Chen Bo, Cai Shichao, Yang Liwei, Cheng Dong, Hang Yuhan, Liang Liyuan, Fan Bo, Chen Tianming, He Feng
School of Environmental Science and Engineering, Yancheng Institute of Technology, Yancheng, Jiangsu 224051, China; Institute of Environmental Processes and Pollution Control, and School of Environment and Civil Engineering, Jiangnan University, Wuxi, Jiangsu 214122, China; College of Environment, Zhejiang University of Technology, Hangzhou 310014, China.
Institute of Environmental Processes and Pollution Control, and School of Environment and Civil Engineering, Jiangnan University, Wuxi, Jiangsu 214122, China.
Water Res. 2025 Aug 5;287(Pt A):124335. doi: 10.1016/j.watres.2025.124335.
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 corrosion and carbon tetrachloride (CT) degradation kinetics. The results show that, during the early stage (≤ 24 h), low-concentration HA (HA/CMC-nZVI: 2-8) enhanced the hydrogen evolution reaction (HER) of CMC-nZVI up to 1.36 fold by forming Fe-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 from the start of the reaction (final Fe consumption by HA: 62.0 %). In this study we also developed a modified differential HER approach to quantitatively determine HA-induced Fe consumption. This confirmed that quinone moieties in HA compete for electrons and are reduced to hydroquinones, thereby consuming Fe. In CT degradation, HA accelerated the initial reaction (rate constant k increased from 0.010 min to 0.038 min) 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 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 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.
