The paper presents data on the research of the radionuclide contamination redistribution in the ecosystems of natural lakes at the Semipalatinsk test site and adjacent territories. Natural lakes, which are the research objects, are located on the territory of the test sites, in the zone of their influence, in the zone impacted by radioactive fallout or in the "background" territories. Sampling of water, bottom sediments and plants was carried out, in which the content of radionuclides 241Am, 137Cs, 90Sr and 239+240Pu was determined. Based on the obtained quantitative data, distribution coefficients (Kd) for sediments and water, as well as concentration ratio (FV) for plants and sediments were calculated.
This article presents research findings on3H in abiotic environmental compartments, specifically, the ‘water-soil-air’ system. All of the research areas are located within the Semipalatinsk Test Site (STS): the perimeter of the ‘Degelen’ site, the riverside zone of the Shagan river and the ‘background’ area–the southeastern part of the STS (SEP). As research progressed, numerical values of3H and its species were revealed in various environmental compartments. The presence of3H was registered not only in underground nuclear test locations but also in the ‘background’ area–SEP. Maximum3H tritium concentrations in the water were detected at the ‘Degelen’ site (up to 57000±5000 Bq/kg) and the Shagan riv (up to 61500±6000 Bq/kg), in the air of the ‘Degelen’ site (up to 56±11 Bq/m3), in the soil of the ‘Degelen’ site (up to 5170±500 Bq/kg) and the Shagan riv (4100±400 Bq/kg) in the free water, at SEP (up to 1710±170 Bq/kg) in the organic constituent. Based upon all of the findings,3H was found to be readily distributed in abiotic environmental compartments depending on certain conditions. Research suggests that water plays a key role in3H migration processes in the natural system of interest. The second most but equally important constituent is soil and microorganisms of plant and animal origin living there. These assumptions are indirectly proven by research findings that show the HTO and HT air concentration dynamics depending on the sampling location.
This study aimed to assess the activity contamination levels and transfer of artificial radionuclides (241Am, 137Cs, 90Sr, and 239+240Pu) from soils to plants at underground nuclear test borehole locations in the Sary-Uzen site of the Semipalatinsk Test Site. Soil and vegetation samples were collected near warfare boreholes with different contamination patterns, conditionally "background" areas, and fallout plume sites. Peak activity concentrations in soils were recorded near borehole No. 102 for 137Cs and near borehole No. 215 for 241Am, 90Sr, and 239+240Pu. In plants, the highest 137Cs and 90Sr were observed near borehole No. 102, and that of 241Am and 239+240Pu near borehole No. 215. Transfer factors indicated that plant uptake followed the order: 90Sr > 137Cs > 239+240Pu > 241Am. Littoral-aquatic plants accumulated more 90Sr, whereas terrestrial plants accumulated more 239+240Pu. The maximum total exposure dose rate to vegetation reached 74 µGy/day. These findings highlight the influence of test type and contamination pattern on radionuclide behavior in ecosystems and provide a basis for radiological risk assessment in former nuclear test areas.