4 research outputs found
Synthesis of Lithium Phosphorus Oxynitride (LiPON) Thin Films by Li3 PO4 Anodic Evaporation in Nitrogen Plasma of a Low-Pressure Arc Discharge
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 10β8 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 10β6 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°ΡΠΈΠΎΠ½Π½ΠΎ-Π³ΠΈΠ³ΠΈΠ΅Π½ΠΈΡΠ΅ΡΠΊΠ°Ρ ΠΎΡΠ΅Π½ΠΊΠ° ΡΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΡ ΠΈ ΡΠ°ΡΠΏΡΠ΅Π΄Π΅Π»Π΅Π½ΠΈΡ 90Sr ΠΈ 137Cs Π² ΠΈΡ ΡΠΈΠΎΡΠ°ΡΠ½Π΅ ΠΠ±Ρ-ΠΡΡΡΡΡΠΊΠΎΠΉ ΡΠ΅ΡΠ½ΠΎΠΉ ΡΠΈΡΡΠ΅ΠΌΡ
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 ΞΠ (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 β 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+ΞΠ) 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 Fisherβs 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.Π¦Π΅Π»ΡΡ Π½Π°ΡΡΠΎΡΡΠ΅ΠΉ ΡΠ°Π±ΠΎΡΡ ΡΠ²Π»ΡΠ΅ΡΡΡ ΡΠ°Π΄ΠΈΠ°ΡΠΈΠΎΠ½Π½ΠΎ-Π³ΠΈΠ³ΠΈΠ΅Π½ΠΈΡΠ΅ΡΠΊΠ°Ρ ΠΎΡΠ΅Π½ΠΊΠ° ΡΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΡ 90Sr ΠΈ 137Cs Π² ΡΡΠ±Π΅ ΠΠ±Ρ-ΠΡΡΡΡΡΠΊΠΎΠΉ ΡΠ΅ΡΠ½ΠΎΠΉ ΡΠΈΡΡΠ΅ΠΌΡ ΠΈ ΠΈΠ·ΡΡΠ΅Π½ΠΈΠ΅ ΠΎΡΠ½ΠΎΠ²Π½ΡΡ
Π·Π°ΠΊΠΎΠ½ΠΎΠΌΠ΅ΡΠ½ΠΎΡΡΠ΅ΠΉ Π½Π°ΠΊΠΎΠΏΠ»Π΅Π½ΠΈΡ ΡΠ°Π΄ΠΈΠΎΠ½ΡΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² ΠΈΡ
ΡΠΈΠΎΡΠ°ΡΠ½Π΅ ΡΡΠΈΡ
ΡΠ΅ΠΊ. ΠΠ»Ρ Π²ΡΠΏΠΎΠ»Π½Π΅Π½ΠΈΡ Π΄Π°Π½Π½ΠΎΠΉ Π·Π°Π΄Π°ΡΠΈ Π±ΡΠ»ΠΈ ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½Ρ ΠΌΠ½ΠΎΠ³ΠΎΠ»Π΅ΡΠ½ΠΈΠ΅ ΡΠ΅Π·ΡΠ»ΡΡΠ°ΡΡ ΡΠ°Π΄ΠΈΠΎΡΠΊΠΎΠ»ΠΎΠ³ΠΈΡΠ΅ΡΠΊΠΈΡ
ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½ΠΈΠΉ ΡΡΠ±Ρ ΠΈΠ· ΡΠ΅ΠΊ Π’Π΅ΡΠ°, ΠΡΡΡΡ ΠΈ ΠΠ±Ρ Π·Π° ΠΏΠ΅ΡΠΈΠΎΠ΄ 2004β2016 Π³Π³. ΠΡΠΏΠΎΠ»Π½Π΅Π½Π° ΠΎΡΠ΅Π½ΠΊΠ° ΡΡΠ±Ρ ΠΊΠ°ΠΊ ΠΏΠΈΡΠ΅Π²ΠΎΠ³ΠΎ ΠΏΡΠΎΠ΄ΡΠΊΡΠ° ΠΏΠΎ Π΄Π²ΡΠΌ ΠΊΡΠΈΡΠ΅ΡΠΈΡΠΌ: Π°) Π΄ΠΎΠΏΡΡΡΠΈΠΌΡΠ΅ ΡΡΠΎΠ²Π½ΠΈ ΡΠ΄Π΅Π»ΡΠ½ΠΎΠΉ Π°ΠΊΡΠΈΠ²Π½ΠΎΡΡΠΈ ΡΠ°Π΄ΠΈΠΎΠ½ΡΠΊΠ»ΠΈΠ΄ΠΎΠ² (Π‘Π°Π½ΠΠΈΠ 2.3.2.1078-01); Π±) Ρ ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½ΠΈΠ΅ΠΌ ΠΏΠΎΠΊΠ°Π·Π°ΡΠ΅Π»Ρ ΡΠΎΠΎΡΠ²Π΅ΡΡΡΠ²ΠΈΡ Π ΠΈ Π½Π΅ΠΎΠΏΡΠ΅Π΄Π΅Π»Π΅Π½Π½ΠΎΡΡΠΈ Π΅Π³ΠΎ ΠΎΠΏΡΠ΅Π΄Π΅Π»Π΅Π½ΠΈΡ ΞΠ (ΠΠΠ‘Π’ 32161-2013 ΠΈ ΠΠΠ‘Π’ 32163-2013). ΠΠΎΠΊΠ°Π·Π°Π½ΠΎ, ΡΡΠΎ Π±ΠΎΠ»Π΅Π΅ Π²ΡΡΠΎΠΊΠΎΠ΅ ΡΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΠ΅ ΡΠ°Π΄ΠΈΠΎΠ½ΡΠΊΠ»ΠΈΠ΄ΠΎΠ² Π½Π°Π±Π»ΡΠ΄Π°Π΅ΡΡΡ Π² ΠΈΡ
ΡΠΈΠΎΡΠ°ΡΠ½Π΅ ΡΠ΅ΠΊΠΈ Π’Π΅ΡΠ° (1379,1 ΠΠΊ/ΠΊΠ³ ΠΏΠΎ 90Sr ΠΈ 41,9 ΠΠΊ/ΠΊΠ³ ΠΏΠΎ 137Cs). ΠΠ° ΡΠ΅ΠΊΠ°Ρ
ΠΠ±Ρ ΠΈ ΠΡΡΡΡ ΡΡΠ΅Π΄Π½ΠΈΠ΅ ΠΏΠΎΠΊΠ°Π·Π°ΡΠ΅Π»ΠΈ ΡΠ΄Π΅Π»ΡΠ½ΠΎΠΉ Π°ΠΊΡΠΈΠ²Π½ΠΎΡΡΠΈ ΡΠ°Π΄ΠΈΠΎΠ½ΡΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² ΡΡΠ±Π΅ Π±ΡΠ»ΠΈ ΡΡΡΠ΅ΡΡΠ²Π΅Π½Π½ΠΎ Π½ΠΈΠΆΠ΅ ΠΈ ΡΠ»Π°Π±ΠΎ ΠΈΠ·ΠΌΠ΅Π½ΡΠ»ΠΈΡΡ Π½Π° ΠΏΡΠΎΡΡΠΆΠ΅Π½ΠΈΠΈ ΠΎΠ±ΡΠ»Π΅Π΄ΠΎΠ²Π°Π½Π½ΠΎΠ³ΠΎ ΡΡΠ°ΡΡΠΊΠ°: Π΄Π»Ρ 90Sr Π² Π΄ΠΈΠ°ΠΏΠ°Π·ΠΎΠ½Π΅ 6,0β8,1 ΠΠΊ/ΠΊΠ³ (ΡΡΠ΅Π΄Π½Π΅Π΅ 6,8), Π΄Π»Ρ 137Cs β 0,6β1,9 ΠΠΊ/ΠΊΠ³ (ΡΡΠ΅Π΄Π½Π΅Π΅ 1,3). ΠΡΠ΅Π½ΠΊΠ° Π½Π° ΡΠΎΠΎΡΠ²Π΅ΡΡΡΠ²ΠΈΠ΅ ΠΊΡΠΈΡΠ΅ΡΠΈΡΠΌ ΡΠ°Π΄ΠΈΠ°ΡΠΈΠΎΠ½Π½ΠΎΠΉ Π±Π΅Π·ΠΎΠΏΠ°ΡΠ½ΠΎΡΡΠΈ Ρ ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½ΠΈΠ΅ΠΌ ΠΏΠΎΠΊΠ°Π·Π°ΡΠ΅Π»Ρ ΡΠΎΠΎΡΠ²Π΅ΡΡΡΠ²ΠΈΡ Π ΠΈ Π΅Π³ΠΎ Π½Π΅ΠΎΠΏΡΠ΅Π΄Π΅Π»Π΅Π½Π½ΠΎΡΡΠΈ ΞΠ (Π+ΞΠ) ΠΏΠΎΠ΄ΡΠ²Π΅ΡΠ΄ΠΈΠ»Π° Π½Π΅ΠΏΡΠΈΠ³ΠΎΠ΄Π½ΠΎΡΡΡ ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½ΠΈΡ Π² ΠΏΠΈΡΠ΅Π²ΡΡ
ΡΠ΅Π»ΡΡ
ΠΏΠΎ ΡΠ°Π΄ΠΈΠ°ΡΠΈΠΎΠ½Π½ΠΎΠΌΡ ΡΠ°ΠΊΡΠΎΡΡ Π²ΡΠ΅Ρ
ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½Π½ΡΡ
Π²ΠΈΠ΄ΠΎΠ² ΡΡΠ± ΠΈΠ· Ρ. Π’Π΅ΡΠΈ (45β55 >1). Π ΡΠ±Π° ΠΈΠ· Π²ΡΠ΅Ρ
ΠΎΡΡΠ°Π»ΡΠ½ΡΡ
ΠΈΡΡΠ»Π΅Π΄ΠΎΠ²Π°Π½Π½ΡΡ
ΡΡΠ°ΡΡΠΊΠΎΠ² ΠΠ±Ρ-ΠΡΡΡΡΡΠΊΠΎΠΉ ΡΠ΅ΡΠ½ΠΎΠΉ ΡΠΈΡΡΠ΅ΠΌΡ ΠΌΠΎΠΆΠ΅Ρ Π±ΡΡΡ ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½Π° Π² ΠΏΠΈΡΡ Π±Π΅Π· ΠΎΠ³ΡΠ°Π½ΠΈΡΠ΅Π½ΠΈΠΉ (0,06β0,53 < 1). ΠΠ°ΠΊΠΎΠ½ΠΎΠΌΠ΅ΡΠ½ΠΎΡΡΠΈ ΡΠ°ΡΠΏΡΠ΅Π΄Π΅Π»Π΅Π½ΠΈΡ 90Sr ΠΈ 137Cs Π² ΠΈΡ
ΡΠΈΠΎΡΠ°ΡΠ½Π΅ ΠΠ±Ρ-ΠΡΡΡΡΡΠΊΠΎΠΉ ΡΠ΅ΡΠ½ΠΎΠΉ ΡΠΈΡΡΠ΅ΠΌΡ Π½Π° ΡΡΠ°ΡΡΠΊΠ΅ ΠΏΡΠΎΡΡΠΆΠ΅Π½Π½ΠΎΡΡΡΡ 2400 ΠΊΠΌ ΠΏΡΠ΅Π΄ΡΡΠ°Π²Π»Π΅Π½Ρ Π² Π²ΠΈΠ΄Π΅ ΡΠΌΠΏΠΈΡΠΈΡΠ΅ΡΠΊΠΈΡ
ΡΠ΅Π³ΡΠ΅ΡΡΠΈΠΎΠ½Π½ΡΡ
ΠΌΠΎΠ΄Π΅Π»Π΅ΠΉ. ΠΠΎΠ΄Π΅Π»ΠΈ ΠΎΠΏΠΈΡΡΠ²Π°ΡΡ ΡΠ΅Π·ΠΊΠΎΠ΅ ΡΠ½ΠΈΠΆΠ΅Π½ΠΈΠ΅ ΡΠ΄Π΅Π»ΡΠ½ΠΎΠΉ Π°ΠΊΡΠΈΠ²Π½ΠΎΡΡΠΈ ΡΠ°Π΄ΠΈΠΎΠ½ΡΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² ΡΡΠ±Π΅ Π½Π° ΡΡΠ°ΡΡΠΊΠ΅ ΡΠ΅ΠΊ Π’Π΅ΡΠ° β ΠΡΠ΅ΡΡ Π½Π° Π΄Π²Π° ΠΏΠΎΡΡΠ΄ΠΊΠ° Π²Π΅Π»ΠΈΡΠΈΠ½ ΠΏΠΎ 90Sr (Ρ 2000 Π΄ΠΎ 20 ΠΠΊ/ΠΊΠ³) ΠΈ Π½Π° ΠΎΠ΄ΠΈΠ½ ΠΏΠΎΡΡΠ΄ΠΎΠΊ ΠΏΠΎ 137Cs (Ρ 40 Π΄ΠΎ 2 ΠΠΊ/ΠΊΠ³). Π‘ Π²ΡΡΠΎΠΊΠΎΠΉ ΡΡΠ΅ΠΏΠ΅Π½ΡΡ Π΄ΠΎΡΡΠΎΠ²Π΅ΡΠ½ΠΎΡΡΠΈ (R2 >0,86 Π΄Π»Ρ 90Sr ΠΈ R2 >0,92 Π΄Π»Ρ 137Cs) ΠΏΠΎΠΊΠ°Π·Π°Π½ΠΎ Π½Π°Π»ΠΈΡΠΈΠ΅ ΡΡΠ΅ΠΏΠ΅Π½Π½ΡΡ
Π·Π°Π²ΠΈΡΠΈΠΌΠΎΡΡΠ΅ΠΉ ΠΌΠ΅ΠΆΠ΄Ρ ΡΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΠ΅ΠΌ ΡΠ°Π΄ΠΈΠΎΠ½ΡΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² ΠΈΡ
ΡΠΈΠΎΡΠ°ΡΠ½Π΅ ΠΈ ΠΈΡ
ΡΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΠ΅ΠΌ Π² Π²ΠΎΠ΄Π΅, Ρ Π°Π΄Π΅ΠΊΠ²Π°ΡΠ½ΠΎΡΡΡΡ, ΠΏΠΎΠ΄ΡΠ²Π΅ΡΠΆΠ΄Π΅Π½Π½ΠΎΠΉ ΠΊΡΠΈΡΠ΅ΡΠΈΡΠΌΠΈ Π€ΠΈΡΠ΅ΡΠ°. ΠΡΠΎ ΠΌΠΎΠΆΠ΅Ρ Π±ΡΡΡ ΠΈΡΠΏΠΎΠ»ΡΠ·ΠΎΠ²Π°Π½ΠΎ Π΄Π»Ρ ΠΏΡΠ΅Π΄Π²Π°ΡΠΈΡΠ΅Π»ΡΠ½ΠΎΠΉ ΠΎΡΠ΅Π½ΠΊΠΈ ΡΡΠΎΠ²Π½Ρ ΡΠΎΠ΄Π΅ΡΠΆΠ°Π½ΠΈΡ ΡΠ°Π΄ΠΈΠΎΠ½ΡΠΊΠ»ΠΈΠ΄ΠΎΠ² Π² ΡΡΠ±Π΅ Π½Π° ΠΎΡΠ½ΠΎΠ²Π΅ ΡΠ΅Π·ΡΠ»ΡΡΠ°ΡΠΎΠ² ΠΈΠ·ΠΌΠ΅ΡΠ΅Π½ΠΈΠΉ ΡΡΠ΅Π΄Π½Π΅Π³ΠΎΠ΄ΠΎΠ²ΡΡ
ΠΊΠΎΠ½ΡΠ΅Π½ΡΡΠ°ΡΠΈΠΉ ΡΡΠΈΡ
ΡΠ°Π΄ΠΈΠΎΠ½ΡΠΊΠ»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 Obβ-Irtysh river system
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 ΞΠ (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 β 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+ΞΠ) 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 Fisherβs 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