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.
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