Gopher snake (Pituophis catenifer deserticola)3
Maintain denning habitat and dispersal routes.
Wildlife habitat areas (~1000 m radius) should be established over communal dens. The placement of WHAs should be based on local topography and snake dispersal routes. It is possible that in some locations a communal den may not exist. Instead, the snakes may hibernate in small, isolated groups. Where this occurs, any talus slopes, rock outcrops or cliff habitats identified to be important for the conservation of these species should be considered for WHA designation. Design should try to include suitable egg laying (sandy soils) and foraging (riparian) areas.
Minimize disturbance and mortality, particularly road mortality, near snake hibernacula.
Maintain critical structural elements such as wildlife trees, coarse woody debris, rock outcrops and concentrations of boulders.
Minimize disturbance to riparian areas to maintain foraging opportunities.
Maintain microclimatic conditions of hibernacula.
Where migration routes from denning locations to summer habitats have been transected by roadways, use methods such as drift fences, culverts or seasonal road restrictions, to allow the safe passage of snakes.
Where possible, provide a 1 km buffer between WHAs and residential development or proposed developments to minimize disturbances. Rock climbing should be considered a disturbance at sensitive sites.
Riparian areas adjacent to WHA should be managed or restored to ensure range foraging habitat is maintained.
Avoid converting areas adjacent to WHA to an early seral grassland condition.
Follow the seral stage objectives for rangelands as described in Biodiversity Guidebook.
Water birch-red-osier dogwood, Ponderosa pine-black cottonwood-Nootka rose-poison-ivy
Rubber boa (Charina bottae)
Maintain denning habitat and dispersal routes.
Wildlife habitat areas (~1000 m radius) should be established over communal dens. A WHA should include a core area and a buffer. The core area consists of the den plus 30 m radius. The placement of WHAs should be based on local topography and snake dispersal routes. It is possible that in some locations a communal den may not exist. Instead, the snakes may hibernate in small, isolated groups. Where this occurs, any habitats identified to be important for the conservation of these species should be considered for WHA designation.
Minimize disturbance and mortality, particularly road mortality, near snake hibernacula.
Maintain critical structural elements such as wildlife trees, coarse woody debris, rock outcrops and concentrations of boulders.
Minimize disturbance to riparian areas to maintain foraging opportunities.
Maintain microclimatic conditions of hibernacula.
Where migration routes from denning locations to summer habitats have been transected by roadways, use methods such as drift fences, culverts or seasonal road restrictions, to allow the safe passage of snakes.
Follow the seral stage objectives for rangelands as described in Biodiversity Guidebook.
Water birch-red-osier dogwood, Ponderosa pine-black cottonwood-Nootka rose-poison-ivy
3 Gopher snake – species has been split resulting in a change in scientific name.
4 Racer – common name changed.
Night snake (Hypsiglena torquata)
RACER (Coluber constrictor)4
WHA planning objectives
Wildlife habitat area
GWM management objectives
General wildlife measures
Management considerations (not mandatory
Landscape unit planning considerations (not mandatory)
Cross references
WHA planning objectives
Wildlife habitat area
GWM management objectives
General wildlife measures
Management considerations (not mandatory
Where possible, provide a 1 km buffer between WHAs and residential development or proposed developments to minimize disturbances. Rock climbing should be considered a disturbance at sensitive sites.
Riparian areas adjacent to WHA should be managed or restored to ensure foraging habitat is maintained.
Landscape unit planning considerations (not mandatory)
Cross references
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