A habitat-based framework for grizzly bear conservation in Alberta
SE Nielsen, GB Stenhouse, MS Boyce - Biological conservation, 2006 - Elsevier
SE Nielsen, GB Stenhouse, MS Boyce
Biological conservation, 2006•ElsevierGrizzly bear (Ursus arctos L.) populations in Alberta are threatened by habitat loss and high
rates of human-caused mortality. Spatial depictions of fitness would greatly improve
management and conservation action. We are currently challenged, however, in our ability
to parameterize demographic rates necessary for describing fitness, especially across
gradients of human disturbance and for land cover types. Alternative approaches are
therefore needed. We describe here a method of estimating relative habitat states and …
rates of human-caused mortality. Spatial depictions of fitness would greatly improve
management and conservation action. We are currently challenged, however, in our ability
to parameterize demographic rates necessary for describing fitness, especially across
gradients of human disturbance and for land cover types. Alternative approaches are
therefore needed. We describe here a method of estimating relative habitat states and …
Grizzly bear (Ursus arctos L.) populations in Alberta are threatened by habitat loss and high rates of human-caused mortality. Spatial depictions of fitness would greatly improve management and conservation action. We are currently challenged, however, in our ability to parameterize demographic rates necessary for describing fitness, especially across gradients of human disturbance and for land cover types. Alternative approaches are therefore needed. We describe here a method of estimating relative habitat states and conditions as surrogates of fitness using models of occupancy and mortality risk. By combining occurrence and risk models into a two-dimensional habitat framework, we identified indices of attractive sinks and safe harbour habitats, as well as five habitat states: non-critical habitats, secondary habitats (low-quality and secure), primary habitats (high-quality and secure), secondary sinks (low-quality, but high risk), and primary sinks (high-quality and high risk). Primary sink or high attractive sink situations were evident in the foothills where bears were using forest edges associated with forestry and oil and gas activities on Crown lands, while primary habitats or safe harbour sites were most common to protected alpine/sub-alpine sites. We suggest that habitat states and indices be used for setting baseline conditions for management and comparison of habitat conditions over time and identification of grizzly bear conservation reserves. A no net loss policy of critical habitats could be used to maintain existing habitat conditions for landscapes threatened by human development. Under such a policy, conversions of primary habitat would require restoration of equivalent amounts of primary sinks through decommissioning of roads.
Elsevier
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