were lowest for that eq. 3b. The underlying CanCov equations
have been shown to be relatively insensitive to CH of more than
7m (results not shown). Since the vCf estimates from eq. 2, 3a
and b did not vary substantially the vCf estimates from eq. 2 are
used in the following.
Figure 1. Time series of vCf predictions for four vegetation
structural categories (VSC) (a to d) in the study area using
MODIS FPAR to approximate the SurfCov subfactor (eq. 2;
blue line), as the product of eq. 2 and the CanCov subfactor
calculation from eq. 3a (green line) and eq. 3b (red line). Those
three vCf predictions are named Scheme I, IIa, and IIb above.
Dry seasons are symbolised by light yellow bars. The mean
number of MODIS FPAR observations per observation date
were 2548, 713, 4191, 1326, 380, and 129 for the ROIs of the
VSC 1 to 6 respectively for the time period of 02/2000 to
12/2006.
3.2 High temporal frequency soil loss predictions
Figure 2 shows a time series of high temporal remotely sensed
vCf (MODIS FPAR vCf) (eq. 2), annual vCf (BGI vCf),
predicted soil erosion (t) (MODIS FPAR E and BGI E) and
daily rainfall (mm) for a randomly selected coordinate in the
study.
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100
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80
1500000
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Erosion (t)
Daily rainfall (mm)
and vegetative cover factors (times 1000)
1000000
40
500000
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20/02/2000 20/02/2001 20/02/2002 20/02/2003 20/02/2004 20/02/2005 20/02/2006
| Serata MODIS FPAR vCf (times 1000) BGI_vCf (times 1000) «Daily rainfall + MODIS FPAR_E > BGI_E ]
Figure 2. Time series of high temporal remotely sensed vCf
(MODIS FPAR vCf) (eq. 2; green line), annual vCf (BGI_vCf,
bright green line), predicted soil erosion (t) (MODIS FPAR E
and BGI E; dotted brown and orange lines respectively) and
daily rainfall (mm; blue line) for a randomly selected coordinate
in the study. Daily rainfall data from SILO (Jeffrey, Carter et al.
2001).
International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Volume XXXIX-B8, 2012
XXII ISPRS Congress, 25 August — 01 September 2012, Melbourne, Australia
Soil loss predictions from the MODIS FPAR vCf (eq. 2)
coincide well with those from the annual BGI vCf, while the
soil loss predictions from eq. 2 are much higher. This is
regarded as an indication of the dominance of the rainfall
erosivity factor in the USLE. Generally, soil losses are mostly
predicted to occur at the end of the dry seasons with high vCf
values. The wet season 2004/2005 has the highest predicted soil
losses from eq. 2.
Whether the patterns of predicted soil loss for the study area
have some agreement with events of streamflow and changed
water quality at the outlet of the catchment (such as increased
suspended solids) can be judged in comparison to an
independent data set: in-stream measurements of cumulative
daily total suspended solids (Figure 3).
Plots of time series of average daily streamflow at Myuna
station, predicted soil loss (FparErosion) (t), and TSS measures
(mg/l) show some similarities between the onset of events and
the shape of event trajectories but other inconsistencies are
quite prominent (Figure 3).
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Figure 3. Cumulative TSS (mg/l) (grey shade) and streamflow
(cumecs/s) (blue line) at the Myuna station and predicted soil
loss for the study area (FparErosion; in t*10 000 for scaling
purposes) (brown line) for three wet seasons (a) 2003/2004, (b)
2004/2005, and (c) 2005/2006. Predicted soil loss was
calculated from the USLE using Scheme I in Figure lor eq. 2
with MODIS FPAR as approximation for the GC. Data sources:
TSS data by David Post, CSIRO; streamflow from QDERM.
Note different scale for y-axes in a, b, and c.
Discharge events and wet seasons show characteristically
different trajectories of all three variables. The wet season
2004/2005 seems to have the closest fit between all three
trajectories in comparison to the other wet seasons.
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