Wolverine Ecology and Habitat Use
in the
North Columbia Mountains, B.C.
Progress Report 1998:
Krebs, John A. and D. Lewis, Columbia
Basin Fish & Wildlife Compensation Program, 103-333 Victoria St. Nelson,
B.C. V1L 4K3. (250) 352-6874
Email: john.krebs@bchydro.bc.ca
We are currently completing a five-year project investigating demography and
habitat use of a harvested population of wolverine in a 7000 kmē area within
the Kootenay Region of British Columbia. The study area contains 10 registered
traplines, two National Parks, a major transportation corridor, two
hydroelectric reservoirs, active logging areas and supports a substantial
helicopter skiing industry. Wolverine are considered "vulnerable" by the BC
Wildlife Branch and consequently vital rate data are important for evaluating
management/conservation options.
A total of 39 (14F, 25M) adult and subadult wolverine have been captured over
3700 trap-nights using log box traps baited with available road-killed
wildlife. Capture success varied by month and year with best results in
February and March. Population estimates for the study area based on 4 years of
live trapping data are 25.6 (95% CI: 15.6-55.3) and 24.0 (95% CI: 14.7-44.3)
for 1996 and 1997 respectively. Five of the eight mortalities detected during
the study to date have been human caused (3 commercially trapped, 1 highway
kill, 1 railway kill). Annual survival rate was estimated to be 0.79 (95% CI:
0.65 - 0.92) for all age and sex categories combined.
Reproductive data are being gathered through radio-telemetry and follow-up
ground investigations of breeding females after den abandonment, as well as
from trapper-killed carcass submissions. In 1998, only one of the 10
radiocollared females produced young (litter of 2) that survived post den
emergence. Two juvenile males (5.4, 5.8 kg) were captured and implanted with
radio transmitters in June 1998 while accompanying their radio-collared mother.
Ground investigation of the natal densite confirmed it to be in the ESSF
biogeoclimatic zone similar to previous dens; associated with large boulder
talus and woody debris. Thus far breeding females have been found only in
roadless, undeveloped drainages.
Habitat use data (>1200 locations) are being collected through bi-weekly
telemetry flights and snow trailing during winter. Home ranges of males (x =
1005 kmē) were significantly larger than females (x = 300 kmē) and National
Park resident males (x = 543 kmē) had smaller home ranges than non-park males
(x = 1203 kmē). Female home ranges did not differ significantly. At the study
area scale, the distribution of wolverine use is highly clumped in four
distinct utilization peaks. The two largest utilization peaks occur within
Glacier and Mt. Revelstoke National Parks; disproportionate to their land base
within the study area. The remaining peaks are found in the upper Bigmouth -
Windy Creek area and between Downie and Goldstream. Male wolverine appear to be
able to cross large reservoirs and at times, highways during lengthy dispersal
movements (up to 200 km from point of capture). To our knowledge, no
radio-collared females have crossed either reservoir, and only 1 female has
crossed the Trans Canada highway.
The focus for the remainder of the project is on the monitoring of existing
females and kits, identification and characterisation of natal dens in spring
1999 and increasing the amount of snow trailing data. A population census using
motion sensitive cameras will be conducted March - April 1999. Final reports
will be prepared over the next 24 months.
View a
map of the study area
that includes wolverine locations and polygons outlining the utilization peaks
mentioned above. The
peaks
are contours produced by a computer program (ADK or Adaptive Kernel function)
that outlines an animal's home range. These contours, or peaks, define regions
of varying wolverine density, or intensity of use, based on the distribution of
relocation points.
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