis of GC from the reaction of GL with CO2.
Figure 1.
X-ray diffraction patterns of CuO/Al2O3 nanoparticle catalysts calcined at different temperatures: (a) CuO/Al2O3(30%, 400), (b) CuO/Al2O3(30%, 500), (c) CuO/Al2O3(30%, 600), (d) CuO/Al2O3(30%, 700), (e) CuO/Al2O3(30%, 800).
Figure 1.
X-ray diffraction patterns of CuO/Al2O3 nanoparticle catalysts calcined at different temperatures: (a) CuO/Al2O3(30%, 400), (b) CuO/Al2O3(30%, 500), (c) CuO/Al2O3(30%, 600), (d) CuO/Al2O3(30%, 700), (e) CuO/Al2O3(30%, 800).
Figure 2.
FTIR spectra of CuO/Al2O3 nanoparticle catalysts calcined at different temperatures: (a) CuO/Al2O3(30%, 400), (b) CuO/Al2O3(30%, 500), (c) CuO/Al2O3(30%, 600), (d) CuO/Al2O3(30%, 700), (e) CuO/Al2O3(30%, 800).
Figure 2.
FTIR spectra of CuO/Al2O3 nanoparticle catalysts calcined at different temperatures: (a) CuO/Al2O3(30%, 400), (b) CuO/Al2O3(30%, 500), (c) CuO/Al2O3(30%, 600), (d) CuO/Al2O3(30%, 700), (e) CuO/Al2O3(30%, 800).
Figure 3.
SEM images of CuO/Al2O3 nanoparticle catalysts calcined at different temperatures: (a) CuO/Al2O3 (30%, 400), (b) CuO/Al2O3 (30%, 500), (c) CuO/Al2O3 (30%, 600), (d) CuO/Al2O3 (30%, 700), (e) CuO/Al2O3 (30%, 800).
Figure 3.
SEM images of CuO/Al2O3 nanoparticle catalysts calcined at different temperatures: (a) CuO/Al2O3 (30%, 400), (b) CuO/Al2O3 (30%, 500), (c) CuO/Al2O3 (30%, 600), (d) CuO/Al2O3 (30%, 700), (e) CuO/Al2O3 (30%, 800).
Figure 4.
N2 adsorption-desorption isotherms of CuO/Al2O3 nanoparticle catalysts calcined at different temperatures: (a) CuO/Al2O3(30%, 600), (b) CuO/Al2O3(30%, 700), and (c) CuO/Al2O3(30%, 800).
Figure 4.
N2 adsorption-desorption isotherms of CuO/Al2O3 nanoparticle catalysts calcined at different temperatures: (a) CuO/Al2O3(30%, 600), (b) CuO/Al2O3(30%, 700), and (c) CuO/Al2O3(30%, 800).
Figure 5.
CO2-TPD profiles of CuO/Al2O3 nanoparticle catalysts calcined at different temperatures: (a) CuO/Al2O3(30%, 600), (b) CuO/Al2O3(30%, 700), (c) CuO/Al2O3(30%, 800).
Figure 5.
CO2-TPD profiles of CuO/Al2O3 nanoparticle catalysts calcined at different temperatures: (a) CuO/Al2O3(30%, 600), (b) CuO/Al2O3(30%, 700), (c) CuO/Al2O3(30%, 800).
Figure 6.
The effect of reaction temperature on the catalytic activity of CuO/Al2O3(30%, 700) for the reaction of GL with CO2 (Reaction condition: GL: 2.30 g; Cat: 1.0 g; CO2 initial pressure: 4.0 MPa; reaction time: 5 h; 2-cyanopyridine: 6.32 g; DMF: 19.0 g. ).
Figure 6.
The effect of reaction temperature on the catalytic activity of CuO/Al2O3(30%, 700) for the reaction of GL with CO2 (Reaction condition: GL: 2.30 g; Cat: 1.0 g; CO2 initial pressure: 4.0 MPa; reaction time: 5 h; 2-cyanopyridine: 6.32 g; DMF: 19.0 g. ).
Figure 7.
The effect of CO2 initial pressure on the catalytic activity of CuO/Al2O3(30%, 700) for the reaction of GL with CO2 (Reaction condition: GL: 2.30 g; Cat: 1.0 g; reaction temperature: 150 oC; reaction time: 5 h; 2-cyanopyridine: 6.32 g; DMF: 19.0 g. ).
Figure 7.
The effect of CO2 initial pressure on the catalytic activity of CuO/Al2O3(30%, 700) for the reaction of GL with CO2 (Reaction condition: GL: 2.30 g; Cat: 1.0 g; reaction temperature: 150 oC; reaction time: 5 h; 2-cyanopyridine: 6.32 g; DMF: 19.0 g. ).
Figure 8.
The effect of reaction time on the catalytic activity of CuO/Al2O3(30%, 700) for the reaction of GL with CO2 (Reaction condition: GL: 2.30 g; Cat: 1.0 g; CO2 initial pressure: 4.0 MPa; reaction temperature: 150 oC; 2-cyanopyridine: 6.32 g; DMF: 19.0 g. ).
Figure 8.
The effect of reaction time on the catalytic activity of CuO/Al2O3(30%, 700) for the reaction of GL with CO2 (Reaction condition: GL: 2.30 g; Cat: 1.0 g; CO2 initial pressure: 4.0 MPa; reaction temperature: 150 oC; 2-cyanopyridine: 6.32 g; DMF: 19.0 g. ).
Figure 9.
The effect of weight of catalyst on the catalytic activity of CuO/Al2O3(30%, 700) for the reaction of GL with CO2 (Reaction condition: GL: 2.30 g; CO2 initial pressure: 4.0 MPa; reaction temperature: 150 oC; reaction time: 5 h; 2-cyanopyridine: 6.32 g; DMF: 19.0 g. ).
Figure 9.
The effect of weight of catalyst on the catalytic activity of CuO/Al2O3(30%, 700) for the reaction of GL with CO2 (Reaction condition: GL: 2.30 g; CO2 initial pressure: 4.0 MPa; reaction temperature: 150 oC; reaction time: 5 h; 2-cyanopyridine: 6.32 g; DMF: 19.0 g. ).
Figure 10.
The stability of CuO/Al2O3(30%, 700) catalyst on the reaction of GL with CO2 (Reaction condition: GL: 2.30 g; Cat: 1.0 g; CO2 initial pressure: 4.0 MPa; reaction temperature: 150 oC; reaction time: 5 h; 2-cyanopyridine: 6.32 g; DMF: 19.0 g. ).
Figure 10.
The stability of CuO/Al2O3(30%, 700) catalyst on the reaction of GL with CO2 (Reaction condition: GL: 2.30 g; Cat: 1.0 g; CO2 initial pressure: 4.0 MPa; reaction temperature: 150 oC; reaction time: 5 h; 2-cyanopyridine: 6.32 g; DMF: 19.0 g. ).
Figure 11.
FT-IR spectra of reaction mixture with different reaction time: (a) 0 min; (b) 60 min; (c) 120 min; (d) 180 min. .
Figure 11.
FT-IR spectra of reaction mixture with different reaction time: (a) 0 min; (b) 60 min; (c) 120 min; (d) 180 min. .
Scheme 2.
The interaction of CO2 with 2-cyanopyridine to form an intermediate.
Scheme 2.
The interaction of CO2 with 2-cyanopyridine to form an intermediate.
Figure 12.
FT-IR spectra of (a) recovered CuO/Al2O3(30%, 700) and (b) fresh CuO/Al2O3(30%, 700). .
Figure 12.
FT-IR spectra of (a) recovered CuO/Al2O3(30%, 700) and (b) fresh CuO/Al2O3(30%, 700). .
Scheme 3.
The proposed reaction mechanism for the synthesis of GC from GL and CO2 over CuO/Al2O3(30%, 700).
Scheme 3.
The proposed reaction mechanism for the synthesis of GC from GL and CO2 over CuO/Al2O3(30%, 700).
Table 1.
The catalytic activities of supported CuO-based catalysts with different supports for the synthesis of GC from GL and CO2. a.
Table 1.
The catalytic activities of supported CuO-based catalysts with different supports for the synthesis of GC from GL and CO2. a.
Catalyst |
Tcal(oC) |
WCuO(wt%) |
XGL(%) |
YGC(%) |
SGC(%) |
CuO/GO(30%, 500) |
500 |
30 |
49.0 |
14.6 |
29.7 |
CuO/AC(30%, 500) |
500 |
30 |
21.4 |
8.9 |
41.4 |
CuO/SiO2(30%, 500) |
500 |
30 |
38.2 |
10.1 |
26.5 |
CuO/GE(30%, 500) |
500 |
30 |
49.0 |
13.4 |
27.3 |
CuO/Al2O3(30%, 500) |
500 |
30 |
37.8 |
15.0 |
39.8 |
Table 2.
The catalytic activity of CuO/Al2O3 catalysts with different CuO loading amounts and calcination temperatures for the synthesis of GC from GL and CO2.a.
Table 2.
The catalytic activity of CuO/Al2O3 catalysts with different CuO loading amounts and calcination temperatures for the synthesis of GC from GL and CO2.a.
Catalyst |
Tcal(oC) |
WCuO(wt%) |
XGL(%) |
YGC(%) |
SGC(%) |
CuO/Al2O3(5%, 500) |
500 |
5 |
14.6 |
2.8 |
19.2 |
CuO/Al2O3(10%, 500) |
500 |
10 |
17.9 |
6.0 |
33.5 |
CuO/Al2O3(20%, 500) |
500 |
20 |
29.4 |
10.0 |
34.1 |
CuO/Al2O3(30%, 500) |
500 |
30 |
37.8 |
15.0 |
39.8 |
CuO/Al2O3(40%, 500) |
500 |
40 |
51.6 |
15.3 |
29.7 |
CuO/Al2O3(30%, 400) |
400 |
30 |
58.0 |
15.1 |
26.0 |
CuO/Al2O3(30%, 600) |
600 |
30 |
44.0 |
13.6 |
30.9 |
CuO/Al2O3(30%, 700) |
700 |
30 |
41.3 |
17.5 |
42.4 |
CuO/Al2O3(30%, 800) |
800 |
30 |
33.5 |
14.2 |
42.4 |
Table 3.
The BET surface area, total pore volume, and average pore diameter of CuO/Al2O3(30%, 600-800) catalysts.
Table 3.
The BET surface area, total pore volume, and average pore diameter of CuO/Al2O3(30%, 600-800) catalysts.
Catlysts |
SBET (m2/g) |
Total pore volume (cm3/g) |
Average pore diameter (nm) |
Basic site amount (umol/g) |
< 200 oC |
200~400 oC |
>400 oC |
total |
CuO/Al2O3(30%,600) |
111.29 |
0.269 |
7.98 |
171.18(0.19) a
|
367.13(0.42) |
337.15(0.39) |
875.45 |
CuO/Al2O3(30%,700) |
170.52 |
0.277 |
6.65 |
193.86(0.18) |
184.90(0.17) |
703.66(0.65) |
1082.42 |
CuO/Al2O3(30%,800) |
92.70 |
0.240 |
11.42 |
4.91(0.02) |
90.16(0.27) |
233.86(0.71) |
328.93 |
Table 4.
Comparison of catalytic activity of CuO/Al2O3(30%, 700) with the other catalysts for GC synthesis from GL and CO2 a.
Table 4.
Comparison of catalytic activity of CuO/Al2O3(30%, 700) with the other catalysts for GC synthesis from GL and CO2 a.
Catalysts |
T(°C) |
Time(h) |
P(MPa) |
Cat.(wt%) |
Dehydrant |
XGL(%) |
YGC(%) |
TOFb
|
Ref. |
CeO2
|
150 |
5 |
4 |
186.8 |
2-cyanopyride |
- |
78.9 |
0.92 |
[18] |
La2O2CO3–ZnO |
170 |
12 |
4 |
5 |
acetonitrile |
30.3 |
14.3 |
2.59 |
[31] |
CHT-Cl |
170 |
12 |
4 |
3.0 |
acetonitrile |
35.5 |
16.7 |
4.97 |
[30] |
ZnY |
180 |
3 |
10 |
2.0 |
no |
- |
5.8 |
10.58 |
[24] |
Cu/MCM-41 |
150 |
3 |
7 |
1.7 |
acetonitrile |
18.7 |
1.8 |
3.81 |
[29] |
CeO2-nanopolyhedra |
170 |
12 |
10 |
7.4 |
2-cyanopyride |
35.5 |
14.2 |
1.74 |
[35] |
ZnO |
180 |
12 |
15 |
0.6 |
no |
- |
8.1 |
11.35 |
[25] |
Co(OAc)2
|
180 |
6 |
2 |
2.5 |
acetonitrile |
36.7 |
4.6 |
3.33 |
[48] |
ZnWO4-ZnO |
150 |
6 |
5 |
54.4 |
no |
- |
6.5 |
0.22 |
[23] |
CuO/Al2O3(30%, 700) |
150 |
5 |
4 |
43.6 |
2-cyanopyride |
41.3 |
17.5 |
0.87 |
This work |