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锰改性生物炭去除实验中锑的吸附和迁移机制。

The antimony sorption and transport mechanisms in removal experiment by Mn-coated biochar.

机构信息

School of Environmental Studies, China University of Geosciences (Wuhan), 68 Jincheng Road, Wuhan 430078, PR China.

School of Environmental Studies, China University of Geosciences (Wuhan), 68 Jincheng Road, Wuhan 430078, PR China.

出版信息

Sci Total Environ. 2020 Jul 1;724:138158. doi: 10.1016/j.scitotenv.2020.138158. Epub 2020 Mar 23.

DOI:10.1016/j.scitotenv.2020.138158
PMID:32247137
Abstract

A method of Mn-coated biochar production was developed, which showed great removal ability of trivalent antimony (Sb(III)) (0.94 mg g) and pentavalent antimony (Sb(V)) (0.73 mg g), and the adsorption capacity was stable under different pH. According to the adsorption kinetics and isotherm, the adsorption process of both Sb(III) and Sb(V) was chemisorption, which was both monolayer and poly layers heterogeneous chemisorption process. X-ray photoelectron spectroscopy (XPS) and attenuated total reflectance Fourier-transform infrared (ATR-FTIR) spectroscopy analyses indicated that the main oxides and functional groups involved in the adsorption were manganese oxides (MnO), carboxyl and hydroxyl groups and Sb(V) was combined with Mn-coated biochar by inner-sphere complexation. Sb(III) was oxidized by oxygen and MnO which was both on the surface of biochar and dissolved in solution. Furthermore, X-ray absorption near-edge structure (XANES) showed that Sb(V) was the main species after Sb(III) and Sb(V) adsorbed on the Mn-coated biochar. Extended X-ray absorption fine structure (EXAFS) analysis indicated that Sb(III) and MnO formed the monodentate mononuclear and corner-sharing complexes with a structure of Mn-O-Sb on Mn-coated biochar. While Sb(V) and MnO formed inner-sphere complexes including edge-sharing and corner-sharing complexes. The new synthetic material can contribute to develop new remediation strategies for treating Sb-contaminated water.

摘要

开发了一种 Mn 涂层生物炭的生产方法,该方法对三价锑(Sb(III))(0.94 mg g)和五价锑(Sb(V))(0.73 mg g)具有很强的去除能力,并且在不同 pH 值下吸附能力稳定。根据吸附动力学和等温线,Sb(III)和 Sb(V)的吸附过程都是化学吸附,是单层和多层不均匀化学吸附过程。X 射线光电子能谱(XPS)和衰减全反射傅里叶变换红外(ATR-FTIR)光谱分析表明,吸附过程中涉及的主要氧化物和官能团是氧化锰(MnO)、羧基和羟基,Sb(V)通过内配位与 Mn 涂层生物炭结合。Sb(III)被生物炭表面和溶液中溶解的氧和 MnO 氧化。此外,X 射线吸收近边结构(XANES)表明,Sb(III)和 Sb(V)吸附在 Mn 涂层生物炭上后,Sb(V)是主要物种。扩展 X 射线吸收精细结构(EXAFS)分析表明,Sb(III)和 MnO 在 Mn 涂层生物炭上形成了单齿单核和角共享复合物,其结构为 Mn-O-Sb。而 Sb(V)和 MnO 形成了内配位络合物,包括边缘共享和角共享络合物。这种新型合成材料可以为处理 Sb 污染水的新修复策略做出贡献。

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