Laboratory for Radioecology, Rudjer Boskovic Institute, Bijenicka 54, 10 000 Zagreb, Croatia.
Talanta. 2009 Nov 15;80(1):352-62. doi: 10.1016/j.talanta.2009.06.078. Epub 2009 Jul 8.
The paper describes a research of possible application of UTEVA and TRU resins and anion exchanger AMBERLITE CG-400 in nitrate form for the isolation of uranium and thorium from natural samples. The results of determination of distribution coefficient have shown that uranium and thorium bind on TRU and UTEVA resins from the solutions of nitric and hydrochloric acids, and binding strength increases proportionally to increase the concentration of acids. Uranium and thorium bind rather strongly to TRU resin from the nitric acid in concentration ranging from 0.5 to 5 mol L(-1), while large quantities of other ions present in the sample do not influence on the binding strength. Due to the difference in binding strength in HCl and HNO(3) respectively, uranium and thorium can be easily separated from each other on the columns filled with TRU resin. Furthermore, thorium binds to anion exchanger in nitrate form from alcohol solutions of nitric acid very strongly, while uranium does not, so they can be easily separated. Based on these results, we have created the procedures of preconcentration and separation of uranium and thorium from the soil, drinking water and seawater samples by using TRU and UTEVA resins and strong base anion exchangers in nitrate form. In one of the procedures, uranium and thorium bind directly from the samples of drinking water and seawater on the column filled with TRU resin from 0.5 mol L(-1) HNO(3) in a water sample. After binding, thorium is separated from uranium with 0.5 mol L(-1) HCl, and uranium is eluted with deionised water. By applying the described procedure, it is possible to achieve the concentration factor of over 1000 for the column filled with 1g of resin and splashed with 2L of the sample. Spectrophotometric determination with Arsenazo III, with this concentration factor results in detection limits below 1 microg L(-1) for uranium and thorium. In the second procedure, uranium and thorium are isolated from the soil samples with TRU resin, while they are separated from each other on the column filled with anion exchanger in alcohol solutions. Anion exchanger combined with alcohol solutions enables isolation of thorium from soil samples and its separation from a wide range of elements, as well as spectrophotometric determination, ICP-MS determination, and other determination techniques.
本文描述了 UTEVA 和 TRU 树脂以及以硝酸盐形式的强碱性阴离子交换剂 AMBERLITE CG-400 在从天然样品中分离铀和钍方面的潜在应用的研究。分配系数的测定结果表明,铀和钍从硝酸和盐酸溶液中被 TRU 和 UTEVA 树脂吸附,结合强度与酸浓度成正比增加。铀和钍从浓度为 0.5 至 5mol/L 的硝酸中被 TRU 树脂强烈吸附,而样品中存在的大量其他离子对结合强度没有影响。由于在 HCl 和 HNO3 中结合强度的差异,铀和钍可以很容易地在填充有 TRU 树脂的柱上彼此分离。此外,钍以硝酸盐形式从硝酸的醇溶液中非常强烈地结合到强碱性阴离子交换剂上,而铀则不结合,因此可以很容易地将它们分离。基于这些结果,我们已经创建了使用 TRU 和 UTEVA 树脂以及以硝酸盐形式的强碱阴离子交换剂从土壤、饮用水和海水样品中预浓缩和分离铀和钍的程序。在其中一个程序中,铀和钍直接从饮用水和海水样品在 0.5mol/L HNO3 的水中通过填充有 TRU 树脂的柱吸附。结合后,用 0.5mol/L HCl 从铀中分离钍,然后用去离子水洗脱铀。通过应用描述的程序,可以在填充有 1g 树脂并溅洒 2L 样品的柱上实现超过 1000 的浓缩因子。在这个浓缩因子下,用 Arsenazo III 进行分光光度测定,铀和钍的检测限低于 1μg/L。在第二个程序中,铀和钍从土壤样品中用 TRU 树脂分离,然后在填充有强碱性阴离子交换剂的柱上彼此分离。与醇溶液结合的阴离子交换剂可以从土壤样品中分离出钍,并将其与多种元素分离,以及进行分光光度测定、ICP-MS 测定和其他测定技术。