Services on Demand
Print version ISSN 0001-3765
An. Acad. Bras. Ciênc. vol.80 no.2 Rio de Janeiro June 2008
Mauricio Almeida-Gomes; Davor Vrcibradic; Carla C. Siqueira; Mara C. Kiefer; Thaís Klaion; Patrícia Almeida-Santos; Denise Nascimento; Cristina V. Ariani; Vitor N.T. Borges-Junior; Ricardo F. Freitas-Filho; Monique van Sluys; Carlos F.D. Rocha
Departamento de Ecologia, Universidade do Estado do Rio de Janeiro, Rua São Francisco Xavier, 524, 20550-011 Rio de Janeiro, RJ, Brasil
We studied the herpetofaunal community from the Atlantic forest of Morro São João, in Rio de Janeiro State, Brazil, and present data on species composition, richness, relative abundance and densities. We combined three sampling methods: plot sampling, visual encounter surveys and pit-fall traps. We recorded sixteen species of amphibians and nine of reptiles. The estimated densities (based on results of plot sampling) were 4.5 ind/100 m2 for amphibians and 0.8 ind/100 m2 for lizards, and the overall density (amphibians and lizards) was 5.3 ind/100 m2. For amphibians, Eleutherodactylus and Scinax were the most speciose genera with three species each, and Eleutherodactylus binotatus was the most abundant species (mean density of 3.0 frogs/100 m2). The reptile community of Morro São João was dominated by species of the families Gekkonidae and Gymnophtalmidae (Lacertilia) and Colubridae (Serpentes). The gymnophtalmid lizard Leposoma scincoides was the most abundant reptile species (mean density of 0.3 ind/100 m2). We compare densities obtained in our study data with those of other studied rainforest sites in various tropical regions of the world.
Key words: herpetofauna, Atlantic rainforest, Brazil, richness, density.
Estudamos a comunidade herpetofaunística da Mata Atlântica do Morro São João, Estado do Rio de Janeiro, Brasil, e apresentamos dados da composição, riqueza, abundância relativa e densidade das espécies. Combinamos três metodologias de amostragem: parcelas, encontros visuais e armadilhas de queda. Registramos 16 espécies de anfíbios e 9 espécies de répteis. As densidades estimadas (baseadas nos resultados da amostragem através de parcelas) foram 4.5 ind/100 m2 para anfíbios, 0.8 ind/100 m2 para lagartos, e a densidade total (anfíbios e répteis) foi 5.3 ind/100 m2. Para anfíbios, Eleutherodactylus e Scinax foram os gêneros com maior número de espécies, com três espécies cada, e Eleutherodactylus binotatus foi a espécie mais abundante (densidade média de 3.0 anuros/100 m2). A comunidade de répteis do Morro São João foi dominada por espécies da família Gekkonidae e Gymnophtalmidae (Lacertilia) e Colubridae (Serpentes). O lagarto gimnoftalmídeo Leposoma scincoides foi a espécie de réptil mais abundante (densidade média de 0.3 ind/100 m). Comparamos os dados de densidade obtidos no nosso estudo com os de outros estudos em florestas de várias regiões tropicais do mundo.
Palavras-chave: herpetofauna, Mata Atlântica, Brasil, riqueza, densidade.
Within the past fifty years, several studies carried out in rainforest areas have provided data on ecological parameters of tropical herpetofaunal communities throughout the world (e.g. Brown and Alcala 1961, Lloyd et al. 1968, Scott 1976, 1982, Inger 1980a, b, Toft 1982, Fauth et al. 1989, Allmon 1991, Giaretta et al. 1997, 1999, Rocha et al. 2000, 2001, Vonesh 2001, Doan and Arriaga 2002, Doan 2003, Huang and Hou 2004). Despite the increase in the number of studies worldwide, the present knowledge of herpetofaunal communities still remains incomplete (Duellman 1999, Azevedo-Ramos and Galatti 2002, Doan and Arriaga 2002). For the Atlantic Rainforest biome of eastern Brazil, one of the most species-rich and endangered tropical forests on Earth, data on species composition and richness of amphibians and reptiles are limited to studies on a few areas (Heyer et al. 1990, Haddad and Sazima 1992, Sazima and Haddad 1992, Machado et al. 1999, Bernarde and Machado 2000, Machado and Bernarde 2002, Marques and Sazima 2004, Pombal and Gordo 2004, Conte and Machado 2005, Conte and Rossa-Feres 2006, Dixo and Verdade 2006), all of them in southern and southeastern Brazil. Also, only five studies present data on relative densities of frogs in leaf litter communities (Giaretta etal. 1997, 1999, Rocha et al. 2000, 2001, 2007) and none presents density estimates for reptiles. The knowledge about the herpetofauna of forest remnants in Rio de Janeiro State, in particular, is still scarce, and more studies are necessary (Rocha et al. 2003).
Several methods have been used for herpetofaunal sampling, and some of the most frequently used are visual encounter surveys (VES) (e.g. Inger 1980b, Toft 1982, Vasudevan et al. 2001), plot (or quadrat) sampling (e.g. Allmon 1991, Rocha et al. 2000, 2001, Vonesh 2001, Watanabe et al. 2005) and pit-fall traps (e.g. Cechin and Martins 2000, Enge 2001, Dixo and Verdade 2006). In a few cases, more than one method is employed during a study (e.g. Doan 2003, Brasileiro et al. 2005, Loebmann and Vieira 2005, Rocha et al. 2007).
The region of Morro São João, in the northeastern portion of Rio de Janeiro State, is one representativeremnant of Atlantic Rainforest in the State. The area is of special interest because it presently represents an "island" of Atlantic forest surrounded by pastures and farmlands. Nevertheless, there is no published information on the fauna of this area. In the present study, we present data on some community parameters such as species composition, richness, relative abundances and densities of the herpetofaunal community of Morro São João, and compare our results with those reported for other rainforest areas worldwide.
MATERIALS AND METHODS
Morro São João (22º33'S, 42º01'W), located in the municipality of Casimiro de Abreu, State of Rio de Janeiro, southeastern Brazil, is a hill of volcanic origin about 800m high and presently covered by about 640 ha of secondary Atlantic Rainforest. Mean annual temperature in the area is 22-23ºC and annual rainfall (based on data for the nearby town of Barra de São João; Barbieri and Coe-Neto 1999) is 1140 mm.
METHODOLOGY AND ANALYSES
Surveys were carried out during late May and early June 2005. Samplings were done from the base of the hill (and its surroundings) up to an altitude of 320m. In order to obtain a representative dataset of the herpetofauna for the study area we sampled during the day and at night and used three sampling methods: large plots (see Jaeger and Inger 1994), visual encounter surveys (VES; Crump and Scott 1994) and pit-fall traps with drift fences (Corn 1994). Besides, all individuals found during casual encounters in the field (including animals found dead) were also collected.
For the Large-Plot method we established 24 quadrats of 5 ×5 m (25 m2) on the forest floor during the afternoon. We marked the corners of each plot with wooden stakes and the plot was completely enclosed by a 50 cm high soft plastic fence. The bottom of the plastic fence was buried or attached to the ground to prevent animals from escaping. After the sunset, each plot was carefully searched by a crew of five persons wearing head lamps. During searches, each crew member moved up the entire plot on hands and knees, side-by-side. All leaves, branches and stones inside the plot were overturned with the aid of hand rakes and rock crevices and spaces between tree roots were also checked. Vertical tree trunks and shrubs inside the plots were also examined for the presence of scansorial amphibians and reptiles. Each plot was searched for about half an hour.
For VES method, we carried out 120 transects of 30 minutes duration each, totaling 60 hours of sampling effort. The same number of transects (40) was surveyed during each period of the day (diurnal, crepuscular and nocturnal). During each transect, the observer moved at a slow walking pace, carefully searching the surroundings for the presence of amphibians and reptiles.
Two pit-fall trap systems were used for 15 days. Each pit-fall trap system consisted of ten 30-liter buckets (50 cm depth and 50 cm diameter) buried on the ground and set ca. 5m apart, with soft plastic drift fences about 50 cm high extended between them. Six buckets were placed in line and the other four were placed at opposite sides of the fence, perpendicularly to the main axis. Pit-falls were checked once per day (always in the morning) and all frogs and reptiles found in them were removed.
For an estimate of species composition and richness of the herpetofaunal community in the area we considered the species recorded by all three sampling methods, plus those collected during casual encounters. For estimates of density (individuals/100 m2) we considered only the data obtained by the large plot sampling. This method has been the most frequently used in tropical forests worldwide (see Allmon 1991), which allow us to make comparisons with other forested areas for which data is available.
We recorded sixteen species of amphibians (all anurans) and nine species of reptiles at Morro São João (Table I). The amphibian community of Morro São João was dominated by species of the families Hylidae and Brachycephalidae, whereas the reptile community was dominated by species in the families Gekkonidae and Gymnophtalmidae (Lacertilia) and Colubridae (Serpentes) (Table I).
In the plots we recorded 26 individuals in six frog species (plus one unidentified frog that escaped before identification) and five individuals of four reptile species (Table II). The number of frogs per plot ranged from zero (9/24 or 37.5% of all plots) to four (1/24 or 4.2% of all plots) with a mean of 1.1 ± 1.1 frogs per plot. In one-third of the plots (N = 8) in which frogs were found, only one individual was recorded. The total frog density estimated from plot sampling was 4.5 individuals/100 m2 (Table II). The brachycephalid Eleutherodactylus binotatus had the highest density (N = 18; 3.0 ind/100 m2) and comprised about 67% of all frogs found in plots (Table II). All reptiles found in plots were lizards and the number of reptiles per plot ranged from zero (21/24 or 87.5% of all plots) to two (2/24 or 8.4%) with a mean of 0.2 ± 0.6 individuals per plot. The reptile density estimated from large plot sampling was 0.8 individuals/100 m2 (Table II). The lizard Leposoma scincoides (0.3 ind/100 m2; N = 2) comprised 40% of all reptiles found in plots (Table II). The overall herpetofaunal density (amphibians and reptiles) was 5.3 ind/100 m2. Most species recorded in the plots were ground-dwelling animals, but two scansorial lizards (the exotic gekkonid Hemidactylus mabouia and the autochtonous leiosaurid Enyalius brasiliensis) were also found, perched on tree trunks. Two individuals of the stream-dwelling frog Crossodactylus gaudichaudii were found in a plot set near a rocky stream.
Thirteen frog species were found in Morro São João during transect samplings (Table I). The most abundant species recorded in transects were Eleutherodactylusbinotatus (N = 26; 36.6% of all individuals found during transects) and Hypsiboas semilineatus (N = 12; 16.9%). Most frogs were found during the nocturnal (N = 34, or 47.9% of individuals sampled) and crepuscular (N = 21, or 29.6%) transects, whereas the proportion of frogs found during the diurnal transects (N = 16, or 22.5%) was comparatively low (Table III). Five reptile species were recorded in the transects (Table I). The most abundant reptile species recorded during transect sampling were Hemidactylus mabouia (N = 3; 37.5%) and Enyalius brasiliensis (N = 2; 25%). During transect sampling, most reptiles were found during the crepuscular (N = 4, or 50% of individuals sampled) and nocturnal (N = 3, or 37.5%) periods, whereas the proportion of reptiles found during the diurnal transects (N = 1, or 12.5%) was comparatively low (Table III).
Nine frogs in three species were captured in the pit-fall traps (Table I). The most frequently captured species in the pit-falls was Chaunus ornatus (77.8% of all specimens captured). Only one reptile (the lizard Placosoma cordylinum) was captured in pit-falls.
Most animals recorded during the study were found only inside the forest, but some (the frogs Hypsiboas semilineatus, Leptodactylus ocellatus and Scinax alter, and the lizard A. ameiva) were found only on open areas around the forest or at its border and others (the frogs Chaunus ornatus, Crossodactylus gaudichaudii andScinax aff. x-signatus, and the lizard Hemidactylusmabouia) were found both in forest and open habitats.
Our results constitute the first approach to species composition and richness of the herpetofauna of Morro São João, particularly with respect to anurans. Our results were similar to those of other studies on frog community in Central and South American areas, in that species of the family Brachycephalidae (sensu Frost et al. 2006) were the most numerous (Scott 1976, Lieberman 1986, Fauth et al. 1989, Allmon 1991, Giaretta et al. 1997, 1999, Rocha et al. 2000, 2001, Doan and Arriaga 2002). The most abundant frog species found in the plots (representing about 70% of the anuran fauna sampled) and in transects (about 40% of the anurans sampled) was Eleutherodactylus binotatus, which suggests that thismedium-sized frog is the dominant species in the local leaf litter community (at least at that time of the year). Some authors have remarked on the great abundance of eleutherodactylines (now in the family Brachycephalidae; see Frost et al. 2006) in amphibian leaf litter communities from New World tropical forests (e.g. Heyer and Berven 1973, Scott 1976). Those frogs have water-independent reproduction and may be more widely distributed within the forest than species with water-dependent reproduction, which tend to stay not too distant from water bodies (Scott 1976, Lynch and Duellman 1997, Menin 2005).
The data of the present study indicated a similar or higher frog density value compared to other South American sites in Amazonian (e.g. Allmon 1991, Gascon 1996) and Atlantic rainforests (Giaretta et al. 1997, 1999, Rocha et al. 2000, 2001) but lower than that of another Atlantic forest area also in Rio de Janeiro State (8.4 ind/100 m2; Rocha et al. 2007) and that of an area in Amazonian Peru (15.5 ind/100 m2; Toft 1980). In comparison to other tropical areas worldwide where frog densities data are available, the values of present study are, generally, lower than those of Central American (e.g. Heatwole and Sexton 1966, Scott 1976, Lieberman 1986) but equal or higher than that of Asian sites (Inger and Colwell 1977, Inger 1980a, Vasudevan et al. 2001).
The lack of studies providing density data for reptiles or for the overall herpetofaunal community from other Atlantic Rainforest areas prevents comparisonswith our results for Morro de São João. In their study of leaf-litter anurofauna of an Atlantic forest area in São Paulo State, Giaretta et al. (1999) calculated density values only for frogs, but mentioned that two reptiles (one lizard and one snake) were also found in plots. As the total area sampled in their study was 6400 m2, the local reptile density can thus be estimated at 0.03/100 m2 and the lizard density at 0.015/100 m2, which is considerably lower than the value reported in the present study (0.8/100 m2). In general, the reptile density values from Asian sites are similar to those of the present study (Inger and Colwell 1977, Inger 1980a). However, the values reported for Central American sites tend to be much higher (Heatwole and Sexton, 1966, Scott 1976). In Asian rainforests, the overall density values for amphibians and reptiles combined are generally lower or equal to that reported in our study (Inger and Colwell 1977, Inger 1980a), although in the Philippines these values may range from 5.1 to 15.0 ind/100 m2 according to the type of habitat (Brown and Alcala 1961). Values for African areas can be higher (Scott 1982) or lower (Vonesh 2001) than those of the present study. Again,the overall herpetofaunal density values reported forCentral American forests are consistently higher than that found by us (e.g. Heatwole and Sexton 1966, Scott 1976), although Fauth et al. (1989) found densities similar to that of our study.
Based on the pooled data from all three methods (as well as from casual findings), it is apparent that the four most abundant species in the local frog community are E. binotatus, H. semilineatus, C. ornatus and L. ocellatus. Of these, only E. binotatus was well represented in both transects and plot sampling. Pit-fall traps sampled a lower number of individuals and species than the other two methods, but was more efficient for sampling one particular species, the bufonid C. ornatus. In a study at another Atlantic rainforest area in Rio de Janeiro State, pit-falls also seemed more efficient than the other methods for sampling bufonids (Rocha et al. 2007). Some authors (e.g. Toft 1981, Strüssmann et al. 1984) suggested that bufonids may be more active and move for comparatively greater distances along the forest floor than other sympatric frog species, and this may increase their probability of falling in pit-fall traps. On the other hand, only one lizard was caught in pit-falls during our study. Most studies on forest floor herpetofaunas from tropical areas worldwide have shown that the densities of reptiles tend to be comparatively low compared to amphibians (e.g. Heatwole and Sexton1966, Scott 1976, Inger 1980a, Fauth et al. 1989), and our results concur with this trend. Additionally, Cechin and Martins (2000) suggested that bucket size is a factor that can influence the samplings, as small buckets (i.e. volume under 100 liters) may fail to sample some large-sized animals such as adults of many snake species. Thus, bucket size used in our study could also partially explain the results observed for reptiles (no snakes were captured in the pit-falls, for example). Overall, however, pit-falls proved the least efficient of the three sampling methods used in our study, which supports the opinion of Cechin and Martins (2000) that this method is not advantageous for short-term studies (under 20 days).
The data obtained from transects suggest that most amphibians at Morro São João (about 77%) are found during crepuscular and nocturnal periods. However, C. gaudichaudii and H. charadranaetes, two species with diurnal activity, were sampled mainly during the diurnal period. The four specimens of the diurnal lizard E. brasiliensis were all collected during the crepuscular/nocturnal period, but they were all inactive whenfound. At another studied Atlantic forest area, 66% of the leaf-litter frogs sampled were collected during the nocturnal period (Rocha et al. 2000). In another herpetofaunal study in which samplings were done during diurnal and nocturnal periods (using the VES method) in an Amazonian forest site, 80% of the reptiles and amphibians were recorded at night (Doan 2003).
In a comparison of two of the methods used in the present work (VES and quadrat sampling), Doan (2003) found that, both in the diurnal and nocturnal surveys, more individuals and species of amphibians and reptiles were recorded with the VES method than with quadrat (= plot) sampling. Besides, the two methodologies showed great difference in terms of records of terrestrial and arboreal amphibians, with the former tending to be better represented with quadrat sampling and the latter with VES. Similarly, in the present study we also recorded more amphibian and reptile individuals and species with VES than with plot sampling, and most leaf-litter species were sampled by the plot method, whereas treefrogs (Hylidae) were sampled only by VES. Even considering the differences in sampling effort and environmental conditions between Doan's (2003) study and ours, both studies suggest that the VES and plot methods are complementary and thus both methods should be used simultaneously in herpetofaunal inventories.
It is noteworthy that we recorded the presence of the exotic lizard Hemidactylus mabouia in natural areas inside the forest at Morro São João. This species has been introduced in the Americas from Africa via human enterprises and has become established throughout much of the Brazilian territory, though it is usually found associated with human dwellings and anthropically disturbed habitats in general (Carranza and Arnold 2006).The occurrence of H. mabouia inside the forest sharing the habitat with native lizards indicates that this species is not only exotic but is also an invader species in the area of Morro São João.
In conclusion, our results for Morro São João are similar to those of other previous studies (considering the differences in sampling effort) in that they indicate that frogs of the family Brachycephalidae tend to be the most abundant amphibians inhabiting the forest floor leaf litter of New World tropical forests, that densities of South American forest floor amphibians and reptiles tend to be higher or similar to those of the Asian tropics but lower than those of Central America, and that sampling during the crepuscular/nocturnal period may yield the highest values of herpetofaunal richness and abundance in Neotropical rainforests.
The Center for Biodiversity Conservation (CCB) of the Conservation International do Brasil and the Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq) provided financial support. The latter also provided research grants to C.F.D. Rocha (Procs. No. 307 653/2003-0 and 477981/2003-8) and M. Van Sluys (Proc. No. 301401/04-7), and a Post-Doctorate fellowship to M.C. Kiefer (Proc. No. 150353/03-0). Graduate fellowships were granted to M.A. Gomes, V.N.T. Borges-Junior, C.C. Siqueira and D. Nascimento from CNPq, from the Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES) and from the Fundação de Amparo à Pesquisa do Estado do Rio de Janeiro (FAPERJ). The latter also provided additional funding for the study (Proc. No. E-26/100.471/2007) through a grant to C.F.D. Rocha for the "Cientistas do Nosso Estado" program. We also thank C.A.G. Cruz, J.P. Pombal Jr., C. Canedo, B.V.S. Pimenta, E. Izecksohn and M.C.S. Cardoso for helping with the identification of the frog species.
ALLMON WD. 1991. A plot study of forest floor litter frogs, Central Amazon, Brazil. J Trop Ecol 7: 503522. [ Links ]
AZEVEDO-RAMOS C AND GALATTI U. 2002. Patterns of amphibian diversity in Brazilian Amazonia: conservation implications. Biol Conservation 103: 103111. [ Links ]
BARBIERI E AND COE-NETO R 1999. Spatial and temporal variation of rainfall of the East Fluminense coast and Atlantic Serra do Mar, State of Rio de Janeiro, Brazil. In: ABRÃO JJ (Ed), Environmental Geochemistry of Coastal Lagoon Systems, Rio de Janeiro, Brazil. Niterói: UFF/FINEP 6: 4756. [ Links ]
BERNARDE PS AND MACHADO RA. 2000. Riqueza de espécies, ambientes de reprodução e temporada de vocalização da anurofauna em Três Barras do Paraná, Brasil (Amphibia: Anura). Cuad Herpetol 14: 93104. [ Links ]
BRASILEIRO CA, SAWAYA RJ, KIEFER MC AND MARTINS M. 2005. Amphibians of an open Cerrado fragment in southeastern Brazil. Biota Neotrop 5(2): 117. [ Links ]
BROWN WC AND ALCALA AC. 1961. Populations of amphibians and reptiles in the submontane and montane forests of Cuernos de Negros, Phillipines islands. Ecology 42: 628636. [ Links ]
CARRANZA S AND ARNOLD EN. 2006. Systematics, biogeography, and evolution of Hemidactylus geckos (Reptilia: Gekkonidae) elucidated using mitochondrial DNA sequences. Mol Phylogenet Evol 38: 531545. [ Links ]
CECHIN SZ AND MARTINS M. 2000. Eficiência de armadilhas de queda (pitfall traps) em amostragens de anfíbios e répteis no Brasil. Rev Bras Zool 17: 729740. [ Links ]
CONTE CE AND MACHADO RA. 2005. Riqueza de espécies e distribuição espacial e temporal em comunidade de anfíbios anuros (Amphibia: Anura) em uma localidade de Tijucas do Sul, Paraná, Brasil. Rev Bras Zool 22: 940948. [ Links ]
CONTE CE AND ROSSA-FERES D.2006. Diversidade e ocorrência temporal da anurofauna (Amphibia: Anura) em São José dos Pinhais, Paraná, Brasil. Rev Bras Zool 23: 162175. [ Links ]
CORN PS. 1994. Straight-line drift fences and pitfall traps. In: HEYER WR ET AL. (Eds), Measuring and Monitoring Biological Diversity: Standard Methods for Amphibians, Washington DC: Smithsonian Institution Press, p. 109117. [ Links ]
CRUMP ML AND SCOTT JR NJ. 1994. Visual encounter surveys. In: HEYER WR ET AL. (Eds),Measuring and Monitoring Biological Diversity: Standard Methods for Amphibians, Washington DC: Smithsonian Institution Press, p. 8492. [ Links ]
DIXO M AND VERDADE VK. 2006. Leaf litter herpetofauna of the Reserva Florestal de Morro Grande, Cotia (SP). Biota Neotrop 6(2): 119. [ Links ]
DOAN TM. 2003. Which methods are most effective for surveying rain forest herpetofauna? J Herpetol 37: 7281. [ Links ]
DOAN TM AND ARRIAGA WA.2002. Microgeographic variation in species composition of the herpetofaunal communities of Tambopata region, Peru. Biotropica 34: 101117. [ Links ]
DUELLMAN WE. 1999. Patterns of distribution of amphibians. A global perspective. The John Hopkins University Press, Baltimore. 633 p. [ Links ]
ENGE KM. 2001. The pitfalls of pitfall traps. J Herpetol 35: 467478. [ Links ]
FAUTH JE, CROTHER BI AND SLOWINSKI JB. 1989. Elevational patterns of species richness, evenness and abundance of the Costa Rican leaf-litter herpetofauna. Biotropica 21: 178185. [ Links ]
FROST DR ET AL. 2006. The Amphibian Tree of Life. Bull Amer Mus Nat Hist 297: 1370. [ Links ]
GASCON C. 1996. Amphibian litter fauna and river barriers in flooded and non-flooded Amazonian rainforests. Biotropica 28: 136140. [ Links ]
GIARETTA AA, SAWAYA RJ, MACHADO G, ARAÚJO MS, FACURE KG, MEDEIROS HF AND NUNES R. 1997. Diversity and abundance of litter frogs at altitudinal sites at Serra do Japi, Southeastern Brazil. Rev Bras Zool 14: 341346. [ Links ]
GIARETTA AA, FACURE KG, SAWAYA RJ, MEYER JHD AND CHEMIN N. 1999. Diversity and abundance of litter frogs in a montane forest of southeastern Brazil: Seasonal and altitudinal changes. Biotropica 31: 669674. [ Links ]
HADDAD CFB AND SAZIMA I. 1992. Anfíbios anuros da Serra do Japi. In: MORELLATO LPC (Ed), História natural da Serra do Japi: ecologia e preservação de uma área florestal no Sudeste do Brasil. Campinas: Editora da Unicamp/FAPESP, p. 188 211. [ Links ]
HEATWOLE H AND SEXTON OJ. 1966. Herpetofaunal comparisons between two climatic zones in Panama. Amer Mid Nat 75: 4560. [ Links ]
HEYER WR AND BERVEN KA. 1973. Species diversities of herpetofaunal samples from similar microhabitats at two tropical sites. Ecology 54: 642645. [ Links ]
HEYER WR, RAND AS, CRUZ CAG, PEIXOTO OL AND NELSON CE. 1990. Frogs of Boracéia. (São Paulo, SP, Brazil) Arq Zool 31: 231410. [ Links ]
HUANG CY AND HOU PCL. 2004. Density and diversity of litter amphibians in a monsoon forest of southern Taiwan. Zool Stud 43: 795802. [ Links ]
INGER RF. 1980a. Densities of forest-dwelling frogs and lizards in lowland forests of southeast Asia and Central America. Am Nat 115: 761770. [ Links ]
INGER RF. 1980b. Relative abundances of frogs and lizards in forests of southeast Asia. Biotropica 12: 1422. [ Links ]
INGER RF AND COLWELL RK. 1977. Organization of contiguous communities of amphibians and reptiles in Thailand. Ecol Monogr 47: 229253. [ Links ]
JAEGER RG AND INGER RF. 1994. Quadrat sampling. In: HEYER WR ET AL. (Eds), Measuring and Monitoring Biological Diversity: Standard Methods for Amphibians, Washington DC: Smithsonian Institution Press, p. 97102. [ Links ]
LIEBERMAN SS.1986. Ecology of the leaf litter herpetofauna of a Neotropical rainforest: La Selva, Costa Rica. Acta Zool Mex 15: 171. [ Links ]
LLOYD M, INGER RF AND KING W. 1968. On the diversity of reptile and amphibian species in a Bornean rainforest. Am Nat 102: 497515. [ Links ]
LOEBMANN D AND VIEIRA JP. 2005. Relação dos anfíbios do Parque Nacional da Lagoa do Peixe, Rio Grande do Sul, Brasil. Rev Bras Zool 22: 339341. [ Links ]
LYNCH JD AND DUELLMAN WE. 1997. Frogs of the genus Eleutherodactylus inwesternEcuador. Systematics, ecology, and biogeography. Univ Kansas Nat Hist Mus, Spec Publ 23: 1236. [ Links ]
MACHADO RA AND BERNARDE PS. 2002. Anurofauna da Bacia do Rio Tibagi. In: MEDRI ME ET AL. (Eds), A Bacia do Rio Tibagi. Londrina: Edição dos editores, p. 297306. [ Links ]
MACHADO RA, BERNARDE PS, MORATO SAA AND ANJOS L. 1999. Análise comparada da riqueza de anuros entre duas áreas com diferentes estados de conservação no município de Londrina, Paraná, Brasil (Amphibia, Anura). Rev Bras Zool 16: 9971004. [ Links ]
MARQUES OAV AND SAZIMA I. 2004. História natural dos répteis da Estação Ecológica Juréia-Itatins. In: MARQUES OAV ET AL. (Eds), Estação Ecológica Juréia-Itatins. Ambiente físico, flora e fauna. Ribeirão Preto: Holos, p. 257277. [ Links ]
MENIN M. 2005. Padrões de distribuição e abundância de anuros em 64 km2 de floresta de terra-firme na Amazônia Central. Tese de Doutorado. Universidade Federal do Amazonas, 103 p. [ Links ]
POMBAL JP AND GORDO M. 2004. Anfíbios anuros da Juréia. In: MARQUES OAV ET AL. (Eds), Estação Ecológica Juréia-Itatins. Ambiente físico, flora e fauna. Ribeirão Preto: Holos, p. 243256. [ Links ]
ROCHA CFD, VAN SLUYS M, ALVES MAS, BERGALLO HG AND VRCIBRADIC D. 2000. Activity of leaf-litter frogs: when should frogs be sampled? J Herpetol 34: 285287. [ Links ]
ROCHA CFD, VAN SLUYS M, ALVES MAS, BERGALLO HG AND VRCIBRADIC D.2001. Estimates of forest floor litter frog communities: A comparison of two methods. Austral Ecol 26: 1421. [ Links ]
ROCHA CFD, BERGALLO HG, VAN SLUYS M AND ALVES MAS.2003. A biodiversidade nos grandes remanescentes florestais do Estado do Rio de Janeiro e nas restingas da Mata Atlântica. São Paulo: Rima Editora, 160 p. [ Links ]
ROCHA CFD ET AL. 2007. A survey of the leaf-litter frog community from an Atlantic forest area (Reserva Ecológica de Guapiaçu) in Rio de Janeiro State, Brazil, with an estimate of frog densities. Trop Zool 20: 99108. [ Links ]
SAZIMA I AND HADDAD CFB. 1992. Répteis da Serra do Japi: notas sobre história natural. In: MORELLATO LPC (Ed), História natural da Serra do Japi: ecologia e preservação de uma área florestal no Sudeste do Brasil. Campinas: Editora da Unicamp/FAPESP, p. 212237. [ Links ]
SCOTT JR NJ. 1976. The abundance and diversity of the herpetofauna of tropical forest litter. Biotropica 8: 4158. [ Links ]
SCOTT JR NJ. 1982. The herpetofauna of forest litter plots from Cameroon, Africa. In: SCOTT JR NJ (Ed), Herpetological communities: a symposium of the Society for the Study of Amphibians and Reptiles and the Herpetologists' League, August 1977. U.S. Fish and Wildlife Service, Washington DC, p. 145150. [ Links ]
STRÜSSMANN C, VALE MBR, MENEGHINI MH AND MAGNUSSON WE. 1984. Diet and foraging mode of Bufo marinusand Leptodactylus ocellatus. J Herpetol 18: 138146. [ Links ]
TOFT C. 1980. Seasonal variation in populations of Panamanian litter frogs and their prey: a comparison of wetter and drier sites. Oecologia 47: 3438. [ Links ]
TOFT C. 1981. Feeding ecology of Panamanian litter anurans: Patterns in diet and foraging mode. J Herpetol 15: 139144. [ Links ]
TOFT C. 1982. Community structure of litter anurans in a tropical forest, Makokou, Gabon: a preliminary analysis in the minor dry season. Rev Ecol-Terre Vie 36: 223232. [ Links ]
VASUDEVAN K, KUMAR A AND CHELLAM R. 2001. Structure and composition of rainforest floor amphibian communities in Kalakad-Mundanthurai Tiger Reserve. Curr Sci 80: 406412. [ Links ]
VONESH JR. 2001. Patterns of richness and abundance in a tropical African leaf-litter herpetofauna. Biotropica 33: 502510. [ Links ]
WATANABE S, NAKANISHI N AND IZAWA M. 2005. Seasonal abundance in the floor-dwelling frog fauna on Iriomote Island of the Ryuku Archipelago, Japan. J Trop Ecol 21: 8591. [ Links ]
Manuscript received on April 2, 2005; accepted for publication on November 11, 2007; presented by ALEXANDER W.A. KELLNER