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Kinetics Of 2,6-dimethylaniline Degradation By Electro-fenton Process

机译:电子芬顿法降解2,6-二甲基苯胺的动力学

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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_2O_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_2O_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.
机译:已经开发出一种使用不同的电化学电池和光电芬顿工艺来提高铁还原效率的新方法来降解有机有毒污染物。使用UVA光和电流作为电子给体可以有效地引发Fenton反应。 2,6-二甲基苯胺(2,6-DMA)是本研究的目标化合物。确定了初始pH(pH_i),Fe〜(2+)负载,H_2O_2浓度和电流密度的影响,以测试并验证电芬顿法氧化有机化合物的动力学模型。动力学结果表明伪一级降解的证据。当反应pH高于2时,生成无定形的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,然后促进2,6-DMA的降解效率。在本研究中,用于2,6-DMA降解的最佳H_2O_2浓度为25 mM。随着电流密度从3.5增加到10.6 A / m〜2,2,6-DMA的降解增加。草酸是检测到的2,6-DMA降解的主要中间体。使用电解,Fenton,电Fenton和光电Fenton工艺的最终TOC去除效率分别为10%,15%,60%和84%。

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