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溶解态六价铬与针铁矿包裹赤铁矿的相互作用机制。

Interaction mechanism of dissolved Cr(VI) and manganite in the presence of goethite coating.

机构信息

Key Laboratory of Arable Land Conservation (Middle and Lower Reaches of Yangtse River), Ministry of Agriculture and Rural Affairs, Hubei Key Laboratory of Soil Environment and Pollution Remediation, College of Resources and Environment, Huazhong Agricultural University, Wuhan, 430070, Hubei Province, China.

Key Laboratory of Arable Land Conservation (Middle and Lower Reaches of Yangtse River), Ministry of Agriculture and Rural Affairs, Hubei Key Laboratory of Soil Environment and Pollution Remediation, College of Resources and Environment, Huazhong Agricultural University, Wuhan, 430070, Hubei Province, China.

出版信息

Environ Pollut. 2020 May;260:114046. doi: 10.1016/j.envpol.2020.114046. Epub 2020 Jan 25.

Abstract

Hexavalent chromium has aroused a series of environmental concerns due to its high mobility and toxicity. Iron and manganese oxides usually coexist in the environments and influence the speciation and geochemical cycling of chromium. However, the interaction mechanism of iron-manganese oxides with dissolved Cr(VI) remains largely unknown. In this work, the interaction processes of dissolved Cr(VI) and manganite in the presence of goethite coating were investigated, and the effects of pH (2.0-9.0) and iron oxide content were also studied. Manganite-goethite composites were formed with uniform micromorphologies in the system of manganite and Fe(II). In the reaction system of single manganite and Cr(VI), manganite could only adsorb but not reduce Cr(VI), with the adsorption amount decreasing at higher pHs. In the reaction system of manganite-goethite composites and Cr(VI), adsorbed Cr(VI) was reduced to Cr(III) by Fe(II) on composites surface. The generated Cr(III) was then retained as Cr(OH) on the mineral surface. Goethite coating suppressed the re-oxidation of newly formed Cr(III) by manganite. The amounts of adsorbed Cr(VI) and generated Cr(III) increased with increasing iron oxide content, and increased first and then decreased with increasing pH. The Cr(III) formation and Cr(VI) adsorption amount reached the maximum at pH 5.0-6.0. The present work highlights the transformation and retention of Cr(VI) by iron-manganese oxides and provides potential implications for the use of such oxides in the remediation of Cr(VI) polluted waters and soils.

摘要

六价铬因其高迁移性和毒性而引起了一系列环境问题。铁锰氧化物通常共存于环境中,并影响铬的形态和地球化学循环。然而,铁锰氧化物与溶解态 Cr(VI) 的相互作用机制在很大程度上仍不清楚。在这项工作中,研究了在针铁矿涂层存在下溶解态 Cr(VI)与软锰矿的相互作用过程,并研究了 pH 值(2.0-9.0)和氧化铁含量的影响。在软锰矿和 Fe(II) 的体系中形成了具有均匀微观形态的软锰矿-针铁矿复合材料。在单一软锰矿和 Cr(VI)的反应体系中,软锰矿只能吸附而不能还原 Cr(VI),在较高 pH 值下吸附量减少。在软锰矿-针铁矿复合材料和 Cr(VI)的反应体系中,吸附的 Cr(VI)被复合材料表面的 Fe(II)还原为 Cr(III)。生成的 Cr(III)随后作为 Cr(OH)保留在矿物表面。针铁矿涂层抑制了新形成的 Cr(III)被软锰矿的再氧化。随着氧化铁含量的增加,吸附的 Cr(VI)和生成的 Cr(III)的量增加,随着 pH 值的增加先增加后减少。在 pH 5.0-6.0 时,Cr(III)的形成和 Cr(VI)的吸附量达到最大值。本研究强调了铁锰氧化物对 Cr(VI)的转化和保留作用,为铁锰氧化物在修复 Cr(VI)污染水和土壤中的应用提供了潜在的意义。

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