Ting Wang-Ping, Lu Ming-Chun, Huang Yao-Hui
Department of Chemical Engineering, National Cheng Kung University, Tainan 701, Taiwan.
J Hazard Mater. 2009 Jan 30;161(2-3):1484-90. doi: 10.1016/j.jhazmat.2008.04.119. Epub 2008 May 3.
A new approach for promoting ferric reduction efficiency using a different electrochemical cell and the photoelectro-Fenton process has been developed to degrade organic toxic contaminants. The use of UVA light and electric current as electron donors can efficiently initiate the Fenton reaction. 2,6-Dimethylaniline (2,6-DMA) was the target compound in this study. Effects of initial pH (pH(i)), Fe(2+) loading, H(2)O(2) concentration and current density were determined to test and to validate a kinetic model for the oxidation of organic compound by the electro-Fenton process. Kinetic results show evidence of pseudo-first-order degradation. When reaction pH was higher than 2, amorphous Fe(OH)(3(s)) was generated. Increasing ferrous ion concentration from 1.0 to 1.5 mM increased the hydroxyl radicals and then promote the degradation efficiency of 2,6-DMA. The optimal H(2)O(2) concentration for 2,6-DMA degradation in this study was 25 mM. The degradation of 2,6-DMA was increased with the increase of current density from 3.5 to 10.6 A/m(2). Oxalic acid was the major detected intermediate of 2,6-DMA degradation. The final TOC removal efficiencies were 10%, 15%, 60% and 84% using the electrolysis, Fenton, electro-Fenton and photoelectro-Fenton processes, respectively.
已开发出一种使用不同电化学电池和光电芬顿工艺提高铁还原效率的新方法,以降解有机有毒污染物。使用紫外光(UVA)和电流作为电子供体可以有效地引发芬顿反应。本研究中的目标化合物是2,6-二甲基苯胺(2,6-DMA)。测定了初始pH(pH(i))、Fe(2+)负载量、H(2)O(2)浓度和电流密度的影响,以测试和验证电芬顿工艺氧化有机化合物的动力学模型。动力学结果显示了准一级降解的证据。当反应pH高于2时,会生成无定形Fe(OH)(3(s))。将亚铁离子浓度从1.0 mM增加到1.5 mM会增加羟基自由基,进而提高2,6-DMA的降解效率。本研究中2,6-DMA降解的最佳H(2)O(2)浓度为25 mM。随着电流密度从3.5 A/m(2)增加到10.6 A/m(2),2,6-DMA的降解增加。草酸是2,6-DMA降解中主要检测到的中间体。使用电解、芬顿、电芬顿和光电芬顿工艺时,最终的总有机碳(TOC)去除效率分别为10%、15%、60%和84%。