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Remediation of an electroplating contaminated soil by EDTA flushing : chromium release and soil dissolution

机译:EDTA冲洗修复电镀污染的土壤:铬的释放和土壤的溶解

摘要

Purpose: Remediation of soils contaminated with Cr (as Cr(III) complexes/precipitates and/or Cr(VI) oxyanion) and cationic metals (Cu, Ni, Zn, and Pb) by ethylenediaminetetraacetate (EDTA) flushing has been challenging and rarely investigated. This study aimed to evaluate the efficiency of EDTA flushing for metal extraction of soil from an electroplating site, with a specific focus on chromium release and soil dissolution. Materials and methods: Column flushing tests were performed on a sandy soil contaminated by electroplating activities in the field. Three EDTA concentrations (5, 10, and 20 mM) and flow interruptions were employed to investigate the operation of EDTA flushing. Results and discussion: Results demonstrated that Cr, Cu, and Ni were continuously released along with dissolution of Fe, Al, Mg, and Mn throughout the entire flushing process (up to 600 pore volumes), whereas Zn and Pb removal primarily occurred in the first 50-200 pore volumes. By comparing the Cr and Fe release patterns, the observed Cr release by EDTA flushing possibly resulted from a combination of dissolution of Fe oxides, dissolution of metal-chromate precipitates, and ligand competition for the surface sites (substitution reaction). The latter two mechanisms appeared to be more influential at the early stage. It was also revealed that soil dissolution was predominant, and metal extraction became inefficient at the later stage of flushing, especially with the concentrated EDTA solution. On the other hand, when the flushing process was temporarily paused (i. e., flow interruptions), Cr, Cu, Ni, and Zn concentrations elevated, whereas Pb levels in the effluent decreased, indicating the significance of rate-limited metal exchange of newly formed metal-EDTA complexes. Conclusions: In consideration of EDTA utilization efficiency and potential ecological risks, diluted EDTA solution is recommended for field applications.
机译:目的:用乙二胺四乙酸盐(EDTA)冲洗来修复被Cr(作为Cr(III)络合物/沉淀物和/或Cr(VI)氧阴离子)和阳离子金属(Cu,Ni,Zn和Pb)污染的土壤具有挑战性,而且很少调查。这项研究旨在评估EDTA冲洗从电镀场所对土壤进行金属萃取的效率,特别关注铬的释放和土壤溶解。材料和方法:柱冲洗试验是在田间被电镀活动污染的沙质土壤上进行的。使用三种EDTA浓度(5、10和20 mM)和流动中断来研究EDTA冲洗的操作。结果与讨论:结果表明,在整个冲洗过程(最多600个孔体积)中,Cr,Cu和Ni随Fe,Al,Mg和Mn的溶解而不断释放,而Zn和Pb的去除主要发生在冲洗过程中。前50-200个孔体积。通过比较Cr和Fe的释放方式,通过EDTA冲洗观察到的Cr释放可能是由于Fe氧化物的溶解,金属铬酸盐沉淀的溶解以及配体争夺表面位点(取代反应)的综合作用。后两种机制在早期似乎更具影响力。还显示出土壤溶解是主要的,并且在冲洗的后期,尤其是使用浓EDTA溶液时,金属提取效率低下。另一方面,当冲洗过程暂时暂停(即中断流动)时,Cr,Cu,Ni和Zn浓度升高,而流出物中的Pb含量降低,这表明新形成的限速金属交换的重要性金属-EDTA配合物。结论:考虑到EDTA的利用效率和潜在的生态风险,建议将EDTA稀释液用于现场应用。

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