Recovery Plan for the Northern Spotted Owl - DRAFT
Recovery Plan for the Northern Spotted Owl - DRAFT Recovery Plan for the Northern Spotted Owl - DRAFT
II. Review of Natural Vegetation and StandDevelopment - History of ForestManagementA. Coastal Forests and Western Cascades ofOregon and WashingtonForests on federal lands in the western Cascades and Coast Range mountainsof Oregon generally are classified in the western hemlock and silver fir zones byFranklin and Dyrness (1973). There is generally plentiful moisture throughoutthese zones, and plant associations range from oxalis and sword fern on moistsites to Douglas-fir, ocean spray, vine maple, and salal on drier sites. Olderstands in these forests often have a well-developed understory of shrubs andhardwoods such as vine maple, yew, bigleaf maple, salal, salmonberry,rhododendron, hazel, ocean spray, and huckleberry. Conifers in the understoryare primarily western hemlock and western red cedar on moist sites.Grand fir and Douglas-fir may occur on dry sites, and silver and noble fir atupper elevations.1. Natural Forest DevelopmentNatural disturbances in these forests occur over a range of sites, frequencies,intensities, and patterns. Under natural conditions, stand replacement firesoccurred at intervals of about 95 years to more than 500 years (Appendix F)with the longer intervals on moist sites. These fires often burned many thousandsof acres. The mortality of the overstory within these extensive bumsvaried considerably (Spies and Franklin 1991, Morrison and Swanson 1990).Groups of trees and scattered individual trees often survived more than onefire. Thus, the Douglas-fir overstory in old-growth forests is often multi-aged(Franklin and Hemstrom 1981). Even with fire suppression, large fires canoccur, for example, the Tillamook bum in the 1930s and the Oxbow fire in the1960s.Wind effects are most severe on ridge tops and near the coast and ColumbiaGorge, although severe storms like the Columbus Day Storm of 1961 causedmajor disturbances on a wide range of sites (Ruth and Harris 1979). Windeffects are often small-scale, blowing down small groups (less than one acre)and individual trees and breaking tops: although entire stands (more than 20acres) may be blown down. Insect populations (bark beetles) often increaseafter fire or blowdown.Root and stem diseases are widespread, but they generally occur on a smallerscale than wind and fire. They slowly kill groups of trees. Over extensive areas,root disease may affect more than 10 percent of the entire area. Other agentsof disturbance include ice storms, which mostly break the tops of stands ofyoung trees, and mass movement such as landslides, which are importantlocally.Individual trees also die because of competition among trees (Drew andFlewelling 1979). Self-thinning is a natural part of stand development andoccurs much more quickly on more productive sites than on poor sites. Rateof self-thinning is dependent on species composition and stand density.492
These factors act together to affect the rate and course of stand development(Spies et al. 1991). For example, natural succession after fire likely wouldresult in a variety of young stands irregularly stocked with conifers, shrubs,and hardwoods, some large green trees not killed by the fire, and often largeaccumulations of snags and down logs from the previous stand (Spies et al.1988). As stand development continued, conifers would dominate parts ofstands and if they are dense enough, shrubs and hardwoods would be excluded(Oliver 1981). In other parts of the stand, conifers would grow in theopen and develop large crowns and branches, and patches of shrubs andhardwoods would remain. After about 80 years, wind, pathogens, and selfthinningwould kill individual overstory conifers and groups of conifers producingopenings, snags, and down logs. Patches of shade-tolerant conifers,hardwoods, and shrubs would grow in the openings (Alaback and Tappeiner1991). Where shrub layers were dense, tree regeneration would be excluded ortime for its establishment greatly extended. This process of disturbances atirregular intervals would continue producing waves of tree and shrub regeneration,snags, and down logs and providing a diverse structure (Spies andFranklin 1991, Spies et al. 1988, Spies et al. 1990).Natural disturbances to forest stands vary in intensity, distribution, frequency,and size. Viewed in the context of the home range of an owl (about 3,000acres, for example) these disturbances may be extremely small (a 0.05-acreopening, less than 0.0002 percent of a home range) or they could include theentire home ranges of one to many spotted owls.2. Forest Management and Stand DevelopmentWhile timber harvest on private lands began in the late 1800s, major timberharvest programs by the Forest Service and BLM started about 1945 to 1950.Due to concerns for road access, logging methods, watershed impacts, andproviding edge for elk and deer, 'patch cutting" (usually more than 20 acres)was used; that is, stands scattered throughout a watershed were clear-cut andplanted. Since harvesting on federal lands began about 40 years ago, today inmost watersheds young stands are usually 0 to 40 years of age, and there arenatural stands of large old trees. Thus, today there is a strongly bimodal agedistribution between managed and unmanaged stands. In addition, there aresome natural stands of intermediate ages resulting from fire, wind, and earlierharvesting. Harvest by thinning in some areas also has occurred in the last 20to 30 years.Treatments to establish plantations following clear-cutting or fire have tendedto alter secondary succession to ensure well-stocked conifer stands. Thecourse of forest succession following fire or harvesting of mature or old forestsvaries depending upon severity of disturbance, composition of preharvestvegetation, site conditions, availability of conifer seeds, and animal populationlevels. In most situations, if Douglas-fir seed is not available in sufficientquantities immediately after harvest, tree regeneration is slow and irregularand generally unacceptable in terms of meeting wood production objectives.Because of this long, natural regeneration period, most sites are planted assoon after harvesting as possible. To reduce growth of broad-leaved trees,shrubs, and herbs, some type of site preparation (fire, mechanical, chemical) isdone following harvesting and before planting. Planting often is followed bysome treatment that reduces density and vigor of nonconiferous vegetation.The purpose of these practices is to obtain a uniform conifer stand and quicklyachieve conifer crown closure thereby shortening the period of dominance bynonconifers. Stocking control is important for obtaining correct stand structure.Precommercial thinning is done often in 10- to 20-year-old stands toensure uniform conifer spacing and control density of conifers and hardwoods.This is especially necessary on coastal sites where natural regeneration of493
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II. Review of Natural Vegetation and StandDevelopment - History of ForestManagementA. Coastal Forests and Western Cascades ofOregon and WashingtonForests on federal lands in <strong>the</strong> western Cascades and Coast Range mountainsof Oregon generally are classified in <strong>the</strong> western hemlock and silver fir zones byFranklin and Dyrness (1973). There is generally plentiful moisture throughout<strong>the</strong>se zones, and plant associations range from oxalis and sword fern on moistsites to Douglas-fir, ocean spray, vine maple, and salal on drier sites. Olderstands in <strong>the</strong>se <strong>for</strong>ests often have a well-developed understory of shrubs andhardwoods such as vine maple, yew, bigleaf maple, salal, salmonberry,rhododendron, hazel, ocean spray, and huckleberry. Conifers in <strong>the</strong> understoryare primarily western hemlock and western red cedar on moist sites.Grand fir and Douglas-fir may occur on dry sites, and silver and noble fir atupper elevations.1. Natural Forest DevelopmentNatural disturbances in <strong>the</strong>se <strong>for</strong>ests occur over a range of sites, frequencies,intensities, and patterns. Under natural conditions, stand replacement firesoccurred at intervals of about 95 years to more than 500 years (Appendix F)with <strong>the</strong> longer intervals on moist sites. These fires often burned many thousandsof acres. The mortality of <strong>the</strong> overstory within <strong>the</strong>se extensive bumsvaried considerably (Spies and Franklin 1991, Morrison and Swanson 1990).Groups of trees and scattered individual trees often survived more than onefire. Thus, <strong>the</strong> Douglas-fir overstory in old-growth <strong>for</strong>ests is often multi-aged(Franklin and Hemstrom 1981). Even with fire suppression, large fires canoccur, <strong>for</strong> example, <strong>the</strong> Tillamook bum in <strong>the</strong> 1930s and <strong>the</strong> Oxbow fire in <strong>the</strong>1960s.Wind effects are most severe on ridge tops and near <strong>the</strong> coast and ColumbiaGorge, although severe storms like <strong>the</strong> Columbus Day Storm of 1961 causedmajor disturbances on a wide range of sites (Ruth and Harris 1979). Windeffects are often small-scale, blowing down small groups (less than one acre)and individual trees and breaking tops: although entire stands (more than 20acres) may be blown down. Insect populations (bark beetles) often increaseafter fire or blowdown.Root and stem diseases are widespread, but <strong>the</strong>y generally occur on a smallerscale than wind and fire. They slowly kill groups of trees. Over extensive areas,root disease may affect more than 10 percent of <strong>the</strong> entire area. O<strong>the</strong>r agentsof disturbance include ice storms, which mostly break <strong>the</strong> tops of stands ofyoung trees, and mass movement such as landslides, which are importantlocally.Individual trees also die because of competition among trees (Drew andFlewelling 1979). Self-thinning is a natural part of stand development andoccurs much more quickly on more productive sites than on poor sites. Rateof self-thinning is dependent on species composition and stand density.492