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percent. They further reported in Table 6, Mean Herbaceous Production (g/0.25m2) for <br />the Irrigated Pasture Vegetation Type, Nucla East Study Area, 1987, that the average total <br />herbaceous pre- disturbance forage production (including annuals and all perennial forbs <br />and graminoids) averaged 54.2 grams per one quarter square meter. <br />These pre- disturbance data can be compared with the post - reclamation data, wherein in <br />2008 on the Phase II site, allowable plant cover equaled 72.35 percent. The more <br />extensive sampling of the Phase III Bond Release Areas, starting in 2008, resulted in <br />allowable plant averaging 76.00 percent and a desirable forage yield of 65.52 grams. <br />Sampling of these areas in 2009 resulted in allowable plant averaging 80.80 percent and a <br />desirable forage yield of 68.37 grams for the second year's data and allowable plant cover <br />averaging 81.13 percent and a desirable forage yield of 68.37 grams for the first year's <br />data. Sampling of these areas in 2010 resulted in allowable plant averaging 85.07 percent <br />and a desirable forage yield of 82.64 grams for the second year's data and allowable plant <br />cover averaging 81.00 percent and a desirable forage yield of 73.33 grams for the first <br />year's data. Sampling of these areas in 2011 resulted in allowable plant averaging 88.93 <br />percent and a desirable forage yield of 106.49 grams for the second year's data and <br />allowable plant cover averaging 86.80 percent and a desirable forage yield of 79.65 grams <br />for the first year's data. Sampling of these areas in 2012 resulted in allowable plant <br />averaging 86.47 percent and a desirable forage yield of 88.18 grams for the second year's <br />data. While these data were collected using slightly different objectives, they employed <br />identical sampling methodologies and these measurements clearly document that the <br />allowable plant cover and desirable forage production on these Irrigated Pasture Reclaimed <br />Areas is higher in virtually every monitoring effort, than those associated with the <br />baseline Irrigated Pasture conditions. Therefore, these revegetation efforts would have to <br />be considered to be successful and the proposed post- mining land use has been achieved. <br />5. Surface and Ground Water Quality Impact Analysis: <br />A surface and groundwater quantity and quality impact analysis. This analysis must <br />include an assessment of available hydrology data relative to the impact projections <br />contained within the approved Probable Hydrologic Consequences and the applicable <br />Cumulative Hydrologic Analysis. The analysis must show that onsite impacts have been <br />minimized, and that offsite impacts have been prevented. The analysis must include an <br />evaluation of any impact trends which may exist in the available data. <br />Response: The potential surface and ground water impacts from the New Horizon #2 <br />Mine were detailed in Section 2.05.6(3) of the permit, under the Probable Hydrologic <br />Consequences section. The main potential impact is the possible infiltration of water into <br />the replaced overburden leading to the degradation of pyrite, and the subsequent effect <br />this can have on the dissolved solids and pH of the water. <br />5.1 Impact on Ground Water Rights <br />Ground water rights within the vicinity of the New Horizon #2 Mine (2 mile radius) are <br />identified in Appendix 2.04.7 -1 of the permit. A total of 29 ground water rights have been <br />SL -14 03DEC12.wpd 54 <br />