Recovery Plan for the Northern Spotted Owl - DRAFT

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area, structure, ages, location; need for fire protection and fuel breaks: diseaseand insect populations: access, and other uses. When thinning stands, forexample, activities probably should be spread over time and space to avoidhaving large contiguous areas of temporarily open canopy, and to avoid nestingowls. Similarly, treatments such as prescribed burning to reduce fire hazardshould be scheduled with regard to stand structure, owl use, fuel concentrations,fire control strategies, and other considerations.A. Stand Structure and Owl HabitatOwl habitat as used in this report is defined as the stand structures that owlsuse for nesting. This type of habitat is apparently the most critical for survivaland recovery of owls. The structure has been quantified (see Appendix B) bystudies in which tree diameter and heights as well as snags, logs, and othervegetation were inventoried in stands used for nesting. The structures ofstands used for nesting are consistently multistoried with many small treesand fewer large trees per area (Figure G. 1). They are typically mixed specieswith two or more age classes which have developed following one or moredisturbances such as light fire, windthrow, and root diseases. Species in theoverstory are generally redwood, ponderosa pine, sugar pine, western hemlock,and Douglas-fir, while the understory may include western hemlock, westernred cedar, white fir, tanoak, bigleaf maple, and Douglas-fir on dry sites. Thereare often large dead trees and logs on the forest floor. The structures resemblethose of old-growth stands (Spies and Franklin 1991).B. Producing Stand Structure for NorthernSpotted OwlsActual examples of thinning show that reducing the density of overstory treesallows space for trees to produce large crowns and stems, and for trees andshrubs to be established in the understory (Figures G.2 and G.3). If stocking isnot controlled, dense stands may develop (Figure G.4), and it would take manyyears for these stands to produce owl habitat.The following key points emerge from the review of stand development historyand literature (11 and 111) and from developing silviculture prescriptions (IV):1. Disturbances of various sizes and intensities are a natural part of longtermforest stand development.2. Many stands within the range of the owl are growing at high densities(many trees per area). Thinning these stands will increase growth rates,sizes of crowns, and diameters of remaining trees.3. Mortality caused by suppression and crowding among trees is not likelyto provide large snags or logs on the forest floor because only the smallertrees die. Thinning of stands will shift the size of a tree that dies fromdisease, insect, fire, and other causes, to large sizes.4. To provide large snags and logs on the forest floor in young (30 to 80+years) conifer stands, it often may be necessary to kill some of the largertrees in the stand. This is particularly true for stands regenerated afterharvesting or reforestation following a fire.5. Development of a multistoried stand from single-story conifer standsgenerally will require thinning, small openings in the canopy, or someother disturbance to reduce overstory density. If a dense layer of shrubsis present, disturbance or control of this layer likely will be required toestablish conifers or hardwoods which can form the additional layers.6. Young stands (10 to 80+ years) on productive sites develop quite rapidly.486
6E Hardwood snagsLiConifer snagsN I\Trees per acre16012080400Trees per acre107 C87 Hl Hardwoods (H)ft49C35 H32C14 H
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I 1.2:Sp 6/draftRecovery Plan for t
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List of FiguresTable 4.1 Abbreviate
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Recovery ObjectiveSecretary of the
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Management Rules for Designated Con
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Monitoring and Research ProgramThe
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Chapter IIntroduction1
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"Threatened species" means a specie
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B. The Interagency Scientific Commi
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lished works and many government do
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II.A. Natural History of theNorther
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I- \IzXelT - - -.11 I..., ... I.."
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spring. Territories probably are sm
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Northern goshawks (Accipiter gentil
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also use a variety of nest sites in
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Home Range SizeHome range is define
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Table 2.2. Median amounts of old-gr
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3. Life Historycannot reject the hy
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Dispersal1984, Thomas et al. 1990,
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4. ConclusionOur knowledge of the n
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Ca n a d aEastern Washington Cascad
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Table 2.3. Estimated spotted owl ha
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Table 2.4. Significant threats to t
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Table 2.5. Results of surveys for s
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isolated. In these provinces, small
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centers for 30 to 35 spotted owl te
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Southwest Washington occupies a key
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Distribution of Habitat and Populat
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Province Isolation. The eastern Was
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were in suitable habitat condition.
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Estimated acres of forest landbase:
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owned and contain little suitable h
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Vulnerability to Natural Disturbanc
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Douglas-fir/hardwood types, the lat
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miles from the contiguous populatio
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In comparison, the southern part of
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Sacramento River Canyon now provide
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On January 11, 1980, there was an a
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vation Strategy for the Northern Sp
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transfer of one area to the Grand R
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The BLM Spokane (Washington) Distri
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3. National Park ServiceThe followi
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The results of a consultation are s
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- Since landowners already face cut
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4. Cumulative Effects AssessmentThe
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Assessment, Planning, and Monitorin
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Spotted owl nesting sites and activ
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Coastal Oregon Productivity Enhance
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including wildlife. In other cases,
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Currently, the Yakima Indian Nation
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where timber harvest is limited to
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III.A. Recovery Objective and Delis
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4. The population is unlikely to ne
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Needs of other species should be co
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years. The strategy of managing for
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't0
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Finally, the plan recommends mainta
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A total of 1,181 pairs of owls has
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DKnown owlsin the OregonprovincesKn
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mologists, and representatives of o
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this prey species is an appropriate
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After 100 years residual snags will
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2. Fuelwood Gathering. If allowed,
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The application of prescriptions A,
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owls. (Refer to tables in section I
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PRESCRIPTION D -RETAIN OWLS IN MANA
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126
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DCA Management Plans.The recovery p
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Endangered Species Act) or through
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6. Costs to landowners should be re
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The real or perceived disincentives
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authority of the public body to ent
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* Use the recovery plan's recommend
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140
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Supplemental pair areas - Habitat d
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Numbers of owls currently are estim
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Biological goals and implementation
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ning. Also, several unsurveyed area
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Owl pairsKnown owlsin the province3
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- Initiate long-range planning effo
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Table 3.8. Summary comments on the
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from nonfederal lands are needed to
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Eastern Washington Cascades Provinc
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(Owl pairs140 - _ _ _ _ _ _ _ _ _ _
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habitat in DCA WD- 16. Approximatel
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Table 3.12. Summary comments on the
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Ttllwrnook/Astoria area. Provide su
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connectivity between key DCAs. This
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ITable 3.14. Summary comments on th
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crest of the Cascade Mountains. The
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sites on federal lands (figure 3.21
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Owl pairsL I 350- _ _ . ...........
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DCAs, often combined with adjacent
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Owl pairsLiKnown owlsin the provinc
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nesting and roosting habitat until
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Option 3: Management of clusters: g
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Table 3.21. Summary of acreage and
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Owl pairs -Known owlsin the provinc
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and to within 0.5 miles of the acti
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Spotted owls have been found at 86
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their distance from other sites. Ar
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* Recommend population and habitat
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away in some or all of the range. D
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4. What are the population dynamics
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If the monitoring and research prog
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lowlands, eastern Oregon Cascades,
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210
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Stepdown Outline1. Management Tasks
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Table 4.1 Abbreviated Cost TableThe
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continued-TaskPriorityResp. PartyCo
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218
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220
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and the number of invertebrate anim
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Table 5.2. Numbers of other species
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Amphibians and Reptiles: Larch Moun
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228
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230
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Barrows, C. W. 1980. Feeding ecolog
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Clark, R. J., D. G. Smith, and L. H
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Franklin, A. B., J. A. Blakesley, a
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Harestad, A. S., and F. L. Bunnell.
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Lundquist, R. W. and J. M. Mariani.
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O'Halloran, K. 1989. Spotted owl in
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Solis, D. M. 1980. Habitat use by n
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Young, K. D., A. B. Franklin, and J
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248
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250
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Table A.1. General approaches for e
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complete count of the territorial b
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Table A.3. Powera for various desig
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Table A.4. Illustration of a Markov
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Obviously, these statements hold on
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Table A.6. Reliability of trend est
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Demographic AnalysisAs noted earlie
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the estimate (using the simple equa
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however, we know little about the b
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Table A.8. Summary of information n
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predict the power achieved by diffe
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Other studiestached. If dispersing
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impractical at present. We describe
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Conclusionsthe year effect can be i
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280
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282
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284
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owls. Consequently, the issue of wh
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Use of the informationAssessments a
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Recent LiteratureWe might begin by
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Kerms (1989) measured habitat struc
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Hamer (pers. comm.) described 11 ne
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Table B.3. Percent hardwoods in the
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Table B.5. Comparison of habitats u
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Table B.8. Tree density (number of
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and numbers of trees, and percent o
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Under this hypothesis, owl fitness
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suitable habitat for that region (m
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ResultsDiscussionspotted owl habita
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__Discussiondata from 41 sites in t
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Recommendations for Future Research
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314
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Hamer, T. 1988. Home range size of
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318
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320
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Parameter Estimatesfor Individual S
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provided in Table C. 5. Study of th
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Table C.6. Summary of statistics re
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3. ConclusionsThis source of bias i
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330
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Gray Wolf .........................
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formed during the initial meeting t
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provide habitat for the numerous sp
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The ApproachA committee of the Reco
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The List of Threatened and Endanger
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Mammalsoldest trees in a stand. Eig
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ABBFigure D. 1. Distribution of: a)
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KTable D.3. A list of threatened an
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Fishestheir dispersal capabilities
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OlympicNorthcoastalRockyMountainSou
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continued-StatusabState Considered
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continued-SpeciesColumbia sidebandM
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endemic to the Pacific Northwest).
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------continued-SpeciesRhyacophila
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continued-SpeciesFed3tatusa bStateW
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StatusasbOld ForestState Associatio
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Summaryspores (Maser et al. 1978b).
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Biology of Owl Prey, Older Forest A
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Woodrats.-The dusky-footed woodrat
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and are less restrictive under stat
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Stock concept.-The term "stock" was
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Table D.10. List of fish stocks of
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continued-Steelhead-owipu Sea-runTr
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continued-BasinHoodWillametteRogueS
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Table D.13. Washington streams (or
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inland distribution currently decre
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nesting territories in the three st
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However, little is known about the
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Fisher (Martes penncmti)Distributio
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at one time supported marten popula
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each population of these animals is
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species also is found under the bar
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few meters from water after heavy r
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In considering the needs of other s
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Barrows, C. W. 1981. Roost selectio
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Clark, T. W., E. Anderson, C. Dougl
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Hamer, T. E. 1991. Habitat relation
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Mannan, R. W., E. C. Meslow, and H.
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Oakley, A. L., Collins, J. A., Ever
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Solis, D. M. 1983. Summer habitat e
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Washington Natural Heritage Program
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414
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f. Wilderness.g. Livestock grazing.
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I. Monitoring.1. Northern spotted o
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420
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here will reduce some of that habit
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424
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426
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Selection of Forest TypesAt the tim
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eceive as little as 25 inches. Disc
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A. FireThe combination and interact
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Table F.4. Important forest insects
Page 452 and 453: continued-Common Name Causal Agent
Page 454 and 455: D. DiseasesForest diseases in the P
Page 460 and 461: III. Forest Protection in theWest C
Page 462 and 463: 120 100200 500I~~~~.K446Figure F.4.
Page 464 and 465: InsectsDiseasesInsects in this subr
Page 466 and 467: __hardwoods are immune. Shade toler
Page 468 and 469: pests (Schowalter 1988). Black stai
Page 470 and 471: tion and initial attack. If manipul
Page 472 and 473: log and snag density was likely low
Page 474 and 475: B. Management Effects on StandsMana
Page 476 and 477: units (underburning or lop/scatter)
Page 478 and 479: In the higher elevation White Fir a
Page 480 and 481: growth often increases (Reinhardt a
Page 482 and 483: 50rcc4*0-cC)2M CmZ13010-yearI ,...*
Page 484 and 485: In the East Cascades subregion fore
Page 486 and 487: The introduced disease, white pine
Page 488 and 489: VI. Conclusionsmortality will resul
Page 490 and 491: Baker, F.A. 1988. The influence of
Page 492 and 493: Habeck, J.R. 1990. Old-growth ponde
Page 494 and 495: Perry, D.A., and J.G. Borchers. 199
Page 496 and 497: Weatherspoon, C.P., and C.N. Skinne
Page 498 and 499: 482
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Page 504 and 505: Stand AFigure G.2. A--unthmnned Dou
Page 506 and 507: figure 0.3. Effects of thinning Dou
Page 508 and 509: II. Review of Natural Vegetation an
Page 510 and 511: western hemlock, and sometimes othe
Page 512 and 513: year intervals (Appendix F). With t
Page 514 and 515: Live crown ratiobecent)6050IStand A
Page 516 and 517: Basal area growth continued to incr
Page 518 and 519: technology probably will allow some
Page 520 and 521: Stand A. No activities (west side 3
Page 522 and 523: Stand A. No activities (west side o
Page 524 and 525: acre, 4 to 12 inches in diameter),
Page 526 and 527: allow redwood sprout clumps maximum
Page 528 and 529: KAge 15 years - 511 trees per acre,
Page 530 and 531: 6Stems per acre100 _ Stand A. Natur
Page 532 and 533: Basal Area(square feetper acre)50 1
Page 534 and 535: * Opening the canopy in small patch
Page 536 and 537: Drew, T.J. and J.W. Flewelling. 197
Page 538 and 539: Miller, R.E.; D.L. Reukema, and R.L
Page 540 and 541: Tappeiner, J.C., P.M. McDonald, and
Page 542 and 543: 526
Page 544 and 545: 528
Page 546 and 547: 6. Timber supply curve and economic
Page 548 and 549: scientifically credible biological
Page 550 and 551: E. Summary of Preliminary Estimates
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II. General Economic Principles for
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practices may be able to show how s
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Economic patterns show the efficien
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The sustainable yield concept that
Page 560 and 561:
A. Previously Estimated Economic Co
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County receipts were estimated to d
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B. Potential Social Costs of Owl Co
Page 566 and 567:
The contrast between the behavior d
Page 568 and 569:
0U1 n1nDTable H.2. Economic depende
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cḻlTable H.4. Economic characteri
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An analysis completed by the State
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V. Preliminary Evaluation of the Ec
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25-° 20/0M 15-a)CLU)0 10-0CL 5 -0)
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25 -- 20-0co/o 15--Da)a0a)10m~ C) 5
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forestlands. The costs of productio
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In Figure H.8, the equilibrium betw
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foregone and the way they will save
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The income created by the purchase
Page 588 and 589:
Two concepts are useful for underst
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y an estimate of the price that wou
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Table H.10. Comparison of timber em
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of the second year. The same assump
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are generally much lower than for c
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582
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studies at University of Washington
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586
Page 604 and 605:
Most significant late successionall
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to evaluate options. Information in
Page 608 and 609:
Q0Table 1.1. Estimated acres and ow
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soTable 1.3. Estimated acres and ow
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01CDarTable 1.5. Size class distrib
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Table 1.8. Frequency distribution o
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Literature CitedThomas, J.W., E.D.
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602
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- The overlap of home ranges among
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Table J.2. Acreage and owl numbers
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continuedDCA Land AcreageIdent. Sta
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Table J.9. Acrea ?e and owl numbers
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continued-DCA LandIdent. StatusAcre
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-DCAIdent.LandStatusAcreageNRF Tota
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626
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Experience Includes: Assistant Dire
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Education: B.S. in forestry from Or
Page 648 and 649:
Team SupportCharles Bruce, Oregon D
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continued-1 5-24-91 Other SpeciesSu
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continued-9-16 thru9-20-919-19-91Sp
Page 654 and 655:
Perry, D. 1991. The ecology of coar
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2mandate the achievement of recover
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642
Page 660 and 661:
644
Page 662 and 663:
Aspect - the direction a slope face
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Congressionally classified and desi
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Empirical - derived from direct obs
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Hummocky - a landscape characterize
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Mixed conifer - as used in this doc
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Potential habitat - a stand of tree
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Sensitive species - those species t
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Take -Uunder the Endangered Species
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wild, scenic, or recreational by an
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Recovery Plan for the Northern Spotted Owl - DRAFT

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