Full text: Resource and environmental monitoring

  
  
  
presented in figure 3 is based on landform element 
information. 
Soil types, studied at facet and site level, become an 
aggregated attribute at higher levels; it is called a soil 
association. 
Often the higher level is very predictive as to a particular 
soil property: the Hills in our example consist mainly of 
marls (parent material) on which dense clayey soils 
(figure 3) develop unsuitable for tree crops. However, 
when studying the landform element composition in more 
detail it turns out that certain hills are capped with fluvial 
remnants where olives grow well while others consist of 
steep sandstone ridges with shallow soils, where only 
natural vegetation will do. The lower level information in 
this example enables us to adjust general statements based 
on higher level information. 
The rules to predict soil properties have therefore a nested 
format just as the terrain units of the land system 
hierarchy (figure 2) on which they are based. First a 
general rule is formulated based on the major landform. 
That rule is then conditioned by a nested subset of rules in 
accordance with these lower level nested terrain units as 
follows: 
1. If major landform is Hills consisting mainly of marl 
then we expect swelling clays 
1.1 But if the land form element within the Hills is a 
fluvial terrace remnant and/or erosion glacis, then 
we expect permeable medium to coarse textured 
soils 
1.1.1 But if slopes of the terrace remnant are steeper 
than 30 % then soils are very shallow and if the 
unit corresponds with the lower slopes of the 
erosion glacis then soils are dense clayey. 
Because soil properties predict land cover performance 
experts can use the same nested rules to predict land 
cover occurrence starting from major land form level and 
adjusting for specific conditions at more detailed level. 
1. If major landform is Hills consisting mainly of marl 
then we expect cereals 
1.1 But if the land form element within the Hills is a 
fluvial terrace remnant and/or erosion glacis, then we 
expect olives 
1.1.1 But if slopes of the terrace remnants are steeper 
than 30 % then we expect semi-natural vegetation 
and if the unit corresponds with the lower slopes 
of the erosion Glacis then we expect cereals. 
These type of rules have been applied to improve the 
classification results. Some other typical rules are: 
e In serpentinite ultramafic rocks (MuT, figure 3) only 
semi-natural vegetation is present. 
e On hills in soft rocks with marl-rich parent materials 
(HsZ) no rain-fed tree crops are found. 
e On hills in hard rocks from Gneiss (MmG), semi- 
natural vegetation and rain-fed tree crops may occur. 
Annual crops and irrigated tree crop can not be found 
in this area. 
5. RESULTS AND DISCUSSION 
In this section the results are presented of the 3 different 
approaches for classification: (1) standard supervised 
classification (2) topographic normalization before 
supervised classification (3) use of contextual information 
after supervised classification. The results of the different 
approaches will be compared by evaluating error matrices 
and classification accuracy. In all cases the same satellite 
image was used to extract land cover classes. This image 
was georeferenced with acceptable spatial accuracy: 
within the total RMS error of 1.1 pixel (resolution 
30m*30m). Classification accuracy was assessed using an 
independent data set. Land cover data of the geo-database 
of Alora were used. The collection of these data was 
intended to record cover types and not as training data for 
classification, so it even may include fields which are 
having mixed pixels. Accuracy is therefore lower than 
what would be achieved using the accuracy of the training 
set. 
Approach 1. Supervised classification (standard) 
The result of the standard supervised maximum likelihood 
classification for the 4 classes is given in figure 4. 
  
  
  
Table-1 Classification error matrix for standard. 
supervised classification. 
classified | reference data 
data 
irr. tree | rainfed | semi- annual total 
crop tree natural | crops 
crop veget. 
ir. tree | 241 0 l 0 242 
crop 
rain-fed 36 348 45 90 519 
tree crop 
semi-nat. 6 63 151 36 256 
veget. 
annual 4 84 77 275 440 
crops 
287 495 274 401 1457 
  
  
  
  
  
  
  
Table - 2 Classification accuracy. report for standard 
supervised classification. 
  
  
  
  
  
Cover class producers accuracy | users accuracy 
irr. tree crops 83.9% 99.6% 
rain-fed tree crops 70.3% 67.0% 
semi-nat. vegetation | 55.1% 58.9% 
annual crops 68.6% 62.5% 
Overall accuracy 69.7 % 
  
  
Table 2 shows that the overall accuracy is about 70%, 
which is reasonable taking into account the few classes 
and the evaluation with a fully independent data set. 
346 International Archives of Photogrammetry and Remote Sensing. Vol. XXXII, Part 7, Budapest, 1998 
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