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products from litter than negatively influence plant growth. Work in New Mexico, by Fowler and Witte (1987), on plots dominated by One -seed Juniper and Pinyon Pine, the plots were thinned on the basis of 0, 33, 67 and 100 percent of the net crown cover. Five years after thinning the total herbaceous forage production averaged 471, 234, 2,536 and 7,913 pounds of air -dry forage per acre. Summarizing the results of the previous 10 years of new research on the interaction of herbage production and grazing on the Pinyon- Juniper type conversion projects, Clary (1987) summarized six studies, covering dozens of sites performed on grazed sites, that prior to tree removal, the average production was 278 pounds per acre, after tree removal production averaged 525 pounds per acre. Across all grazed sites an average increase of 729 pounds per acre of useable forage was realized. On ungrazed sites, Clary (1987) summarized three studies showing that prior to treatment, the average forage production was 333 pounds per acre, while after treatment the production averaged 666 pounds per acre. Across all grazed sites, the average post treatment useable forage production increased 999 pounds per acre. Revegetation of the Pinyon- Juniper type in the Western states was summarized by Johnsen (1987), who reported that in addition to the normal issues associated with reseeding, the Pinyon - Juniper vegetation type was unique in that Juniper litter reduces the surface soil wetability under the tree canopy, markedly reducing water infiltration. Soils under One -seed Juniper did not wet as deeply as soils in the interspaces between the trees, which could potentially delay or prevent the seedling establishment of other plant species. He also reported that the tree canopy intercepted between 3 to 34 percent of the rainfall. The burning of the Juniper slash after tree removal sometimes left the soil bare for several years and was possibly the result of organic compounds in the Juniper slash which were vaporized during the burning process. Woody Plants Recommended for Use in Coal Mine Reclamation and Wildlife Plantings in Southeastern Colorado. In an early evaluation of the plant species useful in revegetating disturbed lands in the west, Wasser (1982), provided information on the use of 98 total species, including 26 different shrubs and 25 different trees considered to be "important and commonly used for stabilizing and reclaiming surface mined and other disturbed lands" in the Western United States. Among the shrubs considered suitable for plant for coal mine revegetation and which were either encountered in the sampling of the shrub density transects or observed at the Southfield Mine, were included: Big sagebrush, Fourwing Saltbush, True Mountain Mahogany, Curlleaf Mountain Mahogany, Rubber Rabbitbrush, Douglas Rabbitbrush, Antelope Bitterbrush, Skunkbush Sumac and Western Snowberry. Trees included Rocky Mountain juniper, One -seed Juniper and Ponderosa pine. Woody plants recommended for mined land reclamation in Colorado were made by Office of Surface Mining Reclamation and Enforcement (198 8) who reported that of the species of trees or shrubs suitable for planting in Colorado for Colorado Major Land Use Resource Areas (MLRA) which include MLRA -69 corresponding to the Upper Arkansas Valley Rolling Plains area, where the Southfield Mine is located include: Fourwing saltbush. Rubber Rabbitbrush, Russian- 7