Effect of rutile phase on the photocatalytic properties of nanocrystalline titania during the degradation of p-coumaric acid

Abstract Nanocrystalline titania catalysts with high surface area (68–100 m 2 /g) with varying amounts of anatase and rutile phases were tested during the photocatalyzed degradation of p -coumaric acid. This is a pollutant found in agricultural waste waters originating from the wine and olive oil industry. The catalysts were prepared by the same route namely, the hydrolysis of alkoxides followed by densification under hydrothermal conditions (1500–4000 kPa). Hydrolysis of Ti-butoxide gives rise to predominantly anatase containing titania whereas the Ti-ethoxide hydrolysis leads to mixtures of anatase and rutile. Compared to pure anatase or rutile, titania containing both phases shows a significantly higher catalytic activity during the degradation of p -coumaric acid. After preliminary optimization experiments, the degradation of 0.1 mM p -coumaric acid was achieved in 45 min under light irradiation in the presence of H 2 O 2 . The most efficient catalyst is TiO 2 containing 30% rutile and 70% anatase and is prepared by the hydrolysis of tetraisopropyl–orthotitanate. Pore size distribution measurements indicate the presence of mesopores of radii in the range 6–25 A which were responsible for the effective adsorption of the pollutant on the catalyst. Electrophoretic mobility measurements show the isoelectric point for the most efficient catalyst at pH 5.5.

[1]  S. Martin,et al.  Environmental Applications of Semiconductor Photocatalysis , 1995 .

[2]  J. S. Lees,et al.  A structural investigation of titanium dioxide photocatalysts , 1991 .

[3]  Mohammad Khaja Nazeeruddin,et al.  Conversion of light to electricity by cis-X2bis(2,2'-bipyridyl-4,4'-dicarboxylate)ruthenium(II) charge-transfer sensitizers (X = Cl-, Br-, I-, CN-, and SCN-) on nanocrystalline titanium dioxide electrodes , 1993 .

[4]  A. Finiels,et al.  Photocatalytic degradation of hydroxylated biphenyl compounds , 1996 .

[5]  Andrew G. Livingston,et al.  Catalytic wet oxidation of p-coumaric acid: Partial oxidation intermediates, reaction pathways and catalyst leaching , 1996 .

[6]  Y. Z. He,et al.  Study of the room temperature ageing effect on structural evolution of gel-derived nanocrystalline titania powders , 1996 .

[7]  Y. Torii,et al.  TiO2 coating photocatalysts with nanostructure and preferred orientation showing excellent activity for decomposition of aqueous acetic acid , 1996 .

[8]  R. W. Matthews Environment: Photochemical and Photocatalytic Processes. Degradation of Organic Compounds , 1991 .

[9]  I. Willner,et al.  Enhanced photocatalytic degradation of π-donor organic compounds by N,N′-dialkyl-4,4′-bipyridinium-modified TiO2 particles , 1996 .

[10]  C. Minero,et al.  Photocatalytic activity and selectivity of titania colloids and particles prepared by the sol-gel technique: photooxidation of phenol and atrazine , 1993 .

[11]  E. Barrett,et al.  (CONTRIBUTION FROM THE MULTIPLE FELLOWSHIP OF BAUGH AND SONS COMPANY, MELLOX INSTITUTE) The Determination of Pore Volume and Area Distributions in Porous Substances. I. Computations from Nitrogen Isotherms , 1951 .

[12]  A. Heller,et al.  PHOTOCATALYTIC OXIDATION OF BENZENE AND STEARIC ACID ON SOL-GEL DERIVED TIO2 THIN FILMS ATTACHED TO GLASS , 1996 .

[13]  M. Grätzel,et al.  Rutile Formation in Hydrothermally Crystallized Nanosized Titania , 1996 .