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土壤 pH 值对铬(III)的迁移、形态和氧化的影响。

Effect of soil pH on the transport, fractionation, and oxidation of chromium(III).

机构信息

Key Laboratory of Leather Chemistry and Engineering of Ministry of Education, Sichuan University, Chengdu, 610065, China.

National Engineering Laboratory for Clean Technology of Leather Manufacture, Sichuan University, Chengdu, 610065, China.

出版信息

Ecotoxicol Environ Saf. 2020 Jun 1;195:110459. doi: 10.1016/j.ecoenv.2020.110459. Epub 2020 Mar 14.

DOI:10.1016/j.ecoenv.2020.110459
PMID:32182533
Abstract

This work was conducted to study the effect of soil pH (4.0, 6.0, and 8.0) on the transport, fractionation, and oxidation of trivalent chromium [Cr(III)]. Variation in pH altered soil chemical and mineralogical properties such as zeta potential, cation exchange capacity and redox potential of natural soil. Breakthrough curves and batch sorption experiments coupled with fourier transform infrared spectroscopy (FTIR) and X-ray photoelectron spectroscopy (XPS) analyses demonstrated that the easy mobility of Cr(III) in pH 4.0 soil was dominated by the limited coordination effect. The high retention of Cr(III) in pH 8.0 soil was mainly ascribed to the hydrolysis. Incubation experiments indicated that the proportions of Cr in exchangeable fraction decreased with increasing of soil pH and incubation time, and kinetics analysis revealed that the time dependent transformation was controlled by mass transfer and chemical processes (e.g., hydrolysis, ion association). The XPS confirmed the oxidation of Cr(III) in pH 8.0 soil during the incubation period. Furthermore, the content of toxic hexavalent chromium [Cr(VI)] was positively associated with time and initial concentration of Cr(III) released. These results revealed the hazardousness of Cr(III) in soil contaminated simultaneously by inorganic acid and alkali.

摘要

这项工作旨在研究土壤 pH 值(4.0、6.0 和 8.0)对三价铬[Cr(III)]的迁移、形态和氧化的影响。pH 值的变化改变了土壤的化学和矿物性质,如动电电位、阳离子交换容量和自然土壤的氧化还原电位。穿透曲线和批式吸附实验结合傅里叶变换红外光谱(FTIR)和 X 射线光电子能谱(XPS)分析表明,Cr(III)在 pH 4.0 土壤中的易迁移性主要受有限配位效应的控制。Cr(III)在 pH 8.0 土壤中的高保留主要归因于水解作用。培养实验表明,随着土壤 pH 值和培养时间的增加,可交换态 Cr 的比例减少,动力学分析表明,时间依赖性转化受传质和化学过程(如水解、离子缔合)控制。XPS 证实了在培养过程中 pH 8.0 土壤中 Cr(III)的氧化。此外,有毒六价铬[Cr(VI)]的含量与释放的 Cr(III)的初始浓度和时间呈正相关。这些结果揭示了同时受到无机酸和碱污染的土壤中 Cr(III)的危害性。

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