首页> 外文期刊>Applied Catalysis, B. Environmental: An International Journal Devoted to Catalytic Science and Its Applications >Electro-Fenton oxidation of pesticides with a novel Fe3O4@Fe2O3/activated carbon aerogel cathode: High activity, wide pH range and catalytic mechanism
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Electro-Fenton oxidation of pesticides with a novel Fe3O4@Fe2O3/activated carbon aerogel cathode: High activity, wide pH range and catalytic mechanism

机译:新型Fe3O4 @ Fe2O3 /活性炭气凝胶阴极对农药进行电子芬顿氧化:高活性,宽pH范围和催化机理

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摘要

A novel electro-Fenton (E-Fenton) system with the Fe3O4@Fe2O3/activated carbon aerogel (ACA) composite cathode was firstly constructed in this study. Its application on degrading imidacloprid exhibited highly catalytic efficiency over a wide applicable pH range from 3 to 9. The removal of imidacloprid and TOC achieved to 90% within 30 and 60 min, respectively. The nature of composite cathode was examined by BJH, XRD, SEM, TEM, XPS and FT1R techniques. ACA with high surface area of 2410 m~2 g~(-1) and multipli-cated porosities composed of micropores and mesopores worked not only as cathode but also as Fenton catalyst support, enhancing oxidation activity. We proposed reasonable E-Fenton oxidation mechanisms with Fe3O4@Fe2O3/ACA cathode at acidic and basic conditions. At pH 3, it followed a Haber-Weiss mechanism that the dissolved iron ions and surface Fe(II) sites catalyzed the decomposition of H2O2 to generate hydroxyl radicals (~·OH). While at pH 9, it was expected the formation and deactivation of H2O2 complex as well as the catalytic decomposition of H2O2 with surface Fe(Ill) and Fe(II) sites to produce both superoxide anion (~·O2~/HO2~·) and hydroxyl radicals (~·OH), involving an in situ recycling of iron oxide (FeOFe2O3 → Fe2O3).
机译:本研究首次构建了具有Fe3O4 @ Fe2O3 /活性炭气凝胶(ACA)复合阴极的新型电子芬顿(E-Fenton)系统。它在降解吡虫啉中的应用在3至9的宽pH值范围内均显示出很高的催化效率。吡虫啉和TOC的去除率分别在30分钟和60分钟内达到90%。通过BJH,XRD,SEM,TEM,XPS和FT1R技术检查了复合阴极的性质。具有2410 m〜2 g〜(-1)的高表面积且由微孔和中孔组成的多重孔隙的ACA不仅用作阴极,而且用作Fenton催化剂载体,增强了氧化活性。我们提出了在酸性和碱性条件下,Fe3O4 @ Fe2O3 / ACA阴极具有合理的电子芬顿氧化机理。在pH为3时,遵循Haber-Weiss机理,即溶解的铁离子和表面Fe(II)部位催化H2O2分解,生成羟基自由基(〜·OH)。在pH值为9时,可以预期H2O2络合物的形成和失活,以及H2O2在表面Fe(III)和Fe(II)部位的催化分解,从而同时产生超氧阴离子(〜·O2〜/ HO2〜·)和羟基(〜·OH),涉及氧化铁(FeOFe2O3→Fe2O3)的原位回收。

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