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35 <br /> Table 2. Guild/species biological and ecological information related to habitat and connectivity needs, derived from <br /> information in Biotics (NatureServe 2019c) or, where noted, FEIS(Abrahamson nd). <br /> Focal Habitat and movement characteristics Sensitivityto <br /> Guild name species <br /> Taxonomic Barriers to development <br /> (habitat (species Primary stressors <br /> groups in guild Separation distance movement and <br /> type) onetworbservatk) Poe Hobitotcomposition Unsuitable Suitable fragmentation <br /> network{ size <br /> Habitat Habitat I= <br /> breeding:boggy streams,ephemeral Large streams Floodplain and <br /> Wet-mesic amphibians, wetlands,usually in floodplains or and rivers, wetland <br /> (riparian Four-toed , uplands near headwater streams roads, modification, <br /> forests <br /> hardwood 5 ha breeding birds salamander on-breeding:mesic hardwood 1 km 3 km suburban and High sensitivity human <br /> and odonates) orests,mixed hardwood/pine near urban disturbances,water <br /> etlands development pollution,roads <br /> Dry-wet reptiles, <br /> reeding:upland mixed 3-5 km High-traffic- <br /> ardwood/pine,successional(herb, plume roads, <br /> mixed amphibians, of 3 km(minimum Moderate <br /> hardwood/ (forest <br /> Box turtle 20 ha hrub,and woody) 1 km large rivers, Roads,habitat loss <br /> pine forests breeding birds) a cessioding:bottomland hardwood, used) ❑even <br /> sensitivity <br /> uccessional development <br /> Sparsely generalist reeding:upland and bottomland <br /> settled species of large ixed hardwood/pine,successional, None; Roads,dense <br /> mixed and small Bobcat 60 ha 50krn` 200 km` <br /> b ith logs,fallen trees,or rock shelters avoidance of Moderate development, <br /> hardwood/ mammals, or denning buildings and sensitivity human <br /> pine habitats reptiles,(birds) on-breeding:upland and bottomland development disturbances <br /> nixed hardwood/pine,successional <br /> aData in Biotics(NatureServe 2019c)indicate home range size of less than 1 ha;however,to avoid including spurious patches <br /> and to avoid excessive GIS computation time,the observed minimum patch size of approximately 5 ha(based on species <br /> observations in the project area)was used. <br /> 'Derived from minimum Bobcat home range provided in FEIS(Abrahamson nd). <br /> "Derived from Bobcat dispersal information in Biotics(NatureServe 2019c).Dispersal distances for Timber rattlesnake are lower <br /> (7 and 1 km for suitable and unsuitable habitat,respectively),but species observation data do not conclusively support the current <br /> presence of Timber rattlesnake populations in the project area. <br /> Barriers.By definition, characteristics of barriers are similar for terrestrial species within the same guild. <br /> Information in Biotics indicates that developed areas, some roads, and some water bodies are the primary <br /> barriers to movement for the focal species and habitat guilds in this project(Table 2). Developed areas <br /> were identified from developed land cover classes in the EVT layer(LANDFIRE 2014) and building <br /> footprint layers combined across the project area(Apex 2017, Carrboro 2017, Cary 2018, Chatham <br /> County 2015, Durham City-County 2017, Orange County 2010). Areas of open water(large rivers, lakes, <br /> and ponds)were identified from the EVT and NWI(US Fish and Wildlife Service 2017) layers. Streams <br /> that were not wide enough to be identified as open water in the EVT classification were not considered <br /> barriers. To classify roads as either barriers or non-barriers,the scientific literature(as compiled in Ernest <br /> & Sutherland 2017)provides details on traffic volume,road characteristics, and roadway structures that <br /> likely represent barriers to movement for large-and small-animal species groups(adapted for this project <br /> as in Table 3). Roads, road characteristics,roadway structures,and traffic volume data for the project area <br /> were obtained from NCDOT(2019a, 2017). <br /> To represent known or potential wildlife crossing locations,barrier roads were considered permeable to <br /> wildlife passage via known and presumed crossing structures(such as bridges, culverts, or pipes). Bridge, <br /> culvert, and pipe location data were obtained from NCDOT (2019b). Ultimately,however,potential <br /> wildlife crossings were represented primarily as intersections between barrier roads and permanent <br /> streams from the National Hydrography Dataset(USGS 2018)because of incomplete mapping of bridge, <br /> culvert,and pipe locations throughout the project area. Bridge locations over non-barrier roads were <br /> included as potential crossing locations for the sparsely settled mixed habitats guild. <br /> 22 A Landscape Plan for Wildlife Habitat Connectivity <br />