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    磁改性生物炭对水体中磷酸盐吸附特性

    Adsorption characteristics of phosphate in water by magnetically modified biochar

    • 摘要: 针对水体磷污染问题,以青稞秸秆为碳基材料制备生物炭(BC-700),通过共沉淀法将铁基化合物负载至生物炭表面,得到一种具有高吸附容量和强回收能力的磁性生物炭材料(MBC-700),考察了吸附条件(pH、投加量、溶液浓度以及吸附时间)对MBC-700吸附能力的影响,引入动力学模型和等温吸附模型并结合表征分析手段(SEM-EDS、XRD、XPS、FTIR以及VSM)探究MBC-700对水体磷酸盐的吸附机理。结果表明:MBC-700具有丰富的孔隙结构,铁基化合物以FeOOH和Fe3O4形式成功负载至BC-700表面,Fe3O4是MBC-700拥有较高磁性的主要原因,吸附后的磷酸盐以FePO4沉淀物和Fe—O—P络合物存在。MBC-700对磷酸盐的吸附行为是一种可自发的单分子层化学吸附,并且吸附速率受到颗粒内扩散、表面非均匀扩散以及边界层扩散等共同影响,理论最大吸附容量为5.97 mg/g。与此同时,MBC-700在较为广泛的pH范围内(3~7)对磷酸盐均具有一定的吸附能力,碱性环境会受到抑制,阴离子\mathrmCO_3^2- 和\mathrmHCO_3^- 对其吸附具有促进作用,并且MBC-700在磁场作用下的回收率达到98%以上。此外,MBC-700对磷酸盐的吸附机理涉及孔隙填充、静电吸引、配体交换、沉淀作用以及络合作用。研究为水体磷污染和生物炭回收领域提供了科学依据和技术支持。

       

      Abstract: To address phosphorus pollution in water bodies, biochar (BC-700) is derived from highland barley straw as a carbon-based material. Magnetic biochar material (MBC-700) is developed by immobilizing iron-based compounds onto BC-700 surfaces through co-precipitation. Adsorption performance of MBC-700 is systematically investigated under varying conditions, including pH, dosage, initial phosphate concentration, and contact time. Characterization techniques (SEM-EDS, XRD, XPS, FTIR, and VSM) combined with kinetic and isothermal adsorption models are employed to elucidate the adsorption mechanism. Results demonstrate that MBC-700 exhibits a porous structure with iron species (FeOOH and Fe3O4) effectively immobilized on its surface, where Fe3O4 contributes to its strong magnetic properties. Post-adsorption analysis reveals phosphate retention primarily as FePO4 precipitates and Fe—O—P complexes. The adsorption process follows spontaneous monolayer chemisorption kinetics, influenced by intraparticle diffusion, surface heterogeneous diffusion, and boundary layer diffusion, achieving a theoretical maximum adsorption capacity of 5.97 mg/g. MBC-700 maintains effective phosphate removal across a broad pH range (3–7), with enhanced performance in acidic conditions and inhibition in alkaline environments. Notably, coexisting anions (\mathrmCO_3^2- and \mathrmHCO_3^- ) promote adsorption, while magnetic recovery achieves >98% efficiency. Mechanistic studies identify pore filling, electrostatic attraction, ligand exchange, precipitation, and complexation as dominant adsorption pathways. This work provides scientific insights and technical support for addressing phosphorus pollution and advancing biochar recovery technologies.

       

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