Recovery Plan for the Northern Spotted Owl - DRAFT

Recovery Plan for the Northern Spotted Owl - DRAFT Recovery Plan for the Northern Spotted Owl - DRAFT

10.07.2015 Views

Fisher (Martes penncmti)Distribution.-The range of the fisher (a small mammalian carnivore) extendssouth from the forests of central and southeastern Canada to New Englandand the Great Lakes states in the east and from British Columbia to westernMontana and the Sierra Nevada mountains of California in the west (Arthur etal. 1989, Strickland et al. 1982). Prior to European settlement, the fisheroccupied all densely forested areas of Washington, with the most dense populationslocated on the Olympic Peninsula (K. Aubry, U.S. Forest Service,Olympia, Washington, pers. comm. 1991). Although rare, the fisher stilloccurs in the Cascades, Okanogan Highlands, and the Olympic Peninsula (K.Aubry, U.S. Forest Service, Olympia, Washington, pers. comm. 1991). At onetime, the fisher probably was present in all Oregon counties where coniferousforests occurred. Today, the species is known to inhabit forested portions ofthe Cascade, Klamath, Siskiyou, and Blue Mountains (Marshall 1991). Thereare few recent reports from the Coast Range, although a fisher sighting wasreported from the Hebo Ranger District, Lincoln County in 1991. The range ofthe fisher in California extends from the Oregon border in the northwest southto Lake and Sonoma Counties. To the east, the species has been found nearClear Lake in Lassen County, and as far south as Greenhorn Mountain, KernCounty. Fishers range from near sea level in the low coastal areas to above11,000 feet in the Sierra Nevada (California Department Fish and Game 1986).Status.- A petition was filed with the U.S. Fish and Wildlife Service in 1990 tolist the fisher as a threatened species in California, Oregon, and Washington.The petition was denied, based on the inconclusive nature of the information itprovided. An interagency working group subsequently was formed to facilitatesharing on new information of fishers and the FWS included the fisher amongits candidate species in 1991. During the last decade, sightings of fishershave been recorded in Mt. Rainier, Olympic, and North Cascades NationalParks in Washington, but no formal surveys were conducted. Ongoing investigationsin Olympic National Park indicate that the fisher may have beenextirpated from the Olympic Peninsula as a result of extensive habitat alteration(K. Aubry, U.S. Forest Service, Olympia, Washington, pers. comm. 1991).The fisher is a "candidate" species for listing as threatened or endangered inWashington.Trapping and incidental loss caused by nontarget strychnine poisoning (fromwolf and coyote baits) resulted in declines in Oregon fisher populations by the1930s (Irwin 1987). Trapping for fishers has been prohibited in Oregon since1937, but after more than 50 years, populations do not seem to have recovered(Marshall 1991). In 1961, 24 fishers were transplanted from British Columbiato Klamath and Union Counties. No post-release monitoring was conducted,and the status of any resulting fisher population is unknown (Marshall 1991).Incidental sightings in the Cascade, Siskiyou, and Coast Range Mountainscontinue to be reported, but no standardized surveys have been undertaken toassess population status at the state level (Marshall 1991). The fisher is listedas a sensitive species in Oregon and California. Schempf and White (1977)suggested that fishers were relatively common in the northern coastal mountainsof California, but were uncommon or rare in the Sierra Nevada.Natural history and habitat associations.-Fishers inhabit coniferous andmixed coniferous/deciduous forests. Dense, mature to old-growth forests arepreferred during summer for cover and den sites (Jones 1991, Marshall 1991,Washington Department Wildlife 199 lb). In Idaho, stands used by fishersduring the breeding season had more snags, logs, and large-diameter treesrelative to all available habitat. Stands of pole-sized or smaller trees wereavoided, as were open, drier habitats. Jones (1991) reported a preference for388

forested riparian habitats. Fishers in California selected coniferous forestswith a hardwood component for summer habitat (Marshall 1991).Several authors suggest that fishers select habitats with a high degree ofoverhead cover and avoid large openings (Strickland et al. 1982, Marshall1991). In Maine, where population densities are quite high in comparison topopulations in the western states, fishers are tolerant of low-density ruraldevelopment and will cross roads and farm fields to travel among forestedstands. Summer resting sites may be situated in hollow snags, under logs,brush piles, or root wads. Maternal dens usually are situated high in a hollowsnag.Fishers may use a wider variety of habitats during winter than in summer.Forest structure and prey availability are probably the critical factors in theselection of winter habitat. Jones (1991) found that old-growth stands wereimportant winter habitats for fishers in Idaho, but second-growth stands alsowere used. Fishers select stands with large remnant trees and/or logs thathave survived earlier fires in second-growth. Fishers appeared to select forestedriparian areas in winter as well as in summer. Allen (1983) concludedthat stands having a high degree of coniferous tree canopy closure providedoptimal winter habitat. Jones (1991) found no indication that snow conditionsinfluenced winter habitat use by fishers; other authors suggest that fishersmay move to lower elevations to avoid deep snow or to find prey (Marshall1991).Small to medium-sized mammals, birds, and carrion dominate the diet of thefisher; however vegetation, molluscs, and other invertebrates also have beenidentified from digestive tracts (Jones 1991, Arthur et al. 1989). Porcupinesare a major prey species wherever they occur within the range of the fisher(Strickland et al. 1982). Red-backed voles and flying squirrels are importantprey for the fisher in Idaho and Oregon (Ingram 1973). Grenfell and Fasenfest(1979) found false truffles (Rhizopogon) to be an important food of fishers innorthern California. Fishers may be common locally in parts of northernCalifornia and Maine (California Fish and Game 1986, Arthur 1987); otherwisethe species occurs at low densities.Most authors concur that mature and old-growth forests are important habitatsfor fishers. While some believe fishers require large contiguous stands ofold-growth (Marshall 1991, Washington Department Wildlife 199 lb), othersemphasize an apparent selection for habitat diversity within the home range(Strickland et al. 1982). Given the large home ranges of fishers, these twoviews may not be contradictory.Marten Martes arnericana)Distribution.-The marten (a small mammalian carnivore) inhabits the borealforests of North America from Canada and Alaska south to California, Idaho,western Montana, Colorado, Utah, and New Mexico in the west, and the GreatLakes states and northern New England in the east. Historically, the specieswas common throughout the northeastern United States and most of Canada.Loss of habitat compounded by commercial trapping resulted in the extirpationof martens from most of New England and portions of southeastern Canada bythe 1930s (Clark et al. 1987, deVos 1964).Martens have been recorded from most of the mountainous areas of Washingtonincluding the Blue, Cascade, Olympic and Selkirk Mountains, theOkanogan Highlands, the coastal ranges and Vancouver Island. Populationsare most dense in the Cascades, Selkirks, and Okanogan Highlands (WashingtonDepartment Wildlife 199 lb). All of the major mountain ranges in Oregon389

Fisher (Martes penncmti)Distribution.-The range of <strong>the</strong> fisher (a small mammalian carnivore) extendssouth from <strong>the</strong> <strong>for</strong>ests of central and sou<strong>the</strong>astern Canada to New Englandand <strong>the</strong> Great Lakes states in <strong>the</strong> east and from British Columbia to westernMontana and <strong>the</strong> Sierra Nevada mountains of Cali<strong>for</strong>nia in <strong>the</strong> west (Arthur etal. 1989, Strickland et al. 1982). Prior to European settlement, <strong>the</strong> fisheroccupied all densely <strong>for</strong>ested areas of Washington, with <strong>the</strong> most dense populationslocated on <strong>the</strong> Olympic Peninsula (K. Aubry, U.S. Forest Service,Olympia, Washington, pers. comm. 1991). Although rare, <strong>the</strong> fisher stilloccurs in <strong>the</strong> Cascades, Okanogan Highlands, and <strong>the</strong> Olympic Peninsula (K.Aubry, U.S. Forest Service, Olympia, Washington, pers. comm. 1991). At onetime, <strong>the</strong> fisher probably was present in all Oregon counties where coniferous<strong>for</strong>ests occurred. Today, <strong>the</strong> species is known to inhabit <strong>for</strong>ested portions of<strong>the</strong> Cascade, Klamath, Siskiyou, and Blue Mountains (Marshall 1991). Thereare few recent reports from <strong>the</strong> Coast Range, although a fisher sighting wasreported from <strong>the</strong> Hebo Ranger District, Lincoln County in 1991. The range of<strong>the</strong> fisher in Cali<strong>for</strong>nia extends from <strong>the</strong> Oregon border in <strong>the</strong> northwest southto Lake and Sonoma Counties. To <strong>the</strong> east, <strong>the</strong> species has been found nearClear Lake in Lassen County, and as far south as Greenhorn Mountain, KernCounty. Fishers range from near sea level in <strong>the</strong> low coastal areas to above11,000 feet in <strong>the</strong> Sierra Nevada (Cali<strong>for</strong>nia Department Fish and Game 1986).Status.- A petition was filed with <strong>the</strong> U.S. Fish and Wildlife Service in 1990 tolist <strong>the</strong> fisher as a threatened species in Cali<strong>for</strong>nia, Oregon, and Washington.The petition was denied, based on <strong>the</strong> inconclusive nature of <strong>the</strong> in<strong>for</strong>mation itprovided. An interagency working group subsequently was <strong>for</strong>med to facilitatesharing on new in<strong>for</strong>mation of fishers and <strong>the</strong> FWS included <strong>the</strong> fisher amongits candidate species in 1991. During <strong>the</strong> last decade, sightings of fishershave been recorded in Mt. Rainier, Olympic, and North Cascades NationalParks in Washington, but no <strong>for</strong>mal surveys were conducted. Ongoing investigationsin Olympic National Park indicate that <strong>the</strong> fisher may have beenextirpated from <strong>the</strong> Olympic Peninsula as a result of extensive habitat alteration(K. Aubry, U.S. Forest Service, Olympia, Washington, pers. comm. 1991).The fisher is a "candidate" species <strong>for</strong> listing as threatened or endangered inWashington.Trapping and incidental loss caused by nontarget strychnine poisoning (fromwolf and coyote baits) resulted in declines in Oregon fisher populations by <strong>the</strong>1930s (Irwin 1987). Trapping <strong>for</strong> fishers has been prohibited in Oregon since1937, but after more than 50 years, populations do not seem to have recovered(Marshall 1991). In 1961, 24 fishers were transplanted from British Columbiato Klamath and Union Counties. No post-release monitoring was conducted,and <strong>the</strong> status of any resulting fisher population is unknown (Marshall 1991).Incidental sightings in <strong>the</strong> Cascade, Siskiyou, and Coast Range Mountainscontinue to be reported, but no standardized surveys have been undertaken toassess population status at <strong>the</strong> state level (Marshall 1991). The fisher is listedas a sensitive species in Oregon and Cali<strong>for</strong>nia. Schempf and White (1977)suggested that fishers were relatively common in <strong>the</strong> nor<strong>the</strong>rn coastal mountainsof Cali<strong>for</strong>nia, but were uncommon or rare in <strong>the</strong> Sierra Nevada.Natural history and habitat associations.-Fishers inhabit coniferous andmixed coniferous/deciduous <strong>for</strong>ests. Dense, mature to old-growth <strong>for</strong>ests arepreferred during summer <strong>for</strong> cover and den sites (Jones 1991, Marshall 1991,Washington Department Wildlife 199 lb). In Idaho, stands used by fishersduring <strong>the</strong> breeding season had more snags, logs, and large-diameter treesrelative to all available habitat. Stands of pole-sized or smaller trees wereavoided, as were open, drier habitats. Jones (1991) reported a preference <strong>for</strong>388

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