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 NamesChauve-souris argentée (FR) silver-haired bat (EN) Un Murciélago (ES)
Concept ReferenceWilson, 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 CommentsNo 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 ReasonsThis 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 CommentsRange 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 CommentsThe 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 CommentsRenewable 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.