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An overview of BORIS: Bioavailability of Radionuclides in Soils

机译:BORIS概述:土壤中放射性核素的生物利用度

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The ability to predict the consequences of an accidental release of radionuclides relies mainly on the level of understanding of the mechanisms involved in radionuclide interactions with different components of agricultural and natural ecosystems and their formalisation into predictive models. Numerous studies and databases on contaminated agricultural and natural areas have been obtained, but their use to enhance our prediction ability has been largely limited by their unresolved variability. Such variability seems to stem from incomplete knowledge about radionuclide interactions with the soil matrix, soil moisture, and biological elements in the soil and additional pollutants, which may be found in such soils. In the 5th European Framework Programme entitled Bioavailability of Radionuclides in Soils (BORIS), we investigated the role of the abiotic (soil components and soil structure) and biological elements (organic compounds, plants, mycorrhiza, and microbes) in radionuclide sorption/desorption in soils and radionuclide uptake/release by plants. Because of the importance of their radioiso-topes, the bioavailability of three elements, caesium, strontium, and technetium has been followed. The role of one additional non-radioactive pollutant (copper) has been scrutinised in some cases. Role of microorganisms (e.g., K_d for caesium and strontium in organic soils is much greater in the presence of microorganisms than in their absence), plant physiology (e.g., changes in plant physiology affect radionuclide uptake by plants), and the presence of mycorrhizal fungi (e.g., interferes with the uptake of radionuclides by plants) have been demonstrated. Knowledge acquired from these experiments has been incorporated into two mechanistic models CHEMFAST and BIORUR, specifically modelling radionuclide sorption/desorption from soil matrices and radionuclide uptake by/release from plants. These mechanistic models have been incorporated into an assessment model to enhance its prediction ability by introducing the concept of bioavailability factor for radionuclides.
机译:预测放射性核素意外释放的后果的能力主要取决于对放射性核素与农业和自然生态系统不同组成部分相互作用的机制的了解,以及将其形式化为预测模型的水平。已经获得了有关受污染的农业和自然地区的大量研究和数据库,但是由于它们无法解决的可变性,它们在增强我们的预测能力方面的应用受到很大限制。这种可变性似乎是由于对放射性核素与土壤基质,土壤水分,土壤中的生物元素以及可能在此类土壤中发现的其他污染物之间相互作用的不完全了解。在第五个名为“土壤中放射性核素的生物利用度”的欧洲框架计划中,我们研究了非生物(土壤成分和土壤结构)和生物元素(有机化合物,植物,菌根和微生物)在放射性核素吸附/解吸中的作用。土壤和植物对放射性核素的吸收/释放。由于它们的放射性同位素很重要,因此一直遵循铯,锶和tech这三种元素的生物利用度。在某些情况下,还研究了一种其他非放射性污染物(铜)的作用。有微生物存在时,微生物的作用(例如,有机土壤中铯和锶的K_d要比无微生物存在时大得多),植物生理学(例如,植物生理学的变化会影响植物对放射性核素的吸收)以及菌根真菌的存在(例如,干扰植物吸收放射性核素)。从这些实验中获得的知识已被整合到两个化学模型CHEMFAST和BIORUR中,特别是模拟土壤基质中放射性核素的吸附/解吸以及植物吸收/释放的放射性核素。通过引入放射性核素生物利用度因子的概念,将这些机械模型纳入了评估模型,以增强其预测能力。

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