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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> owl use of young, managed timberlands: The significance of <strong>the</strong>owl's relationship to old-growth <strong>for</strong>ests (sensu Old-growth Definition TaskGroup 1986) is obvious: old-growth <strong>for</strong>ests are declining rapidly throughout<strong>the</strong> owl's range as a result of logging (Thomas et al. 1990, USDI 1990). Ifnor<strong>the</strong>rn spotted owls are ecologically dependent (Ruggiero et al. 1988) on oldgrowthor mature <strong>for</strong>ests, <strong>the</strong>n continued logging of <strong>the</strong>ir habitat will lead to<strong>the</strong> probable extinction of <strong>the</strong> population (Thomas et al. 1990, USDI 1990).However, Forsman et al. (1977), Forsman (1988b), and Hays et al. (1989)reported spotted owls occupying young, managed stands at lower densitiesthan in old-growth stands. A managed stand is defined in a broad context,that is, managed stands in which cutting of trees has occurred. This clarificationis necessary because <strong>the</strong>re are no examples of <strong>for</strong>ests in which logging orsilviculture has occurred where <strong>the</strong> response of owls is documented experimentally.Fur<strong>the</strong>r, Forsman (1980), Solis (1983), Forsman et al. (1984),LaHaye (1988), Chavez-Leon (1989), Solis and Gutifrrez (1990), and Sisco(1990) describe habitat used by nor<strong>the</strong>rn spotted owls in both old-growth andmature stands. Their descriptions of mature <strong>for</strong>est structure used by spottedowls is similar to <strong>the</strong> structure of uneven-aged managed <strong>for</strong>ests in northwesternCali<strong>for</strong>nia (Appendix B). Thus, it is not surprising that spotted owls arebeing observed in younger managed timberlands throughout <strong>the</strong> distribution of<strong>the</strong> subspecies (Diller 1989, Irwin et al. 1989b, 1989c, Kerns 1989, Pious1989). There is hierarchy of in<strong>for</strong>mation needed to assess and understand<strong>the</strong>se observations of owls in managed <strong>for</strong>ests. In order of increasing importance,<strong>the</strong>se classes of in<strong>for</strong>mation are 1) presence of individuals, 2) presenceof pairs, 3) density, 4) variation in reproduction, 5) survival schedules, 6)dispersal patterns, 6) ratio of internal to external recruitment, and 7) populationstability. The structure and proportions of habitats used by owls relativeto available habitats are also necessary to evaluate <strong>the</strong> observations. Finally,future harvest patterns must be known and must accommodate owl needs inorder to predict <strong>the</strong> effects of <strong>the</strong> logging activities on <strong>the</strong> birds inhabiting <strong>the</strong>semanaged timberlands.On one side, this habitat variation argues that spotted owls are not habitatspecialists. On <strong>the</strong> o<strong>the</strong>r side, it suggests that spotted owls show adaptiveresponses to regional variation in environmental conditions. Regional variationin habitat selection by owls does not indicate that <strong>the</strong>y will respond positivelyto any human-induced habitat changes in one part of <strong>the</strong>ir range that lead tohabitat conditions similar to those used by owls in o<strong>the</strong>r parts of <strong>the</strong>ir range.An additional problem in assessing variation in habitat use is <strong>the</strong> lack of aconsistent definition of vegetation seral stage classification (see Table F 1 inThomas et al. 1990). Terms such as "old-growth, mature, young age,unmanaged, managed, second-growth" are defined in <strong>the</strong> literature usingdifferent parameters and criteria. This impedes ra<strong>the</strong>r than facilitates communicationamong interested persons.<strong>Owl</strong>s in managed <strong>for</strong>ests within <strong>the</strong> Cali<strong>for</strong>nia Klamath and Cali<strong>for</strong>nia Coastprovinces usually occupy stands with high structural diversity, high canopyclosure, and ei<strong>the</strong>r large-diameter trees or residual old trees (Appendix B).These stands are usually more than 60 years old after partial logging events of<strong>the</strong> past (Thomas et al. 1990). For example, stands in <strong>the</strong> redwood region of<strong>the</strong> Cali<strong>for</strong>nia Coast province described by Kerns (1989) have a structuresimilar to unmanaged (i.e., not previously logged) mature stands occupied byowls in a nearby national <strong>for</strong>est (Solis and Gutierrez 1990). Apparently, <strong>the</strong>fast growth of redwood trees, presence of understory hardwood trees, and <strong>the</strong>remnant old trees within <strong>the</strong> stands facilitate rapid structural development of<strong>the</strong>se coastal <strong>for</strong>ests. Critical aspects yet to be estimated in previously harvested<strong>for</strong>ests are <strong>the</strong> survival, recruitment, dispersal, and reproductive patternsof <strong>the</strong>se birds relative to conspecific populations in unlogged <strong>for</strong>ests.21

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