Key Lab of Pollution Control and Ecosystem Restoration in Industry Clusters, Ministry of Education, School of Environment and Energy, South China University of Technology, Guangzhou 510006, PR China.
State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Sciences, Guiyang 550081, PR China.
Water Res. 2024 Oct 1;263:122195. doi: 10.1016/j.watres.2024.122195. Epub 2024 Jul 31.
Iron minerals in nature are pivotal hosts for heavy metals, significantly influencing their geochemical cycling and eventual fate. It is generally accepted that, vivianite, a prevalent iron phosphate mineral in aquatic and terrestrial environments, exhibits a limited capacity for adsorbing cationic heavy metals. However, our study unveils a remarkable phenomenon that the synergistic interaction between sulfide (S) and vivianite triggers an unexpected sulfidation-reoxidation process, enhancing the immobilization of heavy metals such as cadmium (Cd), copper (Cu), and zinc (Zn). For instance, the combination of vivianite and S boosted the removal of Cd from the aqueous phase under anaerobic conditions, and ensured the retention of Cd stabilized in the solid phase when shifted to aerobic conditions. It is intriguing to note that no discrete FeS formation was detected in the sulfidation phase, and the primary crystal structure of vivianite largely retained its integrity throughout the whole process. Detailed molecular-level investigations indicate that sulfidation predominantly targets the Fe(II) sites at the corners of the PO4 tetrahedron in vivianite. With the transition to aerobic conditions, the exothermic oxidation of CdS and the S sites in vivianite initiates, rendering it thermodynamically favorable for Cd to form multidentate coordination structures, predominantly through the Cd-O-P and Cd-O-Fe bonds. This mechanism elucidates how Cd is incorporated into the vivianite structure, highlighting a novel pathway for heavy metal immobilization via the sulfidation-reoxidation dynamics in iron phosphate minerals.
自然界中的铁矿物是重金属的主要宿主,显著影响着它们的地球化学循环和最终归宿。普遍认为,蓝铁矿是水相和土壤相中普遍存在的一种铁磷酸盐矿物,对阳离子重金属的吸附能力有限。然而,我们的研究揭示了一个显著的现象,即硫化物(S)与蓝铁矿之间的协同相互作用引发了出乎意料的硫化-再氧化过程,增强了重金属如镉(Cd)、铜(Cu)和锌(Zn)的固定化。例如,蓝铁矿与 S 的结合在厌氧条件下促进了 Cd 从水相向固相的去除,并确保 Cd 在转移到好氧条件时稳定地保留在固相相中。有趣的是,在硫化相中未检测到离散的 FeS 形成,并且蓝铁矿的主要晶体结构在整个过程中基本保持完整。详细的分子水平研究表明,硫化主要针对蓝铁矿 PO4 四面体角上的 Fe(II)位点。随着向好氧条件的转变,CdS 和蓝铁矿中的 S 位点的放热氧化作用开始,使得 Cd 形成多配位结构变得热力学有利,主要通过 Cd-O-P 和 Cd-O-Fe 键。该机制阐明了 Cd 是如何掺入蓝铁矿结构中的,突出了通过铁磷酸盐矿物中的硫化-再氧化动力学来固定重金属的新途径。