Recovery Plan for the Northern Spotted Owl - DRAFT

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* Opening the canopy in small patches and preparing the site for seeding orplanting probably will be needed to maintain ponderosa pine and Douglasfirin the forests, if fire is to be excluded to provide owl habitat.SummaryThese silvicultural systems, developed for common types of stands throughoutthe range of the owl, indicate that multilayered stands can be developed ormaintained. Where stands are well stocked with young conifers, thinningthese stands provides space for development of large trees with full crowns,while providing light and moisture for growth of understory trees into multiplelayers. The structure and species composition of multistoried stands can bedeveloped and maintained by opening the overstory to favor establishedseedlings and saplings or to establish new ones.Fire, wind, insects, pathogens, soils, and other environmental variables areimportant within forests throughout the owl's range. They must be evaluatedon a stand by stand basis to determine how they affect stand development.Their potential effects often will be a key in determining the silviculture systememployed. Also, the structure of stands must be considered. Are there hardwoodsor conifers present in the understory which will form multiple layers?Are there shrubs which will prevent or delay the establishment of trees neededto form multilayers? Will the stand produce large snags or only small ones?What will costs or returns be? Therefore, the cases presented are examples ofsystems which might be used to produce owl habitat. In practice,multidisciplinary professional input is needed on the ground to develop andimplement silvicultural systems.Careful implementation, monitoring, and evaluation of treatment effects arealso essential. They indicate the willingness and commitment to ensure thatthe system will produce the desired structure and habitat.As with all silviculture activities, there is an important linkage between planningand implementation. Silviculture systems and practices that are feasibleecologically may be difficult and expensive to carry out. The prescriptionsoutlined here call for thinning, encouraging the growth of advance regenerationof hardwoods and conifers, and establishment of regeneration during thecourse of stand development. All of these practices require care and need to beclosely monitored during and after implementation. Natural disturbances suchas fire, insect outbreaks, and windthrow affect managed and unmanagedstands. These events occur at random, and the timing and nature of theireffects cannot be predicted. After such events occur, managed andunmanaged stands must be evaluated to determine their effects on standdevelopment. In some stands, the effects might be beneficial, in that theywould aid stand development toward old-growth characteristics. In othercases, disturbance might prevent or delay development of desired standstructures.518
Literature CitedAlaback, P.A. 1982. Dynamics of understory biomass in Sitka spruce-westernhemlock forests of southeast Alaska. Ecology. 63:1932-1948.Alaback, P.A., and F. R. Herman. 1988. Long-term response of understoryvegetation to stand density in Picea-Tsuga. Canadian Journal of ForestResearch 18:1522-1530.Alaback, P.A. and J.C. Tappeiner. 1991. Response of western hemlock andearly huckleberry seedlings to forest windthrow. Canadian Journal ofForest Research 21:534-539.Agee, J.K. 1990. The historical role of fire in the Pacific Northwest forests. InWalstad et al. (eds.) Prescribed and natural fires in Pacific Northwestforests, Oregon State University Press. Corvallis, Oregon, 316 pp.Assmann, E. 1970. Principles of forest yield study. Pergammon, New York,506 pp.Atzet, T. and D.L. Wheeler. 1982. Historical and ecological perspectives of fireactivity in the Klamath Geological Province of the Rogue River and SiskiyouNational Forests. USDA Forest Service, Pacific Northwest Region, Portland,Oregon. Region 6 -Range 102, 16 pp.Atzet, T., D.L. Wheeler, B. Smith, J. Franklin, G. Riegel, and D. Thornburgh.1992. Vegetation in reforestation practices in southwestern Oregon andnorthern California. Forest regeneration in southwestern Oregon. ForestResearch Laboratory, Oregon State University, Corvallis, Oregon (In press).Baker, F.S. 1953. Stand density and growth. Journal of Forestry. 51:95-97.Birch, K. 1991. Silviculture systems for Douglas-fir. Report to NorthernSpotted Owl Recovery Team.Brieglieb, P.A. 1952. An approach to density management in Douglas-fir.Journal of Forestry. 50:529-536.Curtis, R.O., G.W. Clendenen, and D.J. DeMars. 1981. A new stand simulatorfor coastal Douglas-fir: DF SIM: A user's guide. USDA Forest ServiceGeneral Technical Report PNW- 128.Curtis, R.O. and D.D. Marshall. 1986. Levels-of-growing-stock cooperativestudy in Douglas-fir. USDA Forest Service Research Paper. PNW-356. 113PP.Curtis, R.O. 1987. Levels-of-growing-stock cooperative study report no. 9-some comparisons of DFSIM estimates with growth in the levels-of-growing-stockstudy. USDA Forest Service Research Paper. PNW-376, 34 pp.Del Rio, E. and A.B. Berg. 1979. Growth of Douglas-fir reproduction in theshade of a managed forest. Research Paper 40, Forest Research Laboratory,Oregon State University, Corvallis, Oregon.Dilworth, J.R. 1980. Growth of western hemlock stands after precommercialthinning. Research Bulletin 33, Forest Research Laboratory, Oregon StateUniversity, Corvallis, Oregon.519
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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
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continued-Common Name Causal Agent
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D. DiseasesForest diseases in the P
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III. Forest Protection in theWest C
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120 100200 500I~~~~.K446Figure F.4.
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InsectsDiseasesInsects in this subr
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__hardwoods are immune. Shade toler
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pests (Schowalter 1988). Black stai
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tion and initial attack. If manipul
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log and snag density was likely low
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B. Management Effects on StandsMana
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units (underburning or lop/scatter)
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In the higher elevation White Fir a
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growth often increases (Reinhardt a
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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
Page 500 and 501: 484
Page 502 and 503: area, structure, ages, location; ne
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 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
Page 552 and 553: II. General Economic Principles for
Page 554 and 555: practices may be able to show how s
Page 556 and 557: Economic patterns show the efficien
Page 558 and 559: The sustainable yield concept that
Page 560 and 561: A. Previously Estimated Economic Co
Page 562 and 563: County receipts were estimated to d
Page 564 and 565: 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
Page 570 and 571: cḻlTable H.4. Economic characteri
Page 572 and 573: An analysis completed by the State
Page 574 and 575: V. Preliminary Evaluation of the Ec
Page 576 and 577: 25-° 20/0M 15-a)CLU)0 10-0CL 5 -0)
Page 578 and 579: 25 -- 20-0co/o 15--Da)a0a)10m~ C) 5
Page 580 and 581: forestlands. The costs of productio
Page 582 and 583: 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
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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
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Most significant late successionall
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to evaluate options. Information in
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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
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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
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Perry, D. 1991. The ecology of coar
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2mandate the achievement of recover
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642
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644
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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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