Institute of Mathematical Machine and System Problems, Kyiv, Ukraine.
Institute of Mathematical Machine and System Problems, Kyiv, Ukraine.
J Environ Radioact. 2019 Nov;208-209:106023. doi: 10.1016/j.jenvrad.2019.106023. Epub 2019 Jul 25.
The compartment model POSEIDON-R with an embedded dynamic food web model was used to assess Cs distributions in the Mediterranean and Black Seas during 1945-2020 due to the weapon testing and accident at the Chernobyl nuclear power plant. Three maximums of contamination of surface waters can be identified from 1950 in the Mediterranean Sea system. Two of them (in 1959 and 1963) were caused by atmospheric deposition due to the nuclear weapon testing. Third maximum in 1986 was related with the Chernobyl accident. Maximum of inventory of Cs in the Mediterranean Sea (11461 TBq) was achieved in 1968, whereas secondary maximum caused by Chernobyl accident in 1986 was almost the same (11460 TBq). The corresponding maximum in the Black Sea (3703 TBq) was reached in 1986. It is approximately two times larger than nuclear weapon tests maximum. The results of simulations conducted with generic parameters agreed well with measurements of Cs concentrations in the water, bottom sediments, and in marine organisms. The inventory in the Mediterranean Sea is most sensitive to the global deposition, whereas water exchange with Atlantic Ocean and the Black Sea plays minor role. The cumulative individual dose for the period 1945-2020 from consumption of marine products contaminated by Cs was in the range 41-130 μSv in the Mediterranean Sea and 213-274 μSv in the Black Sea. The dose increased up to 40% due to Chernobyl accident in the Mediterranean countries and 66-103% in the Black Sea countries comparatively with dose from the global deposition. A useful application of the modelling for monitoring purposes was selection of representative regions in the Mediterranean Sea (5 regions) and in the Black Sea (4 regions) using "etalon" method for classification.
采用嵌入动态食物网模型的 POSEIDON-R 箱式模型,评估了 1945 年至 2020 年期间因切尔诺贝利核电厂的武器试验和事故而在地中海和黑海的 Cs 分布情况。在地中海系统中,可以从 1950 年开始识别出三个地表水受污染的最大值。其中两个(1959 年和 1963 年)是由于核武器试验引起的大气沉积造成的。第三个最大值出现在 1986 年,与切尔诺贝利事故有关。地中海中 Cs 的库存最大值(11461 TBq)出现在 1968 年,而 1986 年因切尔诺贝利事故造成的次大值几乎相同(11460 TBq)。黑海的相应最大值(3703 TBq)出现在 1986 年。它大约是核武器试验最大值的两倍。使用通用参数进行的模拟结果与水中、底泥中和海洋生物中 Cs 浓度的测量结果吻合良好。地中海的库存对全球沉积最为敏感,而与大西洋和黑海的水交换作用则较小。1945 年至 2020 年期间,由于食用受 Cs 污染的海产品而累积的个人剂量在地中海国家为 41-130 μSv,在黑海国家为 213-274 μSv。与全球沉积造成的剂量相比,由于地中海国家的切尔诺贝利事故,剂量增加了 40%,而在黑海国家,剂量增加了 66-103%。该模型的一个有用应用是使用“标准”分类方法在地中海(5 个区域)和黑海(4 个区域)中选择有代表性的区域进行监测。