Wang Hui, Liu Fengping, Zhang Yankun, Gong Xueying, Zhu Jinqi, Tan Wenbing, Yuan Ying, Zhang Jia, Chen Honghan, Xi Beidou
State Key Laboratory of Environmental Criteria and Risk Assessment, and State Environmental Protection Key Laboratory of Simulation and Control of Groundwater Pollution, Chinese Research Academy of Environmental Sciences, Beijing 100012, PR China; Beijing Key Laboratory of Water Resources & Environmental Engineering, China University of Geosciences, Beijing 100083, PR China.
Chinese Academy for Environmental Planning, Beijing 100020, PR China.
J Hazard Mater. 2024 Oct 5;478:135595. doi: 10.1016/j.jhazmat.2024.135595. Epub 2024 Aug 22.
Humic substance (HS)-ferric iron (Fe(III)) coprecipitates are widespread organo-mineral associations in soils and aquifers and have the capacity to immobilize and detoxify Cr(VI). These coprecipitates undergo transformation owing to their thermodynamic instability; however, the effects of this transformation on their environmental behaviors remain unclear, particularly in aerobic environments. In this study, the aerobic transformation of humic acid (HA)-Fe(III) coprecipitates, a representative of HS-Fe(III) coprecipitates, was simulated. The environmental effect was then evaluated after conducting an adsorption-reduction batch experiment toward Cr(VI). The aerobic transformation characteristics, as well as the adsorption/reduction capacity of HA-Fe(III) coprecipitates, were found to depend strongly on their structures. In ferrihydrite (Fh)-like coprecipitates, amorphous Fh is readily transformed into crystalline hematite and goethite at aerobic environments, leading to a much lower specific surface area and adsorption capacity. However, this increasing degree of crystallization enhanced the inductive reduction ability towards Cr(VI) owing to the more significant shift of electron pairs in the FeOC bond toward the HA direction. In HS-like coprecipitates, Fe(III) always serves as a cation bridge connecting HA molecules, but can be reduced to Fe(II) by the associated HA after aerobic transformation. The produced Fe(II), therefore, drove the reduction of the adsorbed Cr(VI). These findings emphasize the pivotal role of aerobic transformation in enhancing the reduction capacity for Cr(VI), which opens a new avenue for the development of in-situ remediation agents for Cr(VI)-contaminated sites.
腐殖质(HS)-铁(III)共沉淀物是土壤和含水层中广泛存在的有机-矿物结合体,具有固定和解毒六价铬(Cr(VI))的能力。由于其热力学不稳定性,这些共沉淀物会发生转化;然而,这种转化对其环境行为的影响仍不清楚,尤其是在有氧环境中。在本研究中,模拟了腐殖酸(HA)-铁(III)共沉淀物(HS-铁(III)共沉淀物的代表)的有氧转化。然后,在对Cr(VI)进行吸附-还原批量实验后评估环境效应。发现HA-铁(III)共沉淀物的有氧转化特性以及吸附/还原能力在很大程度上取决于其结构。在类水铁矿(Fh)共沉淀物中,无定形Fh在有氧环境中很容易转化为结晶赤铁矿和针铁矿,导致比表面积和吸附能力大大降低。然而,这种结晶程度的增加增强了对Cr(VI)的诱导还原能力,这是由于FeOC键中的电子对向HA方向发生了更显著的转移。在类HS共沉淀物中,铁(III)始终作为连接HA分子的阳离子桥,但在有氧转化后可被相关的HA还原为铁(II)。因此,产生的铁(II)推动了吸附的Cr(VI)的还原。这些发现强调了有氧转化在增强对Cr(VI)的还原能力方面的关键作用,这为开发用于修复Cr(VI)污染场地的原位修复剂开辟了一条新途径。