Department of Civil & Environmental Engineering & Earth Sciences, University of Notre Dame, Notre Dame, IN 46556, USA.
Environ Sci Process Impacts. 2018 Oct 17;20(10):1306-1322. doi: 10.1039/c7em00369b.
In recent decades, interest in plutonium mobility has increased significantly due to the need of the United States, as well as other nations, to deal with commercial spent nuclear fuel, nuclear weapons disarmament, and the remediation of locations contaminated by nuclear weapons testing and production. Although there is a global consensus that geologic disposal is the safest existing approach to dealing with spent nuclear fuel and high-level nuclear waste, only a few nations are moving towards implementing a geologic repository due to technical and political barriers. Understanding the factors that affect the mobility of plutonium in the subsurface environment is critical to support the development of such repositories. The importance of redox chemistry in determining plutonium mobility cannot be understated. While Pu(iv) is generally assumed to be immobile in the subsurface environment due to sorption or precipitation, Pu(v) tends to be mobile due to its relatively low effective charge and weak complex formation. This review highlights one particularly important aspect of plutonium behaviour at the mineral-water interface-the concept of surface-mediated reduction, which describes the reduction of plutonium on a mineral surface. It provides a conceptual model for and evidence supporting or refuting each proposed mechanism for surface-mediated reduction including (i) radiolysis at the mineral surface, (ii) electron transfer via ferrous iron or manganese in the mineral structure, (iii) electron shuttling due to the semiconducting properties of the mineral, (iv) disproportionation of Pu(v), (v) facilitation by proton exchange sites, (vi) stabilisation of Pu(iv) due to the increased concentration gradient within the electrical double layer, and (vii) a Nernstian favourability of Pu(iv) surface complexes and colloids. It also provides new perspectives on future research directions.
近几十年来,由于美国以及其他国家需要处理商业乏核燃料、核武器裁军以及受核武器试验和生产污染场所的补救,人们对钚的迁移性的兴趣显著增加。尽管全球普遍认为地质处置是处理乏核燃料和高放废物的最安全的现有方法,但由于技术和政治障碍,只有少数几个国家正在着手建立地质处置库。了解影响钚在地下环境中迁移性的因素对于支持这些处置库的发展至关重要。氧化还原化学在确定钚在地下环境中的迁移性方面的重要性怎么强调都不为过。虽然由于吸附或沉淀,Pu(iv)通常被认为在地下环境中是不移动的,但 Pu(v)由于其相对较低的有效电荷和较弱的络合形成,往往是移动的。本综述重点介绍了钚在矿物-水界面上行为的一个特别重要的方面——表面介导还原的概念,该概念描述了在矿物表面上的钚还原。它为表面介导还原的每个提出的机制提供了一个概念模型,并提供了支持或反驳这些机制的证据,这些机制包括:(i) 矿物表面的辐射分解;(ii) 矿物结构中亚铁或锰的电子转移;(iii) 由于矿物的半导体性质而发生的电子穿梭;(iv) Pu(v)的歧化;(v) 质子交换位促进;(vi) 由于电双层内浓度梯度的增加而稳定 Pu(iv);以及 (vii) Pu(iv)表面络合物和胶体的 Nernst 有利性。它还为未来的研究方向提供了新的视角。