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Fe@FeO 通过三嗪环开环机制促进阿特拉津的电化学矿化。

Fe@FeO promoted electrochemical mineralization of atrazine via a triazinon ring opening mechanism.

机构信息

Key Laboratory of Pesticide & Chemical Biology of Ministry of Education, Institute of Environmental & Applied Chemistry, College of Chemistry, Central China Normal University, Wuhan 430079, PR China; College of Science, Huazhong Agricultural University, Wuhan 430070, PR China.

College of Science, Huazhong Agricultural University, Wuhan 430070, PR China.

出版信息

Water Res. 2017 Apr 1;112:9-18. doi: 10.1016/j.watres.2017.01.024. Epub 2017 Jan 16.

Abstract

In this study, an electrochemical/electro-Fenton oxidation (EC/EF) system was designed to degrade atrazine, by utilizing boron-doped diamond (BDD) and Fe@FeO core-shell nanowires loaded active carbon fiber (Fe@FeO/ACF) as the anode and the cathode, respectively. This EC/EF system exhibited much higher degradation rate, decholorination and mineralization efficiency of atrazine than the electrochemical (EC) and electrochemical/traditional electro-Fenton (EC/TEF) oxidation counterpart systems without Fe@FeO core-shell nanowires. Active species trapping experiment revealed that Fe@FeO could activate molecular oxygen to produce more OH through Fenton reaction, which favored the atrazine degradation. High performance liquid chromatography, high performance liquid chromatography-mass spectrometry and gas chromatography-mass spectrometry were applied to probe the decomposition and mineralization of atrazine during this novel EC/EF process, which revealed that two intermediates of triazinons (the isomerization of hydroxylated atrazine) were generated during the electrochemical/electro-Fenton oxidation of atrazine in the presence of Fe@FeO core-shell nanowires. The experimental and theoretical calculation results suggested that atrazine might be degraded via a triazinon ring opening mechanism, while the presence of Fe@FeO notably accelerated the decholorination process, and produced more hydroxylated products to promote the generation of trazinons and the subsequent ring cleavage as well as the final complete mineralization. This work provides a deep insight into the triazine ring opening mechanism and the design of efficient electrochemical advanced oxidation technologies (EAOTs) for persistent organic pollutant removal.

摘要

在这项研究中,设计了一种电化学/电芬顿氧化(EC/EF)系统,利用掺硼金刚石(BDD)和负载活性碳纤维的 Fe@FeO 核壳纳米线(Fe@FeO/ACF)分别作为阳极和阴极,来降解莠去津。与没有 Fe@FeO 核壳纳米线的电化学(EC)和电化学/传统电芬顿(EC/TEF)氧化对照系统相比,该 EC/EF 系统对莠去津的降解速率、脱氯率和矿化效率都要高得多。活性物质捕获实验表明,Fe@FeO 可以通过芬顿反应激活分子氧产生更多的 OH,这有利于莠去津的降解。高效液相色谱、高效液相色谱-质谱和气相色谱-质谱被用于探测在这种新型 EC/EF 过程中莠去津的分解和矿化,结果表明,在 Fe@FeO 核壳纳米线存在的情况下,电化学/电芬顿氧化莠去津会生成两种三嗪酮中间体(羟化莠去津的异构化)。实验和理论计算结果表明,莠去津可能通过三嗪酮开环机制降解,而 Fe@FeO 的存在显著加速了脱氯过程,并产生了更多的羟基化产物,从而促进了三嗪酮的生成以及随后的环断裂和最终的完全矿化。这项工作深入了解了三嗪环开环机制以及高效电化学高级氧化技术(EAOTs)用于去除持久性有机污染物的设计。

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