11/24/01
|
Species ID |
050300 |
|
Name |
Common Mustached Bat |
|
Other Common Names |
Parnell's Mustached Bat |
|
Category |
05 Mammals |
|
Phylum |
|
|
Subphylum |
|
|
Class |
Mammalia |
|
Subclass |
Theria |
|
Suborder |
Microchiroptera |
|
Family |
Mormoopidae |
|
Genus |
Pteronotus |
|
Species |
parnellii |
|
Subspecies |
|
|
References |
1, 2, 3, 15, 16 |
|
Scientific Synonyms |
Chilonyctris rubiginosus Wagner 1843, Phyllodia parnellii Gray 1843 |
15* Nine subspecies currently recognized: P.p. parnelli (=boothi) (Cuba and Jamaica), P.p. pusillus (Hispaniola), P.p. gonavensis (Gonave island off east coast of Hispaniola), P.p. portoricensin (Puerto Rico), P.p. mexicanus (Sonora and tamaulipas to Oaxaca and Veracruz in Mexico) , P.p. mesoamericanus (on the western coast from Chaipas to western panama and on the east coast from Veracruz and Yucatan to Honduras), P. p. rubinginosus (Honduras to Panama; also Tobago, Trinidad and southern Venezuela to Surinam, eastern Peru, and northeasern Brazil), P.p. fuscus (northeastern Columbia and northern Venezuela except for the Pagaguana peninsula), P.p. paraguensis (Pagauana peninsula of northern Venezuela).
|
Status Code |
Status Translation |
References |
|
271 |
Common: high density, likely to be seen in many places |
4 |
|
271 |
Common: high density, likely to be seen in many places |
24 |
|
DISTRICT |
References |
|
24 |
|
|
Belize |
24 |
|
Cayo |
32 |
|
Corozal |
24 |
|
Orange Walk |
24 |
|
Stann Creek |
24 |
|
Toledo |
24 |
|
Administrative Unit |
Occurrence |
Abundance |
Temporal |
References |
|
Chiquibul Forest Reserve |
Captured or Mist netted and released |
Unknown, insuffient data |
June |
32 |
|
Cockscomb Basin Wildlife Sanctuary |
Captured or Mist netted and released |
Common |
Dry season (Jan-May) |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
September |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
August |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
July |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
November |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
December |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
October |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
February |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
May |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
March |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
January |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
April |
24 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
June |
24 |
|
Mountain Pine Ridge Forest Reserve |
Recorded vocalization. |
Common |
December |
24 |
|
Mountain Pine Ridge Forest Reserve |
Recorded vocalization. |
Common |
March |
24 |
|
Temash-Sarstoon National Park |
Recorded vocalization. |
Common |
January |
24 |
|
Rio Bravo Conservation Area |
Recorded vocalization. |
Common |
July |
24 |
|
BFREE - Private Reserve |
Captured or Mist netted and released |
Common |
November |
24 |
|
BFREE - Private Reserve |
Recorded vocalization. |
Common |
October |
24 |
|
Town or Village, see comments. |
Recorded vocalization. |
Common |
April |
24 |
|
Private land, see comments |
Recorded vocalization. |
Common |
February |
24 |
|
Blue Hole National Park |
Captured or Mist netted and released |
Common |
November |
24 |
|
Cockscomb Basin Wildlife Sanctuary |
Captured or Mist netted and released |
Common |
June |
25 |
|
Cockscomb Basin Wildlife Sanctuary |
Captured or Mist netted and released |
Common |
July |
25 |
|
Cockscomb Basin Wildlife Sanctuary |
Recorded vocalization. |
Common |
June |
21 |
|
Private land, see comments |
Captured or Mist netted and released |
Common |
July |
24 |
|
Private land, see comments |
Captured or Mist netted and released |
Common |
November |
23 |
|
Blue Hole National Park |
Captured or Mist netted and released |
Common |
November |
23 |
|
Vaca Forest Reserve |
Captured or Mist netted and released |
Common |
May |
21 |
|
Temash-Sarstoon National Park |
Captured or Mist netted and released |
Common |
January |
20 |
|
Caracol Archaeological Reserve |
Captured or Mist netted and released |
Common |
October |
19 |
|
Caracol Archaeological Reserve |
Captured or Mist netted and released |
Common |
February |
7 |
|
Caracol Archaeological Reserve |
Captured or Mist netted and released |
Common |
May |
7 |
|
Shipstern Nature Reserve |
Captured or Mist netted and released |
Common |
April |
24,18 |
|
Honey Camp (Proposed) |
Collected as voucher. |
Unknown, insuffient data |
May |
27 |
|
Mountain Pine Ridge Forest Reserve |
Collected as voucher. |
Unknown, insuffient data |
February |
27 |
|
Columbia River Forest Reserve |
Collected as voucher. |
Unknown, insuffient data |
September |
26 |
|
Columbia River Forest Reserve |
Collected as voucher. |
Unknown, insuffient data |
August |
26 |
|
Columbia River Forest Reserve |
Recorded vocalization. |
Common |
February |
11 |
|
Columbia River Forest Reserve |
Collected as voucher. |
Unknown, insuffient data |
July |
27 |
|
Mountain Pine Ridge Forest Reserve |
Collected as voucher. |
Unknown, insuffient data |
July |
27 |
|
Mountain Pine Ridge Forest Reserve |
Collected as voucher. |
Unknown, insuffient data |
April |
26 |
|
Rio Bravo Conservation Area |
Collected as voucher. |
Unknown, insuffient data |
May |
28 |
|
Bladen Nature Reserve |
Unknown, insuffient data |
May |
24 |
|
|
Mountain Pine Ridge Forest Reserve |
Unknown, insuffient data |
July |
24 |
|
|
Mountain Pine Ridge Forest Reserve |
Unknown, insuffient data |
June |
24 |
|
|
Altun Ha Archaeological Reserve |
Collected as voucher. |
Unknown, insuffient data |
March |
12 |
|
Altun Ha Archaeological Reserve |
Collected as voucher. |
Unknown, insuffient data |
February |
12 |
|
Government land |
Recorded vocalization. |
Uncommon |
January |
17 |
|
Altun Ha Archaeological Reserve |
Collected as voucher. |
Dry season (Jan-May) |
12 |
|
|
Rio Bravo Conservation Area |
Captured or Mist netted and released |
Common |
Permanent Resident (Year-round) |
6 |
|
Bladen Nature Reserve |
Captured or Mist netted and released |
Common |
May |
5 |
|
Gallon Jug |
Captured or Mist netted and released |
Common |
Dry season (Jan-May) |
8 |
|
Shipstern Nature Reserve |
Heard |
Common |
Dry season (Jan-May) |
9 |
|
Mountain Pine Ridge Forest Reserve |
Collected as voucher. |
Unknown, insuffient data |
Dry season (Jan-May) |
11 |
|
Private land, see comments |
Collected as voucher. |
August |
13 |
|
|
Altun Ha Archaeological Reserve |
Collected as voucher. |
March |
12 |
|
|
Rio Bravo Conservation Area |
Captured or Mist netted and released |
Dry season (Jan-May) |
14 |
|
Hydrologic Unit Distribution |
References |
|
Temash River |
24 |
|
Macal River |
24 |
|
Sibun River |
24 |
|
Bladen Branch |
24 |
|
New River Lagoon |
24 |
|
North Stann Creek |
25 |
|
Blue Creek |
24,24 |
|
Sarstoon River |
24,20 |
|
ELEVATION Association |
References |
|
1-200 m |
24,29 |
|
401-600 m |
32,24 |
|
0-100 m |
24,20 |
|
601-800 m |
11 |
|
201-400 m |
24 |
|
401-600 m |
19,7 |
|
401-500 m |
24 |
|
0-100 m |
18 |
|
101-200 m |
24,5 |
|
1-200 m |
24,25,23,22,21,17 |
|
601-800 m |
11 |
|
QUAD Distribution |
References |
|
16 00' to 16 15'; 88 45' to 89 00' |
29 |
|
17 30' to 17 45'; 88 45' to 89 00' |
24 |
|
17 15' to 17 30'; 88 30' to 88 45' |
24 |
|
16 45' to 17 00'; 88 45' to 89 00' |
24 |
|
17 00' to 17 15'; 88 30' to 88 45' |
24,23,22 |
|
15 50' to 16 00'; 88 50' to 89 15' |
24,20 |
|
18 00' to 18 15'; 88 00' to 88 15' |
18 |
|
16 15' to 16 30'; 89 00' to 89 15' |
11 |
|
17 30' to 17 45'; 88 15' to 88 30' |
27 |
|
18 00' to 18 15'; 88 15' to 88 30' |
27 |
|
16 45' to 17 00'; 88 15' to 88 30' |
24,25 |
|
17 15' to 17 30'; 88 15' to 88 30' |
27 |
|
18 00' to 18 15'; 88 30' to 88 45' |
27 |
|
16 15' to 16 30'; 89 00' to 89 15' |
26 |
|
17 00' to 17 15'; 89 00' to 89 15' |
21 |
|
16 00' to 16 15'; 88 45' to 89 00' |
27 |
|
16 00' to 16 15'; 89 00' to 89 15' |
24 |
|
17 15' to 17 30'; 88 45' to 89 00' |
27 |
|
17 45' to 18 00'; 89 00' to 89 15' |
28 |
|
17 00' to 17 15'; 88 45' to 89 00' |
24 |
|
16 30' to 16 45'; 88 45' to 89 00' |
32,24,5 |
|
16 30' to 16 45'; 88 30' to 88 45' |
24,17 |
|
17 45' to 18 00'; 88 15' to 88 30' |
12 |
|
17 30' to 17 45'; 89 00' to 89 15' |
24,5 |
|
17 30' to 17 45'; 88 30' to 88 45' |
24,6 |
|
18 15' to 18 30'; 88 15' to 88 30' |
18,7 |
|
16 45' to 17 00'; 89 00' to 89 15' |
24,19,7,9 |
|
16 45' to 17 00'; 88 45' to 89 00' |
26,9 |
|
18 15' to 18 30'; 88 00' to 88 15' |
24,18,11 |
|
16 15' to 16 30'; 88 45' to 89 00' |
27,13 |
|
17 45' to 18 00'; 88 45' to 89 00' |
12 |
|
Holdridge Life Zone Distribution |
References |
|
Subtropical wet |
29 |
|
Subtropical Lower Montane wet |
11 |
|
Subtropical moist |
24 |
|
Tropical wet-transition to Subtropical |
24,20 |
|
Subtropical Lower Montane wet |
24,11 |
|
Tropical moist-transition to Subtropical |
24,24,25,23,22 |
|
Subtropical Lower Montane wet |
26 |
|
Subtropical Lower Montane moist |
32,26 |
|
Tropical wet-transition to Subtropical |
27 |
|
Subtropical wet |
24,5 |
|
Subtropical wet |
17 |
|
Subtropical moist |
21,19,7,8,12 |
|
Subtropical moist |
13 |
|
Subtropical moist |
9 |
Comments on Distribution
17* Las Sierritas, Toledo District. 14* Hillbank; La Milpa. 12* ROM Rockstone Pond. 13* 0.75mi. E Corozal 11* Trapped and recorded at cave W of Sarteneja Airstrip. 5* Quebrada de Oro 2* specimen from Stann Creek Valley 5* Quebrado de Oro
|
Distribution map |
|
|
Vocal signature |
|
|
Vocal signature with call parameters |
|
|
Forest Type Associations |
Seral Stage |
Canopy Closure |
References |
|
Broadleaf Forest Rich in Lime-loving Species |
all stages |
71-100% |
32 |
|
Broadleaf hill forests over limestone in rolling or flat terrain. |
all stages |
71-100% |
32 |
|
Broadleaf Forest Rich in Lime-loving Species; Ramon-Chiquebul Forest. |
all stages |
71-100% |
32 |
|
Lowland broadleaf moist evergreen seasonal forests over poor soils. |
all stages |
71-100% |
24 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
all stages |
71-100% |
24 |
|
Broadleaf Forest Rich in Lime-loving Species: Sapote-ramon-spice forest. |
all stages |
71-100% |
24 |
|
Marsh and Swamp Communities |
all stages |
71-100% |
24 |
|
Disturbed scrub |
all stages |
71-100% |
24 |
|
Freshwater swamp forest (permanently waterlogged), typical variant. |
all stages |
71-100% |
24 |
|
Marsh and Swamp Communities |
all stages |
71-100% |
24 |
|
Broadleaf Forest Rich in Lime-loving Species |
all stages |
71-100% |
24 |
|
This serves to update Wright et al. for urban or agricultural areas devoid of native vegetation. |
all stages |
71-100% |
24 |
|
Agriculture, no native vegetation. |
all stages |
71-100% |
24 |
|
Montane scrub forest over volcanics. |
all stages |
71-100% |
24 |
|
Seasonally waterlogged fire-induced shrubland of the plains. |
all stages |
71-100% |
24 |
|
Broadleaf Forest Rich in Lime-loving Species |
all stages |
71-100% |
24 |
|
Mixed hill forests over poor soils (Mountain Pine Ridge). |
all stages |
71-100% |
24 |
|
Tall herb wetland communities. |
all stages |
71-100% |
24 |
|
Lowland broadleaf moist evergreen seasonal forests over poor soils. |
all stages |
71-100% |
24 |
|
Agriculture, no native vegetation. |
all stages |
71-100% |
24 |
|
Broadleaf hill forests over limestone in steep terrain. |
all stages |
71-100% |
24 |
|
Broadleaf Forest Rich in Lime-loving Species; Chiquebul-Bullhoof Forest |
all stages |
71-100% |
24 |
|
Broadleaf Forest with Few Lime-loving Species |
all stages |
71-100% |
25 |
|
Disturbed scrub |
all stages |
71-100% |
25 |
|
Lowland broadleaf moist evergreen seasonal forests over poor soils. |
all stages |
71-100% |
25 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
all stages |
71-100% |
25 |
|
Broadleaf Forest Rich in Lime-loving Species |
Disturbed |
41-70% |
24 |
|
Broadleaf hill forests over limestone in steep terrain. |
Disturbed |
41-70% |
24 |
|
Broadleaf Forest Rich in Lime-loving Species |
Disturbed |
71-100% |
23 |
|
Broadleaf hill forests over limestone in steep terrain. |
Disturbed |
71-100% |
23 |
|
Broadleaf Forest Rich in Lime-loving Species; Chiquebul-Bullhoof Forest |
Disturbed |
71-100% |
23 |
|
Broadleaf Forest Rich in Lime-loving Species |
Disturbed |
71-100% |
22 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
all stages |
41-70% |
21 |
|
Marsh and Swamp Communities |
Old Growth |
71-100% |
20 |
|
Freshwater swamp forest (permanently waterlogged), typical variant. |
Old Growth |
71-100% |
20 |
|
This serves to update Wright et al. for urban or agricultural areas devoid of native vegetation. |
stage unknown |
Canopy unknown |
24,18 |
|
Dwarf mangrove scrub. |
stage unknown |
Canopy unknown |
18 |
|
Coastal Formations |
stage unknown |
Canopy unknown |
18 |
|
Lowland broadleaf moist semi-evergreen scrub forest. |
all stages |
41-70% |
24,18 |
|
Lowland broadleaf moist evergreen seasonal forests over limestone, northeastern variant. |
stage unknown |
Canopy unknown |
18 |
|
Mixed mangrove scrub. |
stage unknown |
Canopy unknown |
18 |
|
Broadleaf hill forests over limestone in rolling or flat terrain. |
all stages |
41-70% |
24,11 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
all stages |
41-70% |
24,11 |
|
Pine Forest and Orchard Savanna |
all stages |
71-100% |
24 |
|
Broadleaf hill forests over non-calcareous rocks, Santa Maria variant. |
stage unknown |
Canopy unknown |
26 |
|
Marsh and Swamp Communities |
all stages |
71-100% |
24 |
|
Marsh and Swamp Communities |
all stages |
71-100% |
24 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
stage unknown |
Canopy unknown |
29 |
|
Broadleaf Forest Rich in Lime-loving Species; Sapote-Mahogany |
all stages |
Canopy unknown |
24 |
|
Riparian seasonal swamp forests |
all stages |
Canopy unknown |
24 |
|
Marsh and Swamp Communities |
stage unknown |
Canopy unknown |
27 |
|
Broadleaf Forest Moderately Rich in Lime-loving Species; Cohune-Quamwood Forest |
all stages |
Canopy unknown |
24,18 |
|
URBAN, human settlement. |
all stages |
Canopy unknown |
24 |
|
Broadleaf Forest Rich in Lime-loving Species; Ramon-Chiquebul forest. |
stage unknown |
Canopy unknown |
26 |
|
Pine Forest and Orchard Savanna |
stage unknown |
Canopy unknown |
24 |
|
Lowland needle-leaf moist open forests over poor soils. |
stage unknown |
Canopy unknown |
27 |
|
Transitional Low Broadleaf Forest and Shrubland |
stage unknown |
Canopy unknown |
27 |
|
Broadleaf Forest with Occasional Lime-loving Species; Negrito-Cohune Palm Forest. |
stage unknown |
Canopy unknown |
24 |
|
Seasonal swamp forests of Southern and Central Belize, typical variant. |
stage unknown |
Canopy unknown |
29 |
|
Broadleaf Forest with Few Lime-loving Species |
stage unknown |
Canopy unknown |
27 |
|
Cohune Palm Forest |
stage unknown |
Canopy unknown |
24,24 |
|
Broadleaf Forest Moderately Rich in Lime-loving Species; Quamwood-Bastard Mahogany Forest. |
stage unknown |
Canopy unknown |
26 |
|
Needle-leaf hill forests over poor soils (Mountain Pine Ridge). |
stage unknown |
Canopy unknown |
24 |
|
Broadleaf Forest w/Occasional Lime-loving Species; Cohune-Banak forest. |
stage unknown |
Canopy unknown |
24 |
|
Broadleaf Forest Rich in Lime-loving Species |
stage unknown |
Canopy unknown |
26 |
|
Lowland broadleaf rain forest over poor or sandy soils. |
stage unknown |
Canopy unknown |
26 |
|
Marsh and Swamp Communities |
stage unknown |
Canopy unknown |
26 |
|
Broadleaf Forest with few Lime-loving Species |
stage unknown |
Canopy unknown |
26 |
|
Broadleaf hill forests over limestone in rolling or flat terrain. |
mature tree |
Canopy unknown |
26 |
|
Seasonal swamp forests (marsh forests) of Northern Belize, variant 1. |
mature tree |
Canopy unknown |
24 |
|
Broadleaf Forest Rich in Lime-loving Species; Sapote-Mahogany Forest |
mature tree |
Canopy unknown |
24,24,18 |
|
Lowland broadleaf moist evergreen seasonal forest over limestone, northwestern variant. |
mature tree |
Canopy unknown |
24 |
|
Broadleaf Forest Rich in Lime-loving Species: Sapote-Silion forest. |
mature tree |
Canopy unknown |
24 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
mature tree |
Canopy unknown |
24 |
|
Lowland broadleaf rain forests over moderately lime-rich alluvium. |
mature tree |
Canopy unknown |
24 |
|
Broadleaf Forest Rich in Lime-loving Species; Chiquebul-Bullhoof Forest |
Disturbed |
41-70% |
22 |
|
Broadleaf hill forests over limestone in steep terrain. |
Disturbed |
41-70% |
22,19,7 |
|
Broadleaf Forest Rich in Lime-loving Species |
all stages |
41-70% |
21,19,7 |
|
Agriculture, no native vegetation. |
Disturbed |
41-70% |
22 |
|
Transitional Low Broadleaf Forest and Shrubland |
stage unknown |
Canopy unknown |
12 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
stage unknown |
Canopy unknown |
5 |
|
Lowland broadleaf rain forests over moderately lime-rich alluvium. |
stage unknown |
Canopy unknown |
5 |
|
Broadleaf Forest Rich in Lime-loving Species; Sapote-Mahogany Forest |
mature tree |
41-70% |
9 |
|
Transitional Broadleaf Forest Poor in Lime-loving Species |
all stages |
71-100% |
11 |
|
Broadleaf hill forests over limestone in rolling or flat terrain. |
all stages |
71-100% |
11 |
|
Trophic |
|
INSECTIVORE |
References on Trophic Level
16
|
Lifestage |
Food Item Consumed |
Part of Food Item |
|
|
Adult |
Lepidoptera |
Adult stage |
|
|
Adult |
Coleoptera |
Adult stage |
|
|
Adult |
Orthoptera |
Adult stage |
Comments on General Food Habits
16* The Common mustached bat has been variously reported to consume Lepidoptera (Bateman and Vaughan, 1974), mainly Coleoptera (Whitaker and Findley, 1980), and mainly Coleoptera and Lepidoptera (Howell and Burch, 1974). The latter authors reported that the sympatric P. suapurensis consumed mainly Orthoptera, suggesting food was partitioned by the two species. Selectivity in diet was supported by their rejection of lympyrid beetles, arctiid and ctenuchid moths, and the geometrid moth, Thyrinteina arnobia, when fed together other prey insects in the laboratory (Goldman and Henson, 1977).
Life History Narrative
24* This species has been found in virtually every habitat sampled in Belize. It appears to be a wide ranging habitat generalist. 16* Pteronotus parnellii has rather broad habitat associations, occurring in humid to arid habitats from coastal lowlands to 3,000 m (Smith, 1972). It is a common bat throughout its range, roosting during the day in caves and mines, which it often shares with other species of bats. The Common mustached bat prefers to roost in the largest chambers of large, humid caves. It emerges shortly after sunset and remains active for 5 to 7 h. In January a sex ratio of 1:1 of individuals sharing roosts, and frequent visits to the roost during the evening, are coincident with the period of copulation and may represent "swarming" (Goodwin, 1970). Following this period the sexes appear to segregate at different roosts. Pteronotus parnellii does not use night roosts and is assumed to remain "on the wing" during the entire period it is absent from its day roost. These bats fly near the ground and follow definite routes (usually along natural depressions in the topography) when dispersing from day roost to feeding grounds, which may be several kilometers distant (Bateman and Vaughan, 1974). The average flight speed of P. parnellii along a natural flyway is 17.5 km/h (Kennedy et al., 1977).
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. 1:90-92 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 McCarthy, T. J., M. Blake. 1987. Noteworthy bat records from the Maya Mountains Forest Reserve, Belize. Mammalia v. 51, No. 1, pp.161-164 6 Jacobson, S. 1990. Wildlife Inventory of the Rio Bravo Conservation and Management Area. Parts I and II. Appendix 2. 7 Howell, D. 1990. The Bats of Caracol. Parts I and II. 22 pp. Unpub. report for Wildlife Conservation Society. 8 Miller, C.M., B.W. Miller. 1994 (Nov.). Working Checklist: Mammals of Gallon Jug and Chan Chich Lodge Area. Unpublished list. 9 Quigley, H. B., B. W. Miller, C. M. Miller. 1995. Mammal Survey, Shipstern Nature Reserve, April 4-13, 1995. Unpublished report for ITCF. 10 Cartwright, Anne McKnight Furnish. 1977. Patterns of Neotropical Chiroptera Reproduction Including Histological and Ecological Aspects of Bats Collected In Belize. Dissertation for Doctor of Education. Ball State University. Muncie, Indiana. 11 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. 12 ROM. 1995. Collections data from mammal department, Royal Ontario Museum. 13 LSU Museum of Natural Science, Belize collection. August 31, 1995. Curator: Mark S. Hafner. 14 Smith, Rosemary L. 1994. Neotropical Bats as Indicators of Environmental Disturbance. Masters Thesis. Durrell Institute of Conservation and Ecology. pp.64. 15 Koopman, Karl F. 1994. Chiroptera: Systematics (in) Handbook of Zoology. W. de Gruyter. Berlin-NY. p.46. 16 Herd, R. M. 1983. Pteronotus parnellii. Mammalian Species. No.209. pp.1-5. American Society of Mammalogists. 17 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. 18 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. 19 Miller, B.W. and C.M. Miller. 1993. Mist net bat survey. March-April 1992, October 1993. Biodiversity of Caracol Archaeological Reserve. Wildlife Conservation Society Tropical Forest and Reserve Planning Project Belize. Unpublished report. 20 Miller, B.W. 1999. Prliminary reconaisance of the bats of the Sarstoon and Temash rivers. Wildlife Conservation Society, Tropical Forest and Reserve Planning Project, Belize. Unpublished technical report. 21 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. 22 Miller, B.W. 1996. Preliminary reconaisance of the bats of Five Blues Lake National Park. Survey at Tamandua Farm south of Five Blues Lake N.P. Wildlife Conservation Society, Tropical Forest and Reserve Planning Project, Belize. Unpublished data. 23 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. 24 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. 25 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. 26 CM. 1997. Carnegie Musuem, Division of mammals. Data imported on date: 06/13/00. 27 FMNH. 1997. Mammal holdings in the Field Musuem of Natural History, unpublished listing. Data imported pn date: 06/13/00. 28 UF. Florida Sate Musuem Mammal Deptartment, Belize holdings. University of Florida, Gainesville. Imported on date: 09/20/00 29 MSU. Michigan State University. Mammal collection holdings form Belize. Imported on 9/22/00. 30 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. 31 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. 32 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.