Idionycteris phyllotis

(G.M. Allen, 1916)

Allen's Big-eared Bat

G4Apparently Secure Found in 2 roadless areas NatureServe Explorer →
G4Apparently SecureGlobal Rank
Least concernIUCN
MediumThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.106433
Element CodeAMACC09010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassMammalia
OrderChiroptera
FamilyVespertilionidae
GenusIdionycteris
Synonyms
Corynorhinus phyllotisPlecotus phyllotis
Other Common Names
Allen's big-eared 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
This species formerly was included in the genus Plecotus (e.g., see Handley 1959).
Conservation Status
Rank MethodLegacy Rank calculation - Excel v3.1x
Review Date2014-10-27
Change Date2011-05-12
Edition Date2015-03-25
Edition AuthorsHammerson, G.
Threat ImpactMedium
Range Extent200,000-2,500,000 square km (about 80,000-1,000,000 square miles)
Rank Reasons
Spotty range from southern-central Mexico to southern Nevada, southern Utah, and western Colorado; winter distribution and ecology poorly known; status in Mexico is poorly known, but this bat probably is more numerous there than in the United States; overall population size presumed to be fairly large, though individual colonies are small (usually fewer than 100 individuals); trend is uncertain but probably relatively stable or slowly declining; roost sites are vulnerable to abandonment as a result of human activity, and they may be lost through mine closure or reactivation or through incompatible forest management practices or other factors that result in loss of large snags used as maternity roosts; protected at several locations in the United States.
Range Extent Comments
The range encompasses the southwestern United States and part of Mexico, from western Colorado (Hayes et al. 2009), southern Utah (Oliver 2000), and southern Nevada south through Arizona (northwestern, central, southeastern; Hoffmeister 1986) and New Mexico (Mogollon Plateau and western Socorro County in the San Mateo and Magdalena mountains; Frey 2004) to Distrito Federal and Michoacan in southern central Mexico (Simmons, in Wilson and Reeder 2005), including the Sierra Madre Occidental, Sierra Madre Oriental, and Sierra Volcanica Transversal. The range closely approaches California, but as of 2014 no records were available for that state. The winter range is not known. The elevational range extends from 403 to 3,225 meters, with most records at 1,100-2,500 meters (Czaplewski 1983).

Subspecies hualapaiensis: southern Nevada, southern Utah, and northern Arizona (Mohave County and Coconino County north of the Grand Canyon); subspecies phyllotis: remainder of range (Tumlison 1993).
Occurrences Comments
The number of distinct occurrences has not been determined using standardized criteria, but this species likely is represented by multiple subpopulations in the United States and presumably many more in the more extensive range in Mexico (detailed occurrence information is not available for the bulk of the range in Mexico). This species is relatively difficult to capture, and its tree and crevice roosts are difficult to detect without radiotelemetry, so it probably occurs in several to many areas where it has not yet been recorded.
Threat Impact Comments
Threats include recreational entry into occupied caves/mines, active mining in occupied tunnels, vandalism or closure of abandoned mines used as maternity roosts, and timber management practices and other factors that reduce the availability of large pine snags for roosting. Lack of adequate information for Mexican populations prevents precise range-wide assessment of the scope and severity of threat.

Cockrum et al. (1996) reported that the major roost in the tunnel at Union Pass in Mohave County, Arizona, was destroyed by the relocation of the highway and destruction of the tunnel.

Maternity colonies are easily disturbed, often resulting in abandonment (Arizona Game and Fish Department 1997). Limited data suggest that this bat may abandon mines that have been gated to prevent recreational entry, even if the gates are permeable to other bat species (Western Bat Working Group 2005).

This species is not known to incur significant mortality by wind turbines. It is not known to be affected by white-nose syndrome.
Ecology & Habitat

Description

Dorsal pelage tawny brown, with hairs dark brown at the base; wings and membranes unfurred; white patches behind enormous ears; flap (lappet) projects forward from base of ear (Whitaker 1996).

Diagnostic Characteristics

No other big-eared bat has lappets projecting from the ears and extending over the forehead (Hoffmeister 1986).

Habitat

Habitat is primarily wooded areas (e.g., ponderosa pine, pinyon-juniper, pine-oak, Mexican woodland, oak brush) in mountains and canyons but also includes riparian (e.g., cottonwood, willow, tamarisk) woodland or tall shrubland, desert scrub, and open arid habitats (Cockrum and Musgrove 1964, Barbour and Davis 1969, Czaplewski 1983, Hoffmeister 1986, Rabe et al. 1998, Oliver 2000, Adams 2003, Brown and Berry 2004); habitat ranges from Mohave desert scrub of low desert ranges to white fir forest (Hoffmeister 1986). These bats often roost in rock crevices, caves, and mines, and so they are often found near cliffs, rocky slopes, and lava flows (Adams 2003). They are frequently netted along streams or over ponds.

Maternity colonies of 30 to 150 individuals have been found in mine shafts, boulder piles, sandstone crevices, lava beds, and beneath the loose bark of large ponderosa pine snags (Cockrum and Musgrove 1964, Czaplewski 1983, Rabe et al. 1998, Morrell et al. 1999, Adams 2003). In southern Utah, maternity roosts used by at least 15 individuals were in three cracks of the same cliff face; the roosts were on a large northwest-facing cliff, in the eastern side of a small box-canyon, with piñon-juniper woodland on ridge tops and bottoms of canyons (elevation ca. 1,800 m); roosts were in the top one-half of the cliff face, which was tall and highly fractured, with a large talus slope at the base (Siders and Jolley 2009). In northern Arizona, most maternity colonies were under sloughing bark of large-diameter ponderosa pine snags (Solevsky and Chambers 2009). Bachelor roosts were in vertical sandstone cliff faces in piñon-juniper woodlands. Of 11 maternity roosts in snags located in 1993-1995, only one continued to function as a roost in 2006-2007 (Solevsky and Chambers 2009).

Hibernating individuals have been found in a cave in an area of pinyon-juniper woodland in northern Arizona (Hoffmeister 1986), but in general winter ecology is poorly known.

Ecology

Corynorhinus townsendii and Myotis thysanodes associate with I. phyllotis in maternity roosts. Males probably roost solitarily while females form maternity colonies.

Reproduction

In New Mexico, Arizona, and Durango, pregnant females bearing a single embryo have been collected in June. In Arizona, young are born in mid to late June and are volant by late July (Barbour and Davis 1969, Hoffmeister 1986). Lactating females have been found from the second week of June to the first week of August (Czaplewski 1983). Sexual segregation apparently occurs during the maternity season (Rabe et al. 1998, Solevsky and Chambers 2009).
Terrestrial Habitats
Forest - HardwoodForest - ConiferForest - MixedWoodland - HardwoodWoodland - ConiferWoodland - MixedShrubland/chaparralGrassland/herbaceousDesertBare rock/talus/screeCliff
Palustrine Habitats
RiparianAerial
Other Nations (1)
United StatesN3
ProvinceRankNative
ColoradoS1Yes
NevadaS1Yes
UtahS3Yes
ArizonaS2Yes
New MexicoS3Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentNegligible (<1%)High (continuing)
1.3 - Tourism & recreation areasHigh (continuing)
2 - Agriculture & aquacultureNegligible or <1% pop. declineHigh (continuing)
2.3 - Livestock farming & ranchingHigh (continuing)
3 - Energy production & miningSmall (1-10%)Extreme - seriousHigh (continuing)
3.2 - Mining & quarryingHigh (continuing)
4 - Transportation & service corridorsNegligible or <1% pop. declineHigh (continuing)
5 - Biological resource useRestricted - smallModerate - 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%)High (continuing)
8 - Invasive & other problematic species, genes & diseasesNegligible or <1% pop. declineHigh (continuing)
9 - PollutionUnknownUnknownHigh (continuing)
10 - Geological eventsNegligible (<1%)
11 - Climate change & severe weatherPervasive (71-100%)UnknownHigh (continuing)

Roadless Areas (2)
New Mexico (2)
AreaForestAcres
Devils CreekGila National Forest89,916
Eagle PeakGila National Forest34,016
References (44)
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