Abbas Ali Jafari*ab,
Hajar Mahmoudiab and
Habib Firouzabadi*c
aChemistry Department, College of Science, Yazd University, 89195-741 Yazd, Iran. E-mail: jafari@yazd.ac.ir
bInnovation Center, Yazd Science and Technology Park, Yazd, Iran
cLate Professor Moshfegh Laboratory, Chemistry Department, Shiraz University, Shiraz 71454, Iran. E-mail: firouzabadi@chem.susc.ac.ir
First published on 7th December 2015
A novel and recoverable Cu(II)/2-aminobenzenthiol complex immobilized on magnetite/silica nanoparticles (Fe3O4/SiO2 NPs) catalyzed the synthesis of 1,2,3-triazole derivatives via three-component condensation of terminal alkynes, benzyl or alkyl halides, and sodium azide in wet polyethylene glycol (PEG 400/H2O) as a green medium at ambient temperature. The catalytic potentials of some transition metal salt complexes adhered on Fe3O4/SiO2 NPs (5–10 nm) were employed for the one pot 1,2,3-triazole synthesis. The order of catalytic activity of the various transition metal salt complexes for a model reaction was found to be Cu(II) > AgI ∼ CuI > CuCl > Ni(OAc)2 ∼ Co(OAc)2 > ZnCl2. Moreover, the order of catalytic activity of Cu(II) salts supported on Fe3O4/SiO2 NPs was found to be Cu(OAc)2 > CuSO4 ≫ CuCl2 > Cu(NO3)2. The catalytic potential of the complex has been improved significantly when core–shell magnetite/silica has been used instead of magnetite for successful wide-spread syntheses of 1-aryl-1,2,3-triazoles under mild reaction conditions. 1-Aryl-1,2,3-triazoles syntheses require harsh reaction conditions.
Recently, some attempts have started to prepare catalysts supported on magnetic nanoparticles (MNPs) which are easily separable by an external magnetic field from the reaction mixtures. This is highly beneficial for large-scale operation in pharmaceutical and food industries and minimizes the contamination of the final products with the metal catalysts. In this respect, we have recently reported new magnetic catalysts and reagents used in basic organic reactions.21–26
However, it should be declared that, the naked MNPs are extremely chemically active and are easily oxidized in the air.27 Therefore, their protection and the coating of the naked MNPs with organic or inorganic layers is a valuable strategy which also provides useful sites for further functionalization of the material.28,29
Considering the less costs with much higher purity of Cu(II) salts in comparison with the corresponding Cu(I) salts, herein we report preparation of a novel and a magnetically recoverable Cu(OAc)2/2-aminobenzenthiol complex immobilized on magnetite/silica nanoparticles (Fe3O4/SiO2NPs). This magnetic composite has been successfully used as a catalyst for the synthesis of 1,2,3-triazole derivatives via a three-component condensation of terminal alkynes, benzyl or alkyl halides, in the presence of sodium azide under mild conditions.
The preparation steps of the Cu(OAc)2/2-aminobenzenethiol complex immobilized on magnetite/silica nanoparticles (Fe3O4@SiO2/ABT–Cu(OAc)2) are shown in Scheme 1.
The progress of the reaction steps, as demonstrated in Scheme 1, are in accord with their FT-IR spectra as presented in Fig. 1.
The vibration bands at 557 and 1035 cm−1 are the typical IR absorbance induced by Fe–O vibration and stretching vibrations of the Si–O respectively (Fig. 1I). By supporting (3-chloropropyl) trimethoxysilane moiety on Fe3O4@SiO2, the intensity of O–H band at 3000–3600 cm−1 has been decreased. The vibration band of CH2 aliphatic at 2921 cm−1 shows that the (3-chloropropyl)trimethoxysilane moiety has been functionalized on the surface of the Fe3O4@SiO2 (Fig. 1II). The increased intensity of the bands at 1035, 1100, 1254, and the broadening of the peak at 1632 cm−1 is due to nucleophilic substitution of Cl with S atom of 2-aminobenzthiol. The band in 3000–3600 cm−1 region has become sharper which is due to the presence of NH2 functional group (Fig. 1III). By the copper acetate complex formation with Fe3O4@SiO2/ABT, the band intensity at 1632 cm−1 has been increased and the band in the region of 3000–3600 cm−1 has become broader (Fig. 1IV). The resulting new magnetic composite has been further characterized by XRD, XRF, TEM and VSM techniques. The amount of copper(II)acetate supported on Fe3O4/SiO2NPs was determined by atomic absorption method to be in the range of 2.8–3.0 (mmol g−1) (Fig. S1, ESI†). X-ray diffraction analysis confirms the structural order of the Fe3O4@SiO2 and Fe3O4@SiO2/ABT–Cu(OAc)2 compounds and approves the existence of copper acetate on Fe3O4@SiO2 material (Fig. S2†). X-ray fluorescence analysis of Fe3O4@SiO2/ABT–Cu(OAc)2 also (Table S1†) demonstrates the presence of Cu(OAc)2 moiety in the material attached to the magnetite surface.
The magnetization curves of the Fe3O4, Fe3O4@SiO2 and Fe3O4@SiO2/ABT-Cu(OAc)2 nanoparticles recorded at room temperature exhibit a super paramagnetic behavior (zero coercivity and remanence on the magnetization loop) (Fig. 2). The saturation magnetization value of the Fe3O4@SiO2/ABT–Cu(OAc)2 is 17 emu g−1 (Fig. 2c). This number is three times lower than that of naked Fe3O4@SiO2 (Fig. 2b, 55 emu g−1). This is due to the shielding of the Fe3O4@SiO2 surface with the coating material.
![]() | ||
| Fig. 2 Comparison of magnetization loops of (a) Fe3O4 with (b) Fe3O4@SiO2 (ref. 30) and with (c) Fe3O4@SiO2/ABT–Cu(OAc)2 composite. | ||
The thermogravimetric analysis of Fe3O4@SiO2/ABT–Cu(OAc)2 as shown in Fig. S4,† indicates the weight loss (2.27%) in the temperature range of 120–180 °C. This weight loss is mainly related to dehydration of the composite. When the temperature is raised to the range of 240–280 °C, another weight loss (3.21%) is observed, which is attributed to the decomposition of AcO. The third mass loss (22.15%) is observed when the temperature reaches to the range of 300–600 °C. This corresponds to the thermal decomposition of ABT.
Transmission electron microscopy (TEM) image of Fe3O4@SiO2/ABT–Cu(OAc)2 shows the spherical morphology of the material with an average size of 5–10 nm (Fig. 3a). The TEM image of the composite used as a catalyst for the synthesis of 1-benzyl 1,2,3-triazoles as a model reaction after the 1st run of its recycling Fig. 3b showed conservation of its morphology and the size of the particles size (5–10 nm) (Fig. 3).
![]() | ||
| Fig. 3 TEM images of Fe3O4@SiO2/ABT–Cu(OAc)2 before (a) and after the 1st run of recycling (b) for the synthesis 1-benzyl-1,2,3-triazole. | ||
When the core–shell magnetite/silica was employed as a support instead of magnetite, the amount of the supported copper and also the catalytic activity of the complex was significantly improved. A good connectivity of silane group of ABT ligand with SiO2 improves the number of sites for the complex formation with Cu(OAc)2 and as a result, improving the amounts of the copper moiety supported on the shell–core and improving the catalytic activity of the composite (Scheme 2). We have also performed the control experiment with copper salt complex with ABT is immobilized on silica particles for the model reaction. The results obtained for the catalytic activity of silica catalyst was similar with the magnetic one.
The stability of the complexes of Cu(OAc)2 with electron-donating ligands such as 3-amino propyl (AP), 2-iminomethylphenol (IMP) and 2-aminobenzenethiol (ABT) (Scheme 3), attached to the core of magnetite/silica nanoparticles were examined by measuring the amounts of leaching of Cu(II) into the reaction mixtures.
This was studied by graphite furnace atomic absorption analysis and hot filtration test. The ABT ligand (Scheme 3) showed the least amount of leaching in comparison with the other two ligands; IMP and AP in this study (Table S2†). The hot filtration test was also studied for Fe3O4@SiO2/ABT–Cu(OAc)2 catalyst in the reaction of 1,2,3-triazol synthesis. The reaction was not proceeded after separating the catalyst by a permanent magnet. It was compulsory to analyze the filtered reaction mixture by atomic absorption analysis to confirm the absence of metal.
The recycling ability of the complexes with various ligands (Scheme 3, IMP, AP, ABT) was investigated for the synthesis of 1-benzyl-1,2,3-triazole starting from benzyl bromide, phenyl acetylene and sodium azide as a model reaction (Fig. 4). The recycling of the catalysts was repeated for 5 consecutive runs for the reaction. In this regard, ABT ligand proved to be the best reusable catalyst in this respect. We have also found that the life span of the catalyst was long enough to be considered as a stable catalyst. The reaction of benzyl bromide, phenyl acetylene and sodium azide as the model reaction was proceeded efficiently in the presence of the catalyst which was prepared and stored for sixty days (Fig. 5).
![]() | ||
| Fig. 4 The recycling of the catalysts (a) Fe3O4@SiO2/ABT–Cu(OAc)2, (b) Fe3O4@SiO2/IMP–Cu(OAc)2 and (c) Fe3O4@SiO2/AP–Cu(OAc)2 for the synthesis of 1-benzyl-1,2,3-triazole as a model reaction. | ||
The catalytic activity of various metal salts such as Cu(NO3)2, Cu(SO4)2, CuCl2, AgI, CuI, CuCl, Ni(OAc)2, Co(OAc)2, ZnCl2 complexed with Fe3O4@SiO2/ABT for the synthesis of 1-benzyl-1,2,3-triazole as a model reaction at ambient temperature in different media was also investigated (Table 1) (Fig. S3†). The best result was obtained when Fe3O4@SiO2/ABT–Cu(OAc)2 was used in PEG/water (9
:
1) as the solvent (Table 1, Entry 18).
| Entry | Ma | Solventb | Time (h) | Yield (%) |
|---|---|---|---|---|
| a Catalyst (2 mol%).b Solvent (1 mL).c Under N2 atmosphere.d By-product observed.e Catalyst (1 mol%).f Catalyst (4 mol%).g At 50 °C.h At 100 °C. | ||||
| 1 | — | — | 8 | 20 |
| 2 | CuIc,d | — | 1.5 | 80 |
| 3 | CuClc,d | — | 2 | 85 |
| 4 | AgIc,d | — | 1.15 | 80 |
| 5 | Ni(OAc)2 | — | 8 | 50 |
| 6 | Co(OAc)2 | — | 8 | 50 |
| 7 | ZnCl2 | — | 8 | 50 |
| 8 | Cu(NO3)2 | — | 3 | 91 |
| 9 | CuSO4 | — | 1.5 | 92 |
| 10 | CuCl2 | — | 2 | 93 |
| 11 | Cu(OAc)2 | — | 1 | 92 |
| 12 | Cu(OAc)2 | H2O | 8 | 30 |
| 13 | Cu(OAc)2 | EtOH | 8 | 10 |
| 14 | Cu(OAc)2 | PEG | 8 | 30 |
| 15 | Cu(OAc)2 | PEG/H2O(1 : 1) |
5 | 96 |
| 16 | Cu(OAc)2 | PEG/H2O(2 : 1) |
3 | 94 |
| 17 | Cu(OAc)2 | PEG/H2O(4 : 1) |
1 | 95 |
| 18 | Cu(OAc)2 | PEG/H2O(9 : 1) |
0.25 | 95 |
| 19 | Cu(OAc)2e | PEG/H2O(9 : 1) |
0.5 | 97 |
| 20 | Cu(OAc)2f | PEG/H2O(9 : 1) |
0.2 | 92 |
| 21 | Cu(OAc)2g | PEG/H2O(9 : 1) |
0.08 | 93 |
| 22 | Cu(OAc)2h | PEG/H2O(9 : 1) |
0.05 | 92 |
| 23 | Cu(OAc)2 | EtOAc | 8 | 10 |
| 24 | Cu(OAc)2 | CH3CN | 8 | 10 |
| 25 | Cu(OAc)2 | n-Hexane | 8 | 5 |
Then, the obtained optimized conditions were applied for the reaction of different alkynes with various benzyl halides and sodium azide as summarized in Table 2.
We have also extended the scope of the use of the catalyst to the reaction of varieties of diazonium salts with various terminal acetylenes and sodium azide under optimized conditions (Table S3†). As shown in Table 3, diazonium salts bearing either electron-withdrawing or electron-donating substituents on the benzene ring afforded the corresponding 1-aryl-1,2,3-triazole products in excellent yields (Table 3, Entries 1, 2, 6 and 7).
The catalytic activity of Fe3O4@SiO2–ABT/Cu(OAc)2 in comparison with some other reported catalysts for the synthesis of 1-benzyl-1,2,3-triazole is presented. In the presence of this catalyst, the reaction proceeded at ambient temperature within 0.25 h in 95% yield of the desired product (Table 4, Entry 9). Comparison of the results in Table 4, shows an obvious advancement of using Fe3O4@SiO2–ABT/Cu(OAc)2 catalyst with respect to its easy separation by an external magnetic field without using filtration, centrifugation or sedimentation techniques, which are all energy and time-consuming processes. The catalyst recycling with good recycling cycles along with a negligible amount of leaching of the metal with a long life span of the catalyst, are the advancements observed by using this catalyst for the reaction. The media in which the catalyst is highly active is wet PEG that is an eco-friendly media. In addition, in the presence of this catalyst the target molecules are produced with excellent yields.
| Entry | Catalyst | Solvent | Temp. (°C) | Time (h) | Yield (%) |
|---|---|---|---|---|---|
| a Under N2 atmosphere. | |||||
| 1 | Cu/charcoal5 | H2O | 100 | 0.6 | 91 |
| 2 | CuO31 | THF/H2O (0.4 M) | 60 | 24 | 95 |
| 3 | Tris(triazolyl)methanol–Cu(I)a 32 | MeOH : H2O (1 : 1) |
40 | 4 | 99 |
| 4 | Cu3N/Fe3N@SiO2 (ref. 33) | Et3N/CH3CN | 25 | 3 | 84 |
| 5 | Cu-apatite34 | H2O | 100 | 1.5 | 99 |
| 6 | Cu NPs/carbon35 | THF/NEt3 | 65 | 0.16 | 98 |
| 7 | Amberlyst A-21-CuIa 36 | CH2Cl2 | 25 | 18 | 97 |
| 8 | SiO2–NHC–Cu(I)a 37 | — | 25 | 0.5 | 93 |
| 9 | Fe3O4@SiO2–ABT/Cu(OAc)2 | PEG/H2O(9 : 1) |
25 | 0.25 | 95 |
:
9, 1 mL) mixture at room temperature. The progress of the reaction was monitored by TLC (hexane/ethylacetate eluent 4
:
1). After completion of the reaction, the desired 1-benzyl-1,2,3-triazole product was separated by extraction with diethyl ether from the reaction mixture. The product was obtained after concentration of the diethyl ether as highly pure crystalline compounds in good to excellent yields (Table 2).
:
2). After completion of the reaction, ethanol (2 mL) was added to the reaction mixture. The catalyst was separated by a permanent magnet from the reaction mixture. The desired 1-aryl-1,2,3-triazole product were obtained after concentration of the reaction mixture under diminished pressure as highly pure powder compounds in good to excellent yields (Table 3).The results of this study show advances for the use of Fe3O4@SiO2–ABT/Cu(OAc)2 with respect to the other catalysts used for the similar reactions discussed in this article. The catalyst can be easily separated from the reaction mixture by an external magnetic field. This property saves time and energy with respect to filtration or decantation techniques. The reactions proceeded at room temperature in wet PEG400 as an entirely green and safe media in a short reaction time. All the reactions proceeded well with excellent isolated yields.
Footnote |
| † Electronic supplementary information (ESI) available. See DOI: 10.1039/c5ra22909j |
| This journal is © The Royal Society of Chemistry 2015 |