Third Day Poster Session, 17 June 2010 - NanoTR-VI
Third Day Poster Session, 17 June 2010 - NanoTR-VI
Third Day Poster Session, 17 June 2010 - NanoTR-VI
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<strong>Poster</strong> <strong>Session</strong>, Thursday, <strong>June</strong> <strong>17</strong><br />
Theme F686 - N1123<br />
Investigatons on Solar Degradation of Acid Orange 7 (C.I. 15510) In Textile Waste Water With Micro<br />
And Nano Sized Titan Dioxide<br />
1<br />
1,2<br />
USongül Karaaslan AksuUP P* and eref GüçerP<br />
1,2<br />
1<br />
PDepartment of Chemistry, Faculty of Science & Arts, Uluda University, Bursa 16059 , Turkey<br />
PBUTAL - Bursa Test and Analysis Laboratory, The Scientific and Technological Research Council of Turkey, Bursa 16190, Turkey<br />
Abstract- Solar photo degradation of dyes is not effective in a treatment of textile waste water. Catalytic activation is necassery in order to<br />
have suitible kinetics. Titan dioxide is seem to be effective for dye degradation. Changing the size of catalyst and dopped with other metals (such<br />
as Sn IV) its activity might be improved . Our results shown that solar degradation of studied dye is posiple in a hour radiations.<br />
Textile waste water treatment nowadays is still<br />
environmental problem. Azo dyes represent the largest class<br />
of textile dyes in industrial use, accounting for 50% of all<br />
commercial dyes [1]. Due to the large number of aromatics<br />
present in these molecules and the stability of dyes, most azo<br />
dyes are non-biodegradable [2] and conventional treatment<br />
methods are ineffective for decolorization and degradation.<br />
Physical methods such as adsorption, biological methods<br />
(biodegradation) and chemical methods such as chlorination<br />
and ozonation are the most frequently used methods for<br />
removal of the textile dyes from wastewater. Others are<br />
flocculation, reverse osmosis and adsorption onto activated<br />
carbon. Since they are not destructive but only transfer the<br />
contamination from one phase to another, a different kind of<br />
pollution is faced and further treatments are required. Namely,<br />
advanced oxidation processes have been extensively<br />
investigated [3]. Among these processes, heterogeneous<br />
photocatalysis is found as an emerging destructive technology<br />
leading to total mineralization of most of organic pollutants. In<br />
most cases, the degradation is conducted for dissolved<br />
compounds in water with UV-illuminated TiOR2R. Among<br />
various semiconducting materials most attention has been<br />
given to TiOR2R because of its high photocatalytic activity,<br />
resistance to photo-corrosion, low cost, non-toxicity and<br />
favorable band-gap energy. That is why TiOR2R has real<br />
advantage in the photo-catalytic activity [4–5]. A further<br />
important advantage is the fact that the process can be<br />
powered by natural sunlight [6–8], thus reducing significantly<br />
the electrical power requirements and operating costs. It<br />
should be noted that with visible light, the photo-degradation<br />
processes proceed by different routes, involving for example<br />
electron transfer from the excited state of the dye molecules<br />
adsorbed on the TiOR2R surface into the conduction band of<br />
TiOR2R.<br />
The aim of this study is to investigate the photo catalytic<br />
activities of Acid Orange 7 (AO 7) dye which is frequently<br />
used in textile industry. The rate constant of photo catalytic<br />
reactions were determined by using simulation of solar light<br />
and titanium dioxide as a catalyst . The dye content was<br />
determined by using <strong>VI</strong>S spectrometry with the wavelength of<br />
AO7: 485 nm and with using derivative spectroscopy. In<br />
kinetic studies, the most important parameters which effect the<br />
observations were matrix of dye solutions, light intensity and<br />
the structure of catalyst. Relevant kinetic data are summarized<br />
Table 2.<br />
Table 1. Summary of rate constants for the degradation of solutions<br />
Sample k t R1/2R (min)<br />
-5<br />
5,71x 10P AO 7 0,00012 1,50E+08<br />
Textile waste water 0,00010 1,75E+08<br />
-5<br />
5,71x 10P O7 +<br />
0,02 g TiOR2R 0,0147 47<br />
Textile waste water<br />
+0,02 g TiOR2R 0,00010 1,75E+08<br />
Textile waste water<br />
+0,02 g (Ti,Sn)OR2R 0,008 87<br />
Using FTIR spectroscopic data, it was shown that dye is<br />
linked to three Titanium surface metallic cations through two<br />
oxygen atoms from the sulfonate group and the oxygen atom<br />
of the carbonyl group of the dyes (Fig 1).<br />
Figure 1. Proposed adsorption mode of AO7 on the surface<br />
Scanning electron microscopy (SEM) was employed the<br />
characterized surface morphology of the catalyst. It can be<br />
seen from Fig. 2<br />
Figure 2. SEM images of AO7- TiOR2<br />
It was shown that decomposition was completed in a hour.<br />
*Corresponding author: songulkar@yahoo.com<br />
[1] C. Rafols, D. Barcelo. Journal of Chromatography A, 777 <strong>17</strong>7-<br />
192 (1997)<br />
[2] S. Liakou, S. Pavlou, G. Lyberatos, Water Sci. Technol. 35 (4)<br />
279–286 1997) .<br />
[3] C. Guillard, H. Lachheb, A. Houas, M. Ksibi, E. Elaloui, J.M.<br />
Herrmann, J. Photochem. Photobiol. A: Chem. 158 27–36 (2003).<br />
[4] K. Nagaveni, G. Sivalingam, M.S. Hegde, G. Madras, Appl.<br />
Catal. B: Env. 48 83–93 (2004) .<br />
[5] C.E. Bonancea, G.M. Nascimento, M.L. Souza, M.L. A.<br />
Temperini, C.Paola, Appl. Catal. B: Env. 69 34–42(2006) .<br />
[6] M. Saquib, M. Muneer , Dyes Pigments;53: 237-49 (2002).<br />
[7] V. Augugliaro, C. Baiocchi, A.B. Prevot, E. Garc´a-Lopez, V.<br />
Loddo, S. Malato, et al. Chemosphere;49.1223–30 (2002).<br />
[8] M. Stylidi, DI Kondarides, XE Verykios, Appl Catal B Environ<br />
40:271-86 (2003).<br />
6th Nanoscience and Nanotechnology Conference, zmir, <strong>2010</strong> 799