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草酸修饰的零价铁负载生物炭对 Cr(VI) 污染土壤的强化修复

Enhanced remediation of Cr(VI)-contaminated soil by modified zero-valent iron with oxalic acid on biochar.

作者信息

Xie Lihong, Chen Qingjun, Liu Yiyang, Ma Qiyan, Zhang Jinlan, Tang Chenliu, Duan Guilan, Lin Aijun, Zhang Tingting, Li Shangyi

机构信息

Department of Environmental Science and Engineering, College of Chemical Engineering, Beijing University of Chemical Technology, Beijing 100029, China.

China National Petroleum and Chemical Planning Institute, Beijing 100013, China.

出版信息

Sci Total Environ. 2023 Dec 20;905:167399. doi: 10.1016/j.scitotenv.2023.167399. Epub 2023 Oct 2.

Abstract

Hexavalent chromium (Cr(VI)) is carcinogenic and widely presented in soil. In this study, modified zero-valent iron (ZVI) with oxalic acid on biochar (OA-ZVI/BC) was prepared using wet ball milling method for the remediation of Cr(VI)-contaminated soil. Microscopic characterizations showed that ZVI were distributed on the biochar uniformly and confirmed the enhanced interface interaction between biochar and ZVI by wet ball milling. Electrochemical analysis indicated the strong electron transfer ability and enhanced corrosion behavior of OA-ZVI/BC. Moreover, inhibitory efficiencies of Cr(VI) removal with the addition of 1,10-phenanthroline suggested abundant Fe generation in OA-ZVI/BC, which might facilitate the reduction of Cr(VI) to Cr(III). Theory calculation further demonstrated the ZVI modified by oxalic acid was more susceptible to solid-solid interfacial reactions with Cr(VI), and more electrons were transferred to Cr(VI). When applied to Cr(VI)-contaminated soil, OA-ZVI/BC could passivate 96.7 % total Cr(VI) and maintained for 90 days. The toxicity characteristic leaching procedure (TCLP) and simple based extraction test (SBET) were used to evaluate the leaching toxicity and bioaccessibility of Cr(VI), respectively. The TCLP-Cr(VI) decreased to 0.11 mg·L after OA-ZVI/BC treatment, much lower than that of soils with ZVI/BC and OA-ZVI remediation (1.5 mg·L and 4.1 mg·L). The bioaccessibility of Cr(VI) reduced by 93.5 % after 3-month remediation. Sequential extraction showed that Cr fractions in the soil after OA-ZVI/BC remediation was converted from acetic acid-extractable (HOAc-extractable) to more stable forms (e.g., residual and oxidizable forms). Benefiting from the synergies of oxalic acid, biochar and wet ball milling, OA-ZVI/BC exhibited an excellent performance on the remediation of Cr(VI)-contaminated soil, whose mechanisms involved adsorption, reduction (Fe/Fe, Fe/Fe) and co-precipitation. This study herein develops a promising ZVI technology in the remediation of heavy metal-contaminated soil.

摘要

六价铬(Cr(VI))具有致癌性,在土壤中广泛存在。本研究采用湿球磨法制备了负载于生物炭上的草酸改性零价铁(OA-ZVI/BC),用于修复Cr(VI)污染土壤。微观表征显示,零价铁均匀分布于生物炭上,证实了通过湿球磨增强了生物炭与零价铁之间的界面相互作用。电化学分析表明OA-ZVI/BC具有较强的电子转移能力和增强的腐蚀行为。此外,添加1,10-菲啰啉后对Cr(VI)的去除抑制效率表明OA-ZVI/BC中产生了大量的铁,这可能有助于将Cr(VI)还原为Cr(III)。理论计算进一步证明,经草酸改性的零价铁更容易与Cr(VI)发生固-固界面反应,有更多电子转移至Cr(VI)。当应用于Cr(VI)污染土壤时,OA-ZVI/BC可钝化96.7%的总Cr(VI),并保持90天。毒性特性浸出程序(TCLP)和简单碱提取试验(SBET)分别用于评估Cr(VI)的浸出毒性和生物可利用性。经OA-ZVI/BC处理后,TCLP-Cr(VI)降至0.11 mg·L,远低于采用ZVI/BC和OA-ZVI修复的土壤(分别为1.5 mg·L和4.1 mg·L)。经过3个月的修复,Cr(VI)的生物可利用性降低了93.5%。连续提取表明,OA-ZVI/BC修复后土壤中的Cr形态从醋酸可提取态(HOAc-可提取态)转化为更稳定的形态(如残渣态和可氧化态)。得益于草酸、生物炭和湿球磨的协同作用,OA-ZVI/BC在修复Cr(VI)污染土壤方面表现出优异性能,其作用机制包括吸附、还原(Fe/Fe、Fe/Fe)和共沉淀。本研究开发了一种在修复重金属污染土壤方面具有前景的零价铁技术。

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