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Photochemical behavior of ferrihydrite-oxalate system: Interfacial reaction mechanism and charge transfer process

机译:Ferrihydite-草酸系统的光化学行为:界面反应机理和电荷转移过程

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摘要

Heterogeneous photochemical reactions associated with natural iron (hydr)oxides and oxalic acid have attracted a great deal of scientific attention in the application of organic pollutants degradation. However, the reaction mechanism is still unclear due to the complicated iron cycles and reactive oxygen species (ROS) generation. In this study, the in situ attenuated total reflectance-Fourier transform infrared spectroscopy was implemented to investigate the adsorption process and photochemical behavior of oxalic acid on the surface of ferrihydrite. A comprehensive reaction mechanism from the perspective of charge transfer process, including homogeneous-heterogeneous iron cycling and ROS generation, was illustrated in detail. We found that oxalic acid was first adsorbed on the surface of ferrihydrite with a mononuclear bidentate binding geometry. Interestingly, this mononuclear bidentate complex on the surface of ferrihydrite was stable under visible light irradiation. Subsequently, the whole complex departed from ferrihydrite surface through non-reduction dissolution with the form of Fe(C2O4)(+). In the solution, the Fe(C2O4)(+) complexes would quickly convert to Fe(C2O4)(2)(-) complexes. Under visible light irradiation, the electrons generated from the photolysis of Fe(C2O4)(2)(-) complex reacted with O-2 to form O-2(center dot-)/center dot OOH. Meanwhile, Fe(III) was reduced to Fe(II). Finally, the produced O-2(center dot-)/center dot OOH could react with Fe(II) through a one-step way to generate center dot OH, which possessed higher center dot OH formation efficiency than that through the two-step way of H2O2 as the intermediates. This study helps us with understanding of in-situ photochemical reaction mechanism of ferrihydrite-oxalic acid system, and also provides guidance to effectively utilize widespread iron (hydr)oxides and organic acids in natural environment to develop engineered systems for water treatment. (C) 2019 Elsevier Ltd. All rights reserved.
机译:与天然铁(乙酸)氧化物和草酸相关的异质光化学反应引起了有机污染物降解的大量科学关注。然而,由于复杂的铁循环和反应性氧(ROS)产生,反应机制仍然尚不清楚。在该研究中,实施了原位减毒的总反射率 - 傅里叶变换红外光谱,以研究草酸在Ferrihydry表面上的吸附过程和光化学行为。详细说明了一种综合反应机制,包括均相异质铁循环和生成,包括均相异质铁循环和ROS产生。我们发现,首先用单核双齿结合几何体吸附在Ferrihydrite的表面上的草酸。有趣的是,在富勒霉石表面上的这种单核状物的络合物在可见光照射下稳定。随后,整个复合物通过具有Fe(C 2 O 4)(+)的形式的非还原溶解来脱离Ferrihydrite表面。在溶液中,Fe(C 2 O 4)(+)配合物将迅速转化为Fe(C2O4)(2)( - )复合物。在可见光照射下,从Fe(C2O4)(2)( - )复合物的光解产生的电子与O-2反应以形成O-2(中心点 - )/中心点OOH。同时,Fe(III)减少到Fe(II)。最后,所产生的O-2(中心DOT - )/中心点OOH可以通过一步的方式与Fe(II)反应,以产生中心点OH,其具有比通过两步的中心点OH形成效率更高的中心点OH形成效率H2O2作为中间体的方式。本研究有助于我们理解Ferrihydrite-草酸系统的原位光化学反应机制,还提供了有效地利用自然环境中广泛的铁(氢)氧化物和有机酸的指导来开发用于水处理的工程化系统。 (c)2019 Elsevier Ltd.保留所有权利。

著录项

  • 来源
    《Water Research》 |2019年第1期|10-19|共10页
  • 作者单位

    Cent China Normal Univ Key Lab Pesticide & Chem Biol Inst Environm & Appl Chem Minist Educ Coll Chem Wuhan 430079 Hubei Peoples R China;

    Chinese Acad Sci Guangdong Prov Key Lab Mineral Phys & Mat Guangzhou Inst Geochem 511 Kehua St Guangzhou 510640 Guangdong Peoples R China;

    Cent China Normal Univ Key Lab Pesticide & Chem Biol Inst Environm & Appl Chem Minist Educ Coll Chem Wuhan 430079 Hubei Peoples R China;

    Cent China Normal Univ Key Lab Pesticide & Chem Biol Inst Environm & Appl Chem Minist Educ Coll Chem Wuhan 430079 Hubei Peoples R China;

    Cent China Normal Univ Key Lab Pesticide & Chem Biol Inst Environm & Appl Chem Minist Educ Coll Chem Wuhan 430079 Hubei Peoples R China;

    Cent China Normal Univ Key Lab Pesticide & Chem Biol Inst Environm & Appl Chem Minist Educ Coll Chem Wuhan 430079 Hubei Peoples R China;

  • 收录信息 美国《科学引文索引》(SCI);美国《工程索引》(EI);
  • 原文格式 PDF
  • 正文语种 eng
  • 中图分类
  • 关键词

    Oxalic acid; Ferrihydrite; In-situ ATR-FTIR; Fe(III)-Ox complex; Reactive oxygen species;

    机译:草酸;Ferrihydite;原位ATR-FTIR;Fe(III)-OX综合体;反应性氧;

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