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The basic framework of corridor analysis consists of identifying areas of habitat which are suitable for the wildlife species in question. Habitat suitability depends upon the needs of a given species. It can be approximated by overlaying layers such as current vegetation, topography (aspect, slope, elevation), distance to water, and perhaps climatic variables such as average temperature and precipitation. Because different wildlife species vary in their sensitivity to human disturbance, habitat suitability is constrained by disturbance variables such as distance to roads, distance to towns, traffic volumes, hunting status, etc. Generally, a coverage of known distribution of a species (sightings, radio-telemetry locations, hunter-kill and road-kill sites) is also developed. A probability
contour is finally developed from the convergence of these coverages
to indicate the likelihood of a given area being suitable for
a given species. Where this probable habitat connects areas of
known population centers, it is often termed a corridor. |
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Mountain
Lion Corridor Pilot Project For example,
to model suitable habitat for mountain lions we initially used
1:100,000 coverages developed by the Interior Columbia Basin
Ecosystem Management Project. Current vegetation coverages (structure
stages and cover types) were derived from NOAA AVHRR imagery
and were mapped using 1 km2 pixels. Predicted road density was
derived by ICBEMP scientists using layers of management regions,
lifeforms, elevation, slopes, and UPS roads using a rule-based
algorhythm. These layers were reclassified, combined, and assigned
a road density class for each possible combination. Streams,
and lakes, were vector-based layers derived from TIGER and USGS
databases. Known mountain lion distribution coverage was derived
from hunting district and hunter survey data. Because mountain
lion habitat suitability is strongly correlated with availability
of prey species, coverages of known mule deer, elk, and mountain
sheep distributions were also used. This Pilot
Project was completed using ICBEMP data during the summer of
1996. Radio-locations of dispersing cougar were used in cooperation
with the Montana Department of Fish, Wildlife, and Parks to
see if cougars travel within the areas we identify as probable
movement corridors. This project was completed during the summer
of 1997. Early results are displayed on the CERI cougar
dispersal pages. Recent results and future GPS radiolocation
results will be displayed on our Dispersal
Study pages. |
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Beartooth
Game This area, in the Big Belt Mountains, is represented using Landsat MSS imagery overlaid with a USGS streams layer. Holter Lake is located on the left side of the image with the north end of Canyon Ferry Reservoir at the bottom of the image. Juvenile lions tagged with radios in this area are likely to disperse in almost any direction. The next step was to take a closer look at
the corridor areas identified using the Montana
Gap Analysis data to refine our corridor analysis. 2) neutral habitat 3) favorable habitat 4) preferred habitat This model is done on a large scale using
1-square kilometer pixels. It also incorporates Implicit in the model are:
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