Research Article |
Corresponding author: Vinícius Cardoso Cláudio ( vcclaud@gmail.com ) Corresponding author: Ricardo Moratelli ( rimoratelli@gmail.com ) Academic editor: Valeria Da Cunha Tavares
© 2020 Vinícius Cardoso Cláudio, Gedimar Pereira Barbosa, Fabrício Braga Rassy, Vlamir José Rocha, Ricardo Moratelli.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Cardoso Cláudio V, Barbosa GP, Rassy FB, Rocha VJ, Moratelli R (2020) The bat fauna (Mammalia: Chiroptera) of Carlos Botelho State Park, Atlantic Forest of Southeastern Brazil, including new distribution records for the state of São Paulo. Zoologia 37: 1-32. https://doi.org/10.3897/zoologia.37.e36514
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Carlos Botelho State Park (PECB) is a large remnant of Atlantic Forest in Southeastern Brazil, with more than 37,000 ha. As its bat fauna is still unknown, we performed the first bat survey on PECB, to provide data on the distribution, natural history and taxonomy of the species. Fieldwork was conducted monthly, from October 2016 to September 2017. Captures were made using ground-level mist-nets (39600 m2.h), canopy mist-nets (2017.5 m2.h) and searches for roosts (42 hours).We captured 412 bats from 34 species of Phyllostomidae, Molossidae and Vespertilionidae. A total of 11 species were captured only in ground-level mist-nets, five in canopy mist-nets, and seven in roosts. Dermanura cinerea Gervais, 1856, Eptesicus taddeii Miranda, Bernardi & Passos, 2006, Glyphonycteris sylvestris Thomas, 1896 and Lampronycteris brachyotis (Dobson, 1879) are rare on surveys conducted in the Atlantic Forest of São Paulo and were captured in canopy mist-nets. Micronycteris schmidtorum Sanborn, 1935 and Molossus currentium Thomas, 1901 constitute the first record for the state of São Paulo, and were captured in canopy mist-nets and roosts, respectively. The species richness registered for PECB surpasses other surveys conducted in Atlantic Forest localities that use only ground-level mist-nets. Our results reinforce the importance of employing mixed capture methods, such as elevated mist-nets and searches for roosts.
Capture methods, morphology, survey, taxonomy
The Atlantic Forest includes a large variety of phytophysiognomies, leading to an expressive environmental diversity, which has provided conditions for the occurrence of numerous species, resulting in the establishment of an extremely rich biotic complex (
Currently, Atlantic Forest remnants comprise 28% of their original area, considering all the successional stages and phytophysiognomies: forests, natural grasslands, restingas and mangroves (
The larger remnants and endemism areas of the biome are located on Southeast and South regions, key regions to conservation strategies (
Due to their large niche breadth, bats play indispensable ecological roles in tropical forests (
Species identifications can be major impediment to interpreting inventory results (
The Carlos Botelho State Park (Parque Estadual Carlos Botelho – PECB) is a protected area created in 1982 (24°06'55"–24°14'41"S; 47°47'18" – 48°07'17"W; Fig.
From October 2016 to September 2017, we conducted 48 nights of sampling at PECB in localities ranging from 80 to 850 m of elevation. On each night 10 ground-level mist-nets (0.5–3 m height) and one canopy mist-net (~ 8–10.5 m) were used. Nets remained opened from dusk to 4 hours after sunset, and samplings were conducted during the new moon (
Field identifications were based on keys provided by
Bat species from Carlos Botelho State Park, São Paulo, Brazil, captures divided by sampling method and voucher specimens in the collections of Universidade Federal de São Carlos – campus Sorocaba (ZSP) and the Museu Nacional, Universidade Federal do Rio de Janeiro (MN).
Species | Method | Total | Voucher material | ||
Ground | Canopy | Roost | |||
Phyllostomidae | |||||
Micronycterinae | |||||
Lampronycteris brachyotis (Dobson, 1879) | – | 1 | – | 1 | ZSP 040 |
Micronycteris microtis Miller, 1898 | 2 | – | – | 2 | ZSP 011, ZSP 028 |
Micronycteris schimdtorum Sanborn, 1935 | – | 1 | – | 1 | ZSP 013 |
Desmodontinae | |||||
Desmodus rotundus (É. Geoffroy, 1810) | 16 | 2 | – | 18 | ZSP 006, ZSP 031 |
Diphylla ecaudata (Jentink, 1893) | 4 | – | – | 4 | ZSP 039, ZSP 049 |
Phyllostominae | |||||
Mimon bennettii (Gray, 1838) | 1 | – | – | 1 | ZSP 041 |
Trachops cirrhosus (Spix, 1823) | 3 | – | – | 3 | ZSP 024 |
Glossophaginae | |||||
Anoura caudifer (É. Geoffroy, 1818) | 20 | 6 | 15 | 41 | ZSP 001, ZSP 012 |
Anoura geoffroyi Gray, 1838 | 22 | 6 | – | 28 | ZSP 014, ZSP 057 |
Glossophaga soricina (Pallas, 1766) | – | – | 1 | 1 | ZSP 060 |
Carolliinae | |||||
Carollia perspicillata (Linnaeus, 1758) | 95 | – | – | 95 | ZSP 008, ZSP 022, ZSP 023, ZSP 045 |
Glyphonycterinae | |||||
Glyphonycteris sylvestris Thomas, 1896 | – | 2 | – | 2 | ZSP 033, ZSP 042 |
Stenodermatinae | |||||
Artibeus fimbriatus Gray, 1838 | 37 | 8 | 1 | 46 | ZSP 027, ZSP 037 |
Artibeus lituratus (Olfers, 1818) | 7 | 3 | – | 10 | ZSP 015, ZSP 056 |
Artibeus obscurus (Schinz, 1821) | 27 | 4 | – | 31 | ZSP 009, ZSP 025 |
Dermanura cinerea Gervais, 1856 | 7 | 1 | – | 8 | ZSP 035, ZSP 036 |
Platyrrhinus lineatus (É. Geoffroy, 1810) | – | 1 | – | 1 | ZSP 032 |
Platyrrhinus recifinus (Thomas, 1901) | 1 | – | – | 1 | ZSP 055 |
Pygoderma bilabiatum (Wagner, 1843) | 3 | – | – | 3 | ZSP 043, ZSP 044 |
Sturnira lilium (É. Geoffroy, 1810) | 27 | 4 | – | 31 | ZSP 002 |
Sturnira tildae de la Torre, 1959 | 5 | – | – | 5 | ZSP 029, ZSP 038 |
Vampyressa pusilla (Wagner, 1843) | 1 | – | – | 1 | ZSP 058 |
Molossidae | |||||
Molossinae | |||||
Cynomops abrasus (Temminck, 1826) | – | – | 1 | 1 | ZSP 021 |
Molossops neglectus Williams & Genoways, 1980 | – | 1 | – | 1 | ZSP 016 |
Molossus currentium Thomas, 1901 | – | – | 1 | 1 | ZSP 050 |
Molossus molossus (Pallas, 1766) | – | – | 28 | 28 | ZSP 003, ZSP 018, ZSP 020, ZSP 053 |
Molossus rufus É. Geoffroy, 1805 | – | – | 3 | 3 | ZSP 019, ZSP 026, ZSP 059 |
Vespertilionidae | |||||
Vespertilioninae | |||||
Eptesicus taddeii Miranda, Bernardi & Passos, 2006 | 2 | 1 | – | 3 | ZSP 017, ZSP 048 |
Histiotus velatus (I. Geoffroy, 1824) | – | – | 13 | 13 | ZSP 004, ZSP 046 |
Lasiurus ebenus Fazzolari-Corrêa, 1994 | 1 | – | – | 1 | MN 83982 |
Myotinae | |||||
Myotis albescens (É. Geoffroy, 1806) | – | – | 2 | 2 | ZSP 005 |
Myotis nigricans (Schinz, 1821) | 20 | – | 1 | 21 | ZSP 010, ZSP 051 |
Myotis riparius Handley, 1960 | 2 | – | – | 2 | ZSP 007, ZSP 052 |
Myotis ruber (É. Geoffroy, 1806) | 1 | – | 1 | 2 | ZSP 047, ZSP 054 |
Total species | 22 | 14 | 11 | 34 | – |
Total captures | 304 | 41 | 67 | 412 | – |
Comparison between the results of bat inventories conducted in the Atlantic Forest of Southeastern Brazil, including sampling efforts, number of captures and species, and sampling methods. *Mist-nets installed inside roosting sites (caves).
Protected area, state | Sampling effort | Number of species | Number of captures | Sampling methods | References |
Parque Estadual da Cantareira, São Paulo | 136,080 m2.h | 22 | 598 | Ground-level mist-nets |
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Parque Estadual Intervales, São Paulo | - | 24 | 371 | Ground-level mist-nets |
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Parque Estadual da Ilha do Cardoso, São Paulo | 61,776 m2.h | 27 | 393 | Ground-level mist-nets |
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Reserva Biológica do Tinguá, Rio de Janeiro | – | 28 | 655 | Ground-level mist-nets |
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Parque Estadual Carlos Botelho, São Paulo | 41,618 m2.h, 42h of search for roosts |
34 | 412 | Ground-level mist-nets, elevated mist-nets, and search for roosts | This study |
Parque Estadual Turístico do Alto Ribeira, São Paulo | 25,320 m2.h | 35 | 2002 | Ground-level mist-nets, elevated mist-nets, and search for roosts* |
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Thirteen skull measurements based on
Randomized accumulation curves were constructed to assess the completeness of sampling effort and compare different survey techniques, according to Cowell et al. (
We captured 412 bats, distributed into three families and 34 species (Table
Individual-based species accumulation curve of bat species captured in Parque Estadual Carlos Botelho with 39,600 m2.h of ground-level mist-nets (Blue), and with 2017.5 m2.h of canopy mist-nets (Red); the analysis of the curve indicates that it is still in a accumulation stage. Error bars show confidence interval (95%).
The randomized accumulation curve of ground-level mist-nets captures showed a slight tendency to level off, however, the curve is still in an accumulation stage (Fig.
Among the 34 species reported, 11 were obtained exclusively with ground-level mist nets, five exclusively with canopy mist-nets, and seven exclusively with the search for roosts. Additionally, the first occurrence records for Micronycteris schmidtorum Sanborn, 1935 and Molossus currentium Thomas, 1901 for the state of São Paulo, along with all other molossids captured, were made with canopy nets or search for roosts. Molossids are rarely captured in ground-level mist-nets due to its foraging habits (
The employment of mixed methodologies for bat sampling also showed positive results in other studies and it has been encouraged by many authors (
Below we provide the list of species, identification, morphology description, distribution and natural history notes for all the species captured on PECB. The taxonomic arrangement and nomenclature follow
Lampronycteris Sanborn is a monotypic genus represented by L. brachyotis Dobson, 1879. It is morphologically similar to Glyphonycteris O. Thomas, 1896, Micronycteris Gray, 1866, Neonycteris Sanborn, 1949, and Trinycteris Sanborn, 1949, which also occur in Brazil (
In Brazil the species occurs in the Amazon, Cerrado and Atlantic Forest biomes, in the states of Acre, Amazonas, Goiás, Rondônia, Pará, Tocantins, Piauí, Bahia, Espírito Santo, São Paulo, Mato Grosso, and Paraná (
The only specimen was captured in May. It is an adult non-reproductive female captured in a mist-net suspended 8 m over a small stream in sampling site M5 (Appendix
Bat species captured in Carlos Botelho State Park, São Paulo state, Brazil: (4) Lampronycteris brachyotis; (5) Micronycteris microtis; (6) Micronycteris schmidtorum; (7) Desmodus rotundus; (8) Diphylla ecaudata; (9) Mimon bennettii; (10) Trachops cirrhosus; (11) Anoura caudifer; (12) Anoura geoffroyi; (13) Glossophaga soricina; (14) Carollia perspicillata; (15) Glyphonycteris sylvestris.
Selected measurements (mm) and weigth (g) for specimens of Micronycterinae and Desmodontinae from PECB, São Paulo state, Brazil. * Mean values from
Measurement | Micronycterinae | Desmodontinae | |||||||||||
Lampronycteris brachyotis | Micronycteris microtis | Micronycteris schimdtorum | Desmodus rotundus | Diphylla ecaudata | |||||||||
ZSP 040 ♀ | ZSP 011 ♂ | ZSP 028 ♀ | ZSP 013 ♂ (PECB) | (Brazil)* | ZSP 006 ♀ | ZSP 031 ♂ | ZSP 039 ♂ | ZSP 049 ♂ | |||||
W | 16.0 | 10.5 | 8.5 | 9.0 | – | 34.0 | 39.5 | 30.0 | 27.0 | ||||
BL | 60.66 | 50.94 | 41.28 | 49.52 | 42.80 (n = 2) | 83.52 | 80.42 | 70.91 | 68.38 | ||||
FA | 41.50 | 34.11 | 34.93 | 35.56 | 33.95 (n = 4) | 64.01 | 61.55 | 53.44 | 52.59 | ||||
TL | 16.96 | 14.88 | 15.46 | 17.67 | – | 28.44 | 27.62 | 21.92 | 21.97 | ||||
EL | 17.66 | 21.29 | 21.64 | 18.37 | 17.57 (n = 3) | 17.67 | 19.66 | 13.45 | 13.46 | ||||
TRL | 5.90 | 6.93 | 6.28 | 5.73 | – | 6.74 | 7.33 | 6.97 | 5.52 | ||||
GLS | 21.81 | 18.79 | 18.30 | 20.13 | 19.07 (n = 4) | 25.92 | 24.96 | 23.00 | 23.48 | ||||
CI | 19.68 | 16.38 | 16.19 | 17.62 | – | 23.11 | 21.96 | 20.41 | 20.77 | ||||
BB | 8.77 | 7.80 | 7.50 | 8.06 | 7.85 (n = 4) | 13.00 | 12.45 | 11.50 | 11.38 | ||||
ZB | 10.76 | 8.76 | 8.80 | 9.18 | 8.93 (n = 3) | 12.20 | 12.42 | 12.61 | 12.37 | ||||
PB | 5.02 | 3.91 | 3.91 | 4.41 | 4.20 (n = 3) | 5.74 | 5.77 | 6.70 | 6.80 | ||||
CC | 3.99 | 3.07 | 3.11 | 3.36 | 3.17 (n = 4) | 6.36 | 6.46 | 5.77 | 5.71 | ||||
MB | 9.03 | 7.52 | 7.48 | 7.96 | 8.62 (n = 4) | 11.57 | 11.68 | 11.39 | 11.34 | ||||
PL | 10.61 | 9.14 | 8.57 | 9.67 | – | 10.21 | 9.55 | 7.48 | 7.66 | ||||
MXTL | 8.28 | 6.88 | 6.66 | 7.76 | 7.27 (n = 4) | 3.73 | 3.62 | 3.54 | 3.67 | ||||
MLTL | 6.89 | 5.84 | 5.66 | 6.47 | – | 1.41 | 1.31 | 1.47 | 1.76 | ||||
DL | 14.79 | 11.86 | 11.64 | 12.52 | 11.96 (n = 3) | 15.36 | 14.82 | 13.68 | 13.87 | ||||
MNTL | 9.42 | 7.57 | 7.62 | 8.24 | 7.57 (n = 4) | 8.06 | 7.06 | 6.40 | 6.54 | ||||
CH | 5.15 | 3.65 | 3.69 | 4.61 | – | 6.37 | 6.00 | 4.53 | 4.56 |
Eight species of Micronycteris Gray, 1866, occur in Brazil (
In Brazil the species is recorded in Amazon, Cerrado and Atlantic Forest biomes, in the states of Amazonas, Pará, Amapá, Rondônia, Bahia, Rio de Janeiro, Espírito Santo, Minas Gerais, São Paulo and Mato Grosso (
We captured one adult male and one adult female of M. microtis, which were both taken in ground-level mist-nets in sampling sites M3 and M16 (Appendix
Micronycteris schmidtorum belong to the “pale venter" group, and can be distinguished from other pale venter species based on several morphological features. Micronycteris schmidtorum and M. brosseti are morphologically closer. Both present intermediate interauricular band with moderate notch, have the calcar longer than the hindfoot, and the dorsal fur larger than 7 mm, while in M. minuta, M. homezorum and M. sanborni the band is high and deep-notched, the calcar is equal or smaller than the hindfoot, and the dorsal fur is smaller than 7 mm (
The species was previously recorded in the Amazon, Caatinga, Cerrado and Atlantic Forest, in the states of Amapá, Amazonas, Pará, Tocantins, Mato Grosso, Maranhão, Paraíba, Pernambuco, Alagoas, Sergipe, Bahia, and Minas Gerais (
We captured one adult male in October, which was taken in a mist-net elevated 8 m over a wide trail in sampling site M4 (Appendix
Desmodus rotundus is the only species in Desmodus Wied-Newied, 1826. Desmodontinae also includes other two species, Diaemus youngii (Jentink, 1893) and Diphylla ecaudata Spix, 1823 (
In Brazil the species is recorded in all biomes and states (
We captured 18 individuals (5 males and 13 females) of D. rotundus, of which 16 were taken in February, March, April, June, July, August and October in ground-level mist-nets in sampling sites M2, M14, M16, M18, M19, M23, M24, M25, M29, M34, M36 and M39, in different elevations and plant physiognomies; and two on June in a mist-net elevated 8 m in sampling site M33 (Appendix
This species can be separated from D. rotundus and D. youngii as described above and by presence of a shorter and well-furred uropatagium. Diphylla ecaudata also differs from D. youngii by the presence of a short calcar and absence of white tips on the wings (
In Brazil, the species is recorded in the Amazon, Atlantic Forest, Cerrado and Caatinga biomes, in the states of Amazonas, Acre, Rondônia, Pará, Amapá, Tocantins, Ceará, Pernambuco, Sergipe, Bahia, Minas Gerais, Espírito Santo, Rio de Janeiro, São Paulo, Paraná, and Santa Catarina (
Three males and one female were captured in April, June, August and September in mist-nets set at ground-level in sampling sites M17, M25, M28 and M34 (Appendix
Mimon bennettii (Gray, 1838) is the only species of Mimon (Gray, 1847) registered in Brazil (
The species is recorded in all Brazilian biomes, except Pampas, occurring in the states of Amapá, Piauí, Bahia, Mato Grosso, Mato Grosso do Sul, Goiás, Minas Gerais, Espírito Santo, Rio de Janeiro, São Paulo, Paraná, and Santa Catarina (
We captured one non-reproductive female in May, with a ground-level mist-net crossing a wide stream in sampling site M18 (Appendix
Locality records of Micronycteris schmidtorum in Brazil. The map numbers correspond to the records as indicated in Fig.
Map | Locality | Coordinates | Author |
1 | Parque Nacional Montanhas do Tumucumaque, Amapá | 02°10.00'N, 54°34.00'W |
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2 | Manaus, Amazonas | 02°24.00'S, 59°43.00'W |
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3 | Alter do Chão, Pará | 02°30.00'S, 54°57.00'W |
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4 | Santarém, Pará | 02°27.00'S, 54°40.00'W |
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5 | Belém, Pará | 01°27.00'S, 48°30.00'W |
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6 | Inhamum Municipal Environmental Protection Area, Caxias, Maranhão | 04°53.00'S, 43°22.00'W |
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7 | Reserva Biológica Guaribas, Paraiba | 06°42.00'S, 35°11.00'W |
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8 | Exu, Pernambuco | 07°30.00'S, 39°42.00'W |
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9 | São Lourenço da Mata, Pernambuco | 08°00.00'S, 35°01.00'W |
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10 | Paraíso do Tocantins, Tocantins | 10°10.00'S, 48°52.00'W |
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11 | Reserva Particular do Patrimônio Natural (RPPN) Sitio Pau-Brasil, Cururipe, Alagoas | 10°06.00'S, 36°13.00'W |
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12 | Parque Nacional Serra de Itabaiana, Areia Branca, Sergipe | 10°46.00'S, 37°21.00'W |
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13 | Aurora do Tocantins, Tocantins | 12°35.00'S, 46°32.00'W |
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14 | APA Cabeceiras do Rio Cuiabá, Rosário Oeste, Mato Grosso | 14°19.00'S, 55°43.00'W |
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15 | Médio Rio São Francisco, Bahia | 13°25.00'S, 43°04.00'W |
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16 | Vitória da Conquista, Bahia | 14°51.00'S, 40°51.00'W |
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17 | Ilhéus, Bahia | 14°46.00'S, 39°01.00'W |
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18 | Una, Bahia | 15°16.00'S, 39°04.00'W |
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19 | Parque Estadual Rio Doce, Minas Gerais | 19°44.00'S, 42°34.00'W |
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20 | Carlos Botelho State Park, São Paulo | 24°12.00'S, 47°56.00'W | This study |
Selected measurements (mm) and weigth (g) for specimens of Phyllostominae, Glyphonycterinae and Glossophaginae from PECB, São Paulo state, Brazil. See Material and Methods for description of measurements.
Measurement | Phyllostominae | Glyphonycterinae | Glossophaginae | |||||||||||
Mimon bennettii | Trachops cirrhosus | Glyphonycteris sylvestris | Anoura caudifer | Anoura geoffroyi | Glossophaga soricina | |||||||||
ZSP 041 ♀ | ZSP 024 ♂ | ZSP 033 ♂ | ZSP 042 ♂ | ZSP 001 ♂ | ZSP 012 ♀ | ZSP 014 ♀ | ZSP 057 ♂ | ZSP 060 ♂ | ||||||
W | 22.0 | 32.0 | 18.0 | 12.0 | 12.0 | 12.0 | 22.0 | 17.5 | 10.5 | |||||
BL | 65.83 | 74.32 | 52.12 | 55.39 | 61.22 | 53.32 | 69.79 | 63.05 | 54.13 | |||||
FA | 57.29 | 57.89 | 40.96 | 43.30 | 38.18 | 36.17 | 42.00 | 42.23 | 36.92 | |||||
TL | 24.77 | 25.55 | 15.02 | 15.98 | 13.87 | 14.00 | 16.20 | 15.52 | 15.64 | |||||
EL | 35.30 | 27.20 | 17.89 | 15.87 | 13.86 | 12.57 | 14.33 | 15.87 | 15.35 | |||||
TRL | 13.99 | 10.27 | 6.38 | 7.31 | 4.70 | 5.77 | 4.98 | 5.57 | 5.99 | |||||
GLS | 25.55 | 28.08 | 20.96 | 22.01 | 23.00 | 22.52 | 26.23 | 25.52 | 21.06 | |||||
CI | 22.86 | 24.69 | 19.17 | 19.94 | 22.28 | 21.81 | 25.51 | 24.64 | 19.93 | |||||
BB | 9.77 | 11.23 | 9.11 | 9.36 | 9.51 | 8.92 | 9.95 | 9.95 | 8.85 | |||||
ZB | 13.52 | 13.31 | 10.34 | 10.62 | 10.03 | 9.52 | 11.20 | 11.30 | 9.84 | |||||
PB | 4.71 | 5.18 | 5.01 | 5.01 | 4.78 | 4.49 | 5.19 | 5.26 | 4.90 | |||||
CC | 5.40 | 5.75 | 3.52 | 3.77 | 4.52 | 4.20 | 4.61 | 4.86 | 3.90 | |||||
MB | 10.53 | 11.69 | 8.62 | 8.93 | 8.94 | 8.68 | 10.10 | 9.80 | 8.78 | |||||
PL | 12.75 | 11.22 | 9.86 | 10.39 | 12.81 | 12.41 | 15.26 | 14.20 | 11.53 | |||||
MXTL | 9.56 | 10.20 | 8.30 | 8.77 | 8.41 | 8.32 | 10.23 | 9.50 | 7.40 | |||||
MLTL | 8.01 | 8.19 | 6.63 | 7.27 | 7.25 | 7.03 | 8.54 | 7.46 | 5.51 | |||||
DL | 17.14 | 18.19 | 13.60 | 14.50 | 16.83 | 16.35 | 19.20 | 17.83 | 14.43 | |||||
MNTL | 10.89 | 11.40 | 9.18 | 10.05 | 9.35 | 8.77 | 11.30 | 10.53 | 8.32 | |||||
CH | 5.92 | 4.97 | 3.81 | 4.19 | 4.27 | 3.64 | 4.57 | 4.90 | 4.26 |
Monotypic, T. cirrhosus is easily distinguished from other members of Phyllostominae by the elongated papillae-like projections around the mouth (
In Brazil the species occurs in all biomes, except Pampas, with records in the states of Amazonas, Acre, Rondônia, Roraima, Pará, Amapá, Tocantins, Mato Grosso, Mato Grosso do Sul, Goiás, Paraná, São Paulo, Rio de Janeiro, Minas Gerais, Espírito Santo, Bahia, Sergipe, Alagoas, Pernambuco, Paraíba, Ceará, and Piauí (
Field observations, We captured two males and one female of T. cirrhosus, which were taken in ground-level mist-nets in sampling sites M4, M10 and M16 (Appendix
Anoura Gray, 1838 is represented in Brazil by A. caudifer (É. Geoffroy, 1818) and A. geoffroyi Gray, 1838 (
In Brazil the species is recorded in all biomes, except Caatinga, occurring in the states of Acre, Amazonas, Amapá, Bahia, Espírito Santo, Goiás, Minas Gerais, Mato Grosso do Sul, Mato Grosso, Pará, Paraná, Rio de Janeiro, Rio Grande do Sul, Santa Catarina, and São Paulo (
We recorded 41 specimens, 20 of which (12 males and 8 females) were taken in ground-level mist-nets in sampling sites M3, M4, M6, M7, M11, M16, M19, M20, M21, M22, M23, M25, M27, M29 and M38; six (1 male and 5 females) were taken at mist-nets elevated 8 m in sampling sites M5 and M9; and 15 were captured inside a culvert in sampling site S1 (Appendix
The diagnosis of A. geoffroyi is described above. Specimens from PECB (ZSP 014, 057; see Table
In Brazil, the species is recorded in all biomes, in the states of Amapá, Bahia, Ceará, Espírito Santo, Goiás, Minas Gerais, Mato Grosso do Sul, Mato Grosso, Pará, Paraíba, Pernambuco, Piauí, Paraná, Rio de Janeiro, Rio Grande do Sul, Santa Catarina, Tocantins, and São Paulo (
We recorded 28 specimens, 22 of which (5 males and 17 females) were taken in ground-level mist-nets in the sampling sites M4, M6, M7, M17, M20, M21, M23, M26 and M32; and six (2 males and 4 females) at mist-nets elevated 8 m in sampling sites M5, M6, M7, M20 and M31 (Appendix
Three species of Glossophaga É. Geoffroy, 1818 occur in Brazil: G. commissarisi Gardner, 1962, G. longirostris Miller, 1898, and G. soricina (Pallas, 1766) (
In Brazil, the species is recorded in all biomes and states (
We captured one adult male in September in a building roof, in sampling site S17 (Appendix
Carollia Gray, 1838 is represented in Brazil by C. benkeithi Solari & Baker, 2006, C. brevicauda (Schinz, 1821) and C. perspicillata (Linnaeus, 1758) (
Specimens from PECB (ZSP 008, 022, 023, 045; see Table
In Brazil the species is widely distributed, recorded in all biomes and states (
We captured 95 individuals (51 males and 44 females), all of them were taken at ground-level mist-nets in sampling sites M3, M4, M5, M6, M10, M13, M14, M16, M17, M18, M19, M20, M21, M22, M23, M24, M25, M27, M28, M31, M33 and M34 (Appendix
Selected measurements (mm) and weigth (g) for specimens of Carolliinae and Stenodermatinae from PECB, São Paulo state, Brazil. See Material and Methods for description of measurements.
Measurement | Carolliinae | Stenodermatinae | ||||||||||||
Carollia perspicillata | Pygoderma bilabiatum | Artibeus fimbriatus | Artibeus lituratus | Artibeus obscurus | ||||||||||
ZSP 022 ♂ | ZSP 045 ♂ | ZSP 043 ♂ | ZSP 044 ♂ | ZSP 027 ♀ | ZSP 037 ♂ | ZSP 015 ♀ | ZSP 056 ♂ | ZSP 009 ♂ | ZSP 025 ♀ | |||||
W | 15.0 | 19.0 | 18.0 | 16.0 | 48.0 | 49.5 | 64.5 | 65.0 | 39.0 | 43.0 | ||||
BL | 59.93 | 55.65 | 59.60 | 59.22 | 81.02 | 81.61 | 94.72 | 88,37 | 77.50 | 77.82 | ||||
FA | 39.07 | 42.25 | 37.91 | 37.19 | 67.61 | 64.71 | 68.04 | 70,29 | 57.11 | 58.01 | ||||
TL | 16.99 | 16.34 | 19.82 | 21.16 | 28.72 | 27.05 | 30.06 | 26,61 | 22.94 | 21.16 | ||||
EL | 19.51 | 17.23 | 18.83 | 18.95 | 19.85 | 23.00 | 19.13 | 22,67 | 21.59 | 21.88 | ||||
TRL | 6.77 | 6.53 | 6.99 | 6.80 | 4.90 | 7.18 | 6.32 | 7,78 | 7.32 | 6.59 | ||||
GLS | 22.06 | 22.32 | 20.42 | 20.46 | 31.28 | 32.10 | 32.60 | 31.82 | 27.79 | 28.26 | ||||
CI | 19.97 | 20.41 | 17.57 | 17.40 | 28.06 | 28.53 | 28.95 | 28.22 | 25.00 | 25.73 | ||||
BB | 9.19 | 9.54 | 10.66 | 10.31 | 13.40 | 13.32 | 13.64 | 13.70 | 12.45 | 12.38 | ||||
ZB | 10.80 | 11.12 | 13.85 | 13.72 | 18.33 | 19.03 | 19.75 | 18.30 | 16.64 | 17.06 | ||||
PB | 5.32 | 5.46 | 7.94 | 7.85 | 7.35 | 7.69 | 7.86 | 6,54 | 6.69 | 6.38 | ||||
CC | 4.87 | 4.93 | 6.16 | 6.08 | 9.08 | 8.95 | 9.35 | 8.47 | 7.73 | 7.44 | ||||
MB | 9.35 | 9.75 | 11.04 | 10.75 | 14.44 | 14.93 | 15.62 | 14.82 | 13.44 | 13.33 | ||||
PL | 10.37 | 10.22 | 6.59 | 6.83 | 15.78 | 16.15 | 16.04 | 15.90 | 14.02 | 14.40 | ||||
MXTL | 7.28 | 7.38 | 5.49 | 5.62 | 11.27 | 11.92 | 11.94 | 11.06 | 10.41 | 10.36 | ||||
MLTL | 5.78 | 5.91 | 4.49 | 4.59 | 9.68 | 10.08 | 10.14 | 9.42 | 8.89 | 8.86 | ||||
DL | 13.99 | 14.45 | 12.02 | 12.03 | 21.61 | 21.41 | 21.87 | 21.83 | 19.55 | 19.69 | ||||
MNTL | 8.57 | 8.56 | 5.79 | 6.00 | 13.55 | 13.49 | 13.67 | 13.05 | 11.87 | 11.19 | ||||
CH | 5.38 | 5.28 | 4.36 | 4.53 | 9.14 | 8.83 | 9.89 | 10.03 | 8.06 | 7.91 |
Glyphonycteris Thomas is represented in Brazil by G. behnii (Peters, 1856), G. daviesi (Hill, 1965) and G. sylvestris Thomas, 1896 (
In Brazil the species is recorded in the Amazon, Cerrado and Atlantic Forest, occurring in the states of Amazonas, Amapá, Minas Gerais, Pará, Paraná, Rio de Janeiro, Roraima, São Paulo, and Tocantins (
We captured two adult males, in March and May, in mist-nets elevated 8 m over a wide stream, in sampling sites M18 and M24 (Appendix
Five species of Artibeus Leach, 1821 are found in Brazil: A. concolor Peters, 1865, A. fimbriatus Gray, 1838, A. lituratus (Olfers, 1818), A. obscurus (Schinz, 1821) and A. planirostris (Spix, 1832) (
Artibeus fimbriatus can be distinguished from A. planirostris by its larger size, the presence of sparse hairs on the dorsal side of the uropatagium and forearm (almost naked in A. planiostris), by the base of the noseleaf attached to the upper lip (separated in A. planirostris), and longer dorsal fur, close to 8 mm (6–8 mm in A. planirostris –
The PECB specimens (ZSP 027, 037; see Table
In Brazil, the species is recorded in all biomes, except Amazon, occurring in Distrito Federal and in the states of Ceará, Pernambuco, Sergipe, Bahia, Minas Gerais, Espírito Santo, Rio de Janeiro, São Paulo, Mato Grosso do Sul, Paraná, Santa Catarina, Rio Grande do Sul, Paraíba and Maranhão (
We recorded 46 specimens, 37 of which (14 males and 23 females) were taken in ground-level mist-nets set in sampling sites M7, M14, M16, M18 M20, M21, M24, M26, M27, M28, M32, M35, M36 and M38; eight (4 males and 4 females) in mist-nets elevated 8 m in sampling sites M14, M24, M26, M28 and M31; and one adult female on a building roof, in sampling site S2 (Appendix
The distinction between A. lituratus and A. fimbriatus is discussed above. A. lituratus can be externally distinguished from A. planirostris and A. obscurus by its larger size; well-marked facial stripes (poorly marked to absent on the other two); lack of ventral frosting (present on the other two species); base of the noseleaf attached to the upper lip, while is always separated in A. planirostris and in some A. obscurus; and dorsal side of the uropatagium densely furred, which is almost naked in A. planirostris and A. obscurus. Artibeus lituratus can also be distinguished from A. planirostris by the presence of dense fur on the dorsal side of the forearm (almost naked in A. planirostris). Additionally, A. lituratus has short dorsal fur (6–8 mm), which is longer in A. obscurus (8–10 mm –
In Brazil, the species is recorded in all biomes and states (
We captured 10 specimens, seven of which (4 males and 3 females) were taken in ground-level mist-nets in sampling sites M6, M18, M19, M21, M22 and M32; and three (1 male and 2 females) in mist-nets elevated 8 m in sampling sites M15, M20 and M24 (Appendix
The distinction of A. obscurus from A. lituratus and A. fimbriatus is discussed above. Artibeus obscurus and A. planirostris are similar in size and can be externally distinguished using the length of dorsal fur (8–10 mm in A. obscurus, 6–8 mm in A. planirostris), fur on the dorsal side of the forearm (densely furred in A. obscurus and almost naked in A. planirostris), and a more strong ventral frosting in A. obscurus, which is usually darker than A. planirostris (
In Brazil, the species is recorded in all the biomes except Pampas, in the states of Amazonas, Acre, Rondônia, Pará, Amapá, Roraima, Ceará, Piauí, Paraíba, Pernambuco, Sergipe, Bahia, Mato Grosso, Mato Grosso do Sul, Minas Gerais, Espírito Santo, Rio de Janeiro, São Paulo, Paraná, and Santa Catarina (
We recorded 31 captures, of which 27 (10 males and 17 females) were taken in mist-nets set at ground-level in the sampling sites M3, M4, M5, M16, M18, M21, M22, M23, M24, M25, M27, M28, M37 and M38, and four females in mist-nets elevated 8 m in the sampling sites M5, M18, M24 and M28 (Appendix
Four species of Dermanura Gervais, 1856 are found in Brazil: D. anderseni (Osgood, 1916), D. bogotensis (Andersen, 1906), D. cinerea Gervais, 1856, and D. gnoma (Handley, 1987) (
In Brazil, the species is recorded in the Amazon, Atlantic Forest, Caatinga and Cerrado biomes, in the states of Amazonas, Acre, Rondônia, Pará, Amapá, Roraima, Tocantins, Maranhão, Piauí, Paraíba, Pernambuco, Alagoas, Sergipe, Bahia, Mato Grosso, Minas Gerais, Goiás, Espírito Santo, Rio de Janeiro, São Paulo, Paraná, and Santa Catarina (
One of the eight (5 males and 3 females) individuals was captured in a mist-net elevated 8 m over a stream in sampling site M27, and the other seven were taken in mist-nets set at ground-level in the sampling sites M21, M22, M23, M25, M27 and M28 (Appendix
Bat species captured in Carlos Botelho State Park, São Paulo state, Brazil: (18) Artibeus fimbriatus; (19) Artibeus lituratus; (20) Artibeus obscurus; (21) Dermanura cinerea; (22) Platyrrhinus lineatus; (23) Platyrrhinus recifinus; (24) Pygoderma bilabiatum; (25) Sturnira lilium; (26) Sturnira tildae; (27) Vampyressa pusilla; (28) Cynomops abrasus; (29) Molossops neglectus.
Selected measurements (mm) and weigth (g) for specimens of Stenodermatinae from PECB, São Paulo state, Brazil. See Material and Methods for description of measurements.
Measurement | Stenodermatinae | ||||||||||||
Dermanura cinerea | Platyrrhinus lineatus | Platyrrhinus recifinus | Sturnira lilium | Sturnira tildae | Vampyressa pusilla | ||||||||
ZSP 035 ♀ | ZSP 036 ♀ | ZSP 032 ♀ | ZSP 055 ♂ | ZSP 002 ♂ | ZSP 029 ♀ | ZSP 038 ♀ | ZSP 058 ♂ | ||||||
W | 14.0 | 13.0 | 23.0 | 20.0 | 21.0 | 23.0 | – | 9.0 | |||||
BL | 55.57 | 54.22 | 58.09 | 62.26 | 62.70 | 63.75 | 66.43 | 50.69 | |||||
FA | 40.15 | 40.69 | 44.82 | 42.51 | 44.20 | 46.61 | 45.29 | 34.48 | |||||
TL | 16.33 | 15.70 | 18.03 | 16.01 | 18.56 | 19.66 | 18.55 | 12.91 | |||||
EL | 12.89 | 13.16 | 16.26 | 14.75 | 14.40 | 18.40 | 18.38 | 13.99 | |||||
TRL | 5.21 | 5.34 | 5.15 | 5.42 | 6.24 | 5.43 | 6.36 | 5.19 | |||||
GLS | 20.46 | 21.04 | 24.77 | 25.10 | 23.89 | 24.41 | 23.51 | 20.10 | |||||
CI | 18.44 | 18.42 | 22.31 | 23.18 | 21.35 | 21.97 | 21.05 | 18.46 | |||||
BB | 9.59 | 9.02 | 10.43 | 10.71 | 10.71 | 10.60 | 10.82 | 8.75 | |||||
ZB | 12.51 | 11.65 | 14.33 | 14.69 | 14.36 | 14.74 | 14.51 | 11.72 | |||||
PB | 4.68 | 4.49 | 5.43 | 5.92 | 6.11 | 6.18 | 5.98 | 5.05 | |||||
CC | 5.78 | 5.33 | 6.26 | 6.31 | 6.29 | 6.17 | 5.62 | 4.89 | |||||
MB | 10.12 | 9.50 | 11.33 | 11.93 | 11.29 | 11.36 | 11.43 | 9.54 | |||||
PL | 10.00 | 9.99 | 12.29 | 12.50 | 10.27 | 10.75 | 10.69 | 9.60 | |||||
MXTL | 6.56 | 6.75 | 9.33 | 9.42 | 6.83 | 7.00 | 6.81 | 6.83 | |||||
MLTL | 5.79 | 5.89 | 7.84 | 7.86 | 5.39 | 5.61 | 5.57 | 5.38 | |||||
DL | 12.97 | 13.23 | 16.93 | 17.44 | 15.62 | 15.60 | 15.23 | 12.76 | |||||
MNTL | 7.05 | 7.35 | 10.60 | 10.45 | 8.51 | 7.88 | 7.76 | 7.33 | |||||
CH | 5.01 | 5.45 | 5.96 | 5.99 | 6.12 | 6.02 | 5.82 | 4.26 |
In Brazil, Platyrrhinus Saussure, 1860 is represented by eight species: P. angustirostris Velazco, Gardner & Patterson, 2010, P. aurarius (Handley & Ferris, 1972), P. brachycephalus (Rouk and Carter, 1972), P. fusciventris Velazco, Gardner & Patterson, 2010, P. incarum (Thomas, 1912), P. infuscus (Peters, 1880), P. lineatus (É. Geoffroy, 1810) and P. recifinus (Thomas, 1901) (
The distinction between P. lineatus and P. recifinus is based on several characters, such as: presence of one interramal vibrissae in P. lineatus, absent in P. recifinus; tricolored dorsal fur in P. lineatus, tetracolored in P. recifinus; larger size in P. lineatus (forearm > 45 mm, < 46 mm in P. recifinus); lower incisors bilobed in P. lineatus, trilobed or flat in P. recifinus (
In Brazil, the species is recorded in all biomes, in the states of Tocantins, Piauí, Paraíba, Pernambuco, Alagoas, Sergipe, Bahia, Goiás, Mato Grosso, Mato Grosso do Sul, Minas Gerais, Espírito Santo, Rio de Janeiro, São Paulo, Paraná, Santa Catarina and Rio Grande do Sul (
In March we captured one adult female in a mist-net elevated 8 m over a wide stream in sampling site M24 (Appendix
The diagnosis of P. recifinus is discussed above. The specimen from PECB (ZSP 055; see Table
In Brazil, the species is recorded in the Atlantic Forest, Cerrado and Caatinga, in the states of Alagoas, Bahia, Espírito Santo, Minas Gerais, Paraíba, Paraná, Pernambuco, Rio de Janeiro, and São Paulo (
In September we captured one adult male in a mist-net set at ground-level on a wide trail in sampling site M22 (Appendix
Pygoderma Peters, 1863 is a monotypic genus represented by P. bilabiatum (Wagner, 1843) (
In Brazil the species is recorded in the Atlantic Forest, Caatinga, Cerrado and Pantanal biomes, in the states of Alagoas, Bahia, Espírito Santo, Minas Gerais, Mato Grosso do Sul, Paraíba, Pernambuco, Paraná, Rio de Janeiro, Rio Grande do Sul, Santa Catarina, and São Paulo (
The three individuals (2 males and 1 female) were captured in May and June, in mist-nets set at ground-level on dirt roads, in sampling sites M31 and M34 (Appendix
Sturnira Gray, 1842 is represented in Brazil by S. giannae Velazco & Patterson, 2019, S. lilium (É. Geoffroy, 1810), S. magna de la Torre, 1966 and S. tildae de la Torre, 1959 (
In Brazil, the species is recorded in all biomes except the Amazon, in South, Southeastern, and part of the Northeastern and Center-West regions (
We captured 31 individuals, of which 27 (14 males and 13 females) were taken in mist-nets set at ground-level in sampling sites, M2, M13, M17, M20, M22, M23, M26, M29, M31, M32, M34, M35, M37 and M39, and four males in mist-nets elevated 8 m, in sampling sites M1, M31 and M32 (Appendix
The distinction between S. tildae and most congeners is discussed above. Sturnira tildae can be distinguished from S. giannae by the color pattern of the dorsal fur (tetracolored in S. tildae and bicolored in S. giannae); the length of the dorsal fur (> 8 mm in S. tildae and 4–6 mm in S. giannae); and the length of metacarpals III and IV (Met III < IV in S. tildae and Met III = IV in S. giannae –
In Brazil, the species is recorded in Amazonia, Atlantic Forest, Cerrado and Caatinga, on the states of Amazonas, Acre, Rondônia, Pará, Amapá, Roraima, Tocantins, Sergipe, Mato Grosso, Mato Grosso do Sul, Bahia, Minas Gerais, Espírito Santo, Rio de Janeiro, São Paulo, Paraná, and Santa Catarina (
The five (2 males and 3 females) individuals were captured in mist-nets set at ground-level in sampling sites M5, M16, M22, M28 and M35 (Appendix
In Brazil, Vampyressa Thomas, 1900 is currently represented by V. pusilla (Wagner, 1843) and V. thyone Thomas, 1909 (
In Brazil, the species is recorded in the Atlantic Forest, Cerrado and Pantanal biomes, in the states of Goiás, Mato Grosso do Sul, Bahia, Alagoas, Minas Gerais, Espírito Santo, Rio de Janeiro, São Paulo, Paraná, Santa Catarina and Rio Grande do Sul (
In September we captured an adult male in a mist-net set at ground-level on a wide trail in sampling site M21 (Appendix
Five species of Cynomops Thomas, 1920 are registered in Brazil: C. abrasus (Temminck, 1826), C. greenhalli Goodwin, 1958, C. milleri (Osgood, 1914), C. mastivus (Thomas, 1911) and C. planirostris (Peters, 1866) (
In Brazil, the species is recorded in all biomes, except Pampas, in the states of Goiás, Maranhão, Minas Gerais, Mato Grosso do Sul, Mato Grosso, Pará, Paraíba, Piauí, Rio de Janeiro, Santa Catarina, and São Paulo (
In December we captured an adult male in a roosting site on a building roof in sampling site S7 (Appendix
Selected measurements (mm) and weigth (g) for specimens of Molossinae from PECB, São Paulo state, Brazil. See Material and Methods for description of measurements.
Measurement | Molossinae | ||||||||||||||
Cynomops abrasus | Molossus currentium | Molossus molossus | Molossops neglectus | Molossus rufus | |||||||||||
ZSP 021 ♂ | ZSP 050 ♂ | 6 ♂ (South America) | ZSP 003 ♀ | ZSP 018 ♂ | ZSP 020 ♀ | ZSP 053 ♀ | ZSP 016 ♀ | ZSP 019 ♂ | ZSP 026 ♂ | ZSP 059 ♂ | |||||
W | 30.0 | 22.5 | – | 15.5 | 19.0 | 21.0 | 14.5 | 11.5 | 42.0 | 21.0 | 35.5 | ||||
BL | 73.88 | 64.36 | – | 60.36 | 67.68 | 60.33 | 55.05 | 54.37 | 86.08 | 73.33 | 75.65 | ||||
FA | 45.50 | 40.43 | 41.25 | 39.17 | 38.94 | 39.50 | 38.88 | 36.73 | 51.11 | 50.32 | 51.20 | ||||
TL | 14.70 | 15.20 | – | 14.62 | 13.69 | 14.63 | 12.68 | 11.77 | 19.48 | 21.22 | 19.79 | ||||
EL | 16.64 | 9.57 | – | 11.76 | 12.11 | 12.23 | 11.13 | 11.40 | 13.49 | 13.29 | 15.07 | ||||
TRL | 4.66 | 4.50 | – | 3.66 | 3.85 | 4.93 | 3.79 | 1.83 | 4.40 | 2.97 | 3.60 | ||||
GLS | 21.58 | 18.92 | 18.89 | 17.46 | 18.26 | 17.99 | 17.34 | 15.57 | 23.97 | 21.82 | 22.92 | ||||
CI | 20.85 | 16.74 | 18.27 | 16.38 | 16.59 | 16.01 | 15.92 | 15.03 | 21.20 | 20.11 | 20.71 | ||||
BB | 10.50 | 9.82 | 9.64 | 8.99 | 9.11 | 9.53 | 9.16 | 8.14 | 11.32 | 11.53 | 10.93 | ||||
ZB | 15.02 | 11.85 | 11.85 | 11.07 | 10.77 | 11.22 | 10.74 | 10.04 | 14.19 | 13.27 | 14.15 | ||||
PB | 5.32 | 4.29 | 3.92 | 4.03 | 4.15 | 3.95 | 4.10 | 4.79 | 4.69 | 4.81 | 4.50 | ||||
CC | 5.62 | 5.01 | 5.04 | 4.46 | 4.70 | 4.62 | 4.23 | 4.27 | 6.26 | 6.04 | 6.53 | ||||
MB | 11.62 | 10.55 | – | 9.87 | 9.24 | 9.95 | 9.78 | 8.33 | 12.27 | 12.14 | 12.05 | ||||
PL | 9.32 | 6.95 | – | 6.70 | 6.82 | 6.68 | 6.63 | 7.32 | 8.48 | 8.33 | 8.52 | ||||
MXTL | 7.67 | 6.32 | 6.78 | 6.30 | 6.22 | 6.30 | 6.06 | 6.06 | 8.25 | 8.08 | 8.34 | ||||
MLTL | 6.21 | 4.97 | – | 4.93 | 4.82 | 4.98 | 4.97 | 4.86 | 6.60 | 6.44 | 6.51 | ||||
DL | 16.00 | 12.85 | – | 12.12 | 12.60 | 12.36 | 12.32 | 11.13 | 16.40 | 15.48 | 16.57 | ||||
MNTL | 9.15 | 7.39 | – | 7.38 | 7.05 | 7.15 | 6.90 | 7.09 | 9.41 | 9.33 | 9.54 | ||||
CH | 4.85 | 3.92 | – | 3.88 | 3.63 | 4.00 | 3.74 | 3.76 | 5.13 | 4.81 | 4.96 |
Both species of Molossops Peters, 1866 are found in Brazil: M. neglectus Williams & Genoways, 1980 and M. temminckii (Burmeister, 1854) (
In Brazil, the species is recorded in the Amazon, Atlantic Forest and Cerrado biomes, in Amazonas, Minas Gerais, Pará, Paraná, Rio de Janeiro, Rio Grande do Sul, and São Paulo states (
A pregnant female was captured in November in a mist-net elevated 8 m over a trail in sampling site M7 (Appendix
Molossus É. Geoffroy, 1805 is represented in Brazil by six species: M. aztecus Saussure, 1860, M. coibensis J.A. Allen, 1904, M. currentium Thomas, 1901, M. molossus (Pallas, 1766), M. pretiosus Miller, 1902, and M. rufus É. Geoffroy, 1805 (
Molossus currentium and M. molossus can be distinguished by the larger size in M. currentium, with forearm averaging 41.3 mm in males and 41.9 mm in females; and in M. molossus averaging 40.2 mm in males and 39.5 mm in females (
In Brazil, the species is recorded only in the Pantanal biome in Mato Grosso state (
In June we captured an adult male in a roosting site on a building roof, in sampling site S9 (Appendix
The distinction between M. molossus and other congeners is discussed above. Specimens from PECB identified as M. molossus (ZSP 003, 018, 020, 053; see Table
In Brazil, the species is recorded in all biomes and in all states, except Rio Grande do Norte (
We captured 28 individuals (4 males and 24 females) in roosting sites on building roofs in sampling sites S2 and S7 (Appendix
The distinction between M. rufus and M. pretiosus from other Brazilian congeners is discussed above. Molossus rufus is larger than M. pretiosus (forearm ranging from 46.7 to 55.2 mm in M. rufus and from 44.6 to 49.0 mm in M. pretiosus); the shape of the upper incisors (long and slightly convergent in M. pretiosus, short, spatulated and in contact in M. rufus); general fur coloration (dark brown in M. pretiosus and dark or reddish brown in M. rufus) and face and membranes coloration (not black, slightly paler, in M. pretiosus and black in M. rufus) (
In Brazil, the species is recorded in all biomes, except Pampas, on the states of Alagoas, Amazonas, Amapá, Bahia, Ceará, Espírito Santo, Maranhão, Minas Gerais, Mato Grosso do Sul, Mato Grosso, Pará, Paraíba, Pernambuco, Piauí, Paraná, Rio de Janeiro, Roraima, Rio Grande do Sul, Santa Catarina, and São Paulo (
We captured 3 adult males in roosting sites on building roofs in sampling sites S7 and S17 (Appendix
Six species of Eptesicus Rafinesque, 1820 occur in Brazil: E. andinus J.A. Allen, 1914, E. brasiliensis (Desmarest, 1819), E. chiriquinus Thomas, 1920, E. diminutus Osgood, 1915, E. furinalis (d'Orbigny and Gervais, 1847) and E. taddeii Miranda, Bernardi & Passos, 2006 (
In Brazil, the species is only known from the Atlantic Forest, on the states of São Paulo, Paraná, Santa Catarina, and Rio Grande do Sul (
Two adult females were taken on mist-nets set at ground-level in sampling sites M20 and M34, and one was taken on a mist-net elevated 8 m over a trail, in sampling site M7 (Appendix
Locality records of Molossus currentium in Brazil. The map numbers correspond to the records as indicated in Fig.
Map | Locality | Coordinates | Author |
1 | Corumbá, Mato Groso | 19°00.19'S, 57°23.48'W |
|
2 | Carlos Botelho State Park, São Paulo | 24°11.00'S, 47°55.00'W | This study |
Selected measurements (mm) and weigth (g) for specimens of Vespertilioninae and Myotinae from PECB, São Paulo state, Brazil. See Material and Methods for description of measurements.
Measurement | Vespertilioninae | Myotinae | ||||||||||||||||
Eptesicus taddeii | Histiotus velatus | Lasiurus ebenus | Myotis albescens | Myotis nigricans | Myotis riparius | Myotis ruber | ||||||||||||
ZSP 017 ♂ | ZSP 048 ♀ | ZSP 004 ♂ | ZSP 046 ♀ | ZSP 030 ♂ | ZSP 005 ♀ | ZSP 010 ♂ | ZSP 051 ♂ | ZSP 007 ♀ | ZSP 052 ♂ | ZSP 047 ♂ | ZSP 054 ♂ | |||||||
W | 12.0 | 12.0 | 13.0 | 11.0 | 12.5 | 9.0 | 5.0 | 4.5 | 5.0 | 5.0 | 7.5 | 7.0 | ||||||
BL | 61.43 | 56.47 | 62.02 | 58.92 | 62.13 | 54.09 | 41.77 | 42.30 | 43.42 | 41.89 | 49.87 | 48.26 | ||||||
FA | 47.33 | 47.15 | 45.80 | 47.42 | 45.67 | 37.15 | 34.07 | 33.74 | 33.46 | 34.39 | 41.23 | 39.32 | ||||||
TL | 20.48 | 19.62 | 20.24 | 20.03 | 21.42 | 16.71 | 15.42 | 14.83 | 14.43 | 14.67 | 17.10 | 16.70 | ||||||
EL | 16.34 | 10.35 | 26.11 | 27.31 | 15.32 | 11.62 | 12.38 | 11.90 | 11.17 | 13.68 | 14.25 | 16.34 | ||||||
TRL | 6.80 | 7.87 | 12.12 | 12.92 | 7.53 | 6.52 | 5.37 | 6.56 | 6.52 | 6.58 | 8.26 | 9.11 | ||||||
GLS | 17.86 | 17.90 | 18.43 | 18.12 | 13.9 | 14.50 | 13.34 | 13.67 | 13.42 | 13.47 | 15.63 | 15.14 | ||||||
CI | 16.86 | 16.87 | 17.19 | 16.80 | 13.93 | 13.61 | 12.56 | 12.99 | 12.72 | 12.67 | 14.93 | 14.37 | ||||||
BB | 8.29 | 8.29 | 8.20 | 8.04 | 8.28 | 7.05 | 6.62 | 6.27 | 6.67 | 6.96 | 7.19 | 6.85 | ||||||
ZB | 11.79 | 11.98 | 10.18 | 10.15 | 9.91 | 8.50 | 7.80 | 7.98 | 8.17 | 8.50 | 9.54 | 9.44 | ||||||
PB | 4.15 | 4.20 | 4.18 | 3.97 | 4.64 | 3.89 | 3.55 | 3.46 | 3.42 | 3.67 | 3.76 | 3.84 | ||||||
CC | 5.46 | 5.45 | 5.06 | 4.84 | 5.52 | 3.66 | 3.23 | 3.29 | 3.59 | 3.63 | 4.16 | 4.35 | ||||||
MB | 8.72 | 9.06 | 8.37 | 8.30 | 8.38 | 7.08 | 6.54 | 6.53 | 6.69 | 6.90 | 7.59 | 7.35 | ||||||
PL | 9.30 | 9.11 | 9.11 | 9.21 | 6.38 | 6.86 | 6.83 | 7.00 | 7.07 | 7.16 | 8.07 | 7.98 | ||||||
MXTL | 6.80 | 6.76 | 6.08 | 5.98 | 4.70 | 5.07 | 4.92 | 4.94 | 5.06 | 5.04 | 6.17 | 5.85 | ||||||
MLTL | 5.19 | 5.39 | 5.00 | 4.76 | 3.70 | 4.15 | 4.07 | 4.04 | 4.42 | 4.15 | 5.25 | 4.85 | ||||||
DL | 13.34 | 13.61 | 12.71 | 12.64 | 9.58 | 8.95 | 9.46 | 9.49 | 9.88 | 9.90 | 12.19 | 11.43 | ||||||
MANTL | 8.31 | 8.29 | 6.58 | 7.47 | 5.53 | 6.60 | 6.38 | 6.31 | 6.55 | 6.32 | 7.90 | 7.47 | ||||||
CH | 4.64 | 4.81 | 3.94 | 4.34 | 3.28 | 1.93 | 2.78 | 2.70 | 2.79 | 2.90 | 3.48 | 3.58 |
Bat species captured in Carlos Botelho State Park, São Paulo state, Brazil: (32) Molossus currentium; (33) Molossus molossus; (34) Molossus rufus; (35) Eptesicus taddeii; (36) Lasiurus ebenus; (37) Histiotus velatus; (38) Myotis albescens; (39) Myotis nigricans; (40) Myotis riparius; (41) Myotis ruber.
According to
Our specimen represents the second record of L. ebenus since its description (see
The adult male was captured in February in a ground-level mist-net set over a small stream in sampling site M20 (Appendix
In Brazil, Histiotus Gervais, 1856 is represented by H. alienus Thomas, 1916, H. diaphanopterus Feijó, Rocha & Althoff, 2015, H. laephotis Thomas, 1916, H. montanus (Philippi & Landbeck, 1861), and H. velatus (I. Geoffroy, 1824) (
In Brazil, the species occurs in the Atlantic Forest, Cerrado, Pantanal and Pampas biomes, in Mato Grosso, Goiás, Minas Gerais, Espírito Santo, Rio de Janeiro, São Paulo, Paraná, Santa Catarina, and Rio Grande do Sul states (
All the 13 specimens (1 male and 12 females) captured were taken in building roofs in sampling site S2 (Appendix
In Brazil, Myotis Kaup, 1829 is represented by M. albescens (É. Geoffroy, 1806), M. izecksohni Moratelli et al., 2011, M. lavali Moratelli et al., 2011, M. levis (I. Geoffroy, 1824), M. nigricans (Schinz, 1821), M. riparius Handley, 1960, M. ruber (É. Geoffroy, 1806) and M. simus Thomas, 1901 (
In Brazil, the species is recorded in the Amazon, Atlantic Forest, Caatinga, and Pantanal, occurring in the states of Acre, Amazonas, Amapá, Bahia, Minas Gerais, Mato Grosso do Sul, Pará, Paraná, Rio de Janeiro, Rondônia, Roraima, Rio Grande do Sul, and São Paulo (
In October, we captured two pregnant females in a building roof, in sampling site S2 (Appendix
Myotis nigricans and M. riparius can be distinguished from M. lavali, which is similar in size, by the unicolored or weakly bicolored dorsal fur (strongly bicolored in M. lavali;
In Brazil, the species apparenlty occurs in all the biomes, with records for the states of Amazonas, Amapá, Bahia, Ceará, Pará, Piauí, Paraíba, Pernambuco, Rio Grande do Norte, Roraima, Sergipe, Tocantins, Mato Grosso, Mato Grosso do Sul, Goiás, Paraná, Rio Grande do Sul, Santa Catarina, Minas Gerais, São Paulo, Rio de Janeiro, and Espírito Santo (
We captured 21 individuals, of which 20 (13 males and 7 females) were taken on ground-level mist-nets, in different sampling sites and elevations: M3, M4, M11, M17, M20, M21, M27, M29, M37 and M39. One adult male was captured in abandoned roof tiles, in sampling site S12 (Appendix
The distinction of M. riparius from M. simus, M. levis, M. albescens, M. ruber, M. lavali and M. nigricans is discussed above. Myotis riparius can be distinguished from M. izecksohni by the wooly and shorter dorsal fur (ca 5 mm), which is silky and long (7.8–8.5 mm) in M. izecksohni (
In Brazil, the species is recorded in all biomes in the states of Acre, Amazonas, Amapá, Bahia, Minas Gerais, Pará, Paraná, Rio de Janeiro, Rio Grande do Sul, Santa Catarina, São Paulo, and Tocantins (
One adult male and one adult female were captured in ground-level mist-nets set at wide trails, on sampling sites M2 and M39 (Appendix
Myotis ruber can be distinguished from their congeners by the general fur coloration, which is bright cinnamon red on the dorsum and yellowish on venter, and higher sagittal and lambdoidal crests. Myotis simus and M. riparius can present similar coloration, but the attachment of wing membranes on feet and the fur length readily distinguish M. ruber from M. simus; and the larger forearm length and higher sagittal crests distinguish M. ruber from M. riparius (
In Brazil, the species is recorded in the Atlantic Forest and Cerrado, on the states of Bahia, Pernambuco, Minas Gerais, Paraná, Rio Grande do Sul, Santa Catarina, São Paulo, Rio de Janeiro, and Espírito Santo (
We captured two adult males, both in secondary dense forest. One was taken in a ground-level mist-net set along a river in sampling site M29, and another was taken in a building roof, in sampling site S2 (Appendix
We are thankful to the staff of Parque Estadual Carlos Botelho for the logistical support. VCC and GPB had received MSc scholarships from Programa de Pós-Graduação em Conservação da Fauna and Fundação Parque Zoológico de São Paulo. RM has received support from CNPq, Fundação de Apoio a Pesquisa do Estado do Rio de Janeiro – FAPERJ, and the Smithsonian Institution. This study was financed in part by the Coordenação de Aperfeiçoamento de Pessoal de Nível Superior – Brazil (CAPES) – Finance Code 001.
Information on bats sampling sites selected on Carlos Botelho State Park, São Paulo state, Brazil. The mist-net (M) and search for roost (S) codes correspond to the sampling sites as indicated in Fig.
Map | Plant physiognomy | Coordinates | Altitude (m) |
---|---|---|---|
M1 | Dense Secondary Forest | 24°03'29"S, 47°59'37"W | 789 |
M2 | Dense Secondary Forest | 24°03'26"S, 47°58'09"W | 819 |
M3 | Submontane Dense Ombrophilous Forest | 24°11'45"S, 47°55'24"W | 89 |
M4 | Submontane Dense Ombrophilous Forest | 24°12'05"S, 47°55'59"W | 50 |
M5 | Submontane Dense Ombrophilous Forest | 24°11'46"S, 47°55'34"W | 75 |
M6 | Submontane Dense Ombrophilous Forest | 24°12'05"S, 47°56'09"W | 46 |
M7 | Montane Dense Ombrophilous Forest | 24°03'52"S, 47°59'16"W | 800 |
M8 | Montane Dense Ombrophilous Forest | 24°03'38"S, 47°58'47"W | 783 |
M9 | Open Secondary Forest | 24°04'15"S, 47°59'12"W | 727 |
M10 | Montane Open Ombrophilous Forest | 24°08'16"S, 48°00'02"W | 821 |
M11 | Submontane Dense Ombrophilous Forest | 24°11'38"S, 47°55'13"W | 96 |
M12 | Submontane Dense Ombrophilous Forest | 24°11'47"S, 47°55'42"W | 69 |
M13 | Submontane Dense Ombrophilous Forest | 24°11'43"S, 47°55'25"W | 106 |
M14 | Montane Dense Ombrophilous Forest | 24°06'16"S, 47°58'57"W | 761 |
M15 | Dense Secondary Forest | 24°03'42"S, 47°58'32"W | 824 |
M16 | Submontane Dense Ombrophilous Forest | 24°12'04"S, 47°55'57"W | 51 |
M17 | Montane Dense Ombrophilous Forest | 24°04'56"S, 47°57'04"W | 836 |
M18 | Submontane Dense Ombrophilous Forest | 24°12'22"S, 47°57'00"W | 52 |
M19 | Dense Secondary Forest | 24°03'40"S, 47°59'18"W | 775 |
M20 | Montane Open Ombrophilous Forest | 24°10'23"S, 47°59'06"W | 648 |
M21 | Open Secondary Forest | 24°12'10"S, 47°56'26"W | 45 |
M22 | Submontane Dense Ombrophilous Forest | 24°11'45"S, 47°55'28"W | 82 |
M23 | Submontane Dense Ombrophilous Forest | 24°12'07"S, 47°57'04"W | 74 |
M24 | Submontane Dense Ombrophilous Forest | 24°12'15"S, 47°57'02"W | 60 |
M25 | Submontane Dense Ombrophilous Forest | 24°12'21"S, 47°57'09"W | 55 |
M26 | Montane Dense Ombrophilous Forest | 24°06'29"S, 47°59'07"W | 750 |
M27 | Submontane Dense Ombrophilous Forest | 24°11'52"S, 47°55'47"W | 65 |
M28 | Submontane Dense Ombrophilous Forest | 24°12'04"S, 47°55'57"W | 51 |
M29 | Dense Secondary Forest | 24°03'53"S, 47°59'59"W | 709 |
M30 | Dense Secondary Forest | 24°03'37"S, 47°59'34"W | 813 |
M31 | Montane Dense Ombrophilous Forest | 24°03'55"S, 47°57'13"W | 810 |
M32 | Montane Dense Ombrophilous Forest | 24°06'17"S, 47°58'49"W | 752 |
M33 | Dense Secondary Forest | 24°04'00"S, 47°59'44"W | 739 |
M34 | Montane Dense Ombrophilous Forest | 24°04'06"S, 47°58'08"W | 848 |
M35 | Submontane Dense Ombrophilous Forest | 24°11'06"S, 47°56'01"W | 225 |
M36 | Montane Dense Ombrophilous Forest | 24°03'32"S, 47°56'29"W | 787 |
M37 | Submontane Dense Ombrophilous Forest | 24°11'41"S, 47°55'18"W | 92 |
M38 | Submontane Dense Ombrophilous Forest | 24°11'43"S, 47°55'03"W | 170 |
M39 | Montane Dense Ombrophilous Forest | 24°03'48"S, 47°59'15"W | 806 |
S1 | Montane Dense Ombrophilous Forest | 24°10'13"S, 47°58'13"W | 580 |
S2 | Dense Secondary Forest | 24°03'25"S, 47°59'38"W | 786 |
S3 | Submontane Dense Ombrophilous Forest | 24°11'44"S, 47°55'34"W | 77 |
S4 | Submontane Dense Ombrophilous Forest | 24°12'05"S, 47°56'10"W | 46 |
S5 | Montane Dense Ombrophilous Forest | 24°03'52"S, 47°59'16"W | 800 |
S6 | Montane Dense Ombrophilous Forest | 24°03'50"S, 47°59'10"W | 774 |
S7 | Submontane Dense Ombrophilous Forest | 24°11'37"S, 47°55'13"W | 96 |
S8 | Submontane Dense Ombrophilous Forest | 24°11'52"S, 47°57'13"W | 120 |
S9 | Submontane Dense Ombrophilous Forest | 24°11'35"S, 47°55'12"W | 99 |
S10 | Dense Secondary Forest | 24°03'40"S, 47°59'18"W | 775 |
S11 | Open Secondary Forest | 24°04'39"S, 47°58'38"W | 741 |
S12 | Submontane Dense Ombrophilous Forest | 24°12'04"S, 47°55'57"W | 51 |
S13 | Dense Secondary Forest | 24°03'57"S, 47°59'31"W | 781 |
S14 | Submontane Dense Ombrophilous Forest | 24°12'38"S, 47°58'02"W | 110 |
S15 | Dense Secondary Forest | 24°03'37"S, 47°59'34"W | 813 |
S16 | Montane Dense Ombrophilous Forest | 24°03'51"S, 47°58'37"W | 813 |
S17 | Dense Secondary Forest | 24°03'22"S, 47°59'36"W | 788 |