Myotis leibii

(Audubon and Bachman, 1842)

Eastern Small-footed Myotis

G4Apparently Secure Found in 8 roadless areas NatureServe Explorer →
G4Apparently SecureGlobal Rank
EndangeredIUCN
Medium - lowThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.106402
Element CodeAMACC01130
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNEndangered
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassMammalia
OrderChiroptera
FamilyVespertilionidae
GenusMyotis
Synonyms
Myotis subulatusMyotis subulatus leibii(Audubon and Bachman, 1842)
Other Common Names
Chauve-souris pygmée de l'Est (FR) Eastern Small-footed Bat (EN) Un Murciélago (ES) Vespertilion pygmée de l'Est (FR)
Concept Reference
Wilson, D. E., and D. M. Reeder (editors). 2005. Mammal species of the world: a taxonomic and geographic reference. Third edition. The Johns Hopkins University Press, Baltimore. Two volumes. 2,142 pp. [As modified by ASM the Mammal Diversity Database (MDD) at https://www.mammaldiversity.org/index.html]
Taxonomic Comments
Formerly, M. ciliolabrum was included as a subspecies of M. leibii (or M. subulatus). Analysis by Ammerman et al. (2016) of nuclear amplified fragment length polymorphism (AFLP) markers recovered distinct genetic lineages or clusters that corresponded to the recognized species defined by morphology, M. californicus, M. ciliolabrum, and M. leibii.
Conservation Status
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
Rank Reasons
Widespread in southeastern Canada and eastern United States; numerous localities but very spotty distribution; rarely found in large numbers; historically the total numbers counted have been very low in comparison to the total number of caves and mines surveyed; recent data indicate relatively stable populations and no apparent significant impact of white-nose syndrome.
Range Extent Comments
The 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).
Occurrences Comments
The number of distinct occurrences has not been determined using standardized criteria, but the species is represented by a large number of collection/observation sites and locations (as defined by IUCN). The species has been found in 289 hibernacula (USFWS 2013; time frame not reported). In recent years (but prior to the prevalence of white-nose syndrome), it was counted at approximately 125 hibernacula (Amelon and Burhans 2006). Recent surveys have greatly increased the number of localities above those known historically; the number of hibernacula may be significantly larger than currently known. Intensive cave and mine surveys have been undertaken in most states where the species occurs, but some sites probably remain unsearched in most states, and some likely roost sites are inaccessible to surveyors. Also, this relatively secretive bat may go undetected in sites where it is present.
Threat Impact Comments
The 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).
Ecology & Habitat

Description

This is a very small bat with tiny feet, a dark mask, and dark ears. The tragus is long and pointed, and the tail reaches the edge of the interfemoral membrane. There are no prominent chin or nose flaps. The dorsal pelage is pale yellowish brown to golden brown. The ears are black, and the face has a black "mask." The belly hair varies from pale buff to whitish. The bases of the hairs on the back are blackish; wing and tail membranes are very dark brown. The base of the interfemoral membrane and under surfaces of wing membranes are sparsely furred. The calcar has a definitive keel. Sexes are similar; females have two mammae. Size is very small, with total length 72 to 84 mm, tail 30 to 39 mm, hind foot 6 to 8 mm, forearm 30-36 mm, and wingspread 212 to 248 mm; adult mass is 3 to 8 grams (Banfield 1974, Godin 1977, Schwartz and Schwartz 1981, Merritt 1987).

Excellent photographs of small-footed bats and their skulls have been published, including Barbour and Davis (1969, 1974), Whitaker (1980), and Merritt (1987). Also see skull illustrations in van Zyll de Jong (1984).

Diagnostic Characteristics

This bat differs from other sympatric bats by a) small size, < 8.5 cm, b) small hind foot, < 8 mm, c) black face, d) long-keeled calcar, and e) absence of a dark shoulder patch. It differs from M. lucifugus by having golden-tinted, almost yellowish fur and a shorter forearm. It differs from Pipistrellus subflavus by its lighter color, especially the light pinkish forearms, and lack of a keeled sternum (Godin 1977). The skull is much flatter than that of M. lucifugus, and the braincase is narrower; a sagittal crest may be present (Banfield 1974, Godin 1977, Schwartz and Schwartz 1981, Merritt 1987). See Whitaker and Hamilton (1998) for a key to the vespertilionid bats of eastern North America.

Habitat

Habitat is mostly hilly or mountainous, generally in or near deciduous or coniferous forest. Like many other bat species, this one often forages over ponds and streams; foraging habitat also includes riparian forests, upland forests, clearings, stripmines, and ridgetops (see USFWS 2013). Foraging flights tend to be slow and often within a few meters of the ground or water surface (Davis et al. 1965; Brack et al., unpublished, cited by USFWS 2013).

Warm-season roosts may be primarily in cracks or crevices of rocky outcrops or talus slopes but also have been found in buildings (including the slate roof of a house), bridges (e.g., in expansion joints, guardrail crevices), towers, hollow trees, spaces beneath the loose bark of trees, road cuts, rocky dams, caves, and mines (Tuttle 1964, Barbour and Davis 1969, Best and Jennings 1997, Roble 2004, Johnson and Gates 2008, Johnson et al. 2011, O'Keefe and LaVoie 2011, USFWS 2013, Whitby et al. 2013). The species relies heavily on rock roosts or similar man-made structures during the summer months (Erdle and Hobson 2001, Johnson et al. 2011). Roosts often are exposed to the sun but also may be under moderate to extensive canopy cover (Johnson et al. 2011, Thomson and O'Keefe 2012). Recaptures of marked individuals in successive years indicate that the bats exhibit fidelity to their summer roosts (see USFWS 2013).

In West Virginia, M. leibii used primarily ground-level rock roosts in talus slopes and rock fields, and sometimes roosted in vertical cliff faces; males and females frequently switched roosts (Johnson et al. 2011). Ground-level roosts had low canopy cover but were located close to vegetation. Ground-level roosts generally were a few hundred meters from ephemeral water sources; roosts used by females were closer to ephemeral water sources than were those used by males.

In Tennessee, two individuals found in April were under a large flat rock at the edge of a quarry surrounded by woods and cow pastures (Tuttle 1964). In late July and early August in southern Illinois, many individuals, including post-lactating females and juveniles were found under loose rocks on exposed rock outcrops (Whitby et al. 2013). In Ontario, about 12 of these bats were found in July behind the door of a shed that was kept open (i.e., positioned against the wall) (Hitchcock 1955). These bats have been seen resting in limestone caves in West Virginia in spring and summer (Krutzsch 1966).

By far most records come from observations of bats hibernating in winter in caves and mine tunnels. Hibernation occurs in solution and fissure caves and mine tunnels (including coal, iron, copper, and talc mines). Dunn and Hall (1989) noted that 52 percent of Pennsylvania hibernacula were small caves of less than 150 meters (500 feet) in length. Situations near the entrance where the air is relatively cold and dry seem to be preferred (Barbour and Davis 1969), though sometimes deeper locations are used (Schwartz and Schwartz 1981). Roost sites often are deep in crevices, or under rocks or in crevices on the cave floor, where the bats can be very difficult to find (Davis 1955, Krutzsch 1966, Martin et al. 1966). These bats are usually found singly or occasionally in small clusters, but many may be packed in a crevice; often they hang among other species (Marin et al. 1966). Individuals exhibit a high degree of fidelity to hibernacula and can be found in the same site in multiple years (Gates et al. 1984).

Ecology

Possible predators include domestic cats, mink, raccoons, opossum, fish, frogs, snakes, and birds of prey. Most of these are known to prey occasionally on other Myotis species (Barbour and Davis 1969).

Reproduction

Breeding may occur in the fall, with the sperm stored in the uterus over winter. Active gestation lasts probably two months, with a single offspring born annually, probably in early July (Merritt 1987).

Survival rates are significantly lower for females (42%) than for males (76%) (van Zyll de Jong 1985). One individual is reported to have lived 12 years (Hitchcock 1965).

Colonies are usually small (< 15, e.g. Hitchcock 1955), though a few number in the hundreds. Small maternity colonies of 12 to 20 individuals occurring in buildings have been reported (Merritt 1987).
Terrestrial Habitats
Forest - HardwoodForest - ConiferForest - MixedBare rock/talus/screeCliff
Palustrine Habitats
RiparianAerial
Other Nations (2)
United StatesN3
ProvinceRankNative
TennesseeS2Yes
New HampshireS1Yes
MassachusettsS1Yes
IllinoisS1Yes
IndianaS2Yes
ArkansasS1Yes
District of ColumbiaSNRYes
VirginiaS2Yes
North CarolinaS2Yes
MissouriS2Yes
South CarolinaS2Yes
MarylandS1Yes
OhioSHYes
OklahomaS1Yes
VermontS1Yes
GeorgiaS2Yes
New YorkS2Yes
PennsylvaniaS2Yes
ConnecticutS1BYes
New JerseyS1Yes
MaineS1Yes
West VirginiaS2Yes
KentuckyS2Yes
CanadaN2
ProvinceRankNative
QuebecS1Yes
OntarioS2Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentNegligible (<1%)High (continuing)
1.1 - Housing & urban areasHigh (continuing)
2 - Agriculture & aquacultureNegligible (<1%)Moderate - slightHigh (continuing)
2.1 - Annual & perennial non-timber cropsHigh (continuing)
3 - Energy production & miningSmall (1-10%)Slight or 1-10% pop. declineHigh (continuing)
3.2 - Mining & quarryingHigh (continuing)
4 - Transportation & service corridorsNegligible (<1%)Moderate - slightHigh (continuing)
5 - Biological resource useNegligible (<1%)Moderate - slightHigh (continuing)
5.3 - Logging & wood harvestingHigh (continuing)
6 - Human intrusions & disturbanceRestricted - smallModerate - slightHigh (continuing)
6.1 - Recreational activitiesHigh (continuing)
7 - Natural system modificationsNegligible (<1%)Moderate - slightHigh (continuing)
7.1 - Fire & fire suppressionHigh (continuing)
7.2 - Dams & water management/useHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesRestricted - smallSerious or 31-70% pop. declineHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesHigh (continuing)
9 - PollutionUnknownUnknownHigh (continuing)
10 - Geological eventsNegligible (<1%)
11 - Climate change & severe weatherPervasive (71-100%)UnknownHigh (continuing)

Roadless Areas (8)
North Carolina (3)
AreaForestAcres
Chunky Gal (addition)Nantahala National Forest3,336
Lost CovePisgah National Forest5,944
Wesser BaldNantahala National Forest4,061
Virginia (5)
AreaForestAcres
Adams PeakGeorge Washington National Forest7,135
James River AdditionJefferson National Forest1,140
Kelley MountainGeorge Washington National Forest7,590
Saint Marys AdditionGeorge Washington National Forest1,454
The PriestGeorge Washington National Forest5,737
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