Impact mechanisms of humic acid on the behavior of CMC-stabilized nZVI in groundwater: Implications for long-term chlorinated contaminant remediation

文献类型： 外文期刊

第一作者： Chen, Bo

作者： Chen, Bo;Hang, Yuhan;Chen, Tianming;Chen, Bo;Cai, Shichao;Yang, Liwei;He, Feng;Chen, Bo;Cai, Shichao;Yang, Liwei;He, Feng;Chen, Bo;Cheng, Dong;Liang, Liyuan;Fan, Bo

作者机构：

关键词： Zero valent iron; Electron competition; Chlorinated hydrocarbons; Groundwater remediation; Natural organic matter

期刊名称：WATER RESEARCH （ 影响因子：12.4； 五年影响因子：12.9 ）

ISSN： 0043-1354

年卷期： 2025 年 287 卷

页码：

收录情况： SCI

摘要： Stabilized nanoscale zero valent iron (nZVI) is commonly used as a reductant during groundwater remediation of halogenated hydrocarbons. However, humic acid (HA) in groundwater can affect the environmental behavior of nZVI during contaminant degradation. This study investigated the effects of HA on carboxymethyl cellulose-stabilized nZVI (CMC-nZVI) by studying hydrogen evolution, Fe-0 corrosion and carbon tetrachloride (CT) degradation kinetics. The results show that, during the early stage (<= 24 h), low-concentration HA (HA/CMCnZVI: 2-8) enhanced the hydrogen evolution reaction (HER) of CMC-nZVI up to 1.36 fold by forming Fe2+-HA complexes that prevented passivation. In contrast, high-concentration HA (mass ratio: 24) inhibited HER during the entire reaction period, as HA rapidly and directly consumed Fe-0 from the start of the reaction (final Fe-0 consumption by HA: 62.0 %). In this study we also developed a modified differential HER approach to quantitatively determine HA-induced Fe0 consumption. This confirmed that quinone moieties in HA compete for electrons and are reduced to hydroquinones, thereby consuming Fe-0. In CT degradation, HA accelerated the initial reaction (rate constant kCT increased from 0.010 min(-1) to 0.038 min(-1)) but significantly reduced electron efficiency (from 6.4 % to 1.3 %) and material longevity at HA/CMC-nZVI ratio of 2-24. Due to HA-mediated depletion of CMC-nZVI, the residual Fe-0 had limited capacity for CT degradation after 24 h. The column experiments further confirmed this adverse effect of HA. However, the coexisting ions in actual groundwater were found to mitigate the Fe-0 consumption induced by HA. This study reveals HA's dual role in CT remediation: initially HA enhances ZVI reactivity, but subsequently HA reduces ZVI reactivity due to electron competition. This provides novel insights for the optimization of ZVI dosing in groundwater remediation.

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