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铁锰改性生物炭用于协同稳定冶炼厂污染土壤中的锑和砷

Iron-Manganese-Modified Hydrochar for Synergistic Stabilization of Antimony and Arsenic in Smelter-Impacted Soils.

作者信息

Wang Junhuan, Geng Yue, Hou Hong, Li Xianjun

机构信息

State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China.

Fujian Key Laboratory of Toxicant and Drug Toxicology, Medical College, Ningde Normal University, Ningde 352100, China.

出版信息

Toxics. 2025 Aug 10;13(8):674. doi: 10.3390/toxics13080674.

Abstract

Soil co-contamination with antimony (Sb) and arsenic (As) presents significant ecological and human health risks, demanding effective stabilization solutions. This study evaluated iron-manganese-modified hydrochar (FMHC) for synergistic Sb-As stabilization in contaminated smelter soils. Through 60-day natural aging and 30 accelerated aging cycles, we assessed stabilization performance using toxicity leaching tests (acid/water/TCLP), bioavailable fraction analysis, bioaccessibility assessment, and Wenzel sequential extraction. The key findings reveal that FMHC (5 wt%) achieves durable stabilization: (1) leaching concentrations remained stable post-aging (Sb: 0.3-4.5 mg·L, >70% stabilization; As: <0.4 mg·L, >94% stabilization); (2) bioavailable fractions showed maximum reductions of 64% (Sb) and 53% (As), though with some fluctuation; and (3) bioaccessible As was consistently reduced (55-77%), while Sb exhibited greater variability (maximum 58% reduction). Speciation analysis revealed similar stabilization pathways: Sb stabilization resulted from decreased non-specifically and specifically adsorbed fractions, while As stabilization involved the reduction in non-specifically/specifically adsorbed and amorphous to poorly crystalline Fe/Al hydrous oxide-bound fractions. These transformation mechanisms explain FMHC's superior performance in converting labile Sb/As into stable forms, offering a sustainable solution for the green remediation of Sb-As co-contaminated soils in mining areas.

摘要

土壤中锑(Sb)和砷(As)的共同污染带来了重大的生态和人类健康风险,需要有效的稳定化解决方案。本研究评估了铁锰改性生物炭(FMHC)对冶炼厂污染土壤中锑和砷的协同稳定作用。通过60天的自然老化和30个加速老化周期,我们使用毒性浸出试验(酸/水/TCLP)、生物可利用部分分析、生物可及性评估和温泽尔连续萃取法评估了稳定化性能。主要研究结果表明,5%(重量)的FMHC实现了持久的稳定化:(1)老化后浸出浓度保持稳定(Sb:0.3 - 4.5 mg·L,稳定率>70%;As:<0.4 mg·L,稳定率>94%);(2)生物可利用部分最大减少了64%(Sb)和53%(As),不过有一些波动;(3)生物可及性砷持续减少(55 - 77%),而锑的变化更大(最大减少58%)。形态分析揭示了类似的稳定化途径:锑的稳定化是由于非特异性和特异性吸附部分减少,而砷的稳定化涉及非特异性/特异性吸附以及无定形到结晶度差的铁/铝水合氧化物结合部分的减少。这些转化机制解释了FMHC在将不稳定的锑/砷转化为稳定形式方面的卓越性能,为矿区锑 - 砷共同污染土壤的绿色修复提供了可持续的解决方案。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/95ff/12390139/a6aac182aa7c/toxics-13-00674-g001.jpg

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