The transformation of the hydrological regime of floodplains due to climate change and anthropogenic impact on water redistribution processes within natural landscapes can significantly impact the bioavailability of long-lived radioactive isotopes of cesium and strontium. A laboratory experiment demonstrated that varying the moisture content of alluvial soil within 40–100% from its full water-holding capacity leads to the redistribution of ¹³⁷Cs and ⁹⁰Sr between different chemical forms. Soil saturation with water increases the proportion of water-soluble ¹³⁷Cs, while the proportion of water-soluble ⁹⁰Sr decreases. The ion-exchangeable form of ¹³⁷Cs remains unaffected by soil moisture. The behavior of the ion-exchangeable form of ⁹⁰Sr in response to changes in soil moisture is dependent on soil characteristics: a significant increase in the proportion of ⁹⁰Sr was observed in sod-gley soil developed on sandy alluvium as soil moisture increased; however, this phenomenon was not observed in sod-gleyed soil developed on loamy alluvium. The proportion of ¹³⁷Cs extracted by sodium tetraphenylborate increases when alluvial soils are saturated with water. Similarly, the mobile form of ⁹⁰Sr behaves in the same manner, but when soil moisture reaches 100% of its full water-holding capacity in sod-gley soil, a sharp decrease in the proportion of the mobile form of this radionuclide is observed. Overall, there is a trend towards increased proportions of bioavailable forms of ¹³⁷Cs and ⁹⁰Sr in alluvial soils with increased moisture content, although the pecularities and magnitude of this phenomenon depend on the specific soil characteristics.
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