Yanan Wang,
Xuewei Lang,
Guoqing Zhao,
Huanhui Chen,
Yiwei Fan,
Linqing Yu,
Xiuxiu Ma and
Zhirong Zhu*
Department of Chemistry, Tongji University, 1239, Siping Road, Shanghai 200092, China. E-mail: zhuzhirong@tongji.edu.cn; Fax: +86-21-65981097; Tel: +86-21-65982563
First published on 1st April 2015
A variety of cesium supported catalysts with amorphous SiO2 as a carrier were prepared by vacuum impregnation and ultrasonic impregnation methods, which were used for the synthesis of methyl acrylate by aldol condensation of methyl acetate and formaldehyde. The as-prepared catalysts were characterized by XRD, N2 adsorption–desorption, NH3-TPD, CO2-TPD, XPS, ICP and TG. The results indicated that the bifunctional Cs–La–Sb/SiO2 showed a high conversion of methyl acetate as well as a high yield of methyl acrylate, which was attributed to the weak acid–base sites and the formation of basic Cs–O–Si species with the addition of antimony and lanthanum, respectively. Furthermore, Cs–La–Sb/SiO2-(V) prepared by vacuum impregnation showed a high initial catalytic activity, but its activity sharply decreased due to the loss of active species. Comparatively, Cs–La–Sb/SiO2-(U) prepared by ultrasonic impregnation showed a good stability owing to the cavitation effect of ultrasonic waves. The conversion of methyl acetate and yield of methyl acrylate remained above 20% and 9.0% (based on methyl acetate) for 100 h without obvious deactivation. Moreover, carbon deposition was the main factor for the deactivation of Cs–La–Sb/SiO2-(U), and the coked catalyst could be regenerated by calcination in air.
Two types of heterogeneous catalyst are applied for the formation of acrylates by vapor phase aldol condensation. One is considered as solid acid catalysts (e.g. V2O5, P2O5);19–26 the other is solid base catalyst, such as oxides or hydroxides of alkali metals and alkaline earth metals supported on porous materials (e.g. SiO2, ZrO2, Al2O3, TiO2, MgO and ZSM-5).26–35 Nevertheless, more attentions are paid to solid base catalysts for vapor phase aldol condensation because of the easy preparation and high catalytic activity. SiO2 supported cesium catalyst was reported to be a good solid base catalyst for vapor phase aldol condensation. Mamoru Ai27 studied the vapor-phase aldol condensation of methyl propionate with formaldehyde over a series of silica-supported alkali and alkaline earth metal catalysts and found that silica-supported cesium catalyst showed a higher selectivity than other catalysts. SiO2 modified by mixed metals was developed to further improve the catalytic performance for vapor phase aldol condensation. Zr–Mg–Cs/SiO2 catalyst,30 Zr–Fe–Cs/SiO2 catalyst31 and Bi–Cs/SiO2 catalyst35 exhibited good reusability and long cycle life for the aldol condensation of methyl propionate and formaldehyde.
Ordered mesoporous silica material SBA-15 now received much attention as support for solid base catalyst used in vapor phase aldol condensation thanks to its special two-dimensional hexagonal structure,31,36,37 and well catalytic performance31,38 was obtained over this kind of catalyst. Compared to SBA-15, common amorphous SiO2 was easily synthesized with lower cost. If the catalyst prepared using common amorphous SiO2 shows the similar catalytic performance, the catalyst would have higher industrial application value.
A large number of papers have reported the preparation of methacrylic acid26,29,34 and methyl methacrylate19,27,28,30,31,33,35 by vapor phase aldol condensation, while little has studied the formation of methyl acrylate by aldol condensation of formaldehyde and methyl acetate. However, vanadium phosphorus oxides as solid acid catalyst was studied for the aldol condensation of formaldehyde and methyl acetate by Ai M.20,25 and Feng X. et al.24 For the source of formaldehyde, formalin is much more attractive than trioxymethylene and methylal because of the price and available. This paper investigated the catalytic performance of vapor phase aldol condensation of formaldehyde and methyl acetate using the aqueous solution of 36% HCHO as the source of formaldehyde over amorphous SiO2 supported cesium catalyst prepared by vacuum impregnation and ultrasonic impregnation. Then, lanthanum and antimony species were added to improve the catalytic activity which was the first time for the catalyst used in vapor phase aldol condensation. Also, the deactivation mechanisms of the catalysts prepared by different impregnation methods were discussed.
The concentration of the metal salt was determined by the desired metal-loading (4.7 wt% based on the quality of the support for Cs, 2.5 wt% for La, and 2.5 wt% for Sb) and the amount of water (ethanol for SbCl3) that the support can absorb during the impregnation. The catalysts prepared by vacuum impregnation under 6 × 10−2 Pa were donated as Cs/SiO2-(V) and Cs–La–Sb/SiO2-(V). The catalysts prepared by ultrasonic impregnation for 2 h were donated as Cs/SiO2-(U), Cs–Sb/SiO2-(U) and Cs–La–Sb/SiO2-(U). For Cs–Sb/SiO2 and Cs–La–Sb/SiO2 catalysts, the impregnation of antimony, lanthanum and cesium was finished step by step. All the impregnated catalysts were dried overnight in air at 100 °C and then calcined in flowing air at 600 °C for 1 h.
The N2 adsorption–desorption isotherm of catalyst was measured by a Surface Area Analyzer (NOVA 2200e, Quantachrome) at 77 K in order to investigate the textural properties of catalysts. The samples were firstly outgassed at 50 °C for 30 min and then at 300 °C (150 °C for deactivated catalysts) for 3 h before measurement. The total surface area was calculated by multi-points BET method using thee adsorption data in the relative pressure range from 0.05 to 0.30. The total pore volume was determined from the amount absorbed at the relative pressure of about 0.99. The pore size distribution curve and mean pore diameter were calculated by the BJH model. Micropore surface area and micropore volume were calculated by t-plot method.
The amount of cesium, lanthanum and antimony in the catalysts was identified by inductively coupled plasma (ICP, OPTIMA2100DV, Perkin Elmer).
The acidity and basicity of the catalysts were measured by temperature-programmed desorption of ammonia (NH3-TPD) and carbon dioxide (CO2-TPD) on a PX200 TPD/TPR instrument equipped with a TCD (CHEMBET 3000).
X-ray photoelectron spectroscopy (XPS) measurements were conducted on AXIS Ultra DLD spectrophotometer in order to analyze the surface properties of the catalysts.
Thermogravimetric (TG) analysis of the deactivated catalysts was carried out on a STA409 PC analyzer. The samples were heated from room temperature to 800 °C with a rate of 10 °C min−1 under air in a flow of 30 mL min−1.
GC-MS (Agilent 5973N) was used to determine the composition of soluble coke in deactivated catalysts. The framework of deactivated catalyst was eliminated using 15% HF, and then the soluble coke was extracted with CH2Cl2.
The aldol condensation reaction was carried out in a single pass, fixed bed flow reactor made of a stainless steel tube mounted vertically in the furnace at atmospheric pressure. Formalin, an aqueous solution of HCHO (36%), was used as a source of formaldehyde (HCHO). HCHO was dissolved in methyl acetate (MeOAc) with a molar ratio of 1/10, and methanol (HCHO/CH3OH = 1, wt) was added into the reaction feed in order to avoid the polymerization of formaldehyde and prevent the formation of side product acetic acid (AA) from hydrolysis of MeOAc. The mixed solution was injected in from the top of reactor using a syringe pump, and nitrogen was fed in from the top of the reactor. The reaction was carried out at 380 °C and 1.0 h−1 WHSV. The product was collected and analyzed by an HP5890 gas chromatograph equipped with a 30 m HP Innowax capillary column and an FID detector.
The activity of catalyst was measured by testing the conversion of MeOAc; the selectivity and yield of MA and acetone which were calculated by equations below.
CMeOAc (conversion of MeOAc) = (MeOAcin,mol − MeOAcout,mol)/MeOAcin,mol × 100% |
SMA (selectivity of MA) = MAout,mol/(MeOAcin,mol − MeOAcout,mol) × 100% |
YMA (yield of MA) = CMeOAc × SMA |
The N2 adsorption–desorption isotherm and pore size distribution curve of SiO2 support are shown in Fig. 2. The N2 adsorption–desorption isotherm of SiO2 support belonged to classic type-IV according to the classification of the International Union of Pure and Applied Chemistry (IUPAC).40 There was a clear H3-type hysteresis loop in the isotherm curve at the relative pressure of 0.7–1.0, which indicated the mesoporosity of the SiO2 support. The pore size distribution curve of SiO2 support indicated a sharp peak centred at 17.95 nm. The textural properties (surface area, pore volume and mean pore diameter) of SiO2 supported cesium catalysts and parent SiO2 are listed in Table 1. After modification of SiO2 support with metal species, the surface area and pore volume both decreased, which indicated that the metal oxide components were loaded into the channels.30 However, the mean pore diameter of SiO2 supported cesium catalysts, Cs/SiO2-(V) and Cs/SiO2-(U), increased slightly from 17.95 nm to 17.97 nm and 17.99 nm. It was because that the cesium species blocked some micropores of SiO2 support,31 which also caused the decrease of micropore surface and micropore volume. There was a significant reduction in the surface area and pore volume for Cs–La–Sb/SiO2 owing to the more modification by cesium, lanthanum and antimony. For different catalysts prepared by vacuum and ultrasonic impregnation, catalysts prepared by ultrasonic impregnation possessed slightly lower surface area (114.3 m2 g−1, 105.8 m2 g−1) and pore volume (0.708 cm3 g−1, 0.671 cm3 g−1) than catalysts prepared by vacuum impregnation (114.9 m2 g−1 and 106.4 m2 g−1, 0.706 cm3 g−1 and 0.674 cm3 g−1). However, the pore volume of Cs/SiO2-(U) was higher than that of Cs/SiO2-(V) due to the instrumental and analysis error. The amount of active components supported on SiO2 is summarized in Table 2. The ICP results showed that the actual amount of active components supported on SiO2 was closed to the theoretical loading amount. It can be seen that the amount of the active components in the catalysts prepared by ultrasonic impregnation was higher than the catalysts prepared by vacuum impregnation. Wang et al.41 studied influences of different impregnation methods for Cs/HX catalyst, and reported that ultrasonic impregnation benefited the sufficient diffusion of impregnation solution into the channels of support. More metal active components supported on SiO2 also caused lower pore structural parameters of the catalysts prepared by ultrasonic impregnation.
Catalysts | Surface area (m2 g−1) | Pore volume (nm) | Mean pore diameter (nm) | ||
---|---|---|---|---|---|
Total | Micropore | Total | Micropore | ||
SiO2 | 156.2 | 35.28 | 0.840 | 0.017 | 17.95 |
Cs/SiO2-(V) | 114.9 | 30.75 | 0.706 | 0.013 | 17.97 |
Cs/SiO2-(U) | 114.3 | 30.01 | 0.708 | 0.014 | 17.99 |
Cs–Sb/SiO2-(U) | 111.2 | 28.76 | 0.683 | 0.012 | 17.72 |
Cs–La–Sb/SiO2-(V) | 106.4 | 25.70 | 0.674 | 0.012 | 17.52 |
Cs–La–Sb/SiO2-(U) | 105.8 | 24.96 | 0.671 | 0.012 | 17.48 |
Catalysts | Cs (wt%) | La (wt%) | Sb (wt%) |
---|---|---|---|
Cs/SiO2-(V) | 4.46 | — | — |
Cs/SiO2-(U) | 4.67 | — | — |
Cs–La–Sb/SiO2-(V) | 4.48 | 2.12 | 2.18 |
Cs–Sb/SiO2-(U) | 4.60 | — | 2.19 |
Cs–La–Sb/SiO2-(U) | 4.62 | 2.26 | 2.19 |
The acidity and basicity of SiO2 supported cesium catalysts were determined respectively by temperature-programmed desorption of NH3 and CO2. Fig. 3 depicts the desorption profiles of NH3 on different SiO2 supported cesium catalysts. The amount of acid sites can be obtained from the area of desorption peak. All catalysts exhibited a peak below 300 °C which was assigned to desorption of NH3 adsorbed on weak acid sites. The NH3-TPD profiles of Cs/SiO2 catalysts also showed a high temperature peak at around 350 °C corresponding to strong acid sites generated by the impurities on the surface of SiO2. Moreover, Cs–Sb/SiO2-(U) catalyst exhibited more weak and medium acid sites than Cs/SiO2-(U) attributed to the medium Lewis and Bronsted acidity possessed by antimony species.42 While, lanthanum species of Cs–La–Sb/SiO2 catalysts covered the strong acid sites and resulted in no high temperature desorption peak of NH3 over Cs–La–Sb/SiO2 catalysts. Fig. 4 shows the CO2-TPD results of the SiO2 supported cesium catalysts. The peak in the range of 150 °C and 300 °C, corresponding to weak basic sites, was exhibited on cesium-supported SiO2 catalysts. It is worth noting that desorption peak of CO2 on Cs–La–Sb/SiO2 catalyst shifted to higher temperature. Meanwhile, the catalyst prepared by ultrasonic impregnation showed the desorption peak at higher temperature than the catalyst prepared vacuum impregnation due to more active components supported on SiO2 (as shown in Table 2).
The XPS measurement of SiO2 supported cesium catalyst was investigated to determine the chemical state of metallic species on SiO2. The wide XPS spectra (Fig. 5A) confirmed that Cs/SiO2 catalysts contain cesium (724 eV), silicon (103.4 eV) and oxygen (531.6 eV). Meanwhile, lanthanum (834.9 eV) was detected on Cs–La–Sb/SiO2 catalysts. An overlapping for O 1s and Sb 3d5/2 photoelectron lines would exist at around 532 eV,43 so the XPS spectra of antimony was not clearly showed in the wide XPS spectra of Cs–La–Sb/SiO2. The high-resolution Cs 3d5/2 spectra of cesium-supported catalysts (Fig. 5B) showed three peaks at 724.5 eV, 725.2 eV and 726 eV which can be assigned to Cs2O2,44 Cs2O45 and Cs11O3,46 respectively. Moreover, all Cs 3d5/2 spectra of SiO2 supported cesium catalysts showed a peak at 724 eV corresponded to Cs in SiO2,45 Yan et al. also reported Si–O–Cs species in Cs/SBA-15 catalyst.38 The percentage contents of these cesium species determined by normalization method were listed in Table 3. From the NH3-TPD profile of Cs–La–Sb/SiO2 catalyst in Fig. 3, it can be easily seen that the strong acid site on the surface of SiO2 were neutralized by lanthanum species. The content of base Cs–O–Si structure remarkably increased after addition of lanthanum which changed the surface properties of SiO2 support as shown in Table 3.
Catalyst | Cs–O–Si (wt%) | Cs2O2 (wt%) | Cs2O (wt%) | Cs11O3 (wt%) |
---|---|---|---|---|
Cs/SiO2-(V) | 23.34 | 31.29 | 39.86 | 5.51 |
Cs/SiO2-(U) | 28.75 | 22.60 | 41.93 | 6.72 |
Cs–Sb/SiO2-(U) | 30.78 | 24.51 | 40.22 | 4.49 |
Cs–La–Sb/SiO2-(V) | 65.19 | 16.58 | 16.40 | 1.83 |
Cs–La–Sb/SiO2-(U) | 58.01 | 21.79 | 18.91 | 1.29 |
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Fig. 7 Catalytic stability of Cs–La–Sb/SiO2 catalysts for aldol condensation of HCHO and MeOAc: (A) Cs–La–Sb/SiO2-(V); (B) Cs–La–Sb/SiO2-(U). |
In order to clarify the deactivation mechanism, the crystal structure and pore structure of used catalysts were characterized by XRD and N2 adsorption–desorption analysis. It can be seen from Fig. 8 that the frameworks of used Cs–La–Sb/SiO2 catalysts were not destroyed during the reaction and no new phases occurred. Table 4 lists the textural properties (surface area, pore volume and mean pore diameter) of used catalysts. The surface area and pore volume of both the used Cs–La–Sb/SiO2-(U) and Cs–La–Sb/SiO2-(V) catalysts reduced because of the carbon deposition on catalysts.
Catalyst | Surface area (m2 g−1) | Pore volume (cm3 g−1) | Mean pore diameter (nm) | ||
---|---|---|---|---|---|
Total | Micropore | Total | Micropore | ||
Used Cs–La–Sb/SiO2-(V) | 96.2 | 6.27 | 0.489 | 0.002 | 9.572 |
Used Cs–La–Sb/SiO2-(U) | 84.7 | 5.89 | 0.403 | 0.002 | 9.063 |
From the discussion above, coke deposited on the catalysts was probably a main factor responsible for the deactivation for the deactivation of the catalysts. The thermo stability properties of the coke on the deactivation catalysts were investigated by a TG analyzer. As shown in Fig. 9, there were two distinct weight loss steps displayed on the deactivated catalysts. The first weight loss from room temperature to 300 °C was due to the desorption of physically adsorbed water, and the second weight loss occurred from 300 °C to 550 °C, which was definitely owing to the combustion of deposited coke on deactivated catalysts. The second weight loss in the temperature from 300 °C to 550 °C could be considered as the coke amount on the deactivated catalyst. So, the amount of coke deposition for used Cs–La–Sb/SiO2-(V) was 1.4 wt%, while 2 wt% coke deposition was obtained over used Cs–La–Sb/SiO2-(U). The coke may be removed through carbon combustion under 500 °C in air. Also, the nature of soluble coke on catalysts was further analyzed by GC-MS. Fig. 10 showed the compositions of soluble coke. The composition of soluble coke in two deactivated catalysts was mainly aromatic hydrocarbon. Toluene, DMBs, TriMBs and hextraMB were all detected.
The deactivated catalysts were regenerated at 500 °C for 3 h under a steam of air. The catalytic performances of regenerated Cs–La–Sb/SiO2-(U) and Cs–La–Sb/SiO2-(V) catalysts were shown in Fig. 11. It clearly indicated that activity of Cs–La–Sb/SiO2-(U) was restored. The conversion of methyl acetate was up to 20.36% and the yield of methyl acrylate is up to 9.24%. The conversion of methyl acetate and the yield of methyl acrylate were approximately 12.34% and 4.90%, respectively over regenerated Cs–La–Sb/SiO2-(V) catalyst. So, the deactivated Cs–La–Sb/SiO2-(U) catalyst was regenerated completely and the deactivation of Cs–La–Sb/SiO2-(U) mainly resulted from carbon deposition.
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Fig. 11 Catalytic performance of regenerated Cs–La–Sb/SiO2 catalysts for aldol condensation of HCHO and MeOAc. |
However, Cs–La–Sb/SiO2-(V) catalyst still exhibited unsatisfactory catalytic performance after removing the carbon deposition. Besides carbon deposition, the loss of active component was another important factor that might cause the deactivation of catalysts. The metal contents of used Cs–La–Sb/SiO2 catalysts were determined by ICP. The results were listed in Table 5, showing the metal content of used Cs–La–Sb/SiO2-(U) catalyst was almost in accord with the fresh catalyst. While the cesium content of Cs–La–Sb/SiO2-(V) catalyst sharply decreased after reaction. So, the loss of active component was the main factor of the deactivation of Cs–La–Sb/SiO2-(V) catalyst prepared by vacuum impregnation. According to the studies of the water solubility and diffusion in alkali silicate melts,47 there was a tendency to leach in the presence of water for alkali metal ions in the silicate. The alkali oxide crystallites tended to agglomerate on the support and the agglomeration of cesium compounds was quite hygroscopic48 and prone to dissolving in water, which resulted in the loss of cesium. From Table 5, it could easily seen that Cs–La–Sb/SiO2-(U) prepared by ultrasonic impregnation could prevent the agglomerate of cesium compounds. The physical and chemical effects of ultrasonic cavitation during ultrasonic impregnation had an impact on the property of catalysts. Ultrasonic cavitation could reduce the agglomeration between particles and improve the dispersion of cesium on the surface. In addition, the ultrasonic cavitation could enhance the interaction between the cesium species and the silica. This indicated that the Cs–La–Sb/SiO2-(U) prepared by ultrasonic impregnation had a good reusability.
Catalysts | Cs (wt%) | La (wt%) | Sb (wt%) |
---|---|---|---|
Used Cs–La–Sb/SiO2-(V) | 2.84 | 2.06 | 2.14 |
Used Cs–La–Sb/SiO2-(U) | 4.53 | 2.11 | 2.14 |
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