|
Species ID |
050280 |
|
Name |
Davy's Naked-backed Bat |
|
Other Common Names |
Lesser Naked-backed Bat |
|
Category |
05 Mammals |
|
Phylum |
|
|
Subphylum |
|
|
Class |
Mammalia |
|
Subclass |
Theria |
|
Suborder |
Microchiroptera |
|
Family |
Mormoopidae |
|
Genus |
Pteronotus |
|
Species |
davyi |
|
Subspecies |
|
|
References |
1, 2, 3, 11 |
|
Scientific Synonyms |
Pteronotus suapurensis calvus Goodwin 1958 |
11* Three subspecies: P. d. fulvus (Sonora and Nuevo Leon to Honduras), P. d. davyi (Nicaragua to Trinidad and Lesser Antilles), P. d. incae (northwestern Peru). The northeastern Brazilian populations have not been allocated subspecifically. *12 Chilonycteris gymnonotus Natterer, 1843 was for many years considered a junior synonym of Pteronotus davyi Gray, 1838. Smith (1977), upon examination of the type specimen of C. gymnonotus, found that the specimen actually represented the larger congener P. suapurensis. The name C. gymnonotus predates P. suapurensis by 61 years, and is now accepted (Honacki et al., 1982) as the correct name of the big naked- backed bat. The subgenus Pteronotus is most closely related and most similar to the subgenus Chilonycteris; Phyllodia represents an earlier evolutionary divergence in the Pteronotus lineage (Smith, 1972). Within the subgenus Pteronotus, Smith (1972) considered P. davyi to have diverged less in an evolutionary sense than P. gymnonotus. A number of other vernacular names have been applied to P. davyi; the little naked-backed bat and Davy's naked backed bat are most common (Hall, 1981; Smith, 1972). In Spanish literature this bat is more appropriately called "murcilago de falsas espaldas desnudas," meaning false naked-backed bat (Villa-A., 1967:180). In Trinidad it has been called the Trinidadian naked-backed bat (Goodwin and Greenhall, 1961).
Status
|
Status Code |
Status Translation |
References |
|
271 |
Common: high density, likely to be seen in many places |
4 |
|
DISTRICT |
References |
|
Belize |
13 |
|
Cayo |
14 |
|
Corozal |
13 |
|
Orange Walk |
13,20 |
|
Stann Creek |
13 |
|
Toledo |
13 |
|
Administrative Unit |
Occurrence |
Abundance |
Temporal |
References |
|
Chiquibul Forest Reserve |
Captured or Mist netted and released |
Common |
June |
14 |
|
Cockscomb Basin Wildlife Sanctuary |
Captured or Mist netted and released |
Common |
Dry season (Jan-May) |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
August |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
September |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
January |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
May |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
July |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
October |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
March |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
February |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
December |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
APRIL |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
November |
13 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
June |
13 |
|
Town or Village, see comments. |
Recorded vocalization, tape or Anabat. |
Common |
March |
13 |
|
Town or Village, see comments. |
Recorded vocalization, tape or Anabat. |
Common |
October |
13 |
|
Town or Village, see comments. |
Recorded vocalization, tape or Anabat. |
Common |
APRIL |
13 |
|
Mountain Pine Ridge Forest Reserve |
Recorded vocalization, tape or Anabat. |
Common |
March |
13 |
|
Shipstern Nature Reserve |
Captured or Mist netted and released |
Common |
APRIL |
13 |
|
El Pilar |
Recorded vocalization, tape or Anabat. |
Common |
March |
13 |
|
Slate Creek Preserve |
Recorded vocalization, tape or Anabat. |
Common |
October |
13 |
|
Private land, see comments |
Recorded vocalization, tape or Anabat. |
Common |
February |
13 |
|
Temash-Sarstoon National Park |
Recorded vocalization, tape or Anabat. |
Common |
January |
13 |
|
Rio Bravo Conservation Area |
Recorded vocalization, tape or Anabat. |
Common |
November |
13 |
|
Columbia River Forest Reserve |
Recorded vocalization, tape or Anabat. |
Common |
February |
13 |
|
BFREE - Private Reserve |
Captured or Mist netted and released |
Common |
November |
13 |
|
BFREE - Private Reserve |
Recorded vocalization, tape or Anabat. |
Common |
October |
13 |
|
Blue Hole National Park |
Recorded vocalization, tape or Anabat. |
Common |
November |
19 |
|
Cockscomb Basin Wildlife Sanctuary |
Recorded vocalization, tape or Anabat. |
Common |
June |
18 |
|
Cockscomb Basin Wildlife Sanctuary |
Recorded vocalization, tape or Anabat. |
Common |
July |
18 |
|
Columbia River Forest Reserve |
Captured or Mist netted and released |
Fairly common |
February |
17 |
|
Vaca Forest Reserve |
Captured or Mist netted and released |
Common |
May |
16 |
|
Vaca Forest Reserve |
Captured or Mist netted and released |
Common |
APRIL |
16 |
|
Columbia River Forest Reserve |
Captured or Mist netted and released |
Fairly common |
February |
9 |
|
Cockscomb Basin Wildlife Sanctuary |
Recorded vocalization, tape or Anabat. |
Common |
May |
18 |
|
Government land |
Recorded vocalization, tape or Anabat. |
Uncommon |
January |
14 |
|
Government land |
Captured or Mist netted and released |
6 |
||
|
Rio Bravo Conservation Area |
Captured or Mist netted and released |
Permanent Resident (Year-round) |
4 |
|
|
Gallon Jug |
Captured or Mist netted and released |
Dry season (Jan-May) |
7 |
|
|
Shipstern Nature Reserve |
Captured or Mist netted and released |
Dry season (Jan-May) |
8 |
|
|
Rio Bravo Conservation Area |
Captured or Mist netted and released |
Dry season (Jan-May) |
10 |
|
Hydrologic Unit Distribution |
References |
|
Rio Hondo |
13 |
|
Belize River |
13 |
|
Sarstoon River |
13 |
|
Sibun River |
13 |
|
Macal River |
14,13 |
|
Temash River |
13 |
|
Blue Creek |
13 |
|
Aquacate Creek |
13 |
|
Bladen Branch |
13 |
|
North Stann Creek |
18 |
|
New River |
10 |
|
ELEVATION Association |
References |
|
401-600 m |
14,13 |
|
201-400 m |
13 |
|
0-100 m |
13,15 |
|
1-200 m |
14,13,20,19,18,16,14 |
|
601-800 m |
13,17,9 |
|
QUAD Distribution |
References |
|
16 30' to 16 45'; 88 45' to 89 00' |
14 |
|
16 15' to 16 30'; 89 00' to 89 15' |
9 |
|
17 30' to 17 45'; 88 45' to 89 00' |
13 |
|
17 45' to 18 00'; 88 45' to 89 00' |
13 |
|
16 30' to 16 45'; 88 15' to 88 30' |
13 |
|
16 45' to 17 00'; 89 00' to 89 15' |
13 |
|
15 50' to 16 00'; 88 50' to 89 15' |
13 |
|
17 45' to 18 00'; 89 00' to 89 15' |
13 |
|
17 15' to 17 30'; 88 30' to 88 45' |
13 |
|
17 00' to 17 15'; 88 30' to 88 45' |
13,19 |
|
16 45' to 17 00'; 88 15' to 88 30' |
13,18 |
|
16 15' to 16 30'; 89 00' to 89 15' |
13,17,9 |
|
16 45' to 17 00'; 88 30' to 88 45' |
21 |
|
16 00' to 16 15'; 88 45' to 89 00' |
20 |
|
16 30' to 16 45'; 88 30' to 88 45' |
13,14 |
|
17 30' to 17 45'; 89 00' to 89 15' |
13,4 |
|
17 30' to 17 45'; 88 30' to 88 45' |
13,6 |
|
17 00' to 17 15'; 89 00' to 89 15' |
14,13,16,6 |
|
17 00' to 17 15'; 88 45' to 89 00' |
13,6 |
|
18 15' to 18 30'; 88 00' to 88 15' |
13,15,6 |
|
16 15' to 16 30'; 89 00' to 89 15' |
6 |
|
18 00' to 18 15'; 88 30' to 88 45' |
20,7 |
|
16 00' to 16 15'; 89 00' to 89 15' |
13,8 |
|
16 15' to 16 30'; 89 00' to 89 15' |
9 |
|
Holdridge Life Zone Distribution |
References |
|
Subtropical Lower Montane wet |
9 |
|
Subtropical Lower Montane wet |
13 |
|
Subtropical Lower Montane moist |
14,13,17,9 |
|
Tropical wet-transition to Subtropical |
13 |
|
Subtropical moist |
13,20,16,15,14 |
|
Subtropical moist |
8 |
|
Subtropical wet |
13 |
|
Tropical moist-transition to Subtropical |
13,20,19,18,13 |
Comments on Distribution
14* Las Sierritas, Toledo District.
10* Hill Bank; La Milpa
8* Harp trapped at cave west of Sarteneja airstrip,in second growth.
6* Central Farm; Ontario; Teakettle; Unitedville; Tower Hill BSI;
Aguacate; San Antonio, Toledo.
|
Map of known distribution |
|
|
Vocal signature with fundamental harmonic |
|
|
Vocal signature with feeding buzz |
|
|
Vocal signature with call paramters shown |
|
|
Forest Type Associations |
Seral Stage |
Canopy Closure |
References |
|
Broadleaf hill forests over limestone in rolling or flat terrain. |
all stages |
71-100% |
14 |
|
Broadleaf Forest Rich in Lime-loving Species; Ramon-Chiquebul Forest. |
all stages |
71-100% |
14 |
|
Broadleaf Forest Rich in Lime-loving Species; Chiquebul-Bullhoof Forest |
Disturbed |
0-40% |
14 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
all stages |
71-100% |
13 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
all stages |
71-100% |
9 |
|
Broadleaf Forest Rich in Lime-loving Species; Ramon-Chiquebul forest. |
all stages |
71-100% |
9 |
|
Broadleaf hill forests over limestone in rolling or flat terrain. |
all stages |
71-100% |
9 |
|
Riparian seasonal swamp forests |
all stages |
71-100% |
13 |
|
Marsh and Swamp Communities |
all stages |
71-100% |
13 |
|
Lowland broadleaf moist evergreen seasonal forests over limestone, central-western variant. |
all stages |
71-100% |
13 |
|
Marsh and Swamp Communities |
all stages |
71-100% |
13 |
|
Seasonal swamp forests (marsh forests) of Northern Belize, variant 1. |
all stages |
71-100% |
13 |
|
Montane scrub forest over volcanics. |
all stages |
71-100% |
13 |
|
Cohune Palm Forest |
all stages |
71-100% |
13,20 |
|
Inland well-drained shrubland over poor soils. |
all stages |
71-100% |
13 |
|
Transitional Low Broadleaf Forest and Shrubland |
all stages |
71-100% |
13 |
|
Marsh and Swamp Communities |
all stages |
71-100% |
13,20 |
|
Broadleaf Forest Rich in Lime-loving Species |
all stages |
71-100% |
13,20 |
|
Lowland broadleaf moist evergreen seasonal forests over poor soils. |
all stages |
71-100% |
13,20 |
|
Broadleaf Forest w/Occasional Lime-loving Species; Cohune-Banak forest. |
all stages |
71-100% |
13 |
|
Freshwater swamp forest (permanently waterlogged), typical variant. |
all stages |
71-100% |
13 |
|
Marsh and Swamp Communities |
all stages |
71-100% |
13 |
|
This serves to update Wright et al. for urban or agricultural areas devoid of native vegetation. |
all stages |
71-100% |
13,20 |
|
Agriculture, no native vegetation. |
all stages |
71-100% |
13,20 |
|
Broadleaf hill forests over limestone in steep terrain. |
all stages |
71-100% |
13 |
|
Broadleaf Forest Rich in Lime-loving Species |
all stages |
71-100% |
13,20 |
|
Lowland broadleaf moist evergreen seasonal forest over limestone, northwestern variant. |
all stages |
71-100% |
13,20 |
|
Broadleaf Forest Rich in Lime-loving Species: Sapote-ramon-spice forest. |
all stages |
71-100% |
13,20 |
|
Broadleaf hill forests over limestone in rolling or flat terrain. |
all stages |
71-100% |
13 |
|
Needle-leaf hill forests over poor soils (Mountain Pine Ridge). |
all stages |
71-100% |
13 |
|
Pine Forest and Orchard Savanna |
all stages |
71-100% |
13 |
|
Lowland broadleaf rain forests over moderately lime-rich alluvium. |
all stages |
71-100% |
13 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
all stages |
71-100% |
13 |
|
This serves to update Wright et al. for urban or agricultural areas devoid of native vegetation. |
all stages |
71-100% |
13 |
|
Seasonally waterlogged fire-induced shrubland of the plains. |
all stages |
71-100% |
13 |
|
Pine Forest and Orchard Savanna |
all stages |
71-100% |
13 |
|
Broadleaf Forest Rich in Lime-loving Species: Sapote-Silion forest. |
all stages |
71-100% |
13,20 |
|
Agriculture, no native vegetation. |
all stages |
71-100% |
13 |
|
Broadleaf Forest with Occasional Lime-loving Species; Negrito-Cohune Palm Forest. |
all stages |
71-100% |
13 |
|
URBAN, human settlement. |
Disturbed |
0-40% |
19 |
|
Lowland broadleaf moist evergreen seasonal forests over poor soils. |
all stages |
71-100% |
18 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
all stages |
71-100% |
18 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
Old Growth |
Canopy unknown |
17 |
|
Broadleaf hill forests over limestone in rolling or flat terrain. |
Old Growth |
Canopy unknown |
17 |
|
Broadleaf Forest Rich in Lime-loving Species; Ramon-Chiquebul forest. |
Old Growth |
Canopy unknown |
17 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
all stages |
41-70% |
16 |
|
Lowland broadleaf moist semi-evergreen scrub forest. |
all stages |
71-100% |
13,15 |
|
Broadleaf Forest Rich in Lime-loving Species; Sapote-Mahogany Forest |
all stages |
71-100% |
13,15 |
|
Broadleaf Forest Rich in Lime-loving Species; Chiquebul-Bullhoof Forest |
all stages |
71-100% |
13 |
|
Broadleaf Forest with few Lime-loving Species |
Canopy unknown |
Canopy unknown |
20 |
|
Broadleaf Forest Rich in Lime-loving Species; Sapote-Mahogany |
all stages |
71-100% |
13,20 |
|
Broadleaf Forest w/Occasional Lime-loving Species; Cohune-Banak forest. |
Disturbed |
41-70% |
19 |
|
Broadleaf Forest Rich in Lime-loving Species |
all stages |
71-100% |
13 |
|
Disturbed scrub |
all stages |
71-100% |
13 |
|
Broadleaf Forest with Few Lime-loving Species |
Canopy unknown |
Canopy unknown |
21 |
|
Broadleaf Forest Moderately Rich in Lime-loving Species; Cohune-Quamwood Forest |
all stages |
41-70% |
16 |
|
Agriculture, no native vegetation. |
Disturbed |
0-40% |
16 |
|
Broadleaf Forest with Few Lime-loving Species |
all stages |
71-100% |
13 |
|
Broadleaf Forest Rich in Lime-loving Species; Sapote-Mahogany Forest |
mature tree |
41-70% |
8 |
|
Land Use/Land Cover Associations |
References |
|
Protection |
8 |
|
Trophic |
|
INSECTIVORE |
References on Trophic Level
12
|
Lifestage |
Food Item Consumed |
Part of Food Item |
|
|
Adult |
Lepidoptera |
Adult stage |
|
|
Adult |
Dermaptera |
Adult stage |
|
|
Adult |
Diptera |
Adult stage |
Comments on General Food Habits
12* The diet of lesser naked-backed bats includes many species of Lepidoptera (Howell and Burch, 1974), some dipterans, and occasionally earwigs (Forficulidae, Sphingolabis sp.; Villa-R., 1967), P. davyi drinks on the wing (Hill and Smith, 1984). Lesser naked-backed bats do not adapt well to drinking from a dish in the lab, but quickly learn to pursue and catch flying insects in an enclosed room. P davyi may capture 25 fruitflies/min (Novick, 1963). The species probably is not in much direct danger from man's development, due to the undesirability of the unusually hot, humid caves favored by P. davyi (Birney et al., 1974), though destruction of foraging areas could endanger some populations.
|
References/Lifestage |
Reference Numbers |
|
References/Lifestage |
Reference Numbers |
Life History Narrative
12* Lesser naked-backed bats occur in moist to seasonally dry habitats (Bateman and Vaughman, 1974; Birney et al., 1974; Matson and Patten, 1975; Smith, 1972; Wilson, 1983). P. davyi incae occurs in mesic habitats on both sides of the Andes in Peru (Koopman, 1978). Within these habitats, P. davyi selects the darker recesses of hot, humid caves and mines (Bateman and Vaughan, 1974; Birney et al., 1974; Goodwin and Greenhall, 1961; Villa-R., 1967). Manmade structures, such as chicken pens, are sometimes utilized as roosts (Goodwin and Greenhall, 1961). Daytime roosts are shared with numerous other species of bats, but most notably other mormoopids, Natalus, Artibeus jamaicensis, Macrotus, Tadarida brasiliensis, and Desmodus rotundus. Lesser naked-backed bats often are the dominant species in a roost (Bateman and Vaughman, 1974; Birney et al., 1974), but they rarely roost alone (Villa-R., 1967). Long-range movements of lesser naked-backed bats have not been recorded, but P. davyi is the only mormoopid to have invaded the Lesser Antilles (Jones and Phillips, 1970). Of 117 bat species on adjacent continental South America, only 12 have succeeded in colonizing the Antilles (Koopman, 1982). Birth is coincident with the onset of the rainy season, which increases number and availability of insect resources (Bateman and Vaughan, 1974). Lactation may continue through July. Maturation of young is rapid, enhanced by the seasonal abundance of insects (Smith, 1972).
|
References/Result |
Reference Numbers |
1 McCarthy, T. J. 1993. Checklist: Mammals of Belize. BAS Newsletter 25 (2-3). 2 Hall, E. R. 1981. Mammals of North America. Second ed. John Wiley & Sons. New York. 1:94-95 3 Koopman, Karl F. 1993. Chiroptera. in Wilson, D. E., and D. M. Reeder, eds, Mammalian species of the world, 2nd ed, Smithsonian Institution Press, Washington, D.C., pp. 137-241. 4 Emmons, L. H. 1990. Neotropical Rainforest Mammals, a field guide. University of Chicago Press. Chicago and London. p.52-53 5 Anonymous. Rio Bravo Mammal List Update. 1994. Unpublished list. pp.1-2 6 McCarthy, T. J. 1987. Distributional records of bats from the Caribbean lowlands of Belize and adjacent Guatemala and Mexico. In: Studies in Neotropical Mammalogy: Essays in Honor of Philip Hershkovitz (B.D. Patterson and R.M. Timm, eds.). Fieldiana:n.s. No. 39:137-162. 7 Miller, C.M., B.W. Miller. 1994 (Nov.). Working Checklist: Mammals of Gallon Jug and Chan Chich Lodge Area. Unpublished list. 8 Quigley, H. B., B. W. Miller, C. M. Miller. 1995. Mammal Survey, Shipstern Nature Reserve, April 4-13, 1995. Unpublished report for ITCF. 9 Miller, B.W. 1997. Columbia River Forest Reserve Expedition 17-23 February, 1997, Bat Survey. Wildlife Conservation Society Tropical Forest and Reserve Planning Project Belize. Technical Report. 19 pp. 10 Smith, Rosemary L. 1994. Neotropical Bats as Indicators of Environmental Disturbance. Masters Thesis. Durrell Institute of Conservation and Ecology. pp.64. 11 Koopman, Karl F. 1994. Chiroptera: Systematics in Handbook of Zoology. W de Gruyter. Berlin-NY. p. 71. 12 Adams, James K., 1989. Pteronotus davyi. Mammalian Species No. 346. pp.1-5. American Society of Mammalogists. 13 Miller, B.W. 2001. Community Ecology of the Non-phyllostomid bats of Northwestern Belize, with a landscape level assessment of the bats of Belize. PhD. Dissertation. University of Kent, Durrell Institute of Conservation and Ecology. 14 Miller, B.W. and C.M. Miller. 1998. Las Sierritas, Toledo District, Belize. Rapid Environmental Appraisal Report for Mott MacDonald, Ltd. 6-10 January 1998. 15 Bartschi, D. 1998. Chiropteres de al Reserva Naturelle de Shipstern et de ses environs (Nord du Belize): Inventaire et biologie. Masters Thesis University of Neuchatel, Switzerland. 101 pp. 16 Miller, B.W. and C.M. Miller. 1999. Harp trap and acoustic bat survey, April 11, 1996 and May 16, 1999, upper entrance of Actun Chapot Cave. Vaca Forest Reserve. Wildlife Conservation Society Tropical Forest and Reserve Planning Project Belize. Unpublished report. 17 Miller, B.W. 1996. Report on the non-phyllostomid bats of Columbia River Forest Reserve. Joint expedtion with Forest Department. Wildlife Conservation Society, Tropical Forest and Reserve Planning Project, Belize. Unpublished data. 18 Miller, B.W. and C.M. Miller. 1999. Results of a survey of bats of the Cockscomb Basin Wildlife Sanctuary. Wildlife Conservation Society, Tropical Forest and Reserve Planning Project, Belize. Technical Report for Belize Audubon Society. 16 pp. 19 Miller, B.W. 2000. Survey of the bats of Blue Hole National Park and adjacent Jaguar Creek. Wildlife Conservation Society, Tropical Forest and Reserve Planning Project, Belize. Technical Report for Belize Audubon Society. 20 FMNH. 1997. Mammal holdings in the Field Musuem of Natural History, unpublished listing. Imported on 06/13/00. 21 USNM. 1995. Collections data from mammal department, United States National Museum. Imported on date: 06/13/00. 22 O'Farrell, M. J. and B. W. Miller. 1999. Use of Vocal Signatures for the Inventory of Free-flying Neotropical Bats. Biotropica 31(3):507-516. 23 O'Farrell, M. J. and B. W. Miller. 1997. A New Examination of Echolocation Calls of Some Neotropical Bats (Emballonuridae and Mormoopidae). Journal of Mammalogy 87(3):954-963. 24 Miller, B.W. 2001. Preliminary survey of the bats of Las Cuevas BM Field Station, and Ek Tun lodge property on Macal River. June 16-20, 2001. WCS Tropcial Forest and Reserve Planning Project Technical Report.