锌锰铁改性生物炭去除废水中镉的性能及作用机制OA
Performance and Mechanism of Zinc-Manganese-Iron Modified Biochar in Removing Cadmium from Wastewater
以柚子皮为原料,利用锌锰铁浸渍改性制备柚皮生物炭(ZMF@BC),探讨生物炭在不同条件下对废水中Cd(Ⅱ)的去除效果及作用机制.通过共存离子吸附竞争、吸附-解吸、批量吸附实验,红外光谱(FT-IR)和 X-射线衍射分析(XRD)等对 ZMF@BC 的吸附性能和机理进行探讨.结果表明,pH 6.0 时,由于离子竞争力减弱,生物炭对 Cd(Ⅱ)有较好吸附效果.水中常见共存离子对 Cd(Ⅱ)的竞争吸附影响从大到小顺序为:Na+、Mg2+、Ca2+、K+.ZMF@BC 对Cd(Ⅱ)的吸附符合 Langmuir 模型和准二级动力学模型,属于单分子层化学吸附,最大吸附量为 32.3 mg/g;热力学结果显示吸附为自发过程;经 5 次吸附-解吸后,仍能保持起始吸附量的 85.1%.ZMF@BC 可利用表面金属氧化物中的 Zn、Fe 和Mn 以离子交换形式吸附 Cd(Ⅱ),也可通过铁氧化物特有的络合机制和静电吸附固定 Cd(Ⅱ).
Heavy metal pollution is widespread and increasingly severe,cadmium(Cd)in water is potentially toxic,and can be transferred and enriched into the human body through the food chain and other ways,endangering human health.Adsorption method has garnered significant attention in the treatment of heavy metal pollution,and different biomass materials can affect the adsorption effect of biochar on heavy metals in water to a certain extent.In this study,magnetic pomelo peel biochar(ZMF@BC)was prepared from agricultural waste pomelo peel as raw material via zinc-manganese-iron impregnation modification to investigate the removal effect and mechanism of biochar on Cd(Ⅱ)in water under different conditions.The adsorption performance of ZMF@BC on Cd(Ⅱ)was analyzed by coexisting ion competition adsorption,adsorption-desorption,etc.The adsorption mechanism was also explored using batch adsorption experiments,Fourier Transform Infrared Spectroscopy(FT-IR),and X-ray Diffraction Analysis(XRD).The results showed that at pH 6.0,the biochar adsorbed Cd(Ⅱ)with a maximum adsorption capacity of 26.3 mg/g due to the reduced ionic competitiveness,and the competitive adsorption of Cd(Ⅱ)by common cations coexisting in the water was in the following order:Na+>Mg2+>Ca2+>K+.The adsorption of Cd(Ⅱ)by ZMF@BC was in accordance with Langmuir and quasi-secondary kinetic models,suggesting monolayer chemical adsorption.The thermodynamic results showed that the adsorption process was spontaneous,and the adsorption-desorption could maintain 85.1%of the initial adsorption amount after five adsorption-desorption cycles.ZMF@BC can absorb Cd(Ⅱ)through ion exchange by using the Zn,Fe,and Mn in the metal oxides on its surface,and also be immobilized through the complexation mechanism specific to the iron oxides.
段紫嫣;叶顺云;张俊渝;李安玉;姜峰;苏铭;邓华
广西生态脆弱区环境过程与修复重点实验室(广西师范大学),广西 桂林 541006||漓江流域绿色治理与低碳发展广西高校工程研究中心(广西师范大学),广西 桂林 541006广西生态脆弱区环境过程与修复重点实验室(广西师范大学),广西 桂林 541006||漓江流域绿色治理与低碳发展广西高校工程研究中心(广西师范大学),广西 桂林 541006广西生态脆弱区环境过程与修复重点实验室(广西师范大学),广西 桂林 541006||漓江流域绿色治理与低碳发展广西高校工程研究中心(广西师范大学),广西 桂林 541006广西生态脆弱区环境过程与修复重点实验室(广西师范大学),广西 桂林 541006||漓江流域绿色治理与低碳发展广西高校工程研究中心(广西师范大学),广西 桂林 541006广西生态脆弱区环境过程与修复重点实验室(广西师范大学),广西 桂林 541006||漓江流域绿色治理与低碳发展广西高校工程研究中心(广西师范大学),广西 桂林 541006广西生态脆弱区环境过程与修复重点实验室(广西师范大学),广西 桂林 541006||漓江流域绿色治理与低碳发展广西高校工程研究中心(广西师范大学),广西 桂林 541006广西生态脆弱区环境过程与修复重点实验室(广西师范大学),广西 桂林 541006||漓江流域绿色治理与低碳发展广西高校工程研究中心(广西师范大学),广西 桂林 541006
资源环境
镉生物炭改性吸附机理废水
cadmiumbiocharmodifiedadsorptionmechanismwastewater
《广西师范大学学报(自然科学版)》 2026 (3)
214-224,11
广西重点研发计划(GKAB22035038)
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