School of Environment and Energy, South China University of Technology, Guangzhou 510006, PR China.
School of Environment and Energy, South China University of Technology, Guangzhou 510006, PR China; South China Institute of Environmental Sciences, Ministry of Environmental Protection (MEP), Guangzhou 510655, China.
J Hazard Mater. 2021 Aug 5;415:125563. doi: 10.1016/j.jhazmat.2021.125563. Epub 2021 Mar 3.
In this paper, Phenol, 4-Chlorophenol (4-CP), 2,4-Dichlorophenol (2,4-DCP) and 2,4,6-Trichlorophenol (2,4,6-TCP) were selected as model pollutants to explore the oxidant mechanism by ferrate (Fe(VI)). The reactions between ferrate (1000 μM) and four phenolic compounds (100 μM) were conformed to the second-order reaction kinetics at pH 9.2, and the order of k followed as: k (129 M s) > k (96 M s) > k (44 M s) > k (12 M s). Meanwhile, the degradation rates of all four compounds by Fe(VI) increased with increased pH (3.1-9.2). A total of 14 degradation products were identified by Liquid chromatography-Time-of-Flight-Mass Spectrometry (LC-TOF-MS), and two pathways including hydroxylation of benzene ring and substitution of chlorine atom were proposed. Hydroxyl radicals, played a vital role during the degradation of phenolic compounds. Moreover, density functional theory calculations were used to explore the degradation mechanisms. The results showed that the hydroxyl radical was more favorable to substitute chlorine atom than hydrogen atom, and the substitution on ortho-position was more favorable than para-position for all four compounds. The findings of this study could greatly improve our understanding on the degradation mechanism of chlorophenol-like compounds by Fe(VI) for environmental remediation.
本文选择苯酚、4-氯苯酚(4-CP)、2,4-二氯苯酚(2,4-DCP)和 2,4,6-三氯苯酚(2,4,6-TCP)作为模型污染物,探讨高铁酸盐(Fe(VI))的氧化剂机制。在 pH 值为 9.2 时,高铁酸盐(1000 μM)与四种酚类化合物(100 μM)之间的反应符合二级反应动力学,k 值的顺序为:k(129 M s)> k(96 M s)> k(44 M s)> k(12 M s)。同时,Fe(VI)对所有四种化合物的降解速率均随 pH 值(3.1-9.2)的增加而增加。通过液相色谱-飞行时间质谱(LC-TOF-MS)共鉴定出 14 种降解产物,并提出了包括苯环羟基化和氯原子取代两种途径。羟基自由基在酚类化合物的降解过程中起着至关重要的作用。此外,还使用密度泛函理论计算来探讨降解机制。结果表明,对于所有四种化合物,羟基自由基更有利于取代氯原子而不是氢原子,且对位取代比邻位取代更有利。本研究的结果可以大大提高我们对 Fe(VI)降解类似氯酚类化合物的环境修复机制的理解。