Myotis thysanodes

Miller, 1897

Fringed Myotis

G4Apparently Secure Found in 5 roadless areas NatureServe Explorer →
G4Apparently SecureGlobal Rank
Least concernIUCN
MediumThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.100426
Element CodeAMACC01090
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassMammalia
OrderChiroptera
FamilyVespertilionidae
GenusMyotis
Other Common Names
Chauve-souris à queue frangée (FR) fringed bat (EN) Fringed 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/.
Conservation Status
Rank MethodLegacy Rank calculation - Excel v3.1x
Review Date2016-04-04
Change Date2012-07-20
Edition Date2015-03-31
Edition AuthorsHammerson, G.
Threat ImpactMedium
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Rank Reasons
Widespread but patchy distribution in western North America; many occurrences in wide range of habitats, but abundance is apparently relatively low; trend is poorly known, but slow declines are probable; primary threats include roost loss and disturbance; not yet known to be afflicted by white-nose syndrome, but this potentially devastating pathogen could eventually spread into the range of M. thysanodes. Theoretical considerations and population models suggest that future climate change may result in substantial declines or widespread extirpations over the next century. Thus better information is needed on abundance and trend.
Range Extent Comments
Patchy range includes western North America from southcentral British Columbia south through the western United States to Veracruz and Chiapas in southern Mexico; west to the Pacific coast, east to the Black Hills region of Wyoming-South Dakota-Nebraska, and western Texas (O'Farrell and Studier 1980; Nagorsen and Brigham 1993; Simmons, in Wilson and Reeder 2005). Winter range is little known. Elevational range extends from sea level along the Pacific coast to around 2,440 meters in Colorado (Armstrong et al. 1994), 2,715 meters in Utah (Oliver 2000), and 2,850 meters in New Mexico (Barbour and Davis 1969).
Occurrences Comments
The number of distinct occurrences has not been determined using standardized criteria, but this species is represented by a large number of roost sites, collection sites, and locations (as defined by IUCN).

Hasenyager (1980) listed 10 collection sites in Utah. Nagorsen and Brigham (1993) mapped approximately 10 collection sites in British Columbia. Schmidly (1977) mapped 17 collection sites in Texas. Keinath (2004) mapped more than 50 sites in Colorado, Wyoming, South Dakota, Nebraska, and Kansas (1 site), but many of these (including all 14 in Wyoming) were based on observations prior to 1990. Many additional localities exist in other portions of the range.
Threat Impact Comments
A primary threat is human disturbance of roost sites, especially maternity colonies, through recreational caving and mine exploration (O'Farrell and Studier 1980, Arizona Game and Fish Department 1993, Keinath 2004). Unprotected caves in South Dakota are heavily used and vandalized (Doug Backlund, pers. comm., 1998), and in Wyoming caves are threatened by recreational use (Mary Neighbours, pers. comm., 1998). Other threats include closure of abandoned mines, renewed mining at historic sites, toxic material impoundments, pesticide spraying, vegetation conversion, livestock grazing, timber harvest (particularly loss of snags that serve as roost sites for tree-roosting populations), and destruction of buildings and bridges used as roosts (Western Bat Working Group species account, 2005; Keinath 2004). Disturbance or destruction of water sources and riparian habitat may negatively affect some populations (George Oliver, pers. comm., 1998). This species is not known to incur signficiant mortality from turbines at wind energy facilities (Arnett and Baerwald 2013) or from white-nose syndrome.

Hypotheses and models of Adams and Hayes (2008), Adams (2010), and Hayes (2011) suggested that M. thysanodes populations in the Southern Rocky Mountains region may be at significant risk of local or regional extinction over the coming 100 - 200 years, if average temperatures significantly increase and surface water resources decrease.
Ecology & Habitat

Habitat

These bats occur primarily at middle elevations in desert, riparian, grassland, and woodland habitats, but they have been recorded at 2,850 meters in spruce-fir habitat in New Mexico, and at low elevations along the Pacific Coast (Barbour and Davis 1969, O'Farrell and Studier 1980, Hoffmeister 1986, Armstrong et al. 1994, Oliver 2000, Foresman 2001, Ammerman et al. 2012). Roosts are in caves, mines, cliff faces, rock crevices, old buildings, bridges, snags, and other sheltered sites (Barbour and Davis 1969, Rabe et al. 1998, Cryan et al. 2001, Foresman 2001, Weller and Zabel 2001, Lacki and Baker 2007, Hayes 2011). In South Dakota, the bats roosted in rock crevices and often changed roosts to nearby locations; maternity colonies maintained group integrity through roost changes, and females carried nonvolant young with them through roost changes (Cryan et al. 2001). In spring and summer in northern California, the bats roosted in snags in early to medium stages of decay and switched roosts often (Weller and Zabel 2001). Rabe et al. (1998) documented roosting in ponderosa pine snags in northern Arizona. On the east side of the Cascade Range in Oregon and Washington, females roosts primarily in rock crevices, infrequently in ponderosa pine snags; roost changes to nearby sites were frequent (Lacki and Baker 2007). In Colorado, most maternity roosts were in crevices of rock faces, sometimes in abandoned mines or in an abandoned cabin; roost changes were infrequent (Hayes 2011). In spring and summer, males roost separately and rarely are found in nursery colonies (Nagorsen and Brigham 1993). Winter habits are poorly known; hibernacula include caves, mines, and buildings (Western Bat Working Group species account, 2005).

Reproduction

Ovulation, fertilization, and implantation occur in spring (O'Farrell, in Wilson and Ruff 1999). Gestation lasts 50-60 days. Births occur from mid-May to mid-July, with substantial variation among regions and within particular colonies (O'Farrell and Studier 1973, Ammerman et al. 2012). Litter size is 1. Young can fly at 16-17 days. Colony size ranges up to several hundred; colonies begin to disperse by October.
Terrestrial Habitats
Woodland - ConiferWoodland - MixedGrassland/herbaceousDesertBare rock/talus/screeCliffSuburban/orchardUrban/edificarianAerial
Palustrine Habitats
Riparian
Other Nations (2)
CanadaN3
ProvinceRankNative
British ColumbiaS2Yes
SaskatchewanSNAYes
United StatesN4
ProvinceRankNative
WashingtonS3Yes
South DakotaS2Yes
NevadaS2Yes
MontanaS3Yes
CaliforniaS3Yes
ColoradoS3Yes
ArizonaS3Yes
WyomingS2BYes
New MexicoS4Yes
IdahoS3Yes
TexasS3Yes
Navajo NationS4Yes
UtahS3Yes
OregonS2Yes
NebraskaSNRYes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentNegligible (<1%)High (continuing)
2 - Agriculture & aquaculturePervasive - largeSlight or 1-10% pop. declineHigh (continuing)
2.3 - Livestock farming & ranchingHigh (continuing)
3 - Energy production & miningSmall (1-10%)Moderate - slightHigh (continuing)
3.2 - Mining & quarryingHigh (continuing)
4 - Transportation & service corridorsNegligible (<1%)High (continuing)
5 - Biological resource useSmall (1-10%)Moderate - slightHigh (continuing)
5.3 - Logging & wood harvestingHigh (continuing)
6 - Human intrusions & disturbanceSmall (1-10%)Moderate - slightHigh (continuing)
6.1 - Recreational activitiesHigh (continuing)
6.3 - Work & other activitiesHigh (continuing)
7 - Natural system modificationsNegligible (<1%)High (continuing)
8 - Invasive & other problematic species, genes & diseasesUnknownUnknownLow (long-term)
9 - PollutionUnknownUnknownHigh (continuing)
10 - Geological eventsNegligible (<1%)
11 - Climate change & severe weatherPervasive (71-100%)Slight or 1-10% pop. declineHigh (continuing)
11.1 - Habitat shifting & alteration
11.2 - Droughts

Roadless Areas (5)
Arizona (1)
AreaForestAcres
Ash CreekPrescott National Forest7,663
New Mexico (4)
AreaForestAcres
Alamo CanyonSanta Fe National Forest8,639
Apache Kid ContiguousCibola National Forest67,542
Canyon CreekGila National Forest9,824
Gila BoxGila National Forest23,759
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