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Immobilization of Arsenite and Arsenate Ions in Aqueous Sample Using Calcium Alumino-Zincate

机译:使用钙铝锌酸盐固定亚砷酸盐和砷酸盐离子

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Recently, a lot of problems concerning the contamination of the soil and groundwater by heavy metals such as chromium and lead have occurred, and the enlargement of the pollution area by diffusion of their ions has been also extremely worried. In addition, the arsenic pollution of well water in South Asia nations is a serious problem though it is not a metallic element. It was expected that the reaction of arsenic with cement compounds was similar to that of chromium, because both elements were dissolved in water as oxyanion. In general, large-scale facilities for chemical multi-staged process are necessary to remove the toxic anions such as chromate, arsenite and arsenate ions (denoted as Cr[VI], As[III] and As[V] respectively). The removal of those anions from the contaminated water by hydration of cement or cement compound is an advantageous method technically and economically because it needs neither large-scale facilities nor the elaborate setup. Many researches concerning the immobilization of Cr[VI] in mono-sulfate type hydrate (AFm) or tri-sulfate type hydrate (AFt) by hydration of calcium aluminates such as C3A have been reported. Moreover, coauthors are also planning to report on the immobilization of Cr[VI] by hydration of calcium alumino-zincates in this symposium. In this report, the immobilization process of As[III] and As[V] by calcium alumino-zincates, the influence of Cr[VI] coexisting in their arsenic solutions and the effect of Ca(OH)2 addition on the removal reaction were investigated. The compound 14CaO.5Al2O3.6ZnO (C14A5Z6 for short) was used as calcium alumino-zincate. The results obtained were summarized as follows: 1) Both As[III] and As[V] were removed from aqueous sample by addition of C14A5Z6, however, the removal rates of them were much lower than that of Cr[VI]. 2) The removal of As[III] from aqueous sample was accelerated by Cr[VI], though that of As[V] was hardly affected. 3) The addition of Ca(OH)2 to C14A5Z6 was effective to the removal of As[III] and As[V] from aqueous sample, and the removal rate of As[V] was considerably larger than that of As[III].
机译:最近,已经发生了关于土壤和地下水的污染的许多问题,如铬和铅,并且通过离子的扩散扩大了污染区域的扩大也非常担心。此外,南亚国家井水的砷污染是一个严重的问题,但它不是金属元素。预期砷与水泥化合物的反应类似于铬的反应,因为将两个元素溶于氧气中的水中。通常,用于化学多阶段方法的大规模设施是消除毒性的毒性阴离子,例如铬酸盐,砷酸盐和砷酸酯离子(分别表示为[III]和作为[V])。通过水泥或水泥化合物的水化从污染水中除去这些阴离子是技术上和经济的有利方法,因为它既不需要大规模设施也不需要精心设置。已经报道了许多关于通过水化铝酸钙如C3a的单硫酸盐型水合物(AFM)或三硫酸盐型水合物(AFT)的Crγ或三硫酸盐型水合物(AFT)的许多研究。此外,共同忠诚也计划通过在该研讨会中的铝锌酸钙的水合来报告Cr [VI]的固定。在本报告中,作为[iii]和作为[V]的固定过程和通过氧化钙酸钙的影响,Cr [Vi]在其砷溶液中共存的影响以及Ca(OH)2对去除反应的影响调查。化合物14CaO.5Al 2O3.6ZnO(SHORT C14A5Z6)用作氧化铝铝酸钙。得到的结果总结如下:1)通过加入C14A5Z6从水性样品中除去作为[v],但它们的去除率远低于Cr [VI]。 2)通过Cr [VI]将其从水性样品中除去作为[III],尽管作为[V]的影响几乎没有受到影响。 3)加入Ca(OH)2至C14A5Z6对于从水性样品中除去作为[III]和作为[V]的方法,并且作为[V]的去除率大大大于[III] 。

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