Xu Fei, Li Peiyue, He Qiang, Ning Jing, Li Xiaofei
School of Water and Environment, Chang'an University, No. 126 Yanta Road, Xi'an 710054, Shaanxi, China; Key Laboratory of Subsurface Hydrology and Ecological Effects in Arid Region of the Ministry of Education, Chang'an University, No. 126 Yanta Road, Xi'an 710054, Shaanxi, China; Key Laboratory of Eco-hydrology and Water Security in Arid and Semi-arid Regions of the Ministry of Water Resources, Chang'an University, No. 126 Yanta Road, Xi'an 710054, Shaanxi, China.
School of Water and Environment, Chang'an University, No. 126 Yanta Road, Xi'an 710054, Shaanxi, China; Key Laboratory of Subsurface Hydrology and Ecological Effects in Arid Region of the Ministry of Education, Chang'an University, No. 126 Yanta Road, Xi'an 710054, Shaanxi, China; Key Laboratory of Eco-hydrology and Water Security in Arid and Semi-arid Regions of the Ministry of Water Resources, Chang'an University, No. 126 Yanta Road, Xi'an 710054, Shaanxi, China.
J Contam Hydrol. 2025 Nov;275:104677. doi: 10.1016/j.jconhyd.2025.104677. Epub 2025 Jul 19.
Iron (Fe) and manganese (Mn) are key redox-sensitive elements in soil-groundwater systems, and their primary environmental risk lies in their ability to influence the mobilization and release of co-occurring hazardous contaminants, such as arsenic. Previous studies have primarily focused on variations in aqueous-phase concentrations of Fe/Mn. However, under fluctuating groundwater conditions, the dynamic transformation mechanisms of different forms of Fe/Mn in soil remain underexplored. This study addressed this gap by employing dynamic groundwater table simulation experiments. The responses of various forms of Fe and Mn in the soil to fluctuations in groundwater levels were investigated and quantitatively evaluated the contribution ratios of different Fe/Mn forms to geochemical processes. The results show that a decrease in the groundwater table increases the redox potential (Eh), creating an oxidative environment that promotes the enrichment of oxide-bound iron/manganese (Ox-Fe/Mn) and a reduction in organic matter-bound iron/manganese (Om-Fe/Mn). For Fe, only the Ox-Fe and Om-Fe forms are affected by groundwater level fluctuations, while the exchangeable form (EXC-Fe) and carbonate-bound form (Carb-Fe) remain at a low level with insignificant changes. However, all four forms of Mn change significantly with the groundwater level fluctuations. Quantitative analysis revealed that redox processes involving Ox-Fe/Mn are the primary drivers of Fe/Mn cycling in the soil-groundwater system, contributing more than 50 % on average. This research provides key insights into the fate and transformation of Fe and Mn in soil and aims to assess their potential environmental risks.
铁(Fe)和锰(Mn)是土壤 - 地下水系统中对氧化还原敏感的关键元素,它们主要的环境风险在于其影响同时存在的有害污染物(如砷)的迁移和释放的能力。以往的研究主要集中在铁/锰水相浓度的变化上。然而,在地下水位波动的情况下,土壤中不同形态铁/锰的动态转化机制仍未得到充分研究。本研究通过进行动态地下水位模拟实验填补了这一空白。研究了土壤中各种形态的铁和锰对地下水位波动的响应,并定量评估了不同铁/锰形态对地球化学过程的贡献率。结果表明,地下水位下降会增加氧化还原电位(Eh),形成一个促进氧化物结合铁/锰(Ox - Fe/Mn)富集并减少有机质结合铁/锰(Om - Fe/Mn)的氧化环境。对于铁而言,只有Ox - Fe和Om - Fe形态受地下水位波动影响,而可交换态(EXC - Fe)和碳酸盐结合态(Carb - Fe)保持在较低水平且变化不显著。然而,锰的所有四种形态都随地下水位波动而显著变化。定量分析表明,涉及Ox - Fe/Mn的氧化还原过程是土壤 - 地下水系统中铁/锰循环的主要驱动力,平均贡献率超过50%。本研究为土壤中铁和锰的归宿与转化提供了关键见解,并旨在评估它们潜在的环境风险。