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Predictive-descriptive models for gas and solute diffusion coefficients in variably saturated porous media coupled to pore-size distribution: IV. Solute diffusivity and the liquid phase impedance factor.

机译:与孔隙尺寸分布耦合的可变饱和多孔介质中气体和溶质扩散系数的预测描述模型:IV。溶质扩散率和液相阻抗系数。

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The solute diffusion coefficient in soil (D< sub>P) and its dependency on volumetric soil-water content ( theta ) and matric potential (- psi ) governs release of dissolved chemicals from low-permeable zones of contaminated soils. Further inspired by the intriguing early history of research findings on mineral nutrition of plants and the key role of ion diffusion played in this, we present a model directly linking the ion (solute) diffusion coefficient in variably saturated soil with both theta and psi . In literature, a linear relationship between the liquid phase impedance factor f< sub>l (ratio of relative solute diffusion coefficient, D< sub>P/D< sub>0, to theta ) and theta is typically observed. Assuming a linear impedance factor equation (LIFE), we couple the LIFE with the Campbell soil-water retention model to relate f< sub>l and D< sub>P/D< sub>0 to soil-water matric potential. For loamy and clayey soils, the LIFE-Campbell model in agreement with measured data shows an almost linear relationship between f< sub>l and pF [=log(- psi )] between pF 1.7 and 4.2 (from near field capacity to plant wilting point moisture contents), while the relation between D< sub>P/D< sub>0 and pF is more nonlinear. We also evaluate links between LIFE threshold water content theta < sub>th (where solute diffusion ceases because of disconnected or thin water films), LIFE slope H (related to pore network tortuosity), and basic soil physical parameters. Linking theta < sub>th to a newly defined soil physical characteristic (FC< sub>vol; the volumetric content of clay plus organic matter) showed to be highly promising. For 21 soils, the value of theta < sub>th (m3 H2O m-3 soil) is close to FC< sub>vol (m3 fines m-3 soil), with theta < sub>th typically > FC< sub>vol for compacted or aggregated soils, and theta < sub>th=0.8 FC< sub>vol for seven nonaggregated and noncompacted soils with between 5 and 40% clay. Furthermore, theta < sub>th exhibits a nonlinear relationship with the Philips soil-water sorptivity (S). The LIFE slope H is typically close to unity but is also affected by soil aggregation and compaction. The LIFE-Campbell type model is useful to illustrate effects of pore-size distribution and soil type on solute diffusivity and the impedance factor of the soil liquid phase.
机译:溶质在土壤中的扩散系数(D P )及其对土壤水含量(theta)和基质势(-psi)的依赖性决定着溶解化学物质从受污染土壤的低渗透率区域释放。受到有趣的植物矿物质营养研究成果的早期历史以及离子扩散在其中发挥的关键作用的进一步启发,我们提出了一个模型,该模型将变饱和土壤中的离子(溶质)扩散系数与theta和psi直接联系在一起。在文献中,液相阻抗因子f l (相对溶质扩散系数D P / D 0 theta)和theta通常会被观察到。假设线性阻抗因子方程(LIFE),我们将LIFE与Campbell土壤保水模型耦合,以将f l 和D P / D 0 < / sub>到土壤-水基质的潜力。对于壤土和黏土,LIFE-Campbell模型与实测数据一致,表明f l 和pF [= log(-psi)]之间的线性关系介于pF 1.7和4.2之间(来自近场)枯萎病的水分含量),而D P / D 0 与pF之间的关系更为非线性。我们还评估了LIFE阈值水含量theta th (由于不连续的水膜或薄水膜而使溶质扩散停止),LIFE坡度H(与孔隙网络曲折度有关)与基本土壤物理参数之间的联系。将θ th 与新定义的土壤物理特性(FC vol ;粘土加有机物的体积含量)联系起来非常有前途。对于21种土壤,theta th (m3 H2O m-3土壤)的值接近FC vol (m3细粒m-3土壤),其中theta th 通常> FC vol 用于压实或聚集的土壤,theta th = 0.8 FC vol 用于七个非聚集和非压实的土壤5至40%的黏土。此外,theta th 与Philips的土壤水吸附度(S)呈非线性关系。 LIFE坡度H通常接近于1,但也受土壤聚集和压实的影响。 LIFE-Campbell型模型可用于说明孔径分布和土壤类型对溶质扩散率和土壤液相阻抗因子的影响。

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