Effects of acidity and inorganic ions on the photocatalytic degradation of different azo dyes

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Abstract

Effects of acidity and inorganic ions that are common in industrial effluent on the photocatalytic degradation of azo dyes, Procion Red MX-5B (MX-5B) and Cationic Blue X-GRL (CBX), have been investigated in UV illuminated TiO2 dispersions. There are significant differences between adsorption and photodegradation of MX-5B and those of CBX to the change of solution pH. The results indicated that CBX photodegradation was favored at the surface of TiO2, while that of MX-5B occurred in the aqueous phase. At pH 2.4, SO42−, H2PO4, ClO4 and F in general increased the decolorization rates of MX-5B and CBX by enhancing the adsorption of the selected dyes on the surface of TiO2. At pH 10.8, most of the selected anions inhibited the photocatalytic oxidation (PCO) to decolorize and degrade CBX and MX-5B. These results demonstrated that inorganic anions affect the photodegradation of dyes by their adsorption onto the surface of TiO2 and trapping positive hole (h+) and radical dotOH. Inorganic cationic ions, such as Cu2+ and Ni2+ had strong inhibition on the PCO decolorization of MX-5B at pH 10.8. On the contrary, no significant effect was observed at the same concentration of metal cations at pH 2.4.

Introduction

Heterogeneous photocatalytic oxidation (PCO) for wastewater treatment has received much attention by various research groups. Numerous types of catalysts and contaminants have been investigated on laboratory scale [1], [2]. However, very few commercial applications of this technology are available at present. One of the major reasons is the deactivation of the photocatalyst when photocatalysis is utilized to treat real wastewater [3]. Therefore, information on the long-term activity of photocatalysts is needed for the application of photocatalysis. Heterogeneous photocatalysis is a process in which the illumination of an oxide semi-conductor, usually TiO2 in the form of anatase or rutile, produces photo-excited electrons (e) and positive charged holes (h+). The photo-excitation of the semi-conductor particles by UV light changes the energy state of the electrons from the valence band of the solid to the conduction band. The formation of active species was previously discussed in detail [4]. The effects of salty water on the PCO products of liquid 3-octanol and 3-octanone were studied [5]. A number of studies have examined the effect of various inorganic ions on TiO2 slurry photocatalysts [6], [7] and on fixed-bed photocatalysts where the TiO2 was attached to a support, e.g. the inside wall of a borosilicate glass spiral [5], [8], and the surface of porous silica gel or fiberglass mesh [9]. There seems to be a general consensus that the effect of organic ions on photocatalysis depends on geometric configuration of the reactor and the structures of the organic compounds to be degraded.

Organic dyes are one of the major groups of pollutants in wastewaters produced from textile and other industrial processes [10]. These wastewaters are highly colored. The more complex environmental problem associated with the textile industry is that organic dyes are resistant to microbial degradation and they can be converted to toxic or carcinogenic compounds [11]. Heterogeneous photocatalysis has been considered as a cost-effective alternative as pre- or post-treatment of the biological treatment process for the purification of dye-containing wastewater [11], [12]. The occurrence of dissolved inorganic ions is rather common in dye-containing industrial wastewaters. They can significantly influence the photocatalytic reactions for the treatment of dyes. A study on the effects of inorganic ions on PCO degradation of dye will therefore be very useful for understanding the mechanism of the photocatalytic decolorization of dyes in TiO2 dispersions under UV irradiation.

In this paper, we examined the effects of several types of inorganic ions (SO42−, H2PO4, ClO4, F, Cu2+ and Ni2+) that are common in synthetic dye-containing effluent on the photodegradation of two selected azo dyes in TiO2 aqueous dispersions under UV irradiation. These two azo dyes have different adsorption modes on the surface of TiO2. The photodegradation rates showed different patterns with the changes of pH. In addition, the effects of different inorganic ions on and the mechanisms of photodegradation of these two azo dyes were discussed.

Section snippets

Chemicals

TiO2 (P-25, ca. 80% anatase, 20% rutile; BET area, ca. 50 m2 g−1) was obtained from Degussa Co., Germany. The azo dye, Procion Red MX-5B (MX-5B), shown in Fig. 1A was manufactured by Imperial Chemicals Industries. Another azo dye, Cationic Blue X-GRL (CBX) shown in Fig. 1B, was provided by Shanghai Chemical Company, China. They were used without further purification. All other reagents were analytical grade. The pH of the solution was adjusted with HCl or NaOH.

Adsorption experiments

All equilibrium adsorption studies

Effects of pH

Fig. 2A and B shows the changes of adsorption and decolorization of MX-5B and CBX with pH. Clearly, the adsorption of MX-5B decreased with pH increasing. However, the photodegradation rate of MX-5B increased under UV irradiation with the decrease of adsorption of MX-5B. We have confirmed in a previous study that, in the decolorization of MX-5B, the more active bonds including the CN bonds linked to the benzene ring or the naphthalene ring were hydroxylated first [14]. The photodegradation of

Conclusions

Results in this study indicate that the adsorption and photocatalytic degradation (decolorization) of two azo dyes, namely, MX-5B and CBX, are very different. Aqueous phase reactions favored the decolorization of MX-5B, while photodegradation of CBX took place mainly on the surface of TiO2. The difference was due to the difference in physico-chemical properties of two azo dyes. In order to efficiently treat target azo dyes by PCO, the appropriate pH should be used for specific azo dye.

In

Acknowledgements

The study was supported by a research grant of Research Grant Council, Hong Kong SAR Government to P.K. Wong and J.C. Yu, and a research grant of National Science Foundation of China (Contract No. 20007004) and the National 863 Project of China (2002AA6409040) to C. Hu.

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