Xie JianXiong, Wei Hang, Sun MengQiang, Huang Ling, Zhong Jie, Wu YuHui, Zou Qi, Chen Zhiliang
Guangdong Engineering Technology Research Center of Heavy Metal Pollution Control and Restoration in Farmland Soil, South China Institute of Environmental Sciences, MEE, Guangzhou 510535, China; Chinese Research Academy of Environmental Sciences, Beijing 10012, China.
Guangdong Engineering Technology Research Center of Heavy Metal Pollution Control and Restoration in Farmland Soil, South China Institute of Environmental Sciences, MEE, Guangzhou 510535, China.
Sci Total Environ. 2024 Nov 10;950:175052. doi: 10.1016/j.scitotenv.2024.175052. Epub 2024 Jul 27.
Co-contamination of soil and groundwater with arsenic (As) and cadmium (Cd) is widespread. Sulfidized Nanoscale Zero-Valent Iron (S-nZVI) is effective in removing As and Cd from contaminated environments. However, the mechanisms governing As and Cd removal from systems containing both species are still unclear. This study investigated the effectiveness of S-nZVI in the simultaneous removal of Cd(II) and As(III) from contaminated solutions and their interaction mechanisms. Adsorption experiments were conducted under aerobic conditions to investigate the effect of Cd(II) and As(III) on their co-immobilisation at different As(III) and Cd(II) concentrations. S-nZVI was characterised before and after the reaction to elucidate the mechanism of its simultaneous immobilisation of As(III) and Cd(II). Batch experiments revealed that the presence of Cd(II) and As(III) together considerably promotes the passivation of S-nZVI. The adsorption of Cd(II) at Cd:As = 1:3 was 198.37 mg/g, which was 27.6 % higher than that in Cd(II)-only systems, and the adsorption of As(III) at As:Cd = 1:3 was 204.05 mg/g, which was 175 % higher than that in As(III)-only systems. The results of X-ray photoelectron spectroscopy and Fourier-transform infrared spectroscopy indicated that the removal of Cd(II) and As(III) by S-nZVI involves electrostatic adsorption, complexation and oxidation reactions, amongst which electrostatic adsorption and ternary-complex generation are responsible for the synergistic effect. As and Cd ions can form two types of surface complexes with FeOH or FeS on the outer layer of S-nZVI: anionic bridging to form Fe-As-Cd and cationic bridging to form Fe-Cd-As. This investigation elucidates the synergistic action of Cd(II) and As(III) during their removal using S-nZVI. Thus, S-nZVI is a promising material for the combined removal of Cd(II) and As(III), which can mitigate environmental pollution.
土壤和地下水同时受到砷(As)和镉(Cd)污染的情况很普遍。硫化纳米零价铁(S-nZVI)能有效去除受污染环境中的As和Cd。然而,从含有这两种物质的体系中去除As和Cd的机制仍不清楚。本研究调查了S-nZVI同时去除污染溶液中Cd(II)和As(III)的有效性及其相互作用机制。在有氧条件下进行吸附实验,以研究不同As(III)和Cd(II)浓度下Cd(II)和As(III)对它们共固定化的影响。对反应前后的S-nZVI进行表征,以阐明其同时固定As(III)和Cd(II)的机制。批量实验表明,Cd(II)和As(III)同时存在会显著促进S-nZVI的钝化。在Cd:As = 1:3时,Cd(II)的吸附量为198.37 mg/g,比仅含Cd(II)的体系高27.6%;在As:Cd = 1:3时,As(III)的吸附量为204.05 mg/g,比仅含As(III)的体系高175%。X射线光电子能谱和傅里叶变换红外光谱结果表明,S-nZVI去除Cd(II)和As(III)涉及静电吸附、络合和氧化反应,其中静电吸附和三元络合物的形成是协同效应的原因。As和Cd离子可与S-nZVI外层的FeOH或FeS形成两种类型的表面络合物:阴离子桥联形成Fe-As-Cd,阳离子桥联形成Fe-Cd-As。本研究阐明了Cd(II)和As(III)在使用S-nZVI去除过程中的协同作用。因此,S-nZVI是一种有前景的用于联合去除Cd(II)和As(III)的材料,可减轻环境污染。