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过氧化氢对四种不同的富铬土壤中铬的氧化态和溶解度的影响。

Hydrogen peroxide effects on chromium oxidation state and solubility in four diverse, chromium-enriched soils.

作者信息

Rock M L, James B R, Helz G R

机构信息

Department of Chemistry and Biochemistry and Water Resources Research Center, University of Maryland, College Park 20742, USA.

出版信息

Environ Sci Technol. 2001 Oct 15;35(20):4054-9. doi: 10.1021/es010597y.

Abstract

High concentrations of H2O2 are being tested for in situ oxidation and remediation of buried organic contaminants in soils and groundwater. Peroxide is being considered as a direct chemical oxidant in Fenton-type reactions or as a source of oxidizing equivalents in bioremediation schemes. How H2O2 affects the oxidation state and solubility of Cr(III) and Cr(VI), common co-contaminants with organic chemicals, is explored here in four chemically diverse soils containing elevated levels of Cr. Soil contaminated with soluble Cr(VI) from chromite ore processing residue and soil containing high levels of recently reduced Cr (III) from electroplating waste both released dissolved Cr(VI) after single applications of up to 24 mM H2O2. In no case was there evidence that H202 reduced preexisting Cr(VI) to Cr(III), even though this would be allowed thermodynamically. Chromate in the leachates exceeded the U.S. EPA drinking water standard for total dissolved Cr (2 microM) by a factor of 10-1000. Anaerobic conditions in an organic-rich, tannery waste-contaminated soil protected Cr(III) from oxidation and mobilization. Mineral forms of Cr in serpentinitic soil near a former chromite mine also resisted oxidation on the time scale of days. Mobilization of Cr(VI) could be a hazardous consequence of using H2O2 for in situ remediation of chemically complex wastes, but H2O2 could prove attractive for ex situ treatment (i.e., soil washing). This paper demonstrates marked differences among Cr-contaminated soils in their capacity to release Cr(VI) upon chemical treatment with H2O2.

摘要

目前正在测试高浓度过氧化氢用于原位氧化和修复土壤及地下水中掩埋的有机污染物。在芬顿型反应中,过氧化物被视为直接化学氧化剂,或者在生物修复方案中作为氧化当量的来源。本文研究了过氧化氢如何影响铬(III)和铬(VI)的氧化态及溶解度,铬(III)和铬(VI)是与有机化学品常见的共污染物,研究对象为四种含铬量较高且化学性质不同的土壤。来自铬铁矿加工残渣的可溶性铬(VI)污染土壤以及来自电镀废料的近期大量还原态铬(III)污染土壤,在单次施加高达24 mM过氧化氢后均释放出溶解态铬(VI)。在任何情况下,均没有证据表明过氧化氢将预先存在的铬(VI)还原为铬(III),尽管从热力学角度来看这是可行的。渗滤液中的铬酸盐超过了美国环境保护局规定的总溶解铬(2 microM)饮用水标准10至1000倍。在富含有机物的制革厂废料污染土壤中的厌氧条件可保护铬(III)不被氧化和迁移。在一个 former chromite mine附近的蛇纹岩土中,铬的矿物形态在数天时间尺度内也能抵抗氧化。使用过氧化氢对化学性质复杂的废物进行原位修复时,铬(VI)的迁移可能会产生有害后果,但过氧化氢可能对异位处理(即土壤冲洗)具有吸引力。本文证明了受铬污染的土壤在用过氧化氢进行化学处理后释放铬(VI)的能力存在显著差异。

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