Laserfiche WebLink
both sites could be used to predict the time frame of slightly elevated spoil water quality. This <br />ratio - 3"/13", as applied to 1500 years results in a time frame of 346 years until all the pyrite is <br />oxidized. When considering all the variables involved, this means that it could dissipate within a <br />range of 200 to 500 years. The TDS should begin to drop before this time. Once the pyrite is <br />fully oxidized and other salts are flushed out, the backfill water quality should approach the <br />existing stream water quality, possibly dropping to 800 to 1200 mg/1 TDS. It is not likely that the <br />backfill water will ever reach the low TDS of the ditch- run water as seepage from the <br />overburden zones into the backfill will continue as long as the 2nd Park irrigation continues. <br />Impacts To Receiving Waters — Tuttle Draw As described earlier, drainage through the NHN <br />backfill material will move to the south following the path of least resistance along the pit floor <br />and issue at the general location of Spoil Spring # 1, (see Map 2.04.7-1). Spoil Spring #1, is the <br />spoil water discharge from the old Peabody Nucla Mine (New Horizon #1 Area permit) and has <br />been monitored since 1987. Spoil Spring #1 water mixes with irrigation runoff and return water <br />from Nygren Draw and then discharges into Tuttle Draw located about 1600 ft. downstream <br />from the spoil spring. Tuttle Draw enters the San Miguel River approximately 2 miles to the <br />southwest. <br />Historic sample data (since 1987) from surface water sites, NPDES 001, SW -N3, and the San <br />Miguel River has shown that the concentration of TDS in these sources varies inversely with the <br />flow volume. Total dissolved solids (TDS) increase during the low flow periods and decrease <br />during the high flow periods. For NPDES 001 and SW -N3 high flows correspond with the <br />irrigation season; however, the San Miguel River is typically in low flow condition during the <br />irrigation season. During the non -irrigation season flows from NPDES 001 and SW -N3 are low <br />and TDS is higher while the San Miguel TDS is lower due to the higher flow, (see Table <br />2.05.6(3)-4 of New Horizon #2 Area permit). This presents both a high and low flow case which <br />are complicated by the fact that spoil spring flow predicted to occur after the New Horizon Mine <br />has been reclaimed (2013-2014) has not yet occurred. Therefore, the impacts to the receiving <br />waters will be evaluated for both high and low cases, with and without irrigation, and including <br />the predicted spoil spring flows from New Horizon Mine and the existing spoil spring flow from <br />the old Peabody Nucla Mine (New Horizon 1 permit area). The irrigation case corresponds to the <br />September/October time period when flows are fairly low in the San Miguel River. The non - <br />irrigation period corresponds to March/April when flows in the San Miguel are usually at peak. <br />As described previously, irrigation of the reclaimed NHN Mine will produce a flow in the spoil <br />of about 81 ac-ft./yr,( at full irrigation). Over the length of the irrigation season (165 days) this is <br />an average of about 0.248 cfs. During the non -irrigation season the flow from the NHN backfill <br />spring will mimic flow levels from the old Peabody Mine or about 0.041 cfs. The TDS values for <br />the NHN backfill spring discharge were averaged from sample analyses from NPDES 001 <br />discharges from 1987 to 2000 and reported on Table 2.05.6(3)-4 of the New Horizon #2 Area <br />permit. The Tuttle Draw TDS and flow values were also averaged from analyses and <br />Section 2.05.6(3) Page 25 April 2016 (PR -01) <br />