College of Metallurgy and Energy, North China University of Science and Technology, 21 Bohai Street, Tangshan, 063210, China.
Biomass Group, College of Engineering, Nanjing Agricultural University, 40 Dianjiangtai Road, Nanjing, 210031, China.
Environ Sci Pollut Res Int. 2023 Mar;30(12):33737-33755. doi: 10.1007/s11356-022-24491-7. Epub 2022 Dec 10.
Reed straw and electric furnace dust (EFD) waste were used to prepare magnetic Fe-C composite (EFD&C) by co-precipitation and high-temperature activation method to remove Cr(VI) from water. The magnetic EFD&C owned a large specific surface (536.61 m/g) and a porous structure (micropores and mesopores), and had an efficient removal capacity for Cr(VI). Under conditions of pH (2), the addition amount of EFD&C (1 g/L), the adsorption time (760 min), and the temperature (45 °C), the maximum adsorption capacity reached 111.94 mg/g. The adsorption mechanism mainly attributed to chemical adsorption (redox), Cr(VI) reduced to Cr(III) by Fe(II) and Fe(0) (from FeO and Fe components in EFD) and surface functional groups of -OH, C = C, C-C and O-C = O (from biochar), and secondary attributed to physical adsorption, Cr(VI) and Cr(III) (from reduced Cr(VI)) adsorbed into the porous structure of EFD&C. This study provided a feasible solution for the preparation of adsorbents for adsorbing heavy metals from iron-containing metallurgical solid waste and biomass waste, which contributed to reducing the environmental pollution and lowering the cost of adsorbent preparation.
reed 秸秆和电炉粉尘(EFD)废物被用于通过共沉淀和高温活化方法制备磁性 Fe-C 复合材料(EFD&C),以从水中去除 Cr(VI)。磁性 EFD&C 具有较大的比表面积(536.61 m/g)和多孔结构(微孔和介孔),对 Cr(VI)具有高效的去除能力。在 pH(2)、EFD&C 添加量(1 g/L)、吸附时间(760 min)和温度(45°C)的条件下,最大吸附容量达到 111.94 mg/g。吸附机制主要归因于化学吸附(氧化还原),Fe(II)和 Fe(0)(来自 EFD 中的 FeO 和 Fe 成分)和 -OH、C ═ C、C-C 和 O-C ═ O(来自生物炭)将 Cr(VI)还原为 Cr(III),其次是物理吸附,Cr(VI)和 Cr(III)(来自还原的 Cr(VI))被吸附到 EFD&C 的多孔结构中。本研究为从含铁冶金固体废物和生物质废物中制备吸附重金属的吸附剂提供了可行的解决方案,有助于减少环境污染和降低吸附剂制备成本。