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Wind Erosion in Western Queensland Australia

Modelling Land Susceptibility to Wind Erosion in Western ... - Ninti One

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Chapter 3 – Modell<strong>in</strong>g Land Erodibility ReviewWEELS has a process-based system that simulates w<strong>in</strong>d erosion when u * exceeds u *t . Fourmodules are comb<strong>in</strong>ed to compute u *t . The modules account for soil moisture, soil erodibility,soil roughness, and land use effects on the static threshold. Soil erodibility is calculated as afunction of soil properties <strong>in</strong>clud<strong>in</strong>g soil gra<strong>in</strong> size distribution and soil type. Landmanagement conditions such as cultivation methods, crop type, crop rotations and land usescenarios are then used to adjust the soil erodibility, soil roughness and land use factors(Böhner et al., 2003).WEELS computes soil erodibility then <strong>in</strong>dependently accounts for soil moisture andvegetation cover factors by <strong>in</strong>tegrat<strong>in</strong>g these <strong>in</strong>to the w<strong>in</strong>d erosivity component of the model.Soil erodibility is quantified us<strong>in</strong>g a dimensionless factor K which expresses the <strong>in</strong>tr<strong>in</strong>sicsusceptibility of a dry, freshly cultivated sandy soil to erosion. Values for K are computed asa function of the mean weighted diameter of the texture (by particle size distribution), organicmatter content and the proportion of aggregates > 0.63 mm:( MWD) 0.04( DA)log K = 1.24 4.21%(3.18)where MWD is the soil particle mean weighted diameter (mm), and %DA is the weightpercentage of aggregates > 0.63 mm (%) calculated as:(%Silt % Clay) + % DA = 2.42+ 8.6[ log( % OM )]+ 44.5 (3.19) % Sand where %DA is the aggregate portion > 0.63 mm (%), %OM is the weight percent soil organicmatter, and %Silt, %Clay, %Sand are the soil silt, clay and sand fractions (%). BothEquations 3.18 and 3.19 are regression equations derived from field experimentation <strong>in</strong>Germany (Böhner et al., 2003). Field measurements of %DA can also be used as <strong>in</strong>put to themodel. Soil erodibility <strong>in</strong>creases as K <strong>in</strong>creases; however, K is considered static <strong>in</strong> WEELSand does not vary <strong>in</strong> response to changes <strong>in</strong> climate and management conditions. Vegetationeffects on u *t are considered by a logarithmic adjustment to u *t . The WEELS soil moisturemodule relies on a simple soil water budget that operates for sandy soils, so modelapplication is currently limited to sandy soils.82

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