催化学报  2014, Vol. 35 Issue (9): 1475-1481   PDF (1205 KB)    
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王芳
戴洪兴
邓积光
谢少华
杨黄根
韩文
Nanoplate-aggregate Co3O4 microspheres for toluene combustion
Fang Wang, Hongxing Dai , Jiguang Deng, Shaohua Xie, Huanggen Yang, Wen Han    
Key Laboratory of Beijing on Regional Air Pollution Control and Laboratory of Catalysis Chemistry and Nanoscience, Department of Chemistry and Chemical Engineering, College of Environmental and Energy Engineering, Beijing University of Technology, Beijing 100124, China
Abstract: Nanoplate-aggregate microspherical Co3O4 was prepared by an ethylenediamine-assisted hydrothermal route and characterized by means of numerous techniques. Their catalytic activities for toluene combustion were evaluated. The Co3O4 sample obtained using 1.0 ml of ethylenediamine and a hydrothermal treatment at 140 ℃ for 12 h had a nanoplate-aggregate microspherical morphology. This microspherical Co3O4 sample with a surface area of 66 m2 g-1 had a higher adsorbed oxygen concentration and better low-temperature reducibility than bulk Co3O4. Over the Co3O4 microsphere sample, the temperatures required for 50% and 90% toluene conversions were 230 and 254 ℃, respectively, at a space velocity of 20000 ml g-1 h-1. The good catalytic performance of the Co3O4 microsphere sample was related to its large surface area, high oxygen adspecies concentration, and good low-temperature reducibility.
Key words: Cobalt oxide microsphere     Nanoplate morphology     Surfactant-assisted hydrothermal synthesis     Toluene combustion    
纳米片聚结Co3O4微球催化甲苯燃烧
王芳, 戴洪兴 , 邓积光, 谢少华, 杨黄根, 韩文    
北京工业大学环境与能源工程学院北京市区域大气污染控制重点实验室和化学化工系, 北京100124
摘要:采用乙二胺辅助的水热法制备了纳米片聚结的Co3O4微球. 利用多种分析技术表征了其物化性质,并评价了其对甲苯燃烧的催化活性. 结果表明,由添加1.0 ml乙二胺经140 ℃水热处理12 h后制得的Co3O4样品呈纳米片聚结的微球状表面形貌. Co3O4微球样品的比表面积约为66 m2 g-1. 与体相Co3O4样品相比,Co3O4微球样品具有较高的氧吸附物种浓度和较好的低温还原性. 当空速为20000 ml g-1 h-1时,在Co3O4微球样品上甲苯转化率达到50%和90%时的反应温度分别为230和254 ℃. 这与该样品具有较大的比表面积、较高的氧吸附物种浓度和较好的低温还原性相关.
关键词氧化钴微球     纳米片形貌     表面活性剂辅助水热合成     甲苯燃烧    

1. Introduction

Most volatile organic compounds (VOCs) emitted from industrial and transportation activities are harmful to the environment and human health. Catalytic oxidation is one of the most effective ways to remove VOCs,and transition metal oxides are the most commonly used catalysts. Co3O4 is a versatile transition metal oxide and shows good catalytic performance for the oxidation of VOCs due to its excellent reducibility and plentiful oxygen vacancies [ 1, 2, 3 ]. The physicochemical properties of Co3O4 strongly depend on its morphology and exposed crystal faces [ 4, 5, 6 ]. In the past years,a large number of Co3O4 samples with different morphologies (nanowires [ 7, 8 ],nanorods [ 4, 9, 10 ],nanocubes [ 5, 11, 12 ],and nanospheres [ 13, 14 ]) have been fabricated,and some of them were applied for the oxidation of VOCs. For instance,Co3O4 nanoparticles showed good activity in catalyzing VOC oxidation [ 15 ]. Xue et al. [ 16 ] observed a significant effect of Co3O4 morphology on catalytic activity of Au/Co3O4 for ethylene oxidation.

Previously,our group has used silica (SBA-16 or KIT-6)- and polymethyl methacralate-tempalting,hydrothermal,and microemulsion methods to make ordered mesoporous Co3O4 [ 17, 18 ],spherical Co3O4 [ 19 ],and porous Co3O4 nanowires and nanorods [ 2 ],and we found that they performed well in the combustion of VOCs. To the best of our knowledge,however,there have been no reports on catalytic oxidation of toluene over nanoplate-aggregate microspherical Co3O4. In this work,we report the ethylenediamine-assisted hydrothermal preparation of Co3O4 microspheres and their catalytic performance for toluene combustion.

2. Experimental
2.1. Catalyst preparation

The nanoplate-aggregate microspherical Co3O4 sample was prepared using the ethylenediamine-assisted hydrothermal method. Co(NO3)2×6H2O (2.91 g) was dissolved in 30 ml deionized water,and 9 ml NH3×H2O aqueous solution (28 wt% NH3×H2O:H2O = 1:3,v/v) was then added dropwise to the Co(NO3)2 aqueous solution. After stirring for 0.5 h,0.5,1.0 or 2.0 ml ethylenediamine was added under stirring for 0.5 h. The mixed solution was transferred to a 50-ml Teflon-lined stain­less steel autoclave,which was sealed and heated at 120,140,160,or 200 °C for 12 h. After the autoclave was cooled to room temperature (RT),the resulting precipitate was filtered out,washed with deionized water and absolute ethanol three times,dried in an oven at 60 °C for 24 h,and ground uniformly. Finally,the powder was calcined in air using a ramp of 1 °C min−1 from RT to 500 °C and maintained at this temperature for 4 h,thus generating the Co3O4 samples. The Co3O4 sample obtained with 1.0 ml ethylenediamine in the hydrothermal treatment at 140 °C for 12 h was denoted as Co3O4 microsphere. The Co3O4 samples obtained with 0,0.5,and 2.0 ml ethylenediamine in the hydrothermal treatment at 140 °C for 12 h were denoted as Co3O4-1,Co3O4-2,and Co3O4-3,respectively. The Co3O4 samples obtained with 1.0 ml ethylenediamine in the hydrothermal treatment at 120,160,and 200 °C for 12 h were denoted as Co3O4-4,Co3O4-5,and Co3O4-6,respectively. For comparison,a bulk Co3O4 (Co3O4-bulk) sample was prepared by thermally decomposing Co(NO3)2 in air at 600 °C for 3 h. All of the chemicals (AR) were purchased from Beijing Chemical Reagent Company and used without further purification.

2.2. Catalyst characterization

X-ray diffraction (XRD) patterns of the samples were recorded on a Bruker D8 Advance diffractometer with Cu Kα radiation and nickel filter (l = 0.15406 nm). The scanning electron microscopic (SEM) images of the samples were recorded on a Gemini Zeiss Supra 55 apparatus (operating at 10 kV). BET (Brunauer-Emmett-Teller) surface areas of the samples were measured by N2 adsorption at -196 °C on a Micromeritics ASAP 2020 analyzer. The samples were outgassed at 250 °C for 2.5 h under vacuum before measurement. X-ray photoelectron spectroscopy (XPS,VG CLAM 4 MCD analyzer) was used to determine the Co 2p,O 1s,and C 1s binding energies (BEs) of surface species using Mg Ka (hv = 1253.6 eV) as the excitation source.

Hydrogen temperature-programmed reduction (H2-TPR) experiments were carried out on a chemical adsorption analyzer (Autochem II 2920,Micromeritics). The sample (40-60 mesh,0.025 g) was loaded to a fixed-bed U-shaped quartz microreactor (i.d. = 4 mm) and pretreated in a O2 flow (30 ml min−1) at 500 °C for 1 h. After cooling in the same atmosphere to RT,a He flow (30 ml/min) was passed to purge the sample for 15 min. Finally,the pretreated sample was exposed to 5vol% H2/Ar mixture (50 ml min−1) and heated at a ramp of 10 °C min−1 from RT to 550 °C. The H2 concentration of the effluent was monitored online by a chemical adsorption apparatus. The reduction peak was calibrated against that of the complete reduction of well-characterized CuO powders (Aldrich,99.995%).

2.3. Catalytic evaluation

A continuous flow fixed-bed quartz microreactor (i.d. = 4 mm) was used to determine catalyst activity for the oxidation of toluene. To minimize the effect of hot spots,0.6 g quartz sands (40-60 mesh) was used to dilute the sample (0.1 g). The total flow rate of the reactant mixture (0.1% toluene + O2 + N2 (balance)) was 33.3 ml min−1,giving a toluene/O2 molar ratio of 1/400 and a space velocity (SV) of 20000 ml g−1 h−1. The toluene was obtained by passing a N2 flow through a bottle containing pure toluene (AR) chilled in an ice-water isothermal bath. the SV was changed through the amount of sample. In the case of water vapor addition,3.0 vol% H2O was introduced by passing the feed stream through a water saturator at RT. Reactants and products were analyzed online by a gas chromatograph (GC-2010,Shimadzu) equipped with a flame ionization detector (FID) and a thermal conductivity detector (TCD) using a stabilwax@-DA column (30 m in length) for VOC separation and a 1/8 in Carboxen 1000 column (3 m in length) for permanent gas separation. The carbon balance throughout the investigation was estimated to be 99.5%.

3. Results and discussion
3.1. Crystal phase composition,morphology,and surface area

Figure 1 shows the XRD patterns of the Co3O4 samples. The two samples possessed a cubic Co3O4 crystal structure with well-indexed planes (JCPDS PDF #74-1657). The difference in diffraction intensity reflected the discrepancy in crystallinity. As can be seen from Fig. 2,the particles of the Co3O4 bulk sample were irregular polyhedra. The Co3O4 sample derived from the ethylenediamine-assisted hydrothermal route was composed of microspherical entities as several layers of a number of nanoplates (Fig. 2(b)-(d)). With a change in the preparation conditions (added amount of ethylenediamine or hydrothermal temperature),the morphology of the Co3O4 samples obtained was irregular (Fig. 3). Therefore,we investigated in detail only the Co3O4 bulk and Co3O4 microsphere samples. The surface areas of the Co3O4 bulk and Co3O4 microsphere samples were 9.8 and 66.2 m2 g−1,respectively,whereas the Co3O4-i (i = 1-6) samples showed a surface area of 33.2,43.5,50.1,39.3,54.2,and 26.9 m2 g−1,respectively.

Fig. 1. XRD patterns of Co3O4 bulk (1) and Co3O4 microspheres (2).

Fig. 2. SEM images of Co3O4 bulk (a) and Co3O4 microspheres (b-d).

Fig. 3. SEM images of Co3O4-1 (a),Co3O4-2 (b),Co3O4-3 (c),Co3O4-4 (d),Co3O4-5 (e),and Co3O4-6 (f).
3.2. Surface composition,Co oxidation state,and oxygen species

Figure 4(a) illustrates the Co 2p3/2 XPS spectra of the samples. The Co 2p3/2 signal at 780.0 eV showed the presence of surface Co3+ species,while the Co 2p3/2 signal at 781.9 eV together with the shake-up satellite at 785.5 eV confirms the presence of surface Co2+ species [ 20 ]. It can be observed from Table 1 that the surface Co3+/Co2+ molar ratio (1.44) of the Co3O4 microsphere was lower than that (1.65) of Co3O4 bulk,indicating a higher surface Co2+ concentration in the former. That is,the Co3O4 microsphere sample possessed more oxygen vacancies than the bulk counterpart. It is well known that the adsorbed oxygen species concentration is associated with the oxygen vacancy density. For an oxygen-deficient material,more oxygen vacancies give a higher oxygen adspecies concentration. This was substantiated by the O 1s XPS result. As shown in Fig. 4(b),an asymmetrical O 1s XPS signal was recorded for each sample,which was deconvoluted into the peaks of several kinds of surface oxygen species. The oxygen adspecies at 529.3,530.3,531.8,and 533.4 eV were assignable to the surface lattice oxygen (Olatt),adsorbed oxygen (Oads,e.g.,O2-,O22-,or O-),hydroxyl and/or carbonate species,and adsorbed molecular water [ 21, 22 ],respectively. Compared to the Co3O4 b ulk sample,the Oads/Olatt molar ratio of the microspherical Co3O4 sample was much higher,indicating a higher Oads concentration.

Fig. 4. Co 2p3/2 (a) and O 1s (b) XPS spectra of Co3O4 bulk (1) and Co3O4 microspheres (2).

Table 1
Surface element compositions,H2 consumption,and catalytic activities of the Co3O4 bulk and Co3O4 microsphere samples.
3.3. Reducibility

Figure 5(a) illustrates the H2-TPR profiles of the Co3O4 samples. The reduction of Co3O4 proceeds via the sequence of Co3O4CoOCo0 [ 9 ]. The first peak at 227-230 °C was due to the reduction of Co3+ to Co2+ and the removal of oxygen adspecies. The reduction peaks at 279-292 and 316-341 °C corresponded to the reduction of Co2+ to Co0 [ 23 ]. If the cobalt ions in Co3O4 were only Co3+ and only Co2+ and reduced to Co0,the H2 consumption would be 18.07 and 13.33 mmol g−1,respectively. Actually,the H2 consumptions of the Co3O4 bulk and Co3O4 microsphere samples were 16.08 and 15.48 mmol g−1,respectively. Furthermore,the low-temperature H2 consumption (3.22 mmol g−1) of the Co3O4 bulk sample was higher than that (3.10 mmol g−1) of the Co3O4 microsphere sample,indicating that there was more Co3+ in Co3O4 bulk (i.e.,the Co3O4 microsphere sample possessed a higher oxygen vacancy concentration and hence a higher oxygen adspecies concen­tration). Therefore,the cobalt species in the Co3O4 samples were present in a mixed valence (Co 3+ and Co2+),which was in good agreement with the XPS results.

Fig. 5. H2-TPR profiles (a) and initial H2 consumption rate as a function of inverse temperature (b) of Co3O4 bulk (1) and Co3O4 microspheres (2).

It is better to evaluate the low-temperature reducibility of a sample using the initial (where less than 25% oxygen in the sample was removed for the first reduction peak) H2 consumption rate [ 24 ]. Figure 5(b) shows the initial H2 consumption rate as a function of inverse temperature of the Co3O4 samples. Obviously,the initial H2 consumption rate of the nanoplate-aggregate Co3O4 microsphere sample was higher than that of the Co3O4 bulk sample. This difference in low-tem­perature reducibility was in consistent with the difference in their Oads concentrations and catalytic performance.

3.4. Catalytic performance

In the quartz sand blank experiment,no conversion of toluene was observed below 400 °C,indicating that under the adopted conditions there was no occurrence of homogeneous reactions. Figure 6(a) shows catalytic activity of the samples for toluene combustion. It can be clearly seen that the microspherical Co3O4 sample outperformed the bulk counterpart,with the T10%,T50%,and T90% (temperatures required for toluene conversion of 10%,50%,and 90%,respectively) of 190,230,and 254 °C at SV = 20000 ml g−1 h−1 (Table 1),respectively. Toluene was completely oxidized to CO2 and H2O over the Co3O4 samples,and there were no incomplete oxidation products,as substantiated by the carbon balance (99.5%) in each run. To better evaluate the catalytic activity of the samples,we use the specific reaction rates (normalized by weight amount and surface area of the sample) versus reaction temperature,as shown in Fig. 6(b) and (c),respectively. It is observed that the changing trend in specific reaction rate normalized by weight amount of the sample versus temperature was rather similar to that for toluene conversion versus temperature,but different from the specific reaction rate normalized by surface area of the sample versus temperature. This result indicated that the surface area had an important influence on the catalytic act ivity of the sample.

Fig. 6. Toluene conversion (a),specific reaction rate normalized by catalyst amount (b),and specific reaction rate normalized by the surface area of the catalyst (c) as a function of temperature over Co3O4 bulk (1) and Co3O4 microspheres (2). Reaction conditions: 0.1% toluene,toluene/O2 molar ratio = 1/400,SV = 20000 ml g−1 h−1.

To examine the effect of water vapor on the catalytic performance,we conducted toluene oxidation in the presence of 3.0 vol% water vapor over the microspherical Co3O4 sample. As shown in Fig. 7,the addition of water vapor at 260 °C did not lead to a significant decrease in toluene conversion,but introduction of water vapor at 220 °C induced a drop in toluene conversion by 4%. This result was possibly due to the competitive adsorption of water,toluene,and oxygen. When the water vapor was cut off,toluene conversion at 220 °C was restored to almost the initial value in the absence of water vapor. Therefore,the deactivation due to water vapor introd­uction was reversible.

Fig. 7. The effect of 3.0 vol% water vapor on the catalytic activity at 220 °C (1) and 260 °C (2) over Co3O4 microspheres. Reaction conditions: 0.1% toluene,toluene/O2 molar ratio = 1/400,SV = 20000 ml g−1 h−1.

Figure 8 shows the effect of SV on the catalytic activity of the Co3O4 microsphere sample. As expected,the toluene conversion increased with the drop in SV. In order to examine the catalytic stability,we carried out the 100 h on-stream reaction experiment over the Co3O4 microsphere sample at 250 °C and 20000 ml g−1 h−1. As shown in Fig. 9,no significant loss in activity was observed. This result demonstrated that the microspherical Co3O4 sample was stable under the adopted conditions.

Fig. 8. Toluene conversion as a function of reaction temperature at different SV values over the nanoplate-aggregate microspherical Co3O4 catalyst. Reaction conditions: 0.1% toluene,toluene/O2 molar ratio = 1/400.

Fig. 9. Toluene conversion as a function of on-stream reaction time over the nanoplate-aggregate microspherical Co3O4 sample. Reaction conditions: 0.1% toluene,toluene/O2 molar ratio = 1/400,SV = 20000 ml g−1 h−1,250 °C.

In the past years,many materials have been used as the catalyst for toluene combustion. The activities of these catalysts are summarized in Table 2. Usually,the specific reaction rate normalized by the sample amount is used to compare the catalytic activity of different samples. At a given reaction temperature (150 or 250 °C),the specific reaction rate (0.0376 mmol g−1 h−1 at 150 °C or 0.711 mmol g−1 h−1 at 250 °C) over the Co3O4 microshperes was much higher than those over Mn3O4 [ 25 ],a-Mn2O3 [ 25 ],b-MnO2 [ 25 ],bulk Co3O4 [ 17 ],LaMnO3 [ 26 ],and 5 wt% Au/CeO2 [ 27 ],but lower than those over Co3O4-HT-CTAB [ 2 ],mesoporous Co3O4 [ 17, 18 ],and 0.5 wt% Pd/LaMnO3 [ 28 ].

Table 2
Comparison on the activity of various catalysts for toluene combustion.

It is well established that the oxidation of organics over a transition metal oxide involves a Mars-van Krevelen mechanism,where organic molecules are oxidized by the lattice oxygen of the metal oxide,and the partially reduced metal oxide is then re-oxidized by the gas phase oxygen [ 29, 30, 31 ]. Wang et al. [ 31 ] attributed the higher reactivity of manganese oxide to the improvement in oxygen activation ability,which enhanced the combustion of ethanol and acetaldehyde. In the case of Co3O4,lattice oxygen could be consumed by reaction with toluene and then replenished by gas phase oxygen [ 32, 33 ]. Thus,the lattice oxygen of cobalt oxide is of great importance in toluene oxidation. The low-temperature reducibility reflects the reactivity of the lattice oxygen in Co3O4. As shown in Fig. 5,the lattice oxygen reactivity (i.e.,low-temperature reducibility) of the Co3O4 microspheres was higher than that of Co3O4 bulk. Surface oxygen vacancies also have an important role to play [ 34, 35 ]. The presence of oxygen vacancies favors the activation of oxygen molecules to active oxygen adspecies. The microspherical Co3O4 sample possessed a higher oxygen adspecies concentration (which is related to the surface oxygen vacancy density) than the Co3O4 bulk sample,in good agreement with their catalytic activity sequence. In addition,the surface area (66 m2 g−1) of nanoplate- aggregate Co3O4 microspheres was much higher than that (10 m2 g−1) of Co3O4 bulk. Therefore,we conclude that the large surface area,high oxygen adspecies concentration,and good low-tem­perature reducibility accounted for the good catalytic performan­ce of the nanoplate-aggregate Co3O4 microspheres for toluene combustion.

4. Conclusions

The nanoplate-aggregate microspherical Co3O4 catalyst was prepared using an ethylenediamine-assisted hydrothermal strategy. This catalyst had a cubic crystal structure and was comprised of nanoplate-aggregate microspheres. The microspherical Co3O4 sample outperformed the bulk counterpart,giving the T50% and T90% of 230 and 254 °C at SV = 20000 ml g−1 h−1,respectively. The large surface area,high surface oxygen adspecies concentration,and good low-temperature reducibility of the Co3O4 microspheres were responsible for its high catalytic performance.

References
[1] Hu L H, Peng Q, Li Y D. J Am Chem Soc, 2008, 130: 16136
[2] Bai G M, Dai H X, Deng J G, Liu Y X, Wang F, Zhao Z X, Qiu W G, Au C T. Appl Catal A, 2013, 450: 42
[3] Haber J, Turek W. J Catal, 2000, 190: 320
[4] Xie X W, Li Y, Liu Z Q, Haruta M, Shen W J. Nature, 2009, 458: 746
[5] Hu L H, Sun K Q, Peng Q, Xu B Q, Li Y D. Nano Res, 2010, 3: 363
[6] Yu Y B, Takei T, Ohashi H, He H, Zhang X L, Haruta M. J Catal, 2009, 267: 121
[7] Mahmoud W E, Al-Agel F A. J Phys Chem Solids, 2011, 72: 904
[8] Sun Y, Lv P, Yang J Y, He L, Nie J C, Liu X W, Li Y D. Chem Commun, 2011, 47: 11279
[9] Teng F, Chen M D, Li G Q, Teng Y, Xu T G, Hang Y C, Yao W Q, Santhanagopalan S, Meng D D, Zhu Y F. Appl Catal B, 2011, 110: 133
[10] Nguyen H, El-Safty S A. J Phys Chem C, 2011, 115: 8466
[11] Wang Y, Zhong Z Y, Chen Y, Ng C T, Lin J Y. Nano Res, 2011, 4: 695
[12] Cao F, Wang D Q, Deng R P, Tang J K, Song S Y, Lei Y Q, Wang S, Su S Q, Yang X G, Zhang H J. CrystEngComm, 2011, 13: 2123
[13] Qiao R, Zhang X L, Qiu R, Kim J C, Kang Y S. Chem Eur J, 2009, 15: 1886
[14] Sun G B, Zhang X Q, Cao M H, Wei B Q, Hu C W. J Phys Chem C, 2009, 113: 6948
[15] Garcia T, Agouram S, Sánchez-Royo J F, Murillo R, Mastral A M, Aranda A, Vázquez I, Dejoz A, Solsona B. Appl Catal A, 2010, 386: 16
[16] Xue W J, Wang Y F, Li P, Liu Z T, Hao Z P, Ma C Y. Catal Commun, 2011, 12: 1265
[17] Deng J G, Zhang L, Dai H X, Xia Y S, Jiang H Y, Zhang H, He H. J Phys Chem C, 2010, 114: 2694
[18] Xia Y S, Dai H X, Jiang H Y, Zhang L. Catal Commun, 2010, 11: 1171
[19] Liu Y X, Dai H X, Deng J G, Zhang L, Zhao Z X, Li X W, Wang Y, Xie S H, Yang H G, Guo G S. Inorg Chem, 2013, 52: 8665
[20] Liotta L F, Di Carlo G, Pantaleo G, Venezia A M, Deganello G. Appl Catal B, 2006, 66: 217
[21] Rousseau S, Loridant S, Delichere P, Boreave A, Deloume J P, Vernoux P. Appl Catal B, 2009, 88: 438
[22] Ponce S, Peña M A, Fierro J L G. Appl Catal B, 2000, 24: 193
[23] Sexton B A, Hughes A E, Turney T W. J Catal, 1986, 97: 390
[24] Chen K D, Xie S B, Bell A T, Iglesia E. J Catal, 2001, 198: 232
[25] Kim S C, Shim W G. Appl Catal B, 2010, 98: 180
[26] Irusta S, Pina M P, Menéndez M, Santamaría J. J Catal, 1998, 179: 400
[27] Scirè S, Minicò S, Crisafulli C, Satriano C, Pistone A. Appl Catal B, 2003, 40: 43
[28] Musialik-Piotrowska A, Landmesser H. Catal Today, 2008, 137: 357
[29] Grbic B, Radic N, Markovic B, Stefanov P, Stoychev D, Marinova Ts. Appl Catal B, 2006, 64: 51
[30] Santos V P, Pereira M F R, Órfão J J M, Figueiredo J L. Appl Catal B, 2010, 99: 353
[31] Wang R H, Li J H. Environ Sci Technol, 2010, 44: 4282
[32] Baldi M, Finocchio E, Milella F, Busca G. Appl Catal B, 1998, 16: 43
[33] Luo J, Zhang Q H, Garcia-Martinez J, Suib S L. J Am Chem Soc, 2008, 130: 3198
[34] Chen X, Shen Y F, Suib S L, O'Young C L. J Catal, 2001, 197: 292
[35] Tang Q H, Liu T, Yang Y H. Catal Commun, 2008, 9: 2570