Rääf Christopher, Martinsson Johan, Eriksson Mats, Ewald Jens, Javid Reza G, Hjellström Martin, Isaksson Mats, Rasmussen Joel, Sterner Thomas, Finck Robert
Medical Radiation Physics, Department of Translational Medicine, Malmö, Lund University, 205 02, Malmö, Sweden.
Medical Radiation Physics, Department of Translational Medicine, Malmö, Lund University, 205 02, Malmö, Sweden.
J Environ Radioact. 2023 Dec;270:107268. doi: 10.1016/j.jenvrad.2023.107268. Epub 2023 Aug 17.
Land remediation is an important part of restoration measures after a radioactive fallout containing long-lived fission products such as Cs. In this multidisciplinary study, we focused on three main issues related to remediation of contaminated urban areas. First, we assessed how much decontamination contributes to reducing resident radiation exposure and how much this reduction depends on the timing of implemented measures. Second, we calculated direct and indirect costs of decontamination in an industrialized country such as Sweden. Finally, in a survey study, we considered reactions of Swedish citizens to being given the hypothetical option of moving to a site decontaminated after radioactive fallout and how this predicted response might influence the design of contingency plans. The main findings are that clean-up operations must be done within the first few years after a fallout to contribute significantly to reducing residual dose. If conducted within 1-2 years, large-scale decontamination can, on average, avert 20-200 manSv per km residential area and unit ground deposition of Cs (1 MBq). The estimated direct costs (in 2020 purchasing power) would amount to 100 million Euro per km decontaminated residential area (comparable to Japanese estimates after the Fukushima accident), generating 39,000 m of radioactive waste on average, mainly in the form of Cs-contaminated topsoil. In our survey study of 2291 Swedish respondents about their willingness to return to decontaminated homes, women, families with resident children, and high-income earners exhibited more skepticism about returning, even if authorities were to deem it safe. The demographic pattern in attitudes was similar to that found among evacuees in the Fukushima prefecture after 2011. We conclude that predefined ranges of measured Cs ground deposition can be used as guidance for rescue leaders in the early post-accident phase in long-term planning for affected areas. This planning should include timing and intensity of decontamination measures, duration of evacuation, and risk communication to citizens. Because some citizens expressed both high risk perception and risk aversion, however, timely and dialogic communication is unlikely to limit a shift after the incident to an older and more male-dominated population composition. There is a risk that those who can afford to do so will move away, whereas people whose wealth is locked in property (houses or businesses) will feel stuck. Perceptions of unfairness may fray the social fabric and complicate resettlement, which in some cases may mean inefficient outlay of decontamination costs. We believe that the issue of monetary compensation to affected residents requires priority in future work.
土地修复是含有铯等长寿命裂变产物的放射性沉降后恢复措施的重要组成部分。在这项多学科研究中,我们关注了与受污染城市地区修复相关的三个主要问题。首先,我们评估了去污对减少居民辐射暴露的贡献程度,以及这种减少在多大程度上取决于实施措施的时机。其次,我们计算了在瑞典这样的工业化国家进行去污的直接和间接成本。最后,在一项调查研究中,我们考虑了瑞典公民对于被给予搬到放射性沉降后已去污场地这一假设选项的反应,以及这种预测的反应可能如何影响应急计划的设计。主要研究结果是,清理行动必须在沉降后的头几年内进行,才能对减少残留剂量做出显著贡献。如果在1 - 2年内进行,大规模去污平均每平方公里居民区和每单位铯地面沉积量(1兆贝可)可避免20 - 200人希沃特的辐射剂量。估计直接成本(按2020年购买力计算)将达到每平方公里去污居民区1亿欧元(与福岛事故后日本的估计相当),平均产生39000立方米放射性废物,主要形式为受铯污染的表层土壤。在我们对2291名瑞典受访者关于他们返回已去污家园意愿的调查研究中,女性、有常住子女的家庭以及高收入者对返回表现出更多疑虑,即使当局认为这样做是安全的。态度上的人口统计学模式与2011年后福岛县撤离者中发现的模式相似。我们得出结论,测量得到的铯地面沉积量的预定义范围可作为事故后早期阶段救援负责人对受影响地区进行长期规划的指导。该规划应包括去污措施的时机和强度、疏散持续时间以及与公民的风险沟通。然而,由于一些公民既表现出高风险认知又表现出风险厌恶,及时且对话式的沟通不太可能限制事件发生后向年龄更大、男性主导程度更高的人口构成转变。存在这样一种风险,即有能力这样做的人会搬走,而财富锁定在房产(房屋或企业)中的人会感到被困住。不公平感可能会破坏社会结构并使重新安置复杂化,在某些情况下这可能意味着去污成本的低效支出。我们认为,在未来的工作中,向受影响居民提供货币补偿的问题需要优先考虑。