Laserfiche WebLink
6 <br />With exception of the Cordero and Big Sky plots, one plot was constructed at <br />each mine. Replicated plots were constructed at the Cordero mine, and two plots, <br />one using overburden spoil and a second using interburden spoil, were constructed <br />at the Big Sky mine. Replicated plots were also constructed at the Belle Ayr <br />mine in the fall of 1980, but at the time of writing this report, there were <br />essentially no data available from these plots. <br />SEEDBED PREPARATION <br />Prior to cultural operations, a sample of spoil and one of soil were taken <br />from each plot, placed in a cloth bag, and air dried. In the laboratory, these <br />samples were sieved to remove particles larger than 2 mm in diameter, and, <br />for certain laboratory analyses, portions were ground to a nominal 150 mesh <br />(0.105 mm). The samples were then analyzed using standard agronomic methods as <br />described in Appendix A. <br />Each plot was fertilized with N and P immediately preceding seeding; reclam- <br />ation research has demonstrated that N and P fertilizer increase both aboveground <br />and belowground biomass (Holechek et al., 1981). For those plots located north <br />of Gillette, Wyoming, 3 kg of superphosphate (equivalent to 130 lb P /acre) and <br />'3 kg of ammonium nitrate (equivalent to 95 lb N /acre) were applied to each plot. <br />Due to the possibility of increasing the osmotic stress to an undesirable level, <br />the rate of N fertilizer application was reduced to 1.5 kg per plot (equivalent <br />to 47 lb N /acre) for those plots south of Gillette. The rate of P application <br />was not changed for these plots. <br />The fertilizer was broadcast on the surface and rototilled into the surface <br />15 cm of soil or spoil. However, when soil depth was less than 15 cm, the fer- <br />tilizer was raked into the soil to a depth of 3 to 8 cm. <br />Each plot was then raked and large clods and rocks that would interfere <br />with planting were removed. A roller weighing approximately 40 kg was pulled <br />across the plot to produce a firm seedbed. <br />SEEDING <br />The five different species of perennial grasses used in this experiment are <br />as follows: <br />Common Name <br />Crested Wheatgrass <br />Pubescent Wheatgrass <br />Thickspike Wheatgrass <br />Western Wheatgrass <br />Green Needlegrass <br />COLORADO SCHOOL OF MINES RESEARCH INSTITUTE <br />Variety <br />Nordan <br />Luna <br />Critana <br />Rosanna <br />Lodorm <br />Scientific Name Source <br />Agropyron cristatum <br />Agropyron trichophorum <br />Agropyron dasystachyum <br />Agropyron smithii <br />Stipa viridula <br />W. Kansas <br />E. Montana <br />E. Montana <br />E. Montana <br />E. Montana <br />Prior to seeding the green needlegrass, the seeds were stratified by soaking in <br />water for 12 hr followed by storage in the dark at 4 °C for 10 days. <br />To establish a vegetative constant, crested wheatgrass was planted in all <br />plots. This species appeared best suited, in the authors' opinion, to tolerate <br />the range of edaphic and climatic conditions present in the NGP. In the central <br />portion of each plot, seven rows of crested wheatgrass were planted; row spacing <br />was 30 cm. Based on ecological conditions, such as soil type, climate, etc., two <br />other grass species were selected for each plot, and six rows of each of these <br />species were planted. <br />