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硫化天然赤铁矿用于去除水体中镉的研究

Removal of Cadmium from Water Using Sulfidized Natural Hematite

  • 摘要: 镉(Cd)作为高毒性重金属,易通过土壤、水体累积并进入食物链危害生态与人类健康,因此对受Cd污染水土进行修复成为全球环境治理的热点课题。天然赤铁矿储量丰富、成本低、环境友好且化学性质稳定,对Cd等重金属有一定去除能力,但因其结晶度高、表面活性位点少,制约 了对Cd的去除效果。本研究在前人研究成果基础上,对天然赤铁矿开展探究,结果表明:天然赤铁矿进行球磨硫化改性后,可以增大比表面积并引入硫官能团,有望提升赤铁矿的界面反应活性。本研究利用天然赤铁矿制备球磨硫化赤铁矿(BMSH),去除水溶液中Cd(Ⅱ),并探讨了影响Cd(Ⅱ)去除效果的主要因素(包括溶液pH、初始浓度、投加量和反应时间)。采用SEM、TEM、XRD等对合成材料进行表征,结果表明硫化赤铁矿的比表面积增大,活性位点增多,其表面形成FeS。BMSH去除Cd(Ⅱ)的机制包括吸附与置换作用:Cd(Ⅱ)先通过化学吸附作用结合到BMSH表面,吸附的Cd(Ⅱ)会置换BMSH表面FeS中的Fe,进而Cd与S结合形成CdS,实现Cd(Ⅱ)稳定去除。在180min时,BMSH对Cd(Ⅱ)去除率达到95.87%,是天然赤铁矿的5倍。近中性条件更利于BMSH去除Cd(Ⅱ),去除率随着反应时间和投加量的增加而增大。水溶液中BMSH对Cd(Ⅱ)吸附是化学吸附,吸附过程符合准二级反应动力学模型(R2>0.9999)。BMSH具备高反应活性、环境适应性,使其在高效去除Cd污染领域具有良好的应用前景。

     

    Abstract: Cadmium (Cd), a highly toxic heavy metal, readily accumulates in soil and water bodies before entering the food chain, posing threats to ecosystems and human health. Consequently, remediation of Cd-contaminated environments has become a global environmental governance priority. Natural hematite, abundant in reserves, cost-effective, environmentally friendly, and chemically stable, possesses a certain capacity to remove heavy metal ions like Cd. However, its high crystallinity and limited surface-active sites constrain its Cd removal efficiency. Building upon prior research, this work investigated natural hematite and found that ball-milled sulfidation modification could enlarge its specific surface area and introduce sulfur functional groups, potentially enhancing interfacial reactivity. This study utilized natural hematite to prepare ball-milled sulfidized hematite (BMSH) for removing Cd(Ⅱ) from aqueous solutions, while investigating key factors affecting Cd(Ⅱ) removal efficiency (including solution pH, initial concentration, dosage, and reaction time). Characterization of the synthesized material via SEM, TEM, and XRD revealed that sulfur-modified hematite exhibited increased specific surface area, enhanced active sites, and the formation of FeS on its surface. The Cd(Ⅱ) removal mechanism of BMSH involves adsorption and displacement: Cd(Ⅱ) first chemisorbs onto the BMSH surface, where adsorbed Cd(Ⅱ) displaces Fe from the surface FeS. Subsequently, Cd combines with S to form CdS, achieving stable Cd(Ⅱ) removal. At 180min, BMSH achieved a Cd(Ⅱ) removal rate of 95.87%, five times that of natural hematite. Near-neutral conditions further enhanced BMSH’s Cd(Ⅱ) removal efficiency, with removal rates increasing with reaction time and dosage. The adsorption of Cd(Ⅱ) by BMSH in aqueous solutions is chemisorption, conforming to pseudo-second-order kinetic models (R2>0.9999). BMSH’s high reactivity and environmental adaptability confer promising application prospects for efficient Cd pollution removal. The BRIEF REPORT is available for this paper at http://www.ykcs.ac.cn/en/article/doi/10.15898/j.ykcs.202506110162.

     

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