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    Study of the Power Beam Pattern of RATAN-600 During the Deep RZF Survey (1998-2003)

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    This paper proposes a method for constructing an experimental power beam pattern (PB) of RATAN-600 based on the sample of NVSS sources observed in the process of a deep sky survey near local zenith. The data obtained from observations of radio sources at wave 7.6 cm in nine bands of the survey (the 2002 and 2003 sets) are used to construct vertical PB of the telescope at rather large offsets from the central horizontal section of the PB (+/-36'). The experimental PBs obtained using different methods are compared and the root-mean-square deviations of the experimental PB from the corresponding computed PB are determined. The stability of the power beam pattern in its central part (+/-6') during the RATAN-600 Zenith Field (RZF) survey (1998-2003) and the accuracies of the fluxes of the sources observed within the framework of this survey and included into the RZF catalog are estimated.Comment: 15 pages, 17 figure

    Π Π°Π΄ΠΈΠ°Ρ†ΠΈΠΎΠ½Π½ΠΎ-гигиСничСская ΠΎΡ†Π΅Π½ΠΊΠ° содСрТания ΠΈ распрСдСлСния 90Sr ΠΈ 137Cs Π² ΠΈΡ…Ρ‚ΠΈΠΎΡ„Π°ΡƒΠ½Π΅ Обь-Π˜Ρ€Ρ‚Ρ‹ΡˆΡΠΊΠΎΠΉ Ρ€Π΅Ρ‡Π½ΠΎΠΉ систСмы

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    The aim of the work is the radiation-hygienic assessment of 90Sr andΒ  137Cs content in fish of the Ob-Irtysh river system and the study of the basic laws of the radionuclides accumulation in the ichthyofauna of these rivers. To perform this task, long-term results of radioecological studies of fish from the Techa, Irtysh and Ob rivers for the period 2004-2016 were used. Fish as a food product was evaluated according to two criteria: a) permissible levels of radionuclides specific activity (SanPiN 2.3.2.1078-01); b) using the indicator of conformity Π’ and uncertainty of its definition Ξ”Π’ (GOST 32161-2013 and GOST 32163-2013). It is shown that a higher content of radionuclides is observed in the ichthyofauna of the Techa river (1379.1 Bq/kg for 90Sr and 41.9 Bq/kg for 137Cs). On the Ob and Irtysh rivers, the average specific activity of radionuclides in fish was significantly lower and slightly changed during the surveyed area: for 90Sr in the range of 6.0 Γ· 8.1 Bq/kg (mean 6.8), for 137Cs – 0.6 Γ· 1.9 Bq/kg (mean 1.3). Assessment for compliance with radiation safety criteria using the indicator of compliance and its uncertainty (Π’+Ξ”Π’) confirmed the unsuitability of use for food purposes by the radiation factor of all studied fish species from the Techa river (45Γ·55 >1). Fish from all other studied areas of the Ob-Irtysh river system can be used for food without restrictions (0,06Γ·0,53 < 1). The distribution of 90Sr and 137Cs in the ichthyofauna of the Ob-Irtysh river system part over a 2400 km is presented in the form of empirical regression models. The models describe a sharp decrease in the radionuclides specific activity in fish in the Techa and Iset rivers by two orders for 90Sr (from 2000 to 20 Bq/kg), and by one order for 137Cs (from 40 to 2 Bq/kg). With a high degree of reliability (R2>0.86 for 90Sr and R2>0.92 for 137Cs), the presence of power relationships between the content of radionuclides in the ichthyofauna and their content in water was shown, with adequacy confirmed by Fisher’s F-criteria. This can be used for a preliminary assessment of the radionuclides level in fish based on the results of measurements of the average annual concentrations of these radionuclides in water.ЦСлью настоящСй Ρ€Π°Π±ΠΎΡ‚Ρ‹ являСтся Ρ€Π°Π΄ΠΈΠ°Ρ†ΠΈΠΎΠ½Π½ΠΎ-гигиСничСская ΠΎΡ†Π΅Π½ΠΊΠ° содСрТания 90Sr ΠΈ 137Cs Π² Ρ€Ρ‹Π±Π΅ Обь-Π˜Ρ€Ρ‚Ρ‹ΡˆΡΠΊΠΎΠΉ Ρ€Π΅Ρ‡Π½ΠΎΠΉ систСмы ΠΈ ΠΈΠ·ΡƒΡ‡Π΅Π½ΠΈΠ΅ основных закономСрностСй накоплСния Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² ΠΈΡ…Ρ‚ΠΈΠΎΡ„Π°ΡƒΠ½Π΅ этих Ρ€Π΅ΠΊ. Для выполнСния Π΄Π°Π½Π½ΠΎΠΉ Π·Π°Π΄Π°Ρ‡ΠΈ Π±Ρ‹Π»ΠΈ ΠΈΡΠΏΠΎΠ»ΡŒΠ·ΠΎΠ²Π°Π½Ρ‹ ΠΌΠ½ΠΎΠ³ΠΎΠ»Π΅Ρ‚Π½ΠΈΠ΅ Ρ€Π΅Π·ΡƒΠ»ΡŒΡ‚Π°Ρ‚Ρ‹ радиоэкологичСских исслСдований Ρ€Ρ‹Π±Ρ‹ ΠΈΠ· Ρ€Π΅ΠΊ Π’Π΅Ρ‡Π°, Π˜Ρ€Ρ‚Ρ‹Ρˆ ΠΈ Обь Π·Π° ΠΏΠ΅Ρ€ΠΈΠΎΠ΄ 2004–2016 Π³Π³. Π’Ρ‹ΠΏΠΎΠ»Π½Π΅Π½Π° ΠΎΡ†Π΅Π½ΠΊΠ° Ρ€Ρ‹Π±Ρ‹ ΠΊΠ°ΠΊ ΠΏΠΈΡ‰Π΅Π²ΠΎΠ³ΠΎ ΠΏΡ€ΠΎΠ΄ΡƒΠΊΡ‚Π° ΠΏΠΎ Π΄Π²ΡƒΠΌ критСриям: Π°) допустимыС ΡƒΡ€ΠΎΠ²Π½ΠΈ ΡƒΠ΄Π΅Π»ΡŒΠ½ΠΎΠΉ активности Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² (БанПиН 2.3.2.1078-01); Π±) с использованиСм показатСля соотвСтствия Π’ ΠΈ нСопрСдСлСнности Π΅Π³ΠΎ опрСдСлСния Ξ”Π’ (Π“ΠžΠ‘Π’ 32161-2013 ΠΈ Π“ΠžΠ‘Π’ 32163-2013). Показано, Ρ‡Ρ‚ΠΎ Π±ΠΎΠ»Π΅Π΅ высокоС содСрТаниС Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π½Π°Π±Π»ΡŽΠ΄Π°Π΅Ρ‚ΡΡ Π² ΠΈΡ…Ρ‚ΠΈΠΎΡ„Π°ΡƒΠ½Π΅ Ρ€Π΅ΠΊΠΈ Π’Π΅Ρ‡Π° (1379,1 Π‘ΠΊ/ΠΊΠ³ ΠΏΠΎ 90Sr ΠΈ 41,9 Π‘ΠΊ/ΠΊΠ³ ΠΏΠΎ 137Cs). На Ρ€Π΅ΠΊΠ°Ρ… Обь ΠΈ Π˜Ρ€Ρ‚Ρ‹Ρˆ срСдниС ΠΏΠΎΠΊΠ°Π·Π°Ρ‚Π΅Π»ΠΈ ΡƒΠ΄Π΅Π»ΡŒΠ½ΠΎΠΉ активности Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² Ρ€Ρ‹Π±Π΅ Π±Ρ‹Π»ΠΈ сущСствСнно Π½ΠΈΠΆΠ΅ ΠΈ слабо измСнялись Π½Π° протяТСнии обслСдованного участка: для 90Sr Π² Π΄ΠΈΠ°ΠΏΠ°Π·ΠΎΠ½Π΅ 6,0–8,1 Π‘ΠΊ/ΠΊΠ³ (срСднСС 6,8), для 137Cs – 0,6–1,9 Π‘ΠΊ/ΠΊΠ³ (срСднСС 1,3). ΠžΡ†Π΅Π½ΠΊΠ° Π½Π° соотвСтствиС критСриям Ρ€Π°Π΄ΠΈΠ°Ρ†ΠΈΠΎΠ½Π½ΠΎΠΉ бСзопасности с использованиСм показатСля соотвСтствия Π’ ΠΈ Π΅Π³ΠΎ нСопрСдСлСнности Ξ”Π’ (Π’+Ξ”Π’) ΠΏΠΎΠ΄Ρ‚Π²Π΅Ρ€Π΄ΠΈΠ»Π° Π½Π΅ΠΏΡ€ΠΈΠ³ΠΎΠ΄Π½ΠΎΡΡ‚ΡŒ использования Π² ΠΏΠΈΡ‰Π΅Π²Ρ‹Ρ… цСлях ΠΏΠΎ Ρ€Π°Π΄ΠΈΠ°Ρ†ΠΈΠΎΠ½Π½ΠΎΠΌΡƒ Ρ„Π°ΠΊΡ‚ΠΎΡ€Ρƒ всСх исслСдованных Π²ΠΈΠ΄ΠΎΠ² Ρ€Ρ‹Π± ΠΈΠ· Ρ€. Π’Π΅Ρ‡ΠΈ (45–55 >1). Π Ρ‹Π±Π° ΠΈΠ· всСх ΠΎΡΡ‚Π°Π»ΡŒΠ½Ρ‹Ρ… исслСдованных участков Обь-Π˜Ρ€Ρ‚Ρ‹ΡˆΡΠΊΠΎΠΉ Ρ€Π΅Ρ‡Π½ΠΎΠΉ систСмы ΠΌΠΎΠΆΠ΅Ρ‚ Π±Ρ‹Ρ‚ΡŒ использована Π² ΠΏΠΈΡ‰Ρƒ Π±Π΅Π· ΠΎΠ³Ρ€Π°Π½ΠΈΡ‡Π΅Π½ΠΈΠΉ (0,06–0,53 < 1). ЗакономСрности распрСдСлСния 90Sr ΠΈ 137Cs Π² ΠΈΡ…Ρ‚ΠΈΠΎΡ„Π°ΡƒΠ½Π΅ Обь-Π˜Ρ€Ρ‚Ρ‹ΡˆΡΠΊΠΎΠΉ Ρ€Π΅Ρ‡Π½ΠΎΠΉ систСмы Π½Π° участкС ΠΏΡ€ΠΎΡ‚ΡΠΆΠ΅Π½Π½ΠΎΡΡ‚ΡŒΡŽ 2400 ΠΊΠΌ прСдставлСны Π² Π²ΠΈΠ΄Π΅ эмпиричСских рСгрСссионных ΠΌΠΎΠ΄Π΅Π»Π΅ΠΉ. МодСли ΠΎΠΏΠΈΡΡ‹Π²Π°ΡŽΡ‚ Ρ€Π΅Π·ΠΊΠΎΠ΅ сниТСниС ΡƒΠ΄Π΅Π»ΡŒΠ½ΠΎΠΉ активности Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² Ρ€Ρ‹Π±Π΅ Π½Π° участкС Ρ€Π΅ΠΊ Π’Π΅Ρ‡Π° – Π˜ΡΠ΅Ρ‚ΡŒ Π½Π° Π΄Π²Π° порядка Π²Π΅Π»ΠΈΡ‡ΠΈΠ½ ΠΏΠΎ 90Sr (с 2000 Π΄ΠΎ 20 Π‘ΠΊ/ΠΊΠ³) ΠΈ Π½Π° ΠΎΠ΄ΠΈΠ½ порядок ΠΏΠΎ 137Cs (с 40 Π΄ΠΎ 2 Π‘ΠΊ/ΠΊΠ³). Π‘ высокой ΡΡ‚Π΅ΠΏΠ΅Π½ΡŒΡŽ достовСрности (R2 >0,86 для 90Sr ΠΈ R2 >0,92 для 137Cs) ΠΏΠΎΠΊΠ°Π·Π°Π½ΠΎ Π½Π°Π»ΠΈΡ‡ΠΈΠ΅ стСпСнных зависимостСй ΠΌΠ΅ΠΆΠ΄Ρƒ содСрТаниСм Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² ΠΈΡ…Ρ‚ΠΈΠΎΡ„Π°ΡƒΠ½Π΅ ΠΈ ΠΈΡ… содСрТаниСм Π² Π²ΠΎΠ΄Π΅, с Π°Π΄Π΅ΠΊΠ²Π°Ρ‚Π½ΠΎΡΡ‚ΡŒΡŽ, ΠΏΠΎΠ΄Ρ‚Π²Π΅Ρ€ΠΆΠ΄Π΅Π½Π½ΠΎΠΉ критСриями Π€ΠΈΡˆΠ΅Ρ€Π°. Π­Ρ‚ΠΎ ΠΌΠΎΠΆΠ΅Ρ‚ Π±Ρ‹Ρ‚ΡŒ использовано для ΠΏΡ€Π΅Π΄Π²Π°Ρ€ΠΈΡ‚Π΅Π»ΡŒΠ½ΠΎΠΉ ΠΎΡ†Π΅Π½ΠΊΠΈ уровня содСрТания Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² Ρ€Ρ‹Π±Π΅ Π½Π° основС Ρ€Π΅Π·ΡƒΠ»ΡŒΡ‚Π°Ρ‚ΠΎΠ² ΠΈΠ·ΠΌΠ΅Ρ€Π΅Π½ΠΈΠΉ срСднСгодовых ΠΊΠΎΠ½Ρ†Π΅Π½Ρ‚Ρ€Π°Ρ†ΠΈΠΉ этих Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² Π²ΠΎΠ΄Π΅

    ΠžΡ†Π΅Π½ΠΊΠ° влияния эксплуатации Ρ€Π΅Π°ΠΊΡ‚ΠΎΡ€Π° БН-800 Π½Π° содСрТаниС Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² мСстных ΠΏΡ€ΠΎΠ΄ΡƒΠΊΡ‚Π°Ρ… питания Ρ€Π°ΠΉΠΎΠ½Π° БСлоярской АЭБ

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    The research results are presented as an analysis of long-term data on the effect of gas-aerosol emissions and liquid discharges of Beloyarsk NPP and the Institute of Reactor Materials on the content of artificial radionuclides in local foodstuffs. It was noted that the distance and directions from radiation-hazardous facilities do not significantly affect the accumulation of 90Sr and 137Cs in potatoes and milk. The investigation of a wide range of foodstuffs from the private households of 23 settlements, forests, rivers, and a reservoir of the 30-km zone of the Beloyarsk NPP influence showed that the operation of the BN-800 reactor since 2016 did not lead to a registered increase in the content of artificial radionuclides in agricultural and natural foodstuffs. The maximum specific activities of 90Sr (0.84 Bq/kg) and 137Cs (0.26 Bq/kg) in root vegetables, potatoes, melons and vegetables were noted before the start of operation of the new power unit and were 45 and 300 times, respectively, lower than the current SanPiN standards. The highest content of 90Sr in milk (0.41 Bq/l) was 60 times lower than the requirements of SanPiN, 137Cs (0.11 Bq/l) was 900 times less than the permissible levels. In poultry, the specific activity of 90Sr (0.2-0.3 Bq/kg) and 137Cs (0.13-0.16 Bq/kg) has remained stable low in recent years, and the standardised content of 137Cs in beef (maximum 0.12 Bq/kg) more than 1.5 thousand times lower than the requirements of SanPiN. The highest concentration of 137Cs in wild berries, found in strawberries (1.27 Bq/kg), was 125 times less than SanPiN standards. The content of 90Sr in mushrooms was at the level of 0.1-2.5 Bq/kg, the content of 137Cs is slightly higher than - 0.6-5.8 Bq/kg. The maximum recorded specific activity of 137Cs in mushrooms was more than 80 times lower than the requirements of SanPiN. During the observation period, a decrease of up to 20% or more in the content of artificial radionuclides in samples of 5 fish species was noted; the maximum levels of 90Sr and 137Cs in it were 14 times lower than the strictest SanPiN standards (using fish for baby food). Selective radiation monitoring of foodstuffs of Beloyarsk NPP area aimed at 3H and 14C showed that the content of these radionuclides in foodstuffs was low, close to the background level. In agricultural products, 3H and 14C accumulated to a greater extent in potatoes and milk, and in natural products – in rough boletus and bream. There was noted a need to continue research on the accumulation of 3H and 14C in foodstuffs of Beloyarsk NPP vicinity.Π’ Ρ€Π°Π±ΠΎΡ‚Π΅ прСдставлСн Π°Π½Π°Π»ΠΈΠ· ΠΌΠ½ΠΎΠ³ΠΎΠ»Π΅Ρ‚Π½ΠΈΡ… Π΄Π°Π½Π½Ρ‹Ρ… ΠΏΠΎ влиянию Π³Π°Π·ΠΎΠ°ΡΡ€ΠΎΠ·ΠΎΠ»ΡŒΠ½Ρ‹Ρ… выбросов ΠΈ ΠΆΠΈΠ΄ΠΊΠΈΡ… сбросов БСлоярской АЭБ ΠΈ Π˜Π½ΡΡ‚ΠΈΡ‚ΡƒΡ‚Π° Ρ€Π΅Π°ΠΊΡ‚ΠΎΡ€Π½Ρ‹Ρ… ΠΌΠ°Ρ‚Π΅Ρ€ΠΈΠ°Π»ΠΎΠ² Π½Π° содСрТаниС Ρ‚Π΅Ρ…Π½ΠΎΠ³Π΅Π½Π½Ρ‹Ρ… Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² мСстных ΠΏΠΈΡ‰Π΅Π²Ρ‹Ρ… ΠΏΡ€ΠΎΠ΄ΡƒΠΊΡ‚Π°Ρ…. ΠžΡ‚ΠΌΠ΅Ρ‡Π΅Π½ΠΎ, Ρ‡Ρ‚ΠΎ расстояниС ΠΈ направлСния ΠΎΡ‚ Ρ€Π°Π΄ΠΈΠ°Ρ†ΠΈΠΎΠ½Π½ΠΎ опасных ΠΎΠ±ΡŠΠ΅ΠΊΡ‚ΠΎΠ² Π·Π½Π°Ρ‡ΠΈΠΌΠΎ Π½Π΅ Π²Π»ΠΈΡΡŽΡ‚ Π½Π° Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΠ΅ 90Sr ΠΈ 137Cs Π² ΠΊΠ°Ρ€Ρ‚ΠΎΡ„Π΅Π»Π΅ ΠΈ ΠΌΠΎΠ»ΠΎΠΊΠ΅. На ΠΏΡ€ΠΈΠΌΠ΅Ρ€Π΅ ΡˆΠΈΡ€ΠΎΠΊΠΎΠ³ΠΎ ряда ΠΏΡ€ΠΎΠ΄ΡƒΠΊΡ‚ΠΎΠ² питания ΠΈΠ· частного сСктора 23 насСлСнных ΠΏΡƒΠ½ΠΊΡ‚ΠΎΠ², лСсов, Ρ€Π΅ΠΊ ΠΈ Π²ΠΎΠ΄ΠΎΡ…Ρ€Π°Π½ΠΈΠ»ΠΈΡ‰Π° 30-ΠΊΠΈΠ»ΠΎΠΌΠ΅Ρ‚Ρ€Π²ΠΎΠΉ Π·ΠΎΠ½Ρ‹ влияния БСлоярской АЭБ ΠΏΠΎΠΊΠ°Π·Π°Π½ΠΎ, Ρ‡Ρ‚ΠΎ эксплуатация с 2016 Π³. Ρ€Π΅Π°ΠΊΡ‚ΠΎΡ€Π° БН-800 Π½Π΅ ΠΏΡ€ΠΈΠ²Π΅Π»Π° ΠΊ рСгистрируСмому ΡƒΠ²Π΅Π»ΠΈΡ‡Π΅Π½ΠΈΡŽ содСрТания Ρ‚Π΅Ρ…Π½ΠΎΠ³Π΅Π½Π½Ρ‹Ρ… Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² ΡΠ΅Π»ΡŒΡΠΊΠΎΡ…ΠΎΠ·ΡΠΉΡΡ‚Π²Π΅Π½Π½ΠΎΠΉ ΠΈ ΠΏΡ€ΠΈΡ€ΠΎΠ΄Π½ΠΎΠΉ ΠΏΠΈΡ‰Π΅Π²ΠΎΠΉ ΠΏΡ€ΠΎΠ΄ΡƒΠΊΡ†ΠΈΠΈ. ΠœΠ°ΠΊΡΠΈΠΌΠ°Π»ΡŒΠ½Ρ‹Π΅ ΡƒΠ΄Π΅Π»ΡŒΠ½Ρ‹Π΅ активности 90Sr (0,84 Π‘ΠΊ/ΠΊΠ³) ΠΈ 137Cs (0,26 Π‘ΠΊ/ΠΊΠ³) Π² ΠΊΠΎΡ€Π½Π΅ΠΏΠ»ΠΎΠ΄Π°Ρ…, ΠΊΠ°Ρ€Ρ‚ΠΎΡ„Π΅Π»Π΅, Π±Π°Ρ…Ρ‡Π΅Π²Ρ‹Ρ… ΠΈ ΠΎΠ²ΠΎΡ‰Π°Ρ… ΠΎΡ‚ΠΌΠ΅Ρ‡Π°Π»ΠΈΡΡŒ Π΄ΠΎ Π½Π°Ρ‡Π°Π»Π° эксплуатации Π½ΠΎΠ²ΠΎΠ³ΠΎ энСргоблока ΠΈ Π±Ρ‹Π»ΠΈ Π² 45 ΠΈ 300 Ρ€Π°Π· соотвСтствСнно Π½ΠΈΠΆΠ΅ Π΄Π΅ΠΉΡΡ‚Π²ΡƒΡŽΡ‰ΠΈΡ… Π½ΠΎΡ€ΠΌΠ°Ρ‚ΠΈΠ²ΠΎΠ² БанПиН. НаиболСС высокоС содСрТаниС Π² ΠΌΠΎΠ»ΠΎΠΊΠ΅ 90Sr (0,41 Π‘ΠΊ/Π») Π±Ρ‹Π»ΠΎ Π² 60 Ρ€Π°Π· Π½ΠΈΠΆΠ΅ Ρ‚Ρ€Π΅Π±ΠΎΠ²Π°Π½ΠΈΠΉ БанПиН, 137Cs (0,11 Π‘ΠΊ/Π») Π² 900 Ρ€Π°Π· мСньшС Π½ΠΎΡ€ΠΌΠ°Ρ‚ΠΈΠ²ΠΎΠ². Π’ мясС домашнСй ΠΏΡ‚ΠΈΡ†Ρ‹ ΡƒΠ΄Π΅Π»ΡŒΠ½Π°Ρ Π°ΠΊΡ‚ΠΈΠ²Π½ΠΎΡΡ‚ΡŒ 90Sr (0,2–0,3 Π‘ΠΊ/ΠΊΠ³) ΠΈ 137Cs (0,13–0,16 Π‘ΠΊ/ΠΊΠ³) Π² послСдниС Π³ΠΎΠ΄Ρ‹ остаСтся ΡΡ‚Π°Π±ΠΈΠ»ΡŒΠ½ΠΎ Π½ΠΈΠ·ΠΊΠΎΠΉ, Π° Π½ΠΎΡ€ΠΌΠΈΡ€ΡƒΠ΅ΠΌΠΎΠ΅ содСрТаниС 137Cs Π² говядинС (максимально – 0,12 Π‘ΠΊ/ΠΊΠ³) Π±ΠΎΠ»Π΅Π΅ Ρ‡Π΅ΠΌ Π² 1,5 тыс. Ρ€Π°Π· Π½ΠΈΠΆΠ΅ Ρ‚Ρ€Π΅Π±ΠΎΠ²Π°Π½ΠΈΠΉ БанПиН. НаиболСС высокая концСнтрация 137Cs Π² лСсных ягодах, обнаруТСнная Π² зСмляникС (1,27 Π‘ΠΊ/ΠΊΠ³), мСньшС Π½ΠΎΡ€ΠΌΠ°Ρ‚ΠΈΠ²ΠΎΠ² БанПиН Π² 125 Ρ€Π°Π·. Π‘ΠΎΠ΄Π΅Ρ€ΠΆΠ°Π½ΠΈΠ΅ 90Sr Π² Π³Ρ€ΠΈΠ±Π°Ρ… находится Π½Π° ΡƒΡ€ΠΎΠ²Π½Π΅ 0,1–2,5 Π‘ΠΊ/ΠΊΠ³, 137Cs нСсколько Π²Ρ‹ΡˆΠ΅ – 0,6–5,8 Π‘ΠΊ/ΠΊΠ³. Максимально зафиксированная ΡƒΠ΄Π΅Π»ΡŒΠ½Π°Ρ Π°ΠΊΡ‚ΠΈΠ²Π½ΠΎΡΡ‚ΡŒ 137Cs Π² Π³Ρ€ΠΈΠ±Π°Ρ… Π½ΠΈΠΆΠ΅ Ρ‚Ρ€Π΅Π±ΠΎΠ²Π°Π½ΠΈΠΉ БанПиН Π±ΠΎΠ»Π΅Π΅ Ρ‡Π΅ΠΌ Π² 80 Ρ€Π°Π·. ΠžΡ‚ΠΌΠ΅Ρ‡Π΅Π½ΠΎ ΡƒΠΌΠ΅Π½ΡŒΡˆΠ΅Π½ΠΈΠ΅ Π·Π° ΠΏΠ΅Ρ€ΠΈΠΎΠ΄ наблюдСний Π΄ΠΎ 20% ΠΈ Π±ΠΎΠ»Π΅Π΅ содСрТания Ρ‚Π΅Ρ…Π½ΠΎΠ³Π΅Π½Π½Ρ‹Ρ… Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² ΠΏΡ€ΠΎΠ±Π°Ρ… 5 Π²ΠΈΠ΄ΠΎΠ² Ρ€Ρ‹Π±; ΠΌΠ°ΠΊΡΠΈΠΌΠ°Π»ΡŒΠ½Ρ‹Π΅ ΡƒΡ€ΠΎΠ²Π½ΠΈ 90Sr ΠΈ 137Cs Π² Π½Π΅ΠΉ Π±Ρ‹Π»ΠΈ Π½ΠΈΠΆΠ΅ Π½Π°ΠΈΠ±ΠΎΠ»Π΅Π΅ ТСстких Π½ΠΎΡ€ΠΌΠ°Ρ‚ΠΈΠ²ΠΎΠ² БанПиН (использованиС Ρ€Ρ‹Π±Ρ‹ для дСтского питания) Π² 14 Ρ€Π°Π·. Π’Ρ‹Π±ΠΎΡ€ΠΎΡ‡Π½Ρ‹ΠΉ Ρ€Π°Π΄ΠΈΠ°Ρ†ΠΈΠΎΠ½Π½Ρ‹ΠΉ ΠΊΠΎΠ½Ρ‚Ρ€ΠΎΠ»ΡŒ ΠΏΠΈΡ‰Π΅Π²Ρ‹Ρ… ΠΏΡ€ΠΎΠ΄ΡƒΠΊΡ‚ΠΎΠ² Ρ€Π°ΠΉΠΎΠ½Π° БСлоярской АЭБ Π½Π° 3H ΠΈ 14C ΠΏΠΎΠΊΠ°Π·Π°Π», Ρ‡Ρ‚ΠΎ содСрТаниС этих Ρ€Π°Π΄ΠΈΠΎΠ½ΡƒΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² ΠΏΡ€ΠΎΠ΄ΡƒΠΊΡ‚Π°Ρ… питания находится Π½Π° Π½ΠΈΠ·ΠΊΠΎΠΌ, Π±Π»ΠΈΠ·ΠΊΠΎΠΌ ΠΊ Ρ„ΠΎΠ½ΠΎΠ²ΠΎΠΌΡƒ ΡƒΡ€ΠΎΠ²Π½Π΅. Π’ ΡΠ΅Π»ΡŒΡΠΊΠΎΡ…ΠΎΠ·ΡΠΉΡΡ‚Π²Π΅Π½Π½ΠΎΠΉ ΠΏΡ€ΠΎΠ΄ΡƒΠΊΡ†ΠΈΠΈ 3H ΠΈ 14C Π² большСй стСпСни Π½Π°ΠΊΠ°ΠΏΠ»ΠΈΠ²Π°ΡŽΡ‚ΡΡ Π² ΠΊΠ°Ρ€Ρ‚ΠΎΡ„Π΅Π»Π΅ ΠΈ ΠΌΠΎΠ»ΠΎΠΊΠ΅, ΠΈΠ· ΠΏΡ€ΠΈ- Ρ€ΠΎΠ΄Π½Ρ‹Ρ… ΠΏΡ€ΠΎΠ΄ΡƒΠΊΡ‚ΠΎΠ² Π² ΠΏΠΎΠ΄Π±Π΅Ρ€Π΅Π·ΠΎΠ²ΠΈΠΊΠ΅ ΠΈ Π»Π΅Ρ‰Π΅. ΠžΡ‚ΠΌΠ΅Ρ‡Π΅Π½Π° Π½Π΅ΠΎΠ±Ρ…ΠΎΠ΄ΠΈΠΌΠΎΡΡ‚ΡŒ продолТСния исслСдований ΠΏΠΎ ΠΈΠ·ΡƒΡ‡Π΅Π½ΠΈΡŽ накоплСния 3H ΠΈ 14C Π² ΠΏΡ€ΠΎΠ΄ΡƒΠΊΡ‚Π°Ρ… питания Ρ€Π°ΠΉΠΎΠ½Π° БСлоярской АЭБ

    Radiation-hygienic assessment of the concentration and distribution of <sup>90</sup>Sr and <sup>137</sup>Cs in ichthyofauna of the Ob’-Irtysh river system

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    The aim of the work is the radiation-hygienic assessment of 90Sr andΒ  137Cs content in fish of the Ob-Irtysh river system and the study of the basic laws of the radionuclides accumulation in the ichthyofauna of these rivers. To perform this task, long-term results of radioecological studies of fish from the Techa, Irtysh and Ob rivers for the period 2004-2016 were used. Fish as a food product was evaluated according to two criteria: a) permissible levels of radionuclides specific activity (SanPiN 2.3.2.1078-01); b) using the indicator of conformity Π’ and uncertainty of its definition Ξ”Π’ (GOST 32161-2013 and GOST 32163-2013). It is shown that a higher content of radionuclides is observed in the ichthyofauna of the Techa river (1379.1 Bq/kg for 90Sr and 41.9 Bq/kg for 137Cs). On the Ob and Irtysh rivers, the average specific activity of radionuclides in fish was significantly lower and slightly changed during the surveyed area: for 90Sr in the range of 6.0 Γ· 8.1 Bq/kg (mean 6.8), for 137Cs – 0.6 Γ· 1.9 Bq/kg (mean 1.3). Assessment for compliance with radiation safety criteria using the indicator of compliance and its uncertainty (Π’+Ξ”Π’) confirmed the unsuitability of use for food purposes by the radiation factor of all studied fish species from the Techa river (45Γ·55 &gt;1). Fish from all other studied areas of the Ob-Irtysh river system can be used for food without restrictions (0,06Γ·0,53 &lt; 1). The distribution of 90Sr and 137Cs in the ichthyofauna of the Ob-Irtysh river system part over a 2400 km is presented in the form of empirical regression models. The models describe a sharp decrease in the radionuclides specific activity in fish in the Techa and Iset rivers by two orders for 90Sr (from 2000 to 20 Bq/kg), and by one order for 137Cs (from 40 to 2 Bq/kg). With a high degree of reliability (R2&gt;0.86 for 90Sr and R2&gt;0.92 for 137Cs), the presence of power relationships between the content of radionuclides in the ichthyofauna and their content in water was shown, with adequacy confirmed by Fisher’s F-criteria. This can be used for a preliminary assessment of the radionuclides level in fish based on the results of measurements of the average annual concentrations of these radionuclides in water

    Assessment of the impact of the BN-800 reactor operation on the radionuclides content in local foodstuffs in the vicinity of Beloyarsk NPP

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    The research results are presented as an analysis of long-term data on the effect of gas-aerosol emissions and liquid discharges of Beloyarsk NPP and the Institute of Reactor Materials on the content of artificial radionuclides in local foodstuffs. It was noted that the distance and directions from radiation-hazardous facilities do not significantly affect the accumulation of 90Sr and 137Cs in potatoes and milk. The investigation of a wide range of foodstuffs from the private households of 23 settlements, forests, rivers, and a reservoir of the 30-km zone of the Beloyarsk NPP influence showed that the operation of the BN-800 reactor since 2016 did not lead to a registered increase in the content of artificial radionuclides in agricultural and natural foodstuffs. The maximum specific activities of 90Sr (0.84 Bq/kg) and 137Cs (0.26 Bq/kg) in root vegetables, potatoes, melons and vegetables were noted before the start of operation of the new power unit and were 45 and 300 times, respectively, lower than the current SanPiN standards. The highest content of 90Sr in milk (0.41 Bq/l) was 60 times lower than the requirements of SanPiN, 137Cs (0.11 Bq/l) was 900 times less than the permissible levels. In poultry, the specific activity of 90Sr (0.2-0.3 Bq/kg) and 137Cs (0.13-0.16 Bq/kg) has remained stable low in recent years, and the standardised content of 137Cs in beef (maximum 0.12 Bq/kg) more than 1.5 thousand times lower than the requirements of SanPiN. The highest concentration of 137Cs in wild berries, found in strawberries (1.27 Bq/kg), was 125 times less than SanPiN standards. The content of 90Sr in mushrooms was at the level of 0.1-2.5 Bq/kg, the content of 137Cs is slightly higher than - 0.6-5.8 Bq/kg. The maximum recorded specific activity of 137Cs in mushrooms was more than 80 times lower than the requirements of SanPiN. During the observation period, a decrease of up to 20% or more in the content of artificial radionuclides in samples of 5 fish species was noted; the maximum levels of 90Sr and 137Cs in it were 14 times lower than the strictest SanPiN standards (using fish for baby food). Selective radiation monitoring of foodstuffs of Beloyarsk NPP area aimed at 3H and 14C showed that the content of these radionuclides in foodstuffs was low, close to the background level. In agricultural products, 3H and 14C accumulated to a greater extent in potatoes and milk, and in natural products – in rough boletus and bream. There was noted a need to continue research on the accumulation of 3H and 14C in foodstuffs of Beloyarsk NPP vicinity
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