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2018-08-08_PERMIT FILE - C1982056A (11)
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2018-08-08_PERMIT FILE - C1982056A (11)
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Last modified
8/30/2023 12:54:45 PM
Creation date
9/17/2018 7:27:46 AM
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Template:
DRMS Permit Index
Permit No
C1982056A
IBM Index Class Name
Permit File
Doc Date
8/8/2018
Section_Exhibit Name
2.04 Environmental Resources
Media Type
D
Archive
Yes
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Mass Transit System Analysis and Big Game Road-Kill Monitoring Plan <br /> As discussed in the previous section, at least certain segments of the access road and haul road proposed for the <br /> Foidel Creek Mine pass in close proximity to portions of big game winter concentration areas or critical winter <br /> range. Haul truck traffic will travel along existing County Roads No. 27 and No. 33, and haul truck traffic along <br /> these roads will be significantly increased by the proposed mine operation. The Fish Creek Borehole/Shaft access <br /> road will primarily follow existing dirt roads, although some widening and upgrading of the existing roads will be <br /> necessary (see Map 19, Elk Biological Features, and Map 20, Mule Deer Biological Features, for proposed road <br /> locations). <br /> Because of the proximity of these roads to mule deer and elk winter concentration areas and critical winter range, <br /> the CMLRD and wildlife regulatory agencies have raised the concern that with increased traffic levels on these <br /> roads, the incidence of vehicle/big game collisions could become significant. Related to this concern, the <br /> regulatory agencies have requested that TCC analyze the potential need for instituting a mass transit system for its <br /> employees using the Fish Creek Borehole/Shaft Area access road and develop a plan for monitoring big game road- <br /> kills along the haul road. This section will address these requests. <br /> In order to evaluate the potential need for a mass transit system, information on the actual or expected incidence of <br /> big game road-kills should be available. Since monitoring of road-kills has not previously occurred along county <br /> roads adjacent to the permit area, information on the expected incidence of big game road-kills are difficult to <br /> derive. However, certain inferences on the potential for road-kills can be made based on projected traffic levels for <br /> the mine, a general knowledge of the numbers of distribution of elk and mule deer near the areas of concern, and <br /> previous road-kill studies. <br /> Coal haul truck and employee automobile access traffic levels projected for the Foidel Creek Mine are provided on <br /> Table 44, Truck Haulage, and Table 45, Auto Access Traffic. Peak haul truck traffic would occur in 1987 with 90 <br /> loads per day or approximately one haul load on the road every fifteen minutes. Return travel by empty trucks <br /> would double these numbers. The auto access traffic levels are based on each employee driving his own vehicle. <br /> These levels would be reduced significantly by car-pooling. The current level of car-pooling by TCC personnel is <br /> approximately two employees for each car. If this trend continues during development and operation of the Foidel <br /> Creek Mine, a 50 percent reduction in automobile access traffic would be realized. Peak automobile access traffic <br /> would occur in 1992 at 397 round trips per day and remain constant until 2015. If one assumes car-pooling would <br /> occur at the rate of two people for each car, the maximum access traffic level would be reduced to approximately <br /> 200 round-trips per day. In 2016, total daily traffic on RCR27 was approximately 835 vehicles (all types) per day, <br /> with 510 being passenger vehicles, 295 being commercial trucks, and 30 being coal haul trucks. <br /> Shift changes for the access traffic are expected at 7:00 am, 3:00 pm, and 11:00 am. However,there is a possibility <br /> that each of these changes may be modified. The amount of access traffic for each shift change during peak traffic <br /> years (1992-2015) would be approximately 278, 278, and 238 cars on the access road around the time of each 7:00 <br /> am, 3:00 pm, 11:00 am shift change, respectively. These members would be halved if two-for-one car-pooling <br /> occurs. <br /> The total magnitude of elk and mule deer migration through the permit area and use of critical winter range in the <br /> permit area has not been well documented. General observations made by Terrell Johnson (the Applicant's wildlife <br /> biologist) during aerial surveys for the general area indicate that the greatest numbers (400-500) of elk occur in <br /> Twentymile park during migration in late fall and early winter. As winter progresses and snow levels in the park <br /> increase, most of these animals move on to wintering areas to the west of the permit area, although some remain in <br /> critical winter range on the permit area (see Map 19, Elk Biological Features). There is less known concerning the <br /> migration of mule deer through Twentymile park, but numbers of migrating mule deer in the park are thought to be <br /> significantly less than those observed for elk. In the spring, elk migrate back to summer ranges, but not as many <br /> are observed passing through the permit area due to their tendency to stay along the mountain shrub zones along the <br /> perimeter of the park. A summer population of elk also resides in the foothills along the <br /> RN 17-07 2.04-76 02/15/18 <br />
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