Skip to main content
. 2014 Oct 3;2(1):cou043. doi: 10.1093/conphys/cou043

Table 1:

The biological, anthropogenic and habitat-related covariates considered to explain body condition of grizzly bears in Alberta, Canada

Covariate Rationale References Data source
Reproductive class Based on gender, age and presence of cub(s)-of-year, which influence habitat selection patterns and energetic demands, individuals were classified as adult males or females (>5 years old), juvenile males or females (2–5 years old) or adult females with cub(s)-of-year Boulanger et al. (2013) Nielsen et al. (2013a) Grizzly bear capture data
Number of previous captures Multiple handlings may adversely influence body condition Cattet et al. (2008)
Capture date (Julian date) Seasonal changes in food availability and habitat selection during the non-denning period may influence body condition McLellan (2011)
Index of habitat net-energy demand Factors related to anthropogenic disturbance and habitat characteristics influence predicted hair cortisol concentrations in grizzly bears. Predicted hair cortisol concentration values are interpreted as a sex-specific indicator of net-energy demand Macbeth et al. (2010) Bourbonnais et al. (2013) Bryan et al. (2013) Bourbonnais et al. (2013)
Roads (distance decay) Provide human access to grizzly bear habitat; contribute to landscape fragmentation; herbaceous foods are present in areas adjacent to roads Munro et al. (2006) Berland et al. (2008) Roever et al. (2008) Graham et al. (2010) AESRD; FRIGBP; Landsat 5 TM; Landsat 7 ETM + 
Oil and gas well sites (distance decay) Localized areas of human activity; create forest edges and contribute to landscape fragmentation Laberee et al. (2014)
Density of secondary linear features (km/km2) Seismic lines, power lines and pipelines create forest edges and contribute to landscape fragmentation and provide access to grizzly bear habitat Linke et al. (2005) Stewart et al. (2013)
Density of forest harvest blocks (km/km2) Disturbance features associated with presence and abundance of herbaceous foods Nielsen et al. (2004a, c) Munro et al. (2006) Berland et al. (2008)
Percentage of parks and protected areas Considered core refugia and represent a marked contrast in land use compared with the surrounding industrialized landscape Gibeau et al. (2002)
Elevation (variation) Influences vegetation composition, human access and potential habitat net-energy demand Nielsen et al. (2004b, c) Bourbonnais et al. (2013) Landsat 5 TM; Landsat 7 ETM+; DEM
Crown closure (variation) Influences understory vegetation abundance and growth of herbaceous foods Franklin et al. (2002, 2003) Nielsen et al. (2013a)
Percentage of conifer tree cover Characterization of forest species distribution and correlated with berry abundance Franklin et al. (2002, 2003)
Percentage of mixed and broadleaf tree cover Influences distribution of herbaceous foods and correlated with presence of ungulates Nielsen et al. (2010) Stewart et al. (2013)
Percentage of regenerating forest Regenerating forests have greater availability of herbaceous foods Nielsen et al. (2004c, 2010)
Percentage of shrub and herbaceous landcover Correlated with availability of herbaceous foods and berries Franklin et al. (2002, 2003)
Forest age Younger seral forests have a greater abundance of herbaceous foods Nielsen et al. (2004c, 2010)
Vegetation productivity Total vegetation productivity (cumulative greenness) influences availability of herbaceous foods Coops et al. (2008) Fontana et al. (2012) AVHRR DHI
Vegetation seasonality Seasonal variability (coefficient of variation) in vegetation productivity influences timing and availability of herbaceous foods Coops et al. (2008) Fontana et al. (2012)

Abbreviations: AESRD, Alberta Environment and Sustainable Resource Development; AVHRR, Advanced Very High Resolution Radiometer; DEM, digital elevation model; DHI, Dynamic Habitat Index; ETM+, Enhance Thematic Mapper Plus; FRIGBP, Foothills Research Institute Grizzly Bear Project; TM, Thematic Mapper.