Abstract
Characteristics of radioactive contamination of soils as a result of radiation accidents at Chernobyl nuclear power plant (USSR/Ukraine), Fukushima dai-ichi nuclear power plant (Japan), and Mayak PA (USSR/Russia) are considered. The evaluation of the efficiency methods for returning radioactively contaminated lands to farming use is given. It is shown that after a radiation accident, the major part of radionuclides is fixed in the upper 5–7 cm layer of a soil; further slow migration of a radionuclide to deeper layers of a soil occurs. Over 36 years after radiation accident, 137Cs and 90Sr radionuclides are located in a plowing horizon (0–25 cm); therefore, they are available for roots. The effectiveness of rehabilitation activities depends on physicochemical characteristics of a soil, radionuclides speciation in a soil solution, and a species of growing plant. The most efficient methods suggested for decrease of 137Cs and 90Sr radionuclides transfer from a soil to agricultural plants are transfer of the upper layer of radioactively contaminated soil to a depth of 80 cm and deeper (radionuclides transfer decreases up to a factor of 50) and addition of ferrocyanide sorbents based on natural aluminosilicates (up to a factor of 20). Addition of various ameliorators results in decrease of radionuclides transfer by up to 5 times independently of ameliorator type.
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Voronina, A.V., Semenishchev, V.S., Blinova, M.O., Sanin, P.J. (2015). Methods for Decrease of Radionuclides Transfer from Soil to Agricultural Vegetation. In: Walther, C., Gupta, D. (eds) Radionuclides in the Environment. Springer, Cham. https://doi.org/10.1007/978-3-319-22171-7_11
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DOI: https://doi.org/10.1007/978-3-319-22171-7_11
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