表面负载镁和磷改性褐煤吸附剂:高效吸附和固定化修复cd污染的水和土壤

Yibo Cheng, Tao Wen, Weizhi Zhou, Yali Yuan, Ruilian Sun
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引用次数: 0

摘要

褐煤是一种资源丰富的材料,具有良好的吸附性能,可以作为一种环保型的重金属脱除材料。本研究采用化学改性的方法,将镁离子和磷酸离子负载到褐煤(LM)表面,制备改性的褐煤材料Mg-LM和P-LM,用于污染水体和土壤中Cd (II)的吸附和固定化。表征分析表明,Mg- lm中引入了可交换的Mg离子,增强了其孔隙结构;Mg-LM和P- lm对Cd (II)的吸附符合拟二级动力学模型和Langmuir等温模型,P- lm对Cd (II)的吸附符合准二级动力学模型。mg - lm和P-LM对Cd (II)的最大吸附量分别为1033 mg/g和55 mg/g。P-LM处理对土壤DTPA-Cd含量的降低幅度(32.9%)大于Mg-LM(20.2%)和LM(11.1%)处理。此外,连续的BCR提取证实,Mg-LM和P-LM促进了土壤中不稳定Cd组分向稳定Cd组分的转化。XRD、FTIR和XPS结果表明,静电相互作用、离子交换、表面络合和沉淀可能是Mg-LM和P-LM吸附和固定Cd (II)的主要机理。结果表明,Mg-LM对cd污染水体的修复效果优于P-LM,而对cd污染土壤的修复效果较差。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Surface-loaded magnesium and phosphorus-modified lignite adsorbents: Efficient adsorption and immobilization for remediation of Cd-contaminated water and soil

Surface-loaded magnesium and phosphorus-modified lignite adsorbents: Efficient adsorption and immobilization for remediation of Cd-contaminated water and soil
Lignite is a resource-rich material with favorable adsorption properties and can be used as an environmentally friendly material for removing heavy metals. In this study, we loaded magnesium and phosphate ions onto the surface of lignite (LM) by using chemical modification to generate modified lignite materials, Mg-LM and P-LM, which were used for the adsorption and immobilization of Cd (II) in polluted water and soil. Characterization analysis showed the introduction of exchangeable Mg ions and enhancement of the pore structure in Mg-LM; the increase in the number of oxygenated functional groups and, exchangeable calcium ions and P content of P-LM may favor the adsorption and immobilization of Cd (II). Cd (II) adsorption on Mg-LM and P-LM was consistent with the pseudo-secondary kinetics and Langmuir isotherm models. The maximum adsorption capacity of Cd (II) on Mg-LM and P-LM was 1033 mg/g and 55 mg/g, respectively. The reduction in the soil DTPA-Cd content (32.9%) was greater under P-LM treatment than under Mg-LM (20.2 %) and LM (11.1 %) treatments. In addition, successive BCR extractions confirmed that Mg-LM and P-LM promoted the transformation of unstable Cd fractions to stable Cd fractions in the soil. The XRD, FTIR, and XPS results indicated that electrostatic interactions, ion exchange, surface complexation and precipitation might be the main mechanisms involved in the adsorption and immobilization of Cd (II) by Mg-LM and P-LM. Our results suggest that Mg-LM is more suitable than P-LM for the remediation of Cd-contaminated water, and less applicable than in Cd-contaminated soil.
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