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首页> 外文期刊>Chemical engineering journal >Degradation of diclofenac and carbamazepine by the copper(II)-catalyzed dark and photo-assisted Fenton-like systems
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Degradation of diclofenac and carbamazepine by the copper(II)-catalyzed dark and photo-assisted Fenton-like systems

机译:铜(II)催化的深色和光助芬顿样体系降解双氯芬酸和卡马西平

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摘要

The oxidative degradation of two pharmaceutical compounds (diclofenac and carbamazepine, denoted as DCF and CBZ) by the Cu(II)-catalyzed Fenton (Cu(II)/H2O2) and the photo-Fenton (UV/Cu(II)/H2O2) systems was examined, with a focus on the parameters that affected the oxidant production, such as the solution pH, the Cu(II) concentration, and the radical scavengers. The degradation of DCF and CBZ in the Cu(II)/H2O2 and UV/Cu(II)/H2O2 systems followed the pseudo-first-order kinetics, which exhibited increasing rate constants with the increasing concentration of Cu(II). In the Cu(II)/H2O2 system, the optimal degradation of the target contaminants was observed at approximately pH 8, which is attributed to the combined effects of two pH-dependent factors: (1) the accelerated Cu(II) reduction by H2O2 with increasing pH and (2) the shift of the main oxidant from the hydroxyl radical (OH) to the cupryl ion (Cu[III]) at high pH values. The complete prevention of the degradation of DCF and CBZ in the presence of excess tert-butanol indicates that ~·OH is dominantly responsible for the contaminant degradation. The UV-A irradiation significantly enhanced the degradation of the target contaminants over the entire pH range studied (pH 3-10) and slightly shifted the optimal pH conditions to lower values (pH 6-7). The enhanced degradation of the contaminants by the UV/Cu(II)/H2O2 system appears to result from the accelerated Cu(II) reduction by the hydroperoxyl/superoxide radicals (HO2~O/O2~(·-)), which are produced via the photolysis of H2O2.
机译:Cu(II)催化的Fenton(Cu(II)/ H2O2)和光Fenton(UV / Cu(II)/ H2O2)氧化降解两种药物化合物(双氯芬酸和卡马西平,表示为DCF和CBZ)对系统进行了检查,重点是影响氧化剂产生的参数,例如溶液的pH值,Cu(II)浓度和自由基清除剂。在Cu(II)/ H2O2和UV / Cu(II)/ H2O2系统中DCF和CBZ的降解遵循拟一级动力学,随着Cu(II)浓度的增加,速率常数增加。在Cu(II)/ H2O2系统中,在大约pH 8时观察到目标污染物的最佳降解,这归因于两个pH依赖因素的综合作用:(1)H2O2加速Cu(II)还原随着pH值的升高,以及(2)在高pH值下,主要氧化剂从羟基(OH)转移到铜离子(Cu [III])。在过量叔丁醇存在下,完全防止DCF和CBZ降解表明〜·OH是污染物降解的主要原因。 UV-A辐照在整个研究的pH范围内(pH 3-10)显着增强了目标污染物的降解,并将最佳pH条件略微移至了较低的值(pH 6-7)。 UV / Cu(II)/ H2O2系统对污染物的降解增强似乎是由于氢过氧化物/超氧化物自由基(HO2〜O / O2〜(·-))加速了Cu(II)还原通过H2O2的光解。

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