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首页> 外文期刊>International Journal of Quantum Chemistry >Sorption mechanisms of cesium on (Cu2FeII)-Fe-II(CN)(6) and Cu-3(II)[Fe-III(CN)(6)](2): Hexacyanoferrates and their relation to the crystalline structure
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Sorption mechanisms of cesium on (Cu2FeII)-Fe-II(CN)(6) and Cu-3(II)[Fe-III(CN)(6)](2): Hexacyanoferrates and their relation to the crystalline structure

机译:铯在(Cu2FeII)-Fe-II(CN)(6)和Cu-3(II)[Fe-III(CN)(6)](2)上的吸附机理:六氰基高铁酸盐及其与晶体结构的关系

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(Cu2FeII)-Fe-II(CN)(6). xH(2)O and Cu-3(II)[Fe-III(CN)(6)](2). xH(2)O can be prepared with reproducible chemical compositions and structures after careful washing. They have cubic structures with iron vacancies. In (Cu2FeII)-Fe-II(CN)(6), copper occupies two different sites: Cu1 in position 4b linked to Fe through the CN groups, and Cu2 not linked to the CN groups and partially occupying the interstitial 24e positions. The second type of site is not present in Cu-3(II)[Fe-III(CN)(6)](2). Sorption kinetics and isotherms were determined for cesium on both hexacyanoferrates by batch experiments, On Cu-3(II)[Fe-III(CN)(6)](2), the maximum uptake is only 0.073 Cs/Fe (at./at.), On (Cu2FeII)-Fe-II(CN)(6) the uptake reaches 1.5 Cs/Fe, The sorption kinetics include at least two steps: a t(1/2) variation until approximately 72 h and then a slow evolution studied up to 6 months. The sorption mechanism is complex. The main process seems to be diffusion of ion pairs, followed by a reorganization of the solid, resulting in one or more new solid phases. The presence of the Cu2 site seems to play a favorable role in the sorption, Owing to its good midterm stability and the first rapid step of exchange, (Cu2FeII)-Fe-II(CN)(6). xH(2)O seems to be one of the most promising compounds for the recovery of cesium from nuclear liquid wastes. (C) 1998 Academic Press. [References: 36]
机译:(Cu2FeII)-Fe-II(CN)(6)。 xH(2)O和Cu-3(II)[Fe-III(CN)(6)](2)。仔细清洗后,xH(2)O可以制备成可再现的化学成分和结构。它们具有带有铁空位的立方结构。在(Cu2FeII)-Fe-II(CN)(6)中,铜占据两个不同的位置:位置4b中的Cu1通过CN基团与Fe连接,Cu2未连接CN基团并部分占据间隙24e位置。第二种类型的位点在Cu-3(II)[Fe-III(CN)(6)](2)中不存在。通过分批实验确定了铯在六价高铁酸盐上的吸附动力学和等温线。在Cu-3(II)[Fe-III(CN)(6)](2)上,最大吸收量仅为0.073 Cs / Fe(at./ at。),在(Cu2FeII)-Fe-II(CN)(6)上的吸收达到1.5 Cs / Fe。吸附动力学包括至少两个步骤:at(1/2)变化直到大约72 h然后缓慢进化研究长达6个月。吸附机理很复杂。主要过程似乎是离子对的扩散,然后是固体的重组,从而产生一个或多个新的固相。由于其良好的中期稳定性和第一个快速交换步骤(Cu2FeII)-Fe-II(CN)(6),Cu2位点的存在似乎在吸附中起了有利作用。 xH(2)O似乎是从核废液中回收铯的最有希望的化合物之一。 (C)1998年学术出版社。 [参考:36]

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