School of Computer and Artificial Intelligence, Hefei Normal University, Hefei, Anhui 230601, China.
Department of Computer Science, Hong Kong Baptist University, Hong Kong 999077, China.
J Hazard Mater. 2024 Dec 5;480:135397. doi: 10.1016/j.jhazmat.2024.135397. Epub 2024 Aug 2.
Vegetation barriers are an important environmental characteristic of spent fuel road transportation accidents. Spent fuel vessels may be affected by force majeure factors during transportation, which leads to damage to spent fuel assemblies and containers and can cause radionuclides to gradually release from assemblies to vessels to the external environment. In this work, considering the growth periods of coniferous vegetation barriers and vessel type, a radionuclide dispersion model based on computational fluid dynamics (CFD) was established by adding a decay term and a pressure loss term. The simulations showed that, first, compared to the small (Type-II) vessel, the effects of fluid flow around the large vessel (Type-I) have a more significant impact on radionuclide dispersion. The backflow around the Type-I vessel causes leaked radionuclides to disperse towards the vessel, and the larger the vessel is, the more significant the rise of the leaked radionuclide plume tail will be due to the increased negative pressure gradient area. Moreover, the area contaminated exceeding the maximum allowable concentration by radioactivity for the Type-I vessel is reduced gradually with the growth of coniferous vegetation barriers due to the weakening of the backflow effect by growing vegetation. Second, compared to vegetation barriers of 15 years and 23 years, the horizontal distance exceeding the maximum allowable concentration of the leaked I dispersion from Type II vessels near vegetation barriers for 12 years is the longest. The older the vegetation barrier is, the shorter the horizontal dispersion range, and the shape of radionuclide dispersion gradually transforms from flat to semicircular with vegetation barrier growth, but this could cause a greater radioactive accumulation effect near the leakage point, and the maximum concentration of leaked I reached 0.54 kBq·m for leaked radionuclides from the Type II vessel under vegetation barriers of 23 years. In addition, improvement suggestions based on the proposed method are presented, which will enable the Standards Institutes to apply the research methodologies described herein across various scenarios. ENVIRONMENTAL IMPLICATION: Compared to nonradioative pollutants, radioactive pollutants are intercepted by vegetation barriers and then migrate to the soil through leaves, stems, and roots, which can contaminate the surrounding environment. Considering the effects of vessel type and coniferous vegetation growth, a radionuclide dispersion model based on CFD was established. Suggestions for decontaminating radioactive pollution areas have been proposed based on the simulation results of hypothetical scenarios. The scenario applicability improvements based on the proposed model could assist relevant Standards Institutes to making improving measures.
植被屏障是乏燃料道路运输事故的一个重要环境特征。乏燃料容器在运输过程中可能会受到不可抗力因素的影响,导致乏燃料组件和容器损坏,并可能导致放射性核素逐渐从组件释放到容器中,然后释放到外部环境中。在这项工作中,考虑到针叶林植被屏障和容器类型的生长周期,通过添加衰减项和压力损失项,建立了一个基于计算流体动力学(CFD)的放射性核素扩散模型。模拟结果表明,首先,与小(II 型)容器相比,大(I 型)容器周围的流体流动对放射性核素扩散的影响更为显著。I 型容器周围的回流会导致泄漏的放射性核素向容器方向扩散,并且容器越大,由于负压梯度区域的增加,泄漏的放射性核素羽流尾部的上升幅度就越大。此外,由于生长的植被减弱了回流效应,I 型容器的放射性污染面积逐渐减小。其次,与 15 年和 23 年的植被屏障相比,在植被屏障附近,II 型容器泄漏的 I 型放射性核素的水平距离超过最大允许浓度的时间最长为 12 年。植被屏障越老,水平扩散范围越短,随着植被屏障的生长,放射性核素的扩散形状逐渐从平面变为半圆形,但这可能会导致泄漏点附近放射性积累效应更大,最大浓度为 0.54 kBq·m 的 II 型容器在 23 年的植被屏障下泄漏的 I 型放射性核素。此外,根据提出的方法提出了改进建议,这将使标准机构能够将本文所述的研究方法应用于各种情况。环境影响:与非放射性污染物相比,放射性污染物被植被屏障拦截,然后通过叶片、茎和根迁移到土壤中,从而污染周围环境。考虑到容器类型和针叶林生长的影响,建立了基于 CFD 的放射性核素扩散模型。根据假设情景的模拟结果,提出了放射性污染区域去污的建议。基于提出的模型对情景适用性的改进可以帮助相关标准机构采取改进措施。