Wind Erosion Impacts on Dryland Soils Ted M. Zobeck, Research Soil Scientist USDA, Agricultural Research Service Lubbock, TX Presentation Overview • • • • • Defining the Scope Soil Formation Aeolian Processes Characteristics of sediment Local Effects – Coppice dunes, islands of fertility • Regional/Global Effects – Proximity to source, loess, Terra Rossa Soils Aeolian deposits occur over much of the globe. Their origin and subsequent development widely varies. Today I will focus on aeolian processes in arid and semi-arid dryland regions. Source FAO, 2002 Wind erosion is a significant aeolian process that produces many effects on soils and landscapes in dryland systems, comprising almost forty percent of the Earth’s land surface. Although wind erosion occurs in almost all climatic regions, it is a dominant process in arid and semi-arid regions. Source FAO, 2002 Wind erosion is active today! Meadow, Texas September 3, 2011, Photo: Ted Zobeck A local man follows his sheep during a dust storm on April 12, 2010 in Huailai county, Hebei Province. Photo: CFP Phoenix, Arizona July 5, 2011. Photo: Assoc. Press Queensland Australia October 2013 Photo: Karen Emmott in ABC Queensland So how do aeolian processes affect soils? First, let’s have a very brief review of the soil and wind erosion processes…. Wind erosion often occurs when soils are bare, loose, dry and subjected to erosive winds. Most prevalent in coarse-textured soils. What we observe to measure the impacts of wind erosion depends upon what and where we sample! Effect of sampling height on particle size Mean diameter varied from 100 µm at 0.15 m to 50 µm at 2 m Zobeck and Fryrear, 1986a This impacts transport of minerals, nutrients, organic matter, microbes… Mean nutrient content and enrichment ratios for dust caught at 0.15 m to 2.0 m for 6 dust storms in west Texas Na K Ca Mg CEC OM Amount 0.06 1.06 7.01 1.19 9.34 4.18 Enrichment Ratio 2.1 1.6 2.0 1.2 2.1 2.0 Nutrients in cmole (+)/kg and OM in g/kg From Zobeck & Fryrear, 1986b Removal of soil can be quite large… During a field campaign from 1989-1997 at Big Spring, Texas, observed soil loss due to wind erosion on an agricultural field varied from about 40 to 290 Mg/Ha/Yr The field was kept bare, smooth, and erodible. Van Pelt & Zobeck, 2004 Creep and Saltation material is usually trapped near the source and impacts local vegetation and surface features Van Pelt & Zobeck, 2004 Erosion of patchy vegetation in grasslands/shrublands has significant impacts on soil properties and redistribution of nutrients and sediment. (Ravi at al., 2010) Differences in soil properties under plants and openings are often observed • Compared with intershrub areas, the shrub patches had a higher soil porosity, infiltration capacity, water-holding capacity, hydraulic conductivity, structural stability, and organic matter content, and lower bulk density. (Stavi et al, 2009). • In another study, total and mineralizable soil N, and total and respirable organic C in the surface 5 cm were significantly greater for soil under plants than soil from openings. (Hook et al., 1991) Let’s look at material that moves greater distances… Where does all of the ‘dust’ go? Well….That depends….. Dust affects nearby ecosystems and soils A recent study by Hirmas and Graham (2011) presented evidence for how the Fry Mountains of California act as a topographic ‘baffle’ against the prevailing wind and trapping aeolian sediment. Studies have discovered how distance from the source affects soils in many ways A 390 km transect in west Texas showed decreasing sand size with distance from the hypothesized Pecos River source (E. M. Seitlheko [with B.L. Allen], 1975) There have been many other studies of the effects of proximity to a source region when studying soils with aeolian parent materials, particularly loess soils. But what about loess? Much of the world’s loess occurs in mid-latitudes associated with glaciation… (Thomas and Wiggs, 2008) Desert Loess Formation Tsoar and Pye, 1987 • Loess mainly medium silt size transported near the surface and so is relatively close to source • Availability of silt source and wind needed • Suitable dust trap very important – Topographic obstacles – Moist ground – Vegetated surfaces • Dust blown during glacial periods from certain deserts (Sinai, Soviet Central Asia, China) accumulated loess in neighboring semi-arid areas Observed Dust Deposition Rates • • • • Global 10 to over 200 t km-2 yr-1 (Pye, 1987) Israel 57-217 t km-2 yr-1(Yaalon and Ganor, 1975) Australia 5-10 t km-2 yr-1 (Tiller et al., 1987) Nigeria 137-181 t km-2 yr-1 (McTainsh and Walker, 1982) • Central and west (Edwards Plateau)Texas 12 t km-2 yr-1 (Rabenhorst et al, 1984) • SHP West Texas 77-103 t km-2 yr-1 (Crabtree, 2005) • S. Nevada and S. California 4 to 30 t km-2 yr-1 (Reheis and Kihl, 1995). • SW California average of 78 t km-2 yr- (Hirmas and Graham, 2011) Dust affects distant ecosystems and soils • Saharan dust has been identified as the most important parent material of soils of the Caribbean Islands and Florida Keys as shown by Al2O3/TiO2, Ti/Y, Ti/Zr, Ti/Th ratios (Muhs, et al., 1990) Dust affects distant ecosystems and soils Hawaiian rain forests receive nutrients from Asia and sustains the productivity of these rain forests (Chadwich et al, 1999). – P is the main regulator of biological activity in oldest sites Rate of P loss from soil Atmospheric contribution of P Dust affects distant ecosystems and soils • ‘Terra Rossa’ soils of Mallorca, Spain developed from African dust (Muhs, et al., 2010) Aeolian processes do indeed impact soil genesis, mineralogy, fertility, and landscape evolution in arid and semi-arid regions and around the globe. 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