Critical role of soil-applied molybdenum dioxide composite biochar material in enhancing Cr(VI) remediation process: The driver of Fe(III)/Fe(II) redox cycle.

IF 8 2区 环境科学与生态学 Q1 ENVIRONMENTAL SCIENCES
Mingxuan Liu, Heng Li, Qiang Fu, Tianxiao Li, Renjie Hou, Ping Xue, Xuechen Yang, Mo Li, Dong Liu
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引用次数: 0

Abstract

Heavy metal contamination of agricultural land due to sewage irrigation, over-application of fertilizers and pesticides, and industrial activities. Biochar, due to its rich functional groups and excellent electrochemical performance, is used for the remediation of heavy metal-contaminated farmland. However, the remediation mechanism remains uncertain due to the influence of minerals and multi-element composite pollution on soil. Therefore, introducing transition metal oxide MoO2 to prepare biochar composite remediation materials enhances the adsorption and reduction of soil Cr (Ⅵ). This study compared the differences in Cr (Ⅵ) improvement under different pollution systems and pH conditions and explored the potential mechanism of Fe (Ⅲ)/Fe (Ⅱ) redox cycling in Cr (Ⅵ) remediation. The results showed that both biochar MoO2 ball-milling composite (BC + M) and biochar-loaded MoO2 (BC/M) retained the original biochar (BC) remediation method for Cr (Ⅵ). Among them, the remediation of BC/M was the most stable, with the maximum remediation value ranging from approximately 6.52 to 58.58 mg/kg. In different pollution systems, Cd and Pb exhibited competitive adsorption toward Cr (Ⅵ), but they enhanced Cr (Ⅵ) remediation by promoting adsorption and self-complexation. In acidic conditions (pH = 4), BC/M showed the best remediation effect, with a reduction kinetic constant of 34.61 × 10-3 S-1 and a maximum adsorption capacity of 61.64 mg/g. Fe (Ⅲ)/Fe (Ⅱ) redox cycling accelerated the reduction of Cr (Ⅵ) (R2 = 0.81), and MoO2 promoted the Fe (Ⅲ)/Fe (Ⅱ) redox cycle. BC/M enhanced the Fe (Ⅱ) formation efficiency by 66.39% and 71.81% compared to BC + M and BC at pH = 4. The introduction of MoO2 and biochar composite materials enhanced the reduction process of Cr (Ⅵ), with BC/M achieving the optimal remediation level. This study reveals the potential mechanisms of MoO2 and biochar composite materials in soil Cr (Ⅵ) remediation, providing a reference and insight for the preparation of Cr (Ⅵ) remediation materials and the treatment of contaminated farmland.

土壤施用二氧化钼复合生物炭材料在增强六价铬修复过程中的关键作用:铁(III)/铁(II)氧化还原循环的驱动力。
由于污水灌溉、过度施用化肥和杀虫剂以及工业活动,农田受到重金属污染。生物炭因其丰富的功能基团和优异的电化学性能,被用于重金属污染农田的修复。然而,由于矿物质和多元素复合污染对土壤的影响,其修复机制仍不确定。因此,引入过渡金属氧化物 MoO2 制备生物炭复合修复材料,可增强对土壤中 Cr(Ⅵ)的吸附和还原作用。本研究比较了在不同污染体系和 pH 值条件下,铬(Ⅵ)改善效果的差异,并探讨了铁(Ⅲ)/铁(Ⅱ)氧化还原循环在铬(Ⅵ)修复中的潜在机制。结果表明,生物炭 MoO2 球磨复合材料(BC + M)和生物炭负载 MoO2(BC/M)均保留了原有的生物炭(BC)对铬(Ⅵ)的修复方法。其中,BC/M 的修复效果最为稳定,最大修复值约为 6.52 至 58.58 mg/kg。在不同的污染体系中,镉和铅对铬(Ⅵ)表现出竞争性吸附,但它们通过促进吸附和自络合增强了铬(Ⅵ)的修复效果。在酸性条件下(pH = 4),BC/M 的修复效果最好,其还原动力学常数为 34.61 × 10-3 S-1,最大吸附容量为 61.64 mg/g。铁(Ⅲ)/铁(Ⅱ)氧化还原循环加速了铬(Ⅵ)的还原(R2 = 0.81),MoO2 促进了铁(Ⅲ)/铁(Ⅱ)氧化还原循环。与 BC + M 和 BC(pH = 4)相比,BC/M 可使 Fe(Ⅱ)的形成效率分别提高 66.39% 和 71.81%。二氧化锰和生物炭复合材料的引入增强了铬(Ⅵ)的还原过程,其中 BC/M 达到了最佳修复水平。该研究揭示了二氧化锰和生物炭复合材料在土壤铬(Ⅵ)修复中的潜在机理,为制备铬(Ⅵ)修复材料和处理受污染的农田提供了参考和启示。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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来源期刊
Journal of Environmental Management
Journal of Environmental Management 环境科学-环境科学
CiteScore
13.70
自引率
5.70%
发文量
2477
审稿时长
84 days
期刊介绍: The Journal of Environmental Management is a journal for the publication of peer reviewed, original research for all aspects of management and the managed use of the environment, both natural and man-made.Critical review articles are also welcome; submission of these is strongly encouraged.
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