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<br />grams to recover indigenous trout, enhance wildtrout fisheries, and operate hatcheries <br />for recreational fishing waters. Assessments linked to conservation strategies and plans <br />will help both state and federal agencies to work as partners in joint fisheries and habitat <br />management programs (URMCC 1995). <br /> <br />3. Habitat protection through agency stewardship and decision making is essential to <br />maintain existing populations in occupied habitats. Since streams follow no .political. <br />boundary, agencies need to coordinate basin-wide strategies and programs. An eco- <br />system approach must be taken to protect and maintain aquatic biodiversity and viable <br />populations. Interstate, as well as in-state agency coordination is necessary, as is <br />agency accountability in decision-making. Since most existing BCT populations are <br />found in small, headwater streams on National Forests, including wilderness and road- <br />less areas, it is incumbent on the Forest Service to judiciously restrict land use activities <br />that may pose habitat disruption and loss, or tend to place the populations further at <br />risk. Protection of BCT populations in the future will primarily be dependent on federal <br />agency management for healthy aquatic ecosystems, i.e. stable watershed soils, rooted <br />terrestrial and riparian vegetation, and clean water (quality and quantity). <br /> <br />4. Regulatory mechanisms need to be employed where necessary, to ensure population <br />protection and genetic integrity. Stream closures, total or partial, as well as harvest <br />regulations as developed by the States need to be considered and implemented, where <br />necessary. Both population and habitat specific area relationships need to be reviewed <br />and jointly agreed upon by state and federal managers. This will ensure BCT protection, <br />especially where access, facilities, and user pressure are viewed as possible risks to the <br />subspecies. <br /> <br />B) ENHANCEMENT <br /> <br />Agency emphasis should be toward providing management activities and decisions that provide <br />habitat enhancement so as to ensure long-term maintenance of reliable pure populations. Conserva- <br />tion enhancement should require maintenance of multiple local or sub-basin populations. Overall <br />ecosystem sub-basin health is important to proper aquatic ecosystem function and processes. Any <br />activities which allow habitat disruption and/or fragmentation that threatens the diversity, stability, and <br />persistence of pure populations should not be allowed. Management decisions made on the basis <br />of phylogeographic interpretation of extant patterns of biological diversity will both promote and <br />protect natural processes which have and will continue to mold the genetics of pure cutthroat <br />populations. <br /> <br />1. Within each geographic area, or major sub-basin occupied by pure populations repre- <br />sentative core areas should be selected to provide long-term healthy habitats and <br />strong populations. The highest priority areas for providing critical components in <br />aquatic ecosystems would be either wilderness and roadless areas, followed by remote, <br />limited activity areas so as not to compromise the pure population. Areas so designated <br />would provide a cornerstone for maintaining the biological diversity of the sub-basin <br />ecosystem. Such areas could be designated as genetic reserves or preserves and <br />incorporated within Forest Plans as special interest areas (SIA's), i.e. Zoological, or <br />research natural areas (RNA's). <br /> <br />2. Maintenance of pure populations, within sub-basins may require removal of non-native <br />or exotic species which threaten or place at risk the continued existence of the cutthroat <br />trout. This may be necessary within the sub-basins in which pure populations occupy <br /> <br />54 <br />