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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 5 – Land Erodibility Model Developmentsurfaces has been observed by the authors, these areas which occur along the river systemsdissect<strong>in</strong>g the study area were not <strong>in</strong>cluded <strong>in</strong> the mask.5.4 Model Input DataSoil texture data (clay content <strong>in</strong> topsoil) at a 1 x 1 km spatial resolution was acquired fromthe <strong>Australia</strong>n Natural Resources Atlas (ANRA), as used by Shao et al. (1994). Foliageprojective cover (FPC – a vertical projection of tree canopy cover) data for 2003 were used asa representative measure of tree cover. FPC data at a 30 x 30 m spatial resolution weresourced from the Statewide Landcover and Trees Study (SLATS), and were derived fromLandsat ETM+ satellite imagery by the methods of Danaher et al. (2004). Aerial photographassessments (1:250 000 scale) of the extent of stony pavements with<strong>in</strong> the study area wereused to derive the stone cover mask and were sourced from the <strong>Western</strong> Arid Regions LandUse Study (WARLUS; QDPI, 1974). Daily spatial data of grass cover (%) and soil water(mm per top 10 cm of profile) were obta<strong>in</strong>ed from the <strong>Australia</strong>n pasture growth modelAussieGRASS (Carter et al., 1996a,b; Littleboy and McKeon, 1997). AussieGRASS is run ata 5 x 5 km spatial resolution on a daily time-step and can be used to h<strong>in</strong>d-cast pastureconditions from 1890 to present. All data except FPC were rescaled to a 5 x 5 km resolutionfor modell<strong>in</strong>g with AUSLEM. The FPC data were used at the 30 x 30 m resolution asrescal<strong>in</strong>g resulted <strong>in</strong> a significant loss of tree cover detail (due to sub-grid scale averag<strong>in</strong>g ofthe sparse tree cover <strong>in</strong> the study region), and poor model performance <strong>in</strong> regions where treecover is a significant control on w<strong>in</strong>d erosion.Calibration and validation of AussieGRASS was carried out <strong>in</strong> <strong>Queensland</strong> pasturecommunities, so the model can be expected to perform best <strong>in</strong> the current study area.However, model performance may vary between pasture communities due to plantphysiological and growth characteristics. AussieGRASS output is most accurate over areas25 to 50 times the resolution of its 5 x 5 km <strong>in</strong>puts (Carter et al., 1996b). This hasimplications for AUSLEM output validation and <strong>in</strong>terpretation, which must also beconducted at these scales.142

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