HR: 0800h
AN: P31B-0990 [Abstracts]
TI: Representation of Vegetation and other Non-erodible Elements in Aeolian Sediment Transport
Models
AU: * King, J
EM: kingj@uoguelph.ca
AF: Wind Erosion Laboratory
Department of Geography
University of Guelph, University of Guelph, Guelph, ON N1G 2W1
Canada
AU: Nickling, W G
EM: nickling@uoguelph.ca
AF: Wind Erosion Laboratory
Department of Geography
University of Guelph, University of Guelph, Guelph, ON N1G 2W1
Canada
AU: Gillies, J A
AF: Division of Atmospheric Sciences
Desert Research Institute, 2215 Raggio Parkway, Reno, NV 89512
United States
AB:
The presence of non-erodible elements is well understood to be a reducing factor for soil erosion by wind, but the limits of
its protection of the surface and erosion threshold prediction is complicated by the varying geometry, spatial organization
and density of the elements. The predictive capabilities of some of the most recent models for estimating wind driven
particle fluxes are reduced due to the poor representation of the effectiveness of vegetation to reduce wind erosion and dust
emissions.
Two approaches have been taken to account for roughness effects on sediment transport thresholds. Marticorena and Bergametti
(1995) in their dust emission model parameterize the effect of roughness on threshold with the assumption that there is a
relationship between roughness density and the aerodynamic roughness length of a surface and that the partitioning of shear
stress can be estimated based on this relationship. Raupach et al. (1993) offer a different approach based on physical
modeling of wake developments behind individual roughness elements and the partition of the surface stress and the total
stress over a roughened surface. This geometric and drag coefficient based-predictive model allows the user to specify
available inputs to describe most environments and generate the ratio that characterizes the erosion threshold of an
initially bare erodible surface with the threshold once non-erodible elements are present. The objective of this presentation
is to quantify the precision and accuracy of these two threshold wind erosion models by comparing model predictions with
field and wind tunnel measurements with airflow over a range of roughness element scales, shapes, and distributions.
The comparison between the models shows the partitioning approach to be a good framework to explain the effect of roughness
on entrainment (and potentially transport) of sediment by wind. Both models provided very good agreement for the wind tunnel
experiments using solid objects on a non-erodible surface, however their performance when tested in a field environment is
less favourable. The Marticorena and Bergametti (1995) approach displays a scaling dependency when the difference between the
roughness length of the surface and the overall roughness length is too great, creating a negative partition. While the
Raupach et al. (1993) model requires more inputs than that of Marticorena and Bergametti (1995) its predictions are better
due to the incorporation of more variations in the roughness geometry and the alterations to the flow they can cause.
DE: 5415 Erosion and weathering
DE: 5445 Meteorology (3346)
DE: 3307 Boundary layer processes
DE: 1625 Geomorphology and weathering (1824, 1886)
DE: 0343 Planetary atmospheres (5405, 5407, 5409, 5704, 5705, 5707)
SC: Planetary Sciences [P]
MN: 2004 AGU Fall Meeting