International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Vol XXXV, Part B4. Istanbul 2004
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Figure 2: (a) Predicted soil losses from rain-fed fields
for 1972. Black areas are masked out areas of basalt,
built-up areas and rangeland areas. (b) Predicted soil
losses from rangeland for the same year. Black areas
are masked out built-up, basalt and cultivated areas.
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Figure 3: (a) Predicted soil losses from rain-fed fields
for 1992. Black areas are masked out areas of basalt,
built-up areas, rangelands and irrigated cropland. (b)
Predicted soil losses from irrigated cropland in 1992.
Black areas are masked out areas of basalt, built-up
areas, rangelands and rain-fed fields. (c) Predicted soil
losses from rangeland for the same year. Black areas
are masked out built-up, basalt and cultivated areas.
3.3 Verification of the Soil Loss Maps
3.3.1 The Verification Data Set: It was not
possible to validate the predicted soil loss maps for
1972 and 1992 in the years for which the data was
acquired. However, an attempt to verify the soil loss
model was made by comparing the soil loss
predictions for 1992 with evidence of soil loss from
47 rain-fed fields at the end of the 1998/1999 wet
season. The presence or absence of visual evidence of
soil erosion in these fields was used to determine
whether erosion had occurred or not during the
preceding wet season.
The method proposed by the FAO (1979) for the
identification of soil erosion using post-erosion
evidence was adopted. This method uses simple
visual criteria (Plates 1, 2, 3 and 4). Furthermore, it
has been found that the least ambiguous evidence of
soil erosion by water in the fields was rilling (Plate 1).
Therefore, most of the subsequent model verification
relies on rilling as a surrogate for ‘observed soil loss’.
Plate 1: Rills formation by the coalescence of two
plough furrows.
Plate 2: A trail of eroded sediment across a cracked
silt-rich surface.
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