Gibeau, M. and Herrero, S. 2002. Eastern Slopes Grizzly Bear Project:
A Progress Report for 2001 (ESGBP): April 2002. 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).
Year 8 - 2001
EASTERN SLOPES GRIZZLY BEAR PROJECT
A progress
report for 2001
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
ACKNOWLEDGMENTS
GOALS AND OBJECTIVES
STUDY AREA
METHODS
RESULTS
WEBSITE
POPULATION STUDIES
CAPTURE
TELEMETRY DATA SET
POPULATION DEMOGRAPHICS
LITERATURE CITED
LIST OF TABLES
Table 1. Grizzly bear capture data in the Bow River Watershed, Alberta, 2001
Table 2. Status of all grizzly bears captured in the Bow River Watershed, Alberta,
as of November 2001
Table 3. Unduplicated grizzly bear females with cubs of the year in the Bow River
Watershed, Alberta, 1993 - 2001
Table 4.
Number of unduplicated females with cubs of the year (COY), and 6 year
running averages in the Bow River Watershed, Alberta, 1993 - 2001
Table 5. Reproductive status of known female grizzly bears in the Bow River
Watershed, Alberta, 2001
Table 6. Summary of grizzly bear mortalities in the Bow River Watershed, Alberta,
1993 - 2001
Table 7. Summary of grizzly bear translocations in the Bow River Watershed,
Alberta, 1993 – 2001
Table 8.
Summary of known grizzly bear mortalities and removals by jurisdiction and
activity in the Bow River Watershed, Alberta, 1993-2001
ACKNOWLEDGMENTS
A very successful seventh field season would not have
been possible without the dedication of field biologists S. Ciancone, C. Hague, M. Koppang 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
C. Mamo, 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 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 2001 our research continued to focus 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.
Determine how the distribution of humans affects a bear's ability to use
the landscape.
Determine if population connectivity is being impeded by major
transportation corridors.
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 the Columbia Mountains 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
A concerted effort to deploy GPS radio collars in Canmore and the Lake Louise areas was the only
planned trapping in 2001. Three additional grizzly bears were
captured during management actions (Table 1).
Table 1. Grizzly bear
capture data in the Bow River Watershed, Alberta, 2001.
ID |
Sex |
Age Estimate |
Weight (kg) |
Area |
Comments |
45 |
M |
7a |
102 |
Lake
Louise |
recapture for GPS collar |
51 |
M |
12a |
155
est. |
Lake
Louise |
recapture |
56 |
F |
7a |
97 |
Lake
Louise |
recapture for GPS collar |
59 |
F |
7a |
84 |
Lake
Louise |
recapture for GPS collar |
68 |
M |
6a |
136 |
Canmore |
recapture for GPS collar |
70 |
F |
4a |
73 |
Canmore |
recapture for GPS collar |
71 |
F |
3 |
70 |
Banff |
management capture |
72 |
F |
8 |
90 |
Lake
Louise |
GPS
collar |
73 |
M |
3 |
95 |
Storm Mtn. |
management capture |
74 |
M |
subadult |
86 est. |
Spray Lakes |
|
* 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 2456 point locations for the 2001
field season. Of these 341 (14 %) were from the air and 2115 (86%)
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 65
individuals have been handled (Table 2). Of those, 17 have died, and
23 are currently radio collared. The sex/age breakdown of the
current radio collared sample is as follows:
14 adult females
5 adult males
2 subadult females
2 subadult male
Table 2. Status of all
grizzly bears captured in the Bow River Watershed, Alberta, as of November
2001.
|
ID |
Sex |
Age class 1 |
Age-first
capture 2 |
Monitoring Period
day/month/year |
Fate |
Cause 3 |
Recent sighting |
10 |
M |
AD |
13a |
07/05/94-12/06/96 and
19/04/97-10/06/98 |
lost |
drop collar |
|
11 |
M |
SA |
4b |
20/05/94 - 03/96 |
|
|
|
11 |
|
AD |
|
03/96 - 23/07/97 |
lost |
drop collar |
|
12 |
M |
AD |
13b |
19/05/94 - 05/10/94 |
dead |
self defense |
|
13 |
M |
SA |
5a |
20/05/94 - 03/95 |
|
|
|
13 |
|
AD |
|
03/95 - 31/10/01 |
active |
|
|
14 |
M |
AD |
9a |
19/05/95 - 24/10/96 |
lost |
no signal - b |
|
15 |
M |
AD |
6a |
20/05/94 - 31/10/01 |
active |
|
|
16 |
M |
SA |
5a |
16/08/93 - 03/94 |
|
|
|
16 |
|
AD |
|
03/94 - 05/07/96 |
dead |
removed to zoo |
|
17 |
F |
AD |
10a |
02/06/94 - 12/07/96 |
lost |
drop collar |
10/99 |
18 |
F |
AD |
6a |
30/05/94 - 31/10/01 |
active |
|
|
19 |
M |
AD |
6b |
13/05/94 - 14/05/94 |
dead |
accidental |
|
20 |
M |
AD |
11a |
14/05/94 - 07/07/94 |
lost |
drop collar |
|
21 |
M |
SA |
3a |
21/05/94 - 26/07/95 |
dead |
problem wildlife |
|
22 |
M |
AD |
14a |
21/05/94 - 28/05/94 |
dead |
legal hunting |
|
23 |
M |
SA |
3a |
28/05/94 - 08/08/96 |
dead |
problem wildlife |
|
24 |
F |
SA |
5a |
31/05/94 - 03/95 |
|
|
|
24 |
|
AD |
|
03/95 - 31/10/01 |
active |
|
|
25 |
M |
AD |
6a |
31/05/94 - 21/09/94 |
lost |
drop collar |
07/95 |
26 |
F |
AD |
18a |
08/06/94 - 21/09/99 |
dead |
self defense |
|
27 |
F |
SA |
2a |
13/06/94 - 15/09/95 |
lost |
no signal - b |
06/99 |
28 |
F |
AD |
22a |
08/06/94 - 09/08/96 |
dead |
natural |
|
29 |
M |
SA |
2a |
never collared |
|
|
|
30 |
F |
AD |
9a |
28/09/94 - 31/10/01 |
active |
|
|
31 |
F |
AD |
7c |
25/06/94 - 27/04/96 |
lost |
drop collar |
|
32 |
F |
AD |
13b |
04/06/94 - 18/10/97 |
lost |
drop collar |
|
|
ID |
Sex |
Age class 1 |
Age-first
capture 2 |
Monitoring Period
day/month/year |
Fate |
Cause 3 |
Recent sighting |
33 |
F |
AD |
19a |
14/06/94 - 22/09/99 and 03/08/00 -
31/10/01 |
active |
|
|
34 |
M |
AD |
6a |
17/05/95 - 05/11/96 |
lost |
no signal - b |
|
35 |
F |
SA |
4a |
17/05/96 - 20/09/97 |
dead |
treaty Indian |
|
36 |
F |
AD |
8a |
23/07/93 - 31/10/01 |
active |
|
|
37 |
F |
AD |
10a |
27/06/94 - 31/10/01 |
active |
|
|
38 |
M |
D |
1a |
never collared |
|
|
|
39 |
F |
SA |
3a |
10/05/95 - 18/08/96 |
lost |
no signal - b |
|
40 |
F |
AD |
15c |
15/05/95 - 03/06/00 |
dead |
natural |
|
41 |
F |
AD |
12a |
28/05/95 - 09/05/01 |
lost |
no signal - b |
|
42 |
M |
AD |
7a |
30/05/95 - 06/10/00 |
lost |
no signal - b |
10/01 |
43 |
M |
SA |
5a |
24/05/96 - 05/10/96 |
dead |
illegal |
|
44 |
M |
SA |
4a |
13/06/95 - 23/08/96 |
dead |
treaty Indian |
|
45 |
M |
D |
4a |
19/05/98 - 22/06/99 |
lost |
drop collar |
|
45 |
|
AD |
|
03/06/00 - 31/10/01 |
active |
|
|
46 |
F |
AD |
11a |
15/06/95 - 31/10/01 |
active |
|
|
47 |
F |
AD |
9a |
02/06/96 - 31/10/01 |
active |
|
|
48 |
F |
D |
2a |
02/06/96 - 06/97 |
|
|
|
48 |
|
SA |
|
06/97 - 10/09/97 |
lost |
no signal - c |
|
49 |
M |
D |
2a |
02/06/96 - 06/97 |
|
|
|
49 |
|
SA |
|
06/97 - 29/05/98 |
lost |
no signal - b |
08/01 |
50 |
M |
SA |
4a |
17/06/96 - 20/06/96 |
lost |
no signal - a |
|
51 |
M |
AD |
8a |
23/05/97 - 10/06/98 and 25/06/01 -
31/10/01 |
active |
|
|
52 |
M |
AD |
7b |
16/05/97 - 31/10/01 |
active |
|
|
53 |
M |
SA |
3a |
15/05/97 - 20/10/98 |
dead |
illegal |
|
54 |
M |
AD |
15a |
03/06/97 - 10/10/99 |
lost |
no signal -c |
|
55 |
F |
AD |
6a |
07/06/97 - 10/09/99 |
lost |
drop collar |
10/99 |
56 |
F |
D |
3a |
26/05/97 - 06/98 |
|
|
|
56 |
|
SA |
|
06/98 - 03/00 |
|
|
|
56 |
|
AD |
|
03/00 - 30/09/01 |
dead |
accidental |
|
57 |
F |
SA |
5a |
17/05/97 - 03/98 |
|
|
|
57 |
|
AD |
|
03/98 - 31/10/01 |
active |
|
|
58 |
M |
AD |
9a |
08/06/97 - 23/09/97 |
dead |
problem wildlife |
|
59 |
F |
D |
3a |
26/05/97 - 06/98 |
|
|
|
59 |
|
SA |
|
06/98 - 03/00 |
|
|
|
59 |
|
AD |
|
03/00 - 31/10/01 |
active |
|
|
60 |
F |
D |
3a |
26/05/97 - 06/98 |
|
|
|
60 |
|
SA |
|
06/98 - 03/00 |
|
|
|
60 |
|
AD |
|
03/00 - 17/08/00 |
dead |
accidental |
|
61 |
F |
AD |
12a |
11/06/97 - 20/08/99 |
lost |
no signal -c or a |
|
62 |
F |
AD |
8a |
12/06/97 - 29/06/01 |
lost |
no signal - b |
|
63 |
F |
AD |
7a |
08/06/99 - 31/10/01 |
active |
|
|
64 |
F |
AD |
10a |
03/06/99 - 31/10/01 |
active |
|
|
65 |
F |
D |
4a |
15/05/98 - 06/99 |
|
|
|
65 |
|
SA |
|
06/99 - 03/00 |
|
|
|
65 |
|
AD |
|
03/00 - 06/08/00 |
lost |
drop collar |
|
|
ID |
Sex |
Age class 1 |
Age-first
capture 2 |
Monitoring Period
day/month/year |
Fate |
Cause 3 |
Recent sighting |
66 |
F |
SA |
4a |
13/06/99 - 03/01 |
|
|
|
66 |
|
AD |
|
03/01- 31/10/01 |
active |
|
|
67 |
M |
SA |
3a |
13/06/99 - 10/10/99 |
dead |
accidental |
06/00 |
68 |
M |
SA |
5a |
03/08/00 - 03/01 |
|
|
|
68 |
|
AD |
|
03/01 - 02/08/01 |
lost |
removed - b |
|
69 |
F |
SA |
3a |
14/09/00 - 06/08/01 |
lost |
removed - b |
|
70 |
F |
SA |
3a |
14/09/00 - 31/10/01 |
active |
|
|
71 |
F |
SA |
3a |
19/07/01 - 31/10/01 |
active |
|
|
72 |
F |
AD |
8a |
18/06/01 - 31/10/01 |
active |
|
|
73 |
M |
SA |
3a |
09/09/01 - 31/10/01 |
active |
|
|
74 |
M |
SA |
n/a |
07/09/01 - 31/10/01 |
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
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 - 2001.
|
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 |
Family
Identification |
Most Cubs Observed |
Location |
# of
Sightings |
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 |
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
|
Simpson
River |
4 |
Bear #
47 1998 |
2
|
Kananaskis Lakes |
3 |
Bear #
55 1998 |
1
|
Cascade
River |
9 |
Bear #
57 1998 |
2
|
Plateau Mtn |
6 |
Bear #
18 1999 |
1
|
Bryant
Creek |
4 |
Bear #
26 1999 |
2
|
Nakiska |
1 |
Bear #
36 1999 |
2
|
Upper
Bow River |
5 |
Bear #
56 2000 |
1
|
Lake
Louise |
10 |
Bear #
37 2000 |
2
|
Elbow
River |
3 |
A -
2000 |
2
|
Elpoca Cr. |
2 |
Bear #
30 2001 |
3
|
Lake
Louise |
4 |
Bear #
47 2001 |
2
|
Kananaskis Lakes |
5 |
Bear #
56 2001 |
2
|
Lake
Louise |
85 |
Bear #
57 2001 |
2
|
Plateau Mtn |
4 |
Bear #
62 2001 |
2
|
Cascade
River |
2 |
Family
Identification |
Most Cubs Observed
|
Location |
# of
Sightings |
Bear #
66 2001 |
2
|
Bow
River |
3 |
A -
2001 |
2
|
Lake
Louise |
2 |
B - 2001 |
3 |
Cascade River |
2 |
Table 4. Number of unduplicated females with cubs of the year
(COY), and 6 year running averages in the Bow River Watershed, Alberta,
1993 - 2001.
Year |
Females
w/COY |
Total
# COY |
Mean
litter
size |
6 year running averages |
F w/COY |
# cubs |
Litter size |
1993 |
6 |
11 |
1.8 |
|
|
|
1994 |
9 |
15 |
1.6 |
|
|
|
1995 |
9 |
20 |
2.2 |
|
|
|
1996 |
5 |
10 |
2.0 |
|
|
|
1997 |
2 |
5 |
2.5 |
|
|
|
1998 |
8 |
12 |
1.5 |
6.5 |
12.2 |
1.9 |
1999 |
3 |
5 |
1.6 |
6.0 |
11.2 |
1.9 |
2000 |
3 |
5 |
1.6 |
5.0 |
9.5 |
1.9 |
2001 |
8 |
18 |
2.2 |
4.8 |
9.2 |
1.9 |
Reproductive success of radio collared females was
determined through year to year visual observations between 1994 and 2001
(Table 5). Year to year cub survivorship can be tracked by referring
to the table and comparing the number of cubs observed in a given year to
the previous years observations.
Reproductive data from collared females is being be used to construct an
estimate of whether the sample population is increasing or decreasing.
Table 5. Reproductive status of known female grizzly bears in
the Bow River Watershed, Alberta, 2001.
Female |
Location |
Age at first |
|
|
|
Cubs In |
|
|
|
|
|
# |
|
capture |
94 |
95 |
96 |
97 |
98 |
99 |
2000 |
2001 |
|
17 |
Cascade River |
10 |
0 |
1yoy |
1 |
off air |
2yoy |
2 |
|
|
|
18 |
Bryant Creek |
6 |
0 |
3yoy |
2 |
2 |
2* |
1yoy |
1 |
1 |
|
24 |
Highwood Pass |
5 |
0 |
0 |
2yoy |
2 |
2* |
0 |
0 |
0 |
|
26 |
Nakisa |
18 |
2* |
2yoy |
1 |
0 |
0 |
2yoy/died |
0 |
|
|
27 |
Cascade River |
2 |
| |