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EDTA 洗脱对土壤中重金属残留形态和迁移性的影响。

Influence of EDTA washing on the species and mobility of heavy metals residual in soils.

机构信息

School of Environmental Science and Engineering, Sun Yat-sen University, University Town, Guangzhou 510006, China.

出版信息

J Hazard Mater. 2010 Jan 15;173(1-3):369-76. doi: 10.1016/j.jhazmat.2009.08.087. Epub 2009 Aug 25.

DOI:10.1016/j.jhazmat.2009.08.087
PMID:19748734
Abstract

Aiming to estimate the potential risk of ethylenediaminetetraacetic acid (EDTA)-enhanced soil washing, the heavy metal species and their mobility in the washed soil under different combinations were investigated by batch leaching tests and the sequential extraction procedure. Results demonstrate that the metal removal efficiency was rather low (less than 12%), partially due to the significant Ca dissolution and strong bonding between metals and the soil as well as the insufficient EDTA dosage. The washing combination of 0.0005 M EDTA and half-an-hour washing can enhance the instant mobility of Ni, Zn and Pb possibly owing to the slow detachment of EDTA-destabilized metals. Metal fractionation also exhibits the corresponding increase in their labile exchangeable fractions. Therefore, a more concentrated EDTA solution for a longer duration often decreased their mobility. The increase in some fractions of a curtain metal implies the redistribution of this metal during the EDTA soil washing. The pathway of such a redistribution may vary for different metals, but the redistribution to organic matter is often a slow process, while that to carbonates or Fe/Mn oxides is a faster one and even may occur in a half hour washing with 0.0005 M EDTA solution. These redistribution processes may also increase the metal chemical availability. Therefore, we should prudently control the chelating reagent concentration and washing duration to finally minimize the mobility and availability of the remaining heavy metals when designing the soil washing for the remediation of metal-contaminated soils.

摘要

为了评估乙二胺四乙酸(EDTA)强化土壤洗脱的潜在风险,通过批式浸出试验和连续提取程序研究了不同组合下洗脱土壤中重金属的形态及其迁移性。结果表明,金属去除效率相当低(低于 12%),部分原因是 Ca 的大量溶解以及金属与土壤之间的强结合作用,以及 EDTA 用量不足。由于 EDTA 不稳定的金属缓慢脱落,0.0005 M EDTA 和半小时洗脱的组合可能会增强 Ni、Zn 和 Pb 的瞬时迁移性。金属形态也表现出其可交换态分数相应增加。因此,较长时间使用浓度较高的 EDTA 溶液通常会降低其迁移性。一些金属的某些形态分数增加表明,在 EDTA 土壤洗脱过程中,这种金属发生了再分配。这种再分配的途径可能因金属而异,但向有机物的再分配通常是一个缓慢的过程,而向碳酸盐或 Fe/Mn 氧化物的再分配则较快,甚至可能在 0.0005 M EDTA 溶液半小时的洗脱中发生。这些再分配过程也可能增加金属的化学可利用性。因此,在设计用于修复重金属污染土壤的土壤洗脱时,我们应谨慎控制螯合剂浓度和洗脱时间,以最终最小化剩余重金属的迁移性和可利用性。

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