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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 4 –Modell<strong>in</strong>g Soil Erodibility Dynamics0.84 mm diameter) on the soil surface (Chepil, 1950a). The soil ASD is a function of thelevel of soil aggregation and physical or biological crust<strong>in</strong>g (Zobeck, 1991). These propertiesare determ<strong>in</strong>ed by soil texture, chemistry, organic matter content, and dynamic factors suchas climate (e.g. ra<strong>in</strong>fall, temperature) and land management (Figure 4.1). Soil moisture is animportant control on soil erodibility and is a transient factor that may be considered<strong>in</strong>dependent of the soil <strong>in</strong>herent w<strong>in</strong>d erodibility which is primarily determ<strong>in</strong>ed by the ASD(Merrill et al., 1997).Figure 4.1 Flow chart illustrat<strong>in</strong>g the relationships between soil erodibility controls with<strong>in</strong> alandscape. Grey boxes represent environmental conditions and processes that determ<strong>in</strong>e soil surfaceconditions and the impact of disturbance mechanisms on the availability of loose erodible materialThe susceptibility of a land surface to w<strong>in</strong>d erosion is highly sensitive to changes <strong>in</strong> soilerodibility. This sensitivity is most evident when crusted soil surfaces are disturbed bycultivation or trampl<strong>in</strong>g by livestock. Belnap and Gillette (1997), for example, reported a 73-92% decrease <strong>in</strong> the threshold friction velocity (u *t ) required for gra<strong>in</strong> mobilisation onmoderately disturbed sandy soils. Numerous studies have reported similar responses for arange of soils and types of surface disturbance (e.g. Williams et al., 1995; Leys and Eldridge,100

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