Eolian Suspension Above the Saltation Layer, the Concentration Profile

ABSTRACT The acquisition of a new set of data on dust emission obtained at Owens Lake, California, was used to assess the performance of a previously published theoretical model that describes the normalized concentration profile of material in suspension above an actively emitting surface as a logarithmic function. The normalized concentration profile has more commonly been modeled as a power law. Least-squares regression was used to fit both the logarithmic and the power-law model to approximately 20 hours of data on 10-minute average concentration profiles. Results for all these data combined and for each individual profile indicated that the logarithmic model better explains the concentration gradient profile than the power-law model. The predicted behavior of the model parameters, including a concentration scaling parameter * and a transfer coefficient for suspended particles , was examined. It was observed that * divided by a defined reference concentration was relatively invariant during emission events as predicted by the model and had a value of 0.18 (± 0.02). For the reference heights at which particle concentration and wind speed were measured (1.7 and 9 m) the transfer coefficient for suspended particles was approximately 0.22 (± 0.05) of the calculated momentum transfer coefficient defined here as the wind speed at the reference height divided by the friction velocity.

[1]  Y. Shao Physics and Modelling of Wind Erosion , 2001 .

[2]  William G. Nickling,et al.  Dust emission and transport in Mali, West Africa , 1993 .

[3]  K. Pye Aeolian dust and dust deposits , 1987 .

[4]  Dale A. Gillette,et al.  A qualitative geophysical explanation for hot spot dust emitting source regions , 1999 .

[5]  M. Reheis,et al.  Dust deposition in southern Nevada and California, 1984-1989: Relations to climate, source area, and source lithology , 1995 .

[6]  M. López Wind erosion in agricultural soils: an example of limited supply of particles available for erosion , 1998 .

[7]  R. J. Kind,et al.  A critical examination of the requirements for model simulation of wind-induced erosion/deposition phenomena such as snow drifting , 1976 .

[8]  Dale A. Gillette,et al.  Fine Particulate Emissions Due to Wind Erosion , 1977 .

[9]  R. Stull An Introduction to Boundary Layer Meteorology , 1988 .

[10]  Chris Houser,et al.  The emission and vertical flux of particulate matter <10 μm from a disturbed clay‐crusted surface , 2001 .

[11]  Thomas E. Gill,et al.  Eolian sediments generated by anthropogenic disturbance of playas: human impacts on the geomorphic system and geomorphic impacts on the human system , 1996 .

[12]  R. J. Kind,et al.  One-dimensional aeolian suspension above beds of loose particles—A new concentration-profile equation , 1992 .

[13]  R. Bagnold,et al.  The Physics of Blown Sand and Desert Dunes , 1941 .

[14]  D. Gillette,et al.  Microscale transport of sand‐sized soil aggregates eroded by wind , 1974 .

[15]  Ludwig Prandtl,et al.  Essentials of fluid dynamics : with applications to hydraulics, aeronautics, meteorology and other subjects , 1952 .

[16]  J. Garratt The Atmospheric Boundary Layer , 1992 .

[17]  Kenneth Pye,et al.  Dust transport and the question of desert loess formation , 1987 .

[18]  Robert S. Anderson,et al.  Sediment transport by wind: Toward a general model , 1986 .