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• Mass Transit System Analysis and Bie Game Road-Kill Monitorine Plan <br />As discussed in the previous section, a[ least certain segments of [he access road and haul road proposed for the <br />Foidel Crcek 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 [ruck 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 />[he CMLRD and wildlife regulatory agencies have raised the concern that with increased traffic levels on these <br />roads, [he incidence of vehicle/big game collisions could become significant Related to this concern, the <br />regulatory agencies have requested [ha[ 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 <br />road-kills along [he 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 gamc road-kills are difficult to <br />derive. However, certain inferences on the potential for road-kills can be made based on projected traffic levels <br />for the mine, a general knowledge of the numbers of distribution of elk and mule deer near the areas of concern, <br />and previous road-kill studies. <br />• Coal haul [ruck 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 [his 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. <br />Shift changes for the access traffic are expected at 7:00 am, 3:00 pm, and 11:00 am. However, there is a <br />possibility [hat each of these changes may be modified. The amount of access traftc for each shift change during <br />peak traffic years (1992-2015) would be approximately 278, 278, and 238 cars on the access road around the time <br />of each 7:00 am, 3:00 pm, I I :00 am shift change, respectively. These numbers would be halved if two-for-one <br />car-pooling 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 <br />wildlife biologist) during aerial surveys for die general area indicate that the greatest numbers (400-500) of elk <br />occur in Twentymile park during migration in late fall and early winter. As winter progresses and snow levels in <br />the park increase, most of these animals move on to wintering areas to [he west of the penni[ area, although some <br />remain in critical winter range on the permit area (see Map 19, Elk Biological Features). There is less known <br />• concerning the migration of mule deer through Twentymile park, but numbers of migrating mule deer in the park <br />are thought to be significantly less than those observed for elk. In dte spring, elk migrate back to summer ranges, <br />but not as many are observed passing through the permit area due to their tendency [o stay along the mountain <br />shrub zones along the perimeter of the park. A summer population of elk also resides in the foothills along the <br />MR 97-154 2.04-7G Revised 10/02/97 <br />