The International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences. Vol. XXXVII. Part B7. Beijing 2008
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is used to remove flat area as well as buildings. The use of color
and texture features extracted from the aerial images make it is
possible to merge segments in a semantic way and lead to
delineate forest boundary automatically.
2. MATREIAL AND METHOD
2.1 Aerial images
The true color ( RGB) aerial images in our database have been
made available by Swiss Federal Office of Topography
(Swisstopo) with an average scale of 1:30,000. The images are
oriented block by block and orthorectified with a resolution of
0.5m. The landscapes of Switzerland are very heterogeneous
which can be divided into Jura, Swiss Plateau, Prealps, Alps,
and South-western slopes of the Alps. Our test sites (green
points in Fig.l) include mixed industry areas, agriculture areas,
wines areas etc. which belong to Swiss plateau and Prealpine
areas.
0 50 100 Kilometers
Fig. 1 Test sites
2.2 LIDAR Data
The LIDAR data was acquired between 2001 and 2004 by
Swisstopo. Average flight height above ground was between
1000m and 1500m and the footprint varies between 0.8m and
1.2m. Fig. 2 shows the DTM of Switzerland where there is no
LIDAR data above 2000m. Canopy Height Model (CHM) is a
LIDAR-derived product for deriving relevant vegetation
Fig. 3a Aerial Image Fig. 3b DOM
Fig. 3c DTM Fig. 3c CHM
Fig.3 Aerial image, DTM, DOM and CHM
2.3 NFI Sample Plot Design and Forest Definition
In the first NFI a 1km sampling grid was used. The
intersections define the location of about 12'000 NFI1 sample
plots in the forest. As in the NFI2 and NFI3, only half of the
plots were investigated terrestrially.
As shown in Fig. 4 the NFI-specific forest definition is applied
to aerial imagery in a regular 500m grid. For the terrestrial
sample plots a coarse grid with 1.4km grid was chosen. The
discrimination of forest and non-forest areas in aerial
photographs requires an unambiguous reproducible forest
definition. The used NFI forest definition is the aspects of a
stocking evaluated by the following stand criteria that can be
measured in the aerial photograph: width, crown coverage and
dominant stand height:
• Width: The width of the stocked part of the interpretation area
is at least 25m.
• Crown coverage: The crown coverage of the stocked part of
the interpretation area has to be larger than or equal to 20%.
• Dominant stand height: The stocking has to have a dominant
stand height of 3 m.
For a positive forest decision the following conditions apply:
The minimum width is 25m with crown coverage of 100% and
the required dominant stand height. With increasing width the
minimum crown coverage is allowed to decrease. The smallest
acceptable threshold for the crown coverage is 20% at a
minimum width of 50m.
information. From the raw data points, the Digital Terrain
Model (DTM) and the Digital Surface Model (SM) is D
interpolated (2.5m x 2.5m). The CHM is obtained by
calculating the difference between DSM and DTM. Fig. 3
shows the DTM, DSM, and CHM of one analyzed aerial image.