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Recovery Plan for the Northern Spotted Owl - DRAFT

Recovery Plan for the Northern Spotted Owl - DRAFT

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disturbance, natural succession is a relatively slow process, especially duringlate seral stages. Thus, stable habitats are provided <strong>for</strong> species that cannotdisperse readily from one suitable habitat to ano<strong>the</strong>r. Large conifers alsoprovide significant horizontal and vertical complexity. Individual trees havedeep crowns, often with trunks and limbs that are de<strong>for</strong>med or scarred bywind, lightning, or mistletoe infection. Broken tree tops and irregular branchesprovide nesting habitat <strong>for</strong> many species. The understory of shade-toleranttrees, such as western hemlock, provide fur<strong>the</strong>r vertical divesity. Openingsdevelop in <strong>the</strong> canopy as a result of mortality of dominant trees. As <strong>the</strong> canopyopens, sunlight penetrates to <strong>the</strong> <strong>for</strong>est floor, and a diverse layer of shrubs and<strong>for</strong>bs develops, fur<strong>the</strong>r increasing spatial complexity of <strong>the</strong> <strong>for</strong>est.Perhaps one of <strong>the</strong> most important features of old-growth <strong>for</strong>ests is <strong>the</strong> greatquantity of dead wood <strong>the</strong>y contain. Biomass of snags and down logs reaches80 tons per acre in stands 500 years old (Spies and Cline 1988) with aboutone-third of this in snags and two-thirds in down logs (David Perry, OregonState University, pers. comm.). Snags provide shelter and nest sites <strong>for</strong> anumber of bird and mammal species. Harris and Maser (1984) suggest thatelimination of snags in a mature, unmanaged Douglas-fir <strong>for</strong>est in <strong>the</strong> CascadeMountains would reduce <strong>the</strong> number of resident wildlife species (not includingbats) from 90 to about 80. Elimination of snags and logs would reduce <strong>the</strong>number to about 60. Snags are especially important to nonmigratory birds:Mannan (1977) found that about 60 percent of bird species in Douglas-fir<strong>for</strong>ests during <strong>the</strong> winter were cavity-nesters.Down logs are important features in terrestrial and aquatic habitats. Downlogs contribute to structural diversity, provide hiding cover <strong>for</strong> small animals,and provide moist microhabitats during dry periods. Dead and decaying woodon <strong>the</strong> <strong>for</strong>est floor contain important water reserves that buffer <strong>the</strong> effects of<strong>the</strong> summer drought periods typical of <strong>the</strong> region (Perry 1991). Logs are alsoimportant elements of stream ecosystems. They provide baffles and dams thatcreate pools and backwaters, increasing diversity of habitats within <strong>the</strong>sesystems. Logs and coarse woody debris also provide food <strong>for</strong> aquatic insects,which in turn provide food <strong>for</strong> predators at higher trophic levels. Fish biomassis related closely to quantity of coarse woody debris in Northwest streams(Harmon et al. 1986). Streams in managed <strong>for</strong>ests typically contain few largelogs.There is not likely to be additional recruitment of extremely large diameter logsbecause rotation cycles are too short to permit <strong>the</strong> growth and mortality ofextremely large trees.Large numbers of terrestrial organisms also use coarse woody debris <strong>for</strong> foodand shelter. Important examples include <strong>the</strong> nor<strong>the</strong>rn flying squirrel andwestern red-backed vole. These important spotted owl prey species feed onmycorrhizal fungi, which appear to be associated with decaying logs (Maser etal. 1985, Ure and Maser 1982). O<strong>the</strong>r vertebrates that use logs includesalamanders, shrews, and marten (McComb 1991), as well as large numbers ofinvertebrates such as insects, slugs, and centipedes (Harmon et al. 1986,Parsons etal. 1991).Older <strong>for</strong>ests are productive and valuable as wildlife habitat although <strong>the</strong>irvalue in this regard often has been underestimated. Isaac (1952) referred toold-growth as "biological deserts." Norse (1990) has suggested that thismisperception was partly a result of preoccupation with game species, whichtend to be less abundant in mature <strong>for</strong>ests than in early seral environments.Because of <strong>the</strong> complex combination of characteristics required, it is doubtfulthat managed <strong>for</strong>ests with short rotations and even-aged management can335

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