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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III. Forest Protection in theWest Cascades SubregionA. The Natural History of DisturbanceFireIn the moist Douglas-fir forests of the Coast Range of Oregon, the WashingtonCascades, and the Olympics, fire return intervals are long (Fahnestock andAgee 1983) and most forests are first-generation post-fire forests less than 750years old. This would suggest a fire return interval somewhat less than 750years. The fire cycle model of Agee and Flewelling (1983), which is based onclimate, could not reproduce a natural fire rotation (essentially a fire cycle) lessthan 3,500 years using 20th Century climate patterns, and even with significantalteration in climate input to the model, fire return intervals could only bebrought down to about 900 years. They suggest that perhaps much largerthan average events may have occurred in the past (also suggested byHenderson and Peter 1981, for the southeastern Olympics) as a result of shorttermbut very extreme changes in two or more of the climate parameters thatdrive the model.Large fires have occurred in the historic past (Morris 1934) but our knowledgeof old-growth forest establishment dates is so weak as to preclude firm hypothesesabout disturbance pulses of the presettlement past. The forests aroundMt. Rainier appear to have had a major fire event about 750 years ago(Hemstrom and Franklin 1982) and similar aged stands have been identified inthe southern and western Olympics (Agee personal observation). A series ofabout 650-year-old and/or 450- to 500-year-old fires is apparent from the dataof Henderson and Peter (1981) in the southern Olympics; Franklin andHemstrom (1981) and Yamaguchi (1986) in the southern Washington Cascades;and Huff (1984) and legend (Quinault Natural Resources 1983) in thewestern Olympics. Although forest age-class data are sparse, these are alsotimes of sunspot minima identified by Stuiver and Quay (1980), using tree-ringanalysis of carbon- 14 activity. If large fire events are associated with theseperiods of general global cooling, they may represent periods where alteredsynoptic weather patterns, particularly during the growing season, containedhigher lightning frequency and foehn (east) wind patterns.444In moist Douglas-fir forests, long early seral tree recruitment (e.g., 75 to 100years for Douglas-fir) has been documented after disturbance by fire (Franklinand Hemstrom 1981). This pattern is not characteristic of all prehistoric fires.For example, Huff (1984) showed a 60-year recruitment interval for a ca. 1465fire in the western Olympics, while Yamaguchi (1986) shows that about 95percent of Douglas-fir was recruited within 40 years after a fire in ca. 1300near Mount St. Helens. However, even on these sites the regeneration period isdecades long and probably represents some regeneration from trees thatinitially colonized the burn and grew large enough to produce viable seed tohelp completely restock the stand. Lack of seed source, brush competition,and/or reburns have been identified as factors delaying regeneration on suchsites (Franklin and Hemstrom 1981). Patterns of reburns on the Tillamook fireof 1933 at 6-year intervals (1939, 1945, 1951) (Pvne 1982), at Mt. Rainier inthe late 19th Century, and at the southern Washington Yacolt burn of 1902(Gray 1990) are evidence these sites will rebum. High surface fire potentialduring early succession in Douglas-fir forest was identified by Isaac (1940) as a"vicious cycle" of positive feedback, encouraging rhizomatous bracken fern(Pteridium aqutihnum): this pattern was quantified by Agee and Huff (1987).Given sufficient sources for reignition (e.g., the original Yacolt and Tillamook

ums and all rebums are thought to have been human-ignited), the reburnhypothesis is likely to be true in certain areas. However, it is not clear whetherrebums were a common event prior to European settlement in the moistportion of the Douglas-fir region.After crown closure, potential surface fire behavior declines, and then graduallyincreases in the old-growth seral stage (Agee and Huff 1987). Rebums inroughly 100-year-old stands during the late 1400s (Henderson and Peter 1981)may suggest that crown fire behavior independent of surface fuels in thesethick-canopied stands may be an additional significant type of fire. Currentknowledge is insufficient to tell.For many years, the pattern of stand replacement fire summarized above was aparadigm of fire for the west side Douglas-fir region. Recent work, particularlyin the Oregon Cascades in drier western hemlock plant associations, suggestsa higher fire frequency, and different ecological role, for fire in mesic to dryDouglas-fir forest, reinforcing the output of the climate-based fire cycle model(Agee 1991 a). A site in the western Oregon Cascades (Stewart 1986) near theH. J. Andrews Experimental Forest regenerated after a stand replacement firein ca. 1530, but had experienced three partial mortality fires since then, in ca.1660, 1860, and 1890. Some of these were in the settlement period and probablyreflect human-caused fires of that period, but the partial mortality associatedwith them is significant. Over a broader area several miles to the southeastencompassing similar forest types, Morrison and Swanson (1990) suggesta natural fire rotation of 95 to 145 years over the last 5 centuries, well belowthat of the moist Douglas-fir forests of Washington. The patchiness of at leastsome of the fires is illustrated by the fire severity maps in Morrison andSwanson (1990). A similar fire regime was noted by Means (1982) on dry Douglas-firsites in the western Oregon Cascades and by Agee and Dunwiddie(1984) for dry Douglas-fir forests in Washington's San Juan Islands. Anotherfire history analysis was completed by Teensma (1987) near the area studiedby Morrison and Swanson. Using conservative methods that did not recognizeunderburns with no resulting regeneration or substantial fire-scarring of trees,Teensma estimated a natural fire rotation of 100 years over the last 5 centuries.If fires of moderate severity are removed from the analysis, a stand-replacementmean fire return interval is 130 to 150 years, suggesting that intensefires are a significant part of the natural fire regime in this area, but thatfires of lower severity also occur. Other stands of 500 years age or older existwithout much evidence of recurrent fire.These studies indicate that a variable fire regime with shorter fire return intervalsthan moist Washington Douglas-fir forests occur in the central OregonCascades, and in other mesic to dry Douglas-fir forests. It is, in a sense, atransitional area to the Klamath subregion in terms of fire history.Huff (1984) has summarized the species response to disturbance regimes formoist Douglas-fir forests. If fire is absent for 700 to 1,000 years on wet sites,Douglas-fir will drop out of the stand, and western hemlock, Pacific silver fir,or western redcedar will be the primary seed source for post-fire regeneration.On sites with fire return intervals in the 300- to 600-year range, well withinthe longevity of individual Douglas-fir, mixed dominance of Douglas-fir andwestern hemlock or Pacific silver fir will result from a typically severe standreplacement fire (Figure F.4). By age 200+years, the characteristics of oldgrowthare almost always present. The Douglas-fir component, having developedafter the previous centuries-old fire, provides the large live tree criterion.Both Douglas-fir and the more dense western hemlock begin to supply thelarge log component as they begin to die from suppression, disease, orwindthrow.445

III. Forest Protection in <strong>the</strong>West Cascades SubregionA. The Natural History of DisturbanceFireIn <strong>the</strong> moist Douglas-fir <strong>for</strong>ests of <strong>the</strong> Coast Range of Oregon, <strong>the</strong> WashingtonCascades, and <strong>the</strong> Olympics, fire return intervals are long (Fahnestock andAgee 1983) and most <strong>for</strong>ests are first-generation post-fire <strong>for</strong>ests less than 750years old. This would suggest a fire return interval somewhat less than 750years. The fire cycle model of Agee and Flewelling (1983), which is based onclimate, could not reproduce a natural fire rotation (essentially a fire cycle) lessthan 3,500 years using 20th Century climate patterns, and even with significantalteration in climate input to <strong>the</strong> model, fire return intervals could only bebrought down to about 900 years. They suggest that perhaps much largerthan average events may have occurred in <strong>the</strong> past (also suggested byHenderson and Peter 1981, <strong>for</strong> <strong>the</strong> sou<strong>the</strong>astern Olympics) as a result of shorttermbut very extreme changes in two or more of <strong>the</strong> climate parameters thatdrive <strong>the</strong> model.Large fires have occurred in <strong>the</strong> historic past (Morris 1934) but our knowledgeof old-growth <strong>for</strong>est establishment dates is so weak as to preclude firm hypo<strong>the</strong>sesabout disturbance pulses of <strong>the</strong> presettlement past. The <strong>for</strong>ests aroundMt. Rainier appear to have had a major fire event about 750 years ago(Hemstrom and Franklin 1982) and similar aged stands have been identified in<strong>the</strong> sou<strong>the</strong>rn and western Olympics (Agee personal observation). A series ofabout 650-year-old and/or 450- to 500-year-old fires is apparent from <strong>the</strong> dataof Henderson and Peter (1981) in <strong>the</strong> sou<strong>the</strong>rn Olympics; Franklin andHemstrom (1981) and Yamaguchi (1986) in <strong>the</strong> sou<strong>the</strong>rn Washington Cascades;and Huff (1984) and legend (Quinault Natural Resources 1983) in <strong>the</strong>western Olympics. Although <strong>for</strong>est age-class data are sparse, <strong>the</strong>se are alsotimes of sunspot minima identified by Stuiver and Quay (1980), using tree-ringanalysis of carbon- 14 activity. If large fire events are associated with <strong>the</strong>seperiods of general global cooling, <strong>the</strong>y may represent periods where alteredsynoptic wea<strong>the</strong>r patterns, particularly during <strong>the</strong> growing season, containedhigher lightning frequency and foehn (east) wind patterns.444In moist Douglas-fir <strong>for</strong>ests, long early seral tree recruitment (e.g., 75 to 100years <strong>for</strong> Douglas-fir) has been documented after disturbance by fire (Franklinand Hemstrom 1981). This pattern is not characteristic of all prehistoric fires.For example, Huff (1984) showed a 60-year recruitment interval <strong>for</strong> a ca. 1465fire in <strong>the</strong> western Olympics, while Yamaguchi (1986) shows that about 95percent of Douglas-fir was recruited within 40 years after a fire in ca. 1300near Mount St. Helens. However, even on <strong>the</strong>se sites <strong>the</strong> regeneration period isdecades long and probably represents some regeneration from trees thatinitially colonized <strong>the</strong> burn and grew large enough to produce viable seed tohelp completely restock <strong>the</strong> stand. Lack of seed source, brush competition,and/or reburns have been identified as factors delaying regeneration on suchsites (Franklin and Hemstrom 1981). Patterns of reburns on <strong>the</strong> Tillamook fireof 1933 at 6-year intervals (1939, 1945, 1951) (Pvne 1982), at Mt. Rainier in<strong>the</strong> late 19th Century, and at <strong>the</strong> sou<strong>the</strong>rn Washington Yacolt burn of 1902(Gray 1990) are evidence <strong>the</strong>se sites will rebum. High surface fire potentialduring early succession in Douglas-fir <strong>for</strong>est was identified by Isaac (1940) as a"vicious cycle" of positive feedback, encouraging rhizomatous bracken fern(Pteridium aqutihnum): this pattern was quantified by Agee and Huff (1987).Given sufficient sources <strong>for</strong> reignition (e.g., <strong>the</strong> original Yacolt and Tillamook

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