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include identifying areas for acquisition or special management <br /> designations, applying integrated weed control and vegetation management, <br /> assuring that hydrologic requirements are met and that proposed projects <br /> will not compromise them, managing grazing to avoid impacts during <br /> sensitive times of the year (during flowering and fruit set) , and managing <br /> recreation and other activities to avoid trampling, compaction, and other <br /> adverse impacts to habitat. Some type of population and habitat <br /> monitoring should be initiated in each watershed until such time as a <br /> complete monitoring plan is designed and implemented. <br /> 3. Identify, protect, and manage populations in disjunct habitats. Watershed <br /> ID Teams will be focusing their attention on recovery of the orchid in <br /> habitats created and maintained by natural hydrologic systems. However, <br /> occurrences of the orchid outside of those areas must be protected and <br /> managed as well . Recovery actions should include acquisition, special <br /> land management designations, and management agreements to manage habitat, <br /> securing water rights or negotiating quantities and timing of flow (e.g. , <br /> from irrigation systems) , and vegetation, grazing, and recreation <br /> management. Population and habitat monitoring should also be conducted. <br /> 4. Develop orchid population and habitat recovery goals and delisting <br /> criteria. Watershed ID Teams will make recommendations for orchid <br /> population sizes and distribution and habitat conditions that should be <br /> attained within the watershed for recovery and delisting of the orchid. <br /> These recommended recovery goals for each watershed will need to be <br /> integrated with each other and incorporated into overall recovery goals <br /> and delisting criteria for the orchid throughout its range. <br /> 5. Inventory remaining potential habitat. Recent discoveries of the orchid <br /> have extended its known range northward to include the North Platte River <br /> drainage in Wyoming and areas between there and Colorado Springs along the <br /> Front Range of Colorado (See Figure 1 for locations of known and <br /> historical occurrences) . Recovery of the orchid cannot be complete until <br /> the full range and habitat preferences of the orchid are understood and <br /> the genetic and ecological relationships within and between populations <br /> elucidated. Priority areas for additional inventory include: the <br /> headwaters of the North Platte River, the Laramie Basin, and the upper <br /> Green River and its tributaries in Wyoming; drainages along the Front <br /> Range north of Boulder, Colorado, including within the Pawnee National <br /> Grasslands; along the Green River and its tributaries between Brown's Park <br /> (in Colorado and Utah) and Jensen, Utah; and portions of the Colorado <br /> River and its tributaries in Colorado and Utah. Drainages, seeps, and <br /> springs in the eastern Great Basin of Utah and Nevada should also be <br /> inventoried, especially since an historical location at Willow Springs in <br /> far western Utah was recently reconfirmed. <br /> 6. Conduct genetic, life history, ecology, and habitat management studies. <br /> In order to assess and maintain the full genetic variability inherent in <br /> this species, know how to establish and maintain minimum viable <br /> populations, and understand how to assess and manage orchid habitat, <br /> genetic, population biology, ecology, and habitat management studies are <br /> necessary. <br /> 31 <br />