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GENERAL40898
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Last modified
8/24/2016 8:00:00 PM
Creation date
11/23/2007 10:55:22 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1999002
IBM Index Class Name
General Documents
Doc Date
7/22/1999
Doc Name
FINAL ENVIRONMENTAL IMPACT STATEMENT VOL 1 CHAPTER 5 AND 6
Media Type
D
Archive
No
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CNAPTERFIVE o~rait Eis Beu~slons <br />The Parachute Creek station is the most downstream station in the drainage basin and is located <br />neaz the town of Pazachute. The station neaz Bead-Salle} Parachute is 0.6 nvle downstream <br />from the confluence of West and East Forks Pazachute Creek neaz Gardner Gulch. <br />Water Quality <br />In general, the water quality in the Parachute Creek drainage basin is typical of surface waters <br />from semi-arid areas of western Colorado. The water is slightly alkaline, with mean pH values <br />ranging from 8.0 to 8.5. The major anion in these waters is bicarbonate, with some carbonate <br />present when the pH exceeds 8.3. The concentrations of trace metals in the waters aze generally <br />low and are well below established water quality standards. Concentrations of chemical <br />constituents are generally lowest in the upstream reaches of the Parachute Creek drainage. <br />Farther down the Parachute Creek drainage, soluble salts accumulate from artural runoff and <br />irrigation return flows (COE 1985). Table 3.3-2 presents a summary of the available water <br />qualiri information for stations 09093000 (near Parachute) and 09093500 (at Parachute). The <br />complete raw data from the USGS records are provided in Appendix J of the Final EIS. <br />Comparison of the available water gualiri information to the Colorado Ambient Water Oualiri <br />Standards indicates that the maximum concentrations recorded for cadmium. lead, and selenium <br />occasionally exceed the chronic aquatic life standards. The exceedances were observed in less <br />than 15 percent of the data. All other pazameters aze within the applicable standazds for both <br />sampling stations over the period of record. <br />Page 3-16: Groundwater Flow <br />Groundwater elevations in the Upper Aquifer range from approximately 7,4(10 feet msl in the <br />southern part of the basin to 5,800 feet msl in the northern portion of the basin neaz the <br />confluences of Piceance Creek and Yellow Creek with the White River. In the Project Area, <br />groundwater generally flows from the southwest to the northeast. Robson at~d Saulnier (1980) <br />estimated horizontal hydraulic gradients ranging from 20 to as much as 120 :feet per mile within <br />the basin, with a gradient of approximately 35 feet per mile evident in the Project Area (Robson <br />and Saulnier 1980). Potentiometric surface maps constmcted for the Upper and Lower Aquifers <br />Robson and Saulnier aze presented in Figures 3 4-1 and 3 4-2 respectively <br />Paee 3-17 <br />The potentiometric map for the Lower Aquifer fFieure 3.4-21 shows groundwater elevations and <br />potentiometric contour configurations sunilaz to those of the Upper Aquifer. Horizontal <br />hydraulic gradients in the Lower Aquifer range from 20 to 130 feet per mile; and the flow <br />direction is generally from the southwest to the northeast. The horizontal gradient in the Project <br />Area is estimated to be approximately 25 feet per mile toward the northeast. <br />An assessment of differences in potentiometric head between the Upper and Lower Aquifers <br />indicates that a downwazd vertical eradient exists in the hieher topographic •rreas in the project <br />viciniri and an upwazd vertical eradient ispresent in topographically lower •ueas alone Piceance <br />Creek (Robson and Saulnier 19801 Vertical eradients indicate the potential for eroundwater <br />movement from the Upper Aquifer downwazd throueh the Mahoeanv Zone into the Lower <br />Aquifer or the potential for azoundwater movement upwazd from the Lower Aquifer across the <br />Maho¢anv Zone into the Upper Aquifer. with the rate of movement controlled by the vertical <br />
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