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Recovery Plan for the Northern Spotted Owl - DRAFT

Recovery Plan for the Northern Spotted Owl - DRAFT

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The following section contains an example of <strong>the</strong> application of salvage guidelinesin <strong>the</strong> Douglas-fir/Western Hemlock Zone of <strong>the</strong> western Oregon andWashington Cascades. The example shows how specific guidelines would bedeveloped <strong>for</strong> an area where an old-growth <strong>for</strong>est stand suffered catastrophicdisturbance.Applying Salvage Guidelines in Western Washington and OregonThis example is developed <strong>for</strong> salvage of a hypo<strong>the</strong>tical stand that suffered astand-replacing fire. Prior to <strong>the</strong> fire, <strong>the</strong> stand would have been classified asold-growth. Live tree densities <strong>for</strong> <strong>the</strong> original stand are in Table 3.1Snag RetentionSnag decomposition rates are related inversely to diameter. Equationsdeveloped by McComb and Ohmann (pers. comm.) predict that in westernWashington and Oregon <strong>the</strong> probability of snags less than 20-inch dbhpersisting <strong>for</strong> 100 years is near zero. Above this diameter, probabilities ofsnag survival increase rapidly <strong>for</strong> western hemlock and Douglas-fir.Snags more than 20-inch dbh are especially important <strong>for</strong> cavity-nestingbirds. Nelson (1989) found significant selection by cavity-nesters <strong>for</strong> snagsof this size. Smaller snags were not selected. Carey et al. (1991) andLundquist and Mariani (1991) also found greater use of larger snags. Sinceflying squirrels, an owl prey species, are secondary cavity users, management<strong>for</strong> higher densities of primary cavity-nesters will benefit squirrels and,indirectly, owls. Retention of all snags more than 20-inch dbh will maximize<strong>the</strong> number of residual snags available to flying squirrels, while providingimportant habitat <strong>for</strong> bird species responsible <strong>for</strong> <strong>the</strong> excavation of cavitiesused by squirrels.Application of <strong>the</strong> guidelines <strong>for</strong> salvage to an old-growth <strong>for</strong>est in <strong>the</strong>Oregon Cascades will provide retention of an average of 17 Douglas-fir and 9hemlock snags per acre based on mean live-tree densities (Table 3.1) <strong>for</strong>those <strong>for</strong>ests (Spies pers. comm.). Because of <strong>the</strong> diversity of initial diameters,predicting snag population survivorship is complex. However, projectionsbased on decay rate constants of Harmon et al. (1986) suggest thatabout two Douglas-fir snags per acre will remain in 100 years. The equationsof McComb and Ohmann (pers. comm.) predict that as many as four tosix Douglas-fir and one hemlock snags per acre may persist. These estimatesare within <strong>the</strong> range of densities commonly found in naturally regeneratedstands at that age (Carey et al. 1991, Huff et al. 1991, Spies andFranklin 1991).Table 3.1. Live tree densities in example old-growth western hemlock/Douglas-firstand prior to stand-replacing fire.Stem Density per Acre by Size Class2 to 4 inches 4 to 20 inches 20 to 40 inches 40 to 60 inches 60 inches+Douglas-fir 10 17 8 7 2Westernhemlock 23 33 8 1 0115

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