Although previously well-documented in the mountains of the Blue Ridge Ecoregion of western North Carolina, the northern long-eared bat Myotis septentrionalis was only recently discovered in coastal North Carolina in 2007. After being listed as a federally threatened species in April 2015, a five-year effort of mist net surveys and tracking was initiated to better understand the species’ distribution and behavior in eastern North Carolina. Since 2015, 163 healthy northern long-eared bats have been captured, and the documented range of the species has expanded from 4 coastal counties to 19. Captures occurred in all months of the year and mostly occurred in or adjacent to wetland forests. Captures were limited to the Middle Atlantic Coastal Plain Ecoregion of the state, and the maximum distance from the Atlantic Ocean or associated sounds was <87 km. Northern long-eared bats have not been documented in the Southeastern Plains or Piedmont Ecoregions of North Carolina. The lack of captures in the middle portion of the state suggests geographically disjunct populations of the species in North Carolina. During late fall–winter netting and tracking, northern long-eared bats were observed to be active throughout most of the winter and roosted in trees. Across three late fall–winter seasons from 2015–2018, 43 northern long-eared bats were tracked to 165 winter roost trees. Most (94.6%) winter roost trees occurred in wetland forest. Winter roost trees varied greatly in species, diameter-at-breast-height, status (dead or live), and type of roost (cavity, crack, crevice, or exfoliating bark). The species’ lack of long-term hibernation in coastal North Carolina documents a vastly different survival strategy as opposed to the well-documented hibernation strategy the species is known to use in the rest of its range. This portion of the state is nearly devoid of caves or mines suitable for hibernacula, but also experiences milder winters with low-level insect activity. During spring 2019, 21 reproductive females were captured in the northernmost portion of the coastal plain of North Carolina and tracked to 64 maternity roost trees. Pregnant females began to be captured on April 25, and juveniles began to be captured on June 16. This indicates that pups are likely born in late May in the northern portion of the coastal plain of North Carolina, but birth likely occurs earlier in the southern portion of the coastal plain of the state. Most (92.2%) maternity roost trees occurred in wetland forest. Maternity roost trees varied greatly in species, diameter-at-breast-height, status, and type of roost. Swab samples collected during late fall–winter from 198 bats from species susceptible to white-nose syndrome provided no evidence of Pseudogymnoascus destructans. Since northern long-eared bats in coastal North Carolina are active most of the winter and not dependent upon caves or mines for hibernation, they are likely not susceptible to white-nose syndrome. With the species in sharp decline elsewhere due to white-nose syndrome, this coastal North Carolina population and a recently discovered coastal South Carolina population may serve as a refugium for the species.