Gibeau, M. and Herrero, S. 2001. Eastern Slopes Grizzly Bear Project:
A
Progress Report for 2000 (ESGBP): April 2001. Eastern Slopes Grizzly
Bear Project, University of Calgary, Calgary, AB.
Note: You can also download a PDF version of this report.
NEW FEATURE: Table of Contents links and Table links are activated
in this file (HTML format).
EASTERN SLOPES
GRIZZLY BEAR PROJECT:
A progress report for 2000
Prepared for the Eastern Slopes Grizzly Bear Steering
Committee
This paper contains preliminary results of an
on-going study and should not be cited
without permission from the authors.
TABLE OF CONTENTS
LIST OF TABLES
Table 1. Grizzly bear capture data
in the Bow River Watershed, Alberta, 2000
Table 2. Status of all grizzly bears captured in
the Bow River Watershed, Alberta, as of November 2000
Table 3. Unduplicated grizzly bear females with
cubs of the year in the Bow River Watershed, Alberta, 1993 - 2000
Table 4. Number of unduplicated females with
cubs of the year (COY), and 6 year running averages in the Bow River
Watershed, Alberta, 1993 - 2000
Table 5. Reproductive status of known female
grizzly bears in the Bow River Watershed, Alberta, 2000
Table 6. Summary of grizzly bear mortalities in
the Bow River Watershed, Alberta, 1993 - 2000. 9
Table 7. Summary of grizzly bear translocations
in the Bow River Watershed, Alberta, 1993 - 2000
Table 8. Summary of known grizzly bear
mortalities and removals by jurisdiction and activity in the Bow River
Watershed, Alberta, 1993-2000
ACKNOWLEDGMENTS
A very successful seventh field season would not have been possible
without the dedication of field biologists C. Hague, B. McClarty and S.
Stevens. Their efforts were augmented through the largely volunteer
support of C. Campbell. Assistance in coordination of field staff was
provided by A. Dibb, S. Donelon and T. Hurd. Trapping was conducted by the
Banff National Park Warden Service and Alberta Natural Resources Service.
Veterinary care was provided by Dr. Todd Shury. Several Alberta
Conservation Officers and Banff National Park Wardens provided invaluable
safety backup, field assistance and logistical support through all stages
of monitoring. Exemplary flying skills were provided by Alpine Helicopters
of Canmore and fixed wing pilot M. Dupuis and T. Kulbida of Wildlife
Observation Air Services.
The Eastern Slopes Grizzly Bear Steering Committee helped implement and
guided this research. All steering committee participants contribute
either money, time or both toward the objectives. Through the Steering
Committee, governments, industry, business and conservation groups work
together to support this project. The supporters include:
Alberta Environment
Natural Resources Service (NRS)
Lands & Forest Service
Alberta Cattle Commission
Alberta Conservation Association
Alberta Energy Utilities Board Committee (EUB)
Alberta Off-Highway Vehicle Association
Alberta Sport, Recreation, Parks, and Wildlife Foundation
Alpine Helicopters
AMOCO Canada Petroleum Co. Ltd.
Anonymous Foundation donor
Bow Valley Naturalists
British Columbia Ministry of Environment
Wildlife Division
Calgary Area Outdoor Council (CAOC)
Calgary Zoo
Canadian Association of Petroleum Producers (CAPP)
Canadian Pacific Charitable Foundation
Canadian Parks and Wilderness Society (CPAWS)Calgary/Banff Chapter
Canmore Collegiate High School
Crown of the Continent Electronic Data Atlas
Eagle Terrace Developments
Elbow Valley Campgrounds
Friends of Banff
Friends of Kananaskis Country
|
Foothills Model Forest
Grizzly Bear Project
Human Resources Development Canada
Husky Oil
Miistakis Institute
Mistaya Communications
Mountain Electronics
Mountain Equipment Co-op
National Science and Engineering Research Council
(NSERC)
Parks Canada
Resorts of the Canadian Rockies
Rigel Energy
Shell Canada LimitedSpray Lakes Sawmills (1980) Ltd.
Springbank Middle School
Switching Gear
Totem Outdoor Outfitters
Three Sisters Resorts
University of Alberta
University of Calgary
Faculty of Environmental Design
Resources & the Environment Program
Warner Guiding and Outfitting Ltd.
Wilburforce Foundation
Wilderness Medical Society
World Wildlife Fund Canada (WWF) |
GOALS AND OBJECTIVES
During 2000 our research focused on gathering basic reproductive and
mortality data for analysis of demographic parameters. Another important
research question we focused on is how do grizzly bear's spatial and
temporal use patterns differ in areas of high human presence compared to
areas with low human presence in a landscape, some of which is dominated
by tourism activities? Our situation is unique in that no other grizzly
bear study area in North America has both a high volume transcontentinal
highway and railway dissecting occupied grizzly bear habitat along with
intensive tourism. Analysis has never been done on the effects of such
levels of human presence on grizzly bears. One important question is the
extent to which the Bow River Valley continues to function as a major
movement corridor for bears providing connectivity between habitats.
The overall goal of ESGBP research is to understand how developments
and human-induced mortality impact grizzly bears. Specific research
objectives include:
1. Determine the basic demographic parameters for the grizzly bear
population within the study area.
2. Detect spatial and temporal activity patterns of bears given various
levels of human influences.
3. Determine how the distribution of humans affects a bear's ability to
use the landscape.
4. Determine if population connectivity is being impeded by major
transportation corridors.
5. Determine what adjustments to human activities would give bears
better access to resources.
6. Suggest management alternatives for integrating land uses compatible
with bear habitat and survival needs for the study area.
STUDY AREA
The area of interest remains unchanged from year 1 with the
approximately 11,400 km2 Bow River Watershed, from its
headwaters to approximately where it meets the prairies, as the core study
area. The greater study area defined by the movement of radio-collared
bears is about 22,000 km2 or roughly twice the size of the core
study area. At the largest scale our research encompasses the 42,000 km2 Central Rockies Ecosystem (Komex International 1995).
METHODS
Methods for both the capture and monitoring of bears remain unchanged
from the detailed description found in the year 1 progress report (Gibeau
and Herrero 1995). Approximately 25 grizzly bears per year have active
radio-collars. These bears are monitored from air and ground wherever they
go and our budget permits. Aerial monitoring gives infrequent, but
relatively unbiased data regarding location. This facilitates
understanding of home range, movements and habitat use. Ground-based
research allows intensive monitoring of grizzly bear activities related to
development features such as towns, highways, campgrounds and trails.
Mortality is monitored using both aerial and ground-based telemetry. The
radio-telemetry monitoring area includes lands under several different
jurisdictions. In the British Columbia portion of these lands, where some
of our radio-collared grizzly bears are found, there is a Western Slopes
Bear Research Project which provides complementary data and will allow a
broader ecosystem versus provincial boundary-based understanding of
grizzly bears in the Central Rockies Ecosystem.
RESULTS
WEBSITE
Most of the ESGBP publications plus
considerable other related material can be found on this, the ESGBP website, and is available for
downloading. Go to the Research Publications Section.
POPULATION
STUDIES
CAPTURE
There was no planned trapping effort in 2000 although 4 grizzly bears
were captured during management actions (Table 1).
Table 1. Grizzly bear capture data in the Bow
River Watershed, Alberta, 2000.
ID |
Sex |
Age Estimate |
Weight (kg) |
Area |
Comments |
33 |
F |
25a* |
n/a |
Two Jack |
recapture |
68 |
M |
5a |
n/a |
Two Jack |
|
69 |
F |
3a |
93 |
Nakiska |
|
70 |
F |
3a |
79 |
Nakiska |
|
* certainty code a= +/- 0 years, b= +/- 1-2 years, c= +/- 2-3 years
TELEMETRY DATA SET
Aerial and ground monitoring from early April until the first week of
November produced 1641 point locations for the 2000 field season. Of these
439 (27 %) were from the air and 1202 (73%) from ground monitoring. Aerial
locations were biased toward early morning hours. Ground locations were
biased towards where observers could travel easily.
Since the project began in May 1994 a total of 61 individuals have been
handled (Table 2). Of those, 15 have died, and 24 are currently radio
collared. The sex/age breakdown of the current radio collared sample is as
follows:
15 adult females 5 adult males
3 subadult females 1 subadult male
Table 2. Status of all grizzly bears captured in
the Bow River Watershed, Alberta, as of November 2000.
|
ID
|
Sex
|
Age class 1
|
Age at first
capture 2
|
Months monitored
|
Fate
|
Cause 3
|
Most recent sighting 4
|
|
10
|
M
|
AD
|
13a
|
07/94 - 06/96 and 04/97 - 06/98
|
lost
|
drop collar
|
|
|
11
|
M
|
SA
|
4b
|
05/94 - 03/96
|
|
|
|
|
11
|
|
AD
|
|
03/96 - 07/97
|
lost
|
drop collar
|
|
|
12
|
M
|
AD
|
13b
|
05/94 - 10/94
|
dead
|
self defense
|
|
|
13
|
M
|
SA
|
5a
|
05/94 - 03/95
|
|
|
|
|
13
|
|
AD
|
|
03/95 - 10/00
|
active
|
|
|
|
14
|
M
|
AD
|
9a
|
05/95 - 05/97
|
lost
|
no signal - b
|
|
|
15
|
M
|
AD
|
6a
|
05/94 - 10/00
|
active
|
|
|
|
16
|
M
|
SA
|
5a
|
08/93 - 03/94
|
|
|
|
|
16
|
|
AD
|
|
03/94 - 07/96
|
dead
|
removed to zoo
|
|
|
17
|
F
|
AD
|
10a
|
06/94 - 07/96
|
lost
|
drop collar
|
10/99
|
|
18
|
F
|
AD
|
6a
|
05/94 - 10/00
|
active
|
|
|
|
19
|
M
|
AD
|
6b
|
05/94 - 05/94
|
dead
|
accidental
|
|
|
20
|
M
|
AD
|
11a
|
05/94 - 07/94
|
lost
|
drop collar
|
|
|
21
|
M
|
SA
|
3a
|
05/94 - 07/95
|
dead
|
problem wildlife
|
|
|
22
|
M
|
AD
|
14a
|
05/94 - 05/94
|
dead
|
legal hunting
|
|
|
23
|
M
|
SA
|
3a
|
05/94 - 08/96
|
dead
|
problem wildlife
|
|
|
24
|
F
|
SA
|
5a
|
05/94 - 03/95
|
|
|
|
|
24
|
|
AD
|
|
03/95 - 10/00
|
active
|
|
|
|
25
|
M
|
AD
|
6a
|
05/94 - 09/94
|
lost
|
drop collar
|
07/95
|
|
26
|
F
|
AD
|
18a
|
06/94 - 09/99
|
dead
|
self defense
|
|
|
27
|
F
|
SA
|
2a
|
06/94 - 09/95
|
lost
|
no signal - b
|
06/99
|
|
28
|
F
|
AD
|
22a
|
06/94 - 08/96
|
dead
|
natural
|
|
|
29
|
M
|
SA
|
2a
|
never collared
|
|
|
|
|
30
|
F
|
AD
|
9a
|
09/94 - 10/00
|
active
|
|
|
|
31
|
F
|
AD
|
7c
|
06/94 - 04/96
|
lost
|
drop collar
|
|
|
32
|
F
|
AD
|
13b
|
06/94 - 10/97
|
lost
|
drop collar
|
|
|
33
|
F
|
AD
|
19a
|
06/94 - 09/99 and 08/00 - 10/00
|
active
|
|
|
|
34
|
M
|
AD
|
6a
|
05/95 - 11/96
|
lost
|
no signal - b
|
|
|
35
|
F
|
SA
|
4a
|
05/96 - 09/97
|
dead
|
treaty Indian
|
|
|
36
|
F
|
AD
|
8a
|
06/93 - 10/00
|
active
|
|
|
|
37
|
F
|
AD
|
10a
|
06/94 - 10/00
|
active
|
|
|
|
38
|
M
|
D
|
1a
|
never collared
|
|
|
|
|
39
|
F
|
SA
|
3a
|
05/95 - 08/96
|
lost
|
no signal - b
|
|
|
40
|
F
|
AD
|
15c
|
05/95 - 06/00
|
dead
|
natural
|
|
|
41
|
F
|
AD
|
12a
|
05/95 - 10/00
|
active
|
|
|
|
42
|
M
|
AD
|
7a
|
05/95 - 10/00
|
active
|
|
|
|
43
|
M
|
SA
|
5a
|
05/96 - 10/96
|
dead
|
illegal
|
|
|
44
|
M
|
SA
|
4a
|
06/95 - 08/96
|
dead
|
treaty Indian
|
|
|
ID
|
Sex
|
Age class 1
|
Age at first
capture 2
|
Months monitored
|
Fate
|
Cause 3
|
Most recent sighting 4
|
|
45
|
|
AD
|
|
06/00 - 10/00
|
active
|
|
|
|
46
|
F
|
AD
|
11a
|
06/95 - 10/00
|
active
|
|
|
|
47
|
F
|
AD
|
9a
|
06/96 - 10/00
|
active
|
|
|
|
48
|
F
|
D
|
2a
|
06/96 - 06/97
|
|
|
|
|
48
|
|
SA
|
|
06/97 - 09/97
|
lost
|
no signal - c
|
|
|
49
|
M
|
D
|
2a
|
06/96 - 06/97
|
|
|
|
|
49
|
|
SA
|
|
06/97 - 06/98
|
lost
|
no signal - b
|
10/99
|
|
50
|
M
|
SA
|
4a
|
06/96 - 06/96
|
lost
|
no signal - a
|
|
|
51
|
M
|
AD
|
8a
|
05/97 - 06/98
|
lost
|
drop collar
|
|
|
52
|
M
|
AD
|
7b
|
05/97 - 10/00
|
active
|
|
|
|
53
|
M
|
SA
|
3a
|
05/97 - 10/98
|
dead
|
illegal
|
|
|
54
|
M
|
AD
|
15a
|
06/97 - 10/99
|
lost
|
no signal -c
|
|
|
55
|
F
|
AD
|
6a
|
06/97 - 09/99
|
lost
|
drop collar
|
10/99
|
|
56
|
F
|
D
|
3a
|
05/97 - 06/98
|
|
|
|
|
56
|
|
SA
|
|
06/98 - 03/00
|
|
|
|
|
56
|
|
AD
|
|
03/00 - 10/00
|
active
|
|
|
|
57
|
F
|
SA
|
5a
|
05/97 - 03/98
|
|
|
|
|
57
|
|
AD
|
|
03/98 - 10/00
|
active
|
|
|
|
58
|
M
|
AD
|
9a
|
06/97 - 09/97
|
dead
|
problem wildlife
|
|
|
59
|
F
|
D
|
3a
|
05/97 - 06/98
|
|
|
|
|
59
|
|
SA
|
|
06/98 - 03/00
|
|
|
|
|
59
|
|
AD
|
|
03/00 - 10/00
|
active
|
|
|
|
60
|
F
|
D
|
3a
|
05/97 - 06/98
|
|
|
|
|
60
|
|
SA
|
|
06/98 - 03/00
|
|
|
|
|
60
|
|
AD
|
|
03/00 - 08/00
|
dead
|
accidental
|
|
|
61
|
F
|
AD
|
12a
|
06/97 - 08/99
|
lost
|
no signal -c or a
|
|
|
62
|
F
|
AD
|
8a
|
06/97 - 10/00
|
active
|
|
|
|
63
|
F
|
AD
|
7a
|
06/99 - 10/00
|
active
|
|
|
|
64
|
F
|
AD
|
10a
|
06/99 - 10/00
|
active
|
|
|
|
65
|
F
|
D
|
4a
|
05/98 - 06/99
|
|
|
|
|
65
|
|
SA
|
|
06/99 - 03/00
|
|
|
|
|
65
|
|
AD
|
|
03/00 - 08/00
|
lost
|
drop collar
|
|
|
66
|
F
|
SA
|
4a
|
06/99 - 10/00
|
active
|
|
|
|
67
|
M
|
SA
|
3a
|
06/99 - 10/99
|
lost
|
no signal - b
|
06/00
|
|
68
|
M
|
SA
|
5a
|
08/00 - 10/00
|
active
|
|
|
|
69
|
F
|
SA
|
3a
|
09/00 - 10/00
|
active
|
|
|
|
70
|
F
|
SA
|
3a
|
09/00 - 10/00
|
active
|
|
|
1 D = dependent, SA = subadult, AD = adult (>5 years old)
2 certainty code from tooth analysis: a = +/- 0 years, b = +/-
1-2 years, c = +/- 2-3 years
3 (a) High probability that disappearance was related to death,
(b) High probability that disappearance was unrelated to death, (c) No
indication of which of the above 2 choices is more likely
4 sightings of animals who’s collar has either failed or
dropped off
POPULATION
DEMOGRAPHICS
Observations from the research team as well as records from Banff
National Park and Alberta Natural Resources Service established a minimum
unduplicated count of females with cubs for the year (Table 3). Over time,
a minimum count of sows with cubs (Table 4) can be established and used as
a trend indicator (Knight et al. 1995).
Table 3. Unduplicated grizzly bear females with
cubs of the year in the Bow River Watershed, Alberta, 1993 - 2000.
Family
Identification |
Most Cubs Observed |
Location |
# of
Sightings |
A - 1993 |
1 |
Bryant Creek |
2 |
B - 1993 |
2 |
Fatigue Creek |
1 |
C - 1993 |
2 |
Moraine Lake |
1 |
D - 1993 |
2 |
Cascade River |
1 |
E - 1993 |
2 |
Elbow R. / Nahahi Ridge |
3 |
F - 1993 |
2 |
Kananaskis Lakes |
4 |
A - 1994 |
2 |
Lower Cascade River |
1 |
B - 1994 |
1 |
Moose Mtn. / Elbow R. |
2 |
C - 1994 |
2 |
Mt. Indefatigable |
4 |
D - 1994 |
1 |
Bryant Cr. / Mt. Nestor |
2 |
Bear #28 1994 |
1 |
Upper Cascade River |
2 |
Bear #30 1994 |
3 |
Baker Lake / Pipestone R. |
5 |
Bear #36 1994 |
1 |
Upper Bow River |
2 |
Bear #46 1994 |
2 |
Pipestone River |
1 |
Bear #47 1994 |
2 |
Kananaskis Lakes |
2 |
A - 1995 |
2 |
West Bragg Cr / Powderface |
3 |
B - 1995 |
2 |
Skogan Pass / Wasootch |
3 |
C - 1995 |
2 |
Upper Spray / Albert R. |
3 |
Bear #17 1995 |
1 |
Cascade River |
13 |
Bear #18 1995 |
3 |
Bryant Cr. / Assiniboine |
10 |
Bear #26 1995 |
2 |
Nakiska / Evans Thomas |
6 |
Bear #31 1995 |
2 |
Highwood River |
3 |
Bear #32 1995 |
3 |
Forty Mile Cr. / Elk Lake |
12 |
Bear #33 1995 |
3 |
Cascade River / Stoney Cr. |
14 |
A - 1996 |
1 |
Cascade R. / Grassy Ridge |
1 |
B - 1996 |
3 |
Mid Spray River |
1 |
Bear #24 1996 |
2 |
Highwood Pass |
25 |
Bear #36 1996 |
2 |
Upper Bow River |
8 |
Bear #37 1996 |
2 |
Elbow / Sheep Rivers |
3 |
A - 1997 |
2 |
Wind Valley |
2 |
B - 1997 |
3 |
Elbow Lakes |
2 |
Family
Identification |
Most Cubs Observed |
Location |
# of
Sightings |
A - 1998 |
1 |
West Bragg Creek |
2 |
B - 1998 |
2 |
Palliser Range |
2 |
C - 1998 |
1 |
Pipestone River |
1 |
Bear # 33 1998 |
2 |
Cascade River |
4 |
Bear # 41 1998 |
1 |
| |