“…Stabil ity classes make it pos si ble to de ter mine the depend ence of the pa ram e ters of ver ti cal and hor i zon tal dis per sion of con tam i nants in the ABL, un der dif ferent weather con di tions, used in math e mat i cal mod els for cal cu lat ing the con cen tra tion fields of con tam inants. The ad van tage of the Pasquill-Vogt sta bil ity class sys tem over the Pasquill sta bil ity classes is that there is no need to use ad di tional data from me te o rolog i cal sta tions to de ter mine the at mo spheric sta bil ity classes and they can be de ter mined based on the data from the SODAR/RASS mea sur ing com plex, based on the wind speed at a height of 10 m and the ver ti cal gra di ent of the air tem per a ture in the lower 120-me ter of the ABL [5].…”
Section: Re Sults and Discussionmentioning
confidence: 99%
“…The ob ser va tion mon i tor ing sys tem, which includes the SODAR/RASS mea sur ing com plex and a data pro cess ing sub sys tem, car ries out au to matic record ing and ac cu mu la tion of the mea sure ment data. This sub sys tem pro vides for main tain ing a da ta base and cal cu lat ing a set of the ABL dis per sion char ac teris tics by means of the spe cially de vel oped soft ware [5].…”
Section: Meth Od Ol Ogymentioning
confidence: 99%
“…There fore, at var i ous stages of the NPP life cy cle (con struc tion, op er a tion, and de com mis sion ing) a detailed study of the ABL at mo spheric dis per sion con ditions is car ried out at the NPP sites. In par tic u lar, it is en vis aged to de velop au to mated ra di a tion mon i tor ing sys tems and their main com po nents -ABL pa ram e ters mea sur ing sys tems [5]. Ac cord ing to [5,6], the key tasks of such mon i tor ing are: -to de ter mine the ABL dis per sion char ac ter is tics that are re quired for cal cu la tions of the po ten tial ra di a tion im pact on plant per son nel, the pub lic and the en vi ron ment in case of vi o la tions in normal NPP op er a tion, in clud ing ac ci dents, -to pre dict and timely de tect the trends in fluc tu ations of the ABL dis per sion char ac ter is tics over time, and -to de velop rec om men da tions aimed at mit i gat ing the ad verse im pact of NPP on the en vi ron ment.…”
Section: Introductionmentioning
confidence: 99%
“…In par tic u lar, it is en vis aged to de velop au to mated ra di a tion mon i tor ing sys tems and their main com po nents -ABL pa ram e ters mea sur ing sys tems [5]. Ac cord ing to [5,6], the key tasks of such mon i tor ing are: -to de ter mine the ABL dis per sion char ac ter is tics that are re quired for cal cu la tions of the po ten tial ra di a tion im pact on plant per son nel, the pub lic and the en vi ron ment in case of vi o la tions in normal NPP op er a tion, in clud ing ac ci dents, -to pre dict and timely de tect the trends in fluc tu ations of the ABL dis per sion char ac ter is tics over time, and -to de velop rec om men da tions aimed at mit i gat ing the ad verse im pact of NPP on the en vi ron ment. The ABL mon i tor ing pro vides for im ple men tation of con tin u ous ob ser va tion of the ABL sta tus, and first of all, the wind speed and di rec tion, as well as the air tem per a ture, which de ter mine the mode of at mospheric dis per sion.…”
Due to the fact that the potential threat to the health to the public living
near nuclear power plants is largely determined by the level of air pollution
by radionuclides, identification of the dispersion conditions of pollutants
in the atmospheric boundary layer is of great importance in the development
of engineering protection means for nuclear facilities. In turn, the
engineering protection of nuclear power plants provides for the development
of automated radiation monitoring systems and their main components, i. e.
atmospheric boundary layer status monitoring systems. When analyzing and
predicting the radiation situation in the vicinity of nuclear power plants,
the determination of atmospheric dispersion variability parameters over time
is essential. This research is aimed at assessing interannual and
intra-annual variability of atmospheric dispersion parameters in the
Belorussian nuclear power plant siting region based on the atmospheric
boundary layer monitoring data. This study has revealed the relative
interannual stability of the main average annual atmospheric dispersion
characteristics throughout the observation period in 2015-2019. At the same
time, the average seasonal values of the atmospheric boundary layer
dispersion parameters are characterized by significant fluctuations thereof
over the annual course. The feasibility of such monitoring for other
potentially hazardous industrial facilities, such as thermal power plants and
chemical plants, is also noted.
“…Stabil ity classes make it pos si ble to de ter mine the depend ence of the pa ram e ters of ver ti cal and hor i zon tal dis per sion of con tam i nants in the ABL, un der dif ferent weather con di tions, used in math e mat i cal mod els for cal cu lat ing the con cen tra tion fields of con tam inants. The ad van tage of the Pasquill-Vogt sta bil ity class sys tem over the Pasquill sta bil ity classes is that there is no need to use ad di tional data from me te o rolog i cal sta tions to de ter mine the at mo spheric sta bil ity classes and they can be de ter mined based on the data from the SODAR/RASS mea sur ing com plex, based on the wind speed at a height of 10 m and the ver ti cal gra di ent of the air tem per a ture in the lower 120-me ter of the ABL [5].…”
Section: Re Sults and Discussionmentioning
confidence: 99%
“…The ob ser va tion mon i tor ing sys tem, which includes the SODAR/RASS mea sur ing com plex and a data pro cess ing sub sys tem, car ries out au to matic record ing and ac cu mu la tion of the mea sure ment data. This sub sys tem pro vides for main tain ing a da ta base and cal cu lat ing a set of the ABL dis per sion char ac teris tics by means of the spe cially de vel oped soft ware [5].…”
Section: Meth Od Ol Ogymentioning
confidence: 99%
“…There fore, at var i ous stages of the NPP life cy cle (con struc tion, op er a tion, and de com mis sion ing) a detailed study of the ABL at mo spheric dis per sion con ditions is car ried out at the NPP sites. In par tic u lar, it is en vis aged to de velop au to mated ra di a tion mon i tor ing sys tems and their main com po nents -ABL pa ram e ters mea sur ing sys tems [5]. Ac cord ing to [5,6], the key tasks of such mon i tor ing are: -to de ter mine the ABL dis per sion char ac ter is tics that are re quired for cal cu la tions of the po ten tial ra di a tion im pact on plant per son nel, the pub lic and the en vi ron ment in case of vi o la tions in normal NPP op er a tion, in clud ing ac ci dents, -to pre dict and timely de tect the trends in fluc tu ations of the ABL dis per sion char ac ter is tics over time, and -to de velop rec om men da tions aimed at mit i gat ing the ad verse im pact of NPP on the en vi ron ment.…”
Section: Introductionmentioning
confidence: 99%
“…In par tic u lar, it is en vis aged to de velop au to mated ra di a tion mon i tor ing sys tems and their main com po nents -ABL pa ram e ters mea sur ing sys tems [5]. Ac cord ing to [5,6], the key tasks of such mon i tor ing are: -to de ter mine the ABL dis per sion char ac ter is tics that are re quired for cal cu la tions of the po ten tial ra di a tion im pact on plant per son nel, the pub lic and the en vi ron ment in case of vi o la tions in normal NPP op er a tion, in clud ing ac ci dents, -to pre dict and timely de tect the trends in fluc tu ations of the ABL dis per sion char ac ter is tics over time, and -to de velop rec om men da tions aimed at mit i gat ing the ad verse im pact of NPP on the en vi ron ment. The ABL mon i tor ing pro vides for im ple men tation of con tin u ous ob ser va tion of the ABL sta tus, and first of all, the wind speed and di rec tion, as well as the air tem per a ture, which de ter mine the mode of at mospheric dis per sion.…”
Due to the fact that the potential threat to the health to the public living
near nuclear power plants is largely determined by the level of air pollution
by radionuclides, identification of the dispersion conditions of pollutants
in the atmospheric boundary layer is of great importance in the development
of engineering protection means for nuclear facilities. In turn, the
engineering protection of nuclear power plants provides for the development
of automated radiation monitoring systems and their main components, i. e.
atmospheric boundary layer status monitoring systems. When analyzing and
predicting the radiation situation in the vicinity of nuclear power plants,
the determination of atmospheric dispersion variability parameters over time
is essential. This research is aimed at assessing interannual and
intra-annual variability of atmospheric dispersion parameters in the
Belorussian nuclear power plant siting region based on the atmospheric
boundary layer monitoring data. This study has revealed the relative
interannual stability of the main average annual atmospheric dispersion
characteristics throughout the observation period in 2015-2019. At the same
time, the average seasonal values of the atmospheric boundary layer
dispersion parameters are characterized by significant fluctuations thereof
over the annual course. The feasibility of such monitoring for other
potentially hazardous industrial facilities, such as thermal power plants and
chemical plants, is also noted.
“…The comprehensive environmental monitoring program includes hygienic parameters for assessing radiation doses and the control of ecological contamination. Soil [3], bottom riverbed sediments [3,4], surface water [5] and the atmospheric boundary layer [6] can be selected as objects of environmental studies. The main technogenic radionuclides present in discharges, emissions and radioactive waste during the operation of nuclear power plants, as well as natural radionuclides, have been selected as controlled parameters [7,8].…”
Field studies on the pre-operational period of a Belarusian NPP have allowed us to determine the "background" level of gamma-emitting radionuclides in individual components of the environment. The results of measuring the dose rate at the NPP construction site are from 0.048 to 0.089 μSv/h. External radiation in the surveyed area is at 96% due to 40 K, 226 Ra and 232 Th. The radionuclides in the surface soil layer are: 40 K -from 530 to 700 Bq/kg; 226 Ra -from 30 to 55 Bq/kg; and 232 Th -from 17 to 35 Bq/kg; 137 Cs from 2 to 13 Bq/kg. The dose rate in the floodplain of the Viliya River from 0.033 to 0.082 μSv/h. The activity concentrations of the radionuclides in the surface soil layer of the floodplain of the Viliya River are: 40 K -from 390 to 690 Bq/kg; 226 Ra -from 33 to 50 Bq/kg; 232 Th -from 15 to 50 Bq/kg; 137 Cs -from 3 to 12 Bq/kg. The activity concentration of carbon-14 and tritium in the dominant vegetation species were determined to be: from 74.4 to 111.5 pMC and less than lower range limit, respectively.
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