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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 2 – Land Erodibility Controlsparticle entra<strong>in</strong>ment and quantifies susceptibility to w<strong>in</strong>d erosion through the thresholdfriction velocity (u *t ) at which particle entra<strong>in</strong>ment will occur. This method is frequently used<strong>in</strong> process-based w<strong>in</strong>d erosion modell<strong>in</strong>g (e.g. Marticorena and Bergametti, 1995; Shao,2000). Computation of u *t to assess erodibility provides a measure that is <strong>in</strong>dependent of, butaccounts for the dependence of w<strong>in</strong>d erosion on w<strong>in</strong>d erosivity.Aeolian abrasion processes can affect assessments of soil and land erodibility. This isrelevant to assess<strong>in</strong>g erodibility through soil erosion rates, but has not always beenconsidered <strong>in</strong> these studies. Aeolian abrasion (described <strong>in</strong> Section 2.2.7) is the process bywhich f<strong>in</strong>e clay-sized particles are emitted <strong>in</strong>to the atmosphere. The process is a response tosaltation (Section 2.2.1), whereby bounc<strong>in</strong>g (saltat<strong>in</strong>g) particles and/or particles on the soilsurface break down or become detached due to particle impact forces. Soils with high sandcontent are typically mobile and are considered highly erodible (Table 2.2). However, they donot necessarily produce large quantities of dust. This may be the case if the relativeproportion of f<strong>in</strong>e (clay) particles <strong>in</strong> the soil is low (Pye, 1987). Soils with high clay contentmay have a low erodibility due to strong <strong>in</strong>ter-particle b<strong>in</strong>d<strong>in</strong>g or surface crust<strong>in</strong>g. However,with the <strong>in</strong>troduction of some abrasion mechanism to release the f<strong>in</strong>e particles, clay soils canbe significant dust emitters. The presence of abrasion material is governed by soil surfaceconditions, and the availability of sand size particles, for example from a neighbour<strong>in</strong>g dunesource. When assess<strong>in</strong>g erodibility it is important to recognize and separate potential soilmobility measured by erosion rates as dist<strong>in</strong>ct from potential dust production <strong>in</strong>duced byaeolian abrasion (e.g. McTa<strong>in</strong>sh et al., 1999 – Land Erodibility Index).2.1.3 Def<strong>in</strong>itions of ErodibilityThe terms ‘soil erodibility’ and ‘land erodibility’ will be used <strong>in</strong> this thesis to describe theseparate but related conditions of soil and land susceptibility to w<strong>in</strong>d erosion. The terms aredef<strong>in</strong>ed as follows:Soil Erodibility:The susceptibility of a soil to mobilisation by w<strong>in</strong>d. Soil erodibility is spatially variable andtemporally dynamic, and is a related to the availability of loose erodible material (< 0.84 mm)on the soil surface as determ<strong>in</strong>ed by aggregation (aggregate size distribution and aggregatestability), surface crust<strong>in</strong>g and soil moisture content. Factors controll<strong>in</strong>g soil erodibility are31

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