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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 Dean EIS Revisions <br />The initial segment of the pipeline corridor from the Piceance Site processing facility to the <br />Greasewood Compressor Station will cross or follow existing drainages including Piceance <br />Creek and Hatch Gulch. Shallow groundwater in alluvial sediments will likely exist along this <br />portion of the pipeline. From the Greasewood Compressor Station, the corridor vends southerly <br />about 7 miles along Collins and Stewart gulches, in which alluvial groundwater conditions may <br />exist. Approximately 7 miles from the Greasewood Compressor Station, the ~~orridor moves <br />from Stewart Gulch to uplands and trends along Barnes Ridge. The upland a~~eas aze underlain <br />by the Upper and Lower Aquifers discussed in Section 3.1.1. At Davis Point, the corridor <br />descends from the uplands into the Pazachute Creek drainage, which it follows to the Parachute <br />Site final processing facilities. <br />A summary of the USGS water quality information available for <br />Lower Aquifer wells along the pipeline route is presented in Table 3.4-5. Ba:>ed on the limited <br />USGS data, the water quality of the alluvium and Upper Aquifer along the pipeline route is <br />similaz to that described for the Piceance Site. Water quality of the Lower Acluifer appeazs to be <br />better along the pipeline route than at the Piceance Site. However, as discussed above for the <br />Lower Aquifer, the depths and units monitored by these wells aze not known. <br />Historic groundwater quality data were collected from wells in the Parachute Creek watershed <br />from the mid-1970s to the eazly 1980s (COE 1985). These data indicate that the alluvial waters <br />aze slightly alkaline, ranging in pH from 7.2 to 8.2. The major anions aze sulfate and <br />bicarbonate. TDS concentrations range from 366 to 7,033 mg/l (COE 1985). The USGS <br />database seazch identified one well along the East Fork of Parachute Creek (~~ppendix K). This <br />well was analyzed for pH (7.3) and hazdness (580 mg/1) only. <br />Page 3-24; Meteorology and Air Quality <br />Visibility is considered an AQRV, and received special consideration in Section 169 of the Clean <br />Air Act. In accordance with the Clean Air Act, the Environmental Protection Agency (EPA) <br />has recently published regional haze <br />re ations, designed to protect the visual resources in the certain National P:~rks and Wilderness <br />areas. <br />The Piceance Creek Basin and Parachute Creek valley are Class II air quality areas, as are most <br />regions of the state. Class II attainment azeas under PSD regulations have specified allowable <br />increases (increments) of pollutants above legally defined baselines (background that may never <br />be exceeded. These areas aze also subject to state and/or national ambient stmdazds. Class II <br />PSD increments and applicable state and/or national ambient air quality standards (NAAQS) aze <br />listed in Table 3.5-2. Class I azeas (Figure 3.5-2), which have ~:~y <br />siaAdafds smaller PSD increments, aze also located in the region. These include the Flat Tops <br />and Mount Zirkel Wilderness Areas, which aze closest at 41 miles (66 km) acid 89 miles (143 <br />km), respectively 4~ess~.ulaclr-aFe • <br />. The Mazoon Bells Wilderness Area is 50 miles (80 <br />5-16 <br />
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