Ahmad Bayat,
Mehdi Shakourian-Fard,
Nona Ehyaei and
Mohammad Mahmoodi Hashemi*
Department of Chemistry, Sharif University of Technology, PO Box 11465-9516, Tehran, Iran. E-mail: mhashemi@sharif.edu
First published on 8th September 2014
A magnetic supported iron (iron(II) acetylacetonate) was synthesized to be used as an efficient and recyclable heterogeneous catalyst for the selective oxidation of sulfides to corresponding sulfoxides using H2O2 as a green oxidant at room temperature. The synthesized Fe3O4@SiO2-APTES(Fe(acac)2) catalyst presented excellent sulfide conversion and good sulfoxide selectivity. It can be easily recovered and reused for 8 reaction cycles without considerable loss of activity. The facile recovery of the catalyst is carried out by applying an external magnet device. The catalyst was fully characterized by techniques of TEM, SEM, XRD, EDS, FTIR, TGA, ICP-AES, VSM and elemental analysis (CHN).
Unprotected MNPs are often unstable and tend to aggregate during the catalytic transformations. Therefore, MNPs are coated by silica which acts as a stabilizer, limiting the effect of the outside environment on the core particles. Encapsulation of MNPs with amorphous silica not only contributes to the amelioration of chemical stability and dispersibility but also combines the advantageous properties of the magnetically responsive core and possible further surface-functionalized silica shell.8,9 At this time, silica-coated MNPs have appeared as versatile supports for the immobilization of active sites to form magnetically recyclable heterogeneous catalysts.6
Magnetically recoverable heterogeneous catalysts have been developed and applied in versatile organic synthesis for a wide range of catalytic reactions, including coupling reactions,10–12 Friedlander reaction,13 hydrogenation, hydroformylation, epoxidation reactions,14 selective oxidation of sulfides to sulfoxides.15
The selective oxidation of sulfides to sulfoxides is a great important in synthesis of chemically useful and biologically active molecules such as drugs.16–18 A stoichiometric amount of organic or inorganic oxidizing agents is required to affect this oxidation process and thus are dangerous and a large amount of toxic waste would be generated.19,20 In recent years, the procedures employing molecular oxygen or hydrogen peroxide as a primary oxidant in the presence of a catalyst have been found to be promising. Hydrogen peroxide is a non-toxic, cheap and effective oxidizer reagent. In addition, the oxidation reaction by hydrogen peroxide can be controlled easier than molecular oxygen and air.21–23
So far, some interesting transition metal catalysts have been reported for the sulfide oxidation, including Cu,24 Mo,16 Ti,25 V26 and Fe27 in the presence of a suitable oxidant such as hydrogen peroxide. Owing to low price and low toxicity of iron, Fe complexes have been widely used as homogenous catalysis. Very recently, the elegant work of He and co-workers28 has shown that Fe(acac)2 can be effectively applied for selective oxidation of sulfide to sulfoxide using oxygen in polyethylene glycol (PEG 1000) as solvent.
Although this protocol has shown remarkable properties such as high activity and selectivity in oxidation of sulfide to sulfoxide, but its use has been limited due to the solubility of catalyst in the liquid phase along with reactants. Therefore, the catalyst separation from the reaction products, recycling and reuse is difficult.
One way to solve this drawback is to immobilize catalytic system onto a large surface area solid carrier. One of the solid carriers is magnetic nanoparticles. The use of magnetic nanoparticles enables the separation from reaction mixture by an external magnet and reuse of the catalyst itself. In this study, we report our results about the preparation of Fe3O4@SiO2-APTES(Fe(acac)2) composite as a recoverable heterogeneous nanocatalyst for selective oxidation of sulfides to sulfoxides using 30% hydrogen peroxide as oxidant under mild reaction conditions in ethanol as green solvent.
The room-temperature magnetization in the applied magnetic field was performed by a homemade vibrating sample magnetometer (Meghnatis Daghigh Kavir Company, Iran) from −10000 to +10
000 Oersted. The immobilized iron content on the catalyst was measured by inductively coupled plasma atomic emission analysis (ICP-AES, PerkinElmer Optima 3300 DV). Elemental analysis (CHN analysis) was carried out on PerkinElmer, USA (2400, Series II).
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Scheme 1 Preparation of magnetically recoverable heterogeneous nanocatalyst Fe3O4@SiO2-APTES(Fe(acac)2). |
Typical magnetization curves as a function of the applied field at room temperature are shown in Fig. 2. As seen from Fig. 2, all of the samples exhibit superparamagnetic behavior and had little hysteresis, remanence and coercivity. Low decreasing of saturation magnetization of Fe3O4 from about 70 emu g−1 (a) to almost above 59 emu g−1 (b) for Fe3O4@SiO2 illustrated that the coated silica on Fe3O4 is thin layer and then the weight contribution from nonmagnetic portion is low. Also, the Fe3O4@SiO2-APTES(Fe(acac)2) catalyst could be easily separated by applying an external magnet (Fig. 2). This property provides an easy and efficient way to separate and recycle the catalyst from heterogeneous systems, which minimizes the loss of catalyst during the separation stage.
The transmission electron microscopy (TEM) and scanning electron microscopy (SEM) images for the Fe3O4@SiO2-APTES(Fe(acac)2) catalyst are shown in Fig. 3. Both the TEM and SEM showed that the Fe3O4@SiO2-APTES(Fe(acac)2) nanoparticles were present as spherical and uniform particles and the size of nanoparticles was less than 50 nm. The EDS analysis also confirms the presence of C, N, O, Si, and Fe atoms in the structure of Fe3O4@SiO2-APTES(Fe(acac)2) catalyst (Fig. S1, see ESI†).
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Fig. 3 Transmission electron microscopy (TEM) image (a), scanning electron microscopy (SEM) image (b). |
In order to confirm the existence of organic groups on the surface of Fe3O4@SiO2, FTIR spectra of Fe3O4@SiO2-APTES and the Fe3O4@SiO2-APTES(Fe(acac)2) catalyst are shown in Fig. 4. As shown in Fig. 4a, there are two characteristic absorption bands at 623 cm−1 and 1098 cm−1 which correspond to the stretching vibration of Fe–O and Si–O, respectively.32 The bands at 807 cm−1 and 467 cm−1 are due to the deformation of Si–O bond.33 Fig. 4a also exhibits absorption bands in the 2855 cm−1 and 2927 cm−1 which are assigned to the stretching of C–H bonds and the broad peak at 3423 cm−1 is due to the O–H and N–H vibrations. The band around 1620 cm−1 is due to the bending vibration of water molecules adsorbed on the surface (Fig. 4).
The FT-IR spectrum of Fe3O4@SiO2-APTES(Fe(acac)2) catalyst shows peaks which are clearly different from those of Fe3O4@SiO2-APTES. The FT-IR spectrum of Fe3O4@SiO2-APTES(Fe(acac)2) catalyst (Fig. 4b) shows several new sharp bands in the range of 1300–1600 cm−1 which don't exist in the spectrum of Fe3O4@SiO2-APTES.34
The peaks at 1523 cm−1 and 1573 cm−1 correspond to the double bond of CC and carbonyl group, respectively. The peak at 932 cm−1 and relatively small peak at 1630 cm−1 are also corresponding to stretching vibrations of C–O and C
N bonds, respectively. By going from Fe3O4@SiO2-APTES to Fe3O4@SiO2-APTES(Fe(acac)2) catalyst, the intensity of stretching vibration of C–H bonds at 2863 cm−1, 2932 cm−1 and also the bending vibration of H–C–H bond at 1384 cm−1 increases.34,35 Thus, it can be confirmed that surface modification of the Fe3O4@SiO2-APTES by anchoring of Fe(acac)2 was successful.
Thermogravimetric analysis (TGA) of Fe3O4@SiO2-APTES and Fe3O4@SiO2-APTES(Fe(acac)2) catalyst is seen in Fig. S2.† The first weight loss curve below 200 °C in thermogravimetric analysis (TGA) of Fe3O4@SiO2-APTES and Fe3O4@SiO2-APTES(Fe(acac)2) catalyst is attributed to residual physisorbed water and/or organic solvents, which was applied during their preparation. TGA diagrams of Fe3O4@SiO2-APTES and Fe3O4@SiO2-APTES(Fe(acac)2) show that the largest weight loss occurs between 200 °C and 600 °C. This is due to the decomposition of the grafted organic molecule on the surface which is consistent with covalently bonded organic groups to the surface of MNPs.
The largest weight loss is corresponding to 2.6% and 5.5% of the initial sample weight for Fe3O4@SiO2-APTES and Fe3O4@SiO2-APTES(Fe(acac)2), respectively. The small amount of 5.5% weight loss in the range of 200–600 °C indicates that the Fe3O4@SiO2-APTES(Fe(acac)2) catalyst have a good thermal stability up to 200 °C.
The difference between the largest weight loss for Fe3O4@SiO2-APTES and Fe3O4@SiO2-APTES(Fe(acac)2) could be attributed to the amount of iron acetylacetonate grafted on the surface. A loading 0.114 mmol g−1 for Fe grafted on the Fe3O4@SiO2-APTES obtains from this difference. The Fe content was also measured by elemental analysis (CHN analysis) which indicated a loading of 0.1 mmol g−1. In order to obtain an insight into the accurate amount of Fe grafted on the Fe3O4@SiO2-APTES, inductively coupled plasma atomic emission analysis (ICP-AES) was applied on the Fe(acac)2 solution before and after grafting on the Fe3O4@SiO2-APTES. The Fe content grafted on the Fe3O4@SiO2-APTES was measured about 0.11 mmol g−1. The loading of APTES on the Fe3O4@SiO2 was measured by TGA (Fig. S2a†) and CHN analysis about 0.44 and 0.38 mmol g−1, respectively.
The amount of catalyst was also considered. It was found that the amount of catalyst could remarkably promote conversion of sulfide to sulfoxide. As shown in Table 2, no significant amount of sulfoxide was produced in absence of Fe3O4@SiO2-APTES(Fe(acac)2) catalyst (entry 1). The conversion of sulfide was 72% when the catalyst amount was 0.5 mol% (45 mg). With the increase of the catalyst amount from 0.5 mol% to 2 mol% (180 mg), conversion value was increased from 72% to 97%. When more amounts of catalyst (3 mol% and 4 mol%) were used, the conversion of sulfide and selectivity for sulfoxide did not change remarkably. These results show that 2 mol% of the catalyst was sufficient for oxidation of sulfides to corresponding sulfoxides.
Entry | Catalyst (mol%) | Time (h) | T (°C) | Con.b (%) | Yieldb (%) | Sel.b (%) |
---|---|---|---|---|---|---|
a Reaction conditions: methyl phenyl sulfide (1 mmol), 30% H2O2 (1.5 equiv.), indicated amount of catalyst, ethanol (3 mL) as solvent at reaction temperature; the amount of Fe grafted on the surface was determined by ICP-AES analysis (loading = 0.11 mmol g−1).b Determined by GC with area normalization. | ||||||
1 | — | 24 | 25 | 14 | 13.6 | 97 |
2 | 0.5 | 9 | 25 | 72 | 69 | 96 |
3 | 1 | 6 | 25 | 88 | 85 | 97 |
4 | 2 | 2 | 25 | 97 | 94 | 96 |
5 | 3 | 2 | 25 | 97.7 | 91.8 | 94 |
6 | 4 | 2 | 25 | 97 | 92 | 95 |
7 | 2 | 2 | 40 | 99 | 73 | 74 |
8 | 2 | 2 | 60 | >99 | 47.5 | 48 |
In the next step, we examined the effect of temperature on the oxidation reaction. At room temperature, the obtained conversion and selectivity toward sulfoxide were 97% and 96%, respectively. However, a quantitative conversion was generally observed with the increase of temperature to 40 and 60 °C but over-oxidation of the sulfoxide product to sulfone occurred which reduced the selectivity of the target product (Table 2, entries 7 and 8). Therefore, the best selectivity was obtained in room temperature.
Entry | Substrate | Product | Time (h) | Con.b (%) | Yieldb (%) | Sel.b (%) |
---|---|---|---|---|---|---|
a Reaction conditions: sulfide (1 mmol), 30% H2O2 (1.5 equiv.), Fe3O4@SiO2-APTES(Fe(acac)2) catalyst (2 mol%, 180 mg), ethanol (3 mL) as solvent at room temperature.b Determined by GC with area normalization. | ||||||
1 | ![]() |
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2.7 | 96 | 91 | 95 |
2 | ![]() |
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2.5 | 98 | 96 | 98 |
3 | ![]() |
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2.5 | 95 | 93 | 98 |
4 | ![]() |
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8 | 84 | 80 | 95 |
5 | ![]() |
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6 | 86 | 80 | 93 |
6 | ![]() |
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4 | >99 | 96 | 97 |
7 | ![]() |
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4.5 | 96 | 92 | 96 |
8 | ![]() |
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3 | 95 | 90 | 95 |
9 | ![]() |
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3 | 97 | 88 | 90 |
10 | ![]() |
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3.5 | 96 | 92 | 96 |
11 | ![]() |
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4 | 86 | 76 | 89 |
It would be interesting to know that there is not a clear mechanism for iron-catalyzed sulfoxidation at the present stage. An electrophilic Fe(IV)O (one redox equivalent above the Fe(III) state) has been proposed to be the active oxidizing species involved in oxidation by Fe complexes and O2 or H2O2. Therefore, the presence of Fe(IV)
O complex (high-valent iron oxo complex) is essential in oxidation reactions. The first stage for the formation of Fe(IV)
O complex is performed in situ by the reaction of Fe(II) complex (1) with H2O2 as oxidizing agent to form compound 2 (Scheme 2). Then, O–O bond homolysis/heterolysis of compound 2 results in the generation of compound 3, which is involved in oxygen atom transfer reaction for the oxidation of sulfides to sulfoxides.28,36,37
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Scheme 2 Proposed mechanism for the oxidation of sulfides to sulfoxide using 30% H2O2 in the presence of Fe3O4@SiO2-APTES(Fe(acac)2) catalyst. |
In order to show the efficiency of our methodology, our results in oxidation of methyl phenyl sulfide was compared to literature reports (Table 4). Table 4 clearly point out the efficiency of the proposed methodology (Table 4, last entry) in both activity and reusability of the Fe3O4@SiO2-APTES(Fe(acac)2) catalyst as compared to literature reports involving several homogeneous and heterogeneous systems under various conditions (Table 4, entries 1–7).
Entry | Catalyst | Solvent | Temp (°C) | Time (min) | Yield % | Reusabilitya [ref] |
---|---|---|---|---|---|---|
a The amounts of catalyst and oxidizing agent (H2O2) are 3 mol% and (3 equiv.), respectively. | ||||||
1 | Polymer anchored Cu(II) complex | CH3CN | 25 | 180 | 83 | 5 (ref. 38) |
2 | Ionic liquid-based polyoxometalate salts | MeOH | 25 | 30 | 94.7 | 5 (ref. 39) |
3 | Silica-based tungstate interphase | CH2Cl2:MeOH | 25 | 90 | 82 | 8 (ref. 23) |
4 | Peroxotungstate supported on silica | CH2Cl2:MeOH | 8 | 150 | 91.9 | 6 (ref. 40) |
5 | Fe/SBA-15 | H2O | 25 | 120 | 99 | 10 (ref. 41) |
6 | Bis-[N-(propyl-1-sulfoacid)-pyridinium] hexafluorotitanate | [BPy][BF4] | 25 | 120 | 95 | 6 (ref. 25) |
7 | Molybdate-based Fe3O4 catalyst | CH3CN | 25 | 90 | 91 | 7 (ref. 15) |
This work | Fe3O4@SiO2-APTES(Fe(acac)2) | EtOH | 25 | 120 | 92 | 8 |
Entry 5 indicates that heterogeneous system (Fe/SBA-15) have higher catalytic activity, better reusability than Fe3O4@SiO2-APTES(Fe(acac)2) catalyst but these kinds of heterogeneous catalysts have a problem in recovery in such a way that most heterogeneous systems require a filtration or centrifugation step or a tedious workup of the final reaction mixture to recover the catalyst, although Fe3O4@SiO2-APTES(Fe(acac)2) catalyst can be easily recovered from the reaction mixture only using an external magnet.
A comparison between Fe3O4@SiO2-APTES(Fe(acac)2) catalyst (this work) and molybdate-based Fe3O4 catalyst (entry 7) which are recyclable heterogeneous catalysts by external magnet indicates that the oxidation of sulfides to sulfoxides in EtOH as a green solvent gives almost better results in yield and reusability of the catalyst. On the other hand, less amounts of Fe3O4@SiO2-APTES(Fe(acac)2) catalyst (2 mol%) and H2O2 (1.5 equiv.) as oxidizing agent are used in this work. In addition, the results in Table 4 indicate that the amount of yield and reusability of Fe3O4@SiO2-APTES(Fe(acac)2) catalyst is comparable with the other results summarized in Table 4.
Footnote |
† Electronic supplementary information (ESI) available: The EDS analysis and thermogravimetric analyses (TGA) of Fe3O4@SiO2-APTES and Fe3O4@SiO2-APTES(Fe(acac)2) catalyst. See DOI: 10.1039/c4ra07356h |
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