Abstract

Attempts to mineralize a variety of s-triazine herbicides and dyes containing the triazine ring by the photocatalytic TiO 2 method or by the Fenton process have typically terminated at cyanuric acid as the end product or at precursors such as ammelide, rather than at CO 2 for the carbons and NH 4 + and/or NO 3 − ions for the nitrogens, when such triazines are subjected to OH radical (free or otherwise) oxidation. A recent study on the fate of triazoles (e.g. amitrole) in UV-illuminated titania dispersions [N. Watanabe, S. Horikoshi, A. Kawasaki, H. Hidaka, N. Serpone, Environ. Sci. Technol. 39 (2005) 2320] produced ring-expanded triazine intermediates that ultimately also terminated at cyanuric acid despite efforts to totally mineralize the triazole substrates. Another study [Y.-C. Oh, W.S. Jenks, J. Photochem. Photobiol. A: Chem. 162 (2004) 323] reported that the cyanuric acid ring is degraded by free OH radicals produced from the Fenton reagent and from UV-illuminated TiO 2 aqueous dispersions at various pHs (2–12) whose particle surface was fully fluorinated [C. Minero, G. Mariella, V. Maurino, E. Pelizzetti, Langmuir 16 (2000) 2632]. Our own studies have been unable to degrade cyanuric acid in Fenton solutions, in UV-irradiated naked TiO 2 and fluorinated TiO 2 dispersions, except in a hydrothermal/supercritical aqueous medium [S. Horikoshi, Y. Wada, N. Watanbe, H. Hidaka, N. Serpone, New J. Chem. 27 (2003) 1216] and as reported earlier by others on titania modified by metal complexes. Using various analytical methods (e.g. ESI-MS spectrometry, HPLC-ion chromatography, and UV/visible spectroscopy), we failed to detect any intermediates and mineralized end products that might have resulted from the degradation of this recalcitrant species. We also report ESR and electrochemical results for the characterization of naked TiO 2 and fluorinated TiO 2 specimens. Clearly, cyanuric acid remains a recalcitrant species where OH radicals are the oxidizing agents. The number of OH radicals produced from UV-irradiated TiO 2 (naked) and fluorinated TiO 2 depend on the incident light irradiance; at low light irradiance a greater number of OH radicals are formed on naked TiO 2, whereas at high light irradiance a greater number of OH radicals seems to form in fluorinated TiO 2 (F/TiO 2) than on naked TiO 2 dispersions owing to a rapid degradation of the DMPO spin trap by surface-bound OH radicals taking place on the naked particle surface.

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