3.1 Investigations of the radioecological situation in the area of the Belarusian NPP in the pre-operational period
Instrumental studies in the area of the Belarusian NPP were carried out in August 2019. During the expedition, automotive (Fig. 4) and pedestrian gamma surveys were carried out and the activity concentrations of natural radionuclides were determined, both by a non-destructive method (using the MKS-AT6101DR) and by sampling followed by measurement on a gamma spectrometer with a HPGe detector. The contribution of detected radionuclides to the dose rate on surveyed areas is presented in Fig. 5. The detailed results of the monitoring are presented in [15, 16].
3.2 Investigations of the radioecological situation in the area of the floating nuclear thermal power plant "Akademik Lomonosov"
An example of assessing the radioecological situation was demonstrated during an expedition in October 2021 to the area of the floating thermal power plant (FNPP) “Akademik Lomonosov”, Pevek, Chukotka Autonomous Okrug. A distinctive feature of this expedition was the joint participation of representatives of public organizations, academic and university science. Public organizations can point out the main relevant issues to the objects of atomic energy use, and the scientific community provides a choice of instruments and methods for an objective answer to the needs of society.
On the territory of the floating nuclear power plant, on the territory of Pevek and surrounding area field spectrometric measurements on the surface of soils and coatings were carried out. The use of field spectrometry made it possible to quickly answer the question of what radionuclides caused the external exposure of a person in the surveyed area. The identification of radionuclides was carried out directly at the measurement site, without sampling. At least 20 spectrometric measurements with MKS-AT6101DR were carried out on the territory of the floating nuclear power plant, urban areas, and areas remote from the city.
The performed survey did not reveal the presence of artificial radionuclides in the surveyed areas. The dose rates on surveyed areas are presented in Table 1. The data from Chukothydromet on the dose rate in Pevek since 2013 were analyzed to confirm the correctness of the obtained results. The radiation background in Pevek, on FNPP and the surrounding grounds is completely formed by natural sources: natural radionuclides:40K, 226Ra, 232Th (Fig. 6) and cosmic radiation.
Table 1
– Dose rate values for FNPP and Pevek
Dose rate
|
FNPP site
|
Pevek
|
Surrounding grounds
|
Chukothydromet data for Pevek
|
Average, µSv/h
|
0.07
|
0.12
|
0.18
|
0.13
|
Min, µSv/h
|
0.05
|
0.09
|
0.04
|
0.08
|
Max, µSv/h
|
0.1
|
0.18
|
0.26
|
0.18
|
The results of the expedition indicate that for two years of operation the floating nuclear power plant did not affect to the radioecological situation in the area of its location. The results of the expedition were presented at a press conference for the mass media and demonstrated for residents of Pevek at a meeting in the city administration.
3.3 Investigation of the radioecological situation in the area of uranium mining by the underground leaching method
Public radioecological control of JSC Dalur on uranium mining by in-situ leaching was carried out in September 2020. Reviewing of 42 wells was carried out in two areas differing in life cycle. The expert analysis of the pipeline system did not reveal areas with traces of technological solution leaks on the pipe surfaces or damage to vegetation in surrounding area. The instrumental control methods used in the current project included radiometric studies of production sites and surrounding areas to determine the range of dose rates characteristic of the "background" areas. MKS-AT6101DR and MKS-AT6101S were used as instruments for measuring. Radiometric studies were carried out by the method of pedestrian and automotive gamma survey. The route of the pedestrian gamma survey was chosen to obtain the dose rate values both in the production area and in the surrounding (background) area. Moving along the selected route, the operator performed a gamma scan at the mining site, a field adjacent to the site and the nearest forest area. Field and woodland are taken as background areas. The location of the plots is shown in Fig. 7.
As a result of pedestrian gamma survey, the following data was obtained:
-
61 values of the dose rate in the background section "Forest";
-
125 values of the dose rate in the background section "Field";
-
625 dose rate values at the production site.
Samples of the obtained values of the dose rate in the indicated areas are characterized by specific values of the central tendencies and range (Table 2).
Table 2
Results of dose rate measurement by the method of pedestrian gamma survey
Dose rate
|
Background
|
Mining
|
Field
|
Forest
|
Production area
|
Average, µSv/h
|
0.051
|
0.058
|
0.115
|
Median, µSv/h
|
0.052
|
0.057
|
0.075
|
Standard deviation, µSv/h
|
0.0022
|
0.0046
|
0.0057
|
Despite the close values of the results of measuring the dose rate in the background areas "Forest" and "Field", their central tendencies are statistically significantly different, which confirms the result of comparing the samples by the t-test (p << 0.05). The values of the dose rate of gamma radiation in the area where uranium mining sites are located are specific for various landscape conditions. The abnormal values of the dose rate for the forest landscape exceed 0.053 µSv/h. Abnormal values of the dose rate for the agricultural landscape exceed 0.078 µSv/h.
To determine the reason for the significant difference between clean areas with different landscape conditions, a representative spectrometric study is required. For the comparing the dose rate values at the uranium mining sites, it is necessary to select the measurement results on clean landscapes with similar environmental conditions as background.
3.4 Radiological monitoring of the publicly accessible territory of control area of the Mayak Production Association
As a result of the Kyshtym accident in 1957, more than 20,000 km2 of the territory, later called the East Ural radioactive trace (EURT), was contaminated. The accident resulted to the release into the atmosphere of a large amount of radionuclides, including 137Cs with the longest half-life (30.17 y). Part of the territory of EURT is included in the control zone of the Mayak Production Association. In November 2021 radiological monitoring of the publicly accessible territory of control area was conducted. The aim of the study was to determine the dose rate and the activity concentration of natural radionuclides (40K, 226Ra, 232Th) and 137Cs at different sites. MKS-AT6101DR was used as instrument for measurements.
The results of measurements demonstrated the presence of 137Cs in the soil in 10 surveyed areas out of 16 (Fig. 8). The highest activity concentration of 137Cs (about 100 Bq/kg) is observed on a forest site that was not subjected to mechanical stress, therefore, 137Cs remained in the upper layers of the soil after releases due to accident.
The dose rate values are in the range from 0.046 to 0.121 µSv/h. The activity concentrations of natural radionuclides are: 40K – from 27.6 to 593.0 Bq/kg, 226Ra – from 0 to 23.7 Bq/kg, 232Th – from 0 to 39.6 Bq/kg. Fig. 9 demonstrates the contribution of individual radionuclides to the dose rate.