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Mastozoología neotropical

versión impresa ISSN 0327-9383versión On-line ISSN 1666-0536

Mastozool. neotrop. v.12 n.2 Mendoza jul./dic. 2005

 

Research on bats in the state of Rio de Janeiro, southeastern Brazil

Carlos E. L. Esbérard1,2 and Helena G. Bergallo2

1 Projeto Morcegos Urbanos, Fundação RIOZOO, Quinta da Boa Vista, s/n o, Rio de Janeiro, RJ, Brasil, 20.940-040, cesberard@terra.com.br. 2 Departamento de Ecologia, Universidade do Estado do Rio de Janeiro, Rua São Francisco Xavier 524, 20559-900, RJ, Brasil, bergallo@uerj.br.

Key words: Bat history. Bat list. Bat research. Bat richness.

   Rio de Janeiro (Fig. 1) is one of the most well studied states of Brazil in regard to its bat fauna, due to the concentration of universities and researchers (Bergallo et al., 2003). The first bat mentioned in the literature for Rio de Janeiro was the common vampire bat, Desmodus rotundus, by Hans Staden (1557, apud Tribe, 1987). However, the first scientific citation was of Anoura caudifer (E. Geoffroy, 1818), for which the State of Rio de Janeiro is the type-locality (Lima, 1926).


Fig. 1. Location of the state of Rio de Janeiro in Southeastern Brazil and South America.

   Until the 1970s, most research on bats was done by capturing the animals directly in their refuges or by shooting. The use of mist nets greatly increased the efficiency of capture (see Handley, 1967), resulting in an increase in the knowledge of bat biology and distribution in this geographical unit (Fig. 2). The first reference to the use of mist nets in Rio de Janeiro State dates from 1967 (Peracchi and Albuquerque, 1971).


Fig. 2. Historic evolution of accumulated number of bat species recorded at Rio de Janeiro, southeastern Brazil.

   The first species list for the state, published by Peracchi and Albuquerque (1971), included 12 new records, subsequently complemented with another five species (Peracchi and Albuquerque, 1986).
   In the last 40 years, this list grew rapidly (Fig. 2) due to an increase in the number of researchers, as well as institutions interested in the study of bats. In 1997, a meeting was held to produce a list of threatened species and analyze their conservation status (Bergallo et al., 2000); 62 species were recognized for the Rio de Janeiro state (Rocha et al., 2004).
   Currently, Rio de Janeiro is the most thoroughly sampled state in Brazil, in terms of bats (Bergallo et al., 2003). However, even considering there are inventories in more than 30 different areas, several sites in the state remain poorly sampled, such as the northwestern and the montane areas. Since the 1997 list, new surveys of previously unexplored areas have confirmed the presence of Furipterus horrens in the south (Pol et al., 2003), Myotis levis in a montane area in the south (A. Pol, personal communication), Neoplatymops mattogrossensis and Uroderma bilobatum in the northern part of the state (Avila et al., 2001) and Micronycteris hirsuta (Esbérard, 2004a) and Tonatia brasiliensis (unpublished results) in the northern and central part of the state.
   Additionally, increased sampling efforts in previously sampled areas, such as the Maciço da Tijuca, have confirmed the occurrence of species not previously recorded, despite extensive inventories totaling more than 4000 bats in 189 nights (Esbérard, 1999). That is the case of Uroderma magnirostrum (Nogueira et al., 2003), Phyllostomus discolor (Esbérard, 2003) and Nictynomops laticaudata (unpublished data).
   The total number of species confirmed for the State of Rio de Janeiro in this report (71 species) is larger than previous estimates for this latitude (Findley, 1993) or for the state (Marinho-Filho, 1996) (Table 1). Estimates throughout the latitude have been lower than the observed richness, as in the State of Paraná, where 41 species and 6 families were expected (Marinho-Filho, 1996) and, up to the present, 53 species from 5 families have been recorded (Miretzki, 2003).

   Eight of the 9 bat families occurring in Brazil are represented in the State of Rio de Janeiro, with 41 genera and 71 species (Table 2). This corresponds to 52% of all species known to occur in Brazil, and 74% of all species recorded in the Atlantic Forest biome (Marinho-Filho and Sazima, 1998). About 53% of all phyllostomid species known to occur in Brazil have been recorded in Rio de Janeiro State, as well as 61% of all Vespertilionidae, 56% of Molossidae and 33% of Emballonuridae species.

Table 2
Species of bats recorded in the State of Rio de Janeiro, Brazil. Species marked with an asterisk were listed during the specialist workshop in 1997 (Bergallo et al., 2000). (1) The earlier record of Tonatia brasiliensis was erroneous (see Peracchi and Albuquerque, 1971); (2) Cynomops abrasus includes Molossops brachymeles (Goodwin, 1958).

   These general figures are still an underestimation, since most published studies used only mist net sampling (Bergallo et al., 2003), which underestimates the richness and abundance of insectivorous species (Voss and Emmons, 1996). Few researchers performed captures in refuges. Diversification of capture methods and use of bioacoustical techniques would likely increase or confirm the occurrence of some insectivorous species, as well as species with wider flight areas (Kalko et al., 1996; Voss and Emmons, 1996). Marinho-Filho (1996) listed five species that were not yet recorded in Rio de Janeiro but that, based on their geographical distribution (Fig. 1), should occur there: Noctilio albiventris (present in the states of São Paulo, Minas Gerais and Espírito Santo), Sturnira tildae (distributed from the State of Rio Grande do Sul to the State of São Paulo), Myotis riparius (distributed from the State of Santa Catarina to the State of São Paulo), Eumops bonariensis (present in the State of São Paulo) and Nictynomops aurispinosus (present in the states of São Paulo, Minas Gerais and Espírito Santo) (Fig. 2).
   The state of Rio de Janeiro with its 43 910 km2, and only 17% of its original forest cover (Rocha et al., 2003), represents 0.5% of the Brazilian territory and harbors one of the richest bat faunas in the country. The record of Rhinophylla pumilio in the border of Rio de Janeiro and Espírito Santo states (Tribe, 1987), and the curve of accumulated number of species we obtained (Fig. 2), reinforces the idea that even more species should be confirmed for Rio de Janeiro in the future.

The criticisms and contributions made by Lena Geise, Adriano L. Peracchi, Rui Cerqueira and Davor Vrcibradic and an anonymous referee are gratefully acknowledged; we also thank André Pol, Daniela Dias and Marcia Batista for their help in the bibliography and occurrence records.

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Recibido 13 febrero 2004.
Aceptación final 1º junio 2005.

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