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2012-02-03_HYDROLOGY - M1998013
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2012-02-03_HYDROLOGY - M1998013
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Last modified
8/24/2016 4:48:21 PM
Creation date
2/8/2012 10:58:16 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1998013
IBM Index Class Name
HYDROLOGY
Doc Date
2/3/2012
Doc Name
SWSP
From
OSE
To
Civil Resources, LLC
Permit Index Doc Type
Hydrology Report
Email Name
ECS
Media Type
D
Archive
No
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Mr. Andy Rodriguez, P.E Page 2 of 5 <br />Shores SWSP <br />January 26, 2012 <br />stream depletions that result from mining related exposure of ground water. The DRMS letter <br />identifies four approaches to satisfy this requirement. In accordance with approach nos. 1 and <br />3, you have obtained a bond for $1,045,840 through DRMS for lining or backfilling of the <br />exposed ground water. <br />Depletions <br />Currently 11 acres of ground water surface is exposed at the Shores Pit within the silt <br />pond. The net depletion of ground water due to evaporation from these 11 acres is calculated <br />to be 29.45 acre -feet. Net evaporative depletions were calculated using a gross annual <br />evaporation of 42 inches from the exposed water surface, with a credit of 10.56 inches for <br />effective precipitation. Computation of evaporation under this plan was also reduced during the <br />ice covered period. You have assumed the ice covered period to occur during the months of <br />January and December, based on the average temperatures of 26.99 °F for January and <br />28.62 °F for December; taken from the Longmont 2ESE weather station. However, for the <br />purpose of this SWSP, the Applicant shall replace the net evaporation depletions from the <br />exposed ground water surface area that may occur during the assumed ice covered period (the <br />months of January and December) for any time that the water surface is not completely covered <br />by ice. Computation of the net evaporation during any time that the water surface is not <br />completely covered by ice shall be determined as the pro -rata amount of the monthly gross <br />evaporation rate distribution amount identified in the State Engineer's General Guidelines for <br />Substitute Supply Plans for Sand and Gravel Pits, subtracting the pro -rata amount of the <br />effective precipitation for that period. <br />Ground water from the 11 acre silt pond is used for washing aggregate, dust control and <br />concrete batching. The Applicant anticipates that 387,502 tons of aggregate will be mined <br />during this plan period. The material is mined below the ground water table and is washed; <br />therefore the water retained in the mined product is considered to be 4.0% of the mined material <br />by weight, equal to 11.40 acre -feet. The Applicant estimates that 1.66 acre -feet of water per <br />year will be used for dust control. Approximately 85,000 cubic yards of concrete will be batched <br />onsite at a depletion of 40 gallons per cubic yard, resulting in an annual depletion of 10.43 acre - <br />feet. The net evaporation and operation depletions associated with the Shores pit are estimated <br />to be 52.93 acre -feet, as shown in the attached Table 4 & 5. <br />Dewatering of the site commenced in February 1999 at a rate of 300 gallons per minute <br />and had remained constant during mining of cells A, B, and C. For modeling purposes <br />dewatering was stopped on December 2007 which is the year the slurry walls for the three cells <br />were completed. As long as dewatering operations in cell D remain constant, it is assumed that <br />the accretion credits are sufficient to offset any lagged depletions as this water is not used and <br />immediately returns to the stream. The SWSP accounts for the net depletions at the river that <br />occur due to the past dewatering operations (February 1999 through December 2007) The <br />depletions from past dewatering at the site during the period of this plan total 35.17 acre -feet. <br />The depletions from evaporation, water removed in the mined product, dust suppression, <br />concrete batching and dewatering were lagged to Saint Vrain Creek using a Glover analysis. The <br />following parameters were used in the model to lag operational and evaporative losses: <br />transmissivity (T) = 72,300 gallons per day per foot, specific yield (SY) = 0.2, the distance from <br />the exposed ground water to the creek (X) = 5,409 feet, and the location from the parallel <br />impermeable boundary to the creek (W) = 10,000 feet. The attached Table 5 provides a monthly <br />schedule of lagged depletions to the river system due to operational losses, shown to be 57.22 <br />acre -feet for this plan period. Including depletions due to past dewatering activities, the total <br />lagged depletion to the river system in 2012 is 92.39 acre -feet, as shown on Table 7. <br />
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