College of Geo-Exploration Science and Technology, Jilin University, Changchun, 130026, China.
Key Laboratory of Geochemical Exploration, Institute of Geophysical and Geochemical Exploration, CAGS, Langfang, 065000, Hebei, China.
Environ Geochem Health. 2024 Aug 21;46(10):373. doi: 10.1007/s10653-024-02153-6.
Combined electrokinetic remediation employing reducing agents represents an extensively utilized approach for the remediation of hexavalent chromium (Cr(VI))-contaminated soil. In this investigation, electrokinetic remediation of artificially contaminated kaolin was conducted utilizing a separate circulation system for the anolyte, with a 0.5M solution of acetic acid (HAc) as the electrolyte and foamed iron serving as the anode. The experimental outcomes demonstrated that employing HAc as the electrolyte enhances the electromigration of Cr(VI) and establishes an acidic milieu conducive to the reduction of Cr(VI) by foamed iron, thereby facilitating the rapid reduction of Cr(VI) accumulated in the anolyte through electrokinetic remediation. In the self-prepared contaminated kaolin, the initial concentration of Cr(VI) was 820.26 mg/L. Following the remediation process under optimal experimental conditions, the concentration was significantly reduced to 11.6 mg/L, achieving a removal efficiency of Cr(VI) in the soil of 98.59%. In the optimal experimental setup, the Cr(VI) concentration in the anolyte was reduced to 0.05 mg/L, which is below the EPA's Safe Drinking Water Act standard for Cr(VI) content of 0.1 mg/L. The removal mechanism of Cr(VI) from the electrolyte primarily involves reduction, precipitation, and co-precipitation, with the foamed iron playing a predominant role. HAc and foamed iron exhibit a synergistic effect. The findings of this study substantiate that the integration of foamed iron with HAc is efficacious for the electrokinetic remediation of soil contaminated with Cr(VI).
采用还原剂的联合电动修复方法是修复六价铬(Cr(VI))污染土壤的一种广泛应用的方法。本研究采用单独的阳极电解液循环系统对人工污染高岭土进行电动修复,以 0.5M 乙酸(HAc)溶液作为电解液,泡沫铁作为阳极。实验结果表明,采用 HAc 作为电解液可以增强 Cr(VI)的电迁移,并建立有利于泡沫铁还原 Cr(VI)的酸性环境,从而促进通过电动修复快速还原在阳极电解液中积累的 Cr(VI)。在自制备的污染高岭土中,Cr(VI)的初始浓度为 820.26mg/L。在最优实验条件下进行修复过程后,浓度显著降低至 11.6mg/L,土壤中 Cr(VI)的去除效率达到 98.59%。在最优实验条件下,阳极电解液中的 Cr(VI)浓度降低至 0.05mg/L,低于 EPA 规定的 Cr(VI)含量为 0.1mg/L 的安全饮用水法案标准。从电解液中去除 Cr(VI)的主要机制包括还原、沉淀和共沉淀,泡沫铁起主要作用。HAc 和泡沫铁具有协同作用。本研究结果证实,将泡沫铁与 HAc 结合用于电动修复 Cr(VI)污染土壤是有效的。