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Bucklen Pit SWSP Page 2 of 9 <br /> October 28, 2014 <br /> may not be re-allocated to other areas of ground water exposure within the gravel pit boundaries. Any <br /> pre-81 area that is backfilted will lose the pre-81 exemption should it be excavated in the future. <br /> Additionally the backfilling of a pre-81 area shall not create a credit to be used elsewhere. <br /> Net evaporative depletions were calculated using a gross annual evaporation of 45 inches from <br /> the exposed water surface, with a credit of 9.81 inches for effective precipitation. Computation of <br /> evaporation under this plan was reduced during the ice covered period. You have assumed the ice <br /> covered period to occur during the months of December and January based on the average monthly <br /> temperatures of 29.4°F for December, and 28.6°F for January. Temperature data were obtained from <br /> the Greeley UNC weather station (053553) for the time period of 1967 through 2005. The ice covered <br /> periods may be used to reduce the amount of evaporative losses that need to be replaced; however, <br /> for the purpose of this SWSP, the Applicant shalt replace the net evaporation depletions from the <br /> exposed ground water surface area that may occur during the assumed ice covered period (December <br /> through January) for any time that the pit is not completely covered by ice. Computation of the net <br /> evaporation during any time that the pit is not completely covered by ice shalt be determined as the <br /> pro-rata amount of the monthly gross evaporation rate distribution amount identified in the State <br /> Engineer's General Guidelines for Substitute Supply Plans for Sand and Gravel Pits, subtracting the <br /> pro-rata amount of the effective precipitation for that period. The net depletion of ground water <br /> due to evaporation from the 12.54 acres exposed after December 31, 1980 is projected to total 34.60 <br /> acre-feet during this plan period, as shown on the attached Table 1. <br /> Operational losses associated with mining activities will include water removed with the <br /> mined product and water used for dust control. Up to 200,000 tons of material is projected to be <br /> mined during this plan period. The material will be mined below the ground water table in a <br /> dewatered state and not washed; therefore the water retained in the mined product is considered to <br /> be 2.0% of the mined material by weight. This results in a groundwater loss of 2.94 acre-feet. The <br /> Applicant has estimated that 6,000 gallons of water per day will be used for dust control purposes <br /> during the months of March through October. Water used for dust control purposes is assumed to be <br /> 100% consumed. The amount of water lost to dust control during this plan period is therefore <br /> estimated to be 4.51 acre-feet. The estimated monthly depletions due to operational losses are <br /> shown on the attached Table 2. The total projected operational consumptive use for this plan period <br /> is 7.45 acre-feet. <br /> According to information previously provided to this office, dewatering commenced in <br /> Amendment Area A in the summer of 1998 and is not projected to cease until 2021. Dewatering <br /> occurs through the use of two pumps, with one pump usually running continuously, and two pumps <br /> running in high water events. The water is pumped into two settling ponds north of Amendment Area <br /> A and immediately adjacent to the Cache la Poudre River, where it is allowed to seep and discharge <br /> into the river. Prior to November 2012, the volume of water pumped for dewatering was not included <br /> in the accounting submitted to this office or otherwise tracked. Subsequent SWSP approvals have <br /> required monthly volumes of dewatering discharge into the settling ponds to be recorded. However, <br /> these volumes do not need to be analyzed for depletions to the river as long as pumping remains <br /> relatively constant month to month. Dewatering operations that are constant and continuous will <br /> eventually reach a steady state condition where the accretions to the river generated by dewatering <br /> are equal to the depletions to the river generated by dewatering. Given the tong duration of <br /> historical dewatering operations, it is assumed dewatering operations at the Buckten Pit are in a <br /> steady state condition. At least three (3) years from the expected cessation of dewatering, a plan <br /> that addresses the replacement of tong term lagged depletions, including depletions that occur with <br />