S. Boudjemaa,
E. Vispeb,
A. Choukchou-Braham*a,
J. A. Mayoralb,
R. Bachira and
J. M. Fraileb
aLaboratoire de Catalyse et Synthèse en Chimie Organique, Faculté des Sciences, Université de Tlemcen, Algeria. E-mail: cba@mail.univ-tlemcen.dz
bDepartamento de Química Orgánica, Instituto de Síntesis Química y Catálisis Homogénea, Facultad de Ciencias, Universidad de Zaragoza-CSIC, Pedro Cerbuna, 12, E-50009 Zaragoza, Spain
First published on 12th December 2014
A new heterogeneous catalyst (PVMo/bentonite), consisting of vanadium substituted polyphosphomolybdate with Keggin structure H4[PVMo11O40]·13H2O (PVMo) supported on acid activated bentonite (clay from Hammam Boughrara, Maghnia, Algeria), was prepared by witness impregnation and characterized by X-ray diffraction, BET, Fourier-transformed infrared spectroscopy, 31P NMR, UV-vis diffuse reflectance spectroscopy and thermogravimetric & differential thermal analysis (TG-DTA). X-ray diffraction indicated that PVMo was properly loaded on bentonite as a support. Heterogenization of homogenous catalysts is really interesting, as heterogeneous catalysts are recoverable. Therefore, the synthesized materials can be used as efficient heterogeneous catalysts for epoxidation of cyclohexene. The obtained results showed that a better catalytic activity can be obtained with PVMo/bentonite (81.5% of conversion), by drop addition of H2O2, for 3 hours.
Polyoxometalates (POMs) are early transition metal–oxygen anion clusters that exhibit a variety of structures in chemical composition and architecture. Among various POM structural classes, the Keggin-type POMs occupy an important place in the research domain. In the solid state, POMs are ionic crystals consisting of large polyanions, [XM12O40]n− (X = P, Si… and M = W, Mo), counter-cations (protons, alkalines, transition metals, ammonium salts…) and crystallization water. The acids corresponding to POMs, namely heteropolyacids (HPAs), are known to possess a Brønsted acidity which is stronger than that of many mineral acids or conventional acidic solids; indeed, they can display a strong oxidative power. For these reasons, these clusters are widely investigated, to see whether they can be used as catalysts in reactions requiring both acidic and oxidative conditions; these reactions can be performed in homogeneous as well as heterogeneous systems.12–16
Vanadium incorporated molybdophosphoric acid (PVMo) catalysts show unique catalytic features for oxidation due to their bifunctional character which arises from the redox nature of vanadium and the oxidative/acidic character of molybdophosphoric acid.17 Several authors have investigated V incorporated molybdophosphoric acid catalysts by replacing 1–3 Mo atoms by the corresponding number of V atoms.18,19 The acidic, redox and thermal stability properties of PVMo catalysts are influenced by the degree of V substitution.20 However, owing to their small surface area (<10 m2 g−1) and separation problems from the reaction mixture, their catalytic performances are often limited to heterogeneous catalysis.21 For that reason, several authors proposed to disperse them on porous supports with large surface areas to make the active sites of HPAs more accessible to reactants. The deposition of the modified HPAs on supports is important to increase the surface area. It is always advantageous to use supports like silica, ZrO2, active carbon, SBA-15, and zeolite, etc.22–27
The synergism of clay minerals and heteropolyacids was discussed for the development of many green processes with potential industrial applications.28 Acid modified clay minerals can also be used as efficient supports29 because they exhibit higher surface area, pore volume, pore diameter and higher surface acidity;30 this gives them better adsorption and catalytic properties. In particular, acid treated clay catalysts have received considerable attention in different organic syntheses, as catalysts or as supports, because of their environmental compatibility, low cost and simplicity of use. Using clay catalysts, we can conduct environmentally benign green chemistry both at industrial level and at a laboratory scale. The acid strength of HPA, supported on some of the materials mentioned above, is lower than that of bulk HPA; this is due to the interaction of HPA with surface functional groups of supports. In the case of a composite material, the support has an influence on the acidity function of HPA and vice versa.31 Acid-treated montmorillonite exhibits relatively strong acid sites.32 Several research groups have reported the use of activated clay-supported HPA (e.g., 12-tungstophosphoric acid) in the etherification of phenethyl alcohol with alkanols,33 synthesis of 1,5-benzodiazepine derivatives both in solution and under solvent-free conditions,34 etherification of acetic acid with sec-butanol,29,35 and hydroxyl alkylation of phenol, respectively. Beside HPA, many metals or metal oxides can be strategically supported on activated clay, metal oxide pillared interlayer clays (PILCs), and porous clay heterostructures (PCHs) as catalysts for organic synthesis.36,37
In the present study, we report that HPA like 1-vanado-11-molybdophosphoric acid (PVMo) is supported on acid-activated montmorillonite clay having high surface area, prepared from montmorillonite by HCl acid activation; it is also considered as a solid acid catalyst for the epoxidation of cyclohexene, using hydrogen peroxide as an oxidant. There are various reasons for choosing this reaction as a model from a wide variety of acid catalyzed and oxidation reactions. Cyclohexene epoxidation is attracting both academic and industrial interest in homogeneous and heterogeneous systems.5,8,9,38–49 Cyclohexene epoxide is a valuable organic intermediate, used in the synthesis of products such as chiral pharmaceuticals, pesticides, epoxy paints, rubber promoters, dyestuffs, plant-protection agents and stabilizers for chlorinated hydrocarbons.43,47–51 Again, HPA supported on clay is never used in this reaction. The active centers, responsible for the reactions, are discussed in detail in the manuscript.
Raw clay (montmorillonite) [Hammam Boughrara (Roussel quarry), Algeria] containing silica sand, iron oxide, etc. was purified by a standard sedimentation method to collect the <2 μm fraction before use.
The purified clay (1 g) was refluxed with 1 M HCl acid (100 mL) at 80 °C for 4 h. The slurry was cooled, filtered, washed thoroughly with water and dried in an air oven at 80 °C, for 24 h.53 The clay samples thus prepared were designated as HMont.
Samples having 10 and 20% loading of PVMo on HMont were synthesized by means of the incipient wetness impregnation method. A known amount of PVMo was dissolved in water and the hot support (dried at 120 °C in a furnace, for 6 h) was added to the solution. The dispersion was stirred for 24 h at room temperature, and the solvent was evaporated under vacuum. The catalyst was dried at 100 °C for 4 h and then calcined at 250 °C for 4 h. They were all designated as X% PVMo/HMont.
The surface area and porosity were measured at liquid nitrogen temperature, using Quantachrome Instruments (Nova 1000e). Prior to each adsorption–desorption measurement, the sample was degassed at T = 150 °C for 3 h. The specific surface areas were determined using the BET equation and the microspore volumes by the de Boer's t-method. The αs plots were used to estimate the microporosity where αs = (n/ns) ref (ns) is the amount adsorbed by the reference solid (p/p0 = s).
The materials were characterized by X-ray powder diffraction (XRD) using a Rigaku D/max2500 diffractometer with Cu Kα radiation (λ = 1.541874 Å) in the range 2θ = 2–70° with a step of 0.02° and an acquisition time of 1 s.
Fourier transform infrared (FTIR) spectra were recorded by an Agilent Technologies Cary 600 series FTIR spectrometer using KBr pellets, under atmospheric conditions. The FTIR spectra were obtained in KBr pellets in the range of 400–4000 cm−1, and all spectra were collected at room temperature with a resolution of 4 cm−1.
31P MAS NMR (161.70 MHz) spectra were measured at room temperature on a Bruker Avance 400 spectrometer, where 85% H3PO4 was used as an external reference.
The UV-vis diffuse reflectance spectra of the samples were collected in a JASCO V-670 UV-vis spectrophotometer equipped with a Harrick Praying mantis diffuse reflectance accessory. Spectral grade BaSO4 was used as a reference material.
The thermogravimetric and differential thermal analyses (TG-DTA) measurements of representative samples were carried out using a TA instruments 2960 SDT V3 thermal analyzer. The TG-DTA experiments were performed under argon and nitrogen. About 10 mg of the sample was heated at a rate of 10 °C min−1. Quartz cells were used as sample holders with α-Al2O3 as a reference. The studied temperature range was 25–800 °C.
The conversion, product selectivity and product yield were calculated as follows:
Sample | Contents (wt%) | ||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
SiO2 | Al2O3 | Fe2O3 | CaO | MgO | Na2O | K2O | TiO2 | Pa | Moa | Va | |
a These numbers correspond to the numbers of atoms deduced from the raw wt% found from XRF, as the number of Mo atoms is fixed to 11. | |||||||||||
PVMo | — | — | — | — | — | — | — | — | 0.99 | 11.00 | 1.00 |
HMont | 57.12 | 19.87 | 2.62 | 0.43 | 3.10 | 0.30 | 2.70 | 0.24 | — | — | — |
10% PVMo/HMont | 55.31 | 22.20 | 2.64 | 0.01 | 1.80 | 0.09 | 3.28 | 0.24 | 0.98 | 11.00 | 1.00 |
20% PVMo/HMont | 53.82 | 23.12 | 2.92 | 0.01 | 2.01 | 0.09 | 3.00 | 0.23 | 1.05 | 10.99 | 1.00 |
Sample | SBET/m2 g−1 | Pore V/cm3 g−1 | Vm/cm3 g−1 | Av. pore radius/Å | d001/Å |
---|---|---|---|---|---|
HMont | 195 | 0.27 | 0.007 | 1.89 | 1.65 |
10% PVMo/HMont | 162 | 0.21 | 0.025 | 1.93 | 1.68 |
20% PVMo/HMont | 141 | 0.17 | 0.024 | 1.97 | 1.73 |
The reduction in surface area and pore volume upon PVMo loading might be due to the blockage of pores by PVMo molecules. These observations suggest that the Keggin units do not penetrate inside the pores but rather stay outside of the surface of the support. Although, in most investigations, the authors considered that HPA can enter into the pores of the support,14,54,55 we believe that these conclusions do not take into account the question of anion–anion repulsion and the chemical interaction between the support and HPA protons that could affect the final location of HPA in or on the support.
The complete adsorption–desorption isotherms of calcined samples, are presented in Fig. 1A. All the curves are nearly similar and can be included in type IV in the BDDT classification. The hysteresis loops, at low pressure, indicate the presence of microspores.56–58 Assuming the pores to be cylindrical, the average pore radius can be calculated using the formula r = 2Vp/Sp, where r is the average pore radius, Vp is the pore volume, and Sp is the specific internal surface area of the pores. The average pore radius calculated by this method is reported in Table 2. This shows that with the increase in % loading of PVMo, the average pore radius increases. It is interesting to note that the pore size distribution, determined from the desorption branch of the N2 adsorption isotherm using the Barrett–Joyner–Halenda (BJH) method (Fig. 1B), shows that the average pore sizes of different weight percents of PVMo on HMont are in the microporous region (Fig. 2).
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Fig. 1 (A) N2 adsorption–desorption isotherms. (B) Pore size distribution curves of different samples determined by the BJH method. |
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Fig. 6 UV-vis DR spectra of catalysts: (a) HMont, (b) 10% PVMo/HMont, (c) 20% PVMo/HMont, (d) pure PVMo. |
This band is assigned to (Fe3+ ← O2−, OH− or OH2) charge transfer band for the iron present in the octahedral layer of the clay mineral. The UV-vis spectrum of the catalyst (Fig. 6b and c) showed absorption maxima at 258 and 308 nm. The 258 nm absorption is typical for the Keggin structure of H4PMo11O40,28 while the 308 nm shoulder is characteristic of Vanadium incorporation into Keggin ion.1,51 These bands are due to ligand-to-metal charge-transfer (LMCT) transitions associated with octahedrally coordinated Mo6+ units.67 These two absorption bands are clearly seen in the solid-state UV-vis spectra of 20% PVMo, while in the 10% PVMo, the 308 nm band is hardly seen. Since pure HMont (Fig. 6d) shows no UV absorption, then this result confirm the presence of the undegraded primary Keggin structure of PVMo species in 20% PVMo, but suggests a lack of vanadium substituted HPA species in the case of 10% PVMo.
The DTA/TGA of acid activated clay HMont (Fig. 7B) showed an endothermic signal below 100 °C which represents the dehydration of the smectic structure. A steady loss of mass of about 17%, up to 500 °C, was attributed to the loss of physisorbed and interlayer water and to the dehydroxylation caused by the breaking of structural OH-groups in the support.30,69
The TGA of supported PVMo onto HMont (Fig. 7C and D) showed a mass loss of about 18% within the temperature range of 80–150 °C due to a loss of adsorbed water molecules. A gradual mass loss of about 3%, up to 500 °C, was also observed, which indicates an increase in the thermal stability of PVMo on HMont support. This might be due to the formation of intermolecular bondings between the support and the heteropoly acid; it indicates the presence of a chemical interaction between them.35,70,71
The results show that the way H2O2 60% is added has an impact on conversion (Fig. 9). The best conversion (81.5%) is reached when hydrogen peroxide is drop-wise added during 3 hours, selectivity to 1,2-diol ids very high (91.6%) with a small contribution (4.6%) of allylic oxidation.
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Fig. 9 The effect of addition type of H2O2 60% on the oxidation of cyclohexene (0.025 g catalyst 20% PVMo/HMont, 30 mmol cyclohexene, 30 mmol H2O2, 10 mL CH3CN, 9 h of reaction, 70 °C). |
The catalytic activities of different samples were evaluated for the oxidation of cyclohexene. All the catalytic systems proved to be highly active and selective towards diol. A blank reaction was performed in the absence of catalyst and no product was detected.
Similar oxidation reactions were also carried out with acid activated montmorillonite support and only a negligible catalytic activity was evidenced, and also no desired product was detected. The obtained results clearly indicate that the POM species are responsible for the high oxidation activity of these heterogeneous catalysts. Besides, the large pores of the HMont support permit diffusion of a relatively large quantity of cyclohexene and oxidation proceeds selectively inside the pores of the support.
Generally, the reaction is believed to proceed through the mechanism postulated for Keggin type POMs. Monomeric, dimeric, and tetrameric peroxo species are generated by the reaction of polyoxometalates with hydrogen peroxide, and the peroxo species are supposed to be the active species for epoxidation of olefins within a POM/H2O2 system.42,67,72 It has been postulated that the epoxidation reaction rate and epoxide yield, for the same type of catalytic species, are determined by the catalyst's acid strength.40,73 The lower activity of the PVMo/HMont, in comparison with PVMo catalyst, shows the importance of diffusional limitations. However the high diol selectivity with 20% PVMo/HMont is clearly justified considering the acidity of the support. The catalytic performance of the heterogeneous catalysts is also related to the fine dispersion of the active catalytic species within the supports. Here, the acid Brønsted sites of PVMo, acid Lewis sites of support and redox properties of PVMo are shown to have a crucial effect on the oxidation process. From Table 3, it can also be seen that the catalytic activity of 20% PVMo/HMont is better than that of 10% PVMo/HMont. The importance of the support has been also observed using HPAs immobilized in other supports, such as such as MCM-41 (ref. 24) SiO2, SBA-15, ZrO2-grafted SBA-15.74
Catalysts | Conversion (%) | Sel. epoxide (%) | Sel. diol (%) | Sel. allylic product (%) |
---|---|---|---|---|
a Reaction conditions: 0.025 g catalyst, 30 mmol cyclohexene, 30 mmol H2O2, 10 mL CH3CN, 70 °C, 9 h. | ||||
HMont | 28.5 | — | — | — |
PVMo | 91.1 | 0.4 | 70.4 | 29.2 |
10% PVMo/HMont | 70.6 | 16.9 | 36.8 | 46.3 |
20% PVMo/HMont | 81.5 | 3.8 | 91.6 | 4.6 |
The comparison of the reaction at different temperatures (Table 4) so that, with both supported catalysts, best yields and selectivity's are reached at 70 °C, both results are worse in reactions carried out at lower and higher temperatures.
Catalysts | Temperature/°C | Conversion/% | Sel. epoxide/% | Sel. diol/% | Sel. allylic product/% |
---|---|---|---|---|---|
a Reaction conditions: 0.025 g catalyst, 30 mmol cyclohexene, 30 mmol H2O2, 10 mL CH3CN, 9 h of reaction. | |||||
20% PVMo/HMont | 40 | 24.2 | 3.1 | 61.5 | 35.4 |
60 | 42.7 | 19.9 | 65.7 | 14.4 | |
70 | 81.5 | 3.8 | 91.6 | 4.6 | |
80 | 59.7 | 12.8 | 82.3 | 4.9 | |
10% PVMo/HMont | 60 | 33.5 | 31.8 | 33.3 | 39.9 |
70 | 70.6 | 16.9 | 36.8 | 46.3 | |
80 | 51.4 | 4.6 | 72.3 | 23.1 |
A study was also carried out in order to see the effect of reaction time on the catalytic activity, with 0.025 g of catalyst, 30 mmol of cyclohexene, 30 mmol of hydrogen peroxide, 10 mL of acetonitrile, at the temperature 70 °C. The experimental results (Fig. 10) indicate that the reaction proceeds more slowly in the presence of heterogeneous catalysts. This may be attributed to diffusional restrictions of the reagents inside the pores of the catalyst.
The energy of activation was calculated using rate constant (k) determined at different temperatures. It is a well-established fact that in the oxidation of hydrocarbon, the rate of the reaction is proportional to the product concentration. The conversion vs. time plots obtained in the present work indicate that the cyclohexene oxidation is not an exception to this fact. The reaction is considered to be second order with respect to the product and reactant concentration. The rate expression used by the many workers for oxidation reactions2,10,11 is adopted here.
−d[cyclohexene]/d(t) = k[cyclohexene]2 | (1) |
1/[cyclohexene] = 1[cyclohexene]0 + kt | (2) |
A plot of 1/[cyclohexene] with respect to time gives a linear relationship showing a pseudo-second-order dependence on the cyclohexene, k represent the apparent rate constant. Fig. 11a shows this plot. All the points fall on a straight line which proves that the rate expression holds good under the conditions employed for the reaction in the present work.
Fig. 11b displays the graph of ln(k) obtained from expression (2) within 6 h versus the inverse of the reaction temperature for each temperature. The apparent activation energy (Ea) calculated from the Arrhenius plot (Fig. 11b) was ca. 3.216 kcal mol−1. K. C. Gupta et al. and M. Abrantes et al.75,76 reported the same apparent activation energy. However this value was low to the values reported in many works (Table 5).
Catalyst | Oxidant | Ea (kcal mol−1) | Reference |
---|---|---|---|
a Reaction conditions: 10 mL acetonitrile, 30 mmol cyclohexene, and 0.025 g catalyst, with H2O2–cyclohexene = 1.0. The reaction temperatures, are 40, 60, 70 and 80 °C, respectively. | |||
MoO2 (SAL-SH.)DMF | O2 | 25.8 | 4 |
Uncatalysed | 20.6 | 77 | |
MnO2 | 13 | 78 | |
Ru(III)–EDTA | H2O2 | 8.6 | 79 |
Fe–HPHZ | 2.13 | 2 | |
[(nBu3Sn)2MoO4] | 5 | 3 | |
PVMo/HMont | 3.21 | Present work |
The catalysts were filtered and reused after 9 h of reaction time. They were washed for several times with a solvent, and then dried at room temperature and finally used in cyclohexene oxidation with a fresh reaction mixture. As a typical example, the catalyst 20% PVMo/HMont showed (Fig. 12) a conversion of 81% in the first run, which decreased to about 61, 48 and 39% in the 2nd, 3rd and 4th run, respectively. The amount of catalyst leaching after each run was determined by ICP analysis. In this manner, the filtrates were collected after each run and used to determine the amounts of leached vanadium (Table 6). The decrease in catalytic activity is due to the leaching of HPA (of about 1–2%) from the support into the liquid phase during the catalytic reactions; this was confirmed by the well-known ascorbic acid test.77 Although the catalyst was washed after filtration to remove all the adsorbed reactants and products, retention of some of the adsorbed reactants and products was still possible, and this might cause the blockage of active sites and consequently the decrease in the catalytic activity. The nature of the recovered catalyst was followed by FT-IR. After reusing the catalyst for several times, no change in the FT-IR spectrum was observed. However, the selectivity remained almost unchanged, and the catalysts were therefore reused four times.
Run no. | 1 | 2 | 3 | 4 |
Vanadium leaching (%) | 1.9 | 1.8 | 1.4 | 1.3 |
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