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Chernobyl radionuclides in shellfish
Institution:1. Center for Health and Environmental Risk Research, National Institute for Environmental Studies, Onogawa, Tsukuba, Ibaraki, 305-8506, Japan;2. Center for Global Environmental Research, National Institute for Environmental Studies, Onogawa, Tsukuba, Ibaraki, 305-8506, Japan;1. Department of Radiation Oncology, William Beaumont Hospital, Royal Oak, USA;2. Beaumont BioBank and Erb Family Core Molecular Laboratories, William Beaumont Hospital, Royal Oak, USA;3. Beaumont Neurosurgery, William Beaumont Hospital and Michigan Head and Spine Institute, Royal Oak, USA;4. Division of Geriatric Medicine, William Beaumont Hospital and Department of Internal Medicine, Oakland University-William Beaumont School of Medicine, Royal Oak, USA;5. Department of Psychology, Wayne State University, Detroit, USA;1. Department of Chemical Engineering and Physical Chemistry, University of Extremadura, Avda. De Elvas, s/n, 06071 Badajoz, Spain;2. Department of Plant Biology, Ecology and Earth Science, University of Extremadura, Avda. De Elvas, s/n, 06071 Badajoz, Spain;1. Laboratory for Marmoset Neural Architecture, Brain Science Institute RIKEN, 2-1 Hirosawa, Wako, Saitama 351-0198, Japan;2. Department of Physiology, Keio University School of Medicine, 35 Shinanomachi, Shinjuku, Tokyo 160-8582, Japan;3. Cold Spring Harbor Laboratory, Cold Spring Harbor, New York, NY 11724, United States
Abstract:Radionuclides from the Chernobyl accident arrived at Monaco on 30 April, 1986. A sample of Mytilus galloprovincialis collected six days later showed near-maximum levels of most radionuclides. Monitoring continued for seven months thereafter, peak concentrations being transiently as high as 480 Bq kg−1 (all soft parts, wet weight) for 103Ru. Other radionuclides detected included 132Te, 129mTe, 131I, 106Ru, 134Cs, 137Cs, 110mAg, 140Ba, 125Sb, 95Nb and 141Ce. Biological half-lives for elimination in this environment were generally around 10 days or longer and most elimination curves contained a number of components. Radionuclide contents of the mussels were predicted quite accurately from concentrations observed on air filters collected simultaneously, but were not satisfactorily explained relative to total radionuclide concentrations in the seawater even three days after peak air filter activities. The use of concentration factors from the literature did not improve the latter predictions. This suggests that the radionuclides were absorbed very rapidly from the fallout particles, rather than from radionuclides first solubilised from particles. Patella lusitanica specimens contained activities about 20–50 times higher than those in the mussels.
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