Kirchner G, Baumgartner D
University of Bremen, Department of Physics/FB 1, Germany.
Analyst. 1992 Mar;117(3):475-9. doi: 10.1039/an9921700475.
In three soils typical for Northern Germany including Eutric Cambisol, Orthic Podsol and Eutric Histosol (Food and Agriculture Organization nomenclature), distributions of 90Sr, 134Cs, 137Cs and 239Pu + 240Pu in the soil profiles were determined. Sampling was performed more than 3 years after deposition of Chernobyl fallout nuclides. Migration rates calculated with a compartmental model showed no significant differences between Cs originating from either atomic weapons or Chernobyl fallout. This result indicates that Chernobyl Cs may have reached sorption equilibrium with the soil matrix 3 years after the accident. Both the compartmental model and the dispersion equation reproduce distributions of most of the activities, but fail to reproduce some (minor) activity fractions that show increased mobility.
在三种德国北部典型土壤中,包括雏形土、灰化土和腐泥土(采用联合国粮食及农业组织的命名法),测定了土壤剖面中90锶、134铯、137铯和239钚 + 240钚的分布情况。采样是在切尔诺贝利放射性尘埃核素沉降3年多后进行的。用隔室模型计算得出的迁移率表明,源自核武器或切尔诺贝利放射性尘埃的铯之间没有显著差异。这一结果表明,切尔诺贝利事故后的铯可能在事故发生3年后已与土壤基质达到吸附平衡。隔室模型和扩散方程都能再现大部分活度的分布情况,但无法再现一些显示出迁移性增加的(少量)活度部分。