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Chapter 3 <br />Table 3-~ <br />Acres of Riparian Cover Types in Road Disturbance Buffers and Potential Methane Drainage R'ell <br />Locations <br /> Alternatives 2 and 3 <br />Cover Types <br />Riparian within Road Buffer Riparian within Methane Drainage Well <br />Locations <br />Marsh <1 0 <br />Willow and alder 8 3 <br />Aspen 1 0 <br />Herbaceous <1 0 <br />Total 10 3 <br />Design criteria stipulate MDW would not be <br />located in ripa~:-ian areas unless specifically <br />authorized. However, if MDW were located in <br />riparian areas, vegetation would be damaged <br />and destroyed and soils disturbed, increasing <br />the potential far erosion and surface water <br />sedimentation. Riparian sites would be <br />reclaimed in the same manner as upland sites. <br />However, due to additional available water, <br />riparian vegetation often recovers faster than <br />adjacent upland vegetation. Furthermore, <br />riparian species would likely recolonize the <br />area rapidly following reclamation due to <br />favorable site conditions for hydrophilic <br />vegetation. <br />Less than one acre of wetland vegetation is <br />located within proposed road corridors and <br />MDW windows (Table 3-8). Due to the limited <br />and sensitive nature of these habitats the <br />proposed action would avoid any impacts on <br />wetland vegetation. <br />Sensitive Plants <br />Surface disturbance from new road construc- <br />tion and MDW installation could affect sensi- <br />tive plants if it happens to occur in the same <br />location as a plant population. Design Criteria <br />state appropriate populations or habitats will be <br />surveyed on asite-specific basis prior to ground <br />disturbance. <br />Colorado tansy-aster has not been documented <br />in the project area, and if encounter would not <br />be impacted by the proposed action. If <br />populations are encountered they would be <br />avoided or other mitigation would be <br />implemented to avoid effects on plants or <br />populations, where possible. <br />Rocky Mountain thistle inay benefit from <br />drilling and associated surface disturbance by <br />the creation of suitable habitat (Panjabi and <br />Anderson 2004). If the species is present near <br />an area of disturbance, it may be able to <br />colonize newly disturbed areas. While this <br />species may be adversely affected by off-road <br />vehicle use or inadvertent targeting of the <br />species as part of a noxious weed control <br />program, these impacts are not likely to occur <br />as a result of the proposed project due to <br />required design criteria (Table 2-1). Surveys <br />for sensitive plants would be conducted in <br />likely habitats before disturbance occurs and <br />populations would be avoided or other <br />mitigation implemented to avoid effects on <br />plants or populations, if possible. During <br />sensitive plant surveys, any occurrence of <br />Rocky Mountain thistle would be flagged and <br />mapped to avoid inadvertent herbicide <br />application during weed treatments. Species <br />identif cation information should also be pro- <br />vided to the weed control agent to further <br />decrease the likelihood of species misidentifi- <br />cation. For these reasons, there will likely be a <br />beneficial impact to this species in the creation <br />of disturbance areas suitable for propagation. <br />Table 3-9 displays the surrunary determination <br />88 Deer Creek Ventilation Shaft and E Seain Methane Drainage Wells FEIS <br />1. <br />i-.: <br />i~~ <br />~ <br />• <br /> <br />