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determined on adjacent non -mined areas." <br />The approved reclamation plan is found in Section 2.05.4 of the permit application. The required <br />topsoil replacement thickness is two (2) feet. The approved post - mining land use is rangeland. The <br />Dugout Pond, perimeter ditches, and Pond 2 have been approved to remain as permanent structures. <br />III. OBSERVATIONS AND FINDINGS <br />Revegetation <br />The Keenesburg Mine permit previously utilized comparison of an approved reference area, known <br />as the Osgood reference area, for revegetation success of the reclaimed areas. Comparison to the <br />Osgood reference area was not ideal due to a successional change of the species composition in the . <br />reference area to a community heavily dominated by sand sagebrush and a reduction of forage <br />grasses and forb species over the years. Also, a change in surface ownership of the property upon <br />which the reference area was located caused concerns regarding management of the reference area. <br />CEC proposed revegetation success standards for vegetative cover and herbaceous productivity <br />based on a formula derived from historic data collected on the Osgood reference area and a <br />correlation to precipitation records (TR37, approved June 15, 2006). Permit page 2.05.4 -116b <br />defines the required cover standard for the Keenesburg Strip Mine. The permit states, "Reclaimed <br />areas will be considered successfully reclaimed if the total vegetative cover on the reclaimed area is <br />not less than 90 percent of the predicted calculated cover value with 90 percent statistical <br />confidence using the equation: y= 0.0173x3 — 0.8592x2 + 14.562x — 47.015, where x is the <br />cumulative value of precipitation from September to July of the following year, and y is the <br />resultant vegetation cover." This cover standard is in agreement with Rule 4.15.8. The calculated <br />cover standard for 2009 is 35.7 percent live vegetative cover, based on 13.71 inches of measured <br />precipitation for the preceding September to July. <br />CEC reported in the 2009 vegetation sampling report that the overall vegetative cover for <br />reclaimed areas seeded in 1998, 1999, and 2000 (reclamation areas 2, 5, 6, 7, 9, 10, 15, 16 and <br />19) was 60.96% live vegetative cover. However, per Rule 4.15.1(2) and the Division's 1995 <br />Bond Release Guidelines, noxious species cannot contribute to reclamation success. Table 2 in <br />CEC's revegetation report shows that Bromus tectorum (cheatgrass) contributed 8.3% to the live <br />vegetative cover (LVC) on this Bond Release Block (BRB), and this amount must be removed from <br />the value of 60.96% for a sub -total of 52.66% LVC. <br />Furthermore, in measuring reclamation success the allowable cover contribution of annual and <br />biennial species should not exceed 10 percent (based on Division policy and the Division's 1995 <br />guidelines). Of the 36 plant species sampled on the 1998/1999/2000 BRB, 14 species were <br />determined to be annual or biennial. The 14 annual and biennial species contributed 13.19% of the <br />total cover and 28.67% of the relative cover (from Table 2). To limit the relative cover of annual <br />and biennial species to exactly 10 percent, a portion of these species were removed from a revised <br />Table 2, and the resulting LVC is 44.07 %. <br />C1981 -028, SL -05 5 9/10/2010 <br />