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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 ControlsA number of microbiotic (biological) crust types exist. These are characterized by thebiological organisms driv<strong>in</strong>g crust formation. Organisms associated with microbiotic crustformation <strong>in</strong>clude: mosses and liverworts, lichens, fungi, algae, cyanobacteria, and othermicrobiota. Microbiotic organisms facilitate crust formation by b<strong>in</strong>d<strong>in</strong>g soil particles togetherthrough secretion of gels or b<strong>in</strong>d<strong>in</strong>g with structural filaments. Crust classification systemshave been proposed based on surface micro-topography of the crusted soil (Eldridge andGreene, 1994; Johansen, 1993). These <strong>in</strong>clude: smooth, rugose, roll<strong>in</strong>g, and p<strong>in</strong>nacletopographies. These surface structures generally reflect the climate of the region ofoccurrence. For example, smooth crusts are associated with hot hyper-arid habitats, whilstp<strong>in</strong>nacled crusts are associated with cold climates <strong>in</strong> which frost heav<strong>in</strong>g occurs (Belnap etal., 2001a). As for physical crusts, climate, soil texture, and soil chemistry play importantroles <strong>in</strong> biological crust formation and structural characteristics. The presence and type ofvegetative cover also affect biological crust formation. Vegetation affects the ability ofprecipitation to reach the soil (or crust) surface, and <strong>in</strong> a species-species competition sense(Belnap et al., 2001b).Physical and microbiotic crust formation are particularly sensitive to climate and soil texturalcharacteristics. The amount, <strong>in</strong>tensity, and frequency of precipitation determ<strong>in</strong>e the type ofphysical crust formation, and where present, biological crust growth or degradation (Belnapand Gillette, 1998). In addition to these factors, the precipitation efficiency is regulated bysolar radiation <strong>in</strong>tensity and potential evaporation. These latter factors <strong>in</strong>fluence the rate ofsoil particle transport, deposition and b<strong>in</strong>d<strong>in</strong>g, and the ability of microbiotic organisms toutilise the moisture, or <strong>in</strong> fact survive close to the soil surface. Soil texture, <strong>in</strong> particular sandand clay content, have been found to affect the soil particle b<strong>in</strong>d<strong>in</strong>g, and habitat suitability formicrobiota (Diouf et al., 1990; Skidmore and Layton, 1992). Physical crusts do not formreadily <strong>in</strong> sandy soils due to a lack of f<strong>in</strong>e particles required for <strong>in</strong>ter-particle b<strong>in</strong>d<strong>in</strong>g. Loamyand clay textured soils, however, provide conditions suitable for <strong>in</strong>ter-particle b<strong>in</strong>d<strong>in</strong>g byphysical (structural and depositional) processes, and stable habitats for crust form<strong>in</strong>gmicrobiota.While crust formation may be triggered by precipitation, crust degradation or breakdownoccurs as a result of photo-degradation, burn<strong>in</strong>g, structural breakdown (e.g. <strong>in</strong> self-mulch<strong>in</strong>gsoils), trampl<strong>in</strong>g by livestock, mechanical disturbance, and <strong>in</strong> the case of biological crusts,death (Eldridge and Green, 1994; Belnap and Eldridge, 2001). The extent and <strong>in</strong>tensity of51

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