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ESTABLISHING WYOMING BIG SAGEBRUSH ON MINED LANDS IN WYOMING' <br />Gerald E. Schuman, Laurel E. Vicklund, and Scott E. Belden' <br />Abstract. Revegetation of mined rangelands in the western U.S. requires that a <br />diverse, self - generating plant community be established that includes native woody <br />shrubs that provide important wildlife habitat. Wyoming Department of <br />Environmental Quality, Land Quality Division, on August 6, 1996, amended their <br />revegetation standards to include a shrub density requirement that had been sought <br />by environmental and wildlife groups for over two decades. This standard requires <br />that 1 shrub m' be re- established on 20% of the disturbed area and that 50% of <br />this density be comprised of the dominant species present before mining. In <br />Wyoming and much of the western rangelands, this typically requires the re- <br />establishment of Wyoming big sagebrush (Artemisia tridentate ssp. <br />wyomingensis). Hence, much research has been accomplished in the last 10 -15 <br />years to develop a better understanding of its seed physiology, seedbed ecology, <br />and to develop cultural practices that will aid in its re- establishment. Research has <br />increased our knowledge in many of these important areas of sagebrush re- <br />establishment ecology and have greatly enhanced our ability to establish big <br />sagebrush by direct seeding; however, climatic factors have a great influence on <br />the success of its re- establishment. The paper also compares the cost of direct <br />seeding compared to transplantation of nursery grown seedlings to meet the shrub <br />density standard and shows that direct seeding costs only a fraction of the cost of <br />transplantation. Further research efforts should be concentrated on further <br />improving direct seeding technology and enhanced production of good quality <br />seed. <br />Additional Key Words: direct seeding, success, cost, transplantation. <br />Introduction <br />Revegetation of mined lands in the western U.S. <br />includes much more than just establishing a perennial <br />grass community to protect the soil resource from <br />erosion. In the past two decades regulatory agencies and <br />environmental groups have spent considerable time and <br />effort to ensure that native shrubs are re- established on <br />Taper presented at the 2001 National Meeting of the <br />American Society for Surface Mining and Reclamation. <br />Albuquerque, New Mexico, June 3 -7, 2001. Pub. by <br />ASSMR 3134 Montavesta Rd., Lexington, KY 40502. <br />'Gerald E. Schuman is Soil Scientist, USDA -ARS, High <br />Plains Grasslands Research Stn., 8408 Hildreth Road, <br />Cheyenne, WY 82009; Laurel E. Vicklund is Senior <br />Environmental Coordinator, RAG Coal West Inc., Belle <br />Ayr Mine, P.O. Box 3039, Gillette, WY 82717; and Scott <br />E. Belden is Senior Environmental Supervisor, Powder <br />River Coal Co., North Antelope/Rochelle Complex, <br />Caller Box 3035, Gillette, WY 82717. <br />by <br />39 <br />mined lands in the Great Plains and Great Basin of the <br />western U.S. These lands must be reclaimed to a diverse, <br />self - generating plant community that includes native <br />woody shrubs that provide important wildlife habitat, as <br />well as livestock forage. In fact, considerable effort, from <br />both a regulatory and environmental standpoint has been <br />aimed at a single species, Wyoming big sagebrush <br />(Artemisia tridentate ssp. wyomingensis). Hence, much <br />research has been undertaken to better understand seed <br />physiology, germination, dormancy, viability, seedbed <br />ecology, and cultural practices for establishment of <br />Wyoming big sagebrush on mined lands. This paper <br />reviews the recent research and uses some of the data to <br />make seeding recommendations and to compare the cost <br />of direct seeding to transplantation of sagebrush to meet <br />the shrub density standard for mined lands in Wyoming. <br />Seed Considerations <br />Wyoming big sagebrush seed is very small, making <br />it difficult to harvest, process and plant. Young and <br />Young (1992) report that there are 3500 -3800 seeds g', <br />