Full text: Resource and environmental monitoring

  
  
  
  
semi-natural vegetation also occurs in flat areas along the 
river which was not considered in the decision rules. 
Table 5 also shows that the decision rules were not 
discriminate enough to separate annual crops and semi- 
natural vegetation precisely. Misclassification occurred in 
the major landscape unit HsZ (Fig. 3), where mainly 
annual crops occur, but where in areas with steep slopes 
semi-natural vegetation occurs. Although we tried to cope 
with this by applying rules based on slope steepness, the 
geometric accuracy of the DEM was not enough to 
achieve a higher accuracy. 
Alternatively it was tried statistically with discriminant 
analysis to obtain rules for classifying cases into one of 
the land cover classes from the geo-data set. Agronomic 
data were compared with elevation, slope and aspect 
derived from the DEM. A case is classified, based on its 
discriminant score, in the group where the posterior 
probability is the largest. In table 6 the results are shown. 
Table - 6 Classification results of discriminant analysis 
  
  
  
Actual Predicted group membership 
| group 
no irr. tree | rainfed | semi- annual 
of crop tree natural | crops 
cases crop veget. 
irr. tree 242 234 6 1 ] 
crops 96.7% 2.505 0.4% 0.4% 
rain-fed tree 78 28 39 1 10 
crops 35.9% | 50.0% 1.3% | 12.8% 
semi-nat. 21 6 14 1 0 
vegetation 28.6% | 66.7% 4.8% 0% 
annual 61 28 23 0 10 
crops 45.9% | 37.7% 0% | 16.4% 
  
  
  
  
  
  
  
Percent of “grouped “ cases correctly classified : 70.6%. 
Since this approach gives an overall classification 
accuracy of only about 71%, it was decided not to make 
rules based on this analysis. Therefore in this study we 
only use rules based on expert knowledge, which gives a 
considerable increase in accuracy. 
6. GENERAL DISCUSSION AND CONCLUSIONS 
In this study a number of methods are examined to 
improve classification accuracy of remote sensing images. 
The approach of topographic normalization, using 
Lambertian or non-Lambertian reflectance model, does 
not give a significant difference in accuracy for the study 
area. Land cover classes show a strong topographic 
specialization. For example, the land cover irrigated tree 
crops grows on flat areas near the river, semi-natural 
vegetation grows at higher elevation and on steep slopes 
etc. This approach, removal of ‘topographic information’, 
will probably be more successful in areas where 
topographic specialization is less strong. 
The second approach using soil and topographic 
information in classification gives an 18% increase in 
348 
overall accuracy of the image for the study area. The 
different land cover types in the study area each have 
their specific environment, so that knowledge rules are 
effective. This implies that in comparable areas expert 
rules will improve the classification accuracy 
considerably. However the method demands a good 
understanding of the relation between terrain units and 
land cover and of the significance of the levels of the land 
system hierarchy in order to formulate the rules. When 
that is the case rules based on statistical analysis will not 
give better results than expert knowledge at 
corresponding aggregation levels. 
The extent to which the added data and knowledge may 
be expected to alter the classification accuracy of a single 
object class, depends also on the spectral discrimination. 
When spectral class discrimination is poor, the extra 
information based on contextual knowledge can improve 
the classification. 
Expert rules should always be formulated explicitly, at the 
right aggregation level. Rules should be nested in case 
they combine knowledge from different aggregation 
levels. If an expert rule is too rigid (for example in hilly 
areas no irrigated tree crops occur) then a monitoring 
system may overlook spots where irrigated tree crops do 
occur. General rules may be of help in a good spatial 
generalization of the area. 
Further to this, we expect that in many areas also spatial 
expert rules, for instance describing crop as a function of 
distance to rivers, may improve the accuracy of the 
analysis. 
The following general conclusions can be drawn: 
|l. Topographic normalization, both assuming 
Lambertian or non-Lambertian reflectance, does not 
show significant effect on land cover classification 
accuracy of a rcinote sensing image of the study area. 
The main reason for this seems to be the topographic 
specialization of the different cover types. 
2. Statistical analysis of land cover data in combination 
with topographic data derived from a DEM does not 
show an improvement in classification. accuracy. 
Probably this is caused by the resolution of the DEM, 
which seems still too small. 
3. The accuracy of land cover classification in the study 
area improves considerably, when knowledge based 
on landscape and soil data and its relation to land 
cover is included. An average improvement of 18% in 
land cover classification is achieved. 
4. The measure of improvement in the classification 
accuracy as a result of the application of knowledge- 
based rules depends on: 
e the degree of generalization in defining land 
cover classes 
e The level of aggregation at which rules are 
applied and the degree of adjustment of these 
rules with more specific information from lower 
levels 
e the resolution of the DEM and the thematic 
resolution and accuracy of field data. 
Intemational Archives of Photogrammetry and Remote Sensing. Vol. XXXII, Part 7, Budapest, 1998 
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