Full text: XVIIIth Congress (Part B7)

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Homogenous landscapes usually have certain features of 
textures. Hence, the discrimination of these textures in 
satellite images helps to segment the images to localize 
exactly boundaries of homogeneous landscapes, upon 
which the regression functions are modelled. 
To define a texture, the Gibbs random field probability 
model with double interaction of responses (Jain, 
Gimel'farb, 1995) was used. The model defines a spatial 
homogeneous texture as realisation of Markov's random 
field sample which is given by the Gibbs probability 
distribution. 
If the structure is known, the model allows to generate 
sampling realisations by means of element-by-element 
stochastic relaxation. The model parameters for each 
kind of texture can be estimated in accordance to training 
patterns. First the analytical initial approximation for 
maximum likelihood potential estimations are calculated 
for a lot of interaction types. A map of these interactions 
is generated. This gives the possibility to compare them 
regarding to its strength and to select the most 
representative structure of interactions for the given kind 
of texture. 
After this, the initial estimations of potentials for the 
selected kinds of interactions will be completely 
determined by stochastic approximation. The texture 
analysis proposed above was carried out for an area near 
the Chernobyl Nuclear Power Plant (NPP). Five types of 
landscapes were discriminated on this site: 
1- pine xerophyto-lichenous 
2- oak-pine hazelous grassy 
3 - oak-hornbeam-pine fern-sedgous 
4 - alder marshy forest 
5 - long-fellow non drained lands. 
As a result of the experiment, the discriminated types of 
landscapes were distinguished according to their texture 
except for oak-pine hazelous grassy and oak-hornbeam- 
pine fern-sedgeous forests. 
The result of the automatic segmentation of a satellite 
image subset according to the textures of the landscape 
types showed pine xerophyte-lichenous and sparse 
growth of trees to be discriminated most significantly. 
The other types of landscapes were discriminated some- 
thing weaker. 
The volume of information and the spatial relations of 
investigated phenomena require the use of GIS 
technology. 
For this purposes the GIS TRIAS has been developed by 
the uve Remote Sensing Centre Potsdam to match 
remote sensing data and environmental information 
(Lyalko, Marek et al., 1995a). TRIAS is a MS-Windows 
based user friendly and low cost GIS working on IBM- 
compatible PC's. Similar to other GIS TRIAS allows to 
model the natural phenomena as point, line or areal 
objects. These objects can be connected with relational 
data bases. The definition of object hierarchies, text 
objects and thematic relations between the objects is 
possible, too. 
The following properties and possibilities of TRIAS have 
been used to carry out the investigations: 
- overlaying of vector and raster data 
- Interactive vectorization of raster data 
- flexible catalogue of object classes which is oriented on 
cartographic standards and can be extended on 
thematic characteristics 
457 
- free possibilities for combining topographic and 
thematic map information and various presentation 
models 
- possibilities for generating map output with a great 
number of presentation tools and a comfortable 
connection to network plotters under MS-Windows 
- connection to retrieving features in a relational data 
base. 
The handling of primary remote sensing and ground truth 
information allows to compare great numbers of thematic 
and temporal layers and to derive tendencies with regard 
to spatial and temporal changes of various natural 
components. 
Finally the use of GIS technology allows to carry out the 
classification of the test site for further studies on a 
qualitatively high level. 
3.2 Results 
The programs developed have been used to analyze the 
optical vegetation properties within the southern trail of 
pollution induced by the Chernobyl accident. Primary 
material for the work were multispectral space images 
acquired by the KATE - 200 camera with a focal length of 
200 mm and a ground resolution of about 30 m on the 
,Cosmos" satellite, taken at the 10th of July 1980, as well 
as by the MK - 4 camera with a focal length of 300 mm 
and a resolution of about 20 m on the ,Resource -F-2" 
satellite, taken at the 27th of July 1989. The three 
spectral bands were recorded in the green (500 - 600 
nm), red (600 - 700 nm), and near-infrared band (700 - 
840 nm). Double-negatives of the space photographs 
enlarged by eight times were used for the investigations. 
The brightness values were provided for the various 
landscape elements by image processing at a quite 
dense and regular net of observation points. Thus, each 
point is characterized by its coordinates, brightness in 
three spectral bands, landscape element feature and 
radioactive contamination level. 
In order to get the radioactive contamination level of the 
landscape elements, the map of Cs-137 contamination 
density for soil (scale 1: 200 000) by V. A. Nagorsky 
(firm ,Pripyat', 1993) and also the map of Cs-137 
contamination of coniferous canopy (scale 1: 200 000) 
by À. |. Ostravnenko (1990) were used. Currently Cs-137 
provide the main radioactive contamination of the 
Chernobyl region. 
Nine homogeneous landscapes were identified within the 
limits of the test site. The major elements of landscape 
are pine forest growing on dry soils, grassland, leaf- 
bearing and mixed forest, and agricenouses on dry and 
moist soils. The remaining landscape elements play a 
minor role because of their small area sizes. 
Using regression model (1) described above and the 
programs developed by ZAKIZ, the dependencies for the 
major landscape elements were determined for the red 
and near infrared bands of the space photographs. The 
calculations were carried out for first order polynomials 
(m = 1, m - maximum degree of polynomials). 
For coniferous canopies before and after the Chernobyl 
accident the relations between the spectral properties in 
the red and near-infrared band are absolutely different 
which can only be explained due to radioactive 
contamination. 
Even for vegetation growing on soils with low levels of 
radioactive contamination (less than 2 Ci/km? ) the 
International Archives of Photogrammetry and Remote Sensing. Vol. XXXI, Part B7. Vienna 1996 
 
	        
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