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vegetation cover and site conditions, the Division has determined that the sediment pond is no <br />longer necessary to control disturbed area sedimentation. As such, the Division proposes to <br />discontinue maintenance of the sediment pond spillway riser structure. Leakage of occasional <br />inflows into the buried discharge culvert will be allowed to continue. <br />The Division has chosen to make the demonstration that conditions of Rule 4.05.2(2) have been <br />met, to allow for discontinuance of sediment pond maintenance. Rule 4.05.2(2) requires (in <br />pertinent part) that sedimentation ponds be maintained until "... removal is authorized by the <br />Division and the disturbed area has been revegetated and stabilized," and "the untreated <br />drainage from the disturbed area ceases to contribute additional suspended solids above natural <br />conditions". An additional requirement of 4.05.2(2) is that sediment ponds must be retained and <br />maintained for at least 2 years after the last seeding within the affected watershed. Further, it is <br />Division policy is that sediment ponds must be retained and maintained until a statistically valid <br />demonstration of compliance with the approved vegetation cover standard has been made. <br />The Division conducted vegetation cover sampling in May 2005, and site stability evaluation was <br />conducted during the 2005 growing season (see May and September 2005 DMG inspection <br />reports). Results of these evaluations indicate that the cover standard has been met, and the <br />disturbed area has been stabilized. <br />Quantitative Assessment of Vegetation Cover <br />Vegetation cover sampling was conducted by the Division on May 17 and May 18, 2005. Thirty <br />randomly located, randomly oriented, 10 meter vegetation cover transects were run. At each <br />transect, a tripod mounted ocular 10 point frame was set up every 2 meters, for a total of 50 <br />readings per transect. At each of the 50 points, "hits" were recorded by vegetation species (for <br />live vegetation), litter, rock, or bare ground. The cover summary is presented in Enclosure 1, <br />cover statistics including sample adequacy documentation and demonstration of success is <br />presented in Enclosure 2. Representative photographs of revegetated areas taken in September <br />2005 are included in Enclosure 3, and a site map showing sample transect locations is included <br />in Enclosure 4. <br />The sole vegetation standard applicable to the Fruita Mine is vegetation cover (because of the <br />extensive pre-law disturbance at the site). The mine was never permitted under the permanent <br />regulatory program, but the Division had proposed a cover standard of 25% in a findings <br />document that was prepared prior to forfeiture of the reclamation bond. Based on the data <br />collected, the standard was easily exceeded this year. The applicable criteria is 22.5% <br />vegetation cover (90% of the approved standard). The sample mean from the cover data <br />collected by the Division was 43.9%, and minimum required sample size was calculated to be <br />29.6, based on the standard sample size adequacy formula. As such, the data comprise a <br />statistically valid demonstration of compliance with the cover standard. <br />Annual species, particularly downy brome, or cheatgrass (Anisantha tectorum), provide a major <br />component of the vegetative cover. Downy brome and other annual species are present at <br />similar or higher levels in undisturbed habitats in the mine vicinity. Growth of annual species was <br />enhanced in 2005 by relatively wet conditions in the fall of 2004 and early spring of 2005. <br />However, seeded perennial species are also well established at the site, particularly several <br />species of native shrubs. Seeded perennial species comprise approximately 35% relative <br />vegetation cover. <br />