Full text: Resource and environmental monitoring

  
  
4. THE APPLIED SOFTWARES 
I used the DigiTerra IMAGE software for the orientation, 
rectification and classification purposes. It was developed by my 
college, Kornél Czimber and the DigiTerra Engineering Office, 
and has its own graphic user interface, and the most common 
functions of image processing. For the GIS analysis and layouts 
the ESRI-Autodesk ArcCAD v11.3 and the ESRI ArcView 3.0 
software was used.. 
5. THE ORIENTATIONS 
The Landsat TM image was georeferenced, by the FÓMI RSC. 
The SPOT image was not oriented. | made the orientation with 
the DigiTerra-IMAGE software. I pick the ground control points 
(GCPs) from the DFBM. The accuracy of the orientation was 
0.38 pixel (3.8 m). After the orientation a bilinear resampling 
with 10 m ground resolution was made. Then the Brovey 
transform was prepared with the Landsat TM and SPOT Pan. 
According to certain opinion (Koch et al, 1997) the IHS 
transformation gives better results, but - as it appears below - I 
preferred the Brovey transformation. The result, a 10 m ground 
resolution 7 band multispectral image is very nice for visual 
interpretation, but hardly usable for classification methods. 
I produced ortophotographs from the aerial photographs. Instead 
of using stereo pairs, I applied single photographs with digital 
elevation model (DDM-10). The orientation points were from the 
DFBM, too. The orientation parameters of the P1 are showed in 
Table 2. 
A= 0.27187 ° 
B= -3.78701 ° 
r= 0.757248 
focal = 152.7 mm 
of aerial Z= 4842.4 m 
  
Table 2: The orientation parameters of the P1 photo. 
The average accuracy of the orientation was 2.08 pixel which 
means 5.55 m. After the orientation I made a bilinear resampling 
with 3 m ground resolution. 
The orientation parameters of the P2 are showed in Table 3. 
-0.983063 
-1.70205 ? 
3.41245 ? 
152.13 mm 
Z- 1257.37 m 
  
Table 3: The orientation parameters of the P2 photo. 
The average accuracy of the orientation was 13.9 pixel which 
means 9.73 m. It doesn't seem so good, but according to the 
accuracy of the DFBM it isn't bad. The other reason is the 
resolution used, 300 dpi at the scanning, but our hardware 
possibilities are limited. After the orientation I made a bilinear 
resampling with 0.5 m ground resolution. 
6. THE CLASSIFICATION METHOD 
6.1 The developing of classes 
I used the capabilities of the DigiTerra-IMAGE software in the 
classifications. I made the forests classes based on the National 
Forest Database, and the DFBM. I developed the polygons of 
different classes from forestry point of view. Then I made buffer- 
zones from the polygons with negative values (decreasing the 
area, Figure 4.) for omitting the mixed pixels at the stand's 
boundary. 
  
  
Figure 4: Buffering polygons. 
Then I put the emphasis on the refinement of the training areas. 
The reason for this modification is the different updating time of 
the DFBM and the National Forest Database and the different 
creation time of the images. 10 forest classes were shaped at 
first, these were the followings: robinia, sessile oak, hairy oak, 
hornbeam, birch, beech, larch, scotch pine, austrian pine, spruce. 
6.2 Classification of Landsat TM 
The first step was the examination of the bands. The first band 
was very noisy, the second band was striped, and because of the 
georeference the strips were diagonal. | couldn't remove the 
diagonal strips, becausc only ‘horizontal’ and ‘vertical’ strips are 
removable by the software I used. So the Band I., II., and the VI. 
- because of the insufficient resolution - were omitted from the 
classification method. The next measures was the topographic 
normalisation. The correlation between the bands and the DTM 
was studied at first. | chose an area with homogenous vegetation 
for the statistics. The results are summarised in Table 5. 
  
  
  
  
  
The number | The inclination of the | The correlation 
of the band regression line (m) coefficient 
III. 0.03 0.51 
IV. 0.46 0.87 
V. 0.17 0.85 
VII. 0.07 0.76 
  
  
  
  
  
Table 5: The regression parameters between the bands and the 
DTM. 
It is apparent that the band IV. has the most correlation with the 
DTM. An approaching DTM extraction is possible, when the 
vegetation is homogenous or a land cover map is available. 
366 International Archives of Photogrammetry and Remote Sensing. Vol. XXXII, Part 7, Budapest, 1998 
  
  
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