首页> 外文会议>International symposium on nuclear energy and the environment;NEE; 19961014-18;19961014-18; Beijing(CN);Beijing(CN) >WATER ORGANISMS FROM THE 30km ZONE AFTER THE 1986 CHERNOBYL NPP ACCIDENT. RADIOACTIVE CONTAMINATION AND POSSIBLE RADIOBIOLOGICAL EFFECTS
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WATER ORGANISMS FROM THE 30km ZONE AFTER THE 1986 CHERNOBYL NPP ACCIDENT. RADIOACTIVE CONTAMINATION AND POSSIBLE RADIOBIOLOGICAL EFFECTS

机译:1986年切尔诺贝利核电站事故发生后30公里区域内的水体。放射性污染和可能的放射生物学效应

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Before the 1986 accident, hydrobionts from the NPP cooling pond usually demonstrated contamination with ~(137,134)Cs, ~(90)Sr, ~(54)Mn,~( 60)Co radionuclides (sometimes also ~(51)Cr, ~(58)Co, ~(65)Zn) at concentrations from n·10° to n·10~1 Bq/kg. In some particular cases (Autumn'82 - Spring'83) water plants taken at the sampling stations in the vicinity of NPP were contaminated with radionuclides of Cerium, Zirconium, Niobium, Ruthenium in concentrations up to 10 kBq/kg. After the 4th unit accident, followed by radioactive releases to the environment, water ecosystems of the Chernobyl NPP zone were heavily contaminated with radioactive substances. In late April and early May 1986 total radioactivity of hydrobionts in the cooling pond had increased up to millions times. It was determined mainly by short-living radionuclides. At the end of 1986 in the cooling pond of the Chernobyl NPP concentrations of certain radinuclides was 80 - 1000 kBq/kg in water plants, 0.3 - 250 kBq/kg in molluscs, up to 400 kBq/kg in fish. Afterwards, due to decay, the share of short-living radionuclides decreased and the major role in hydrobionts' radioactive contamination shifted to ~(137)Cs and ~(90)Sr[1].
机译:在1986年事故之前,来自NPP冷却池的水生生物通常表现出〜(137,134)Cs,〜(90)Sr,〜(54)Mn,〜(60)Co放射性核素的污染(有时也〜(51)Cr,〜( 58)Co,〜(65)Zn)的浓度从n·10°到n·10〜1 Bq / kg。在某些特定情况下('82秋季-'83春季)在NPP采样站采集的水生植物被铈,锆,铌,钌的放射性核素污染,浓度最高为10 kBq / kg。在第四次单元事故之后,随后向环境释放放射性,切尔诺贝利核电厂区的水生态系统被放射性物质严重污染。 1986年4月下旬至5月初,冷却池中水合生物的总放射性增加了数百万倍。它主要由短寿命放射性核素确定。 1986年底,在切尔诺贝利核电站的冷却池中,水生植物中某些放射性核素的浓度为80-1000 kBq / kg,软体动物中为0.3-250 kBq / kg,鱼类最高为400 kBq / kg。之后,由于衰变,短寿命放射性核素的份额下降,并且在水溶生物的放射性污染中的主要作用转移到〜(137)Cs和〜(90)Sr [1]。

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