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羟基自由基介导的双氯芬酸降解再探:反应机制和副产物评估的计算方法。

Hydroxyl radical-mediated degradation of diclofenac revisited: a computational approach to assessment of reaction mechanisms and by-products.

机构信息

Department of Chemistry, Bogazici University, 34342, Bebek, Istanbul, Turkey.

Institute of Environmental Sciences, Bogazici University, 34342, Bebek, Istanbul, Turkey.

出版信息

Environ Sci Pollut Res Int. 2017 Aug;24(22):18458-18469. doi: 10.1007/s11356-017-9482-7. Epub 2017 Jun 23.

Abstract

Advanced oxidation processes (AOPs) are based on the in situ production of hydroxyl radicals (•OH) and reactive oxygen species (ROS) in water upon irradiation of the sample by UV light, ultrasound, electromagnetic radiation, and/or the addition of ozone or a semiconductor. Diclofenac (DCF), one of the emerging organic contaminants (EOC), is of environmental concern due to its abundancy in water and is known to be subjected to AOPs. The current study uses density functional theory (DFT) to elucidate the mechanisms of the reactions between •OH and DCF leading to degradation by-products, P1-P9. The initial encounter of DCF with •OH is proposed to lead to either the abstraction of a hydrogen or the addition of the hydroxyl radical to the molecule. The results showed that OH addition radicals (R ) are both kinetically and thermodynamically favored over H abstraction radicals (R ). The intermediate radicals give degradation by-products by subsequent reactions. The by-products P7 and P8 are easily formed in agreement with experimental findings. Finally, acute toxicities at three trophic levels are estimated with the Ecological Structure Activity Relationships program. DCF and most of the by-products were found to be harmful to aquatic organisms, P9 being the only by-product that is not harmful at all three trophic levels.

摘要

高级氧化工艺(AOPs)基于样品在紫外光、超声、电磁辐射照射下或臭氧、半导体添加时,原位产生羟基自由基(•OH)和活性氧物质(ROS)在水中。双氯芬酸(DCF)作为一种新兴的有机污染物(EOC),由于其在水中的丰富度而受到环境关注,并且已知会受到 AOPs 的影响。本研究使用密度泛函理论(DFT)阐明了•OH 与 DCF 之间导致降解副产物 P1-P9 的反应机制。DCF 与•OH 的初始接触被认为会导致氢的提取或羟基自由基的加成到分子上。结果表明,OH 加成自由基(R)在动力学和热力学上都优于 H 提取自由基(R)。中间自由基通过后续反应产生降解副产物。副产物 P7 和 P8 很容易按照实验结果形成。最后,用生态结构活性关系程序估算了三个营养级的急性毒性。发现 DCF 和大多数副产物对水生生物有害,而只有副产物 P9 在三个营养级都没有危害。

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