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2016-12-23_PERMIT FILE - C1982056A (8)
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2016-12-23_PERMIT FILE - C1982056A (8)
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Last modified
3/21/2017 9:27:01 AM
Creation date
2/13/2017 7:47:30 AM
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Template:
DRMS Permit Index
Permit No
C1982056A
IBM Index Class Name
Permit File
Doc Date
12/23/2016
Section_Exhibit Name
2.04 Environmental Resources
Media Type
D
Archive
Yes
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25 percent slopes, map units 68C and 68D. Soil cores #7 and 8 were mapped as Aaberg silty clay, 25-65% slopes, <br />map unit 35F. In Section 17, soil cores #10, 11 and 12 were located within the Binco silty clay loam, 3-25 percent <br />slopes, map units C10 and D10. A narrow inclusion of Cumulic Cryaquoll soil was observed in the small drainage <br />channel bisecting the ventilation pad area in Section 17 (Map 2S). <br />Maximum rooting depth at soil core #2 (Cumulic Cryaquoll) was observed into the seasonal high water table. Soil <br />mottling within the soil profile is a good indication of the depth of the seasonal high water table that can fluctuate <br />with the season and by year. Enhanced vegetation growth and plant species adapted to mesic and riparian sites was <br />also evident adjacent to soil core #2. Unconsolidated stream -laid sediments were observed at 25 inches and <br />exhibited free water within these unconsolidated gravels and coarse sands. Similar soil characteristics were <br />observed in the small drainage channel bisecting the ventilation pad area in Section 17 (Map 2S). <br />The maximum rooting depth at soil core #9 (Menbar series) was observed to a depth of 47 inches with a significant <br />decline in roots noted at shallower depths due to calcareous root restricting horizons. Unconsolidated stream -laid <br />sediments were observed below 105 inches and exhibited free water within these unconsolidated gravels and coarse <br />sands, however, no indicators of AVF soil characteristics were evident in this soil core within the rooting zone. <br />While this colluvial material may overlay water -bearing unconsolidated alluvial strata, these colluvial materials are <br />at a sufficient depth and contain shallow, calcareous root restricting horizons that prevent any subirrigation <br />potential. Reduced vegetation growth and production at this sampling site were evident from the plant species that <br />are more adapted to semi -arid, non -sub -irrigated sites. The field survey observed a distinct soil, vegetation, and <br />topographic boundary between the AVF and the upland portion of the study area containing the proposed <br />ventilation shaft facility access road. <br />Soil core descriptions, surface vegetation, and topographic relief indicate that the existing AVF boundary (as <br />previously defined in Exhibits 7b, 42a, and 46) along Fish Creek in Section 11 should be relocated as shown on <br />Map IS. Approximately 800 feet of proposed road corridor in Section 11 has been relocated upgradient <br />approximately 100 feet to follow an existing abandoned farmstead access road and avoid potential wetland soils <br />along the stock pond shoreline. The remaining 6,314 feet of access road corridor from the fenceline at the south <br />end of the stock pond to the shaft pad have no soil limitations. Soil coring and geologic stratigraphy strongly <br />suggest that the entire ventilation shaft pad is located on a suitable upland Winevada soil series formed over <br />fractured sandstone bedrock parent material. While the previous AVF boundary (shown in green on Map IS) is <br />located within the southwest corer of the shaft pad, the revised AVF boundary (shown in red on Map 1S) lies <br />outside of the proposed shaft pad location. Southern and western portions of the 500 -foot buffer that overlay the <br />Fish Creek channel contain AVF and wetland soils (Map IS). No soil mapping activities were performed on the <br />west side of the railroad corridor within the 500 -foot buffer area since pad and shaft construction activities will not <br />cross the railroad tracks. As construction activities are limited to the ventilation pad and northern and eastern <br />halves of the buffer area, no AVF or wetland soils will be affected. <br />The 9 -East Utility Borehole project area is immediately adjacent and to the south of the 18 -Left Ventilation Shaft <br />Road. Previous soil mapping did not include this area, so the most recent soil mapping (NRCS, 2006) and soil <br />descriptions for this area was obtained and reviewed. The soil types to be affected by disturbance are similar to <br />those for the nearby 18 -Right Vent Shaft disturbance (as discussed above), and include the Rabbitears loam, 3 to 12 <br />percent slopes (68C), and 12 to 25 percent slopes (68D), and the Winevada-Splitro complex, 3 to 25 percent slopes <br />(X8D). Soil depths (A and B1 horizons to gravel or clay) range up to 26 -inches (68C), 22 -inches (68D), and 38 - <br />inches (X81)), respectively. The site-specific soil mapping and soil descriptions have been added as Exhibit 16C, <br />Appendix 4, for reference. <br />MR16-296 2.04-50.2 05/10/16 <br />
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