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Chiroptera Neotropical 19(1): 1163-1178, July 2013 Updated compilation of bat species (Chiroptera) for the Brazilian state of Sergipe, including new records Edson Silva Barbosa Leal 1,2*, Severino Mendes de Azevêdo Júnior 2, Fátima Verônica Pereira Vila Nova3, Deoclécio de Queiroz Guerra 4, Wallace Rodrigues Telino-Júnior 2,5 1 Associação Instituto de Tecnologia de Pernambuco – ITEP/OS, Unidade Gestora de Projetos Barragens da Mata Sul (UGP Barragens), Laboratório de Ecologia e Biodiversidade (LEcoBio). Av. Prof. Luiz Freire, 700 - Cidade Universitária, Bloco B, Sala 109. CEP: 50740-540. Recife, Pernambuco, Brasil. 2 Programa de Pós-Graduação em Ecologia, Universidade Federal Rural de Pernambuco, Recife, Pernambuco, Brasil. 3 Programa de Pós Graduação em Geografia, Universidade Federal de Pernambuco, Centro de Filosofia e Ciências Humanas, Departamento de Ciências Geográficas, Recife, Pernambuco, Brasil. 4 Departamento de Zoologia, Centro de Ciências Biológicas, Universidade Federal de Pernambuco, Recife, Pernambuco, Brasil. 5 Unidade Acadêmica de Garanhuns, Universidade Federal Rural de Pernambuco, Garanhuns, Pernambuco, Brasil. *Corresponding author: [email protected] ARTICLE Manuscript history: Submmited in 16/Mar/2012 Accept in 04/Jan/2013 Available on line in 16/Jul/2013 Section editor: Ludmilla M.S. Aguiar Abstract This article is a summary study of the existing knowledge related to the occurrence and distribution of bat species in Sergipe, Northeastern Brazil, and includes new records of Peropteryx macrotis (Wagner, 1843) and the first record of Diphylla ecaudata Spix, 1823 for this state. The specimens were captured in groundlevel through the use of mist-nets on the Fazenda Mundo Novo (9º 38’31” Lat S, 37º 47’ 18” Long W) under the municipality of Canindé do São Francisco. The morphology of the specimens was compared with previous descriptions of the respective species available in the scientific literature. A total of 43 bat species belonging to 31 genera and eight families (Phyllostomidae = 29 species; Emballonuridae = 3; Molossidae = 3; Noctilionidae = 2; Vespertilionidae = 2; Mormoopidae = 2; Furipteridae = 1; Natalidae = 1) are now known as occurring in Sergipe. Among them, 20 species are found in the Caatinga (10 endemic), and 32 in the Atlantic Forest (20 endemics). The registered richness represents 24.4% of the bat fauna recorded in Brazil. Despite the relatively small size of the Sergipe state (approximately 22,000 km²), much of its area remains unsurveyed, and further studies are clearly necessary in order to define the true diversity of its chiropteran fauna. In particular, the subterranean ecosystems demand special attention due to not only the paucity of data available for these environments, but also the considerable anthropogenic pressures they suffer, facts that may threaten the existence of these unique habitats and the bats that depend on them. Keywords: Atlantic Rainforest, Bats, Caatinga, Check List, Distribution, Sergipe, Northeastern Brazil ! Introduction The order Chiroptera Blumenbach, 1779 includes all bats, the only mammals capable of real flight skills, and currently includes more than 1,100 species belonging to nearly 200 genera in 18 families (Simmons 2005). Bats have a cosmopolitan distribution, and are only absent ! ! ! from polar latitudes and some isolated oceanic islands (Kunz & Pierson 1994). The Order Chiroptera is the second most diverse mammalian order after Order Rodentia, making up one quarter of the recognized mammalian species (as against 40% for rodents), and bats are also among the most abundant mammals at most existing sites (Wilson & Reeder 2005). 1163 Chiroptera Neotropical 19(1): 1163-1178, July 2013 Considering the morphological and paleontological data, chiropterans have traditionally been divided into two suborders, Megachiroptera and Microchiroptera Dobson, 1875, which also reflects the predominant sensory mechanism (vision in Megachiroptera and echolocation in Microchiroptera). More recently, however, molecular analyses have revealed that the Microchiroptera is a paraphyletic group (Peracchi et al. 2006; 2011). Based on this, Peracchi et al. (2011) proposed a new arrangement, dividing the order into two suborders, the Yinpterochiroptera, which encompasses the families Pteropodidae (including the largest bats, known as “flying foxes”), Rhinolophidae, Hipposidaridae, Rhinopomatidae, Craseonysteridae, and Megadermatidae, and the Yangochiroptera, which includes all the remaining families. All the bats are found in South America are members of the latter suborder. A total of 176 species, representing 24.9% of the 701 mammalian known species that occur in Brazil, are chiropterans (Paglia et al. 2012). However, despite the known diversity of Brazilian yangochiropterans, which includes 69 genera distributed in nine families (Peracchi et al. 2011; Moratelli et al. 2011; Castro et al. 2012; Nogueira et al. 2012; Paglia et al. 2012), species richness has tended to increase over time, through the reevaluation of existing taxonomic arrangements, which are poorly defined, on the role (Peracchi et al. 2006). Through a wide review of chiropterian research in Brazil, Bernard et al. (2010) pointed out that data of the occurrence and distribution of Brazilian bats were highly heterogeneous and fragmented, and minimally, well sampled regions represent less than 10% of the country. Furthermore, not a single record is available for approximately 60% of the whole Brazilian area. Given these substantial gaps, there is an urgent need for surveys of the chiropteran fauna of northern and central Brazil (Reis et al. 2006), and in particular the northeastern region of the country (Pacheco et al. 2008). New records of bat species from poorly sampled regions are essential for the definition of geographical ranges, especially the dispersal capacity of these animals (Reis et al. 2006). A number of recent studies in the Northeastern Brazil have provided new insights into the distribution of the number of bat species (Sbragia & Pêssoa 2008; Silva & Marinho-Filho 2010; Silva et al. 2011). The total diversity of the chiropteran fauna of Brazil seems to be in a continuous growth, as well as the presence of species in neighboring countries that almost certainly also occur in Brazil (Bernard et al. 2011), and the many new species that are ! ! ! being described (Tavares et al. 2008; Pacheco et al. 2010; Taddei & Limm 2010; Moratelli et al. 2011; Nogueira et al. 2012) or validated (Vivo et al. 2011) based on the application of molecular techniques, which have revealed a number of complex cryptic species complexes in recent years (Reis et al. 2006; Tejedor et al. 2005; Tejedor 2006; Moratelli et al. 2011). The sampling lacunas observed in the case of the chiropterans are a typical research fact of Brazilian mammals in general (Costa et al. 2005), and few localities have been surveyed adequately. The vast majority of researchers that study bats are located in southeastern Brazil, where there is a general tendency to explore existing localities, rather than new areas (Pacheco et al. 2008), resulting in skewed and incomplete inventories for all Brazilian biomes (Bernard et al. 2010). The smallest Brazilian state, Sergipe, englobes almost equal portions two biomes: Caatinga (49%) and Atlantic Forest (51%) (IBGE 2011). As reported in other regions, the full diversity and distribution of the state’s chiropteran fauna has yet to be evaluated adequately. Additionally to the systematic analysis of zoogeographic patterns, reliable data on species distributions are necessary and essential for the development of effective strategies of conservation and management (Costa et al. 2005). In Sergipe, bats have been studied in a dozen different municipalities – Canindé do São Francisco (Astúa & Guerra 2008; Leal et al. in press), Poço Redondo (Rocha 2010; Rocha et al. 2011b), Riachuelo (Alencar et al. 1994; Rocha et al. 2011a), Rosário do Catete (Alencar et al. 1994), Brejo Grande (Miretzki 2005), Cristianápolis (Hoffmann & Baker 2003), Santo Amaro das Brotas (Feijó & Nunes 2010), Itabaiana (Mikalauskas 2005; Mikalaukas et al. 2006a; 2006b; Gouveia et al. 2009; Rocha et al. 2011a), Propriá (Miretzki 2005), Capela (Mikalaukas et al. 2011; Brito & Bocchiglieri 2012), as well as areas located between Aracajú and São Cristóvão (Rocha et al. 2010) and Areia Branca and Itabaiana (Mikalauskas 2005; Mikalauskas et al. 2006a). While both Rocha et al. (2010) and Mikalauskas et al. (2011) have provided estimates of the chiropteran diversity of Sergipe (27 and 30 species, respectively), neither study provides a comprehensive list of species or localities, nor an analysis of sampling effort in relation to the two principal biomes found in the state. Considering these appointments, and the fact that both the biomes present in Sergipe are suffering widespread and ongoing degradation, the collection of more reliable data on the zoogeography and conservation status of the local chiropteran fauna is increasingly important. The 1164 Chiroptera Neotropical 19(1): 1163-1178, July 2013 Caatinga is considered as one of the three major natural regions of Brazil, along with the Pantanal and the Amazon (Gregorin et al. 2008), one of only 37 with such characteristics worldwide (Conservation International 2003). Similarly, the Atlantic Forest is considered as being one of the planet’s 25 highly endangered biodiversity hotspots, regions of high diversity, with at least 1500 endemic plant species, which have already lost at least three-quarters of their original vegetation cover (Myers et al. 2000). The present study provides an update on the diversity of bats found in the Brazilian state of Sergipe, focusing on species richness at municipality and biome levels. The study also presents the first record of Diphylla ecaudata Spix, 1823 for the state, and a new locality for Peropteryx macrotis (Wagner, 1843). Specimens of both species were captured in an area of Caatinga. Materials and Methods Specimens of D. ecaudata (UAG/UFRPE 0002) and P. macrotis (UAG/UFRPE 0001), both captured on the Fazenda Mundo Novo (9º38’31” S, 37º47’18” W), were examined during a survey of the mammalian fauna of the Xingó hydroelectric power station in June, 2007 (during the dry season). This site is located in the extreme northern part of the Brazilian state of Sergipe, in the municipality of Canindé do São Francisco, within an area of shrubby hyperxerophilous caatinga vegetation, which forms part of the ecoregion known as the Southern Sertaneja Depression (Velloso et al. 2002). The climate is hot and semi-arid, corresponding to the Bsh type on the Köppen classification system (Ab’Saber 1977), with temperatures ranging between 21ºC and 27ºC, and a rainy season between October and April (Velloso et al. 2002). All the specimens reported here were collected in mist-nests set at ground level, with a maximum height of 3 m. Specimens were fixed in 10% formalin and preserved in 70% ethanol. The collection of zoological specimens was authorized by SISBIO/ICMBio through special license no. 11597, and all the material was deposited in the Zoological Collection of the Garanhuns campus of the Federal Rural University of Pernambuco (UFRPE). Morphometric measurements were taken based on the criteria of Vizotto & Taddei (1973), as follows: body mass (BM), head-body length (BL), length of the tail (TL), length of the ear (EL), length of the foot (FT), length of the forearm (FA), length of the third metacarpus (IIIMe), and the length of the first (P1), second (P2), and third (P3) phalanges. External measurements were taken using a pair of calipers accurate to 0.001 mm, and body mass ! ! ! was measured using a portable spring balance (1 g scale). The distributions of the two species in northeastern Brazil and the municipalities surveyed in Sergipe were plotted on maps of the respective regions. For this, the coordinates of the localities were converted into decimals for processing in the ArcGis program, version 9.3. Results and Discussion The available data on the chiropteran fauna of Sergipe indicate that the original records of Alencar et al. (1994) for the occurrence of the common vampire bat, Desmodus rotundus (E. Geoffroy, 1810), are in the municipalities of Riachuelo and Rosário do Catete (Table 1). After a decade with no new records of bats, Mikalauskas (2005) and Mikalauskas et al. (2006 a, b) reported a total of 15 species for the Serra de Itabaiana National Park (Table 1). At the entrance of Casa de Pedra cave, also in Itabaiana, Gouveia et al. (2009) recorded the opportunistic predation of the mormoopid Pteronotus personatus (Wagner, 1843) and the natalid Natalus macrourus (Gervais, 1856) by two anuran species, Rhinella jimi (Stevaux, 2002) (Anura: Bufonidae) and Leptodactylus vastus Lutz, 1930 (Anura: Leptodactylidae), based on the analysis of stomach contents and direct observation. Feijó & Nunes (2010) encountered specimens of Artibeus planirostris (Spix, 1823) and Trachops cirrhosus (Spix, 1823) in the collection of the Federal University of Paraíba (UFPB), the first records of the species from Sergipe. Rocha et al. (2010) after a survey of bats conducted on the campus of the Federal University of Sergipe (UFS), which recorded a total of 18 species, eight of which no previous records for the Sergipe (Table 1), indicate that there are a total of 27 species registered for this state. However, this study that adds data obtained by Alencar et al. (1994), Mikalauskas (2005) and Feijó & Nunes (2010), did not include a number of species registered in other previous studies, such as Furipterus horrens (F. Cuvier, 1828), Xeronycteris vieirai (Gregorin & Ditchfield 2005) (Ástua & Guerra 2008), N. macrourus, P. personatus, (Gouveia et al. 2009), P. macrotis, Lophostoma brasiliense Peters, 1866, Micronycteris megalotis (Gray, 1842), Micronycteris sanborni Simmons, 1996, and Lichonycteris obscura Thomas, 1895 (Rocha 2010). The addition of these taxa brings the total bat fauna for Sergipe to 35 species. More recently, Rocha et al. (2011a) presented the first records of mormoopid bats for the Brazilian Atlantic Forest, based on the observation of sympatric populations of P. personatus, registered previously by Gouveia et al. (2009), and Pteronotus gymnonotus Natterer, 1843 in two caves in Sergipe. One cave was Casa de Pedra 1165 Chiroptera Neotropical 19(1): 1163-1178, July 2013 (Brazilian Speleological catalog number SE01), in the municipality of Itabaiana, which contained an estimated population of 50,000 individuals of each species. The other site was Urubu Cave (SE10) in Riachuelo. Mikalauskas et al. (2011) and Rocha et al. (2011b) subsequently reported the first record of Rhogueessa hussoni Genoways & Baker, 1996 (Vespertilionidae) and Uroderma magnirostrum Davis, 1968 (Phyllostomidae), respectively, for the state and together with the data from Rocha et al. (2011a), set the total number of chiropteran taxa in Sergipe at 38 species, and not in 30 species as indicated by Mikalaukas et al. (2011). Peracchi et al. (2011) refer to the occurrence of Cynomops greenhalli (Goodwin, 1958) in Sergipe, but do not provide details on the locality or the availability of specimens. During a survey of the bat community of the Mata do Junco Wildlife Refuge in the municipality of Capela, Brito & Bocchiglieri (2012) recorded Trinycteris nicefori (Sanborn, 1949) in Sergipe for the first time, and rectified the identification of a specimen of the genus Tonatia Gray, 1827 captured by Rocha et al. (2007) at the same site, which was identified as Tonatia saurophylla Koopmann & Williams, 1951. In addition, the first record of Lonchorrhina aurita Tomes, 1863 in Sergipe is provided by Leal et al. (in press), based on a survey in Canindé do São Francisco. Given these findings, the data available in Ástua & Guerra (2008), Gouveia et al. (2009), Rocha (2010), Peracchi et al. (2011), and Brito & Bocchiglieri (2012), and the records of D. ecaudata and P. macrotis from Fazenda Mundo Novo in Canindé do São Francisco obtained in the present study provide the basis for the rectification of the most recent inventories published by Rocha et al. (2010) and Mikalauskas et al. (2011), who recorded a total of 27 and 30 species for Sergipe, respectively. The present review elevates the total number of bat species known to occur in the state to 43 (Table 1), distributed in 31 genera and eight families (Phyllostomidae = 29; Emballonuridae = 3; Molossidae = 3; Noctilionidae = 2; Vespertilionidae = 2; Mormoopidae = 2; Furipteridae = 1; Natalidae = 1) (Table 2). Of these species, 20 occur in the Caatinga (10 endemic species) and 32 in the Atlantic Forest, with 20 endemics (Table 1). The specimen of D. ecaudata (collected on 13/X/2007) from Canindé do São Francisco represents the first record of this species for Sergipe (Figure 1), while that of P. macrotis (16/X/2007) reconfirms the occurrence of this species in the state (Figure 2). Neither of the specimens presented signs of reproductive activity, and the epiphyses of the metacarpals and digital phalanges of the wings were ossified. Both specimens were captured after 18:00 h at Fazenda Mundo Novo. ! ! ! Diphylla Spix, 1823 is a monotypic genus of hematophagous bat that belongs to the family Phyllostomidae, subfamily Desmodontinae. The type locality is the São Francisco River in Bahia (Simmons, 2005), but the species can be found throughout Brazil, Colombia, Ecuador, Bolivia, Peru, and Venezuela, as well as Central America, ranging as far north as southern Texas. Two subspecies are recognized (Jones & Carter 1976), with the nominal form, D. e. ecaudata, being distributed throughout South America and as far north as eastern Panama, and the second subspecies, D. e. centralis, being found between western Panama and Texas. However, Koopmann (1994) does not recognize subspecies. In Brazil, D. ecaudata has been recorded in all the southern and southeastern states, as well as the Federal District, Amapá, Amazonas, Acre, Pará, and Rondônia in the north, and Bahia, Pernambuco, Alagoas, Piauí, and Paraíba, in the northeast (Oliveira et al. 2003; Peracchi et al. 2006; Reis et al. 2007; Silva & Nascimento 2008; Tavares et al. 2008; Astúa & Guerra 2008; Bernard & Sampaio 2008). Diphylla is the smallest of the hematophagous bats, but is also the most specialized, feeding exclusively on the blood of birds, which are attacked in the region of the tarsus, feet, and cloaca (Greenhall et al 1984). In Brazil, this genus is the second most common desmodontine captured in field studies (Peracchi et al. 2006). The D. ecaudata specimen captured in this study (♂ UAG/UFRPE 0002, body mass: 28.0g, BL: 64.14 mm, EL: 16.12 mm, FA: 51.17 mm, FT: 14.53mm, IIIMe: 47.57 mm, P1: 10.20 mm, P2: 24.33 mm, P3: 17.97 mm) presented the diagnostic characteristics of the species reported by Greenhall et al. (1984), Fazzolari-Côrrea (1995), and Reis et al. (2007), including large eyes, and small, rounded and forward-facing ears. Rudimentary nasal leaf, with a small, rounded horseshoe over the nostrils. Thumb short with no pads. Forearm, legs, and poorly developed interfemural membrane covered in dense pelage. No tail and short heel with warty outgrowth. In addition to P. macrotis, four other Peropteryx species are known to occur in Brazil – Peropteryx kappleri Peters, 1867, P. leucoptera Peters, 1867, P. trinitatis Miller, 1899, and the recently-described P. pallidoptera Lim, Engstron, Reid, Simmons, Voss & Fleck, 2010 (Reis et al. 2007; Castro et al. 2012). While its type locality is Mato Grosso (Brazil), P. macrotis ranges from southern Mexico, including the Yucatan Peninsula, through Central America to northern South America (Yee 2000), where it is found in Venezuela, Colombia, Ecuador, Trinidad and Tobago, Suriname, French Guiana, Peru, Bolivia, Paraguay, and Brazil (Jones & Hood 1993; 1166 Chiroptera Neotropical 19(1): 1163-1178, July 2013 Simmons 2005; Gardner 2008). In Brazil, the species has been recorded in all the eastern states, as well as the Federal District, Amapá, Pará, and Amazonas, in the north, Paraná, in the south, and Goiás and Mato Grosso in the central-western region (Oliveira et al. 2003; Peracchi et al. 2006; Reis et al. 2007; Silva & Nascimento 2008; Tavares et al. 2008; Astúa & Guerra 2008; Bernard & Sampaio 2008). The species occur in all Brazilian biomes (Marinho-Filho & Sazima 1998), and is common in the Caatinga. The P. macrotis specimen captured at Fazenda Mundo Novo in Canindé do São Francisco (♀ UAG/UFRPE 0001, body mass: 4.0g, BL: 40.52 mm, TL: 12.05 mm, EL: 13.75 mm, FA: 43.13 mm, FT: 7.56 mm, IIIMe: 32.17 mm, P1: 10.59 mm, P2: 16.51 mm) presented the diagnostic characteristics reported by Vizotto & Taddei (1973), Jones & Hood (1993), and Gardner (2007), such as black wings connected to the tibia, separated ears with rounded extremities not connected by an interauricular band, forearm length of 43.5–48.2 mm in the females, no dorsal lines, sparse pelage, dark brown on the dorsal surface and lighter in color ventrally. Small wing sac located close to the lower edge of the antebrachial membrane, which opens distally. The specimen captured during the present study differed from P. trinitatis, a similar species, with which P. macrotis may be confused in the field, by the lateral and occlusal aspects of the morphology of the first upper premolar, which is relatively large and has a distinct posterior cusp, in contrast with the small premolar lacking welldefined cusps in P. trinitatis (Simmos & Voss, 1998). Mikalauskas (2005), Miretzki (2005), Feijó & Nunes (2010), Mikalauskas et al. (2006b, 2011), Rocha (2010), Rocha et al. (2010, 2011a, b), and Brito & Bocchigliere (2012) refer to a small number of collections in which specimens from Sergipe have been deposited, emphasizing the overall lack of data on the chiropteran fauna of the state in general, and certain species, in particular. In the specific case of the specimens of the genus Myotis (Vespertilionidae) collected in Sergipe, it is important to note that the populations from the Brazilian Northeast were recently assigned to a new species – Myotis lavali Moratelli et al. 2011 – which would mean that Myotis nigricans (Schimz, 1821) does not occur in the state. This question obviously requires evaluation. The registered richness represents 24.4% of the bat fauna recorded in the Brazil (Castro et al. 2012; Nogueira et al. 2012; Paglia et al. 2012). Despite the relatively small size of the state of Sergipe (approximately 22,000 km²), much of its area remains unsurveyed (Figure 3), and further studies are clearly needed in order to define the ! ! ! true diversity of its chiropteran fauna. In particular, the subterranean ecosystems demand special attention, given not only the paucity of data available for these environments, but also the considerable anthropogenic pressures they suffer, which threaten the existence of these unique habitats and the bats that depend on them (Dantas et al. 2008). Acknowledgments We are grateful to Mr. Mario F. da Silva, taxidermist of the UFPE Zoology Department, for his valuable assistance in the field. We would also like to thank the Remote Sensing and Geoprocessing Laboratory (SERGEO) and the Biogeography and Environmental Study Group (BIOMA) of the Geographic Sciences Department at UFPE for producing the maps. The PostGraduate Program in Ecology at the Federal Rural University of Pernambuco and Brazilian Higher Education Funding Agency (CAPES) provided the first author with a master scholarship. References Ab'Saber A.N. 1977. Os domínios morfoclimáticos na América do Sul. Primeira aproximação. Geomorfologia 52: 1-22. Alencar. 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Faculdade de Filosofia, Ciências e Letras, São José do Rio Preto. Yee D.A. 2000. Peropteryx macrotis. Mammalian species 643: 1-4. Wilson D.E. & Reeder D.M. 2005. Mammals species of the world: a taxonomic and geographic reference. John Hopkins University Press, Baltimore. ! ! ! ! 1171 Chiroptera Neotropical 19(1): 1163-1178, July 2013 Figure 1. Distribution of the available records of the Hairy-legged Vampire Bat, Dyphylla ecaudata, in northeastern Brazil (● = existing record; ■ = new record): (1) Furna Feia, Baraúna, Rio Grande do Norte (Ferreira et al. 2010); (2) Fazenda Bravo,Cabaceiras, Paraíba (Feijó & Langguth 2011); (3) Onça Cave, Fazenda Santana, João Pessoa, Paraíba (Feijó & Langguth 2011); (4) Saltinho Biological Reserve, Rio Formoso, Pernambuco (Guerra 2007); (5) Charles Darwin Ecological Refuge, Igarassú, Pernambuco (Guerra 2007); (6) Tapacurá Ecological Station, São Lourenço da Mata, Pernambuco (Guerra 2007); (7) Fazenda Matumbo, Pedra dos Pontais, Toritama, Pernambuco (Astúa & Guerra 2008); (8) RPPN Maurício Dantas, Betânia/Floresta, Pernambuco (Cruz et al. 2005); (9) Fazenda Araras, Brejo da Madre de Deus, Pernambuco (Silva 2007); (10) RPPN Fazenda Bituri, Serra do Bituri, Brejo da Madre de Deus, Pernambuco (Silva 2007); (11) Pedra do Caboclo, Barra do Farias, Brejo da Madre de Deus, Pernambuco (Astúa & Guerra 2008); (12) Sítio Coendus, Serra da Balança, Belo Jardim, Pernambuco (Astúa & Guerra 2008); (13) Sítio da Gritadeira, Serra da Farinha, Serrote da Gritadeira, Fazenda Maniçoba 13.7 Km SSW, and Serrote das Lajes, 17 Km south of Exú, Pernambuco (Mares et al. 1981; Astúa & Guerra 2008); (14) Trapiche S/A Refinery, Sirinhaém/Rio Formoso, Pernambuco (Soares et al. 2011); (15) Itapipoca, Ceará (Piccinini 1974); (16) Serra Grande S/A Refinery, São José da Lage/Ibateguara, Alagoas (Sá Neto 2003); (17) Fumaça Cave, APA Maribuns Iraquara, Iraquara, Chapada Diamantina, Bahia (Sbragia & Cardoso 2008); (18) Cave, Serra das Confusões, Serra das Confusões National Park, Guaribas, Piauí, (Gregorin et al. 2008); (19) Fazenda Mundo Novo, Canindé do São Francisco, Sergipe (present study). ! ! ! ! ! ! 1172 Chiroptera Neotropical 19(1): 1163-1178, July 2013 ! ! Figure 2. Distribution of the available records of the Lesser Dog-like Bat, Peropteryx macrotis, in northeastern Brazil (● = existing record; ■ = new record): (1) Carrapateira Cave, Felipe Guerra, Rio Grande do Norte (Ferreira et al. 2010); (2) Natal, Rio Grande do Norte (Sanborn 1937; Jones & Hood 1993); (3) Fazenda Riachão do Progresso, Alagoa Grande, Paraíba (Beltrão et al. 2011); (4) Fazenda Bravo, Cabaceiras, Paraíba (Miretzki, 2005; Feijó & Langguth 2011); (5) Boqueirão, Paraíba (Miretzki 2005); (6) Fazenda Curral Picado, 4 km from Alagoinha, Paraíba (Miretzki, 2005; Feijó & Langguth 2011); (7) Pedra da Boca State Park, Araruna, Paraíba (Miretzki, 2005; Feijó & Langguth 2011); (8) Roger neighborhood, João Pessoa, Paraíba (Miretzki 2005; Feijó & Langguth 2011); (9) Mata do Camocim, Tapacurá Ecological Station, São Lourenço da Mata, Pernambuco (Mares et al. 1981); (10) Mata de São João, Paudalho, Pernambuco (Guerra 2007); (11) Caiongo and Compota sugar refineries, Cabo de Santo Agostinho, Ponte dos Carvalhos, Pernambuco (Guerra 2007); (12) Sítio Claranã, Bodocó, Pernambuco (Astúa & Guerra 2008); (13) Apolônio Sales and Icó-Mandantes Projects (CHESF), Petrolândia, Pernambuco (Astúa & Guerra 2008); (14) Fazenda Araras, Brejo da Madre de Deus, Pernambuco (Silva 2007); (15) Exú Agricultural College, 0.7 Km south, Fazenda Batente, 5.5 Km SE, Gambá Sawmill, 19 Km SSW, and Fazenda Pomonha, 21 Km SSW of Exú, Pernambuco (Mares et al. 1981); (16) Pedra Talhada Biological Reserve, Quebrângulo/Lagoa do Ouro, Pernambuco/Alagoas (Souza et al. 2004); (17) Brejões Cave, Serra das Araras, João Dourado/Morro do Chapéu, Chapada Diamantina, Bahia (Sbragia & Cardoso 2008); (18) Fazenda Lajedo, at Km 147 of the BA130 highway, Senhor do Bonfim, Bahia (Mares et al. 1981); (19) flooded area of the Itaparica Dam, Glória, Bahia (Astúa & Guerra 2008); (20) Sobradinho Reservoir, Sobradinho, Bahia (Astúa & Guerra 2008); (21) Rio Jequitinhonha, Belmonte, Bahia (Ávila-Pires 1965); (22) Crateús, Ceará (Oliveira et al. 2003; 2004; Silva & Nascimento 2008); (23) Fazenda Santa Fé, Quixadá, Ceará (Astúa & Guerra, 2008); (24) Serra de Maranguape, Maranguape, Ceará (Piccinini 1973); (25) Araticum Cave at the base of the Serra da Ibiapaba, Vila do Araticum, Ubajara, Ceará (Uieda et al. 1980); (26) Banabuiú, Ceará (Rocha et al. 1999); (27) Serra da Capivara National Park, São Raimundo Nonato, Piauí (Araújo et al. 1998); (28) Serra da Guia, Poço Redondo, Sergipe (Rocha 2010); (29) Fazenda Mundo Novo, Canindé do São Francisco, Sergipe (present study). ! ! ! 1173 Chiroptera Neotropical 19(1): 1163-1178, July 2013 ! ! Figure 3. Distribution of the localities in the northeastern Brazilian state of Sergipe at which bats have been collected, based on the studies of Alencar et al. (1994), Hoffmann & Baker (2003), Mikalauskas (2005), Miretzki (2005), Mikalauskas et al. (2006 a, b), Astúa & Guerra (2008), Gouveia et al. (2009), Feijó & Nunes (2010), Rocha (2010), Rocha et al. (2010), Rocha et al. (2011a), Rocha et al. (2011b) Mikalauskas et al. (2011), Brito & Bocchiglieri (2012), and Leal et al. (in press): 1. Riachuelo; 2. Rosário do Catete; 3. São Cristóvão; 4. Aracajú/São Cristóvão; 5. Santo Amaro das Brotas; 6. Canindé do São Francisco (Astúa & Guerra 2009 and present study); 7. Areia Branca/Itabaiana; 8. Itabaiana; 9. Capela; 10. Poço Redondo; 11. Propriá; 12. Brejo Grande, and 13. Cristianápolis (the geographic coordinates of localities 1, 2, 11, 12, and 13 correspond to the main town in each municipality). ! ! ! ! 1174 Chiroptera Neotropical 19(1): 1163-1178, July 2013 Table 1. Chiropteran species recorded in the Brazilian state of Sergipe by locality and biome. The numbers in parentheses correspond to the localities plotted in Figure 3. Taxon Municipality Locality Biome Coordinates Reference Family Emballonuridae Gervais, 1955 Peropterix macrotis (Wagner, 1843)* Canindé do São Francisco (8) Fazenda Mundo Novo Caatinga 9º 38’31” S, 37º 47’ New record Poço Redondo (12) Serra da Guia Caatinga 18” W Rocha (2010) 9º58’S, 37º52’W Rhynchonycteris naso (Wied-Neuwied, 1820) Aracajú/São Cristovão (5) UFS campus Atlantic Forest 10º 55’ S, 37º 04’ W Rocha et al. (2010) Saccopteryx leptura (Schreber, 1774) Areia Branca/Itabaiana (9) PN Serra de Itabaiana Atlantic Forest 10º 40’ S, 37º 25’ W Mikalauskas (2005) Family Phyllostomidae Gray, 1825 Subfamily Desmodontinae Bonaparte, 1845 Desmodus rotundus (E. Geoffroy, 1810) Riachuelo (1) Not recorded Atlantic Forest Main town Alencar et al. (1994) Rosário do Catete (3) Not recorded Atlantic Forest Main town Alencar et al. (1994) Poço Redondo (12) Serra da Guia Caatinga 9º58’S, 37º52’W Rocha (2010) Capela (11) RVS Mata do Junco Atlantic Forest 10º32’S, 37º03’W Brito & Bocchiglieri (2012) Diphylla ecaudata (Spix, 1823)* Canindé do São Francisco (8) Fazenda Mundo Novo Caatinga 9º 38’31” S, 37º 47’ First record 18” W Subfamily Glossophaginae Bonaparte, 1845 Anoura geoffroyi (Gray, 1838) Aracajú/São Cristovão (5) UFS campus Atlantic Forest 10º 55’ S, 37º 04’ W Rocha et al. (2010) Areia Branca/Itabaiana (9) PN Serra de Itabaiana Atlantic Forest 10º 40’ S, 37º 25’ W Mikalauskas (2005) Poço Redondo (12) Serra da Guia Caatinga 9º58’S, 37º52’W Rocha (2010) Glossophaga soricina (Pallas, 1766) Areia Branca/Itabaiana (9) PN Serra de Itabaiana Atlantic Forest 10º 40’ S, 37º 25’ W Mikalauskas (2005) Aracajú/São Cristovão (5) UFS campus Atlantic Forest 10º 55’ S, 37º 04’ W Rocha et al. (2010) Poço Redondo (12) Serra da Guia Caatinga 9º58’S, 37º52’W Rocha (2010) Capela (11) RVS Mata do Junco Atlantic Forest 10º32’S, 37º03’W Brito & Bocchiglieri (2012) Lichonycteris obscura Thomas, 1895 Poço redondo (12) Serra da Guia Caatinga 9º58’S, 37º52’W Rocha (2010) Lonchophylla mordax (Thomas, 1903) Areia Branca/Itabaiana (9) PN Serra de Itabaiana Atlantic Forest 10º 40’ S, 37º 25’ W Mikalauskas (2005); Mikalauskas et al. (2006a) Canindé do São Francisco (8) Fazenda Mundo Novo Caatinga 9º 38’31” S, 37º 47’ Astúa & Guerra (2008) Poço Redondo (12) Serra da Guia Caatinga 18” W Rocha (2010) 9º58’S, 37º52’W Xeronycteris vieirai (Gregorin & Duchfield, Canindé do São Francisco (8) Fazenda Mundo Novo Caatinga 9º 38’31” S, 37º 47’ Astúa & Guerra (2008) 2005) 18” W Subfamily Phyllostominae Gray, 1825 Lonchorrhina aurita Tomes, 1863 Canindé do São Francisco (8) Fazenda Mundo Novo Caatinga 9º 38’31” S, 37º 47’ Leal et al. no prelo 18” W Lophostoma brasiliense Peters, 1866 Poço Redondo (12) Serra da Guia Caatinga 9º58’S, 37º52’W Rocha (2010) Micronycteris megalotis Gray, 1842 Poço Redondo (12) Serra da Guia Caatinga 9º58’S, 37º52’W Rocha (2010) Micronycteris sanborni (Simmons, 1996) Poço Redondo (12) Serra da Guia Caatinga 9º58’S, 37º52’W Rocha (2010) Micronycteris sp. Areia Branca/Itabaiana (9) PN Serra de Itabaiana Atlantic Forest 10º 40’ S, 37º 25’ W Mikalauskas (2005) Phyllostomus discolor (Wagner, 1843) Areia Branca/Itabaiana (9) PN Serra de Itabaiana Atlantic Forest 10º 40’ S, 37º 25’ W Mikalauskas (2005) Aracajú/São Cristovão (5) UFS campus Atlantic Forest 10º 55’ S, 37º 04’ W Rocha et al. (2010) Santo Amaro das Brotas (7) Not recorded Atlantic Forest Main town Miretzki (2005) Capela (11) RVS Mata do Junco Atlantic Forest 10º32’S, 37º03’W Brito & Bocchiglieri (2012) 1175 ! Chiroptera Neotropical 19(1): 1163-1178, July 2013 Table 1 (cont...) Taxon Phyllostomus hastatus (Pallas, 1766) Tonatia saurophylla Koopmann & Williams, 1951 Trachops cirrhosus (Spix, 1823) Trinycteris nicefori (Sanborn, 1949) Macrophyllum macrophyllum (Schinz, 1821) Subfamily Carolliinae Miller, 1924 Carollia perspicillata (Linnaeus, 1758) Subfamily Stenodermatinae Gervais, 1856 Dermanura cinerea (Gervais, 1856) Artibeus fimbriatus (Gray, 1838) Artibeus lituratus (Olfers, 1818) Artibeus obscurus (Schinz, 1821) Artibeus planirostris (Spix, 1823) Municipality Aracajú/São Cristovão (5) Capela (11) Capela (11) Locality UFS campus RVS Mata do Junco RVS Mata do Junco Biome Atlantic Forest Atlantic Forest Atlantic Forest Coordinates 10º 55’ S, 37º 04’ W 10º32’S, 37º03’W 10º32’S, 37º03’W São Cristovão (4) Capela (11) Not recorded RVS Mata do Junco Atlantic Forest Atlantic Forest Capela (11) Aracajú/São Cristovão (5) RVS Mata do Junco UFS campus Atlantic Forest Atlantic Forest 11º 00’ 54” S, 37º 12’ 21” W 10º32’S, 37º03’W 10º32’S, 37º03’W 10º 55’ S, 37º 04’ W Areia Branca/Itabaiana (9) PN Serra de Itabaiana Atlantic Forest 10º 40’ S, 37º 25’ W Aracajú/São Cristovão (5) Poço Redondo (12) Brejo Grande (14) Cristianápolis (15) Santo Amaro das Brotas (7) Capela (11) UFS campus Serra da Guia Fazenda Capivara Fazenda Cruzeiro Not recorded RVS Mata do Junco Atlantic Forest Caatinga Atlantic Forest Atlantic Forest Atlantic Forest Atlantic Forest 10º 55’ S, 37º 04’ W 9º58’S, 37º52’W Main town Main town Main town 10º32’S, 37º03’W Areia Branca/Itabaiana (9) PN Serra de Itabaiana Atlantic Forest 10º 40’ S, 37º 25’ W Aracajú/São Cristovão (5) Poço Redondo (12) Cristianápolis (15) Capela (11) Areia Branca/Itabaiana (9) Aracajú/São Cristovão (5) Poço Redondo (12) Capela (11) Areia Branca/Itabaiana (9) UFS campus Serra da Guia Fazenda Cruzeiro RVS Mata do Junco PN Serra de Itabaiana UFS campus Serra da Guia RVS Mata do Junco PN Serra de Itabaiana Atlantic Forest Caatinga Atlantic Forest Atlantic Forest Atlantic Forest Atlantic Forest Caatinga Atlantic Forest Atlantic Forest 10º 55’ S, 37º 04’ W 9º58’S, 37º52’W Main town 10º32’S, 37º03’W 10º 40’ S, 37º 25’ W 10º 55’ S, 37º 04’ W 9º58’S, 37º52’W 10º32’S, 37º03’W 10º 40’ S, 37º 25’ W Aracajú/São Cristovão (5) Poço Redondo (12) Brejo Grande (14) Santo Amaro das Brotas (7) Capela (11) Areia Branca/Itabaiana (9) Aracajú/São Cristovão (5) Poço Redondo (12) Santo Amaro das Brotas (6) Capela (11) UFS campus Serra da Guia Fazenda Capivara Not recorded RVS Mata do Junco PN Serra de Itabaiana UFS campus Serra da Guia Not recorded RVS Mata do Junco Atlantic Forest Caatinga Atlantic Forest Atlantic Forest Atlantic Forest Atlantic Forest Atlantic Forest Caatinga Atlantic Forest Atlantic Forest 10º 55’ S, 37º 04’ W 9º58’S, 37º52’W Main town Main town 10º32’S, 37º03’W 10º 40’ S, 37º 25’ W 10º 55’ S, 37º 04’ W 9º58’S, 37º52’W 10º 47’ 20” S, 37º 03’ 16” W 10º32’S, 37º03’W 1176 ! Reference Rocha et al. (2010) Brito & Bocchiglieri (2012) Rocha et al. (2007); Brito e Bocchiglieri (2012) Feijó & Nunes (2010); Brito & Bocchiglieri (2012) Brito e Bocchiglieri (2012) Rocha et al. (2010) Mikalauskas (2005); Mikalauskas et al. (2006a) Rocha et al. (2010) Rocha (2010) Miretzki (2005) Hoffmann & Baker (2003) Hoffmann & Baker (2003) Brito & Bocchiglieri (2012) Mikalauskas (2005); Mikalauskas et al. (2006a) Rocha et al. (2010) Rocha (2010) Miretzki (2005) Brito & Bocchiglieri (2012) Mikalauskas (2005) Rocha et al. (2010) Rocha (2010) Brito & Bocchiglieri (2012) Mikalauskas (2005); Mikalauskas et al. (2006a) Rocha et al. (2010) Rocha (2010) Miretzki (2005) Miretzki (2005) Brito & Bocchiglieri (2012) Mikalauskas (2005) Rocha et al. (2010) Rocha (2010) Miretzki (2005); Feijó & Nunes (2010) Brito & Bocchiglieri (2012) Chiroptera Neotropical 19(1): 1163-1178, July 2013 Table 1. (cont..) Taxon Chiroderma dorie (Thomas, 1891) Municipality Areia Branca/Itabaiana (9) Capela (11) Locality PN Serra de Itabaiana RVS Mata do Junco Biome Atlantic Forest Atlantic Forest Coordinates 10º 40’ S, 37º 25’ W 10º32’S, 37º03’W Areia Branca/Itabaiana (9) Areia Branca/Itabaiana (9) PN Serra de Itabaiana PN Serra de Itabaiana Atlantic Forest Atlantic Forest 10º 40’ S, 37º 25’ W 10º 40’ S, 37º 25’ W Aracajú/São Cristovão (5) Poço Redondo (12) Capela (11) Areia Branca/Itabaiana (9) Aracajú/São Cristovão (5) Poço Redondo (12) Capela (11) Aracajú/São Cristovão (5) Poço Redondo (12) UFS campus Serra da Guia RVS Mata do Junco PN Serra de Itabaiana UFS campus Serra da Guia RVS Mata do Junco UFS campus Serra da Guia Atlantic Forest Caatinga Atlantic Forest Atlantic Forest Atlantic Forest Caatinga Atlantic Forest Atlantic Forest Caatinga 10º 55’ S, 37º 04’ W 9º58’S, 37º52’W 10º32’S, 37º03’W 10º 40’ S, 37º 25’ W 10º 55’ S, 37º 04’ W 9º58’S, 37º52’W 10º32’S, 37º03’W 10º 55’ S, 37º 04’ W 9º58’S, 37º52’W Reference Mikalauskas (2005); Mikalauskas et al. (2006b) Brito & Bocchiglieri (2012) Mikalauskas (2005) Mikalauskas (2005); Mikalauskas et al. (2006a) Rocha et al. (2010) Rocha (2010) Brito & Bocchiglieri (2012) Mikalauskas (2005) Rocha et al. (2010) Rocha (2010) Brito & Bocchiglieri (2012) Rocha et al. (2010) Rocha (2010) Poço redondo (12) Serra da Guia Caatinga 9º58’S, 37º52’W Rocha et al. (2011b) Pteronotus personatus (Wagner, 1843) Itabaiana (10) Riachuelo (2) Casa de Pedra Cave Urubu Cave Atlantic Forest Atlantic Forest Golveia et al. 2009; Rocha et al. 2011a Pteronotus gymnonotus Itabaiana (10) Riachuelo (2) Casa de Pedra Cave Urubu Cave Atlantic Forest Atlantic Forest 10º50.050’S, 37º27.027’W 10º43.964’S, 37º09.927’W 10º50.050’S, 37º27.027’W 10º43.964’S, 37º09.927’W Noctilio leporinus (Linnaeus, 1758) Aracajú/São Cristovão (5) Propriá (13) UFS campus Not recorded Atlantic Forest Atlantic Forest 10º 55’ S, 37º 04’ W Main town Rocha et al. (2010) Miretzki (2005) Noctilio albiventris Desmarest, 1818 Aracajú/São Cristovão (5) UFS campus Atlantic Forest 10º 55’ S, 37º 04’ W Rocha et al. (2010) Canindé do São Francisco (8) Fazenda Mundo Novo Caatinga 9º 38’31” S, 37º 47’ 18” W Astúa & Guerra (2008) Chiroderma villosum (Peters 186) Platyrrhinus lineatus (E. Geoffroy, 1810) Sturnira lilium (E.Geoffroy, 1810) Uroderma bilobatum (Peters, 1866) Uroderma magnirostrum Davis, 1968 Family Mormoopidae Saussure, 1860 Golveia et al. (2009); Rocha et al. (2011a) Family Noctilionidae Gray, 1821 Family Furipteridae Gray, 1866 Furipterus horrens (F. Cuvier, 1828) ! 1177 ! Chiroptera Neotropical 19(1): 1163-1178, July 2013 Table 1. (cont..) Taxon Family Natalidae Gray, 1866 Municipality Locality Biome Coordinates Reference Natalus macrourus (Gervais, 1856) Itabaiana (10) Casa de Pedra Cave Atlantic Forest 10.833º S, 37.450º W Golveia et al. (2009) Cynomops planirostris (Pallas, 1766) Aracajú/São Cristovão (5) UFS campus Atlantic Forest 10º 55’ S, 37º 04’ W Rocha et al. (2010) Cynomops greenhalli Goodwin, 1958 Not recorded Not recorded Not recorded Not recorded Peracchi et al. (2011) Molossus molossus (Pallas, 1766) Aracajú/São Cristovão (5) UFS campus 10º 55’ S, 37º 04’ W Rocha et al. (2010) Areia Branca/Itabaiana (9) Aracajú/São Cristovão (5) Poço Redondo (12) Brejo Grande (14) Capela (11) PN Serra de Itabaiana UFS campus Serra da Guia Fazenda Capivara RVS Mata do Junco 10º 40’ S, 37º 25’ W 10º 55’ S, 37º 04’ W 9º58’S, 37º52’W Sede Municipal 10º32’S, 37º03’W Mikalauskas (2005) Rocha et al. (2010) Rocha (2010) Miretzki (2005) Brito & Bocchiglieri (2012) Family Molossidae Gervais, 1856 Atlantic Forest Family Vespertilionidae Gray, 1821 Myotis nigricans (Schinz, 1821) Atlantic Forest Atlantic Forest Caatinga Atlantic Forest Atlantic Forest Rhogueessa hussoni Genoways and Baker, Capela (11) RVS Mata do Junco Atlantic Forest 10º32’S, 37º03’W Mikalauskas et al. (2011) 1996 Sources: Alencar et al. (1994), Hoffmann & Baker (2003), Miretzki (2005), Mikalauskas (2005), Mikalauskas et al. (2006 a, b), Gouveia et al. (2009), Astúa & Guerra (2008), Feijó & Nunes (2010), Rocha (2010), Rocha et al. (2010), Rocha et al. (2011a), Rocha et al. (2011b), Mikalauskas et al. (2011), Peracchi et al., (2011), Brito & Bocchiglieri (2012), and Leal et al. (in press). (*) Present study. 1178 !
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