Nielsen S P, Iosjpe M, Strand P
Department of Environmental Science and Technology, MIL-114, Risø National Laboratory, Roskilde, Denmark.
Sci Total Environ. 1997 Aug 25;202(1-3):135-46. doi: 10.1016/s0048-9697(97)00110-1.
A box model for the dispersion of radionuclides in the marine environment covering the Arctic Ocean and the North Atlantic Ocean has been constructed. Collective doses from ingestion pathways have been calculated from unit releases of the radionuclides 3H, 60Co, 63Ni, 90Sr, 129I, 137Cs, 239Pu and 241Am into a fjord on the east coast of NovayaZemlya. The results show that doses for the shorter-lived radionuclides (e.g. 137Cs) are derived mainly from seafood production in the Barents Sea. Doses from the longer-lived radionuclides (e.g. 239Pu) are delivered through marine produce further away from the Arctic Ocean. Collective doses were calculated for two release scenarios, both of which are based on information of the dumping of radioactive waste in the Barents and Kara Seas by the former Soviet Union and on preliminary information from the International Arctic Sea Assessment Programme. A worst-case scenario was assumed according to which all radionuclides in liquid and solid radioactive waste were available for dispersion in the marine environment at the time of dumping. Release of radionuclides from spent nuclear fuel was assumed to take place by direct corrosion of the fuel ignoring the barriers that prevent direct contact between the fuel and the seawater. The second scenario selected assumed that releases of radionuclides from spent nuclear fuel do not occur until after failure of the protective barriers. All other liquid and solid radioactive waste was assumed to be available for dispersion at the time of discharge in both scenarios. The estimated collective dose for the worst-case scenario was about 9 manSv and that for the second scenario was about 3 manSv. In both cases, 137Cs is the radionuclide predicted to dominate the collective doses as well as the peak collective dose rates.
构建了一个用于模拟放射性核素在覆盖北冰洋和北大西洋的海洋环境中扩散的箱式模型。已根据放射性核素³H、⁶⁰Co、⁶³Ni、⁹⁰Sr、¹²⁹I、¹³⁷Cs、²³⁹Pu和²⁴¹Am向新地岛东海岸一个峡湾的单位释放量,计算了摄入途径的集体剂量。结果表明,短寿命放射性核素(如¹³⁷Cs)的剂量主要来自巴伦支海的海产品生产。长寿命放射性核素(如²³⁹Pu)的剂量则通过远离北冰洋的海产品传递。针对两种释放情景计算了集体剂量,这两种情景均基于前苏联在巴伦支海和喀拉海倾倒放射性废物的信息以及国际北极海评估计划的初步信息。假定了一种最坏情况情景,即倾倒时液态和固态放射性废物中的所有放射性核素都可在海洋环境中扩散。假定乏核燃料中的放射性核素通过燃料的直接腐蚀释放,而忽略防止燃料与海水直接接触的屏障。所选的第二种情景假定,直到防护屏障失效后才会发生乏核燃料中放射性核素的释放。在两种情景中,假定所有其他液态和固态放射性废物在排放时都可用于扩散。最坏情况情景的估计集体剂量约为9人希沃特,第二种情景的估计集体剂量约为3人希沃特。在这两种情况下,¹³⁷Cs都是预计在集体剂量以及集体剂量率峰值方面占主导地位的放射性核素。