Laserfiche WebLink
Rifle Gravel Pit #] July 2023 <br /> In determining demands, SGM referenced the guidelines from the State Engineer's Office <br /> dated April 1, 2011, "General Guidelines for Substitute Water Supply Plans for Sand and <br /> Gravel Pits" (SEO Gravel Pit Guidelines). Item 13 of the SEO Gravel Pit Guidelines provides <br /> direction for estimating water lost with mined aggregate based on multiple factors (such as <br /> washed vs. not washed and mined above the groundwater table vs. mined below the <br /> groundwater table). Material that is mined below the groundwater table that has been <br /> washed is charged 4% moisture content by weight, because the entire 4% is a groundwater <br /> diversion. Essentially, when mined below the groundwater table, the aggregate already has <br /> a 4% by weight moisture content which is not changed by the process of washing. The <br /> entire 4 percent by weight moisture content is then lost with the mined aggregate. <br /> Scott estimated for the entire property they could meet a production rate of 105,000 tons of <br /> aggregate per year, or 13,125 tons per month assuming operations 8 months of the year. <br /> Applying the standard assumption of 4% water by weight results in total annual demand of <br /> 3.09 acre-feet (AF) for 105,000 tons of aggregate. <br /> 8.7.3 Water Used for Dust Control <br /> Dust control water will be captured from the pond, defined as a well per the DWR-SEO. <br /> Scott estimates that the active mining operations will use 25,000 gallons per day for dust <br /> suppression. Based on 30-31 operational days per month, this results in an annual demand <br /> of 18.72 AF. <br /> 8.7.4 Exposed Groundwater Lost Due to Evaporation <br /> Evaporation from exposed groundwater during active mining will occur as mining operations <br /> progress. Annual gross evaporation for the Rifle area is estimated at 45 inches based on the <br /> contours from National Oceanic and Atmospheric Administration Technical Report NWS 33 <br /> dated June 1982, Map No. 3. Annual evaporation was distributed annually using the DWR <br /> General Guidelines for Substitute Water Supply Plans for Sand and Gravel Pits (DWR <br /> Gravel Pit Guidelines) annual distribution for elevations below 6,500 feet. The evaporation <br /> was then reduced to account for periods when the pit is expected to be frozen over when <br /> the average temperature is below freezing, typically December and February for Rifle. A <br /> copy of the DWR GWS Form 27 Permit application is included in Attachment G. <br /> Groundwater will be exposed to the surface during the wet mining operations. The final <br /> surface area of the pond is estimated to be 9.70 acres. It is conservatively estimated that the <br /> total surface area of the pond will be exposed within the first year of operation. The total <br /> annual evaporation of the pond was calculated at 44.28 AF/year, based on a previous <br /> version of the mining proposal that involved a larger pond surface of 12.56 acres. Given that <br /> the pond has been reduced in size, annual evaporation will be lower in fact, but IHC Scott <br /> has elected not to revise the loss calculation downwards since augmentation/supplementary <br /> supply plans have already been prepared. <br /> 8.7.6 Water Used Indoors (Domestic and Commercial) <br /> Scott does not anticipate using water from the site for indoor water demands. As such, there <br /> will be no groundwater demands or depletions associated with domestic or commercial <br /> water depletions. <br /> Potable water is not available from City of Rifle or Town of Silt and drilling a well for potable <br /> water on the property is not feasible given minimal domestic needs and short operating <br /> period. Instead, Scott will truck potable water onto the site to supply employees with potable <br /> 51 <br />