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针铁矿对砷(V)和砷(III)的吸附。

Sorption of arsenic(V) and arsenic(III) to schwertmannite.

机构信息

Southern Cross GeoScience, Southern Cross University, Lismore, NSW 2480, Australia.

出版信息

Environ Sci Technol. 2009 Dec 15;43(24):9202-7. doi: 10.1021/es902461x.

Abstract

This study describes the sorption of As(V) and As(III) to schwertmannite as a function of pH and arsenic loading. In general, sorption of As(V) was greatest at low pH, whereas high pH favored the sorption of As(III). The actual pH of equivalent As(V) and As(III) sorption was strongly loading dependent, decreasing from pH approximately 8.0 at loadings <120 mmol(As) mol(Fe)(-1) to pH approximately 4.6 at a loading of 380 mmol(As) mol(Fe)(-1). Sorption isotherms for As(V) were characterized by strong partitioning to the schwertmannite solid-phase at low loadings and sorption capacities of 225-330 mmol(As(V)) mol(Fe)(-1) at high loadings. In contrast, the As(III) isotherms revealed a weak affinity for sorption of As(III) versus As(V) at low loadings yet a greater affinity for As(III) sorption compared with As(V) at high loadings (when pH > 4.6). Sorption of As(V) and As(III) caused significant release of SO(4)(2-) from within the schwertmannite solid-phase, without major degradation of the schwertmannite structure (as evident by X-ray diffraction and Raman spectroscopy). This can be interpreted as arsenic sorption via incorporation into the schwertmannite structure, rather than merely surface complexation at the mineral-water interface. The results of this study have important implications for arsenic mobility in the presence of schwertmannite, such as in areas affected by acid-mine drainage and acid-sulfate soils. In particular, arsenic speciation, arsenic loading, and pH should be considered when predicting and managing arsenic mobility in schwertmannite-rich systems.

摘要

本研究描述了砷(V)和砷(III)在针铁矿上的吸附随 pH 值和砷负载量的变化关系。一般来说,砷(V)的吸附在低 pH 值时最大,而高 pH 值则有利于砷(III)的吸附。实际的等当量砷(V)和砷(III)吸附 pH 值强烈依赖于负载量,从负载量<120mmol(As) mol(Fe)(-1)时的 pH 值约 8.0 降低到负载量为 380mmol(As) mol(Fe)(-1)时的 pH 值约 4.6。砷(V)的吸附等温线特征为在低负载量时强烈分配到针铁矿固相,在高负载量时吸附容量为 225-330mmol(As(V)) mol(Fe)(-1)。相比之下,砷(III)的等温线在低负载量时显示出对砷(III)吸附比对砷(V)弱的亲和力,但在高负载量时(当 pH > 4.6 时)对砷(III)的吸附比对砷(V)强。砷(V)和砷(III)的吸附导致针铁矿固相内部大量释放 SO(4)(2-),而针铁矿结构没有发生主要降解(通过 X 射线衍射和拉曼光谱可以明显看出)。这可以解释为砷通过掺入针铁矿结构中而不是仅仅在矿物-水界面发生表面络合进行吸附。本研究的结果对针铁矿存在时砷的迁移性具有重要意义,例如在受酸性矿山排水和酸性硫酸盐土壤影响的地区。特别是,在预测和管理富含针铁矿系统中的砷迁移性时,应考虑砷形态、砷负载量和 pH 值。

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