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Adsorption of Pb~(2+), Cd~(2+) and Sr~(2+) ions onto natural and acid-activated sepiolites

机译:天然和酸活化海泡石对Pb〜(2 +),Cd〜(2+)和Sr〜(2+)离子的吸附

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The adsorption mechanisms of Pb~(2+), Cd~(2+) and Sr~(2+) ions on natural sepiolite and the influence of acid treatment on the adsorption capacity of sepiolite were investigated. The point of zero charge, pH_(pzc), is 7.4±0.1 for natural sepiolite and 6.9±0.1 for partially acid-activated sepiolite. The shift of the pH_(pzc) of sepiolites toward lower pH values in solutions of Pb~(2+) and Cd~(2+) ions indicates that specific adsorption of these cations on natural and acid-activated sepiolites occurred, which was more pronounced for Pb~(2+) ions than for Cd~(2+) ions. There was no shift of the pH_(pzc) in solution containing Sr~(2+) ions, suggesting that specific adsorption of this cation did not occur. The affinity for ion exchange with the Mg~(2+) ions from the sepiolite structure was the highest for Pb~(2+) ions, then Cd~(2+), whereas the affinity for Sr~(2+) ions was negligible. The adsorption isotherms suggest that the sequence of the efficiency of the sepiolites adsorption is Pb~(2+) > Cd~(2+) > Sr~(2+). The retention of Pb~(2+) and Cd~(2+) ions by sepiolite occurs dominantly by specific adsorption and exchange of Mg~(2+) ions from the sepiolite structure. The concentration in the external outer sphere of the Stern layer by electrostatic forces is the dominant mechanism for the retention of Sr~(2+) ions on the surface of sepiolites. Despite increases in the surface areas upon acid activation, improvements in the adsorption were not observed, as a result of the decreasing number of Mg-OH groups, as main centers for specific adsorption, and the number of Mg~(2+) ions available for ion exchange with Pb~(2+), Cd~(2+) and Sr~(2+) ions. The removal of Mg-OH groups from the sepiolite also resulted in a decrease in the point of zero charge and an increase of the relative surface acidity, from 2.6±0.1 for the natural to 6.4±0.1 for the acid-activated sepiolite.
机译:研究了Pb〜(2 +),Cd〜(2+)和Sr〜(2+)离子在天然海泡石上的吸附机理以及酸处理对海泡石吸附能力的影响。天然海泡石的零电荷点pH_(pzc)为7.4±0.1,部分酸活化的海泡石的零电荷点为6.9±0.1。在Pb〜(2+)和Cd〜(2+)离子溶液中,海泡石的pH_(pzc)向较低的pH值移动表明,这些阳离子在天然和酸活化的海泡石上发生了特异性吸附,且这种吸附更为明显。 Pb〜(2+)离子比Cd〜(2+)离子明显。在含有Sr〜(2+)离子的溶液中pH_(pzc)没有变化,表明该阳离子没有发生特异性吸附。与海泡石结构中的Mg〜(2+)离子进行离子交换的亲和力对Pb〜(2+)离子最高,然后对Cd〜(2+)最高,而对Sr〜(2+)离子的亲和力最高。微不足道。吸附等温线表明海泡石吸附效率的顺序为Pb〜(2+)> Cd〜(2+)> Sr〜(2+)。海泡石对Pb〜(2+)和Cd〜(2+)离子的保留主要发生于海泡石结构中Mg〜(2+)离子的特异性吸附和交换。静电力在斯特恩层外部外球中的浓缩是将Sr〜(2+)离子保留在海泡石表面的主要机理。尽管酸活化后表面积增加,但由于作为特定吸附的主要中心的Mg-OH基团数量减少以及可用的Mg〜(2+)离子数量减少,因此未观察到吸附的改善。用于与Pb〜(2 +),Cd〜(2+)和Sr〜(2+)离子的离子交换。从海泡石中除去Mg-OH基团也导致零电荷点的减少和相对表面酸度的增加,从天然的2.6±0.1增加到酸活化的海泡石的6.4±0.1。

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