UV–Visible light induced photocatalytic studies of Cu doped ZnO nanoparticles prepared by co-precipitation method
Introduction
The residual dyes from different sources like textile industries, pharmaceutical industries, bleaching industries, dyeing, paper and pulp industries etc. introduces a variety of organic pollutants into the natural resources of water. These pollutants generally contain hazardous organic compounds which can cause severe environmental problems. The discharge of dye containing effluents into the environmental water is undesirable because these colored dyes and their breakdown products are toxic in nature and even may cause cancer or mutagenic to life (Zaharia et al., 2009). These dyes remain in the environment for long time without adequate treatment. Both physical and chemical processes such as precipitation, flocculation, adsorption, ultra-filtration and reverse osmosis are applied to remove these toxic substances generated from dyes in wastewater. However, these techniques are non-destructive processes in which the toxic substances are only removed which in due course of time gets transformed to other toxic substances (Stock et al., 2000). Recently, photocatalytic technique has attracted more attention because it is able to oxidize low concentrations of organic pollutants into non toxic products (Kislov et al., 2009). Photocatalysis utilizes semiconductor photocatalysts to carry out a photo-induced oxidation process to break down organic contaminants and inactivate bacteria and viruses (Chandran et al., 2014, Rehman et al., 2009).
Till now, many kinds of semiconductors have been studied as photocatalysts including TiO2, ZnO, ZnS, WO3, CdS etc. (Parida and Parija, 2006, Sharma et al., 2012, Bhosale et al., 2014). TiO2 is the most widely used effective photocatalyst for its high efficiency, non-toxic nature, photochemical stability and low cost. However, ZnO, a kind of semiconductor that has the similar band gap as TiO2, is not thoroughly investigated. Since the contaminant molecules need to be adsorbed on the surface of photocatalyst before the reaction takes place, the surface area and crystal defects plays a significant role in the photocatalytic activity. Doping of metal oxide with transition metal ions increases the crystal defects and also affects the optical properties by shifting the optical absorption toward the visible region (Wang et al., 2013). Silver is one of the metal that influences the photocatalytic activity of ZnO particles by trapping the photoinduced charge carriers and inhibiting the charge recombination process (Zheng et al., 2007). As silver is very expensive metal so doping with copper (Cu) in ZnO is an alternative to modify absorption and emission in visible region. Cu can enter into the ZnO lattice substitutionally as deep acceptors in combination with neighboring oxygen (O) vacancy (Kanai, 1991). To the best of our knowledge, in most of the studies, pH of the dye solution has been varied by the addition of bases and acids to make it anionic or cationic without varying the pH of as synthesized semiconductor photocatalyst (Ji et al., 2009, Kong et al., 2010). In the present work, nanosized undoped and copper (Cu) doped with TG capped ZnO nanoparticles (NPs) were prepared by co-precipitation route at varying pH. These synthesized NPs were used as a catalyst to examine the photodegradation studies of crystal violet dye as a model of organic compound under UV–Visible irradiations. The effect of doping percentage, capping, pH and loading of catalyst has been investigated on photocatalytic degradation of CV dye. The efficiency of photocatalytic process was investigated in the double distilled water containing CV dye. The effect of pH and doping percentage of as prepared photocatalyst has been studied in detail. The results confirm that Cu doped and capped ZnO NPs synthesized at higher pH shows enhanced UV–Visible light induced degradation of CV dye. Also Cu doped NPs shows better catalytic efficiency than undoped counterparts which are contradictory to the others who have reported that Cu and Mn doped ZnO NPs show nearly same or lesser photocatalytic activity as compared to undoped ZnO NPs (Milenova et al., 2013, Donkova et al., 2010).
Section snippets
Experimental section
For these studies chemicals of analytical grade were purchased from Sigma Aldrich. ZnO NPs were synthesized by chemical co-precipitation method (Sharma et al., 2010). In the first step 40 mL homogeneous solutions of 0.5 M zinc acetate, 1.0% at. wt.% TG and 0.5 M sodium hydroxide were prepared in distilled water separately by stirring them for half an hour. For the synthesis of undoped and capped ZnO NPs, 1.0% TG solution was added to 40 mL solution of 0.5 M zinc acetate in aqueous medium. After half
XRD - Studies
The XRD diffraction peaks of undoped and Cu (1.0–5.0%) doped ZnO NPs synthesized at pH-8.0 is shown in Fig. 1(a). The diffraction peaks corresponding to (1 0 0), (0 0 2), (1 0 1), (1 0 2), (1 1 0), (1 0 3), (2 0 0), (1 1 2) and (2 0 1) planes reveal a highly crystalline hexagonal wurtzite structure (ICDD No. 36-1451) and there is no extra peak corresponding to Cu, oxides of Cu or Cu related secondary and impurity phases in Fig. 1(a) which confirm that Cu has been incorporated to ZnO lattice site rather than
Conclusion
In the present studies firstly TG (1.0%) capped undoped and Cu (1.0–5.0%) doped ZnO NPs were synthesized at pH-8.0 by co-precipitation route. XRD results confirm the formation of doped ZnO samples without any appearance of secondary phase. EDS studies shows the doping of Cu ions into the ZnO lattice. PLE spectra shows large absorption in visible region for Cu doped samples as compared to undoped NPs. PL emission spectra shows emission in visible region due to Cu ions by suppressing the emission
Acknowledgement
The authors thank to Dr. Sachchidanand Srivastava, Research Associate, SSCU, Indian Institute of Science, Bangalore for useful suggestions.
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