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铜掺杂提高了模拟地下水中砷酸盐在羟基磷灰石上的吸附。

Copper doping improves hydroxyapatite sorption for arsenate in simulated groundwaters.

机构信息

Department of Civil Engineering and Geological Sciences, Notre Dame, Indiana 46556, USA.

出版信息

Environ Sci Technol. 2010 Feb 15;44(4):1366-72. doi: 10.1021/es9015734.

Abstract

Hydroxyapatite (HAP) has been widely used to immobilize many cationic heavy metals in water and soils. Compared with its strong sorption for metal cations, the abilities of HAP to sorb metal anions, such as arsenic, are less significant. Improving HAP sorption for anionic arsenic species is important for expanding its application potential because the presence of arsenic in the environment has raised serious health concerns and there is need for cost-effective remediation methods. In this work, we report an innovative method of copper doping to improve a synthetic HAP sorption for arsenate, which is a primary aqueous arsenic species, in simulated groundwaters. The undoped HAP and copper doped HAP (CuHAP) were characterized with XRD, FTIR, N(2) adsorption, and SEM, and then evaluated as sorbents for arsenate removal tests. The experimental results suggest that copper doping changed the morphology and increased the surface area of HAP. The CuHAP sorbed 1.6-9.1x more arsenate than the undoped HAP did in a simulated groundwater at pH of 7.7-8.0. The improved arsenate sorption is presumably due to the increase in surface area of HAP as a result of copper doping. In addition to the copper doping level, the arsenate sorption to HAP and CuHAP can also be increased with increasing water pH and calcium concentration. The experimental data indicate that sorbent dissolution is an important factor governing arsenate sorption to HAP and CuHAP.

摘要

羟基磷灰石(HAP)已广泛用于固定水中和土壤中的许多阳离子重金属。与 HAP 对金属阳离子的强吸附相比,其对金属阴离子(如砷)的吸附能力则不那么显著。提高 HAP 对阴离子砷物种的吸附能力对于扩大其应用潜力很重要,因为环境中砷的存在引起了严重的健康问题,需要经济有效的修复方法。在这项工作中,我们报告了一种通过铜掺杂来改善合成 HAP 对砷酸盐(一种主要的水溶液砷物种)的吸附能力的创新方法,该方法用于模拟地下水中。未掺杂的 HAP 和铜掺杂的 HAP(CuHAP)通过 XRD、FTIR、N2 吸附和 SEM 进行了表征,然后作为吸附剂用于砷酸盐去除测试。实验结果表明,铜掺杂改变了 HAP 的形态并增加了其表面积。在 pH 为 7.7-8.0 的模拟地下水中,CuHAP 比未掺杂的 HAP 多吸附了 1.6-9.1 倍的砷酸盐。砷酸盐吸附的改善可能是由于铜掺杂导致 HAP 表面积增加所致。除了铜掺杂水平外,随着水 pH 值和钙离子浓度的增加,HAP 和 CuHAP 对砷酸盐的吸附也会增加。实验数据表明,吸附剂的溶解是控制 HAP 和 CuHAP 对砷酸盐吸附的一个重要因素。

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