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Ultrasound (US), Ultraviolet light (UV) and combination (US + UV) assisted semiconductor catalysed degradation of organic pollutants in water: Oscillation in the concentration of hydrogen peroxide formed in situ

机译:超声,紫外光和紫外线结合以及US + UV辅助的半导体催化的水中有机污染物的降解:原位形成的过氧化氢浓度的振荡

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摘要

Application of Advanced Oxidation Processes (AOP) such as sono, photo and sonophoto catalysis in the purification of polluted water under ambient conditions involve the formation and participation of Reactive Oxygen Species (ROS) like ?OH, HO_2~?, O_2~(-?), H_2O_2 etc. Among these, H_2O_2 is the most stable and is also a precursor for the reactive free radicals. Current investigations on the ZnO mediated sono, photo and sonophoto catalytic degradation of phenol pollutant in water reveal that H_2O_2 formed in situ cannot be quantitatively correlated with the degradation of the pollutant. The concentration of H_2O_2 formed does not increase corresponding to phenol degradation and reaches a plateau or varies in a wave-like fashion (oscillation) with well defined crests and troughs, indicating concurrent formation and decomposition. The concentration at which decomposition overtakes formation or formation overtakes decomposition is sensitive to the reaction conditions. Direct photolysis of H_2O_2 in the absence of catalyst or the presence of pre-equilibrated (with the adsorption of H_2O_2) catalyst in the absence of light does not lead to the oscillation. The phenomenon is more pronounced in sonocatalysis, the intensity of oscillation being in the order sonocatalysis > photocatalysis≥sonophotocatalysis while the degradation of phenol follows the order sonophotocatalysis > photocatalysis > sonocatalysis > sonolysis > photolysis. In the case of sonocatalysis, the oscillation continues for some more time after discontinuing the US irradiation indicating that the reactive free radicals as well as the trapped electrons and holes which interact with H_2O_2 have longer life time (memory effect).
机译:在环境条件下,声,光和声光催化等高级氧化工艺(AOP)在污水净化中的应用涉及活性氧(ROS)的形成和参与,如?OH,HO_2〜?,O_2〜(-?)。 ),H_2O_2等。其中,H_2O_2是最稳定的,也是反应性自由基的前体。 ZnO介导的声,光和声光催化降解水中苯酚污染物的研究表明,原位形成的H_2O_2不能与污染物的降解定量相关。形成的H_2O_2的浓度不会随着苯酚的降解而增加,并达到平稳状态,或者以波状方式(振荡)变化,并具有清晰的波峰和波谷,表明同时形成和分解。分解超过形成或分解超过分解的浓度对反应条件敏感。在不存在催化剂的情况下或在不存在光的情况下进行预平衡(具有吸附H_2O_2的催化剂)的情况下,H_2O_2的直接光解不会导致振荡。该现象在声催化中更为明显,振荡强度为声催化>光催化≥声光催化,而苯酚的降解遵循声光催化>光催化>声催化>声催化>光催化。在声催化的情况下,振荡在停止US辐射后还会持续更多时间,这表明反应性自由基以及与H_2O_2相互作用的俘获电子和空穴具有更长的寿命(记忆效应)。

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