Abstract

For the long-term safety assessment of direct disposal of spent nuclear fuel in deep geologic repositories, knowledge on the radionuclide release rate from the UO2 matrix is essential. This work provides a conceptual model to explain the results of leaching experiments involving used nuclear fuel or simulant materials in confirmed reducing conditions. Key elements of this model are: direct effect of radiation from radiolytic species (including defects and excited states) in the solid and in the first water layers in contact with its surface; and excess H2 may be produced due to processes occurring at the surface of the spent fuel and in confined water volumes, which may also play a role in keeping the spent fuel surface in a reduced state. The implication is that the fractional radionuclide release rate used in most long-term safety assessments (10−7 year−1) is over estimated because it assumes that there is net UO2 oxidation caused by radiolysis, in contrast with the alternative conceptual model presented here. Furthermore, conventional water radiolysis models and radiation chemical yields published in the literature are not directly applicable to a heterogeneous system such as the spent fuel–water interface. Suggestions are provided for future work to develop more reliable models for the long-term safety assessment of spent nuclear fuel disposal.

Highlights

  • The long-term safety of spent nuclear fuel disposal will have a large impact on the future use of nuclear reactors as a major energy source

  • In the case of direct disposal of nuclear fuel in a deep geologic repository, the fuel assemblies are isolated from the surface environment by a series of engineered barriers embedded in the host rock at a depth of a few hundred meters [1]

  • This work provides an alternative conceptual model to explain the leaching test results involving actual spent nuclear fuel or simulant materials in reducing conditions, which are relevant for deep geologic disposal

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Summary

Introduction

The long-term safety of spent nuclear fuel disposal will have a large impact on the future use of nuclear reactors as a major energy source. In the case of direct disposal of nuclear fuel in a deep geologic repository, the fuel assemblies are isolated from the surface environment by a series of engineered barriers embedded in the host rock at a depth of (typically) a few hundred meters [1]. The spent fuel assemblies (consisting of a number of rods containing fuel (UO2 ) pellets) are encapsulated in a canister that is designed to ensure long-term containment in the conditions expected at the disposal site. Spent nuclear fuel is an intrinsic source of ionizing radiation (alpha, beta, and gamma) debated. Understanding oxidation and reduction processes at the spent fuel–water interface will both lead to the formation of reactive species governing the redox conditions at the UO contribute to improving the conceptual model of radionuclide releases and achieve a more interface. Beta, and gamma radiation are classified as ionizing radiation, which leads to the cleavage of chemical bonds in the traversed medium in a process called “radiolysis”

Spent Nuclear Fuel in Disposal Conditions
Observations from Leaching Tests in Reducing Conditions
Current Conceptual
Mechanism for UO at macroscopic level to the Matrix
Proposed Alternative Conceptual Model
Processes Occurring at the Metal Oxides-Water Interface
Processes Occurring in Confined Water Volumes
Redox Conditions at the Spent Fuel Surface
Outlook on Developments of the Conceptual
Conclusions
Findings
Methods
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