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Recovery Plan for the Northern Spotted Owl - DRAFT

Recovery Plan for the Northern Spotted Owl - DRAFT

Recovery Plan for the Northern Spotted Owl - DRAFT

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The introduced disease, white pine blister rust, has been particularly devastatingto western white pine and sugar pine. Native western gall rust has increasedin plantations of lodgepole pine and also occurs in ponderosa pine.C. Likely Outcome of a Total Protection StrategyOver <strong>the</strong> Next CenturyFireWindInsectsTotal protection in <strong>the</strong> context of this section of <strong>the</strong> report is defined as 'handsoff'management within designated conservation areas <strong>for</strong> <strong>the</strong> next 100 years.A total fire suppression strategy has created <strong>the</strong> multilayered yet unstable<strong>for</strong>est structure present on <strong>the</strong> landscape today. There is a very low probabilitythat any DCA created in <strong>the</strong> East Cascades subregion will avoid catastrophicwildfire over a significant portion of its landscape over <strong>the</strong> next century. MostDCAs will exhibit landscape effects of fire similar to those in <strong>the</strong> Entiat Riverwatershed. Fires of high severity and wide extent (with little overlap) haveburned in 1970, 1974, 1976, and 1988 in areas once capable of supportingowls. In <strong>the</strong> 1970 fire area, many midslope and ridge areas exhibited apresettlement pattern of low intensity fires, with even-aged lodgepole pinestands in valley bottoms, suggesting longer interval, higher severity fires in <strong>the</strong>valleys. With <strong>the</strong> more continuous fuels provided by successful fire protection,<strong>the</strong> 1970 fires were more uni<strong>for</strong>mly stand replacement in nature. One stumpbared by salvage in a burned area of <strong>the</strong> 1988 fire showed a fire-free period of99 years over which a dense, stagnated understory developed (a 60-year-oldponderosa pine was 2 inches in diameter). Be<strong>for</strong>e that, <strong>the</strong> tree survivedunderburns in 1870, 1860, 1850, 1830, and 1817, with earlier fire scarserased by <strong>the</strong> later burns.If fires can be suppressed, root rots are likely to accelerate <strong>the</strong>ir spread. Treessignificantly infected by root rots have an increased probability of windthrow.Such windthrow pockets begin as small circles and eventually widen as <strong>the</strong>root rots spread laterally to susceptible tree species. Resistant species willregenerate or be released in <strong>the</strong> openings, creating a younger, all-sized stand ofprimarily shade tolerant species. These are likely to be affected by o<strong>the</strong>rpathogens or insects and be heavily damaged by wildfires.Fire exclusion, coupled with natural mortality factors, gradually reduce <strong>the</strong>pine and larch components of mixed conifer stands. Insect outbreaks associatedwith <strong>the</strong>se seral species should show a gradual reduction in severity.However, <strong>the</strong> resulting multistoried stands of Douglas-fir and true fir createconditions <strong>for</strong> <strong>the</strong> buildup of defoliators. Douglas-fir tussock moth and westemspruce budworm populations will increase, with frequent outbreaks.Episodes of tree defoliation and/or drought in east side stands will result insevere outbreaks of <strong>the</strong> Douglas-fir beetle and fir engraver beetle. Accumulationsof heavy fuels within stands will make total fire protection very difficult.Large, fire-damaged Douglas-fir trees are susceptible to bark beetle attack.470

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