Comparison between the USLE, the USLE-M and replicate plots to model
rainfall erosion on bare fallow areas
P.I.A. Kinnell
Institute for Applied Ecology, University of Canberra, Canberra, Australia
abstract article info
Article history:
Received 13 January 2016
Received in revised form 11 May 2016
Accepted 20 May 2016
Available online xxxx
It has been proposed that the best physical model of erosion from a plot is provided by a replicate plot (Nearing,
1998). Event data from paired bare fallow plots in the USLE database were used to examine the abilities of rep-
licate plots, the USLE and the USLE-M to model event erosion on bare fallow plots. The Nash-Sutcliffe efficiency
factor as applied to logarithmic transforms of the data was used to evaluate the overall performance of models at
a number of locations. The value of this efficiency factor is influenced by both systematic and stochastic differ-
ences between the pairs. Systematic differences are the result of systematic differences in event runoff or
event sediment concentration or both, and the degree of the impact of them varies as the regression coefficient
for the relationship between the soil losses from the pairs varies from the value of 1.0. In most cases the replicate
model performed better than the USLE-M that modelled event soil loss as a product of observed event runoff and
event sediment concentration directly related to the EI
30
index. Generally, failure of replicates to match runoff
was compensated by the ability of the replicated to determine sediment concentrations better than the USLE-M.
© 2016 Elsevier B.V. All rights reserved.
Keywords:
USLE database
Soil loss prediction
USLE/RUSLE
USLE-M
Runoff
1. Introduction
The Universal Soil Loss Equation (USLE; Wischmeier and Smith,
1965, 1978) and subsequent revisions (eg RUSLE; Renard et al., 1997)
and refinements, have provided a model for predicting soil erosion
loss that has been used rightly and wrongly throughout the world.
The USLE operates mathematically in two steps. The first step is the pre-
diction of long term (~20 years) average annual soil loss from the unit
plot (A
1
), a bare fallow area 22.1 m long on a 9% slope gradient, in
terms of a rainfall runoff factor (R) and a soil dependent factor (K).
A
1
¼ RK ð1Þ
where A
1
has units of mass per unit area, R is the long term product of
storm kinetic energy (E) and the maximum 30-minute intensity (EI
30
),
and K is the loss of soil per unit of R. In order to predict soil losses
from areas which differ from the unit plot, A
1
is multiplied in the second
step by factors that account for slope length (L), slope gradient (S), crop
and crop management (C) and soil conservation practice (P).
A ¼ A
1
LSCP ð2Þ
where L = S = C = P = 1.0 for the unit plot. Eq. (1) provides the means
of taking account of spatial variations in climate and soil. Consequently,
the unit plot is the primary physical model on which the USLE model-
ling approach is based. However, it has been proposed that the best
physical model of erosion from a plot is provided by a replicate plot
(Nearing, 1998). The USLE data base contains data from replicated
bare fallow plots installed at a number of locations. The objective of
work reported here is to examine the concept that “the best physical
model of erosion from a plot is provided by a replicate plot” by analyzing
event data from individual pairs of replicated bare fallow plots
contained in the USLE data base and compare the result with the ability
of the USLE/RUSLE and the USLE-M (Kinnell and Risse, 1998) to model
event soil losses on bare fallow areas.
1.1. Measures of model effectiveness
Replicated plots show “random” (stochastic) variations in soil losses
between them (Wendt et al., 1986) at the event scale that tend to be
normally distributed (Nearing, 1998). The primary issue that concerned
Nearing was the observation that the coefficients of variation were
higher for small soil losses than high soil losses so that he perceived
that the observation that models like the USLE and WEPP (Flanagan
and Nearing, 1995) tended to over predict small soil losses and under
predict large soil losses (Tiwari et al., 2000) was a mathematical phe-
nomenon rather than a function of any bias inherent in the models
themselves. Subsequently, Nearing et al. (1999) examined data from
Catena 145 (2016) 39–46
E-mail address: peter.kinnell@canberra.edu.au.
http://dx.doi.org/10.1016/j.catena.2016.05.017
0341-8162/© 2016 Elsevier B.V. All rights reserved.
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