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TiO2 crystals are widely used in photocatalytic processes due to their low cost and fabulous catalytic performance. As described in our previous study, three types of TiO2 with the main surfaces of {101}, {001} and {100} were synthesized. In this study, the three types of TiO2 are used to investigate roxithromycin (ROX) photocatalytic degradation kinetics and the pH effect. For photocatalytic degradation, the obtained data have shown that the overall order of optimal degradation is shown as {101} > {001} > {100}. The photooxidation kinetics for {101} facet conforms to first-order kinetics at from pH 5 to pH 10, and most of the photooxidation kinetics for {001} and {100} facets are fitted well with the zero-order and second-order kinetics, respectively. The pH effects are varied to the three types of TiO2, of which {101} has the best degradation effect at pH values 4, 7 and 8, while {001} works best at pH 5 or pH 6, and {100} has a relatively obvious effect at pH 4 and pH 9. The relation between adsorption and oxidation has been tested and proved that the strong adsorption corresponds to the fast oxidation.

MnO2 is one of the most widespread and cheapest materials in nature that can both adsorb arsenic and oxidize arsenite [As(III)] to arsenate [As(V)]. In this study, column β-MnO2 [CM] with the main facet of {110} and pincer β-MnO2 [PM] with the facets of {110} and {101} are synthesized and used to remove arsenic in water under different conditions. For the adsorption process, the experimental data are fitted well with the pseudo second-order kinetic model; the Langmuir model is better than the Freundlich model to describe the adsorption equilibrium isotherms. Furthermore, the As(III) oxidation rate can be denoted by the pseudo zero-order kinetic model and is related to the O2 concentration, the pH value, the light source and the initial concentration of As(III). Finally, the oxidation mechanism is investigated, and the oxidant should be related to O2. It is interesting to find that these two kinds of β-MnO2 exhibit different pH effects for both adsorption and oxidation. For As(III), the adsorption and oxidation abilities of CM follow the order pH 9 > pH 7 > pH 4, whereas the adsorption and oxidation orders of PM are pH 4 > pH 7 > pH 9.

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