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Simulation of radionuclides Tc-99 and Am-243 migration in compacted bentonite

机译:压缩膨润土中放射性核素Tc-99和Am-243迁移的模拟

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摘要

The distribution coefficients of radionuclides derived from batch experiments are used to evaluate the migration behavior of radionuclides Tc-99 and Am-243 in compacted bentonite after different times. The effects of times, dispersion coefficient, distribution coefficient and pore water velocity on the concentration distribution of Tc-99 and Am-243 in the environment are also calculated from the theoretical migration equation. Tc-99 is poorly sorbed to bentonite and moves quickly into the environment. Migration of radionuclide increases with increasing dispersion coefficient and decreasing distribution coefficient. The effects of water velocity on the migration of Tc and Am are obvious. Most Am-243 is retained in the first several meters, and 20 m of the backfill-compacted bentonites are sufficient to prevent the migration of radionuclide Am from the repository to the environment. (c) 2004 Elsevier Ltd. All rights reserved.
机译:通过分批实验得出的放射性核素的分布系数,用于评估放射性核素Tc-99和Am-243在压缩膨润土中不同时间后的迁移行为。还根据理论迁移方程计算了时间,分散系数,分布系数和孔隙水速度对环境中Tc-99和Am-243浓度分布的影响。 Tc-99吸附到膨润土的能力很差,并迅速移入环境。放射性核素的迁移随着弥散系数的增加和分布系数的减小而增加。水速对Tc和Am迁移的影响是明显的。大多数Am-243保留在前几米之内,而20 m的回填压实膨润土足以防止放射性核素Am从储存库迁移到环境。 (c)2004 Elsevier Ltd.保留所有权利。

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