Photocatalytic degradation and mineralization of bisphenol A by TiO2 and platinized TiO2

Abstract Bisphenol A (BPA) was degraded photocatalytically by different TiO 2 photocatalysts at pHs 3 and 10. It was found that the mineralization of BPA showed a stronger dependence on the pH and different oxidation products were detected during BPA degradations at pHs 3 and 10. At pH 3, 20 ppm of BPA was completely mineralized into CO 2 after 120 min of UV illumination. However, only 20–30% of the carbon from the BPA was converted into CO 2 for the same illumination time at pH 10. This observation indicated that intermediates formed from degradation at pH 10 are very stable to further photocatalytic oxidation while those intermediates formed at pH 3 are more susceptible to degradation and mineralization. Although the oxidation intermediates obtained from BPA degradation at pH 10 were more difficult to be degraded, Microtox ® toxicity analyses revealed that for all tested photocatalysts, these intermediates were less toxic compared to the parent BPA molecule. As a result, a gradual decrease in toxicity was found for BPA degradation at pH 10. On the contrary, more toxic intermediates were generated during the early stage of BPA oxidation when the experiment was performed at pH 3. In addition, platinization was found to increase the rates of BPA degradation and mineralization. When platinum was loaded (0.2–1.0 wt.%) onto the surface of TiO 2 , the rates of degradation and mineralization were increased 3–6 times. Nevertheless, the existence of platinum deposits did not show any effects on the distribution of intermediate compounds formed from BPA degradation.

[1]  P. Kosky,et al.  The aqueous phase in the interfacial synthesis of polycarbonates. Part 1. Ionic equilibria and experimental solubilities in the BPA-sodium hydroxide-water system , 1991 .

[2]  D. Blake,et al.  Bibliography of Work on the Heterogeneous Photocatalytic Removal of Hazardous Compounds from Water , 1999 .

[3]  T. Waite,et al.  Kinetic modeling of TiO2-catalyzed photodegradation of trace levels of microcystin-LR. , 2003, Environmental science & technology.

[4]  J. D. Laat,et al.  Transformation of carbendazim induced by the H2O2/UV system in the presence of hydrogenocarbonate ions : involvement of the carbonate radical , 2002 .

[5]  J. Sajiki Decomposition of bisphenol-A (BPA) by radical oxygen. , 2001, Environment international.

[6]  D. Ollis,et al.  Photocatalyzed oxidation of alcohols and organochlorides in the presence of native TiO2 and metallized TiO2 suspensions. Part(I):Photocatalytic activity and pH influence , 1999 .

[7]  K. Bundy,et al.  Experimental and mathematical/computational assessment of the acute toxicity of chemical mixtures from the Microtox® assay , 2002 .

[8]  A. Mills,et al.  A web-based overview of semiconductor photochemistry-based current commercial applications , 2002 .

[9]  O Nakasugi,et al.  Bisphenol A in hazardous waste landfill leachates. , 2001, Chemosphere.

[10]  D. Bahnemann,et al.  Enhancement of the photocatalytic activity of various TiO2 materials by platinisation , 2002 .

[11]  A. Yasuhara,et al.  Quantities of bisphenol a leached from plastic waste samples. , 1999, Chemosphere.

[12]  D. Ollis,et al.  Photocatalyzed oxidation of alcohols and organochlorides in the presence of native TiO2 and metallized TiO2 suspensions. Part (II) : Photocatalytic mechanisms , 1999 .

[13]  A. Fernández-Alba,et al.  Toxicity assays: a way for evaluating AOPs efficiency. , 2002, Water research.

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

[15]  D. Bahnemann,et al.  HETEROGENEOUS PHOTOCATALYTIC REACTIONS COMPARING TIO2 AND PT/TIO2 , 2002 .

[16]  A. Fujishima,et al.  Degradation of bisphenol A in water by TiO2 photocatalyst. , 2001, Environmental science & technology.