† Corresponding author. E-mail:
Project supported by the National Basic Research Program of China (Grant No. 2015CB921502), the National Natural Science Foundation of China (Grant Nos. 11474184 and 11174183), the 111 Project (Grant No. B13029), and the Fundamental Research Funds of Shandong University, China.
A facile step-by-step approach is developed for synthesizing the high-efficiency and magnetic recyclable Fe3O4@SiO2@Ag@Ni trepang-like nanocomposites. This method involves coating Fe2O3 nanorods with a uniform silica layer, reduction in 10% H2/Ar atmosphere to transform the Fe2O3 into magnetic Fe3O4, and finally depositing Ag@Ni core-shell nanoparticles on the L-lysine modified surface of Fe3O4@SiO2 nanorods. The fabricated nanocomposites are further characterized by x-ray diffraction, transmission electron microscopy, scanning electron microscope, Fourier transform infrared spectroscopy, and inductively coupled plasma mass spectroscopy. The Fe3O4@SiO2@Ag@Ni trepang-like nanocomposites exhibit remarkably higher catalytic efficiency than monometallic Fe3O4@SiO2@Ag nanocomposites toward the degradation of Rhodamine B (RhB) at room temperature, and maintain superior catalytic activity even after six cycles. In addition, these samples could be easily separated from the catalytic system by an external magnet and reused, which shows great potential applications in treating waste water.
Noble metal (e.g., Pt, Au, Pd, Ag) nanostructures have received considerable attention due to their unique physical and chemical properties, as well as their excellent performance in optical devices,[1] catalysts,[2] fuel cell,[3] and sensors.[4] Especially in the field of water treatment, degradation of organic dye by using noble metal based catalysts has become one of the topics of great interest due to their high activities and efficiencies.[5–8] However, high cost and scarce resources restrict the further applications of the noble metals in practical industry. To solve these problems, recent researches have focused on partially replacing noble metals by other non-noble materials, such as transition metals (Fe, Co, Ni, Cu). Zhang et al. synthesized Ag/Cu@Fe3O4 bimetallic nanoparticles by the co-reduction method, and the as-prepared samples showed superior catalytic activity for the reduction of 4-nitrophenol.[9] Dhanda and Kidwai reported the syntheses and characterizations of the reduced graphene oxide supported AgxNi100−x alloy nanoparticles which exhibit highly catalystic efficiency for p-nitrophenol reduction.[10] Zhang et al. designed uniform Ni/SiO2@Au hollow microspheres and these bimetallic nanocomposites displayed a better catalytic performance than monometallic SiO2@Au microspheres in 4-nitrophenol reduction experiment.[11] It was reported that core–shell nanoparticles are often found to be catalytically more active than their monometallic counterparts and alloy due to the electronic and lattice effects between the adjacent metals.[12,13] Unfortunately, little attention has been paid to synthesizing the bimetallic core-shell nanocomposites which are constructed with noble and non-noble metals, and to investigating their catalytic activities for the degradation of organic dye either.[14]
Metal nanoparticles often suffer aggregation and leaching without protection or surface passivation, owing to their high surface energies. This will lead to fast reducing the catalytic activity and stability. A solving method is normally to immobilize and graft the metal nanoparticles onto inorganic supports, such as polystyrene silica,[15] carbon,[16] and magnetic microspheres.[17,18] Among these catalyst supports, magnetic iron oxide nanoparticles coated with a silica layer are often employed because of their relatively high saturation magnetization, and could be easily recovered by using an external magnetic field.[19–21] The SiO2 shell can not only protect the magnetic core from being corroded but also supply a suitable supporting matrix to incorporate other functional materials. On the other hand, it was believed that the shape of the nanoparticles could greatly affect the catalytic activity for a heterogeneous catalyst system, in which particles with high aspect ratio show higher diffusion and catalytic rate than particles with low aspect ratio.[22–26] Thus, it is also important to select magnetic supports with suitable morphology.
In this work, we develop a simple method of preparing the Fe3O4@SiO2@Ag@Ni trepang-like hybrid nanostructure. As depicted in Fig.
L-lysine, ferric chloride (FeCl3·6H2O), nickel nitrate (Ni(NO3)2·6H2O), silver nitrate (AgNO3), ammonium dihydrogen phosphate (NH4H2PO4), ammonia hydroxide (25 wt%), tetraethyl orthosilicate (TEOS), sodium borohydride (NaBH4 98%), and Rhodamine B were purchased from Aladdin, and ammonia borane (NH3BH3 90%) was purchased from Aldrich. All of them were directly used without further purification.
Monodispersed Fe2O3 nanorods were fabricated through a modified hydrothermal method previously reported.[27] Typically, 0.8 mmol of FeCl3·6H2O and 0.3 × 10−5 mmol of NH4H2PO4 were dissolved in 40-mL deionized water and stirred for 15 min. After that, the solution was transferred into a 50-mL Teflon-lined stainless-steel autoclave and aged at 220 °C for 40 h. When the autoclave cooled to room temperature, the precipitates were centrifuged and washed with deionized water three times. For coating Fe2O3 nanorods with a silica layer, particles were dispersed into a solution containing water (20 mL), absolute ethanol (160 mL), and TEOS (60 μL). The mixture was sonicated for 15 min, then 3-mL ammonia hydroxide solution was added into the mixture drop by drop. After stirring at room temperature for 6 h, the products were washed with ethanol and dried at 50 °C for 12 h.
To convert the obtained Fe2O3@SiO2 nanorods into magnetic Fe3O4@SiO2 nanorods, the sample was calcined at 450 °C in 10% H2/Ar atmosphere for 6 h.
50-mg Fe3O4@SiO2 nanorods and 300-mg L-lysine were added into 50-mL deionized water and sonicated for 60 min. The products were washed with deionized water three times and transferred into a three-neck round-bottom flask containing 30-mL deionized water, then 1-mL Ni(NO3)2 solution (0.02 M) and 1-mL AgNO3 solution (0.02 M) were added. After stirring for 60 min, 4-mL ammonia borane solution (0.5 M) was dropped into the mixture slowly and sonicated for another 30 min under N2 atmosphere. The products were collected by a magnet, purified with deionized water and dried at 50 °C for 6 h. Fe3O4@SiO2@Ag nanocomposites were also fabricated in a similar way by adding 0.04-mmol AgNO3 precursors and without the addition of Ni(NO3)2.
The catalytic activity of the fabricated sample was tested by using the degradation of Rhodamine B as a model reaction. Typically, 1-mL NaBH4 aqueous solution (0.1 M) was added into a 50-mL beaker containing 20 mL of RhB aqueous solution (5 × 10−5 M). Then, 1-mL aqueous dispersion of the Fe3O4@SiO2@Ag nanocomposites (5 mg·mL−1) was dropped into the above solution. A 2-mL mixture was taken out every 3 min and the UV-Vis absorption peak at 553 nm was recorded at room temperature. A similar procedure was used for testing the catalytic activities of Fe3O4@SiO2@Ag nanocomposites and Fe3O4@SiO2 nanorods.
The crystalline structure was investigated by x-ray power diffraction (Bruker D8 ADVANCE). The transmission electron microscopy (TEM), high-resolution transmission electron microscopy (HRTEM) were conducted on a JEM 1200EX microscope operated at 200 kV. The SEM photographs and element analysis were conducted on an S-4800 scanning electron microscope. The Fourier transform infrared spectra (FT-IR) of the samples were measured with a NEXUS 670 FT-IR spectrometer. The ultraviolet-visible (UV-vis) spectrum measurements were recorded on an F-4500 ultraviolet-visible spectrophotometer. The magnetic properties of the products were measured by an alternative gradient magnetometer (2900-04C). The inductively coupled plasma mass spectrum (ICP-MS) was measured by using an Agilent 7500ce system.
The phase and crystalline composition of the as-prepared samples are examined by XRD measurements. Figure
Figure
In order to facilitate the attachments of Ag+, Ni2+ ions, the surfaces of the Fe3O4@SiO2 nanorods are modified with L-lysine. Figure
In the synthesis of Fe3O4@SiO2@Ag@Ni trepang-like nanocomposites, NH3BH3 was used as the reducing agent. It is known that Ni2+ cannot be directly reduced by NH3BH3 because of the low reduction potential (E0 (Ni2+ +/Ni) = −0.25 eV versus SHE). So the Ag+ is reduced first by NH3BH3 due to its high reduction potential (E0 (Ag+/Ag) = +0.80 eV versus SHE) and Ag nanoparticles are formed on the surfaces of Fe3O4@SiO2 nanorods, serving as seeds to induce the subsequent growths of Ni nanoparticles due to the excellent reducing activity of Ag–H species.[29] Finally the Fe3O4@SiO2@Ag@Ni trepang-like nanocomposites are obtained.
The SEM images of the Fe3O4@SiO2@Ag@Ni trepang-like nanocomposites obtained at different magnifications are displayed in Fig.
The morphologies and structures of the Fe3O4@ SiO2@Ag@Ni trepang-like nanocomposites are further investigated by TEM and HRTEM. TEM images in Fig.
The hysteresis loops of the Fe3O4@SiO2 nanorods and Fe3O4@SiO2@Ag@Ni trepang-like nanocomposites are measured by an AGM instrument at the room temperature. As shown in Fig.
Degradation of RhB in the presence of NaBH4 is chosen as a model reaction to evaluate the catalytic activities of the products. Figure
The recyclability of the Fe3O4@SiO2@Ag@Ni trepang-like nanocomposites is shown in Fig.
In this work, a simple step-by-step method of synthesizing the Fe3O4@SiO2@Ag@Ni trepang-like nanocomposites is developed. The as-prepared Fe3O4@SiO2@Ag@Ni trepang-like nanocomposites exhibit an enhanced catalytic property for the degradation of RhB compared with monometallic Fe3O4@SiO2@Ag nanorods. This catalyst could be easily collected from the catalytic system and retains high-efficiency even after six cycles of operation, which shows a great application potential for dealing with environmental issues.
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