Euderma maculatum

(J.A. Allen, 1891)

Spotted Bat

G4Apparently Secure Found in 1 roadless area NatureServe Explorer →
G4Apparently SecureGlobal Rank
Least concernIUCN
LowThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.104813
Element CodeAMACC07010
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassMammalia
OrderChiroptera
FamilyVespertilionidae
GenusEuderma
Other Common Names
Oreillard maculé (FR) spotted bat (EN) Un Murciélago (ES)
Concept Reference
Wilson, D. E., and D. M. Reeder (editors). 2005. Mammal species of the world: a taxonomic and geographic reference. Third edition. The Johns Hopkins University Press, Baltimore. Two volumes. 2,142 pp. [As modified by ASM the Mammal Diversity Database (MDD) at https://www.mammaldiversity.org/index.html]
Taxonomic Comments
Idionycteris is considered a separate genus (see Simmons in Wilson and Reeder 2005).
Conservation Status
Rank MethodLegacy Rank calculation - Excel v3.1x
Review Date2016-04-04
Change Date1996-11-05
Edition Date2015-03-25
Edition AuthorsHammerson, G.
Threat ImpactLow
Range Extent200,000-2,500,000 square km (about 80,000-1,000,000 square miles)
Rank Reasons
Widespread but patchy distribution in western North America; many roost/observation sites and locations; population size unknown but not as rare as previously believed; population trend uncertain but probably relatively stable or slowly declining; primary roosting habitat generally not vulnerable to loss or excessive disturbance; foraging habitat appears to be extensive and not limiting; not often killed by wind turbines; not known to be affected by white-nose syndrome.
Range Extent Comments
Range encompasses western North America from southern British Columbia (north to Fraser River basin near Williams Lake) (Cannings et al. 1999) and south-central Montana south through central and eastern Washington, eastern Oregon, Idaho, western Wyoming, western Colorado, western and southern Nevada, California (Pierson and Rainey 1998), Arizona, western and central New Mexico, and western Texas to central Mexico (Queretaro) (Verts and Carraway 1998, Luce and Keinath 2007). Distribution appears to be patchy with availability of suitable habitat (suitable roosting cliffs and water sources). Winter range is poorly known. Elevational range extends from below sea level to 3,230 meters (Luce and Keinath 2007).
Occurrences Comments
The number of distinct occurrences has not been determined using standardized or meaningful criteria, but this species is represented by a fairly large number of observation sites and locations (as defined by IUCN).
Threat Impact Comments
No major threats are known. Roosting habitat is extensive, remote, and mostly not vulnerable to destruction or excessive disturbance. Potential foraging areas are extensive (Navo et al. 1992, Storz 1995, Priday and Luce 1999) and generally not subject to extensive loss.

Several factors may affect local populations, though the range-wide scope of these threats generally is negligible. Construction of dams that inundate high cliffs and canyon walls may remove some habitat (Snow 1974). Overgrazing of meadows or expansion of invasive plant species might potentially reduce the local food base of these bats (Pierson and Rainey 1998). Timber harvest might benefit the bats by increasing the area of foraging habitat (Schmidt 2003). Disturbance in the form of intensive rock climbing is a potential threat (Pierson and Rainey 1998). Large-scale, non-target pesticide spraying could have adverse effects through secondary poisoning of bats and reduction of their prey base (Hayes and Wiles 2013). Wind turbines have the potential to cause direct mortality and could pose a threat to small local populations (Hayes and Wiles 2013). As of 2012, white-nose syndrome had not been detected in this species.
Ecology & Habitat

Description

Huge pink ears (37-47 mm [Hall 1981] or 45-50 mm [Watkins 1977]); blackish dorsum with a large white spot on each shoulder and on the rump, and white patches at the posterior base of each ear; total length 107-115 mm; forearm 48-51 mm; 16-20 g; greatest length of skull 18.4-19.0 mm (small sample); supraorbital region of skull sharply ridged; no median sagittal crest; 34 teeth (Watkins 1977, Handley 1959, Hall 1981). The newborn young lack any indication of having the adult color pattern (van Zyll de Jong 1985). Four hours after birth, a male weighed 4 g and measured 59 mm in length; tail length was 20 mm, hind foot 11 mm, ear 12 mm, and forearm 21 mm.

Diagnostic Characteristics

Differs from other bats in the unique patterning of the fur and the extremely large ears.

Habitat

This species occurs in various habitats from desert to montane coniferous stands, including open ponderosa pine, pinyon-juniper woodland, canyon bottoms, riparian and river corridors, meadows, open pasture, and hayfields. Active foraging may be mostly in open terrain, including forest clearings, meadows, and open wetlands, sometimes in open areas near buildings (see review in Schmidt 2003) or even golf courses. Roosts, including maternity roosts, generally are in cracks and crevices in cliffs (Wai-Ping and Fenton 1989, Pierson and Rainey 1998, Rabe et al. 1998), sometimes in caves or in buildings near cliffs (Sherwin and Gannon 2005). Winter habits poorly known.

In British Columbia, individuals used the same roost each night May-July, but not after early August (Wai-Ping and Fenton 1989). They foraged mainly in fields near pines and over marshes (Wai-Ping and Fenton 1989).

In Wyoming, these bats were associated with canyons, cliffs, and nearby permanent water, in areas including xeric-shrub grassland, riparian woodland, and high-elevation conifer and aspens habitats (Priday and Luce 1999).

In northwestern Colorado, spotted bats are locally common in various habitats (pinyon-juniper woodland, riparian corridors, over river) in canyons (Navo et al. 1992).

In Garfield County, Utah, Easterla captured a spotted bat in an area that was treeless and rolling for several miles around the site and also surrounded by mountainous terrain. The predominant plant species were sagebrush and rabbitbrush. In the mountainous terrain, the predominant plant was ponderosa (yellow) pine (Snow 1974). In Utah, Snow (1974) reported that bats were captured over a waterhole near limestone cliffs with cracks.

In northern Arizona, radio-tagged individuals foraged mostly in desert scrub but also used woodlands and forests. Maternity roosts were remote and difficult to access (Chambers et al. 2011).

Many bats in New Mexico were caught over waterholes near a sandstone cliff with numerous vertical cracks.

In the Big Bend National Park in Texas, spotted bats were captured near the only water source (a permanent pool) in many square miles, in a shallow, barren, hot, dry canyon with walls of angled, buckled pink and red limestone. The predominant plant species were creosote bush, candelilla, Hechtia, agave, pricklypear, and ocotillo (Snow 1974).

Ecology

Apparently relatively solitary but may hibernate in small clusters (Whitaker 1980). In British Columbia, individuals roosted solitarily during the active season; appeared to maintain exclusive foraging areas (Leonard and Fenton 1983).

Apparently this bat is a rapid flyer. Many of them are injured in the mist nets, indicating a high rate of speed at the collision (Snow 1974). In flight, the ears project forward. The only times the ears are carried erect are when the bat is alert, usually just preparatory to flight. At all other times, the ears lie along the back and are slightly curved (Barbour and Davis 1969).

Vocalizations and Echolocation

The spotted bat makes a wide variety of sounds in communicating and foraging. The voice has been described as sounding like a soft, extremely high-pitched metallic squeak; a hissing noise and a ratlike squeak; and a typical bat chirp. This bat has also been heard clicking the teeth together and making grinding noises by gnashing the teeth. Previous to taking flight, the spotted bat makes clicking or ticking notes (Snow 1974).

The echolocation call is loud and high- pitched; the fundamental frequency sweeps from 12 to 6 kHz and is a double or single steep frequency modulated pulse. The call is repeated at a rate of two to six per second. The sound pressure level is estimated at 80-90 dB at 10 cm, making it a moderate intensity. The echolocation call can clearly be heard by a human at distances of 250 m (van Zyll de Jong 1985).

The low frequency of the echolocation call is useful in both hunting and communications. Due to reduced attenuation and good propagation qualities, the call is good for long-range detection of prey and an increased range of audibility by other bats. The bat is also able to approach the moth more closely and enhance the chance of a successful pursuit due to the moth not being able to detect the low intensity of sound (van Zyll de Jong 1985). Similar calls are made by Plecotis phyllotis (Allen's big-eared bat), Tadarida macrotis (big freetail bat), and Eumops perotis (western mastiff bat) (Snow 1974).

Reproduction

Copulation likely occurs in late summer or fall. Births apparently occur in late May or early June in the south (Snow 1974, Watkins 1977, Schmidly 1977), mid-June to early July in the north (Watkins 1977, Nagorsen and Brigham 1993). Litter size is one. Lactating females have been netted on June 23, 30, and July 1 in New Mexico, on July 9 in New Mexico by Mike Bogan, and on August 10, 15, and 18 in Utah (Barbour and Davis 1969). Females are not known to form maternity colonies (Hayes and Wiles 2013).
Terrestrial Habitats
Woodland - ConiferShrubland/chaparralGrassland/herbaceousDesertBare rock/talus/screeCliff
Palustrine Habitats
HERBACEOUS WETLANDRiparian
Other Nations (2)
CanadaN3
ProvinceRankNative
British ColumbiaS3Yes
United StatesN3
ProvinceRankNative
WyomingS1BYes
OregonS2Yes
MontanaS4Yes
CaliforniaS3Yes
IdahoS3Yes
New MexicoS3Yes
ArizonaS2Yes
TexasS3Yes
ColoradoS2Yes
Navajo NationS4Yes
WashingtonS3Yes
NevadaS2Yes
UtahS4Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentNegligible (<1%)High (continuing)
2 - Agriculture & aquacultureLarge (31-70%)Slight or 1-10% pop. decline
2.3 - Livestock farming & ranchingHigh (continuing)
3 - Energy production & miningSmall (1-10%)Moderate - slightHigh (continuing)
3.2 - Mining & quarryingHigh (continuing)
4 - Transportation & service corridorsNegligible or <1% pop. declineHigh (continuing)
5 - Biological resource useSmall (1-10%)Negligible or <1% pop. declineHigh (continuing)
6 - Human intrusions & disturbanceNegligible (<1%)Slight or 1-10% pop. declineHigh (continuing)
6.1 - Recreational activitiesNegligible (<1%)High (continuing)
7 - Natural system modificationsNegligible (<1%)Extreme or 71-100% pop. declineHigh (continuing)
7.2 - Dams & water management/use
8 - Invasive & other problematic species, genes & diseasesLarge - smallNegligible or <1% pop. declineHigh (continuing)
9 - PollutionUnknownUnknownHigh (continuing)
10 - Geological eventsNegligible (<1%)
11 - Climate change & severe weatherPervasive (71-100%)UnknownHigh (continuing)

Roadless Areas (1)
Nevada (1)
AreaForestAcres
Pine Grove SouthHumboldt-Toiyabe National Forest88,945
References (56)
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