Abstract

Artificial radionuclides ( 137Cs, 90Sr, Pu, and 241Am) are present in soils because of Nuclear Weapon Tests and accidents in nuclear facilities. Their distribution in soil depth varies according to soil characteristics, their own chemical properties, and their deposition history. For this project, we studied the atmospheric deposition of 137Cs, 90Sr, Pu, 241Am, 210Pb, and stable Pb. We compared the distribution of these elements in soil profiles from different soil types from an alpine Valley (Val Piora, Switzerland) with the distribution of selected major and trace elements in the same soils. Our goals were to explain the distribution of the radioisotopes as a function of soil parameters and to identify stable elements with analogous behaviors. We found that Pu and 241Am are relatively immobile and accumulate in the topsoil. In all soils, 90Sr is more mobile and shows some accumulations at depth into Fe–Al rich horizons. This behavior is also observed for Cu and Zn, indicating that these elements may be used as chemical analogues for the migration of 90Sr into the soil.

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