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采用低 pH 值下制备的硅胶负载的氢氧化铁去除水中的砷(III)和砷(V)的研究。

Study of arsenic(III) and arsenic(V) removal from waters using ferric hydroxide supported on silica gel prepared at low pH.

机构信息

Department of Chemistry, Faculty of Science, Ege University, Bornova, Izmir, Turkey.

出版信息

Environ Technol. 2011 Feb-Mar;32(3-4):341-51. doi: 10.1080/09593330.2010.499546.

Abstract

Removal of As(III) and As(V) species using ferric hydroxide supported on silica gel was studied. Laboratory reagent quality silica gel was used as to avoid uncertainties that may be caused by impurities. Ferric hydroxide precipitation was realized at various pH values and a relatively low pH 6.0 was chosen because, at this pH, the highest arsenic removal capacity and removal efficiency were obtained and clear supernatant solution was observed. It was also shown by arsenic speciation analysis at trace level that As(III) is adsorbed onto ferric hydroxide partly without oxidation to As(V); this has been a controversial point in the literature. The effects on arsenic removal of some parameters such as pH, flow rate and matrix ions were investigated. In the batch method, initial pH change of the solution did not significantly affect the arsenic removal efficiencies for As(III) and As(V) in the pH range of 3.1-9.7. This was attributed to the decreases of the initial pH values to around 5 at equilibrium. The column capacities of 1.32 mg As(III)/g sorbent and 1.21 mg As(V)/g sorbent were found for initial concentration of 1.00 mg/L arsenic. Batch capacities were 16.2 mg As(III)/g sorbent and 17.7 mg As(V)/g sorbent for initial arsenic concentration of 100 mg/L. The method was applied successfully to the removal of As(III) and As(V) from drinking water, geothermal water and mineral water.

摘要

使用硅胶负载的氢氧化铁去除砷(III)和砷(V)物种的研究。使用实验室试剂质量的硅胶,以避免杂质可能引起的不确定性。在不同的 pH 值下实现了氢氧化铁沉淀,并选择了相对较低的 pH 值 6.0,因为在该 pH 值下,获得了最高的砷去除容量和去除效率,并且观察到了澄清的上清液。痕量砷形态分析还表明,部分砷(III)被吸附到氢氧化铁上,而没有氧化为砷(V);这在文献中是一个有争议的观点。研究了一些参数,如 pH 值、流速和基质离子对砷去除的影响。在批处理方法中,溶液初始 pH 值的变化在 3.1-9.7 的 pH 范围内对砷(III)和砷(V)的去除效率没有显著影响。这归因于初始 pH 值在平衡时降低到约 5。对于初始砷浓度为 1.00mg/L 的砷,发现 1.32mg As(III)/g 吸附剂和 1.21mg As(V)/g 吸附剂的柱容量。对于初始砷浓度为 100mg/L 的砷,批处理容量为 16.2mg As(III)/g 吸附剂和 17.7mg As(V)/g 吸附剂。该方法成功应用于饮用水、地热水和矿泉水的砷(III)和砷(V)去除。

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