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The number of samples within each parcel varied from 2000 due to management measures undertaken eazly in this yeazs growing season. Recognizing the need to manage Bromus • tectorum {cheatgrass) in the reclamation areas, small controlled burns were conducted within portions of the 1995 reclamation area and within areas not yet topsoiled or revegetated. Sample sites were located in the field through compass triangulation and pacing from known landmazks. Figures 1 and 2 illustrate the location of the reference and reclaimed areas and sample point locations for each azea sampled. In the areas reclaimed in 1985, 1986, 1987, 1999, and 2000 a qualitative evaluation of revegetation success was undertaken this year. The 1985, 1986, and 1987 areas were previously monitored (1994-1998) and after successfully meeting revegetation success criteria, were released from the Phase II liability requirements by the Colorado Division of Minerals and Geology August 11, 1998. This yeaz, qualitative evaluation of these areas included estimating vegetative cover, herbaceous production, and identifying the dominant plant species. Any locations or trends in vegetation development that required attention were also noted. The areas revegetated in 1999 (A Pit and south of the Topsand Piles) and 2000 (former haul roads NE and E of B Pit and S and E of the 1986 E azea) were qualitatively evaluated this yeaz. The Osgood sand reference area was measured and mapped in the field in 1994 by Savage and Savage staff, and this scaled drawing of the reference azea was used. On the scaled drawing, a Cartesian coordinate grid (50x50 feet) was established. Computer generated • random numbers were used to establish a pool of x,y coordinates. Ten vegetation cover and fifteen herbaceous production sample locations were randomly established for the reference area. Sample sites were located in the field through compass triangulation and pacing from known landmarks. FIELD SAMPLING Timing Field investigation was undertaken during the period August 20 through August 23, 2001. This time period coincided with anthesis and maximum development of the majority of plant species found in both the native vegetation community (Osgood sand reference area) and the reclaimed areas at the mine site to be evaluated. The Keenesburg azea experienced a very dry period during the winter and eazly spring of 2001 based on mine site records. Late spring precipitation was heavy, followed by moderate precipitation through the summer. Vegetation Cover Vegetation cover was estimated by the use of the point-intercept method. An ocular point frame (ESCO Associates) was used to minimize instrument error and maximize precision and observer accuracy. Cover transects were 25 meters in length, with two sample data • points collected at 1.0 meter intervals along the transect on opposite sides of the transect _~