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have been where major highways crossed traditional migration routes (e.g., Interstate 70 near Rifle) or where roads <br />run through mule deer winter concentration areas or critical winter range (e.g., the Piceance Creek Road through <br />.Piceance Basin or the Parachute Creek Road from Parachute (Grand Valley) to the Union Oil Shale Plant). The <br />potential for big game road -kills associated with the Foidel Creek Mine would be expected to be much less than <br />these situations due to differences in the total number of animals involved and in the locations of roads with respect <br />to critical winter ranges. Several other factors tend to reduce the potential for road -kills associated with the Foidel <br />Creek Mine operation. First and foremost, employee shift changes will not coincide with the time period when <br />road -kill incidence is highest (sunset to four hours after). Secondly, the principal species of concern would be elk, <br />which by virtue of its size and behavior appears to be less prone to vehicle collisions. And lastly, the posted speed <br />limit for the haul road is 35 mph and will also be 35 mph for the Fish Creek Borehole /Shaft Area access road. <br />These speed limits should significantly reduce the potential for big game /vehicle collisions. <br />Aside from trying to assess the incidence of or potential for big game road - kills, the effectiveness of existing mass <br />transit systems and the cost/benefit ratio of installing such a system should also be analyzed for determining the <br />need for a mass transit system. There are few cases in the state where mass transit systems have been installed to <br />these systems, in terms of reduced incidence of road - kills. Mass transit systems were installed for the Tract C -a and <br />Tract C -b oil shale developments in Piceance Basin. The effectiveness of the mass transit system in reducing mule <br />deer road -kills was not analyzed by Tract C -a (per. comm. Jack Clark, Tract C -a), but some preliminary analysis <br />has been done by Tract C -b (per. comm. Tom Pysto, Occidental Oil Shale Company). Tract C -b has done some <br />preliminary modeling using data collected for several years on variables such as weather conditions, number of <br />road - killed deer, and traffic levels. The data collection period included the time span that their busing program was <br />in operation. Their preliminary findings have, interestingly, indicated that the number of mule deer road -kills were <br />relatively independent: of traffic levels and were more dependent on weather conditions and number of animals <br />concentrated along the road (pers. comm. Tom Pysto, Occidental Oil Shale Company). In other words, they had a <br />higher incidence of road - killed deer when snow levels forced deer to congregate along the road, and this increase <br />occurred independently of traffic levels. These findings may apply only to the Piceance Creek Road, but they do <br />pose some questions regarding the effectiveness of mass transit systems over other methods with respect to <br />• reducing big -game road - kills. <br />Information on cost/benefit analyses of mass transit systems used for reducing big -game road -kills is virtually <br />nonexistent since data. on their effectiveness are not readily available. Reed et al. (1982) used information on <br />vehicle repair costs, economic value of deer, the costs of establishment and maintenance of fencing, and incidence <br />of road - killed mule deer (before and after fencing) to compute a cost - benefit ratio for deer -proof fencing installed <br />along Interstate 70. In their paper, Reed et al. stressed that this type of analysis can only be conducted if before - <br />and -after big -game mortality figures are available for the mitigation technique in question. They also stressed that <br />the decision -maker should be especially cognizant of pre- existing mortality figures before expensive mitigation <br />techniques are employed. <br />In summary, factors such as posted speed limits and timing of peak traffic should considerably reduce the potential <br />for big - game /vehicle collisions. TCC will employ these measures as part of its procedures to minimize road - kills. <br />Since data on baseline levels and projected increases for road -kills are generally lacking, there is a need to have <br />road -kill figures available in order to identify problem areas or address the need or effectiveness of mitigation <br />measures. It is premature at this time to make a decision regarding the need for a mass transit system for the Foidel <br />Creek Mine. It may be advisable to monitor big -game road -kills along the access and haul roads to determine if <br />there is a need for a mass transit system or other mitigative measures. Details of a possible big -game road -kill <br />monitoring program are provided in the response to Rule 2.05.6(2). <br />Development of Road.-Kill Monitoring Plan for County Haulroad <br />One concern expressed by the wildlife regulatory agencies was that increased haul truck traffic, from the main <br />portal along the Country haulroad to the Fish Creek Tipple, may increase the incidence of mule deer or elk road- <br />• kills. The literature was reviewed to evaluate the feasibility of various monitoring programs. The monitoring <br />program was developed in consultation with the CDOW so that the most feasible and cost - effective program could <br />be formulated. <br />RN08 -05 2.04 -70 03/12/10 <br />