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Florida black bear habitat ranked according to habitat preference, proximity of black bear habitat to large parcels of public land, roadless area patch size, and cover type diversity (Cox et al. 1994) 

Florida black bear habitat ranked according to habitat preference, proximity of black bear habitat to large parcels of public land, roadless area patch size, and cover type diversity (Cox et al. 1994) 

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Context 1
... population is now over 15 million people, while about 40 million tourists visit the state annually. Population growth, coupled with residential and commercial development and tourism, have created a strong demand for new roads or improvements, which can seriously impact important habitat systems and the fish and wildlife populations they support. Direct, secondary, and cumulative impacts of roads are well known (Wooding and Brady 1987, Mader 1984, Skoog 1982) and include loss of habitat, habitat fragmentation or degradation, and road mortality. In order to address these problems, the Florida Fish and Wildlife Conservation Commission (FWC) works in cooperation with the Florida Department of Transportation (FDOT) to avoid, minimize, or mitigate the impacts of highways on fish and wildlife resources. Our agency biologists provide technical assistance during the highway planning phase by recommending alternate alignments and designs on new roads or improvement projects to enhance habitat connectivity, protect large habitat systems on public and private lands, and reduce roadkills. A top mitigation priority in this ongoing effort is public land acquisition to increase the size of protected areas of high quality habitat. This paper presents the results of a cooperative effort in 2000 by our agency to provide a prioritized importance ranking of black bear roadkill areas to FDOT for guidance in siting wildlife underpasses on a statewide basis, and to better focus our agency efforts in impact avoidance and mitigation. The Florida black bear, which is listed by our agency as a threatened species, serves as a good focal species for transportation- related habitat connectivity and mortality issues because black bears utilize habitat at the landscape level. Bears also serve as an umbrella species for numerous other mammals, amphibians, and reptiles that occur in similar plant community types, and would benefit from highway structures installed to overcome the barrier effects of roads. We prioritized 15 black bear roadkill problem areas (Gilbert and Wooding 1996) by analyzing and evaluating the roadkill history and the landscape level habitat quality at each site. This was accomplished by converting existing statewide natural resource data, including public lands, Florida black bear Strategic Habitat Conservation Areas (SHCAs) (figure 1), and a ranked Florida black bear habitat map (figure 2) (Cox et. al. 1994, Kautz and Cox 2000) into a GIS (ARCVIEW Version 3.2) grid (196 m pixel). The data layers depict public conservation lands; strategic habitat areas on private land in need of protection or acquisition; and a bear habitat map scored 1 to 10 based on land cover types, proximity to conservation areas, habitat composition within large roadless areas, and habitat diversity. The public conservation lands and strategic conservation areas grids were merged together to create a single grid in which lands that were either in public ownership, or were a strategic habitat were given a value of “1", and all other areas were given a value of “0". Then, the public lands/strategic habitats grid was added to the scored black bear habitat grid to produce a grid with values ranging from 1 to 11. Scores of 11 reflected areas of Florida that were considered to be high quality habitats occurring on public land or within a strategic habitat. Scores of 1 reflected low quality bear habitat not occurring on public land or in a strategic habitat. The merged data layers resulted in a new scored statewide resource map that places greater emphasis on both existing and potential conservation lands available to bears, and shows defined areas where bear habitat protection and land acquisition should occur. The highway segments representing the problem areas were then digitized, and buffered outward 15 km. The result was a 30-km-wide elliptical zone around each problem area which was overlaid on the habitat map to determine a mean buffer habitat score. We also re-analyzed the bear roadkill data, which were systematically collected statewide by our agency from 1976 through 1999 to determine the current roadkill history at each problem area. Seven parameters were calculated for each problem area, and a total value was determined using the following formula to compare and rank the roadway segments: (% of total statewide road kills) + (% of kills in the past 10 years) + (kills per mile) + (adult female kills per mile) + (mean buffer habitat score) + (% of buffer encompassed by conservation lands) + (% of buffer composed of the bear SHCA). To account for differences in scale, the scores were normalized by taking each value as a percentage of the total values within each column for each parameter. Based on our analysis, black bear vehicle collisions occurred statewide, but tended to cluster at 15 chronic bear roadkill problem areas. The 15 roadkill problem areas varied in length from 2.4 to 34.0 miles, and collectively totaled 130 highway miles with a mean length of 8.7 miles. The problem areas were located within four FDOT Districts (1,3,5,7), which included Lake, Marion, Gulf, Hernando, Highlands, Jefferson, and Collier counties. Approximately 34.4 percent of the 729 bear roadkills with known kill locations recorded by our agency from 1976 through 1999 occurred within the problem areas. Table 1 is the prioritized list, while figure 3 depicts the actual location of the 15 chronic bear roadkill problem areas ranked according to the total sum of the normalized scores for each parameter. According to our analysis, the roadkill problem area on SR-46 in Lake County should receive the highest priority for construction of wildlife underpasses, followed by SR-40 through the Ocala National Forest, and US-98 in Jefferson County near the Aucilla River. The results of this study are now being used to address underpass placement to improve habitat connectivity of natural systems bisected by roads, and to reduce highway mortality of the black bear and other wildlife. FDOT began design work for the construction of a new wildlife underpass for the black bear on SR-46 in Lake County in the spring of ...

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... The construction of a series of crossing structures in this area would reduce risks to bears, mitigate additional mortality, and reduce the potential for genetic isolation. These structures should be designed and used with appropriate fencing to encourage bear use and strategically placed at existing bridge sites, at sites identified as having a history of bear-vehicle collisions (Gilbert et al. 2001), and at locations where pedestrian trails intersect the road. ...
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Of American black bears (Ursus americanus) killed by vehicles in Florida from 1976 to 2003, 45% were from the population in central Florida centered in Ocala National Forest (ONF). This area contains 8 of the state's 15 most severe roadkill areas. More bears were killed along State Road 40 (SR-40), which bisects this population, than along any other road in the state. Interest in widening this road provided an opportunity to document bear movements and the frequency with which they crossed SR-40 when average annual daily traffic (AADT) volume was at each of two levels: 5,100 vehicles per day (vpd) in ONF and 15,700 vpd in the adjacent community of Lynne. We analyzed the locations of 86 radiocollared bears (33 F40 M in ONF and 13 F in Lynne) and monitored them 1–3 times/week from May 1999 through May 2003. Forty-eight bears crossed SR-40 a minimum of 388 times. ONF female bears were 2.9 times more likely than Lynne females to cross SR-40, but this rate was only marginally significant. ONF male bears were 4.3 times more likely to cross SR-40 than ONF females and 12.3 times more likely to cross than were Lynne females. We documented the mortality of 7 radiocollared bears by vehicles, 4 males in ONF and 3 females in Lynne. There were no deaths of ONF females due to vehicular collisions, but female bears in Lynne died from vehicle collisions at near the rate of ONF male bears. We recommend that a minimum of 6 crossing structures be incorporated along this highway to reduce the effect of highway expansion on the Ocala population of Florida black bears.
... @BULLET Many of the vehicle-bear problem spots occur on S.R. 40 (Gilbert 2000). ...
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... Implications for Prioritization of Wildlife-Highway Problem Areas for Mitigation Current wildlife-transportation mitigation planning in many states is based primarily on decision-based prioritization models (Smith et al. 1998, Harris and Smith 1999; Schaefer and Smith 2000, Gilbert et al. 2002). Many states use such models to prioritize funding and rank sites for wildlife-highway mitigation projects, and these are based primarily on the presence of threatened and endangered species. ...
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... This technology can be used to create maps and query data, as well as to conduct more sophisticated analyses such as predicting human population growth patterns, modeling the spread of disease or invasive species, and evaluating land use change over time. GIS has become a common tool in wildlife management, used to evaluate habitat-species relationships for multiple purposes including locating rare species (Carter et al. 2006, Greaves et al. 2006, Rachlow and Svancara 2006, identifying areas for conservation (Singleton et al. 2004, Wikramanayake et al. 2004, Peralvo et al. 2005, and identifying hotspots for road kill (Gilbert et al. 2001). ...
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