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Julia Keedy <br />RMCC Combined SWSP <br />October 21, 2013 <br />Page 3of9 <br />Condition 12 of the previous SWSP approval required the Applicant to demonstrate to the <br />State Engineer's Office that they have commenced backfilling or lining of Ready Mixed Pit No. <br />1. The slurry wall has been installed around Cell 3 /RMP1 was approved by the SEO on <br />September 17, 2013. Minimal dewatering occurred over the last few months at Cell3 /RMP1. <br />According to the Applicant, dewatering pumping totaled 3.3 acre -feet in May 2013 with no <br />dewatering in June. Dewatering quantities are reported in the monthly accounting submitted for <br />this SWSP. Any dewatering that occurs after liner approval can be returned to the stream <br />system through surface flow or ground water recharge without need for replacement so long as <br />the operator does not put the water to beneficial use. <br />A water court application for a permanent augmentation plan for the North Tower Pit was <br />filed on March 1, 1990 under case no. 1990CW39. The approval of this plan does not imply a <br />position by our office on any litigation associated with case no. 1990CW39 or any other case. <br />Condition 13 of the previous SWSP required the Applicant to describe steps taken toward a final <br />decree in the case. Since the last SWSP approval, several opposers have stipulated out of the <br />case. A revised draft decree was most recently filed on July 19, 2013. <br />Depletions <br />SWSP depletions are from evaporation of exposed ground water, dewatering, water <br />used to wash mined product, and water lost in mined product. Table 1A (attached) summarizes <br />projected depletions through December 2015. <br />Some mining will occur above the ground water surface and some will occur below the <br />ground water surface. For the projected depletions, all projected mining is assumed to be below <br />the ground water surface and has been charged 4% water loss by weight. Actual accounting <br />will track where the mining occurs and only assess 2% water loss by weight where mining is <br />above the ground water surface. For August 2013 through July 2014, RMCC projects <br />1,600,000 tons of gravel production at this site. This projects to a maximum water loss of 44.1 <br />acre -feet. <br />The area of exposed ground water is expected to be 53.2 acres or less for the period of <br />August 2013 through July 2014. This gross evaporation rate is 44.5 inches per year, which is <br />consistent with the North Tower engineering report revised on March 9, 2012. Using the <br />effective precipitation of 10 inches per year and historical North Tower Pit ET credit of 2.8 acre - <br />feet per year, the projected net evaporative loss from August 2013 through July 2014 is 150.2 <br />acre -feet. <br />The total consumptive use at this site from August 2013 through July 2014 is 41.35 acre - <br />feet with an additional 453 acre -feet from dewatering pumping returned to the South Platte. <br />These depletions do not hit the river instantaneously and thus must be lagged back to the river. <br />With the recent approval of the liner for Bromley Cell 3 /Lot 1, the Applicant has separated the <br />lagging analysis for the Plant Site and Lot 2, which are located east of the McCanne Ditch, with <br />the lined gravel pit expected to block most of the depletions from impacting the South Platte <br />River. Rather, for the Plant Site and Lot 2, the Applicant performed a lagging analysis to the <br />McCanne Ditch, which flows year round and discharges to the South Platte River. The Glover <br />parameters applied for the Plant Site and Lot 2 beginning in November 2013 are as follows: <br />specific yield = 0.2 <br />transmissivity = 100,000 gpd /ft <br />distance from centroid of mining area to McCanne Ditch = 600 feet <br />