Fe(III)负载交换树脂处理废水中As(V)的去除机理

F. Futami, C. Tokoro, Sayaka Izawa, S. Owada
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引用次数: 3

摘要

pH值,导致重金属污染物的沉淀。摘要通过吸附等温线和x射线吸收精细结构光谱分析,研究了铁(III)负载离子交换树脂对砷(V)的去除机理。在pH值为2的条件下,1 h内Fe(III)几乎取代了树脂中所有的反离子;Langmuir交换容量为1.87 mmol Fe/g-resin。铁(III)负载树脂由≈65%的铁(III)和≈35%的水合铁组成。在pH 3、砷浓度为10 mg/dm 3的条件下,反应1 h后吸附密度为0.035 mmol As/g-resin,反应120 h后吸附密度提高到0.74 mmol As/g-resin。As(V)的去除主要通过As(V)和Fe(III)共析出的结晶度差的砷酸铁表面析出进行;也有部分砷(V)吸附在水合铁上。
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Mechanism of As(V) Removal in Wastewater Treatment Using Fe(III)-Supported Exchange Resins
the pH, resulting in the precipitation of heavy metal pollutants 11 . Arsenate (As(V)) and arsenite (As(III)), which are the predominant in-organic arsenic species present in natural aquatic Abstract As(V) removal mechanism using Fe(III)-supported ion exchange resins was elucidated by adsorption isotherms and X-ray absorption fine structure spectroscopy. Fe(III) substituted almost all counter ions in the resin at pH 2 during 1-h reaction; the Langmuir exchange capacity was 1.87 mmol Fe/g-resin. The Fe(III)-supported resin comprised ≈65% Fe(III) and ≈35% ferrihydrite. Under pH 3 and arsenic concentration of 10 mg/dm 3 conditions, a sorption density of 0.035 mmol As/g-resin was obtained after 1-h reaction, and increased to 0.74 mmol As/g-resin after 120-h reaction. As(V) remov al proceeded mainly via surface precipitation of poorly crystalline ferric arsenate via co-precipitation between As(V) and Fe(III); also, some As(V) adsorbed on ferrihydrite.
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