Abstract
Variations of gas diffusivity (ratio of gas diffusion coefficients in soil and free air, DS/D0) with air-filled porosity (ε) influence the transport, degradation, and volatilization of reactive gasses in soil systems. We show that the prediction accuracy of the Penman-Millington-Quirk (PMQ) diffusivity model (introduced in Part VII of this series) is often improved significantly by including as a reference point a measured value of the gas diffusion coefficient (Dfc) at a single soil-water potential, ψ, between −100 and −500 cm H20. As a result, the root mean square error of prediction was reduced by 45% (based on individual DS/D0 measurements) and by ≥ 65% (based on mean values of 6 to 9 closely-spaced DS/D0 measurements) for undisturbed soil samples from six differently textured surface soils. Gas permeability is measured more easily and more rapidly than gas diffusivity, and we suggest that a measured value of gas permeability (kfc) at a single soil-water potential, combined with a tortuous tube permeability model and the PMQ diffusivity model, can also be used to improve DS/D0 predictions. For practical use, a relation between the equivalent tube radius (rfc) at ψ = −100 cm H20 and clay content, taken to represent the soil structure-forming ability, is proposed for surface soils. Gas diffusive transport simulations using the DARC numerical model (Part I of this series) verified that the inclusion of a single (Dfc or kfc) measurement in the DS/D0(ε) predictions can improve simulation accuracy significantly. Dfc- and kfc-based diffusivity models require limited measurement effort and seem promising for site-specific simulations of gas diffusion and reaction.
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