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Opposing Views Attachment #1

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Opposing Views Attachment #1 North Fork Siuslaw LMP Appendix F, Table F-2 (cont.) Appendix F, Table F-2 Continued The following attachments from Dick Artley represent opposing views, with various themes: Attachment 1-timber harvest activities (p. 1), attachment 4-roads (p. 69), attachment 8-fire benefits (p. 125), attachment 9-use of glyphosate (p. 155), attachment 11-wildland-urban fire (p. 259), attachment 15-best science (p. 281), and attachment 18-herbicide label directions (p. 295). All these attachments are included in this document, and are a considered a continuation of Appendix F, Table F-2. After each opposing view in each attachment, a Forest Service (FS) response is included. Opposing Views Attachment #1 Scientists Reveal the Natural Resources in the Forest are Harmed (and some destroyed) by Timber Harvest Activities Note to the Responsible Official who reads these opposing views: There are negative effects caused by nearly all actions … this includes the actions necessary to harvest trees. The public deserves to consider projects proposed to occur on their land with the knowledge of the pros and cons of the project. The Responsible Official will find that none of the literature sources for the opposing views is specific to this project. Information contained in books and/or scientific prediction literature is never specific to individual projects. They describe cause and effects relationships that exist when certain criteria are met … at any location under the vast majority of landscape characteristics. Indeed, the literature in the References section of the draft NEPA document for this project is not specific to the project yet its used to help design this project. The opposing views presented below are not always right or wrong. When responding to opposing views that the Responsible Official believes are “reasonable” please discuss them in the context of this project. In other words, could the resource damage occur as a result of this project. 1 North Fork Siuslaw LMP Appendix F, Table F-2 (cont.) Once again, this gives the public complete project understanding. This allows them to submit meaningful comments. Introduction The following scientific statements describe the natural resources that most likely will sustain damage as a result of timber harvest activities. ----------------------------- Timber Harvest Opposing View #1 - The following document contains pertinent color pictures showing logging damage, thus the article text is not shown here. Please use the link below to access the article. Al-jabber, Jabber M. “Habitat Fragmentation:: Effects and Implications” Clearcuts and forest fragmentation, Willamette NF, Oregon. From: Cascadia Wildland Project, Spring 2003 http://faculty.ksu.edu.sa/a/Documents/Habitat%20Fragmentation%20Effects%20and%2 0Implication.pdf Response: No clear-cutting is proposed. This project proposes thinning (commercial and non- commercial) only in young stands/plantations less than 80 years old (generally 25 to 60 years old) comprised of dense conifer trees (mainly Douglas-fir) that have very little understory vegetation. Thinning and associated actions are designed to speed the development of late-successional and old-growth forest habitats within these stands, which would improve habitat diversity and reduce fragmentation of wildlife habitat in the project area. (Preliminary Analysis (PA), chapter 1, background section). ----------------------------- Timber Harvest Opposing View #2 - “Timber harvest operations have been shown to have many effects on adjacent watercourses and on the aquatic ecosystems they support. This may occur from introductions or loss of woody debris, loss of riparian vegetation, accelerated stream bank and bed erosion, the alteration of natural channel form and process, and the reduction of stream habitat diversity. However, the existing literature 2 North Fork Siuslaw LMP Appendix F, Table F-2 (cont.) indicates one of the most insidious effects of logging is the elevation of sediment loads and increased sedimentation within the drainage basin. Sediment generation from various forestry practices has been studied extensively in the past. Forestry practices which generate suspended sediments include all operations that disturb soil surfaces such as site preparations, clear-cutting, log skidding, yarding, slash burns, heavy equipment operation and road construction and maintenance.” Anderson, P.G. 1996. “Sediment generation from forestry operations and associated effects on aquatic ecosystems” Proceedings of the Forest-Fish Conference: Land Management Practices Affecting Aquatic Ecosystems, May 1-4, 1996, Calgary, Alberta. http://www.alliance-pipeline.com/contentfiles/45____Sediment_generation.pdf Response: Project design criteria (Appendix A), such as no-cut buffers for streams and potentially unstable areas, and restrictions for yarding, roadwork (e.g., new temporary roads would not cross streams), and season of operations are expected to minimize or prevent levels of stream sedimentation that would exceed natural background levels. Please refer to the EA, chapter 3, aquatic habitat and species, and soils and water quality sections; and appendices D and H for additional information. Potential sediment sources mentioned in this paper include stream bank disturbance, in-stream activities, clear cutting and road building. This project does not include any clear cutting no temporary roads are allowed to cross streams. There are streamside buffers to protect stream banks from disturbance. Road maintenance is proposed, but that will reduce the potential to mobilize any sediment that might reach streams ----------------------------- Timber Harvest Opposing View #3 - “Timber harvest will remove dead and dying material from the site and inhibit the recruitment of downed woody material as time progresses. Timber harvest and associated reduced structural complexity and reduced age and size class diversity are all known to reduce population abundance and diversity of ants and a number of birds. For instance, ants are documented to require downed woody material in a variety of sizes and in all stages of decomposition (Torgersen and Bull, 1995). This is an attribute that is negatively correlated with harvest of the dead and dying trees and positively correlated with 3 North Fork Siuslaw LMP Appendix F, Table F-2 (cont.) natural succession, especially after disturbance. Ants and birds are known to predate on insect species which cause mortality to trees, serving as a potentially important population control in the case of epidemics or before they occur (Campbell, Torgersen and Srivastava, 1983). Structural and functional characteristics associated with unlogged forests are also important for canopy arthropods, which play an important role in regulating pest outbreaks (Schowalter, 1989). Structural complexity, functional diversity, diversity of ecological process and diversity of structure in roadless areas are all expected to be less susceptible to the outbreak of pests and regulate insect activity in surrounding homogenized forests (Schowalter and Means, 1989; Franklin, Perry, Schowalter, Harmon, McKee and Spies, 1989). Response: The project proposes to enhance existing poor structural complexity and functional diversity of stands, and ecological processes (EA, chapters 1 and 2). A large body of scientific evidence also indicates that increased edge effect and increased sunlight into stands, resulting from reduced canopy cover associated with timber harvest, can directly promote the population abundance, productivity and persistence of insects which cause mortality to trees of (Roland, 1993; Rothman and Roland, 1998; Kouki, McCullough and Marshall, 1997; Bellinger, Ravlin and McManus, 1989).” “Applying Ecological Principles to Management of the U.S. National Forests” Issues in Ecology Number 6 Spring 2000 http://www.esa.org/science_resources/issues/FileEnglish/issue6.pdf Response: The project proposes to enhance structural complexity, bio-complexity, and species diversity, which would improve functional diversity within stands (PA, chapter 1). No harvesting of existing dead or dying trees is proposed. Dead wood would be created as part of stand treatments. Un-thinned portions of young stands (greater than 50%) and skips/clumps would provide future sources of dead wood (snags and down wood). Plantation thinning has occurred on this forest for several years, with no outbreak of insect infestation. Insect outbreaks are not a major source of forest impacts on the Siuslaw. A project design criterion in Appendix A restricts the timing of the creation of dead wood to minimize any potential insect infestation. 4 North Fork Siuslaw LMP Appendix F, Table F-2 (cont.) The paper focuses primarily on the impacts of clear-cuts. The project does not propose clear-cutting. Canopy cover within plantations would range between 40% and 70% after thinning in the short term. ----------------------------- Timber Harvest Opposing View #4 - “The biggest ecological con job in years is being waged by the U.S. Republican party and their timber industry cronies. They are blaming the recent Western wildfires on environmentalists, and assuring the public that commercial logging will reduce the risk of catastrophic wildfires.” Barry, Glen, Ph.D. “Commercial Logging Caused Wildfires” Published by the Portland Independent Media Center, August 2002. http://portland.indymedia.org/en/2002/08/17464.shtml Response: Reducing wildfire risk through timber harvesting is not practiced on the Siuslaw because large stand-replacing wildfires are
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