The synergistic effect of the photocatalytic ozonation process (PH-OZ) using the photocatalyst TiO2 is usually attributed to influences of the physicochemical properties of the catalyst, pollutant type, pH, temperature, O3 concentration, and other factors. It is also often claimed that good adsorption on the TiO2 surface is beneficial for the occurrence of synergism. Herein, we tested these assumptions by using five different commercial TiO2 photocatalysts (P25, PC500, PC100, PC10 and JRC-TiO-6) in three advanced oxidation systems - photocatalysis (O2/TiO2/UV), catalytic ozonation (O3/TiO2) and PH-OZ (O3/TiO2/UV) - for the degradation of two pollutants (dichloroacetic acid - DCAA and thiacloprid) simultaneously present in water. The synergistic effect in PH-OZ was much more pronounced in the case of thiacloprid, a molecule with low adsorption on the surface of the catalyst - in contrast to DCAA with stronger adsorption. The faster kinetics of catalytic ozonation (O3/TiO2) correlated with the higher exposed surface area of TiO2 agglomerates, independent of the (lower) BET surfaces of the primary particles. Nevertheless, DCAA mineralization on the TiO2 surface was much faster than thiacloprid degradation in solution. Therefore, we propose that a high BET surface area of the photocatalyst is crucial for fast surface reactions (DCAA mineralization), while good dispersion - the high exposed surface area of the (small) agglomerates - and charge separation play an important role in photocatalytic degradation or PH-OZ of less adsorbed organic pollutants (thiacloprid).
Keywords: Adsorption; Neonicotinoids; Synergism; TiO(2) agglomerates; Water purification.
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