Bears and
Cultural
Connections

Bears and Research
in the Canadian
Rockies

Bears and
Habitat

Bears and
Roads

Bears and
People

Bears and
Science

Bear Paw Print Human Impact Bear Paw Print
Bears and Habitat

Efforts to quantitatively and qualitatively assess the impact of human development and activities on bear habitat and habitat-use are a major focus of recent bear research in the Canadian Rockies – especially with respect to grizzly bears.  Significantly less information is available regarding human impacts on black bear habitat in the Canadian Rockies. Those studies that have been conducted tend to focus on specific features such as highways and railways. 


Measuring the cumulative effects of development on grizzly bears
The primary mandate of the Eastern Slopes Grizzly Bear Project (ESGBP) which began in 1994 is “to scientifically define the cumulative effects of development on the regional grizzly bear population.”15  The project focuses on grizzly bears in the Central Rockies Ecosystem which is one of the most highly developed landscapes in North America where grizzlies still survive. (Herrero and Gibeau 1999)

ESGBP researchers have incorporated the three following habitat components and associated models into their assessment of the cumulative effects of development on grizzly bears.

Once developed, these models can be used as predictive tools by changing or “manipulating” certain variables, and then seeing how the modeled results respond to those changes.


Habitat effectiveness
WHAT IS HABITAT EFFECTIVENESS MODELLING?
“Habitat effectiveness models an area’s actual ability to support bears given the quality of the habitat and the extent of human disturbance.” 16

Habitat effectiveness analysis involves constructing a spatial, Geographic Information System (GIS)-based model that generally consists of two major “map layers” or components:  

  • habitat potential layer (reflects the inherent ability of the landscape to support bears)
  • human disturbance layer (reflects the realized ability of the landscape to support grizzly bears after taking into account human disturbance)

By overlaying human disturbance onto habitat potential, the model produces Habitat Effectiveness  Values which “estimate the percentage of habitat that is available after subtracting habitat alienated as a result of human influence.” 17

HABITAT EFFECTIVENESS IN THE CENTRAL ROCKIES ECOSYSTEM
This analysis was applied in Banff, Yoho, and Kootenay National Parks, Kananaskis Country and at a more refined scale in the Lake Louise area of BNP.

  • the Mountain National Parks analysis suggests “widespread habitat alienation in what is supposed to be core refugia for grizzly bears, questioning the ability of the landscape to support a viable population.” 18
  • the Lake Louise analysis supports this statement as habitat effectiveness was determined to be “seriously compromised by human development” in 3 of the 4 Bear Management Units (BMUs) analysed. 19
  • Kananaskis Country results were also cause for concern; they demonstrated that there is “considerable stress” on grizzly bears using 5 of 13 BMUs. 20

Security (Core) Areas
WHAT IS SECURITY AREA MODELLING?
Security areas are “...areas where grizzly bears will be relatively secure from encounters with humans; where bears can meet their energetic requirements while at the same time choosing to avoid people.” 21
 
Security area analysis involves developing a spatial, Geographic Information System (GIS)-based model that generally consists of two “map layers” or components:

  • Suitable habitat layer:  a map identifying suitable foraging habitat patches of all sizes after accounting for landscape and human activity features. 
  • Minimum daily area requirement (m.d.a.r.):  the minimum average daily foraging radius for a female grizzly bear (based on empirical data from wary female grizzly bears)

Overlaying these two components enables researchers to eliminate from the suitable habitat layer all habitat patches which are too small to meet the m.d.a.r. The remaining number of patches and the size of them provide a concrete measure of the extent of habitat fragmentation, especially if the analysis is completed for historic, present and predicted future scenarios of human use.
(Gibeau et al 1996)

SECURTIY AREAS IN THE CENTRAL ROCKIES ECOSYSTEM
Security area analysis was conducted for the Central Rockies Ecosystem.

  • Kananaskis Country, which has an intensive recreation mandate, had the highest percentage (40%) of land not secure due to human use (40%).  It also had the greatest percentage (38%) of its land base within a zone of human influence (these are areas less than 500m from high human use features). (Gibeau 2000)
  • 42% of the National Parks landbase is inherently unsuitable for grizzly bears, contrasted with only 12% for Alberta multiple use lands. However, only 17% of National Parks land had high human influence, compared to 38% for Alberta multiple use lands. (Gibeau 2000)  
  • historic reconstruction of human-use circa 1950s and forecasting into the future circa 2050 (assuming status quo for human-use and no prescribed fire regime) shows a pattern of fragmentation and insularization of habitat within Banff and Kananaskis Country jurisdictions over time:
    — the average size of secure habitat patches in Banff National Park decreased from 218km2 in the 1950s to 56km2 currently to 43km2 around 2050.
    — increase in the number of patches from 13 to 39 to 39

A loss in the ability to foster wary behaviour in grizzly bears accompanies this pattern.
(Gibeau and Herrero 1998)

Linkage Zone Prediction Model
WHAT IS LINKAGE ZONE MODELLING?
Landscape linkages are “...usually understood as linear corridors of habitat that physically connect larger habitat patches in a landscape mosaic.” 22   Within the specific context of the linkage zone prediction model, the ‘landscape mosaic’ includes areas impacted by human activities, and may be defined as “combinations of landscape structural factors that allow wildlife to move through, and live in areas impacted by human actions.” 23
 
Linkage zone analysis involves developing a spatial, Geographic Information System (GIS)-based model that consists of four “map layers” or components:

  • human access route density: includes all roads, railways and high-use trails
  • density and nature of developed human sites: each site is assigned a corresponding zone of influence based on level of human use
  • presence or lack of hiding cover: determined from ecosite maps
  • within a riparian area: stream course and other areas that are expected to meet criteria for bear foods and movements, and for specific “wet-site” vegetation types

Overlaying these components generates a “combined danger score” (minimal, low, moderate and high – the higher the score, the greater the “danger” to bears) that is the result of both the level of human influence and the quality of habitat for bears in a given area. These scores are then used to “identify and quantify potential areas that can act as linkage zones between areas of habitat separated by humans.”
(Source for all:  Gibeau et al 1996)

LINKAGE ZONES IN BANFF NATIONAL PARK
Linkage zone analysis in Banff National Park and surrounds produced the following results:

  • east of the park, there are few potential opportunities for linkage zones
  • including the Trans-Canada Highway fencing and wildlife crossing structures in the analysis produces a dramatic decrease in potential crossing areas.
  • reconstruction of past human use levels (1950s) shows significantly fewer ‘moderate’ and ‘high’ danger scored values than at present, and linkage zones that are more extensive than at present.
    (Gibeau et al 1996)


Effects of industrial resource extraction on grizzly bears
Substantial effort has been directed towards assessing the effects of industrial resource extraction on grizzly bears. The Flathead Bear Study (Flathead River drainage, Southeast British Columbia), which began in the late 1970s and continues today, has conducted a considerable portion of this research. This section contains several highlights and conclusions from their many years of research. 

Potential effects of industry on grizzly bears

“Most grizzly bears (Ursus arctos) live outside parks and reserves and often have to contend with, among other things, resource extraction industries. These activities can affect individual bears and therefore populations by: 1) causing strong, energetically expensive reactions by bears that disrupt their normal behaviour, 2) displacing bears from areas of human use, 3) altering habitats in which bears live, 4) disrupting the bears’ social system, and 5) industrial personnel killing bears or increasing mortality rates indirectly by improving access for hunters, poacher, other resource users, and settlers.” 24
 

Access into bear habitat as a result of industrial activity

“In most cases, increased motorized access that results in a long term increase of human activity and/or settlement with consequent increase in bears being shot is the most significant aspect of industrial developments. If an industrial activity is connected with adequate guidelines to maintain important habitat, properly locate camps, incinerate garbage, restrict use of firearms, and close motorized access after the job is complete, the bear population probably will be maintained at a satisfactory level. Although many bears may be alive when an industry has completed its work, if access remains intact, the grizzly population is placed in a precarious position and may decrease in size and eventually be extirpated.” 25

Immediate responses to human activity and implications for industry
McLellan and Shackleton examined the immediate reactions of grizzly bears in the Flathead to a variety of human activities between 1979 and 1986. Bear responses were categorized according to several factors including:  distance moved from the disturbance, whether or not they moved into the nearest cover, the manner in which they moved off (slowly or quickly).

Some selected findings and the related implications for industry are:

  • bears respond differently to different human activities/stimuli based on their experience.
  • bears showed stronger responses in open areas than in cover, and cover was particularly important in reducing responses of grizzly bears to terrestrial human activities (e.g., person on foot, moving car).
    Implication:  high-human-use areas such as roads should be constructed away from open areas to reduce disturbance. Conversely, where strong reactions of bears to humans are desired, such as at industrial camps or settlements, removing cover by clearing adjacent timber may be beneficial.
  • the strongest reactions were to people on foot and reactions were stronger in areas of low human-use than in high human-use areas.
    Implication:  areas with known seasonal concentrations of bears could be closed to hikers to protect both bears and people
    (Source for all:  McLellan and Shackleton 1989)

    Footnotes and Sources Cited

Bears: Year 2000 and Beyond Bears: Imagination and Reality
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