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首页> 外文期刊>Chemical engineering journal >Electrochemical reductive dechlorination of chlorinated volatile organic compounds (Cl-VOCs): Effects of molecular structure on the dehalogenation reactivity and mechanisms
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Electrochemical reductive dechlorination of chlorinated volatile organic compounds (Cl-VOCs): Effects of molecular structure on the dehalogenation reactivity and mechanisms

机译:氯化挥发性有机化合物(CL-VOC)的电化学还原脱氯:分子结构对脱卤的影响和机制的影响

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摘要

Chlorinated volatile organic compounds (Cl-VOCs) are a group of common contaminants that are widely detected in various polluted media (e.g., water, soil and atmospheric environment). The removal of these compounds has thus attracted considerable worldwide attention. Electrochemical reductive dehalogenation is among one of the most prospective approaches for the treatment of Cl-VOCs. Whereas a wealth of electrochemical data has been obtained over the past years by extensive investigations for these compounds, there is still missing a combined knowledge from individual researches. This review considers polychloromethanes (PCMs), poly-chloroethanes (PCAs) and polychloroethylenes (PCEs) as a whole and, systematically investigates the molecular structure effects on the reductive dehalogenation of Cl-VOCs, in order to highlight their common and specific properties of dehalogenation reactivity and reduction mechanisms and further, try to reveal their intrinsic relationships. Results show that molecular structure plays a vital role in determining the dehalogenation reactivity and dehalogenation mechanisms of Cl-VOCs. The dechlorination reaction is found to become more thermodynamically favored with the degree of chlorination, while an overall promotion effect of chemical groups in Cl-VOCs toward dehalogenation reactivity follows the order: alkyl group beta-chlorine double bond alpha-chlorine. Moreover, based on the electron transfer mechanisms, Cl-VOCs are classified as saturated or un-saturated, where concerted and stepwise dissociative electron transfer mechanisms take place, respectively. Based on the dehalogenation mechanisms, these compounds can be categorized as geminal or vicinal, which principally undergo the hydrodehalogenation pathway and reductive beta-elimination route, correspondingly. The recent development of reductive dehalogenation issues for Cl-VOCs and the possible directions are discussed in the last section.
机译:氯化挥发性有机化合物(CL-VOC)是一组普遍检测到各种污染介质(例如水,土壤和大气环境)的常见污染物。因此,去除这些化合物的全世界关注都是相当大的。电化学还原脱氢是治疗CL-VOC的最前景方法之一。然而,在过去几年中获得了丰富的电化学数据,而对这些化合物的广泛调查,仍然缺少个人研究的综合知识。本综述考虑整体的聚氯甲烷(PCMS),多氯乙烷(PCA)和聚氯乙烯(PCE),系统地研究CL-VOCS的还原脱卤素的分子结构作用,以突出其脱氢的常见和特异性反应性和减少机制进一步,尝试揭示其内在关系。结果表明,分子结构在确定CL-VOCs的脱氢反应性和脱卤方法方面发挥着至关重要的作用。发现脱氯反应随着氯化程度变得更加热,而CL-VOC中的化学基团朝向脱氢反应性的总体促进作用遵循顺序:烷基& & β-氯&双键& α-氯。此外,基于电子转移机制,CL-VOC分别被分类为饱和或未饱和的,其中齐全和逐步离灭电子转移机制发生。基于脱氢机制,这些化合物可分为初始或静脉,其主要经历多牛碱途径和还原β消除途径。最后一节讨论了CL-VOCS的还原脱离问题的最新发展和可能的方向。

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