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Chromium Remediation or Release? Effect of Iron(II) Sulfate Addition on Chromium(VI) Leaching from Columns of Chromite Ore Processing Residue

机译:铬的修复或释放?硫酸铁(II)添加对铬铁矿渣中铬(VI)浸出的影响

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摘要

Chromite ore processing residue (COPR), derived from theudso-called high lime processing of chromite ore, containsudhigh levels of Cr(III) and Cr(VI) and has a pH between 11 andud12. Ferrous sulfate, which is used for remediation ofudCr(VI) contamination in wastewater and soils via reductionudto Cr(III) and subsequent precipitation of iron(III)/chromium-ud(III) hydroxide, has also been proposed for remediationudof Cr(VI) in COPR. Instead, however, addition of FeSO4 toudthe infiltrating solution in column experiments with COPRudgreatly increased leaching of Cr(VI). Leached Cr(VI) increasedudfrom 3.8 to 12.3 mmol kg-1 COPR in 25 pore volumesudwith 20 mM FeSO4, reaching solution concentrations asudhigh as 1.6 mM. Fe(II) was ineffective in reducing Cr(VI) toudCr(III) because it precipitated when it entered the columnuddue to the high pH of COPR, while Cr(VI) in solutionudwas transported away with the infiltrating solution. Theudlarge increase in leaching of Cr(VI) upon infiltration of sulfate,udeither as FeSO4 or Na2SO4, was caused by anion exchangeudof sulfate for chromate in the layered double hydroxideudmineral hydrocalumite, a process for which scanning electronudmicroscopy with energy-dispersive X-ray microanalysisudprovided direct evidence.
机译:铬铁矿加工残渣(COPR)源自铬铁矿的所谓的高石灰加工,含有很高水平的Cr(III)和Cr(VI),pH值为11至ud12。还提出了硫酸亚铁,用于通过还原 udto Cr(III)并随后沉淀铁(III)/铬-ud(III)来补救废水和土壤中的udud(VI)污染。补救 udof Cr(VI)。取而代之的是,在使用COPR的柱实验中,向渗透溶液中加入FeSO4会极大地增加Cr(VI)的浸出。含20 mM FeSO4的25个孔体积中,浸出的Cr(VI)从3.8增加到了12.3 mmol kg-1 COPR,溶液浓度高达1.6 mM。 Fe(II)不能有效地将Cr(VI)还原为 udCr(III),因为它由于进入COPR的pH高而在进入色谱柱时沉淀出来,而溶液中的Cr(VI)随渗透液一起被带走。 。硫酸根渗透过程中铬(VI)的浸出显着增加,无论是FeSO4还是Na2SO4,是由于层状双氢氧化物/铀水铝钙矿中硫酸根与铬酸盐的阴离子交换/ udud引起的。借助能量色散X射线显微分析未提供直接证据。

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