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International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Vol XXXV, Part B4. Istanbul 2004
Moose density for Uusimaa, Finland
Years 2001 to 2003 d Pu
(ER RE)
& m
Au" c
d
eno = versa Ursewevity of Tacrmenngy. Toa of Certbgnanny £ Geonatics 2
Figure 8. Interactive animation of the 3D moose density maps
for Uusimaa including the years 2001-2003.
The interface for this system is the same as for the moose
accident analysis tool. The maps intend to stress the information
about the moose density by a color scale from red to green.
4. CONCLUSIONS
The highways with wildlife fences and other major roads with
heavy traffic have sectored the southern Finland to dozen parts.
The fences hinder the long distant movements of moose and
cause changes in the functioning of moose metapopulations.
The changes can be seen as different moose densities in the
separate sides of the fenced highways. The gradual changes
occur also when highway is fenced. The fenced highway
without proper green bridges or underpasses cuts the winter
pasture areas of the continuous moose population the moose
density peaks start to move gradually away from the highway.
Animals look for better pasture areas. At such areas where there
is good under or overpasses in highways suitable for animal
use, such change has not been discovered. The changes are
gradual and they can be seen in decade long time series.
To calculate the moose density for different years provides us
with the basic data to show us changes in the moose density,
which might be caused by the roads. The Kernel method proves
to be a good tool to calculate the density patterns of the
individual moose locations. By creating a smooth of density
values in which the density at each*location reflects the
concentration of points in the surrounding area, analysts are
able to identify how densities vary across a study area. To
overlay of the moose density and road network map can to
identify “hotspots” concerning the location of a traffic wildlife
accident.
A four dimensional animation can help to visually analyze the
moose density patterns over time. Integrating the maps into an
interactive system makes it easy to navigate between the
different maps created for each point in time. In our example
the time span from 2001 to 2003 appears to be too short to
identify significant changes in the moose density. Further
research should aim to integrate data from a longer time period.
The Finnish hunting association will continue to record moose
data points with individual coordinates, so future research will
be able to consider longer time spans.
413
4.1 Acknowledgements
The Finnish Road Administration in cooperation with the
Helsinki University of Technology — Department of
Cartography & Geoinformatics supported this research.
Additionally we thank the Ministry of Transport and
Communication for financing the MOSSE research project.
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