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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 Review3.4.2 Dust Entra<strong>in</strong>ment and Deposition Model (DEAD)The Dust Entra<strong>in</strong>ment and Deposition Model (DEAD) is a global dust emission and transportmodel (Zender et al., 2003a). The dust entra<strong>in</strong>ment and mobilisation scheme used <strong>in</strong> DEADis similar to that of Marticorena and Bergametti (1995). The model emission scheme isparticle size dependent, with u *t be<strong>in</strong>g computed as a function of soil particle sizedistributions. Modifications are made to u *t by account<strong>in</strong>g for soil moisture effects us<strong>in</strong>g thescheme of Fécan et al. (1999), and surface roughness effects us<strong>in</strong>g the drag partition<strong>in</strong>gscheme of Raupach et al. (1993). The model considers the Owen effect, a positive feedbackof saltation on the surface roughness length and friction velocity, us<strong>in</strong>g the model of Gilletteet al. (1998).Dust source area soil erodibilities <strong>in</strong> DEAD are def<strong>in</strong>ed by soil particle size distributions froma global soil texture dataset (Zender et al., 2003a). Land surface and geographic constra<strong>in</strong>tsare applied to the dust source areas <strong>in</strong> addition to the roughness and moistureparameterisations <strong>in</strong> the emission scheme. The fraction of bare soil surface is described by aparameter which is a function of total vegetation, snow, lake and wetlands cover. Vegetationcover is derived from satellite imagery of Leaf Area Index (LAI) at a 1 x 1 km spatialresolution. These factors are considered constant dur<strong>in</strong>g simulations. A further adjustment ismade for dust source area erodibility S. This adjustment has a basis <strong>in</strong> global dust source areacharacterisations reported by G<strong>in</strong>oux et al. (2001), identified us<strong>in</strong>g Total Ozone Mapp<strong>in</strong>gSpectrometer (TOMS) aerosol optical thickness image data. Zender et al. (2003a) def<strong>in</strong>ed Sas the upstream area from which sediment transported <strong>in</strong> surface runoff may haveaccumulated. The S parameter was <strong>in</strong>cluded to account for the relationship between globaldust source area location and sediment recharge <strong>in</strong> dra<strong>in</strong>age depressions. Zender et al.(2003b) reported on the effects of variants on the S parameter for uniform, topographic,geomorphic and hydrological source erodibility factors on global dust load predictions.Results demonstrated that simulations of global dust emissions are highly sensitive to dustsource area characterisations.Gr<strong>in</strong>i et al. (2005) exam<strong>in</strong>ed dust sources and transport with DEAD us<strong>in</strong>g four soil erodibilityfactors. The soil erodibility factors were def<strong>in</strong>ed to capture characteristics of global dustsource areas and <strong>in</strong>cluded the topographic and geomorphic factors used by G<strong>in</strong>oux (2001)and Zender et al. (2003b), for example:89

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