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Soil mixing depth after atmospheric deposition. I. Model development and validation

机译:大气沉积后的土壤混合深度。一,模型开发与验证

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摘要

Knowledge of a soil mixing depth, or the migration depth of various pollutants in soil, is necessary to assess the soil chemical concentration resulting from atmospheric deposition of a specific air emission source. A mathematical model has been developed that describes the depth and time behavior of the soil concentration of an inert chemical after atmospheric deposition on surfaces. The soil mixing model is based on one-dimensional diffusion theory, and analytic solutions have been derived for the cases of: (1) instantaneous surface deposition; (2) continuous surface deposition; and (3) a finite period of continuous surface deposition, followed by a deposition-free time period. Comparisons of the model with measured soil depth profiles resulting from atmospheric deposition showed good agreement for lead, cesium, and dioxins. The best-fit effective diffusion coefficients in undisturbed soils varied from 0.5 cm~2 yr~-1 to 2 cm2 yr~-1. The soil mixing depth was found to be a strong function of the atmospheric deposition time period. Calculated soil mixing depths in undisturbed soils were 2 cm after one year, 5 cm after five years, and 10 cm after 20 years of continuous atmospheric deposition on the soil surface.
机译:必须了解土壤混合深度或各种污染物在土壤中的迁移深度,才能评估由特定空气排放源在大气中沉积而导致的土壤化学浓度。已经建立了数学模型,该数学模型描述了大气中沉积在表面上后惰性化学品的土壤浓度的深度和时间行为。土壤混合模型基于一维扩散理论,并针对以下情况推导了解析解:(1)瞬时表面沉积; (2)连续的表面沉积; (3)有限的连续表面沉积时间,然后是无沉积时间。该模型与大气沉积物测得的土壤深度剖面的比较表明,铅,铯和二恶英具有很好的一致性。未扰动土壤的最佳拟合有效扩散系数在0.5 cm〜2 yr〜-1至2 cm2 yr〜-1之间。发现土壤混合深度与大气沉积时间段密切相关。在未扰动的土壤中,计算得出的土壤混合深度为一年后2 cm,五年后5 cm和20年后20 cm。

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