Nano-Ag particles doped TiO2 for efficient photodegradation of Direct azo dyes

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Abstract

Silver nanoparticles doped TiO2 has been prepared and characterised by surface analytical methods such as BET surface area, scanning electron micrographs (SEM), X-ray diffraction (XRD), energy dispersive X-ray micro analysis (EDX), electron spin resonance (ESR) and diffuse reflectance spectroscopy (DRS). We have investigated the photocatalytic degradation of two Direct diazo dyes, Direct red 23 (DR 23) and Direct blue 53 (DB 53) in the aqueous suspensions of TiO2 and Ag deposited TiO2 nanoparticles under UV-A light irradiation in order to evaluate the various effects of silver deposition on the photocatalytic activity of TiO2. The presence of silver in TiO2 was found to enhance the photodegradation of DR 23 and DB 53. The higher activity of silver doped TiO2 is due to the enhancement of electron–hole separation by the electron trapping of silver particles.

Graphical abstract

Photocatalytic degradation of two Direct diazo dyes, Direct red 23 (DR 23) and Direct blue 53 (DB 53) in the aqueous suspensions of TiO2 and Ag deposited TiO2 nanoparticles with UV-A light have been investigated. The enhancement of photocatalytic activity of Ag doped TiO2 is found to be due to the following mechanism. Ag nanoparticles be deposited on TiO2 act as electron traps, enhancing the electron–hole separation and the subsequent transfer of the trapped electron to the adsorbed O2 acting as an electron acceptor.

Introduction

Heterogeneous photocatalysis is an alternative economical and harmless technology of advanced oxidation processes (AOP) for removal of organic impurities. During the process, illuminated semiconductor absorbs light and generates active species which leads to complete oxidation of organic components in waste water. A distinct advantage of the photocatalysis lies in its ability to utilise solar energy in the production of active species OHradical dot. Photocatalysis on semiconductors has been studied in many fields. For example: (i) fuel production: hydrogen from water photolysis [1], [2], [3], (ii) removal/recovery of heavy metal ions [4], [5], (iii) water detoxification: removal of toxic, harmful or hazardous pollutants [6], [7], [8], [9], [10], [11].

A great many photocatalysts have been examined for the degradation of organic pollutants in waste water. Among various semiconductor metal oxides, TiO2 has been the focus of photocatalysts under UV irradiation because of its physical and chemical stability, low cost, ease of availability, non-toxicity and electronic and optical properties. Despite the positive attributes of TiO2, there are a few drawbacks associated with its use; it has a high bandgap (Eg > 3.2 eV) and it is excited only by UV light (λ < 388 nm) to inject electrons into the conduction band and to leave holes into the valence band [12]. Thus, this practically limits the use of sunlight or visible light as an irradiation source in photocatalytic reactions on TiO2 [13]. In addition, the high rate of electron–hole recombination on TiO2 particles results in a low efficiency of photocatalysis [14]. For the purpose of overcoming these limitations of TiO2 as a photocatalyst, numerous studies have been recently performed to enhance electron–hole separation and to extend the absorption range of TiO2 into the visible range. These studies include doping metal ions into the TiO2 lattice [15], [16], dye photosensitisation on the TiO2 surface [17], [18], [19], [20], [21], addition of inert support [22] and deposition of noble metals [23], [24], [25], [26], [27], [28], [29], [30], [31], [32], [33], [34].

In particular, noble metal-modified semiconductor nanoparticles become of current importance for maximising the efficiency of photocatalytic reactions. The noble metals such as Pt [23], [24] and Au [25], [26] deposited or doped on TiO2 have the high Schottky barriers among the metals and thus act as electron traps, facilitating electron–hole separation and promotes the interfacial electron transfer process [5], [35], [36], [37]. Most studies of noble metal-modified TiO2 photocatalysts have focused on the details of the photoinduced electron transfer from the conduction band of UV-irradiated TiO2 to noble metals for improving the photocatalytic activity of TiO2 under UV irradiation.

Noble metals doped or deposited on TiO2 are expected to show various effects on the photocatalytic activity of TiO2 by different mechanisms. These noble metals act separately or simultaneously depending on the photoreaction conditions. They may (i) enhance the electron–hole separation by acting as electron traps, (ii) extend the light absorption into the visible range and enhance surface electron excitation by plasmon resonances excited by visible light and (iii) modify the surface properties of photocatalysts.

In the recent years, silver ions have attracted the interests of several researchers [38], [39], [40], because of both their novel effects on the improvement of photoactivity of semiconductor photocatalysis nanocrystallites [39], [40] and their effects on antibacterial activity [38]. These properties can be applied to a tremendous range of applications, for instance, environment, textiles, engineering materials and so on. However, the studies on silver doped photocatalyst nanocrystallites are still limited in the literature [41], [42], [43], [44], [45], [46], [47], [48], [49].

The aim of the present work is to prepare Ag doped TiO2 (anatase) by a photodeposition method and to compare the activity of the photocatalyst before and after surface modification with metallic silver for the degradation of two azo dyes DB 53 and DR 23.

Section snippets

Materials

Titanium dioxide (anatase) with a BET surface area of 21.53 m2/g and perchloric acid were supplied by Qualigen. Direct red 23 (DR 23), C.I. 29160 from S.D. fine and Direct blue 53 (DB 53) C.I. 23860 from CDH were used as such. The structure of these dyes are shown in Fig. 1. Silver nitrate (99.5 wt.%) analytical grade from Merck was used as a silver source for the preparation of Ag doped TiO2 photocatalysts. Double distilled water was used for all the experiments.

Preparation of Ag doped TiO2 photocatalysts

The Ag doped TiO2 catalysts were

UV–visible diffuse reflectance spectra

The reflectance spectra of TiO2 and 0.5, 1, 1.5 and 2 at.% of Ag doped TiO2 catalysts are illustrated in Fig. 3. The spectrum of TiO2 consists of a single absorption below ca. 370 nm usually ascribed to charge-transfer from the valence band (mainly formed by 2p orbitals of the oxide anions) to the conduction band (mainly formed by 3dt2g orbitals of the Ti4+ cations) [50]. The addition of silver ions and subsequent UV irradiation causes significant changes to the absorption spectrum of TiO2

Conclusion

The characterisation of silver doped TiO2 and TiO2 using diffuse reflectance spectroscopy, XRD, SEM, EDX and BET surface area techniques revealed the dispersion of silver metal on the surface of TiO2. The silver doped TiO2 catalysts shows an absorption threshold extended into the visible region. It is obvious that the Ag clusters give rise to localised energy levels in the bandgap of TiO2 into which the valence band electrons of TiO2 are excited at wavelength longer than 370 nm. The photonic

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    Present address: Department of Environmental Engineering and Science, Feng chia University, Taichung, Taivan.

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