多层复合土壤电动力除铬过程中铬的转化和辅助提取。

IF 3.2 3区 环境科学与生态学 Q3 ENGINEERING, ENVIRONMENTAL Environmental Geochemistry and Health Pub Date : 2024-09-24 DOI:10.1007/s10653-024-02242-6
Junnian Wu, Ziwei Lv, Zongqian Zheng, Yupeng Fu, Jiang Li
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引用次数: 0

摘要

提出了多层复合土壤室来提取污染场地土壤中的铬,并深入研究了与价态相关的铬分馏转化。研究了电流、土壤 pH 值和含水量的变化,以及铬分馏的迁移和铬的再分布。结果表明,半峰值电流的持续时间可用于调整处理时间,而且在不同的复合方式中,半峰值电流的持续时间是不同的。此外,使用柠檬酸时,阴极附近土壤中铬的提取效率相对较高,达到 60%。柠檬酸可以促进不同的铬分馏或不同价态之间的转化。柠檬酸还能改善铬的解吸,同时防止水分含量的过度波动。萃取后,铬在土壤室中重新分布。使用去离子水时,六价铬主要以可交换分馏(EXC)的形式向阳极迁移,而铁锰氧化物分馏(Fe-Mn)则可能以阳离子三价铬氢氧化物的形式向阴极迁移。使用柠檬酸时,难以迁移的铬分馏,特别是场地土壤中的铁锰分馏,可以被激活,成为 EXC 和碳酸盐分馏(CAR),然后迁移到阳极或阴极。可交换铬(III)的迁移显著增强。但柠檬酸的使用会导致六价铬在阳极附近转化为三价铬。此外,在迁移过程中,EXC 可能会再次回到铁-锰或转化为残留物分馏(RES)。
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A transformation and auxiliary extraction of Cr during electrokinetic removal of Cr-contaminated multilayer composite soil chamber.

Multilayer composite soil chamber was proposed to extract the Cr of contaminated site soil and insight into transformation of Cr fractionation associated with valence states. The variations of current, soil pH and moisture content were explored, as well as the migration of Cr fractionation and redistribution of Cr. Results indicated that duration of half peak current could be used to adjust treatment time and it varied among different composite ways. Moreover, extraction efficiency of Cr in soil near cathode was relatively higher and reached 60% when citric acid was used. Citric acid could promote the transformation between different Cr fractionations or different valence states. It could also improve the desorption of Cr, and could prevent excessive fluctuations of moisture content at the same time. Cr redistributed acrossed the soil chamber after extraction. When deionized water was used, Cr(VI) significantly migrated toward anode mainly in the form of exchangeable fractionation (EXC) while Fe-Mn oxides fractionation (Fe-Mn) which may be in the form of cationic Cr(III) hydroxides migrated toward cathode. When using citric acid, fractionations that were difficult to migrate of Cr, especially for Fe-Mn in site soils could be activated and became EXC and carbonate fractionation (CAR), then migrated to the anode or cathode. The migration of exchangeable Cr(III) was dramatically enhanced. But the use of citric acid could cause Cr(VI) transformation to Cr(III) near anode. In addition, during the migration process, EXC could go back to Fe-Mn again or transform to residue fractionation (RES).

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来源期刊
Environmental Geochemistry and Health
Environmental Geochemistry and Health 环境科学-工程:环境
CiteScore
8.00
自引率
4.80%
发文量
279
审稿时长
4.2 months
期刊介绍: Environmental Geochemistry and Health publishes original research papers and review papers across the broad field of environmental geochemistry. Environmental geochemistry and health establishes and explains links between the natural or disturbed chemical composition of the earth’s surface and the health of plants, animals and people. Beneficial elements regulate or promote enzymatic and hormonal activity whereas other elements may be toxic. Bedrock geochemistry controls the composition of soil and hence that of water and vegetation. Environmental issues, such as pollution, arising from the extraction and use of mineral resources, are discussed. The effects of contaminants introduced into the earth’s geochemical systems are examined. Geochemical surveys of soil, water and plants show how major and trace elements are distributed geographically. Associated epidemiological studies reveal the possibility of causal links between the natural or disturbed geochemical environment and disease. Experimental research illuminates the nature or consequences of natural or disturbed geochemical processes. The journal particularly welcomes novel research linking environmental geochemistry and health issues on such topics as: heavy metals (including mercury), persistent organic pollutants (POPs), and mixed chemicals emitted through human activities, such as uncontrolled recycling of electronic-waste; waste recycling; surface-atmospheric interaction processes (natural and anthropogenic emissions, vertical transport, deposition, and physical-chemical interaction) of gases and aerosols; phytoremediation/restoration of contaminated sites; food contamination and safety; environmental effects of medicines; effects and toxicity of mixed pollutants; speciation of heavy metals/metalloids; effects of mining; disturbed geochemistry from human behavior, natural or man-made hazards; particle and nanoparticle toxicology; risk and the vulnerability of populations, etc.
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