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Input of Cs-137 and Sr-90 into plants from the surface of soil aggregates and the intraped space

机译:从土壤团聚体表面和内部空间向植物输入Cs-137和Sr-90

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摘要

Soil aggregates with different localization of radionuclides-(a) only on the aggregate surface, (b) only in the intraped space, and (c) uniformly distributed throughout the aggregate volume-have been obtained under laboratory conditions, which has allowed separately assessing the roles of different aggregate parts in the uptake of radionuclides by plant roots and the reaggregation rate of the soil material. The uptake rate of the radionuclides localized on the surface of soil aggregates, especially Cs-137, by plants manifold exceeds their uptake observed at the localization of pollutants throughout the aggregate volume or only in their intraped material. The input rate of radionuclides into plants decreases with time. For Cs-137, this decrease is due to the strengthening of the sorption fixation of the radionuclide (about 15%) and the reaggregation of the soil material (85%). Under natural conditions, at a depth of 10 cm in the dark gray forest soil of a forest belt, aggregates 7-10 mm in size are subjected to 40-75% destruction and reaggregation on the average within a year, which corresponds, with consideration for the statistical dispersion of the initial data, to the aggregate lifetime of 1.5 to 3 years.
机译:在实验室条件下获得了具有不同放射性核素局限性的土壤聚集体-(a)仅在聚集体表面上,(b)仅在内部空间中,以及(c)均匀分布在整个聚集体中,这使得可以分别评估聚集部分在植物根系吸收放射性核素和土壤物质重新聚集速率中的作用。植物歧管对土壤团聚体,特别是Cs-137的放射性核素的吸收速率超过了在整个集聚体中或仅在其内部物质中污染物定位时所观察到的吸收率。放射性核素输入植物的速率随时间降低。对于Cs-137,这种下降是由于放射性核素的吸附固定作用增强(约15%)和土壤物质的重新聚集(85%)。在自然条件下,在林带的深灰色森林土壤中的10厘米深度处,聚集体7-10毫米的大小平均一年内会遭受40-75%的破坏和重新聚集,这相当于对于初始数据的统计分散,总寿命为1.5到3年。

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