Nikić Jasmina, Watson Malcolm, Jokić Govedarica Jovana, Vujić Maja, Pešić Jovana, Rončević Srđan, Agbaba Jasmina
Department of Chemistry, Biochemistry and Environmental Protection, Faculty of Sciences, University of Novi Sad, Trg Dositeja Obradovića 3, 21000 Novi Sad, Serbia.
Materials (Basel). 2024 Oct 18;17(20):5089. doi: 10.3390/ma17205089.
Global concern over arsenic contamination in drinking water necessitates innovative and sustainable remediation technologies. This study evaluates the adsorption performance of Fe-Mn binary oxide (FMBO) nanocomposites developed by coating polyethylene (PE) and polyethylene terephthalate (PET) with FMBO for the removal of As(III) and As(V) from water. Adsorption kinetics were rapid, with equilibrium achieved within 1-4 h depending on the material and pH. PET-FMBO and FMBO exhibited faster rates and higher arsenic removal (up to 96%) than PE-FMBO. Maximum As(III) adsorption capacities ranged from 4.76 to 5.75 mg/g for PE-FMBO, 7.2 to 12.0 mg/g for PET-FMBO, and up to 20.8 mg/g for FMBO, while capacities for As(V) ranged from 5.20 to 5.60 mg/g, 7.63 to 18.4 mg/g, and up to 46.2 mg/g, respectively. The results of the Dubinin-Radushkevich isotherm model, with free energy (E) values exceeding 16 kJ/mol, suggest chemisorption is the dominant mechanism, which is supported by the kinetics data. Given the effective removal of As(III), chemisorption likely proceeds through ligand exchange during the Mn oxide-mediated oxidation of As(III) and complexation with hydroxyl groups on the nanocomposite. These findings highlight the strong potential of Fe-Mn polymer nanocomposites, particularly PET-FMBO, for efficient arsenic removal during practical water treatment applications.
全球对饮用水中砷污染的关注使得创新且可持续的修复技术成为必要。本研究评估了通过用铁锰二元氧化物(FMBO)包覆聚乙烯(PE)和聚对苯二甲酸乙二酯(PET)而制备的FMBO纳米复合材料对水中As(III)和As(V)的吸附性能。吸附动力学很快,根据材料和pH值,1 - 4小时内即可达到平衡。PET - FMBO和FMBO比PE - FMBO表现出更快的吸附速率和更高的砷去除率(高达96%)。PE - FMBO对As(III)的最大吸附容量为4.76至5.75 mg/g,PET - FMBO为7.2至12.0 mg/g,FMBO高达20.8 mg/g,而对As(V)的吸附容量分别为5.20至5.60 mg/g、7.63至18.4 mg/g和高达46.2 mg/g。Dubinin - Radushkevich等温线模型的结果显示,自由能(E)值超过16 kJ/mol,表明化学吸附是主要机制,动力学数据也支持这一点。鉴于As(III)的有效去除,化学吸附可能是在As(III)的锰氧化物介导氧化过程中通过配体交换以及与纳米复合材料上的羟基络合而进行的。这些发现突出了铁锰聚合物纳米复合材料,特别是PET - FMBO,在实际水处理应用中高效去除砷的巨大潜力。