Rank MethodLegacy Rank calculation - Excel v3.1x
Review Date2016-04-04
Change Date2015-03-11
Edition Date2015-03-31
Edition AuthorsHammerson, G.
Threat ImpactMedium - low
Range Extent200,000-2,500,000 square km (about 80,000-1,000,000 square miles)
Number of Occurrences81 - 300
Range Extent CommentsThe range extends from New England, southeastern Ontario, and southwestern Quebec south and west to southeastern Oklahoma, Arkansas, northern Alabama, northern Georgia, and northwestern South Carolina (Menzel et al. 2003). A map is included in Best and Jennings (1997). Within this range, the distribution is very spotty, and the bulk of the occurrences and largest populations are in New York, Pennsylvania, West Virginia, and western Virginia (Amelon and Burhans 2006). The majority of known hibernacula occur in Pennsylvania (n=55), New York (n=53), West Virginia (n=50), Virginia (n=33), Kentucky (n=26), and North Carolina (n=25) (USFWS 2013). This species is apparently extirpated in Connecticut and Ohio (where known from only one specimen). Elevational range extends to at least 700-800 meters in several states, at least 1,125 meters in Kentucky (see Best and Jennings 1997), and to at least 1,447 meters in North Carolina (O'Keefe and LaVoie 2011).
Threat Impact CommentsThe most serious threat to bats in eastern North America is white-nose syndrome (WNS), an often (but not always) lethal condition caused by a fungal pathogen that attacks hibernating bats. WNS was first noticed in 2006 in New York. Since its initial discovery, WNS has spread rapidly and now has been documented throughout the range of Myotis leibii (http://www.fws.gov/whitenosesyndrome/maps/WNSMap_060111_300dpi_DS.jpg). WNS affects Myotis leibii and several other bat species and has resulted in several million bat deaths in eastern North America. As of early 2015, WNS was still spreading but was confined primarily to areas east of the Mississippi River (plus several locations in Arkansas and Missouri, with suspected instances in Iowa and Minnesota). USFWS (2013) reviewed available information on population trends and WNS effects on M. leibii and concluded that WNS does not appear to have caused a significant population decline in hibernating M. leibii.
USFWS (2013) determined that although several activities, such as construction of physical barriers at cave accesses, mining, flooding, vandalism, development, and timber harvest may modify or destroy M. leibii habitat, these activities do not have significant, population-level effects on the species. Climate change, contaminants, wind energy development, and prescribed burning are not believed to be causing population declines in M. leibii (USFWS 2013). Some of these potential or localized threats are discussed further in the following paragraphs.
Closures of mines used for hibernation are a potential threat, but there is no evidence that mine closures are currently affecting Myotis leibii populations (USFWS 2011). Some mines may be threatened by collapse. Ceiling collapse may kill bats outright or, more significantly, alter cave microhabitat enough to make it unsuitable. A few cave occurrences are threatened or have been reduced in quality due to commercialization for tourism.
Threats to summer sites are unknown but likely to be moderate due to alteration of riparian habitats. Conversion of forested habitats to agricultural and residential uses has decreased the amount of preferred habitat in some areas, but the bats do make use of bridges and various other non-natural roost sites. Reliance on loose shale, talus, or karst formations often found in oil-, gas-, and mineral-rich lands makes M. leibii vulnerable to habitat loss associated with natural resource exploitation (Center for Biological Diversity 2010, USFWS 2011).
Development of wind power may pose a threat in some areas. Myotis leibii typically roosts in talus areas that occur on ridgetops. In the Appalachian Mountains, such roosting areas coincide with past, present, and anticipated future wind power development. Thus this bat may be exposed to both habitat loss due to project construction and direct mortality from turbine operation (Center for Biological Diversity 2010, USFWS 2011). However, significant mortality from turbines has not yet been documented (Arnett and Baerwald 2013).
Improper gating of caves to protect bats may result in site abandonment. For example, construction associated with commercializing the Fourth Chute Cave in Ontario, Canada, eliminated the circulation of cold air in one of the unvisited passages where a relatively large number of M. leibii hibernated; the bats were completely displaced as a result of the warmer microclimate produced (Mohr 1972). In other locations (e.g., Aitkin Cave, Pennsylvania), correctly installed gates led to increases in M. leibii populations (Butchkoski, pers. comm., 2012, cited by USFWS 2013).
Human disturbance is a potential threat at approximately half of the known hibernacula in Kentucky, Maryland, North Carolina, Vermont, and West Virginia, but there is no evidence that disturbance has led to population declines (USFWS 2013). With its small numbers and spotty distribution, isolated colonies of M. leibii are particularly vulnerable to extirpation by chance events, especially when concentrated during winter months. On the other hand, in contrast to certain other bats that assemble in vast numbers in relatively few sites, the population of M. leibii as a whole is not vulnerable to localized events.
THREATS TO BATS IN GENERAL: Other than white-nose syndrome, perhaps the most serious threat to cave-dwelling bats is human disturbance during hibernation. Very low levels of noise, light, and heat from lanterns are sufficient to awaken hibernating bats, which then expend energy moving about and deplete critical reserves of body fat. When disturbance is repeated, bats (especially juveniles) are likely to perish. "By the end of the winter energy reserves may be insufficient to meet the demands of the first feeding forays, when emerging insects may be scattered and scarce, or the bats may be too weak to make long flights to their summer territories" (Mohr 1976). Such disturbance is equally lethal, whether caused by vandals, well-meaning spelunkers, or bat researchers.
Intentional killing of bats in caves by clubbing, stoning, burning, bombing, etc,. has been a significant cause of mortality. Documented examples are numerous (Greenhall 1973, Harvey 1976, Tuttle 1979, and others). Bats are sometimes exterminated from commercial caves, or if not, leave or move to suboptimal habitats due to increased disturbance.
Poisoning by pesticides, heavy metals, and other environmental contaminants has been and may remain a significant threat (Clark 1988). Destruction of roost and foraging habitat by reservoir inundation, strip mining (especially limestone), deforestation, drainage of wetlands, development, etc., and pollution or siltation of waterways with consequent decline in insect production are additional potential adverse impacts (Tuttle 1979). Hundreds of thousands of bats have been destroyed by natural flooding of caves (Hall 1962, Brady 1979).