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RULE 4 PERFORMANCE STANDARDS <br />"benign ", nutrient -poor overburden in the attempt to slow or delay emergence and growth by competing <br />grasses and annual weeds, thereby allowing shrub seed additional time to break dormancy and emerge. <br />Prior to seeding taking place one composite sample was taken from each test plot. The constituents <br />analyzed were texture, fetility, pH, percent coarse fragments, electrical conductivity, sodium adsorption <br />ratio, selenium, and boron. To further encourage shrubs growth, the seed mix was heavily weighted <br />toward shrubs. The seed mixture that was used on the test plots is shown below. <br />Seed Mix - Buried Topsoil Test Plot Seed Mix - Colowyo Mine - 2006 <br />Recommended <br />seeds <br />Species <br />Synonym <br />Common Name <br />Seeds/ Ib. <br />lbs. / acre <br />sq. foot <br />Agropyron dasystachyum <br />Elymus lanceolatus ssp. lanceolatus <br />Thickspike Wheatgrass <br />154,000 <br />0.25 <br />0.88 <br />Agropyron smithil <br />Pascopyrum smith /i <br />Western Wheatgrass <br />110,000 <br />0.25 <br />0.63 <br />Agropyron spicatum inerme <br />Pseudoroegnena spicata ssp. /nerme <br />Beardless Bluebunch Wheatgrass <br />117,000 <br />0.50 <br />1.34 <br />Agropyron trachycaulum <br />Elymus trachycaulusssp. trachycaulus <br />Slender Wheatgrass <br />159,000 <br />0.50 <br />1.83 <br />PoaAmp /a <br />Big Bluegrass <br />882,000 <br />0.10 <br />2.02 <br />Subtotal = <br />1.60 <br />6.71 <br />Achillea millifolium <br />Western Yarrow <br />2,770,000 <br />0.10 <br />6.36 <br />w <br />Artem /s /a ludov/ciana <br />Louisiana Sagewort <br />33,600 <br />0.75 <br />0.58 <br />u <br />9 <br />Aster chilensis <br />Uirgu /asterascendens <br />Pacific Aster <br />2,668,000 <br />0.10 <br />6.1 <br />o <br />L/num lewis// <br />Lewis Flax <br />293,000 <br />0.20 <br />1.35 <br />00 <br />Artemis /a fridg/da <br />Fringed Sage <br />4,536,000 <br />0.05 <br />5.21 <br />Penstemon strictus <br />Rocky Mountain Penstemon <br />592,000 <br />0.20 <br />2.72 <br />Subtotal = <br />1.40 <br />22.33 <br />Amelanchieralnifolia <br />Saskatoon Serviceberry <br />25,800 <br />1.50 <br />0.89 <br />Artemisa tridentata vaseyana <br />Mountain Big Sagebrush <br />2,500,000 <br />0.25 <br />14.35 <br />Artemis /a cana <br />Silver Sagebrush <br />850,000 <br />0.75 <br />14.63 <br />Atr/plexcanescens <br />Fourwing Saltbush <br />52,000 <br />1.00 <br />1.19 <br />v <br />Ceratoldeslanata <br />Wiinterfat <br />56,700 <br />2.00 <br />2.60 <br />P <br />m <br />Chrysothamnus nauseosus <br />Rubber Rabbitbrush <br />400,000 <br />0.50 <br />4.59 <br />Pursh /a tridentata <br />Bitterbrush <br />15,000 <br />3.00 <br />1.03 <br />Rosa woodsll <br />Wood's Rose <br />45,300 <br />1.50 <br />1.56 <br />Symphodcarpos rotundifokius <br />.. <br />_. <br />Mountain Snowberry <br />....... <br />75,000 <br />1.50 <br />2.58 <br />..... <br />-. Subtotal "= <br />12.00 . <br />43.44 ' <br />Total <br />1 15.001 <br />72.48 <br />At the peak of each subsequent growing season, or shortly thereafter, for a period of at least 5 years, these <br />test plots will be evaluated for emergent shrub density, ground cover by species, and a visual evaluation <br />of surficial erosion. This data will be reported annually in the Annual Reclamation Report. If data shows <br />that there is promise as a shrub conducive reclamation procedure, CDRMS may be contacted to initiate <br />alternate reclamation procedures for the remainder of Colowyo reclamation. <br />4.15.7 Determining Revegetation Success: General Requirements and Standards <br />During the summer of 1980, two reference areas were selected to represent the two major vegetative <br />communities to be disturbed, sagebrush and mountain shrub. The location of the reference areas are <br />shown on the Vegetation map (Map 4) and Regional Vegetation map (Map 3). Extensive, detailed <br />vegetative sampling was performed, duplicating the methodologies as described in Section 2.04.10. <br />The reference areas were sampled for herbaceous cover, herbaceous productivity and woody plant <br />density. Species diversity was determined utilizing herbaceous cover data from the premining <br />inventory of the sagebrush and mountain shrub communities. The reference areas are approximately <br />seven acres in size. <br />Statistical tests were performed on the vegetative data from the reference areas to prove that they <br />were comparable to the premined area. The parameters compared were herbaceous cover and <br />herbaceous production. <br />Rule 4 Performance Standards 4.15 -7 Revision Date: 10/27/10 <br />11 Revision No.: MR -103 <br />