Lasionycteris noctivagans

(Le Conte, 1831)

Silver-haired Bat

G4Apparently Secure Found in 44 roadless areas NatureServe Explorer →
G4Apparently SecureGlobal Rank
Least concernIUCN
High - mediumThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.104362
Element CodeAMACC02010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassMammalia
OrderChiroptera
FamilyVespertilionidae
GenusLasionycteris
Other Common Names
Chauve-souris argentée (FR) silver-haired bat (EN) Un Murciélago (ES)
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
No subspecies are recognized.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2025-06-08
Change Date2025-06-08
Edition Date2025-06-08
Edition AuthorsHammerson, G. (2015); rev. R. L. Gundy (2025)
Threat ImpactHigh - medium
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences> 300
Rank Reasons
This species has a large range in North America. It has suffered historical declines and is presumed to still be declining. It is threatened by logging, collisions with wind turbines and other energy infrastructure, and climate change-related habitat loss and degradation.
Range Extent Comments
Range extends from southeastern Alaska (Blejwas et al. 2014) and southern Canada south of the Northwest Territories southward to California, Arizona, Texas, and east to Georgia (Yates et al. 1976, Hall 1981, Kunz 1982). There are also limited records from Bermuda (Van Gelder and Wingate 1961) and northern México (Arriaga Flores 2010). These bats are generally absent in the southeastern United States during summer (June- August; Cryan 2003). In Texas, they appear to be primarily spring and fall migrants, though males have been found in mountainous areas of western Texas in May-June (Ammerman et al. 2012). They winter in the Pacific Northwest, in scattered areas of the southwestern United States, and at middle latitudes of the eastern United States approximately south of Michigan and east of the Mississippi River (Izor 1979, Cryan 2003). Males seem to stay farther south in spring and summer than do females, except for populations in British Columbia that do not appear to migrate (Schowalter et al. 1978, Cryan 2003). Using Global Biodiversity Information Facility (GBIF) (2025) records from 2005-2025, range extent is estimated to be 14.75 million km² (RARECAT 2025).
Occurrences Comments
The specific number of distinct occurrences has not been determined using standardized/meaningful criteria, but this species is represented by a large number of detection sites (e.g., roosts, mist net capture sites) and locations (as defined by IUCN).
Threat Impact Comments
Renewable energy, flight paths, and logging are the primary threats in Canada (Adams et al. 2024). Droughts, fire, and temperature extremes are the primary threats in the U.S. (Adams et al. 2024). Droughts, fire, and logging are the primary threats in México. (Adams et al. 2024).

This is one of the bat species most commonly killed by turbines at wind energy facilities (Gruver 2002, Johnson et al. 2003, Fiedler 2004, Johnson 2005, Baerwald and Barclay 2009, Arnett et al. 2008, Baerwald and Barclay 2011, Cryan 2011, Cryan et al. 2012, Ellison 2012, Jameson and Willis 2012). Arnett and Baerwald (2013) estimated that about 149,000-308,000 silver-haired bats were killed at wind energy facilities in the United States and Canada during the period from 2000 to 2011 (18% of total bat fatalities). Wind energy is expected to expand from 61,000 megawatts in 2014 to 350,000 megawatts by 2030, so the cumulative impact from wind turbines on this species could be devastating. Although the size of the overall silver-haired bat population is unknown, the reproductive rate for this species is low, and its ability to sustain the current and anticipated level of impact is doubtful.

Locally, the species experiences habitat loss and fragmentation as a result of clearcutting and other causes of deforestation (Parker 1996, Parker et al. 1996). Over the long term, deforestation and forest management practices presumably have reduced habitat quality (Campbell et al. 1996) and the number of available roost sites (Kunz 1982).

Broadcast application of pesticides to combat forest insect pests potentially has a detrimental impact on bat food resources (M. Perkins, Western Bat Working Group 2005), if not on the bats themselves, but the population-level impact of pesticides and other contaminants is poorly known.
Ecology & Habitat

Habitat

Habitat is primarily forested (frequently coniferous) areas adjacent to lakes, ponds, or streams, including areas that have been altered by humans. During migration, these bats sometimes occur in xeric areas. Summer roosts and nursery sites are in coniferous or deciduous tree foliage, cavities, or under loose bark, sometimes in buildings. In the Pacific Northwest and Black Hills (South Dakota), these bats show an affinity for forests that contain large numbers of snags (Campbell et al. 1996, Mattson et al. 1996, Betts 1998). In winter, individuals have been found in mines, caves, houses, rock crevices, under loose bark, and in hollow trees.

In Oregon, maternity roosts were in cavities high in tall, declining or newly dead trees; roost fidelity of reproductive females varied among individuals: some bats used only 1 or 2 roosts from 8 to at least 13 days; others used 5 or 6 roosts from 1 to 6 days; radio-tagged bats that were in the same colony stayed together during shifts among roosts; bats moved 35 to 1,100 meters between successive roosts (Betts 1998). In South Dakota, maternity aggregations primarily were in woodpecker-created cavities in ponderosa pines (Mattson et al. 1996).

At Long Point, Ontario, late summer/early fall migrants rats roosted in a variety of tree species and human-made structures in natural and developed (e.g., residential) areas (McGuire et al. 2012). In Manitoba, migrants roosted typically in narrow crevices in tree trunks (Barclay et al. 1988).

In the Ouachita Mountains, Arkansas, Perry et al. (2010) radio-tracked 11 bats to 31 day-roosts during winter. Ninety percent of roosts were in trees (5 species): 55 percent of all all roosts were under loose bark of the bole of live overstory Pinus echinata (shortleaf pine), three percent of roosts were in a rock outcrop, and six percent were at ground level (under a tree root or in a cavity at the base of a live pine). Bats selected pine or pine-hardwood stands greater than 50 years old and used forest stands 15-50 years of age less than their availability. Most roosts were on southern topographic aspects, and bats roosted in the rock outcrop on colder days (<5 °C).

See Vonhof and Barclay (1996) for information on characteristics of roost trees in British Columbia. See Campbell et al. (1996) for roost characteristics in Washington.

Ecology

During migration and summer residency, females roost alone or in maternity colonies; males typically roost alone (Barclay et al. 1988, Mattson et al. 1996, Betts 1998).

Reproduction

Copulation occurs in late summer or early fall. Fertilization is delayed until spring. Gestation lasts 50-60 days. Litter of 2 (occasionally 1) young is born in June-July, sometimes later in north (Kunz 1982). Young are able to fly at about 3 weeks. Individuals of both sexes become sexually mature by late summer/early fall of their first year (Cryan et al. 2012). Lifespan appears to be relatively short (oldest individuals estimated to be 12 years old; Schowalter et al. 1978). Maternity colonies are small (Parsons et al. 1986), usually with fewer than 20 individuals but sometimes as many as 55 (in a tree in South Dakota; Mattson et al. 1996).
Terrestrial Habitats
Forest/WoodlandForest - HardwoodForest - ConiferForest - MixedForest EdgeWoodland - HardwoodWoodland - ConiferWoodland - MixedUrban/edificarian
Palustrine Habitats
RiparianAerial
Other Nations (2)
United StatesN3
ProvinceRankNative
AlaskaS4Yes
ConnecticutS3BYes
Navajo NationS3Yes
OhioSNRYes
MississippiS3Yes
TennesseeS4Yes
South CarolinaS3Yes
ColoradoS3Yes
IllinoisS3Yes
MarylandSUYes
IowaS4Yes
Rhode IslandSUYes
UtahS4BYes
WyomingS3BYes
MaineSUYes
IdahoS3Yes
South DakotaS3Yes
IndianaS3Yes
New JerseyS3Yes
PennsylvaniaS1Yes
MissouriS3Yes
ArizonaS3Yes
LouisianaS2MYes
OklahomaS2Yes
New YorkS2BYes
DelawareSUYes
District of ColumbiaS4NYes
MichiganS5Yes
VermontS2BYes
OregonS3Yes
New HampshireS3BYes
North DakotaSNRYes
KentuckyS4MYes
VirginiaSUB,S4NYes
MassachusettsS2Yes
North CarolinaS4Yes
WisconsinS3Yes
WashingtonS3Yes
CaliforniaS3Yes
FloridaSNRYes
MinnesotaSNRYes
KansasSNAYes
NevadaS3Yes
GeorgiaS5Yes
TexasS4Yes
ArkansasSNRYes
MontanaS3Yes
New MexicoS4Yes
AlabamaSNRYes
NebraskaS3Yes
West VirginiaS2Yes
CanadaN5B,NUN,NUM
ProvinceRankNative
AlbertaS3B,SNRMYes
ManitobaS3BYes
British ColumbiaS4Yes
SaskatchewanS5BYes
Northwest TerritoriesSUYes
LabradorSNRYes
Nova ScotiaSUB,S1MYes
QuebecS3BYes
OntarioS3Yes
New BrunswickSUB,S1MYes
Island of NewfoundlandSNRYes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentNegligible (<1%)High (continuing)
2 - Agriculture & aquacultureNegligible (<1%)High (continuing)
2.1 - Annual & perennial non-timber cropsNegligible (<1%)High (continuing)
3 - Energy production & miningLarge - restrictedSerious or 31-70% pop. declineHigh (continuing)
3.3 - Renewable energyLarge - restrictedSerious or 31-70% pop. declineHigh (continuing)
4 - Transportation & service corridorsLarge - restrictedModerate - slightHigh (continuing)
4.4 - Flight pathsLarge - restrictedModerate - slightHigh (continuing)
5 - Biological resource useSmall (1-10%)Serious - slightHigh (continuing)
5.1 - Hunting & collecting terrestrial animalsSmall (1-10%)Serious - slightHigh (continuing)
5.3 - Logging & wood harvestingSmall (1-10%)Serious - slightHigh (continuing)
6 - Human intrusions & disturbanceSmall (1-10%)Negligible or <1% pop. declineHigh (continuing)
7 - Natural system modificationsNegligible (<1%)High (continuing)
8 - Invasive & other problematic species, genes & diseasesLarge (31-70%)Negligible or <1% pop. declineHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesLarge (31-70%)Negligible or <1% pop. declineHigh (continuing)
9 - PollutionRestricted - smallUnknownHigh (continuing)
11 - Climate change & severe weatherPervasive (71-100%)UnknownHigh (continuing)

Roadless Areas (44)
Alaska (2)
AreaForestAcres
KartaTongass National Forest52,117
TwelvemileTongass National Forest37,940
Arizona (1)
AreaForestAcres
Campbell BlueApache-Sitgreaves National Forests7,003
Arkansas (1)
AreaForestAcres
Dismal CreekOzark-St. Francis National Forest9,160
California (4)
AreaForestAcres
Bonanza KingShasta-Trinity National Forest16,402
Steele SwampModoc National Forest18,958
Weaver BallyShasta-Trinity National Forest829
West GirardShasta-Trinity National Forest37,516
Colorado (1)
AreaForestAcres
Comanche Peak Adjacent AreaArapaho & Roosevelt NFs44,158
Georgia (2)
AreaForestAcres
Helton CreekChattahoochee National Forest2,348
Rocky MountainChattahoochee National Forest4,269
Montana (1)
AreaForestAcres
HoodooLolo National Forest105,162
Nevada (1)
AreaForestAcres
Snake - Big WashHumboldt-Toiyabe National Forest4,146
New Mexico (9)
AreaForestAcres
Brushy MountainGila National Forest7,199
Contiguous To Black & Aldo Leopold WildernessGila National Forest111,883
Eagle PeakGila National Forest34,016
Gila BoxGila National Forest23,759
Meadow CreekGila National Forest34,167
Peloncillo (NM)Coronado National Forest43,339
Rancho ViejoSanta Fe National Forest3,827
Ryan HillCibola National Forest34,201
Sawyers PeakGila National Forest59,743
North Carolina (2)
AreaForestAcres
Bald MountainPisgah National Forest11,085
South Mills RiverPisgah National Forest8,588
Oregon (4)
AreaForestAcres
Calf - Copeland CreekUmpqua National Forest15,696
Castle Rock AppendageUmpqua National Forest4,649
LookingglassUmatilla National Forest4,859
Upper Catherine CreekWallowa-Whitman National Forest6,446
Utah (11)
AreaForestAcres
418025Uinta National Forest32,698
Boulder Mtn. / Boulder Top / Deer LakeDixie National Forest110,690
Happy ValleyDixie National Forest14,458
Lamb CanyonWasatch-Cache National Forest4,337
Lewis PeakWasatch-Cache National Forest11,616
Mollens HollowWasatch-Cache National Forest17,690
Mt. Logan NorthWasatch-Cache National Forest18,930
Mt. Logan SouthWasatch-Cache National Forest17,014
SanpitchManti-Lasal National Forest29,129
WellsvilleWasatch-Cache National Forest1,717
Widdop MountainWasatch-Cache National Forest8,011
Virginia (2)
AreaForestAcres
Brush MountainJefferson National Forest6,002
The PriestGeorge Washington National Forest5,737
Washington (3)
AreaForestAcres
BackboneGifford Pinchot National Forest1,201
Blue SlideWenatchee National Forest17,505
Goat Rocks AdjWenatchee National Forest6,108
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