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Last modified
7/29/2009 9:46:00 PM
Creation date
10/12/2006 3:45:47 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8027
Description
Section D General Correspondence - Federal Agencies (Alpha, not Basin Related)
Date
12/6/2002
Author
USDA Forest Service
Title
RMP - Proposed Rules - Federal Register - Part III - 36 CFR Part 219 - National Forest System Land and Resource Management Planning: Proposed Rules
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<br />., <br /> <br />Ul1l113J <br /> <br />Federal Register / Vol. 67, No, 235/ Friday, December 6, 2002/ Proposed Rules <br /> <br />72785 <br /> <br />promote the recOI.'ery of federally listed <br />threatened and endangered species. <br />provide for implementing conservation <br />agreements, and address requirements <br />and recommendations from biological <br />opinions. These requirements are not <br />included under either Option 1 or <br />Option 2 or the proposed rule. The <br />agency reaffirms its commitment to <br />comply with provisions of the <br />Endangered Species Act (ESA), <br />includmg conducting programs for the <br />conservation of endangered and <br />threatened species consistent with the <br />multiple use objectives of plans. but <br />sees no reason to specify this in the rule <br />itself. The ESA is among the relevant <br />statutes listed under 219.2(c)(1). <br />Following adoplion of a final new <br />planning rule, and contingent on which <br />diversity option is selected, the agency <br />fully intends to develop detailed <br />operational guidance on the means to <br />implement the procedural requirements <br />of the new planning rule, particularly <br />with reference to procedures for meeting <br />the NFr...1A diversity requirement. This <br />will include detailed guidance in the <br />agency Directive System, as well as <br />"white papers" and other documents. <br /> <br />Option 7-'i219,13(b) Ecological <br />Component of Sustainability <br /> <br />Option 1 of the proposed rule is most <br />similar to corresponding sections on <br />ecological sustainability in the 2000 <br />rule. In fact. Option 1 was developed <br />from the 2000 rule by significantly <br />streamlining the rule and eliminating <br />significant amounts of procedural detail, <br />as discussed earlier in this preamble. In <br />this option, plan decisions would be <br />developed to provide a high likelihood <br />of supporting, over time, the viability of <br />native and desired non-native <br />vertebrates and vascular plants well <br />distributed within their ranges in the <br />plan area. This viability standard serves <br />as the primary basis for judging <br />achievement of the NFMA diversity <br />requirement in Option 1. This option <br />also contains an ecosystem diversity <br />standard, so that plan decisions would <br />be developed to provide measurable <br />progress toward maintenance or <br />restoration of ecological conditions that <br />support the desired characteristics of <br />ecosystem diversity. However. it is the <br />species viability standard that will <br />provide the clearest measure of <br />achievement of the NFMA diversity <br />requirement under Option 1. <br />Under this option of the proposed <br />rule, analysis of the ecological <br />component of sustainability follows a <br />hierarchical. sequential approach. This <br />option requires ecosystem diversity to <br />be evaluated first, with the goal of <br />ensuring that plan decisions provide <br /> <br />measurable progress toward maintaining <br />or restoring ecological conditions that <br />support the diversity of plant and <br />animal communities and tree species. <br />and other characteristics of ecosystem <br />diversity. Species diversity wouid be <br />evaluated only after consideration of <br />ecosystem diversity. This hierarchical, <br />sequential approach is based on the <br />assumption that conditions capable of <br />supporting viability for most species are <br />likely to be met through provisions for <br />ecosystem diversity. Where this LS not <br />the case, species at risk would be <br />identified and separate analyses of <br />species diversity performed. This <br />approach provides the Responsible <br />Official flexible options for meeting the <br />analytical requirements of Option 1 as <br />the Responsible Official determines the <br />scope and scale of the analysis. There <br />are some required characteristics of <br />ecosystem and species diversity and <br />accompanying evaluation factors, <br />although far fewer than in the 2000 rule. <br />The Responsible Official is not limited <br />to only those characteristics or <br />analytical processes if other information <br />or techniques are available or <br />appropriate. <br />The desired conditions, objectives. <br />standards, identification of suitable and <br />unsuitable land uses, and any special <br />designations and other management <br />areas of fl plfln should provide the <br />framework for management that would <br />maintain or restore ecological <br />conditions that the Responsible Official <br />determines will provide a high <br />likelihood of supporting, over time, the <br />viability of native and desired non- <br />native vertebrates and vascular plants <br />well distributed within their ranges in <br />the plan area. Note that "high <br />likelihood" is not necessarily a <br />statistical or mathematical <br />determination. Rather, it is an <br />application of expert agency judgment <br />based on a reasonable review and <br />consideration of available information. <br /> <br />Option 2-fi279, 13(b) Ecological <br />Component of Sustainability <br /> <br />The second option for addressing the <br />ecological component of sustainability <br />was developed initially by agency <br />research scientists to provide a clear and <br />distinct alternative to Option 1. Several <br />specific objectives or perspectives <br />inOucnced development of Option 2. <br />including: (1) Focus required ecological <br />analyses. as well as the final <br />management standard against which <br />plan decisions are to be judged, at both <br />ecosystem and species levels of <br />ecological organization: (2) require <br />analyses of diversity across multiple <br />geographic areas and timeframes, and <br />especially stress the importance of <br /> <br />analyses conducted over large <br />geographic areas or long timeframes; (3) <br />emphasize the inl1uence of the <br />ecological condition. structure, and land <br />use history of the surrounding <br />landscape, as well as of natural and <br />human-induced disturbance regimes, on <br />the ability to manage NFS lands to <br />achieve biological diversity objectives: <br />and (4) require a more rigorous and <br />structured set of analyses of diversity <br />than contained in Option 1. <br />Option 2 focuses attention on the <br />general objective of maintaining and <br />restoring ecological conditions that <br />provide for biological diversity in the <br />plan area and on the more specific <br />objective of maintaining and restoring <br />ecosystem diversity within landscapes, <br />and within the framework of larger-scale <br />ecosystem analyses, of maintaining and <br />restoring species diversity within <br />ecosystems. In this sense. Option 2 <br />adopts an explicitly hierarchical <br />approach to analyses of biological <br />diversity. as does Option 1. <br />Option 2 focuses allention directly 011 <br />evaluating and maintaining biological <br />diversity in the planning or assessment <br />area. Biological diversity is an inclusive <br />concept employed in the scientific and <br />conservation literature to refer to the <br />variety of living things together with <br />their interactions and processes. It is <br />defined at various levels of ecological <br />organization, but especially three- <br />genes. species, and ecosystems. The <br />general concept of biological diversity <br />incorporates the concept of the diversity <br />of plant and animal communities and <br />tree species as originally used in the <br />language of the NFMA diversity <br />requirement. However, the term <br />"biological diversity" also reflects <br />significant progress in the sciences of <br />ecology and conservation biology over <br />the past 20-25 years. Scientific progress <br />in these fields has revealed substantial <br />new information such as factors that <br />regulate biological diversity and the <br />relationship between biological <br />diversity and ecosystem function and <br />resilience. As a consequence, and <br />consistent with progress in scientific <br />knowledge and conservation practice, <br />the overriding objective ofthEl approach <br />in Option 2 is to focus planning <br />analyses on factors that foster the <br />maintenance and restoration of <br />biological diversity in the planning or <br />assessment area, at both ecosystem and <br />species levels of ecological organization, <br />Option 2 directs the Responsible <br />Official. in the planning process. to <br />follow and fully disclose results of a <br />structured approach to considering and <br />assessing biological diversity at two <br />levels of ecological organization: <br />ecosystem and species. Analyses of <br />
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