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2023-08-30_HYDROLOGY - M2001046
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2023-08-30_HYDROLOGY - M2001046
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Last modified
9/5/2023 8:43:38 AM
Creation date
9/5/2023 8:40:09 AM
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DRMS Permit Index
Permit No
M2001046
IBM Index Class Name
Hydrology
Doc Date
8/30/2023
Doc Name
Substitute Water Supply Plan
From
Division Of Water Resources
To
DRMS
Email Name
ECS
MAC
Media Type
D
Archive
No
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Nix Gravel Pit SWSP <br /> August 30, 2023 <br /> Page 3 of 8 <br /> The estimated water used for dust suppression during the period of this SWSP total 10.17 acre- <br /> feet based on an estimated use of one to four 8,000-gallon truckloads of water per workday <br /> (Table 2). Water withdrawn from the freshwater pond will be used for concrete and asphalt <br /> batching in the future once mining of the slurry lined area begins, but not during this approval <br /> period. <br /> The Applicant has indicated that Cell 1A (consisting of the unlined freshwater and overflow ponds) <br /> will be continuously dewatered at an estimated rate of 3,000 gpm during this approval period. The <br /> overflow pond was expected to be completed and filled with water in July 2023, while the <br /> freshwater pond is expected to be completed and filled with water in June 2024. Both the <br /> freshwater and overflow ponds will be dry mined. Water pumped for dewatering of the overflow <br /> pond will be discharged to the freshwater pond area. Once the overflow pond is completed, water <br /> pumped to dewater the freshwater pond will be discharged to the overflow pond area. After both <br /> ponds are completed, if the freshwater and overflow ponds cannot accept the full volume of <br /> water discharged, excess water will be pumped into a proposed 4 acre recharge pond shown in <br /> Figure 3 (attached). The quantity of water discharged to the recharge pond will be tracked <br /> separately from the water discharged to the freshwater and overflow ponds, and lagged back to <br /> the stream. The Applicant anticipates discharging as much water as possible to the freshwater and <br /> overflow ponds to minimize net depletions. The SWSP for this approval period estimates 80% of <br /> the water discharged from dewatering will be placed in the freshwater and overflow ponds, with <br /> 20% placed in the recharge pond. <br /> Because the freshwater and overflow ponds will be dry mined, the first fill will occur once the <br /> ponds are fully excavated and dewatering of the ponds ceases. According to the "General <br /> Guidelines for Substitute Water Supply Plans for Sand and Gravel Pits", water consumption by the <br /> mining operation will also include water removed from the tributary stream system by the "first <br /> fill" of the gravel pit. The "first fill" is the water that fills the gravel pit and occupies the volume <br /> previously occupied by the removed sand and gravel. For the Nix Pit, the "first fill" was estimated <br /> based on 640,000 tons of aggregate production below the water table during the period of this <br /> SWSP multiplied by the percentage gravel matrix (70% assuming a porosity of 30% and a density of <br /> the material of 1.5 tons/cubic-yard) and then subtracting the volume of water lost with the mined <br /> product. Based on the above, the water removed by the "first fill" was determined to be 204.37 <br /> acre-feet during the period of this SWSP (Table 2). <br /> The IDS AWAS stream depletion model was used to determine the lagged depletions from <br /> evaporation and operational losses, to St. Vrain Creek. The aquifer characteristics used in the <br /> model are: harmonic transmissivity (T) = 47,518 gallons per day per foot, specific yield (SY) = 0.2, <br /> the distance from the centroid of the exposed ground water to the stream X=4,000 feet and the <br /> location of the parallel impermeable boundary W=8,775 feet from the stream. <br /> In addition, as mentioned above the amount of water discharged to the overflow/freshwater <br /> ponds and to the recharge area will be tracked separately and lagged back to the stream. Water <br /> discharged to the overflow/freshwater ponds will be lagged using the unit response function (URF) <br /> shown in Table 4 (attached). Water discharged to the recharge area will utilize a URF (Table 5 <br /> attached) developed using the following aquifer parameters: harmonic transmissivity (T) = 54,974 <br /> gallons per day per foot, specific yield (SY) = 0.2, the distance from the centroid of the exposed <br /> ground water to the stream X=5,377 feet and the location of the parallel impermeable boundary <br /> W=8,660 feet from the stream. <br /> For the purpose of this SWSP, the final 1 percent of the impact to the stream was wrapped into <br /> the first 99% and re-normalized (Table 5). The total water use during the renewal period, <br /> including water pumped for dewatering operations is estimated to be 5,131.6 AF as shown in <br /> Table 2. Based on a total water use estimate of 5,131.6 acre-feet, the total lagged depletions to <br /> St. Vrain Creek during this renewal period are estimated to be 1,093.03 acre-feet. Of these total <br />
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