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    Synthesis of Lithium Phosphorus Oxynitride (LiPON) Thin Films by Li3 PO4 Anodic Evaporation in Nitrogen Plasma of a Low-Pressure Arc Discharge

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    Thin amorphous films of LiPON solid electrolyte were prepared by anodic evaporation of lithium orthophosphate Li3 PO4 in an arc discharge with a self-heating hollow cathode at a nitrogen pressure of 1 Pa. Distribution of the arc current between two electrodes having an anode potential provided independent control of the evaporation rate of Li3 PO4 and the density of nitrogen plasma. Stabilization of the evaporation rate was achieved using a crucible with multi-aperture cover having floating potential. The existence of a threshold value of discharge current (40 A) has been established, which, upon reaching ionic conductivity over 10βˆ’8 S/cm, appears in the films. Probe diagnostics of discharge plasma were carried out. It has been shown that heating the films during deposition by plasma radiation to a temperature of 200β—¦ C is not an impediment to achieving high ionic conductivity of the films. Dense uniform films of LiPON thickness 1 Β΅m with ionic conductivity up to 1 Γ— 10βˆ’6 S/cm at a deposition rate of 4 nm/min are obtained. Β© 2021 by the authors. Licensee MDPI, Basel, Switzerland.Funding: The studies of the coatings were carried out with the financial support of Russian Federation represented by Ministry of Science and Higher Education (project No. 075-15-2021-1348) within the framework of event No. 1.1.12

    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΅

    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
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