Myotis grisescens

A.H. Howell, 1909

Gray Myotis

G3Vulnerable (G3G4) Found in 147 roadless areas NatureServe Explorer →
G3VulnerableGlobal Rank
VulnerableIUCN
High - mediumThreat Impact
Gray bat (Myotis grisescens). Photo by U.S. Fish & Wildlife Service, Public Domain (U.S. Government Work), via ECOS.
U.S. Fish & Wildlife Service, https://www.usa.gov/government-works
Identity
Unique IDELEMENT_GLOBAL.2.104746
Element CodeAMACC01040
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNVulnerable
Endemicendemic to a single nation
KingdomAnimalia
PhylumCraniata
ClassMammalia
OrderChiroptera
FamilyVespertilionidae
GenusMyotis
Other Common Names
Gray Bat (EN)
Concept Reference
Wilson, D. E., and D. M. Reeder (editors). 1993. Mammal species of the world: a taxonomic and geographic reference. Second edition. Smithsonian Institution Press, Washington, DC. xviii + 1206 pp. Available online at: http://www.nmnh.si.edu/msw/.
Taxonomic Comments
Monotypic (Decher and Choate 1995).
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2021-12-02
Change Date2021-12-02
Edition Date2015-08-21
Edition AuthorsHammerson, G.
Threat ImpactHigh - medium
Range Extent200,000-2,500,000 square km (about 80,000-1,000,000 square miles)
Rank Reasons
Essentially restricted to the cave region of the eastern and central United States; many occupied caves (hundreds) exist, and population size is large (a few million), but relatively few caves hold most of the population; total population and number of occupied caves increased in recent decades, due to ongoing cave protection efforts, but some occupied caves remain vulnerable to disturbance. Despite large population size and good recovery, the species is regarded as vulnerable to potential massive mortality from white-nose syndrome (no significant impact was known as of early 2015). The conservation status and rank should be reviewed in the near future as more information becomes available on the impact of white-nose syndrome on this species.
Range Extent Comments
The range extends from southeastern Kansas and central Oklahoma east to western Virginia and western North Carolina, and from Missouri, Illinois, and Indiana south to southern Alabama and northern Florida (Decher and Choate 1995).The primary range is concentrated in the cave regions of Alabama, Arkansas, Kentucky, Missouri and Tennessee, with smaller populations found in adjacent states, including a growing population in a quarry in Clark County, Indiana (USFWS 2009). Summer and winter ranges are essentially the same.
Occurrences Comments
The number of distinct occurrences (subpopulations) has not been determined using standardized criteria. Martin (2007) listed the species as occurring in 384 caves scattered across 11 states (his analysis did not include Indiana). Summering populations of gray bats use multiple caves, and movement between caves is considerable (Tuttle 1976a, Martin 2007).
Threat Impact Comments
Decline began with cave disturbance associated with saltpeter production during the Civil War. Some of the largest colonies were lost as a result of cave commercialization. Some caves were improperly gated.

Cave disturbance was the major factor in the historical decline. Cave protection efforts have greatly reduced this threat. However, human disturbance is the main reason for the continued decline of gray bats in caves that are not protected (USFWS 2009). The species is especially vulnerable due to its high fidelity to particular favored caves, and it is very sensitive to disturbance, including the mere presence of humans with lights; disturbance may result in bats moving to less favorable roosting places.

White-nose syndrome (WNS) recently was detected in this species. This emerging disease potentially could cause large, rapid declines. As of early 2015, no significant impact of the disease had been observed.

The use of forestry insecticides and crop pesticides in areas adjacent to riparian corridors where gray bats forage may reduce the prey base or kill bats that ingest contaminated insects (Northern Prairie Wildlife Research Center). Pesticide contamination (e.g., Clawson and Clark 1989, Clawson 1991) remains a concern but currently is not known to be causing declines (USFWS 2009).

Other threats include deforestation and impoundment of waterways (and subsequent cave inundation). Natural and human-caused flooding remains a secondary threat at some gray bat sites (USFWS 2009).

This species is not known to incur significant mortality from turbines at wind energy facilities (Arnett and Baerwald 2013).

Climate change could have a significant impact on gray bats. It is projected that a rise in ambient temperature could make traditional and currently occupied hibernacula and maternity sites unsuitable for roosting gray bats and cause a shift in the species' range northward. This could adversely affect the species' food supply, or affect the ability of bats to adequately deposit important fat reserves that are critical for winter survival (USFWS 2009). However, no documentation of such effects currently exists (USFWS 2009).
Ecology & Habitat

Description

A bat with unicolored dorsal fur (gray after the mid-summer molt, at other times sometimes chestnut brown or russet); paler below, with hairs darker basally; wing membrane (gray) connects to the foot at the ankle; calcar is unkeeled; total length 80-105 mm; forearm length 40-46 mm; ear length 14-16 mm; tail length 33-45 mm; hind foot 9-12 mm; mass 7-16 g (usually 8-10 g). wingspread 275-300. Distinct sagittal crest on skull. Teeth 38; dentition I 2/3, C 1/1, P 3/3, M 3/3 (Barbour and Davis 1969, Sealander 1979).

Diagnostic Characteristics

Most likely to be confused with M. lucifugus, M. sodalis, M. austroriparius, and M. septentrionalis. Distinguished from these by uniform-colored dorsal fur from base to tip (all others have contrasting shades, bi- or tri-colored dorsal fur) and by attachment of wing membrane at ankle, not at base of toe (Barbour and Davis 1969, Tuttle 1978).

Habitat

Roost sites are nearly exclusively restricted to caves throughout the year (Hall and Wilson 1966, Barbour and Davis 1969, Tuttle 1976), though only a few percent of available caves are suitable (Tuttle 1979). Winter roosts are in deep vertical caves with domed halls. Large summer colonies utilize caves that trap warm air and provide restricted rooms or domed ceilings; maternity caves often have a stream flowing through them and are separate from the caves used in summer by males.

Occasionally non-cave roost sites are used. Hays and Bingman (1964) reported a colony in a storm sewer in Pittsburg, Kansas and, in 1988, a maternity colony was discovered using a storm sewer in Kansas (Decher and Choate 1988). Harvey and McDaniel (1988) located a maternity colony in a storm sewer in downtown Newark, Independence County, Arkansas. There are occasional reports of mines (Sealander 1979, Thom 1981, Brack et al. 1984, Harvey 1988) and buildings (Gunier and Elder 1971) being used as roost sites.

Winter caves are deep and vertical and provide a large volume of air below the lowest entrance that acts as a cold air trap (Tuttle 1976). Cold air flows in and is trapped during successive winters, providing mean annual temperatures 6 degrees C or more below the above-ground mean annual temperature (Tuttle 1978). Hibernation sites often have multiple entrances, good air flow (Martin 2007), and temperatures of approximately 5-9 C, though 1-4 C may be preferred (Tuttle and Kennedy 2005).

In the summer, maternity colonies prefer caves that act as warm air traps or that provide restricted rooms or domed ceilings that are capable of trapping the combined body heat from thousands of clustered individuals (Tuttle 1975, Tuttle and Stevenson 1977). Cave temperatures range from 14 to 24 C. Undisturbed summer colonies may contain up to 250,000 bats, and average 10,000 to 25,000 (Tuttle 1979). Summer caves are nearly always located within 1 km of a river or reservoir over which the bats forage (Tuttle 1979).

Tuttle (1979) showed that forested areas along the banks of streams and lakes provide important protection for adults and young. Young often feed and take shelter in forest areas near the entrance to cave roosts (Tuttle 1979). Do not feed in areas along rivers or reservoirs where the forest has been cleared (LaVal et al. 1977; Tuttle and Stevenson, in prep.).

Yearlings and adult males segregate into nomadic summer colonies that tend to roost in caves within a few kilometers of ones selected by adult females (Layne 1978).

Ecology

Forage in loose groups, but become territorial when insect numbers decrease; territories seem to be controlled by reproductively-active females (Tuttle et al.).

Elder and Gunier (1981) determined that the mean annual survival rate is about 70% in males and 73% in females. Stevenson and Tuttle (1981) found that the after-first-year survival rate is about 55 to 85% in relatively undisturbed colonies, and 57 to 66% in disturbed colonies. Mortality is especially high in spring migration when fat reserves and food supply are low (Tuttle and Stevenson 1977).

Reproduction

Mating occurs in September-October. Adult females store sperm through the winter and become pregnant soon after emergence from hibernation (Gutherie and Jeffers 1938, Harvey 1994, Tuttle and Kennedy 2005)). One young is born late in May or in early June (reported as mid-June for Oklahoma; flying as early as late June or early July). In Florida, young are weaned in mid-July (Layne 1978). Larger colonies are more successful in raising young. Most young are able to fly in 20-35 days, depending on colony size. Individual females typically do not produce young until their second year. Recorded maximum longevity approximately 14-17 years but may be longer (Harvey 1992, Tuttle and Kennedy 2005). Maternity colonies include from a few hundred to many thousands of individuals.

Tuttle (1975) showed that growth rates of non-volant young are positively correlated with colony size, probably because increasing numbers of bats clustering together reduce the thermoregulatory cost per individual (Herreid 1963, 1967). In larger colonies, most young begin to fly from 20 to 25 days after birth, while in smaller colonies, or where colonies have been reduced due to disturbance, this time is increased to 30 to 35 days (Tuttle 1976). In severely reduced colonies, the young sometimes die before achieving flight (Tuttle in Brady et al. 1982). For newly volant young, growth rates and survival are inversely proportional to the distance from their roost to the nearest over-water foraging habitat (Tuttle 1976). Although mothers continue to nurse young for a period after the young are flying, juveniles are apparently left to learn how to hunt on their own (Tuttle and Stevenson).
Palustrine Habitats
Riparian
Other Nations (1)
United StatesN3
ProvinceRankNative
FloridaS1Yes
North CarolinaS1Yes
KansasS1BYes
OklahomaS1Yes
AlabamaS2Yes
South CarolinaS1Yes
MissouriS3Yes
GeorgiaS2Yes
KentuckyS2Yes
IllinoisS1Yes
IndianaS1Yes
TennesseeS2Yes
VirginiaS1Yes
ArkansasS2Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentNegligible (<1%)High (continuing)
2 - Agriculture & aquacultureLarge - smallUnknownHigh (continuing)
3 - Energy production & miningNegligible or <1% pop. declineHigh (continuing)
4 - Transportation & service corridorsSmall (1-10%)Negligible or <1% pop. declineHigh (continuing)
5 - Biological resource useNegligible (<1%)Slight or 1-10% pop. declineHigh (continuing)
5.3 - Logging & wood harvesting
6 - Human intrusions & disturbanceSmall (1-10%)Moderate - slightHigh (continuing)
6.1 - Recreational activitiesHigh (continuing)
7 - Natural system modificationsSmall (1-10%)Moderate - slightHigh (continuing)
7.2 - Dams & water management/use
8 - Invasive & other problematic species, genes & diseasesPervasive - restrictedSerious or 31-70% pop. declineModerate (short-term)
8.1 - Invasive non-native/alien species/diseases
9 - PollutionLarge - smallNegligible or <1% pop. declineHigh (continuing)
10 - Geological eventsNegligible (<1%)
11 - Climate change & severe weatherPervasive (71-100%)UnknownHigh (continuing)

Roadless Areas (147)
Alabama (5)
AreaForestAcres
Blue MountainTalladega National Forest4,986
Cheaha ATalladega National Forest236
Cheaha BTalladega National Forest741
Oakey MountainTalladega National Forest6,129
Reed BrakeTalladega National Forest621
Arkansas (10)
AreaForestAcres
Clifty CanyonOzark-St. Francis National Forest1,963
Devils CanyonOzark-St. Francis National Forest1,877
Dismal CreekOzark-St. Francis National Forest9,160
East ForkOzark-St. Francis National Forest13,037
Gee CreekOzark-St. Francis National Forest7,957
Hurricane CreekOzark-St. Francis National Forest2,279
Indian CreekOzark-St. Francis National Forest7,855
Pedestal RocksOzark-St. Francis National Forest21,957
PenhookOzark-St. Francis National Forest6,566
Richland CreekOzark-St. Francis National Forest571
Georgia (23)
AreaForestAcres
Ben GapChattahoochee National Forest1,292
Big MountainChattahoochee National Forest1,974
Boggs CreekChattahoochee National Forest2,073
Cedar MountainChattahoochee National Forest1,083
Duck BranchChattahoochee National Forest194
Ellicott Rock AdditionChattahoochee National Forest690
Foster BranchChattahoochee National Forest171
Helton CreekChattahoochee National Forest2,348
Indian Grave GapChattahoochee National Forest1,020
Joe GapChattahoochee National Forest5,321
Kelly RidgeChattahoochee National Forest8,325
Ken MountainChattahoochee National Forest527
Lance CreekChattahoochee National Forest9,025
Miller CreekChattahoochee National Forest701
Patterson GapChattahoochee National Forest1,186
Pink KnobChattahoochee National Forest12,127
Rocky MountainChattahoochee National Forest4,269
Sarah's CreekChattahoochee National Forest6,888
Shoal BranchChattahoochee National Forest413
Tate BranchChattahoochee National Forest1,069
Tripp BranchChattahoochee National Forest615
Turner CreekChattahoochee National Forest1,495
Wilson CoveChattahoochee National Forest545
Idaho (1)
AreaForestAcres
Bear CreekCaribou-Targhee National Forest118,582
Illinois (6)
AreaForestAcres
Bay CreekShawnee National Forest120
Burden FallsShawnee National Forest485
Burke BranchShawnee National Forest6,231
Clear SpringsShawnee National Forest11
Eagle CreekShawnee National Forest38
Ripple HollowShawnee National Forest3,788
Indiana (1)
AreaForestAcres
Mogan RidgeHoosier National Forest8,435
Kentucky (1)
AreaForestAcres
WolfpenDaniel Boone National Forest2,835
Missouri (5)
AreaForestAcres
Anderson Mountain Rare II Study AreaMark Twain National Forest2,741
Big Creek Rare II Study AreaMark Twain National Forest9,277
Irish Rare II Study AreaMark Twain National Forest1,226
Spring Creek Rare II Study AreaMark Twain National Forest4,899
Swan Creek Rare II Study AreaMark Twain National Forest7,310
North Carolina (31)
AreaForestAcres
Bald MountainPisgah National Forest11,085
Balsam ConePisgah National Forest10,591
Barkers Creek (addition)Nantahala National Forest975
BearwallowPisgah National Forest4,113
Big Indian (addition)Nantahala National Forest1,155
Boteler PeakNantahala National Forest4,205
Cheoah BaldNantahala National Forest7,795
Cherry Cove (addition)Nantahala National Forest836
Chunky Gal (addition)Nantahala National Forest3,336
Craggy MountainPisgah National Forest2,657
Dobson KnobPisgah National Forest6,111
Graveyard Ridge (addition)Pisgah National Forest1,958
Harper CreekPisgah National Forest7,325
Jarrett CreekPisgah National Forest7,485
Laurel MountainPisgah National Forest5,683
Linville Gorge AdditionPisgah National Forest2,809
Little Indian (addition)Nantahala National Forest640
Lost CovePisgah National Forest5,944
Mackey MountainPisgah National Forest5,934
Middle Prong AdditionPisgah National Forest1,852
Overflow CreekNantahala National Forest3,379
Sam Knob (addition)Pisgah National Forest2,576
Sharptop Ridge (addition)Nantahala National Forest600
Slide HollowPisgah National Forest193
SnowbirdNantahala National Forest8,489
South Mills RiverPisgah National Forest8,588
Tusquitee BaldNantahala National Forest13,670
Wesser BaldNantahala National Forest4,061
Wilson CreekPisgah National Forest4,863
Woods MountainPisgah National Forest9,602
Yellowhammer Branch (add.)Nantahala National Forest1,255
South Carolina (4)
AreaForestAcres
Bee CoveSumter National Forest3,025
Big MountainSumter National Forest2,337
Ellicott Rock 1Sumter National Forest301
Ellicott Rock 2Sumter National Forest517
South Dakota (1)
AreaForestAcres
Indian CreekBuffalo Gap National Grassland24,666
Tennessee (21)
AreaForestAcres
Bald MountainCherokee National Forest11,743
Bald River Gorge AdditionCherokee National Forest1,728
Beaver Dam CreekCherokee National Forest5,070
Big Frog AdditionCherokee National Forest369
Big Laurel Branch AdditionCherokee National Forest5,577
Big Laurel Branch AdditionCherokee National Forest5,577
Brushy RidgeCherokee National Forest7,469
Devil's BackboneCherokee National Forest4,287
Devil's BackboneCherokee National Forest4,287
Flint Mill GapCherokee National Forest9,494
Flint Mill GapCherokee National Forest9,494
Joyce Kilmer Slickrock Add.Cherokee National Forest1,396
Little Frog Addition NECherokee National Forest321
Little Frog Addition NWCherokee National Forest628
London Bridge BranchCherokee National Forest3,387
Rogers RidgeCherokee National Forest4,738
Sampson Mountain AdditionCherokee National Forest3,064
Slide HollowCherokee National Forest4,057
Stone MountainCherokee National Forest5,367
Sycamore CreekCherokee National Forest6,984
Upper Bald RiverCherokee National Forest9,202
Virginia (27)
AreaForestAcres
Bear CreekJefferson National Forest18,274
Beartown Addition AJefferson National Forest1,370
Beartown Addition BJefferson National Forest2,985
Beaver Dam CreekJefferson National Forest1,135
Brushy MountainJefferson National Forest4,168
Dry River (VA)George Washington National Forest1
Garden MountainJefferson National Forest3,960
Gum RunGeorge Washington National Forest12,620
Horse HeavenJefferson National Forest4,748
Hunting Camp Little Wolf CreekJefferson National Forest8,953
Kimberling Creek Addition AJefferson National Forest89
Kimberling Creek Addition BJefferson National Forest196
Laurel ForkGeorge Washington National Forest9,967
Lewis Fork AdditionJefferson National Forest749
Little Dry Run AdditionJefferson National Forest2,204
Little RiverGeorge Washington National Forest27,292
Little Walker MountainJefferson National Forest9,818
Little Wilson Creek Addition AJefferson National Forest78
Little Wilson Creek Addition BJefferson National Forest1,725
Long SpurJefferson National Forest6,417
New London Bridge BranchJefferson National Forest844
North Fork PoundJefferson National Forest4,757
Oak KnobGeorge Washington National Forest10,882
Raccoon BranchJefferson National Forest4,388
Rogers RunJefferson National Forest181
Seng MountainJefferson National Forest6,428
SkidmoreGeorge Washington National Forest5,641
West Virginia (11)
AreaForestAcres
Canaan LoopMonongahela National Forest7,867
Cheat MountainMonongahela National Forest8,191
Dolly Sods Roaring PlainMonongahela National Forest13,392
Dry ForkMonongahela National Forest657
Dry River (WV)George Washington National Forest7,331
East Fork Of GreenbrierMonongahela National Forest7,167
Glady ForkMonongahela National Forest3,239
Laurel ForkMonongahela National Forest1,172
Mcgowan MountainMonongahela National Forest10,504
North Mountain HopevilleMonongahela National Forest6,525
Seneca CreekMonongahela National Forest22,287
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