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Photonic crystals in biology - NanoTR-VI

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PPP MP MPoster Session, Thursday, June 17Theme F686 - N1123Investigatons on Solar Degradation of Acid Orange 7 (C.I. 15510) In Textile Waste Water With MicroAnd Nano Sized Titan Dioxide11,2USongül Karaaslan AksuUP P* and eref GüçerP1,21PDepartment of Chemistry, Faculty of Science & Arts, Uluda University, Bursa 16059 , TurkeyPBUTAL - Bursa Test and Analysis Laboratory, The Scientific and Technological Research Council of Turkey, Bursa 16190, TurkeyAbstract- Solar photo degradation of dyes is not effective <strong>in</strong> a treatment of textile waste water. Catalytic activation is necassery <strong>in</strong> order tohave suitible k<strong>in</strong>etics. Titan dioxide is seem to be effective for dye degradation. Chang<strong>in</strong>g the size of catalyst and dopped with other metals (suchas Sn IV) its activity might be improved . Our results shown that solar degradation of studied dye is posiple <strong>in</strong> a hour radiations.Textile waste water treatment nowadays is stillenvironmental problem. Azo dyes represent the largest classof textile dyes <strong>in</strong> <strong>in</strong>dustrial use, account<strong>in</strong>g for 50% of allcommercial dyes [1]. Due to the large number of aromaticspresent <strong>in</strong> these molecules and the stability of dyes, most azodyes are non-biodegradable [2] and conventional treatmentmethods are <strong>in</strong>effective for decolorization and degradation.Physical methods such as adsorption, biological methods(biodegradation) and chemical methods such as chlor<strong>in</strong>ationand ozonation are the most frequently used methods forremoval of the textile dyes from wastewater. Others areflocculation, reverse osmosis and adsorption onto activatedcarbon. S<strong>in</strong>ce they are not destructive but only transfer thecontam<strong>in</strong>ation from one phase to another, a different k<strong>in</strong>d ofpollution is faced and further treatments are required. Namely,advanced oxidation processes have been extensively<strong>in</strong>vestigated [3]. Among these processes, heterogeneousphotocatalysis is found as an emerg<strong>in</strong>g destructive technologylead<strong>in</strong>g to total m<strong>in</strong>eralization of most of organic pollutants. Inmost cases, the degradation is conducted for dissolvedcompounds <strong>in</strong> water with UV-illum<strong>in</strong>ated TiOR2R. Amongvarious semiconduct<strong>in</strong>g materials most attention has beengiven to TiOR2R because of its high photocatalytic activity,resistance to photo-corrosion, low cost, non-toxicity andfavorable band-gap energy. That is why TiOR2R has realadvantage <strong>in</strong> the photo-catalytic activity [4–5]. A furtherimportant advantage is the fact that the process can bepowered by natural sunlight [6–8], thus reduc<strong>in</strong>g significantlythe electrical power requirements and operat<strong>in</strong>g costs. Itshould be noted that with visible light, the photo-degradationprocesses proceed by different routes, <strong>in</strong>volv<strong>in</strong>g for exampleelectron transfer from the excited state of the dye moleculesadsorbed on the TiOR2R surface <strong>in</strong>to the conduction band ofTiOR2R.The aim of this study is to <strong>in</strong>vestigate the photo catalyticactivities of Acid Orange 7 (AO 7) dye which is frequentlyused <strong>in</strong> textile <strong>in</strong>dustry. The rate constant of photo catalyticreactions were determ<strong>in</strong>ed by us<strong>in</strong>g simulation of solar lightand titanium dioxide as a catalyst . The dye content wasdeterm<strong>in</strong>ed by us<strong>in</strong>g <strong>VI</strong>S spectrometry with the wavelength ofAO7: 485 nm and with us<strong>in</strong>g derivative spectroscopy. Ink<strong>in</strong>etic studies, the most important parameters which effect theobservations were matrix of dye solutions, light <strong>in</strong>tensity andthe structure of catalyst. Relevant k<strong>in</strong>etic data are summarizedTable 2.Table 1. Summary of rate constants for the degradation of solutionsSample k t R1/2R (m<strong>in</strong>)-55,71x 10P AO 7 0,00012 1,50E+08Textile waste water 0,00010 1,75E+08-55,71x 10P O7 +0,02 g TiOR2R 0,0147 47Textile waste water+0,02 g TiOR2R 0,00010 1,75E+08Textile waste water+0,02 g (Ti,Sn)OR2R 0,008 87Us<strong>in</strong>g FTIR spectroscopic data, it was shown that dye isl<strong>in</strong>ked to three Titanium surface metallic cations through twooxygen atoms from the sulfonate group and the oxygen atomof the carbonyl group of the dyes (Fig 1).Figure 1. Proposed adsorption mode of AO7 on the surfaceScann<strong>in</strong>g electron microscopy (SEM) was employed thecharacterized surface morphology of the catalyst. It can beseen from Fig. 2Figure 2. SEM images of AO7- TiOR2It was shown that decomposition was completed <strong>in</strong> a hour.*Correspond<strong>in</strong>g author: songulkar@yahoo.com[1] C. Rafols, D. Barcelo. Journal of Chromatography A, 777 177-192 (1997)[2] S. Liakou, S. Pavlou, G. Lyberatos, Water Sci. Technol. 35 (4)279–286 1997) .[3] C. Guillard, H. Lachheb, A. Houas, M. Ksibi, E. Elaloui, J.M.Herrmann, J. Photochem. Photobiol. A: Chem. 158 27–36 (2003).[4] K. Nagaveni, G. Sival<strong>in</strong>gam, M.S. Hegde, G. Madras, Appl.Catal. B: Env. 48 83–93 (2004) .[5] C.E. Bonancea, G.M. Nascimento, M.L. Souza, M.L. A.Temper<strong>in</strong>i, C.Paola, Appl. Catal. B: Env. 69 34–42(2006) .[6] M. Saquib, M. Muneer , Dyes Pigments;53: 237-49 (2002).[7] V. Augugliaro, C. Baiocchi, A.B. Prevot, E. Garc´a-Lopez, V.Loddo, S. Malato, et al. Chemosphere;49.1223–30 (2002).[8] M. Stylidi, DI Kondarides, XE Verykios, Appl Catal B Environ40:271-86 (2003).6th Nanoscience and Nanotechnology Conference, zmir, 2010 799

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