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Synthesis and Physical Property Characterisation of Spheroidal and Cuboidal Nuclear Waste Simulant Dispersions

机译:球形和长方体核废料模拟物分散体的合成及其物理性质表征

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摘要

This study investigated dispersions analogous to highly active nuclear waste, formed from the reprocessing of Spent Nuclear Fuel (SNF). Non-radioactive simulants of spheroidal caesium phosphomolybdate (CPM) and cuboidal zirconium molybdate (ZM-a) were successfully synthesised; confirmed via Scanning Electron Microscopy (SEM), powder X-ray diffraction (PXRD) and Fourier transform infrared (FTIR) spectroscopy. In addition, a supplied ZM (ZM-b) with a rod-like/wheatsheaf morphology was also analysed along with titanium dioxide (TiO2). The simulants underwent thermal gravimetric analysis (TGA) and size analysis, where CPM was found to have a D50 value of 300 nm and a chemical formula of Cs3PMo12O40·13H2O, ZM-a a D50 value of 10 μm and a chemical formula of ZrMo2O7(OH)2·3H2O and ZM-b to have a D50 value of 14 μm and a chemical formula of ZrMo2O7(OH)2·4H2O. The synthesis of CPM was tracked via Ultraviolet-visible (UV-Vis) spectroscopy at both 25 °C and 50 °C, where the reaction was found to be first order with the rate constant highly temperature dependent. The morphology change from spheroidal CPM to cuboidal ZM-a was tracked via SEM, reporting to take 10 days. For the onward processing and immobilisation of these waste dispersions, centrifugal analysis was utilised to understand their settling behaviours, in both aqueous and 2 M nitric acid environments (mimicking current storage conditions). Spheroidal CPM was present in both conditions as agglomerated clusters, with relatively high settling rates. Conversely, the ZM were found to be stable in water, where their settling rate exponents were related to the morphology. In acid, the high effective electrolyte resulted in agglomeration and faster sedimentation.
机译:这项研究调查了由废核燃料(SNF)的后处理形成的类似于高活性核废料的分散体。成功合成了球状磷钼酸铯(CPM)和长方体钼酸锆(ZM-a)的非放射性模拟物。通过扫描电子显微镜(SEM),粉末X射线衍射(PXRD)和傅里叶变换红外(FTIR)光谱确认。另外,还对提供的具有棒状/麦捆状形态的ZM(ZM-b)以及二氧化钛(TiO2)进行了分析。对模拟物进行热重分析(TGA)和尺寸分析,发现CPM的D50值为300 nm,化学式为Cs3PMo12O40·13H2O,ZM-a的D50值为10μm,化学式为ZrMo2O7( OH)2·3H2O和ZM-b的D50值为14μm,化学式为ZrMo2O7(OH)2·4H2O。 CPM的合成通过紫外可见(UV-Vis)光谱在25°C和50°C下进行跟踪,发现该反应是一阶反应,其速率常数与温度密切相关。通过SEM跟踪了从球形CPM到长方体ZM-a的形态变化,报告需要10天。对于这些废物分散体的后续处理和固定化,利用离心分析来了解它们在水性和2 M硝酸环境中(类似于当前的储存条件)的沉降行为。球形CPM在两种情况下均以团簇形式存在,沉降速率相对较高。相反,发现ZM在水中稳定,其沉降速率指数与形态有关。在酸中,高效的电解质导致团聚和更快的沉降。

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