- Nano Express
- Open Access
One-Step Solvothermal Method to Prepare Ag/Cu2O Composite With Enhanced Photocatalytic Properties
© Deng et al. 2016
- Received: 10 November 2015
- Accepted: 6 January 2016
- Published: 19 January 2016
Ag/Cu2O microstructures with diverse morphologies have been successfully synthesized with different initial reagents of silver nitrate (AgNO3) by a facile one-step solvothermal method. Their structural and morphological characteristics were carefully investigated by means of X-ray diffraction (XRD), scanning electron microscopy (SEM), and transmission electron microscopy (TEM), and the experimental results showed that the morphologies transformed from microcubes for pure Cu2O to microspheres with rough surfaces for Ag/Cu2O. The photocatalytic activities were evaluated by measuring the degradation of methyl orange (MO) aqueous solution under visible light irradiation. The photocatalytic efficiencies of MO firstly increased to a maximum and then decreased with the increased amount of AgNO3. The experimental results revealed that the photocatalytic activities were significantly influenced by the amount of AgNO3 during the preparation process. The possible reasons for the enhanced photocatalytic activities of the as-prepared Ag/Cu2O composites were discussed.
- Photocatalytic activity
Over the past decades, the environmental problem, especially wastewater induced by organic dye pollutants, has become a fatal issue accompanying the rapid industry growth, which restricted the sustainable development of human beings [1–3]. Therefore, a great effort has been made for seeking the highly active photocatalysts which could be applied for the environmental remediation . Recently, the hybrid structures, such as nanocomposites, which group the various materials with different properties together to offer the potential enhanced functions, have attracted much more attention [5, 6]. Metal-metal oxide semiconductor materials as one type of these hybrid structures have also been widely investigated due to their potential applications in the fields such as sensing [7, 8], antibacterial , charge-transfer process [9–11], optoelectronics [12, 13], energy storage , and catalysis [15, 16]. Additionally, it is believed that in the metal-semiconductor composites, metal deposits could act as the electron sinks which trap the photoinduced electrons transferring from the conduction band of semiconductor, while the photoinduced holes could remain on the semiconductor surface, and thus, the recombination of photoinduced electron-hole pairs could be prevented resulting in the improvement of photocatalytic efficiency [17, 18]. Among these metal-semiconductor hybrid structures, Ag/Cu2O composites have been extensively explored based on the following reasons: (1) Ag, as one kind of relatively cheap noble metal, has also been investigated at nanoscale driven by its excellent sensing properties [19, 20], catalytic activities [21, 22], optical properties , thermal properties [24, 25], and inkjet ink particles ; (2) Cu2O, as a typically low-cost and nontoxic p-type semiconductor, has a narrow direct bandgap of 2.0–2.2 eV, which could be used as photocatalysts under visible light [17, 27].
Cu2O has been first investigated as a visible light-driven photocatalyst for water splitting since 1998 . After that, many efforts have been made to improve the photocatalytic efficiency from the two aspects: (1) modulating the growth process to control the chemical stability, size, morphology, and architecture of Cu2O [29–34]; (2) hindering the recombination of photogenerated electron-hole pairs  and photocorrosion [36, 37]. For Cu2O-based photocatalysts, some actions, such as element doping [38–40] and heterojunction forming [41, 42], have been taken to enhance the photocatalytic activity compared with pure Cu2O. Moreover, forming composite was also a very important approach to promote the photocatalytic efficiency for Cu2O-based material [43, 44]. As mentioned above, Ag/Cu2O, as an important composite, has also been considered a way to enhance the photocatalytic activity of Cu2O [16–18, 27, 45]. Generally, Ag could be synthesized by various methods to form different morphologies, such as electrolysis method , biological method , reducing method , photocatalytic process , soaking method , and polyol process . Likewise, there were many approaches to fabricate controllable Cu2O structures, including hydrothermal method , solvothermal method , solution method [6, 16–18], and electrodeposition method [14, 27]. However, there are only a few reports to investigate the effect of Ag content on the photocatalytic efficiency of Ag/Cu2O nanocomposites prepared by electron beam irradiation method . So far, little information is available on the Ag content effect for photocatalytic properties of Ag/Cu2O synthesized by a facile one-step solvothermal method.
In this work, a series of Ag/Cu2O microstructures were fabricated by a facile solvothermal method by adding different amounts of silver nitrate (AgNO3). The effect of Ag content on structures and morphologies of the as-synthesized Ag/Cu2O composites were systematically investigated. Furthermore, the photocatalytic activities of Ag/Cu2O composites prepared with different amounts of AgNO3 for methyl orange (MO) dye in aqueous solution were performed. The results revealed that the photocatalytic activities of the as-prepared samples showed the maximal efficiency on degradation of MO related to the suitable amount of AgNO3. The possible reasons for enhanced photocatalytic activities of the as-prepared Ag/Cu2O composites were proposed.
All the chemical reagents, such as copper (II) nitrate trihydrate (Cu(NO3)2·3H2O), AgNO3, ethylene glycol (EG), and MO, purchased from Sinopharm Chemical Reagent Co., Ltd. (SCRC; China), were of analytical grade and used without further purification. Typically, the samples were prepared as follows, similar to the previous report [40, 49]: 4 mmol Cu(NO3)2·3H2O and certain amount of AgNO3 were dissolved into 80 mL ethylene glycol followed by vigorous stirring to form a homogeneous solution. The mixture was then transferred into 100 mL Teflon-lined stainless steel autoclave. Thereafter, the sealed autoclave was kept at 140 °C for 10 h, followed by cooling down to room temperature naturally. The as-prepared precipitants were collected by centrifugation and washing with deionized water and ethanol several times. Finally, the products were obtained by drying the precipitants at 60 °C for 12 h in a vacuum oven. The samples were named as CA-0, CA-0.2, CA-0.5, CA-1, and CA-2 for the AgNO3 amounts of 0, 0.2, 0.5, 1, and 2 mmol, respectively.
X-ray powder diffraction (XRD) patterns of the as-prepared samples were analyzed by a German X-ray diffractometer (D8-Advance, Bruker AXS, Inc., Madison, WI, USA) equipped with Cu Kα radiation (λ = 0.15406 nm). The morphologies of the as-synthesized products were observed by a field emission scanning electron microscope (FESEM; FEI Quanta FEG250, FEI, Hillsboro, USA) and transmission electron microscopy (TEM; JEOL-200CX, JEOL, Tokyo, Japan). X-ray photo-electron spectroscopy (XPS) was performed on a Thermo ESCALAB 250XI electron spectrometer equipped with Al Kα X-ray radiation (hν = 1486.6 eV) as the source for excitation. The Brunauer-Emmett-Teller (BET) specific surface areas of the products were investigated by N2 adsorption isotherm at 77 K using a specific surface area analyzer (QUADRASORB SI, Quantachrome Instruments, South San Francisco, CA, USA).
The photocatalytic activities of the as-prepared Ag/Cu2O samples were performed by a UV-vis spectrophotometer (TU-1901, Beijing Purkinje General Instrument Co., Ltd, Beijing, China) at room temperature in air under visible light irradiation, which was similar to the previous reports [40, 49]. The visible light was generated by a 500-W Xe lamp equipped with a cutoff filter to remove the UV part with wavelength below 420 nm. In brief, a suspension was formed by dispersing 30 mg of powder into 50 mL of 20 mg/L MO aqueous solution. After that, the suspension was kept in dark for 30 min with stirring to reach the adsorption-desorption equilibrium of MO on the surface of Ag/Cu2O samples. Ca. 3 mL suspension was taken out after a given irradiation time interval and centrifuged to filtrate the sample powders for the following UV-vis spectra test. The concentration of MO was characterized by measuring the absorbance properties at 464 nm in UV-vis spectra to illuminate the photocatalytic activities.
Structural and Morphological Characterization of Samples
Therefore, the formed Cu2+ species may be absorbed on the surface of Cu2O to form CuO for some samples such as CA-0.5 . Meanwhile, the formation of Ag covered on Cu2O to prevent the further reaction to some extent . Nevertheless, metallic Cu could also be observed in some samples depending on the amount of AgNO3. The reason was ascribed to be the broken equilibrium because of the additional reaction of Eq. 10 occurring . When the amount of AgNO3 (CA-0.2) was little, the reaction system was no significant difference from that of preparing sample CA-0. Therefore, almost no metallic Cu was observed in this sample (CA-0.2). Once the amount of AgNO3 was sufficiently enough (CA-2), there was also almost no existence of Cu due to the complete dissolution of Cu into Cu2+ according to Eq. 10. However, if the amount of AgNO3 was not enough (CA-0.5 and CA-1), the reaction system equilibrium would be broken compared with the absence of AgNO3 (CA-0), and Cu would be partly dissolved resulting in the residual of Cu. Thus, the Ag/Cu2O composites were obtained when AgNO3 was added during the fabrication process, which was confirmed by XRD patterns and XPS spectra.
Photocatalytic Activity of Samples
The causes for the vibration of photodegradation rates could be ascribed to as the following according to the literatures [17, 18, 27, 48, 50]: (1) surface plasmon resonance, which means that the photoexcited plasmonic energy in the Ag particles transferred into Cu2O resulting in the more generation of electron-hole pairs in the Cu2O, which is beneficial to improve the photocatalytic activity; (2) Ag particles act as electron sinks, which means the photogenerated electrons transferring from the conduction band of Cu2O to Ag particles, leading to the improvement in photocatalytic activity over an extended wavelength range and to prevent the recombination of photogenerated electron-hole pairs and enhance the interfacial charge-transfer and thus promotes the photocatalytic activity; (3) the enlarged specific surface area also improves the photocatalytic activity by increasing the contact area. However, with the increasement of the AgNO3 content, the photocatalytic effect decreases. The specific surface areas of the as-prepared samples are described in Fig. 7b. The trend of specific surface area vibration was not consistent with the photodegradation rate, especially, for CA-0.5. The reason may be ascribed to the morphology transformation due to the addition of AgNO3, which was in agreement with the SEM and TEM observations. The photodegradation activity vibration could be explained as follows: the excessive Ag causes the aggregation of Ag particles, resulting in the decrease of capturing the photogenerated electrons and the shield of the visible light absorption by Cu2O, leading to the deterioration of photo-utilizing efficiency. In addition to the aforementioned reasons, the morphology was also one of the key factors for the photocatalytic activity. In this work, the morphology transformation experienced the following procedure: regular cube to smooth sphere to rough sphere with the increase of AgNO3. The morphology would not only affect the specific surface area of the as-prepared samples as mentioned above but also influence the exposed crystal surfaces as previously reported [55, 56] which had significant impact on the photocatalytic activity. It is reported that  surfaces had much higher photocatalytic activity for Cu2O and the cubic and spherical particles were mainly covered by  or  surfaces . Combining SEM and TEM observations, the samples were reasonable to have the sequence of photocatalytic activities as shown in Fig. 7a (CA-0 (cube), CA-0.2 (spheres consisted of pyramid particles), CA-0.5 (spheres composed of pyramid particles and other irregular structures), CA-1 (cube and cube formed sphere), CA-2 (sphere composed of cubic particles)). Finally, Cu contained in some samples (CA-0.5 and CA-1) also contributed to the enhanced photocatalytic activities by promoting the rapid separation of photogenerated electrons and holes in the interfaces between Cu and Cu2O [49, 57, 58]. However, the existence of Cu was not the dominant factor responsible for the enhanced photocatalytic activities by comparing the photodegradation rate of CA-1 with CA-0. In a word, the photocatalytic activity of Cu2O on decomposition of MO dye in aqueous solution is enhanced by the formation of Ag particles with suitable amount of Ag content, which plays the dominant role, and the morphology effect.
In summary, Ag/Cu2O composites were successfully synthesized by a facile one-step solvothermal method. The structural and morphological properties were characterized by XRD, SEM, TEM, and XPS, which demonstrated that the AgNO3 amount during the fabrication process significantly affected the surface, size distribution, morphology, and specific surface area of the as-grown Ag/Cu2O composites. The photocatalytic activities of the as-prepared Ag/Cu2O composites on the photodegradation of MO dye were evaluated under visible light irradiation. The results illustrated that Ag particles played an important role in the photodegradation of MO by surface plasmon resonance and acting as electron sinks. However, excessive Ag would decrease the photocatalytic activity because of shielding the visible light absorption by Cu2O and lowering the capture of photogenerated electrons. The photodegradation of MO was also affected by the morphology of the as-prepared samples, though Ag particles were the dominant factor in this work. The as-prepared Ag/Cu2O composites have good stabilities as photocatalysts for photodegradation of MO in aqueous solution, illustrating to be promising in wastewater treatment.
This work was supported by the Encouragement Foundation for Excellent Middle-Aged and Young Scientist of Shandong Province (Grant Nos. BS2014CL012 and BS2013CL020), National Natural Science Foundation of China (Grant Nos. 21505050, 11304120, 61504048, and 61575081), a Project of Shandong Province Higher Educational Science and Technology Program (Grant No. J15LJ06), and Shandong Provincial Natural Science Foundation (ZR2013AM008).
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