Laserfiche WebLink
Greenhouse study: <br />Topsoil <br />Spoil <br />Field study: <br />Topsoil <br />Spoil <br />Table 1 Chemical and physical analyses of topsoil and spoil materiel used in the greenhouse and the field studies. <br />Total <br />pHt SAR EC N <br />6.9 0.04 0.32 2,824 <br />7.0 0.24 0.88 1,826 <br />6.1 0.36 1.40 1,808 <br />7.3 1.27 1.30 998 <br />t Saturation paste. <br />$ Ca, Mg, and Na from saturation paste extract. <br />of winter wheat (Triticum aestivum) and intermediate <br />wheatgrass (Agropyron intermedium); (ii) evaluate the <br />effect of mixing equal parts of topsoil and spoil on the <br />growth of both wheat and intermediate wheatgrass; and <br />(iii) evaluate the effect of N fertilizer on the herbage and <br />root growth of intermediate wheatgrass. The field study <br />was designed to determine the effect of topsoil thickness <br />on the establishment and growth of a diverse mixture of <br />grass, forb, and shrub species. <br />METHODS <br />mmhos/cm <br />ppm <br />The field study was conducted at the Energy Fuels Mine no. 1 lo- <br />cated 32 km southwest of Steamboat Springs, Colo. Soil and spoil ma- <br />terials were obtained from the same area for the greenhouse study. <br />Elevation is 2,135 m, and average annual precipitation is 41 cm. The <br />soil is a Routt loam, which is a fine, montmorillonitic Type Argi- <br />boroll. Topsoil (A horizon) was obtained from an undisturbed sage- <br />brush area. The spoils are from the Williams Fork Formation of the <br />Upper Cretaceous Mesa Verde Group; this formation consists of <br />mixed beds of shale and sandstone. The spoils used in these studies <br />were a heterogeneous mixture of material from the various strata; <br />mixing occurred during mining when the overburden was stripped by a <br />dragline and when the spoil piles were leveled by a bulldozer. <br />Samples of the topsoil and spoil materials used in both the green- <br />house and the field studies were collected for chemical and physical <br />characterization. Percent total N was determined by a modified <br />Kjeldahl procedure (Bremner, 1965), and phosphorus (P) levels were <br />determined by bicarbonate extraction methods (Olsen et al., 1954). <br />Electrical conductivity (EC), Na, Ca, and Mg levels were determined <br />on the saturation paste extract. Partical size distribution was de- <br />termined by the hydrometer method. <br />Greenhouse Study <br />Cans were made of galvanized metal (stove) pipes, 15 cm in diam- <br />eter by 61 cm in length, and were closed on the bottom with a wood <br />plug equipped to allow drainage. The cans were filled with a total of <br />53 cm of either spoil alone or with a topsoil treatment. Spoil material <br />was passed through a 1.3 -cm mesh screen beforehand in order to elim- <br />inate very large rock materials common to spoil. <br />Topsoil thickness treatments were 0, 10, 20, 30, and 46 cm of top- <br />soil placed on top of 53, 43, 33, 23, and 7 cm of spoil, respectively. To <br />simulate mixing topsoil with spoil, 30 cm of a mixture of 50 topsoil <br />and 50% spoil were placed over 23 cm of spoil. Six replications were <br />made of each of the above treatments. An additional five replications <br />of the 0 -, 10 -, 20 -, and 30-cm topsoil depth treatments received a 112 <br />kg /ha N fertilizer application in the form of ammonium nitrate. <br />Each can was planted with 10 seeds of either winter wheat or inter- <br />mediate wheatgrass on 7 Dec. 1976, and rapid germination followed. <br />Topsoil thickness treatments receiving a N fertilizer treatment were <br />planted with only intermediate wheatgrass. The cans were watered <br />three times a week to above field capacity and allowed to drain; this <br />practice maintained the soil moisture well above the permanent wilting <br />point. The plants were thinned out 28 days after planting to leave the <br />three most vigorous seedlings. <br />682 J. Environ. Qual., Vol. 9, no. 4, 1980 <br />NaHCO,- <br />extractable P <br />Cat Mg Na Sand Silt Clay <br />meq /liter <br />40 5.2 3.0 0.1 53 19 28 <br />4 23.2 26.2 1.2 42 30 28 <br />10 5.5 3.4 0.9 66 24 20 <br />5 21.2 7.4 1.4 23 54 23 <br />The greenhouse temperature averaged 22 °C. Sunlight was aug- <br />mented with sodium -vapor lights, and light intensity ranged from a <br />maximum PAR of 1,000 µEinsteins m - ' sec' to a minimum of 100 <br />µEinsteins m sec Daylength was maintained at 14 hours. <br />The first harvest of wheat and intermediate wheatgrass herbage was <br />made on 1 March 1977. At the second harvest, 25 May 1977, the cans <br />were split lengthwise and the soil and spoil washed from the roots. The <br />herbage was separated from the roots, and roots were divided into <br />those growing in the topsoil and those growing in the spoil. All root <br />and herbage material was ovendried at 70 °C for 24 hours and <br />weighed. <br />Data were analyzed by standard analysis of variance and correlation <br />techniques. Tukey's procedure was used where needed to evaluate dif- <br />ferences between means. <br />Field Study <br />The field study was established at the Energy Fuels Mine No. 1 in <br />the fall of 1976. The area had previously been mined, and the spoil <br />material had been reshaped. Topsoil thickness treatments were 0, 10, <br />20, 30, and 46 cm of topsoil placed over spoil. There were two replica- <br />tions. The plots were drilled- seeded with a seed mixture containing 17 <br />grasses, 8 forbs, and 11 shrubs. <br />Each plot was sampled by locating five permanent points across <br />each plot and sampling within a 60 -cm by 91 -cm area centered at each <br />point. Ratings of percent stand were based on a scale of 0 to 100 (0 <br />indicated no seeded plants were present, and 100 indicated the maxi- <br />mum possible stand existed within the rectangular frame used), and <br />composition by species were determined on 21 June 1978, during the <br />second growing season. <br />RESULTS <br />Chemical and physical analyses of the soil and spoil <br />materials used in both studies indicated that these ma- <br />terials have a relatively high potential for revegetation <br />purposes (Table 1). Salt and sodium levels were low (as <br />indicated by EC and sodium adsorption ratio (SAR) <br />values) and pH values were neutral to slightly acidic. <br />Previous analyses showed that the strata making up the <br />overburden were neither saline nor sodic, nor did they <br />contain any mineral or metal in quantities approaching <br />a phytotoxic level.' P levels, and N levels to a lesser <br />extent, were low in spoil materials. Topsoil materials <br />had a sandy clay loam texture and the spoils had a clay <br />loam texture. <br />Greenhouse Experiment <br />Total herbage production (combined weights of the <br />two harvests) of both species increased linearly with top- <br />soil thickness (r = 0.95). Power et al. (1978) reported <br />similar increases in herbage yields with increased thick- <br />' Kent A. Crofts, Energy Fuels Corp., personal communication. <br />