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Comparison of different chelating agents to enhance reductive Cr(VI) removal by pyrite treatment procedure

机译:比较各种螯合剂以提高黄铁矿处理程序对还原性Cr(VI)的去除

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摘要

New technologies involving in-situ chemical hexavalent chromium [Cr(VI)] reduction to trivalent chromium [Cr(III)] with natural Fe(II)-containing minerals can offer viable solutions to the treatment of wastewater and subsurface systems contaminated with Cr(VI). Here, the effects of five different chelating agents including citrate, EDTA, oxalate, tartrate and salicylate on reductive Cr(VI) removal from aqueous systems by pyrite were investigated in batch reactors. The Cr(VI) removal was highly dependent on the type of ligand used and chemical conditions (e.g., ligand concentration). While salicylate and EDTA had no or little effect on Cr(VI) removal, the ligands including citrate, tartrate and oxalate significantly enhanced Cr(VI) removal at pH < 7 relative to non-ligand systems. In general, the efficiency of organic ligands on Cr(VI) removal decreased in the order: citrate >= oxalate tartrate approximate to EDTA > salicylate approximate to non-ligand system. Organic ligands enhanced Cr(VI) removal by 1) removing surface oxide layer via the formation of soluble Fe-Cr-ligand complexes, and 2) enhancing the reductive iron redox cycling for the regeneration of new surface sites. While citrate, oxalate and tartrate eliminated the formation of surface Cr (III) Fe(III)-oxides, the surface phase Cr (III) species was observed in the presence of EDTA and salicylate indicating that Cr(III) complexed with EDTA and salicylate sorbed or precipitated onto pyrite surface, thereby blocking the access of Cr-4(2-) to pyrite surface. The binding of Fe(III) with the disulfide reactive sites (equivalent to Fe-S-S-Fe(III)) was essential for the regeneration of new surface sites through pyrite oxidation. Although Fe(III)-S species was detected at the pyrite surface in the presence of citrate, oxalate and tartrate, Fe(III) complexed with EDTA and salicylate did not strongly interact with the disulfide reactive sites due to the formation of non-sorbing Fe(III)-ligand complexes. The absence of surface Fe(III)-S species indicated that no new reactive sites were generated through Fe redox cycling in the presence of salicylate and EDTA. (C) 2015 Elsevier Ltd. All rights reserved.
机译:新技术涉及将天然六价铬[Cr(VI)]与含有天然Fe(II)的矿物还原为三价铬[Cr(III)]的新技术,可以为废水和受Cr(II)污染的地下系统的处理提供可行的解决方案。 VI)。在此,在间歇反应器中研究了五种不同的螯合剂(包括柠檬酸盐,EDTA,草酸盐,酒石酸盐和水杨酸盐)对黄铁矿从水系统中还原性Cr(VI)去除的影响。 Cr(VI)的去除高度取决于所用配体的类型和化学条件(例如,配体浓度)。尽管水杨酸盐和EDTA对Cr(VI)的去除没有影响或影响很小,但相对于非配体体系,包括柠檬酸盐,酒石酸盐和草酸盐的配体在pH <7时显着提高了Cr(VI)的去除率。通常,有机配体对Cr(VI)去除的效率按以下顺序降低:柠檬酸> =酒石酸草酸盐,近似于EDTA>水杨酸酯,近似于非配体体系。有机配体通过以下方式增强了Cr(VI)的去除:1)通过形成可溶性Fe-Cr-配体络合物去除表面氧化物层,以及2)增强还原铁氧化还原循环,以再生新的表面部位。尽管柠檬酸盐,草酸盐和酒石酸盐消除了表面Cr(III)Fe(III)-氧化物的形成,但在EDTA和水杨酸盐存在下观察到表面相Cr(III)物种,表明Cr(III)与EDTA和水杨酸盐络合吸附或沉淀到黄铁矿表面,从而阻止Cr-4(2-)进入黄铁矿表面。 Fe(III)与二硫键反应位点(相当于Fe-S-S-Fe(III))的结合对于通过黄铁矿氧化再生新的表面位点至关重要。尽管在柠檬酸盐,草酸盐和酒石酸盐的存在下在黄铁矿表面检测到Fe(III)-S物种,但由于形成了非吸附性,与EDTA和水杨酸酯络合的Fe(III)与二硫键的反应位点没有强烈的相互作用。 Fe(III)-配体络合物。没有表面Fe(III)-S物种表明在水杨酸酯和EDTA存在下,通过Fe氧化还原循环没有新的反应位点产生。 (C)2015 Elsevier Ltd.保留所有权利。

著录项

  • 来源
    《Water Research》 |2015年第1期|66-75|共10页
  • 作者单位

    Canakkale Onsekiz Mart Univ, Dept Environm Engn, TR-17100 Canakkale, Turkey;

    Canakkale Onsekiz Mart Univ, Dept Environm Engn, TR-17100 Canakkale, Turkey;

    NanoMagnet Instruments Ltd, Hacettepe Ivedik OSB Teknokent, TR-06370 Ankara, Turkey;

  • 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

    Pyrite; Chromium; Organic ligands; Complexation; Treatment; Oxidation;

    机译:黄铁矿;铬;有机配体;络合物;处理;氧化;

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