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Interaction of gypsum with lead in aqueous solutions

机译:石膏与水溶液中铅的相互作用

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摘要

Sorption processes on mineral surfaces are a critical factor in controlling the distribution and accumulation of potentially harmful metals in the environment. This work investigates the effectiveness of gypsum (CaSO_4{dot operator}2H_2O) to sequester Pb. The interaction of gypsum fragments with Pb-bearing solutions (10, 100 and 1000mg/L) was monitored by performing macroscopic batch-type experiments conducted at room temperature. The aqueous phase composition was periodically determined by Atomic Absorption Spectrometry (AAS), Ion Chromatography (IC) and Inductively Coupled Plasma Optical Emission Spectroscopy (ICP-OES). Regardless of the [Pb_(aq)]_(initial), a [Pb_(aq)]final~(<4mg/L) was always reached. The uptake process was fast (t<1h) for [Pb_(aq)]_(initial)≥100mg/L and significantly slower (t>1week) for [Pb_(aq)]initial~(=10mg/L). Speciation calculations revealed that after a long time of interaction (1month), all the solutions reached equilibrium with respect to both gypsum and anglesite. For [Pb_(aq_]_(initial)≥100mg/L, sorption takes place mainly via the rapid dissolution of gypsum and the simultaneous formation of anglesite both on the gypsum surface and in the bulk solution. In the case of [Pb_(aq)]_(initial)=10mg/L, no anglesite precipitation was observed, but surface spectroscopy (proton Rutherford Backscattering Spectroscopy, p-RBS) confirmed the formation of Pb-bearing surface layers on the (010) gypsum surface in this case also. This study shows that the surface of gypsum can play an important role in the attenuation of Pb in contaminated waters.
机译:矿物表面的吸附过程是控制环境中潜在有害金属的分布和积累的关键因素。这项工作研究了石膏(CaSO_4 {dot operator} 2H_2O)螯合铅的有效性。通过在室温下进行宏观分批式实验来监测石膏碎片与含Pb溶液(10、100和1000mg / L)的相互作用。通过原子吸收光谱法(AAS),离子色谱法(IC)和电感耦合等离子体发射光谱法(ICP-OES)定期确定水相组成。不管[Pb_(aq)] _(初始)如何,总是达到[Pb_(aq)]最终〜(<4mg / L)。对于[Pb_(aq)] _(初始)≥100mg/ L,摄取过程很快(t <1h),而对于[Pb_(aq)]初始〜(= 10mg / L),摄取过程明显较慢(t> 1周)。形态计算表明,经过长时间的相互作用(1个月),所有溶液在石膏和角位点均达到平衡。对于[Pb_(aq _] _(初始)≥100mg/ L,吸附主要是通过石膏的快速溶解和同时在石膏表面和本体溶液中形成角位而发生的。 )] _(初始)= 10mg / L,未观察到角位沉淀,但表面光谱法(质子卢瑟福背散射光谱法,p-RBS)证实了在这种情况下在(010)石膏表面上形成了含铅表面层这项研究表明,石膏表面在污染水中铅的衰减中起着重要作用。

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