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Recovery Plan for the Northern Spotted Owl - DRAFT

Recovery Plan for the Northern Spotted Owl - DRAFT

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Table B.14. Habitata within 1.3 miles of 21 nor<strong>the</strong>rn spotted owl nests on managedlands in <strong>the</strong> eastern Klamath province (Self and Brown, pers. comm.).IAverage Canopy Area Number Nests perDiameter Cover (m, 2 ) of nests m1 2>24" >60% 12.26 10 0.8211-24" >60% 4.94 3 0.61>24" 40-60% 4.23 1 0.2411-24" 40-60% 36.12 7 0.21a Area covered by stands of Douglas-fir with an understory of tanoak and madrone or by stands of Klamath mixed conifers (white fir, Douglas-fir,ponderosa pine, incense cedar, and sugar pine with an understory of oak and maple).. .stand is well below <strong>the</strong> mean in old-growth stands. This hypo<strong>the</strong>sis should beinvestigated carefully because it has important implications <strong>for</strong> <strong>the</strong> design ofstrategies to protect owls in managed <strong>for</strong>estlands.The combination of density (and demographic) data and structural features at<strong>the</strong> nest site and in <strong>the</strong> nest stand provides a powerful data set <strong>for</strong> analyzinghabitat preferences. Similar in<strong>for</strong>mation from o<strong>the</strong>r parts of Cali<strong>for</strong>nia, and on<strong>the</strong> east side of <strong>the</strong> Cascades will be particularly useful in <strong>the</strong> future.Demographic Rates in Different HabitatsResultsThomas et al. (1990) reported that proportion of territories with pairs andreproductive success declined as <strong>the</strong> amount of old-growth declined. Thisconclusion was based both on Forest Service monitoring data and on landscapestudies. Results appearing since Thomas et al. (1990) are described in<strong>the</strong> next section.Meyer et al. (1992) did not find any consistent relationships between <strong>the</strong>number of years that sites were occupied by owls and various measures of<strong>for</strong>est fragmentation.We reanalyzed <strong>the</strong> data from Meyer et al. (1992) to determine whe<strong>the</strong>r turnoverof adults varied with <strong>the</strong> amount of older <strong>for</strong>est (i.e., more than 120 years)present in <strong>the</strong> circle. Persistence of adults was defined as <strong>the</strong> probability thata bird present in a circle at <strong>the</strong> start of a year would be found at <strong>the</strong> site <strong>the</strong>next year, given that <strong>the</strong> site was revisited in <strong>the</strong> following year. The consensusamong spotted owl biologists is that adults rarely change breeding sites (Lintpers. comm., Franklin pers. comm., Gutierrez pers. comm., Miller pers. comm.,Wagner pers. comm.). For example, in <strong>the</strong> Andrews study area in <strong>the</strong> westernOregon Cascades, during 305 pair-years, divorce and settlement elsewhereoccurred in, at most, four cases and was never established with certainty(Swindle and DeStefano pers. comm.). Persistence, as measured above,probably indicates adult survivorship, although we believe this issue needsfur<strong>the</strong>r study. We obtained data from <strong>the</strong> 50 circles studied by Meyer et al.(1992), and Johnson (pers. comm.) supplied us with similar owl and habitat309

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