Photocatalytic degradation of carbofuran using semiconductor oxides
Introduction
The presence of pesticides in the effluent of pesticide formulating and manufacturing industries severely affects the eco-system. They are also used in different forms to overcome the loses from pests in the cultivation of plants. Though they contribute to a great extent in the agricultural productivity, they become major pollutants due to their extensive use. Carbofuran (2,3-dihydro-2,2-dimethylbenzofuran-7-yl methyl carbamate), an insecticide and nameticide, is included in the general group of carbamate derivative pesticides. It is an active acetylcholinesterase inhibitor and is toxic to fish and mammals. Katsumata et al. [1] reported that more than five million pounds of carbofuran were applied in the United States in the year 1995. The use of carbofuran has received intensive concern not only due to its extensive use but also due to its high oral toxicity [2], [3], [4]. Due to its long persistence in water, it is increasingly detected in soil surface and wastewater. It exhibits refractory character to bio-degradation method [5]. Hence an effective and inexpensive technique is badly needed for treating such pollutant. Recently, it has been demonstrated that semi-conducting materials mediated photocatalytic oxidation of organic compounds is a successful, convenient alternative to conventional methods for the removal of organic pollutants from water. Among the various semiconducting materials, TiO2 and ZnO are considered to be promising photocatalysts, particularly TiO2 (anatase), due to its: (i) high photocatalytic activity, (ii) resistance to photocorrosion, and (iii) biological immunity. The high photocatalytic activity of anatase form of TiO2 exhibits good application in the degradation of various organic pollutants [6], [7], [8], [9]. The illumination of these semiconducting particles with light energy produces excited high-energy state of electron and hole pairs (e−/h+) that can migrate to the surface of the particle and initiate a wide range of redox reactions, which can lead to complete mineralization of organic pollutants. The degradation of these compounds takes place via formation of partially oxidized intermediates that also undergo degradation by fragmentation. The complete mineralization of carbofuran was achieved in 16 h with TiO2 coated on glass plates [2]. Twenty percent Mineralization was observed with TiO2 coated on the blades of agitator after 6 h [10]. In the present study TiO2 was used as powder in batch reactor. The effects of experimental parameters such as concentration of carbofuran, pH of the solution, catalyst loading and light intensity on the degradation efficiency were examined and the results are discussed. The degradation efficiencies of TiO2 and ZnO were also compared to select the suitable photocatalyst for the degradation of carbofuran. The degradation of carbofuran was also investigated with low-pressure mercury vapour lamps of wavelengths 254 and 365 nm and their efficiencies were compared. Furthermore, the photoproducts of carbofuran produced during the photocatalytic degradation process have been identified, and based on the formation of intermediates possible degradation pathway of carbofuran is proposed.
Section snippets
Materials
The commercially available TiO2 (Degussa P-25 having 70% anatase and 30% rutile, surface area 50 m2 g−1 and particle size 25 nm) obtained from Degussa Chemical, Germany, was used as the photocatalyst without any further treatment. ZnO (Merck) having surface area 10 m2 g−1 and particle size 0.1–4 μm was commercially procured and used as such. The technical grade sample of carbofuran was received from Sree Ramcides Chemicals, Chennai, India.
Procedures and analytical methods
Photocatalytic degradation of carbofuran was performed in an
Results and discussion
The reaction variables such as: (i) pH of the solution, (ii) initial concentration of carbofuran, (iii) catalyst loading and (iv) light intensity on the rate of degradation were studied with light of 254 nm and the results are delineated below.
Conclusions
The photocatalytic degradation of carbofuran in aqueous medium with Degussa P-25 TiO2 and ZnO at wavelength 254 nm using low pressure mercury vapour lamps was investigated. TiO2 showed higher activity than ZnO. Complete mineralisation of carbofuran with TiO2 was observed within 5 h under optimal conditions. Comparison of rate of degradation of carbofuran at two different wavelengths, 254 and 365 nm, shows slightly higher rate of degradation for 365 nm than 254 nm, contrary to the expectation of
Acknowledgements
The authors gratefully acknowledge the University Grants Commission (UGC), New Delhi, for liberal funding through the Centre with Potential for Excellence in Environmental Sciences (CPEES) at our University and through UGC Special Assistance Programme under DRS scheme awarded to the Department of Chemistry.
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