Gao Yining, Liu Ning, Meng Fangyuan, Dong Leheng, Fei Zhijun, Chen Manjia, Liu Chengshuai, Wu Pan, Tong Hui
College of Resources and Environmental Engineering, Guizhou University, Guiyang 550025, Guizhou, China.
National-Regional Joint Engineering Research Center for Soil Pollution Control and Remediation in South China, Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management, Institute of Eco-environmental Science and Technology, Guangdong Academy of Sciences, Guangzhou 510650, China; School of Geography, South China Normal University, Guangzhou 510631, China.
Water Res. 2025 Sep 1;283:123840. doi: 10.1016/j.watres.2025.123840. Epub 2025 May 16.
The ubiquitous hydrolysis of Fe(III) ions in nature leads to the formation of ferrihydrite (Fh), which then undergoes solid-state transformation into crystalline mineral phases. However, the impact of this process on the geochemical fate of cadmium (Cd) in aquatic environments is not yet fully understood. This investigation systematically examined the partitioning mechanisms of Cd during the aforementioned processes through extraction techniques and multiple characterization methodologies. The experimental results demonstrated that Fe(III) ions first undergo the diffusion-limited aggregation (DLA) stage, forming loosely bound clusters with high Cd co-precipitation capacity. Upon transitioning to the reaction-limited aggregation (RLA) stage, Fe clusters exhibit increased structural complexity, wherein the expansion of radius of gyration predominantly governs Cd retention. As colloidal Fh develops, surface adsorption becomes the predominant mechanism for Cd sequestration. Throughout solid-state transformation in systems containing 1 mol% Cd, dehydroxylation processes induced acidification, facilitating the progressive liberation of Cd. Conversely, in systems with 10 mol% Cd, significant Cd incorporation induces distortion in the crystalline lattice structure, promoting system alkalinization and, consequently, enhancing Cd immobilization. pH gradient solid-state transformation experiments demonstrated that when initial pH values were below 8, final pH measurements were significantly lower than initial values, and vice versa. pH conditions potentially regulate the speciation of Fe within Fh, ultimately exerting substantial influence on Cd partitioning behavior. In summary, Fh formation beneficially stabilizes Cd, while its subsequent solid-state transformation triggers Cd redistribution.
自然界中普遍存在的铁(III)离子水解导致了水铁矿(Fh)的形成,然后水铁矿经历固态转变形成结晶矿物相。然而,这一过程对水生环境中镉(Cd)地球化学归宿的影响尚未完全明确。本研究通过萃取技术和多种表征方法系统地研究了上述过程中镉的分配机制。实验结果表明,铁(III)离子首先经历扩散限制聚集(DLA)阶段,形成具有高镉共沉淀能力的松散结合簇。在转变为反应限制聚集(RLA)阶段时,铁簇的结构复杂性增加,其中回转半径的扩大主要控制着镉的保留。随着胶体Fh的形成,表面吸附成为镉螯合的主要机制。在含有1 mol%镉的体系中进行固态转变时,脱羟基过程引发酸化,促进镉的逐步释放。相反,在含有10 mol%镉的体系中,大量镉的掺入导致晶格结构变形,促进体系碱化,从而增强镉的固定。pH梯度固态转变实验表明,当初始pH值低于8时,最终pH测量值显著低于初始值,反之亦然。pH条件可能调节Fh中铁的形态,最终对镉的分配行为产生重大影响。总之,Fh的形成有利于稳定镉,而其随后的固态转变引发镉的重新分布。