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Table 1. Estimates of costs per Wyoming big sagebrush seedling and values in ( ) represent the cost per hectare to <br />establish 2000 seedlings. <br />Sagebrush <br />sdlgs m 2 <br />1.32' 2.36 <br />2.48 4.43 <br />$100 <br />meet the shrub standard. If we were to use the present <br />day estimated costs of transplantation (Kleinman and <br />Richmond 2000) with 100% survival, direct seeding <br />would only cost 2.4% of the cost of transplantation. <br />The authors realize that seed availability and cost <br />may become a significant consideration in meeting the <br />shrub standard on mined lands in Wyoming where <br />Wyoming big sagebrush is the required species in most <br />situations, but we believe that economics will remain the <br />driving force behind the decisions made by the industry <br />and regulatory personnel in determining the option used <br />in establishing this shrub on mined lands. Seed use <br />efficiency might be much better with nursery grown <br />seedlings, but costs will likely dictate the use of direct <br />seeding and over -ride the seed - use - efficiency <br />concerns/considerations. Demand for native shrub seed <br />will result in improved seed collection and processing <br />and improved cultural practices for orchard production of <br />these species. In fact, local producers have recently <br />begun producing Wyoming big sagebrush under seed <br />orchard conditions (Richard Dunne, personal <br />communication, 1999) to more consistently meet the <br />demand for good quality seed. There may be briefperiods <br />of seed shortages but demand will greatly aid in the <br />development of seed production and in direct seeding <br />practices. Even considering the vast differences in cost <br />between direct seeding vs transplantation, there may be <br />small, site specific areas and instances where the use of <br />nursery grown transplantation might be used to meet a <br />very specialized objective. But it is difficult to visualize <br />transplantation being used to meet the shrub standard in <br />general reclamation practices considering the several <br />44 <br />Seed Cost kg' PLS <br />$200 <br />Survival Rate <br />Cost seedling' (cost ha'') <br />$300 <br />$0.015 $0.008 $0.030 $0.019 $0.045 $0.025 <br />($30) ($17) ($60) ($34) ($90) ($51) <br />$0.016 $0.009 $0.032 $0.018 $0.048 $0.027 <br />($32) ($18) ($64) ($36) ($96) ($54) <br />' These sagebrush seedling densities represent 33 and 59% survival of the densities measured (4.0 seedlings m by <br />Fortier (2000) at the sagebrush seeding rate of 2 kg PLS ha'' and 8 kg PLS ha'' grass seeding rate. b These sagebrush <br />seedling densities (seedlings m) represent 33 and 59% survival of the density (7.5 seedlings m) measured by Fortier <br />(2000) at the sagebrush seeding rate of 4 kg PLS ha' and 8 kg PLS ha' grass seeding rate. Cost per hectare values are <br />rounded to the nearest full dollar. <br />magnitude difference in costs which will not be easily <br />overcome even with major advances in transplantation <br />technology. <br />Summary <br />Much research has been accomplished within the <br />last three decades in attempting to better understand the <br />ecology of Wyoming big sagebrush establishment on <br />mined lands. The interest in this subject was even <br />further raised when the Wyoming Department of <br />Environmental Quality, Land Quality Division <br />established shrub density re- establishment requirements <br />for lands affected after August 6, 1996. This standard <br />requires that a density of 1 shrub m' be re- established on <br />20% of the land area affected and that 50% of the density <br />must be composed of the predominant shrub prior to <br />disturbance. Since Wyoming big sagebrush is widely <br />distributed over Wyoming, that means that it will likely <br />be a major component of the pre -mine plant community <br />and therefore must be re- established on 20% of all coal <br />mined lands to meet the shrub standard. In fact, all lands <br />classified as "grazing/wildlife habitat" must have a shrub <br />component on the other 80% of the reclaimed land, but <br />no specific density is required. Much recent research has <br />been done to better understand the seedbed ecology and <br />seed ecology to enhance establishment of this species <br />from direct seedings. This research has resulted in a <br />better understanding of the role of mulches, topsoil <br />quality, competition, arbuscular mycorrhiza, and seed <br />viability and how these factors can be managed to greatly <br />improve seedling establishment through direct seeding. <br />At today's technology and economics direct seeding is <br />