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Recovery Plan for the Northern Spotted Owl - DRAFT

Recovery Plan for the Northern Spotted Owl - DRAFT

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<strong>Spotted</strong> <strong>Owl</strong> Prey 2timber harvest (Maser et al. 1978b). Hypogeous fungi <strong>for</strong>m symbiotic relationshipswith <strong>the</strong> roots of coniferous trees, and <strong>the</strong>se associations are importantto <strong>the</strong> overall health of <strong>the</strong> trees. The nor<strong>the</strong>rn flying squirrel also consumesfungi (McKeever 1960, Maser et al. 1978b), at least seasonally, although itspends most of its time in <strong>the</strong> <strong>for</strong>est canopy. The flying squirrel also eatsepiphytic lichens that are abundant in <strong>the</strong> <strong>for</strong>est canopy. The nor<strong>the</strong>rn flyingsquirrel, red tree vole, and red-backed vole comprise more than 75 percent of<strong>the</strong> diet of <strong>the</strong> spotted owl in <strong>the</strong> Oregon Cascades, so <strong>the</strong>ir dependence on <strong>the</strong>production of fir needles, fungi, and lichens in coniferous <strong>for</strong>est is important to<strong>the</strong>se food webs and <strong>the</strong> owl.The availability of energy <strong>for</strong> maintenance and reproduction is important to allorganisms, so to properly manage an animal, <strong>the</strong> ecology of its food sourcesmust be considered. Although dietary requirements of a predator may be metby a large range of sources, many species, and <strong>the</strong> spotted owl in particular,are selective in <strong>the</strong> prey <strong>the</strong>y feed upon. Although a variety of species are eatenby <strong>the</strong> owl, only a few species make up <strong>the</strong> majority of <strong>the</strong> owl's diet within agiven region. More than 90 percent of <strong>the</strong> spotted owl prey consists of mammals(Forsman et al. 1984). <strong>Spotted</strong> owl diets and <strong>the</strong> habitat associations ofits prey were reviewed thoroughly by Thomas et al. (1990:20 1). This sectionsummarizes <strong>the</strong>ir report and adds recently published in<strong>for</strong>mation that augments<strong>the</strong>ir work.The diet of nor<strong>the</strong>rn spotted owls varies regionally, but within a region it istypically dominated by two or three species (Thomas et al. 1990). Compositionof diets varies seasonally (Forsman et al. 1984) but appears to be stable overtime based on studies during different years (Thomas et al. 1990). Flyingsquirrels (Glaucomys sabrinus) and woodrats (Neotoma cinerea and N. fuscipes)dominate <strong>the</strong> diet in mesic and dry <strong>for</strong>ests, respectively (Thomas et al. 1990).Snowshoe hares (Lepus americanus) and brush rabbits (Sylvilagus bachmantjtypically represent less than 10 percent of <strong>the</strong> prey based on number of preytaken, but because of <strong>the</strong>ir larger size, <strong>the</strong>y have been reported to comprise upto 25 percent of <strong>the</strong> prey biomass (Forsman et al. 1984:43). Red tree voles(Phenoacomys longicaudus P. porno) and deer mice (Peromyscus maniculatus)may constitute more than 30 percent of prey numbers and more than 10percent of prey biomass regionally (Thomas et al. 1990). Western red-backedvoles (Clethrionomys cali<strong>for</strong>nicus) usually comprise a smaller percent of <strong>the</strong> dietthan do red tree voles and deer mice, generally less than 5 percent of preybiomass (Forsman et al. 1984:41).Nor<strong>the</strong>rn Flying Squirrels.-Nor<strong>the</strong>rn flying squirrels have a broad distributionthroughout coniferous <strong>for</strong>ests and are found in western Washington,Oregon, and nor<strong>the</strong>rn Cali<strong>for</strong>nia (Figure D.5.a). Flying squirrels are arborealmammals and are not resident in recent clear-cuts. They nest in many substrates,including cavities in live and dead trees. Density does not appear to bestrongly dependent on stand age alone. In <strong>the</strong> Oregon Coast Range, flyingsquirrels were more abundant in old-growth than in second-growth standsduring some, but not all, years of a study by Carey et al. (1992). Similardensities were reported in old-growth and second-growth stands in <strong>the</strong> OregonCascades (Rosenberg and Anthony 1992). In an ongoing study in true fir(Abies spp.) <strong>for</strong>ests in Lassen National Forest (north-central Cali<strong>for</strong>nia), preliminarydata suggest squirrel densities are markedly lower in an intensivelymanaged shelterwood cut than in young- and old-growth stands (J. Waters,U.S. Forest Service, Arcata, Cali<strong>for</strong>nia, pers. comm.).2 Contributed by Daniel Rosenberg, Redwood Sciences Laboratory. U.S. Forest Service, Arcata, Cali<strong>for</strong>nia367

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