This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. Integration of Riparian Systems Management Strategies Within the Context of Multiple Use Land Management Programs in Southwestern Wyoming 1 Donald H. Swee~2, J.M. Zilincar3, Bruce H. Smith ,Rodd V. Hardy3 The extent of multiple use activities on public lands in southwest Wyoming place significant pressure on riparian ecosystems. Our experience indicates that by using an integrated, interdisciplinary management approach, it is possible to maintain existing healthy riparian habitat, and improve or recover lost habitat. INTRODUCTION The Rock Springs District of the Bureau of Land Management manages about 6 million acres of public lands in southwest Wyoming. TABLE 1 Riparian Habitat Condition (%) The District is predominately a sagebrush steppe, a high cold desert ranging from 6,000 feet to 9,500 feet in elevation, with an average precipitation of 8 to 12 inches a year. Good Fair Poor 16 46 32 Virtually None 6 Table 2 (Smith 1978) illustrates the trends of the same 607 stream miles of riparian habitat surveyed in the Rock Springs District. District-wide stream habitat surveys have found 1,700 miles of perennial and ephemeral streams on public lands which drain into five major river systems. Watersheds feeding these streams are typically sedimentary basin deposits, predominately sandy in nature. Riparian ecosystems within the district comprise less than 1 percent of the landscape and cross a full spectrum from montane, foothills, desert, and river bottom communities. TABLE 2 Riparian Habitat Trends (%) Good Stable Declining Table 1 (Smith 1978) illustrates conditions of 607 stream miles of riparian habitat surveyed in the Rock Springs District. 42 58 Fair 15 85 Poor 94 6 While 62 percent of the inventoried riparian systems were found to be in fair to good condition, many of these areas were in a declining trend. Good potential for improvement and possible recovery of lost habitat in the 32 percent of riparian systems in poor condition was identified. lpaper presented at the Riparian Ecosystem Management Conference. (University of Arizona, Tucson, April 16-18,1985). A slide show accompanying this paper is available from the address below. 2Donald H. Sweep is the District Manager, Rock Springs District, Bureau of Land Management, U.S. Department of the Interior, P.O. Box 1869, Rock Springs, Wyoming 82902-1869. 3J.M. Zilincar, Public Affairs Officer; Bruce H. Smith, Wildlife Biologist; and Rodd V. Hardy, Range Conservationist. Rock Springs District, Bureau of Land Management, U.S. Department of the Interior, P.O. Box 1869, Rock Springs, Wyoming 82902-1869. The BLM is specifically directed in its Organic Act, the Federal Land Policy and Management Act (FLPMA 1976), to manage the land it administers " ... on the basis of multiple use and sustained yield ••. ". Multiple use management in the BLM recognizes the interrelationships between scientific disciplines and attempts to make full use of the expertise of each discipline in a coordinated 371 attempt to meet specific resource management requirements. improve water quality and habitat. Some of these measures include tree plantings, the use of beavers, placement of gabions, and proper design of road crossings. Since introduction at two sites, beavers have improved the ecological condition of some riparian areas. Aspen and other reinforcing material have been trucked into some sites for use by the planted beaver to reinforce their dams. These dams have raised the water table, reestablished a floodplain, and enhanced riparian vegetation recovery. The multiple use approach is carried out through the Bureau's planning system. Management proposals are open to public review and based on data obtained from field surveys. After broad decisions are reached, activity plans are developed to address specific locations. An example of this is our development of a Rock Springs District Riparian Management Policy (Sweep 1984), which outlines management strategiesfor riparian habitat within all our various programs. Over the past six years, this process has provided the framework for development of numerous riparian projects, studies, special management areas, and broader changes in land management practices. The White Acorn Allotment is located about 67 miles north of Rock Springs. This allotment was part of an area which, in the late 1800's and early 1900's, was heavily gra~ed by sheep but today is used by both cattle and sheep. This 48,000 acre allotment was created in 1969. Ten years later an allotment management plan was written after the Big Sandy Grazing EIS was completed. Before the allotment management plan, several exclosures were proposed as grazing mitigation for favorable riparian management. RIPARIAN MANAGEMENT IN THE ROCK SPRINGS DISTRICT To successfully manage riparian lands, and to restore damaged habitat to potential productivity, a total, ecosystem approach is needed. Depending on the requirements of a specific site, various management techniques may be needed. A total view of the riparian ecosystem will combine specific management efforts into a coordinated approach with appropriate treatments for specific sites, with an overall goal of increased riparian productivity. The most productive forage areas are the subirrigated range sites which are found along perennial streams and in tributary drainages. These subirrigated range sites also make up about four percent of the allotment and occur primarily on private lands. The overall goal of this AMP is the maintenance or improvement of the rangeland through grazing management. Riparian range sites, because of their great value for many uses, are considered to be of utmost importance for maintenance or improvement in rangeland condition. Six pastures have been created. The three most northern pastures are in a rest rotation grazing system. The three southern pastures have been placed in a deferred rotation grazing system. Use of the riparian range sites has been about 55 to 65 percent of the herbaceous species. Willows and other shrub use has been light and upland sites have been used considerably less. Use of grasses in big sage brush communities within one mile of water during 1982 and 1983 was only 15 to 35 percent. For example, a few small riparian monitoring exclosures provided us with specific information that established response or recovery time and site potentials. This information was then used to expand these findings into larger riparian special management units, in which special management techniques, trial grazing systems, or habitat enhancement measures could be tested. To date, these monitoring and special management units number about 60 district-wide, and are providing the basis for our next step into full scale riparian management on a broad basis. Our Huff Creek and Little Muddy Creek monitoring units help to illustrate stream stabilization and recovery under complete rest from livestock grazing. Along with this habitat recovery, Wyoming Game and Fish Department cooperative monitoring has observed an 182 percent improvement in numbers of fish per mile and 334 percent increase in weight of the rare Bonneville cutthroat trout, a candidate species for threatened status designation. The permittee is pleased with the resulting improved vegetation and increased livestock productivity. In the Bone Draw special management unit, consisting of four large riparian exclosures, a riparian habitat was also improved and perennial flows were extended. Stocking assistance from the Wyoming Game and Fish Department and public participation have helped create a nursery area on the Big Sandy River. This has created a nucleus for the development of a seasonal run of rainbow and brown trout up the Big Sandy River, providing a new source of recreation. However, we prefer to manage riparian areas by the use of a rest rotation or deferred grazing system rather than fencing off riparian areas. Fencing off extensive riparian areas is expensive and the cost of annual fence maintenance would be prohibitive. Designing and implementing habitat management plans (HMP) to improve riparian habitat has also proved useful in certain areas. The Thomas Fork and East Front HMPs, designed to improve stream habitat and benefit two rare subspecies of Some riparian areas that are depleted due to past misuse received intensive management. The key is to first stabilize the riparian area by encouraging shrubs and other vegetation growth to 372 '. the cutthroat trout, date back to the late 1970's. improving one. The Red Creek Watershed Management Plan was completed in 1982. This plan was designed to reduce siltation, provide fisheries habitat, and stabilize stream banks by promoting riparian vegetation recovery. Riparian areas will continue to be managed for multiple use. Use will be controlled in a way not to impair the riparian ecosystem. Livestock grazing will continue, but not in a manner to cause harm to the vegetation-watersoil riparian resources. Using grazing systems as a way to improve riparian areas will be encouraged instead of using fenced exclosures. A major objective is to work with, and show the benefits of, sound riparian management to livestock operators and other users of, the public lands and elicit their cooperation. Emphasis is on a total ecosystem rather than scattered sites, with the goal of returning entire watersheds to productivity. This will continue through the multiple-use planning system, open to public view, that the Bureau uses, and with the interdisciplinary approach we are expanding upon in the Rock Springs District. Some of the major pressures on riparian habitat in southwest Wyoming result from energy and mineral development. To mitigate these pressures, we are minimizing surface runoff and accelerated erosion effects on drainage hydrology, and crossing streams with small prefab metal bridges or open bottom culverts to prevent accelerated stream flows, gully cutting, and a lowered water table, which would eliminate riparian habitat. In addition to minimizing adverse impacts, recovery of riparian habitat in poor condition can also be achieved. This can take many forms, including construction of riparian meadow forming structures such as trash catchers or gabions in ephemeral drainages, and the opening of wet meadow riparian sites through the use of pothole developments in order to improve habitat diversity and productivity. Direct planting of lost riparian canopy trees or shrubs is another means being employed in an effort to reestablish not only the condition of riparian habitats, but their structure and function as well. ACKNOWLEDGMENTS The authors express their appreciation to the Rock Springs District Resource Area Managers and their staff for their Riparian Management programs which provided the basis for this paper. LITERATURE CITED Smith, B. 1978. Completion Report, Rock Springs District Stream Survey, 1975-1977. BLM Rock Springs, Wyoming, U.S. Department of the Interior. FLMPA 1976. Public Law 94-579 October 21, 1976, 90 STAT. 2743, Federal Land Policy and Management Act of 1976. Sweep, Donald H. 1984. Instruction Memorandum No. WY-04-84-136, Rock Springs District Riparian Management and Monitoring Program. BLM Rock Springs, Wyoming, U.S. Department of the Interior. A CONTINUING CHALLENGE The process we are beginning is, of necessity, a long-term one. Riparian habitat in southwest Wyoming did not decline overnight, but over the course of decades of misuse; and will not fully recover overnight. The direction of riparian habitat is turning, slowly, from a declining condition to an 373