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两种氯化脂肪烃的电化学比较处理。主要反应副产物的时间进程。

Comparative electrochemical treatments of two chlorinated aliphatic hydrocarbons. Time course of the main reaction by-products.

机构信息

Laboratori d'Electroquímica dels Materials i del Medi Ambient, Departament de Química Física, Facultat de Química, Universitat de Barcelona, Martí i Franquès 1-11, 08028 Barcelona, Spain.

出版信息

J Hazard Mater. 2011 Sep 15;192(3):1555-64. doi: 10.1016/j.jhazmat.2011.06.075. Epub 2011 Jul 1.

Abstract

Acidic aqueous solutions of the chlorinated aliphatic hydrocarbons 1,2-dichloroethane (DCA) and 1,1,2,2-tetrachloroethane (TCA) have been treated by the electro-Fenton (EF) process. Bulk electrolyses were performed at constant current using a BDD anode and an air diffusion cathode able to generate H(2)O(2) in situ, which reacts with added Fe(2+) to yield OH from Fenton's reaction. At 300 mA, almost total mineralization was achieved at 420 min for solutions containing 4mM of either DCA or TCA. Comparative treatments without Fe(2+) (anodic oxidation) or with a Pt anode led to a poorer mineralization. The better performance of the EF process with BDD is explained by the synergistic action of the oxidizing radicals, BDD(OH) at the anode surface and OH in the bulk, and the minimization of diffusional limitations. The decay of the initial pollutant accomplished with pseudo first-order kinetics. Chloroacetic and dichloroacetic acids were the major by-products during the degradation of DCA and TCA, respectively. Acetic, oxalic and formic acids were also identified. The proposed reaction pathways include oxidative and reductive (cathodic) dechlorination steps. Chlorine was released as Cl(-), being further oxidized to ClO(3)(-) and, mostly, to ClO(4)(-), due to the action of the largely generated BDD(OH) and OH.

摘要

酸性水溶液中的氯化脂肪烃 1,2-二氯乙烷(DCA)和 1,1,2,2-四氯乙烷(TCA)已被电-Fenton(EF)工艺处理。在恒电流下进行了 bulk electrolyses,使用 BDD 阳极和空气扩散阴极,能够原位生成 H(2)O(2),它与添加的 Fe(2+)反应,从 Fenton 反应中生成 OH。在 300 mA 时,对于含有 4mM 的 DCA 或 TCA 的溶液,在 420 min 内几乎实现了完全矿化。没有 Fe(2+)(阳极氧化)或使用 Pt 阳极的比较处理导致矿化程度较差。BDD 的 EF 工艺性能更好,这可以解释为氧化自由基的协同作用,BDD(OH)在阳极表面和 OH 在本体中的作用,以及扩散限制的最小化。初始污染物的衰减遵循准一级动力学。在 DCA 和 TCA 的降解过程中,主要的副产物分别是氯乙酸和二氯乙酸。还鉴定出了乙酸、草酸和甲酸。所提出的反应途径包括氧化和还原(阴极)脱氯步骤。由于大量生成的 BDD(OH)和 OH 的作用,氯以 Cl(-)的形式释放,进一步被氧化为 ClO(3)(-)和主要是 ClO(4)(-)。

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