Acessibilidade / Reportar erro

Diversity patterns, research trends and mismatches of the investigative efforts to amphibian conservation in Brazil

Abstracts

The number of papers on biology of amphibians has increased in the recent years. A detailed overview of the publications on amphibians can be very useful in assessing the status of our knowledge about this taxonomic group. Due to the large number of articles published, we aimed to assess the scientific contribution of herpetological researches carried out between the years 2001 and 2010 on Brazilian amphibians, considering the diversity patterns, the threats and the research topics that have been published most often. We applied scientometric attention indexes in the reviewed studies from seven scientific databases. To examine the relationship between the numbers of species recorded locally and regionally at different spatial scales, we used an additive partitioning of diversity in three hierarchical levels (i.e., states, geographic regions and biomes). We evaluated 892 articles and 914 species, which showed that 65 % of the total diversity of Brazilian amphibian species was represented by the beta diversity among the biomes. We identified many differences in the allocation of research efforts for taxonomic groups, threats categories, geographic regions, and research topics, highlighting the main research trends conducted and the priority themes for investigation of further papers on Brazilian amphibians.

amphibians; scientometry; attention index; additive diversity partitioning; temporal trend


O número de artigos sobre biologia de anfíbios tem aumentado nos últimos anos. Um panorama detalhado destas publicações pode ser bastante útil na avaliação do estado do nosso conhecimento sobre este grupo taxonômico. Em função do grande número de artigos publicados no Brasil a cada ano, nós avaliamos a contribuição das pesquisas herpetológicas realizadas entre os anos de 2001 e 2010 no que diz respeito aos anfíbios brasileiros, consideirando os padrões de diversidade, as ameaças e os temas de investigação que mais têm sido publicados. Índices de atenção cienciométricos foram aplicados nos estudos analisados a partir de sete bancos de dados. Para ponderar a relação entre o número de espécies registradas localmente e regionalmente em diferentes escalas espaciais, nós utilizamos análises de partição aditiva da diversidade em três níveis hierárquicos (i.e., estados, regiões geográficas e biomas). Nós avaliamos 892 artigos e 914 espécies, o que mostrou que 65 % do total da diversidade de espécies de anfíbios brasileiros foi representada pela beta diversidade entre os biomas. Nós identificamos muitas diferenças na alocação de esforços de pesquisa para grupos taxonômicos, categorias ameaças, regiões geográficas e tópicos de pesquisa, destacando as principais tendências de investigação desenvolvidas e os temas prioritários para a investigação de novos trabalhos sobre os anfíbios brasileiros.

anfíbios; cienciometria; índice de atenção; partição aditiva de diversidade; tendência temporal


INTRODUCTION

The causes of amphibian populations declining vary from region to region and can show synergistic interactions between more than one threat factor (Davidson and Knapp 2007Davidson C and Knapp RA. 2007. Multiple stressors and amphibian declines: dual impacts of pesticides and fish on yellow-legged frogs. Ecol Appl 17: 587-597., Blaustein et al. 2010Blaustein AR, Walls SC, Bancroft BA, Lawler JJ, Searle CL and Gervasi SS. 2010. Direct and Indirect Effects of Climate Change on Amphibian Populations. Diversity 2: 281-313.). However, habitat alteration accounts for more declines than any other factor (e.g., Beebee and Griffiths 2005Beebee TJC and Griffiths RA. 2005. The amphibian decline crisis: a watershed in conservation biology? Biol Conserv 125: 271-285., IUCN et al. 2006, Halliday 2008Halliday TR. 2008. Why amphibians are important. Int Zoo Yearb 42: 7-14., Becker et al. 2010Becker CG, Fonseca CR, Haddad CFB and Prado PI. 2010. Habitat Split as a Cause of Local Population Declines of Amphibians with Aquatic Larvae. Conserv Biol 24: 287-294.).

There is a substantial amount of evidence of amphibian declines around the world (Stuart et al. 2004Stuart SN, Chanson JS, Cox NA, Young BE, Rodrigues ASL, Fischman DL and Waller RW. 2004. Status and trends of amphibian declines and extinctions worldwide. Science 306: 1783-1786.). Yet, strategies to solve this problem have been developed mainly by scientists from the United States, Western Europe and Australia (Houlahan et al. 2000Houlahan JE, Findlay CS, Schmidt BR, Meyer AH and Kuzmin SL. 2000. Quantitative evidence for global amphibian population declines. Nature 404: 752-755., Young et al. 2001, Brito 2008Brito D. 2008. Amphibian conservation: Are we on the right track? Biol Conserv 141: 2912-2917.). Some regions have developed strategies for studying the problem of amphibian declines and have amassed useful information about potential causes (e.g., Europe, Araújo et al. 2006Araújo MB, Thuiller W and Pearson RG. 2006. Climate warming and the decline of amphibians and reptiles in Europe. J Biogeogr 33: 1712-1728., Australia, Hero et al. 2006, United States, Adams et al. 2013). There is also evidence for amphibian declines in different regions in Brazil (e.g., Heyer et al. 1988Heyer WR, Rand AS, Cruz CAG and Peixoto OL. 1988. Decimations, extinctions, and colonizations of frog populations in southeast Brazil and their evolutionary implications. Biotropica 20: 230-235., Weygoldt 1989Weygoldt P. 1989. Changes in the composition of mountainstream frog communities in the Atlantic mountains of Brazil: frogs as indicators of environmental deteriorations? Stud Neotrop Fauna Environ 243: 249-255., Bertoluci and Heyer 1995Bertoluci J and Heyer RW. 1995. Boracéia Update. Froglog: Newsletter of the IUCN/SSC Amphibian Specialist Group 14: 2-3., Guix et al. 1998Guix JC, Montori A, Llorente GA, Carretero MA and Santos X. 1998. Natural history and conservation of bufonids in four Atlantic rainforest areas of Southerastern Brazil. Herpetol Nat Hist 6: 1-12., Pombal and Haddad 1999Pombal Jr JP and Haddad CFB. 1999. Frogs of the genus Paratelmatobius (Anura: Leptodactylidae) with descriptions of two new species. Copeia 4: 1014-1026., Izecksohn and Carvalho-e-Silva 2001Izecksohn E and Carvalho-e-Silva SP. 2001. Anfíbios do município do Rio de Janeiro, 1a ed., Rio de Janeiro: Editora UFRJ, 148 p., Eterovick et al. 2005Eterovick PC, Carnaval ACOQ, Borges-Nojosa DM, Silvano DL, Segalla MV and Sazima I. 2005. An overview of amphibian declines in Brazil with new records from Serra do Cipó, State of Minas Gerais. Biotropica 37: 166-179.). As in other Latin American countries, understanding and preventing the decline of populations of amphibians is hampered by a lack of information and appropriate governmental policies to address this issue (Juncá 2001Juncá FA. 2001. Declínio mundial das populações de anfíbios. Sitientibus Sér Ci Biol 1: 84-87., Silvano and Segalla 2005Silvano DL and Segalla MV. 2005. Conservation of Brazilian Amphibians. Conserv Biol 19: 653-658.).

Compiling data about species distribution ranges, is an important step in planning conservation actions (Hurlbert and Jetz 2007Hurlbert AH and Jetz W. 2007. Species richness, hotspots, and the scale dependence of range maps in ecology and conservation. Proc Natl Acad Sci USA 104: 13384-13389.), which has been shown in recent studies on Brazilian amphibian communities (e.g., Trindade-Filho et al. 2012Trindade-Filho J, Carvalho RA, Brito D and Loyola RD. 2012. How does the inclusion of Data Deficient species change conservation priorities for amphibians in the Atlantic Forest? Biodivers Conserv 21: 2709-2718., Verdade et al. 2012, Morais et al. 2013Morais AR, Siqueira MN, Lemes P, Maciel NM, De Marco Jr P and Brito D. 2013. Unraveling the conservation status of Data Deficient species. Biol Conserv 166: 98-102.). The greatest diversity of amphibians in the world is recorded in Brazil, with 946 described species (Segalla et al. 2012Segalla MV, Caramaschi U, Cruz CAG, Garcia PCA, Grant T, Haddad CFB and Langone J. 2012. Brazilian amphibians – List of species, Sociedade Brasileira de Herpetologia. Available at: http://www.sbherpetologia.org.br.
http://www.sbherpetologia.org.br...
). However, 33 amphibian species distributed in Brazil are listed in the IUCN Red List, as being 17 vulnerable, 7 endangered, and 9 critically endangered (IUCN 2012IUCN. 2012. IUCN Red List of Threatened Species, version 2012.1. Available at: http://www.iucnredlist.org.
http://www.iucnredlist.org...
). Despite this, the knowledge generated about biogeography and taxonomy of Brazilian amphibians is still fairly recent, because several species are often revalidated, and mainly because every year new species have been discovered (Silvano and Segalla 2005Silvano DL and Segalla MV. 2005. Conservation of Brazilian Amphibians. Conserv Biol 19: 653-658., Toledo and Batista 2012Toledo LF and Batista RF. 2012. Integrative Study of Brazilian Anurans: Geographic Distribution, Size, Environment, Taxonomy, and Conservation. Biotropica 44: 785-792.).

Even though the number of publications dedicated to the conservation of amphibians has increased in recent years, most conservation strategies for the communities of amphibians are still directed at areas of low biodiversity and with non-endangered species (Brito 2008Brito D. 2008. Amphibian conservation: Are we on the right track? Biol Conserv 141: 2912-2917.). An analysis of the national and international conservation measures presented in journals published in recent years can indirectly provide an index of attention to a given taxonomic group (Brito 2008Brito D. 2008. Amphibian conservation: Are we on the right track? Biol Conserv 141: 2912-2917.). Therefore, an overview of the recent publications on amphibians in Brazil can be considered a good sample of the current research conducted on the conservation status of these species.

In this context, we aimed to evaluate the state of knowledge of the herpetological surveys conducted over the last decade on the Brazilian amphibians. On the assumption that the number of publications can be an adequate measurement of scientific productivity, we tested the following hypotheses: (1) there are large differences between the numbers of articles published in relation to taxonomic groups and threat categories, (2) the allocation of research efforts is associated with the species richness of the Brazilian biomes, (3) there is a progressive increase in the number of articles published each year on the Brazilian amphibians, (4) Brazil is the most frequent country among the affiliation of the authors of the papers published about Brazilian amphibians, and (5) there is a temporal variation in the research topics among the articles on Brazilian amphibians. Based on the data assessed, we established diversity patterns, attention indexes and the main research trends of the published studies, thus predicting the priority themes for investigation of further studies.

MATERIALS AND METHODS

Data Acquisition

We used scientometric techniques and multivariate analyses from the collection of information relating to the publications of seven international databases (Web of Science, ScienceDirect, Scopus, Wiley Online Library, BioOne, Scielo, and DOAJ). In these analyses, we only included papers published between 2001 and 2010 that featured the terms “Amphibia*”, “Anura*”, “Caudata”, and/or “Gymnophiona”, along with the word “Brasil” or “Brazil” in their title, abstract, or keywords.

For each selected study, we identified the year of publication, the nationality of the authors, the place of the work, the keywords, the main research topic, the name of the journal and its impact factor, the population trend and the threat category of the species mentioned, according to the IUCN Red List of Threatened Species categories (i.e., Critically Endangered – CR, Endangered – EN, and Vulnerable – VU, IUCN 2012IUCN. 2012. IUCN Red List of Threatened Species, version 2012.1. Available at: http://www.iucnredlist.org.
http://www.iucnredlist.org...
). Species classified as Near Threatened – NT were excluded from the analysis of threat category, because we adopted only the criteria prepared by the IUCN Species Survival Commission (IUCN 2001IUCN. 2001. IUCN Red List Categories and Criteria, version 3.1. Gland, Switzerland and Cambridge, U.K.: Species Survival Commission, World Conservation Union, 32 p.), which refers to term “Threatened” only in the categories CR, EN and VU.

Data Analysis

In accordance to Brito (2008)Brito D. 2008. Amphibian conservation: Are we on the right track? Biol Conserv 141: 2912-2917., we generated three scientometric attention indexes among the studies analyzed. A taxonomic attention index (AI-taxon) was obtained for the families of amphibians presented in each study, dividing the number of articles related to each family by the number of species from the same family, thus providing a general framework of attention to the families of Brazilian amphibians. A threat attention index (AI-threat) was obtained dividing the number of articles dedicated to threatened species by the number of threatened species in each family evaluated. A biogeographic attention index (AI-biogeog) was calculated for the different Brazilian biomes, dividing the number of articles related to each biome by the number of amphibian species recorded per biome. These data were obtained according to the information from articles assessed and from reviews of distribution maps from the IUCN database (IUCN 2012IUCN. 2012. IUCN Red List of Threatened Species, version 2012.1. Available at: http://www.iucnredlist.org.
http://www.iucnredlist.org...
). In addition, we applied a simple linear regression analysis among the number of articles published and the number of species in each group assessed, using the software Ecosim 7.72 (Gotelli and Entsminger 2005Gotelli NJ and Entsminger GL. 2005. EcoSim: Null models software for ecology, version 7.72, Acquired Intelligence Inc. and Kesey-Bear. Avalaible at: http://homepages.together.net/∼gentsmin/ecosim.htm.
http://homepages.together.net/...
). The classification of biomes follows that of the Brazilian Institute of Geography and Statistics (IBGE 2004IBGE. 2004. Mapa da vegetação do Brasil e Mapa de Biomas do Brasil. Available at: http://www.ibge.gov.br.
http://www.ibge.gov.br...
), and the nomenclature of amphibian species follows Frost (2014)Frost DR. 2014. Amphibian Species of the World: an online reference, version 6.0. Avalaible at: http://research.amnh.org/vz/herpetology/amphibia/.
http://research.amnh.org/vz/herpetology/...
.

We analyzed the critical mass corresponding to the geographic regions of each biome from Brazil from the database of the National Council for Scientific and Technological Development (CNPq 2010CNPq. 2010. Painel Lattes: Distribuição Geográfica. Conselho Nacional de Desenvolvimento Científico e Tecnológico. Available at: http://lattes.cnpq.br/painelLattes/mapa.
http://lattes.cnpq.br/painelLattes/mapa...
). We used regression analysis to explore the relationships between the numbers of researchers that have the term “amphibia” in their curriculums with the numbers of published articles on amphibians in each region considered. This analysis was generated by the software Ecosim 7.72 (Gotelli and Entsminger 2005Gotelli NJ and Entsminger GL. 2005. EcoSim: Null models software for ecology, version 7.72, Acquired Intelligence Inc. and Kesey-Bear. Avalaible at: http://homepages.together.net/∼gentsmin/ecosim.htm.
http://homepages.together.net/...
), providing correlation data and probability of significance of the variables analyzed, according to a significance level of 5%.

The compilation of species richness assessed was obtained through a joint evaluation of the IUCN database (IUCN 2012IUCN. 2012. IUCN Red List of Threatened Species, version 2012.1. Available at: http://www.iucnredlist.org.
http://www.iucnredlist.org...
) and the papers considered in this study. To examine the relationships between the numbers of species recorded locally and regionally at different spatial scales, we used an additive partitioning of diversity in three hierarchical levels (i.e., states, geographic regions and biomes). For each spatial level a value of alpha and beta diversity was associated. Thus, α1 and β1 represented the alpha and beta diversity in the lower level (i.e., states), so that β2 and β3 corresponded to beta diversity in the two subsequent levels (i.e., geographical regions and biomes). The statistical significance of each component was measured using a null model, as proposed by Crist et al. (2003)Crist TO, Veech JA, Gering JC and Summerville KS. 2003. Partitioning species diversity across landscapes and regions: A hierarchical analysis of α, β, and γ diversity. Am Nat 162: 734-743.. All analyses for the additive partitioning of diversity were performed by the R software (R Development Core Team 2009R Development Core Team. 2009. R: A language and environment for statistical computing. Vienna: R Foundation for Statistical Computing. Available at: http://www.R-project.org.
http://www.R-project.org...
), using the algorithms “boot” and “mass” through the adipart function in the R package vegan (Oksanen et al. 2009Oksanen J, Kindt R, Legendre P, O'Hara RB, Gavin L, Simpson GL, Solymos P, Stevens MH and Wagner H. 2009. Vegan: Community Ecology Package. R package version 1.15–4. Available at: http://CRAN.R-project.org/package=vegan.
http://CRAN.R-project.org/package=vegan...
).

To assess the similarity in the species composition among the Brazilian biomes, we used a hierarchical cluster analysis based on the Sorensen coefficient (Magurran 2004Magurran AE. 2004. Measuring biological diversity, 2nd ed., Oxford: Blackwell Publishing, 70 p.), reflecting the biogeographic patterns in the structure of amphibian communities in Brazil. This analysis was conducted through the unweighted pair group with arithmetic mean method (UPGMA), performed by the software MVSP (Kovach 2004Kovach WL. 2004. MVSP: Multivariate Statistical Package, version 3.13m. Available at: http://www.kovcomp.co.uk/mvsp/.
http://www.kovcomp.co.uk/mvsp/...
).

From the number of papers published per year it was possible to estimate the temporal trends relative to the number of studies on amphibians in Brazil. To assess the contribution of new species to the advances in the basic taxonomic knowledge of the Brazilian amphibians, we superimposed the number of new species recorded each year on the total number of published articles.

To provide the number of published articles according to each research topic studied, we classified the assessed papers into 15 categories of subjects, so that each paper was placed under only one category (i.e., Taxonomy and systematics, Behavioral ecology, Community ecology, Trophic ecology, Reproductive biology, Morphology, Geographic distribution, Conservation biology, Genetic, Phylogeny, Species inventories, Parasitology, Pharmacology, Population ecology, or Physiology).

RESULTS

We found 892 articles focusing on amphibian species from Brazil in the period analyzed (Table I). In total, we assessed 914 species of amphibians distributed in Brazil. The AI-taxon (taxon-based attention index) showed that Ranidae was the family that received most of the attention among the researchers, unlike the Microhylidae family, which was less studied according to this index (Table I). In general, the values presented by the AI-taxon were low, mainly due to the relatively small number of articles published in relation to the large number of species of each family assessed, although there is a high correlation between these numbers (r2 = 0.97, p < 0.01). For the threatened species, there was not a strong correlation between the number of articles published and the number of species in each family (r2 = 0.54, p = 0.06), where the AI-threat was greater to Leptodactylidae and smaller to Bufonidae. Nevertheless, about 16% of published articles focused on the study of threatened species, which corresponds to only 3.6% of the pool of species assessed (see Table I).

TABLE I
Total number of species, threatened species, published articles, published articles dedicated to threatened species, AI-taxon and AI-threat for each amphibian family recorded in Brazil.

Most of the species cited in the assessed articles showed unknown population trends. Although 804 species of amphibians with geographical distribution in Brazil have been cited in articles published between 2001 and 2010, only 0.6% had an increasing population trend (Table II). However, about 25% of species assessed in different threat categories showed a declining population trend, among which only 15% was effectively considered as threatened (i.e., species categorized as VU, EN or CR). The high proportion of threatened species with declining population trends indicates that the real number of threatened amphibian species in Brazil may be higher than that estimated by the IUCN criteria (see Table II).

TABLE II
Relative number of species listed by threat category and population trend (N = 804), according to the IUCN Red List categories (i.e., NE: Not Evaluated, LC: Least Concern, DD: Data Deficient, NT: Near Threatened, VU: Vulnerable, EN: Endangered, CR: Critically endangered, EX: Extinct).

The AI-biogeog indicated that the biomes that received the most attention from the researchers were the Cerrado and the Atlantic Forest (Fig. 1). However, the Cerrado presented a number of species much smaller than the Atlantic Forest (i.e., 188 compared with 504 species), which explains the difference between the values stated for both biomes (Fig. 1). In addition, this fact can also be explained by the critical mass corresponding to the regions of each biome. There was a high correlation between the relative number of researchers who presented the term “amphibia” on their curriculums with the number of articles published on amphibians in each geographic region of Brazil (r2 = 0.97, p = 0.04). Therefore, the profile of the values of the AI-biogeog was low when compared to the other biomes evaluated (Fig. 1).

Figure 1
Biogeographic attention index (black dots) and total number of amphibian species recorded (white dots) for each biome in Brazil.

The additive partitioning of diversity indicated that the proportion of the data observed for the alpha and beta diversity in the three scales sampled (i.e., states, geographic regions and biomes) basically did not differ from that obtained by random chance (Fig. 2). However, the null model showed a small increase of the expected diversity among biomes when compared to the observed diversity in this scale. The remaining values expected in a random distribution of individuals were lower than those shown by the observed diversity (Fig. 2). The values of the partitioning of diversity showed an apparent complementarity among the scales sampled. Nevertheless, the results showed that 65% of the total species diversity of Brazilian amphibians was represented by the beta diversity among the biomes of the country (Fig. 2).

Figure 2
Additive partitioning of diversity of amphibians recorded in Brazil in three spatial scales. The values on the right refer to the proportion in which the number of times the value expected by the null model (Exp) was higher than that value observed (Obs). The percentage values correspond to the proportion of the number of species recorded in each spatial level, being α1 and β1 the alpha and beta diversity in the lowest level (i.e., states), and β2 and β3, the beta diversity in the two subsequent levels (i.e., geographical regions and biomes).

The biogeographic patterns in the structure of amphibian communities from Brazil reflected by the proportion of similarity of species among the biomes were highly variable, even for neighboring biomes (Fig. 3). The greatest proportion of similarity, indicated by Sorensen's coefficient, was between the Cerrado and the Caatinga, with 49% of similarity. In general, the values obtained were low, not exceeding 50% of similarity, implying a high disparity in the amphibian species composition among the different Brazilian biomes (Fig. 3), which confirms its high beta diversity pattern.

Figure 3
Dendrogram of similarity of amphibian species recorded among the Brazilian biomes.

The increase in the number of studies conducted on amphibians between 2001 and 2010 allowed an addition of 132 new species in Brazil (Fig. 4), among which 60% are distributed in Atlantic Forest, 22% in Cerrado, 12% in Amazon, 3% in Caatinga, 2 % in Pantanal and 1% in Pampa. The affiliation of the authors of the articles analyzed indicated a total of 19 countries that contributed to the publications of the last decade (Fig. 5), but were mostly conducted through partnerships with Brazilian researchers, reflecting the enormous diversity of species found in Brazil and its broad potential for new discoveries regarding the biology of Neotropical amphibians. We identified four languages among the articles assessed, corresponding to 763 publications in English, 127 in Portuguese, one in German and one in Spanish.

Figure 4
Number of published articles on amphibians (bars) and number of new species discovered (line) between 2001 and 2010 in Brazil.

Figure 5
Total number of articles published between 2001 and 2010 on amphibians from Brazil (N = 892) in relation to the country of affiliation of the authors.

The articles that presented new data on geographic distribution of species showed 64 new records of the Brazilian amphibians (Fig. 6). However, taxonomy and systematics were the research topics preferred by the authors considered, representing about 20% of studies, indicating a progressive increase of articles related to the taxonomic reviews and descriptions of new species over the last decade. In contrast, physiology, population ecology, and pharmacology, were the topics least investigated, with about 3% of studies on each topic (Fig. 6).

Figure 6
Total number of articles published between 2001 and 2010 on amphibians from Brazil (N = 892) according to their respective research topics.

DISCUSSION

The increasing number of publications on amphibians from Brazil can be regarded as a result of the progressive increase in the number of researchers interested in Brazilian herpetology. Important trends and biases were observed in relation to the study of Brazilian amphibians. The results showed that there are many differences in the allocation of research efforts for different taxonomic groups and geographic regions, as well as for some research topics.

Some unexpected trends were observed in the attention given to different families of amphibians. The Ranidae family, which is represented by only two species in Brazil, one having been introduced (Lithobates catesbeianus) and the other one being native (L. palmipes), received the highest values on the AI-taxon, possibly because of their economic values. However, the American bullfrog (L. catesbeianus) is considered one of the most harmful invasive species to native amphibian communities (Lowe et al. 2000Lowe S, Browne M, Boudjelas S and De Poorter M. 2000. 100 of the world's worst invasive alien species - A selection from the global invasive species database. Auckland: School of Geography and Environmental Sciences, University of Auckland, 12 p., Giovanelli et al. 2008Giovanelli JGR, Haddad CFB and Alexandrino J. 2008. Predicting the potential distribution of the alien invasive American bullfrog (Lithobates catesbeianus) in Brazil. Biol Invas 10: 585-590.). In Brazil, introductions of this species have occurred since 1930 in associations with the advancement of aquaculture (Fontanello and Ferreira 2007Fontanello D and Ferreira CM. 2007. Histórico da Ranicultura Nacional. Available at: http://www.aquicultura.br/historico.htm.
http://www.aquicultura.br/historico.htm...
). In the last decade, the species was recorded in the field throughout various localities of south, central and southeast of the country (Both et al. 2011Both C, Lingnau R, Santos-Jr A, Madalozzo B, Lima LP and Grant T. 2011. Widespread Occurrence of the American Bullfrog, Lithobates catesbeianus (Shaw, 1802) (Anura: Ranidae), in Brazil. South Am J Herpetol 6: 127-134.), especially in large areas of the Atlantic Forest (Dixo and Verdade 2006Dixo M and Verdade VK. 2006. Leaf litter herpetofauna of the Reserva Florestal de Morro Grande, Cotia (SP). Biota Neotrop 6: 1-20., Conte and Rossa-Feres 2006Conte CE and Rossa-Feres DC. 2006. Diversidade e ocorrência temporal da anurofauna (Amphibia, Anura) em São José dos Pinhais, Paraná, Brasil. Rev Bras Zool 23: 162-175., Both et al. 2011Both C, Lingnau R, Santos-Jr A, Madalozzo B, Lima LP and Grant T. 2011. Widespread Occurrence of the American Bullfrog, Lithobates catesbeianus (Shaw, 1802) (Anura: Ranidae), in Brazil. South Am J Herpetol 6: 127-134.). It remains unknown to what extent this species contributes to the decline of population of some Brazilian amphibians (Young et al. 2001, Silvano and Segalla 2005Silvano DL and Segalla MV. 2005. Conservation of Brazilian Amphibians. Conserv Biol 19: 653-658.). However, already there are some studies about the impacts of the American bullfrog in Brazil, such as competition for microhabitat, changes in acoustic niches, and imbalance among predator-prey relationships in native species (e.g., Silva et al. 2011Silva ET, Ribeiro-Filho OP and Feio RN. 2011. Predation of native anurans by invasive bullfrogs in southeastern Brazil: spatial variation and effect of microhabitat use by prey. South Am J Herpetol 6: 1-10., Boelter et al. 2012Boelter RA, Kaefer IL, Both C and Cechin SZ. 2012. Invasive bullfrogs as predators in a Neotropical assemblage: What frog species do they eat? Anim Biol 62: 397-408., Both and Grant 2012Both C and Grant T. 2012. Biological invasions and the acoustic niche: the effect of bullfrog calls on the acoustic signals of white-banded tree frogs. Biol Lett 8: 714-716.).

More than 2,000 amphibian species are listed as threatened by extinction, to the extent that amphibians are the most threatened vertebrate group in the world (Stuart et al. 2004Stuart SN, Chanson JS, Cox NA, Young BE, Rodrigues ASL, Fischman DL and Waller RW. 2004. Status and trends of amphibian declines and extinctions worldwide. Science 306: 1783-1786.). Although many reductions and extinctions of amphibians have occurred due to the habitat loss, some unidentified processes still threaten 48% of amphibian species arround the world (Stuart et al. 2004Stuart SN, Chanson JS, Cox NA, Young BE, Rodrigues ASL, Fischman DL and Waller RW. 2004. Status and trends of amphibian declines and extinctions worldwide. Science 306: 1783-1786.). This lack of knowledge seriously impairs our ability to plan conservation actions to reverse these trends (Brito 2008Brito D. 2008. Amphibian conservation: Are we on the right track? Biol Conserv 141: 2912-2917.). Our results showed that the level of threat to amphibians in Brazil still remains underestimated due to the lack of knowledge on approximately 25% of the species, which are classified as “Data Deficient” (DD). This trend remained the same when compared to a global scale in relation to amphibians worldwide (IUCN 2012IUCN. 2012. IUCN Red List of Threatened Species, version 2012.1. Available at: http://www.iucnredlist.org.
http://www.iucnredlist.org...
). According to the Global Amphibian Assessment (IUCN et al. 2006), the real number of threatened and extinct species of amphibians can be much larger than currently acknowledged.

According to the relationship between the numbers of species per area, the Atlantic Forest is considered the leader biome in amphibian diversity in Brazil, accounting for about 50% of the total richness of amphibian species of the country (Conservation International et al. 2000, Silvano and Segalla 2005Silvano DL and Segalla MV. 2005. Conservation of Brazilian Amphibians. Conserv Biol 19: 653-658., Haddad et al. 2008Haddad CFB, Toledo LF and Prado C. 2008. Anfíbios da Mata Atlântica, 1a ed., São Paulo: Editora Neotropica, 244 p.). However, the high concentration of amphibian researchers in the southeastern region seems to be the main reason for the high concentration of studies focused in the Atlantic Forest, which can also be applied to the Cerrado. Unlike what occurs in the Brazilian Amazon, where information on the diversity of amphibians is fragmented and not readily available in the scientific literature (Azevedo-Ramos and Galatti 2002Azevedo-Ramos C and Galatti U. 2002. Patterns of amphibian diversity in Brazilian Amazônia: conservation implications. Biol Conserv 103: 103-111.). This lack of information is especially problematic for salamanders and caecilians (Gower and Wilkinson 2005Gower DJ and Wilkinson M. 2005. Conservation Biology of Caecilian Amphibians. Conserv Biol 19: 45-55.). Moreover, the taxonomic uncertainty applied to various groups of Amazonian amphibians makes this region worthy of further attention among the researchers (Caldwell 1996Caldwell JP. 1996. Diversity of Amazonian anurans: the role of systematics and phylogeny in identifying macroecological and evolutionary patterns. In: GIBSON AC (Ed), Neotropical Biodiversity and Conservation. Los Angeles: University of California, Mildred E. Mathias Botanical Garden, USA, p. 73-88., Azevedo-Ramos and Galatti 2002Azevedo-Ramos C and Galatti U. 2002. Patterns of amphibian diversity in Brazilian Amazônia: conservation implications. Biol Conserv 103: 103-111.). To improve this condition, some research groups need to acquire financial funds for applied studies aimed at understanding the basic knowledge of Amazonian herpetofauna, which despite having high species richness, still remains poorly studied.

The increased concern of researchers with the Brazilian amphibians in the last decade was highlighted by the difference among the numbers of published articles over the years 2001 and 2010, which presented 28 and 177 papers respectively. This probably occurred due to amphibians having been widely promoted as indicators of environmental quality (Lebboroni et al. 2006Lebboroni M, Ricchiardino G, Bellavita M and Chelazzi G. 2006. Potential use of anurans as indicators of biological quality in upstreams of central Italy. Amph-Rept 27: 73-79., Sewell and Griffiths 2009Sewell D and Griffiths RA. 2009. Can a single amphibian species be a good biodiversity indicator? Diversity 1: 102-117.), which provides them with a special attention to conservation programs. In addition, amphibians are important components of many types of ecosystems, playing a key role in the dynamics between predators and prey (Blaustein et al. 1994Blaustein AR, Wake DB and Sousa WP. 1994. Amphibian declines: judging stability, persistence, and susceptibility of populations to local and global extinctions. Conserv Biol 8: 60-71.). However, in comparison with other groups of vertebrates, such as birds and mammals, amphibians are still largely unknown (Brito 2008Brito D. 2008. Amphibian conservation: Are we on the right track? Biol Conserv 141: 2912-2917., Halliday 2008Halliday TR. 2008. Why amphibians are important. Int Zoo Yearb 42: 7-14.). This ignorance about amphibians is reflected in the high rates at which new species are being discovered and described. Birds and mammals have been considered traditionally more charismatic than amphibians (Brito 2008Brito D. 2008. Amphibian conservation: Are we on the right track? Biol Conserv 141: 2912-2917.). Thus, there is a need to develop creative approaches to value this group. For example, such approaches could consist in promoting some amphibian species as charismatic through research projects linked to the media.

It is of paramount importance for the Brazilian herpetologists to publish the results of their research, because most of the surveys conducted in the tropics are not made by local scientists, but mainly by researchers from high-income countries (Fazey et al. 2005Fazey I, Fischer J and Lindenmayer DB. 2005. Who does all the research in conservation biology? Biodiv Conserv 14: 917-934.). A review conducted on three of the most important international conservation biology journals (i.e., Conservation Biology, Biological Conservation, and Biodiversity and Conservation) showed that 28% of studies published were from lower-income countries and only 15% of all assessed articles had primary authors from these nations (Fazey et al. 2005Fazey I, Fischer J and Lindenmayer DB. 2005. Who does all the research in conservation biology? Biodiv Conserv 14: 917-934.). However, our results about the affiliation of the authors showed that most of the published studies on amphibians from Brazil in the last decade were conducted by local researchers (i.e., 85% of the total published articles). This high number of publications by Brazilian authors may have been influenced by the growth of local investment in research infrastructure background in the recent years. According to King (2004)King DA. 2004. The scientific impact of nations. Nature 430: 311-316., one measure of a nation's knowledge base is its output of PhD students, which is directly associated with the the growth of infrastructure investment. The science budget allocated in Brazil rose from US$575 million in 2002 to over US$3.3 billion in 2010 (Massarani 2013Massarani L. 2013. Brazil's science investment reaches record high. Nature News (01 August 2013): 13495.). Consequently, the number of PhD researchers trained in Brazil rose from 26,000 in 2001 to approximately 53,000 in 2010, thus only in 2010, more than 12,000 researchers were titrated as PhD in Brazilian postgraduate programs (MCT 2010MCT. 2010. Plano de ação em ciência, tecnologia e inovação: Principais resultados e avanços, Brasília: Ministério da Ciência e Tecnologia, 168 p.).

Even though there is an constant increase in the number of PhD researchers in Brazil, this is still not enough to solve the biodiversity conservation demand in the country (Lawler et al. 2006), which is even more relevant in the case of amphibians (Urbina-Cardona 2008Urbina-Cardona JN. 2008. Conservation of Neotropical herpetofauna: research trends and challenges. Trop Conserv Sci 1: 359-375.). Brazilian specialists agree that local amphibian species richness, taxonomy, geographic ranges, natural history and population status are vastly understudied in our country (Pimenta et al. 2005Pimenta BVS, Haddad CFB, Nascimento LB, Cruz CAG and Pombal Jr JP. 2005. Comment on “status and trends of amphibian declines and extinctions worldwide”. Science 309: 5743., Silvano and Segalla 2005Silvano DL and Segalla MV. 2005. Conservation of Brazilian Amphibians. Conserv Biol 19: 653-658., Verdade et al. 2012). Our results showed that research biases were detected for amphibian species that are more common and more widely distributed, as well as the trends observed at a global scale by Brito (2008)Brito D. 2008. Amphibian conservation: Are we on the right track? Biol Conserv 141: 2912-2917., which showed that most amphibian conservation actions are directed at areas with non-threatened species. According to Schiesari et al. (2007)Schiesari L, Grillitsch B and Grillitsch H. 2007. Biogeographic biases in research and their consequences for linking amphibian declines to pollution. Conserv Biol 21: 465-471., these biases when present, may reflect important consequences for the amphibian conservation in general or declining populations in particular. Particularly for amphibians, the intensity of threat may be inversely related to the abundance or geographic range of a species (Schiesari et al. 2007Schiesari L, Grillitsch B and Grillitsch H. 2007. Biogeographic biases in research and their consequences for linking amphibian declines to pollution. Conserv Biol 21: 465-471.), so that many cases associated with declining populations were recorded at long distances from the research centers or in areas with little investment in science and technology (King 2004King DA. 2004. The scientific impact of nations. Nature 430: 311-316.).

Amphibians are declining practically the entire world, but the lack of long-term regional data hinders the identification of their possible causes, thus hampering the establishment of conservation efforts (Stuart et al. 2004Stuart SN, Chanson JS, Cox NA, Young BE, Rodrigues ASL, Fischman DL and Waller RW. 2004. Status and trends of amphibian declines and extinctions worldwide. Science 306: 1783-1786., Nystrom et al. 2007Nystrom P, Hansson J, Mansson J, Sundstedt M, Reslow C and Brostrom A. 2007. A documented amphibian decline over 40 years: Possible causes and implications for species recovery. Biol Conserv 138: 399-411.). Although the number of articles devoted to amphibians in Brazil has increased in recent years, there is still a great need for an increase in the number of articles focusing on the conservation of amphibians, especially with regards to threatened species, population dynamics and interspecific relations. Even in fragmented landscapes, we still have time to save some critical habitats for the conservation of species through systematic conservation planning (see Margules and Pressey 2000Margules CR and Pressey RL. 2000. Systematic Conservation Planning. Nature 405: 242-253., Margules and Sarkar 2007Margules CR and Sarkar S. 2007. Systematic Conservation Planning, 1st ed., Cambridge: Cambridge University Press, 278 p., Diniz-Filho et al. 2007Diniz-Filho JAF, Bini LM, Pinto MP, Rangel TFLVB, Carvalho P, Vieira SL and Bastos RP. 2007. Conservation biogeography of anurans in Brazilian Cerrado. Biodivers Conserv 16: 997-1008., Loyola et al. 2008Loyola R, Becker CG, Kubota U, Haddad CFB, Fonseca CR and Lewinsohn TM. 2008. Hung out to dry: choice of priority ecoregions for conserving threatened Neotropical anurans depends on life-history traits. PLoS ONE 3: e2120., Sarkar and Illoldi-Rangel 2010Sarkar S and Illoldi-Rangel P. 2010. Systematic conservation planning: an updated protocol. Nat Conservação 8: 19-26.). In addition, we must set priorities to assess whether the current distribution of protected areas include the geographic ranges of amphibian species that are conservation targets in Brazil. However, the selection criteria analyzed must be complemented with social participation, which includes decision makers to promote and understand the socio-economic related issues. Thus the priorization of conservation sites and research topics about Brazilian amphibians would possible at regional levels.

ACKNOWLEDGMENTS

We thank the structural support of the State University of Santa Cruz (UESC), Brazil. We are also grateful to D. Faria, S. Azzopardi, E. Muths, and two anonymous reviewers for their comments and suggestions to the manuscript. This study was funded by the Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES), Brazil (Project # 28007018011P9).

REFERENCES

  • Adams MJ et al. 2013. Trends in amphibian occupancy in the United States. PLoS ONE 8: e64347.
  • Araújo MB, Thuiller W and Pearson RG. 2006. Climate warming and the decline of amphibians and reptiles in Europe. J Biogeogr 33: 1712-1728.
  • Azevedo-Ramos C and Galatti U. 2002. Patterns of amphibian diversity in Brazilian Amazônia: conservation implications. Biol Conserv 103: 103-111.
  • Becker CG, Fonseca CR, Haddad CFB and Prado PI. 2010. Habitat Split as a Cause of Local Population Declines of Amphibians with Aquatic Larvae. Conserv Biol 24: 287-294.
  • Beebee TJC and Griffiths RA. 2005. The amphibian decline crisis: a watershed in conservation biology? Biol Conserv 125: 271-285.
  • Bertoluci J and Heyer RW. 1995. Boracéia Update. Froglog: Newsletter of the IUCN/SSC Amphibian Specialist Group 14: 2-3.
  • Blaustein AR, Wake DB and Sousa WP. 1994. Amphibian declines: judging stability, persistence, and susceptibility of populations to local and global extinctions. Conserv Biol 8: 60-71.
  • Blaustein AR, Walls SC, Bancroft BA, Lawler JJ, Searle CL and Gervasi SS. 2010. Direct and Indirect Effects of Climate Change on Amphibian Populations. Diversity 2: 281-313.
  • Boelter RA, Kaefer IL, Both C and Cechin SZ. 2012. Invasive bullfrogs as predators in a Neotropical assemblage: What frog species do they eat? Anim Biol 62: 397-408.
  • Both C and Grant T. 2012. Biological invasions and the acoustic niche: the effect of bullfrog calls on the acoustic signals of white-banded tree frogs. Biol Lett 8: 714-716.
  • Both C, Lingnau R, Santos-Jr A, Madalozzo B, Lima LP and Grant T. 2011. Widespread Occurrence of the American Bullfrog, Lithobates catesbeianus (Shaw, 1802) (Anura: Ranidae), in Brazil. South Am J Herpetol 6: 127-134.
  • Brito D. 2008. Amphibian conservation: Are we on the right track? Biol Conserv 141: 2912-2917.
  • Caldwell JP. 1996. Diversity of Amazonian anurans: the role of systematics and phylogeny in identifying macroecological and evolutionary patterns. In: GIBSON AC (Ed), Neotropical Biodiversity and Conservation. Los Angeles: University of California, Mildred E. Mathias Botanical Garden, USA, p. 73-88.
  • CNPq. 2010. Painel Lattes: Distribuição Geográfica. Conselho Nacional de Desenvolvimento Científico e Tecnológico. Available at: http://lattes.cnpq.br/painelLattes/mapa.
    » http://lattes.cnpq.br/painelLattes/mapa
  • Conservation International, Fundação SOS Mata Atlântica, Fundação Biodiversitas, Instituto de Pesquisas Ecológicas, Secretária do Meio Ambiente do Estado de São Paulo and SEMAD/Instituto Estadual de Florestas-MG. 2000. Avaliação e ações prioritárias para a conservação da biodiversidade da Mata Atlântica e Campos Sulinos, Brasília: MMA/SBF, 40 p.
  • Conte CE and Rossa-Feres DC. 2006. Diversidade e ocorrência temporal da anurofauna (Amphibia, Anura) em São José dos Pinhais, Paraná, Brasil. Rev Bras Zool 23: 162-175.
  • Crist TO, Veech JA, Gering JC and Summerville KS. 2003. Partitioning species diversity across landscapes and regions: A hierarchical analysis of α, β, and γ diversity. Am Nat 162: 734-743.
  • Davidson C and Knapp RA. 2007. Multiple stressors and amphibian declines: dual impacts of pesticides and fish on yellow-legged frogs. Ecol Appl 17: 587-597.
  • Diniz-Filho JAF, Bini LM, Pinto MP, Rangel TFLVB, Carvalho P, Vieira SL and Bastos RP. 2007. Conservation biogeography of anurans in Brazilian Cerrado. Biodivers Conserv 16: 997-1008.
  • Dixo M and Verdade VK. 2006. Leaf litter herpetofauna of the Reserva Florestal de Morro Grande, Cotia (SP). Biota Neotrop 6: 1-20.
  • Eterovick PC, Carnaval ACOQ, Borges-Nojosa DM, Silvano DL, Segalla MV and Sazima I. 2005. An overview of amphibian declines in Brazil with new records from Serra do Cipó, State of Minas Gerais. Biotropica 37: 166-179.
  • Fazey I, Fischer J and Lindenmayer DB. 2005. Who does all the research in conservation biology? Biodiv Conserv 14: 917-934.
  • Fontanello D and Ferreira CM. 2007. Histórico da Ranicultura Nacional. Available at: http://www.aquicultura.br/historico.htm.
    » http://www.aquicultura.br/historico.htm
  • Frost DR. 2014. Amphibian Species of the World: an online reference, version 6.0. Avalaible at: http://research.amnh.org/vz/herpetology/amphibia/.
    » http://research.amnh.org/vz/herpetology/amphibia/
  • Giovanelli JGR, Haddad CFB and Alexandrino J. 2008. Predicting the potential distribution of the alien invasive American bullfrog (Lithobates catesbeianus) in Brazil. Biol Invas 10: 585-590.
  • Gotelli NJ and Entsminger GL. 2005. EcoSim: Null models software for ecology, version 7.72, Acquired Intelligence Inc. and Kesey-Bear. Avalaible at: http://homepages.together.net/∼gentsmin/ecosim.htm.
    » http://homepages.together.net/
  • Gower DJ and Wilkinson M. 2005. Conservation Biology of Caecilian Amphibians. Conserv Biol 19: 45-55.
  • Guix JC, Montori A, Llorente GA, Carretero MA and Santos X. 1998. Natural history and conservation of bufonids in four Atlantic rainforest areas of Southerastern Brazil. Herpetol Nat Hist 6: 1-12.
  • Haddad CFB, Toledo LF and Prado C. 2008. Anfíbios da Mata Atlântica, 1a ed., São Paulo: Editora Neotropica, 244 p.
  • Halliday TR. 2008. Why amphibians are important. Int Zoo Yearb 42: 7-14.
  • Hero JM et al. 2006. Overview of the conservation status of Australian Frogs. Pac Conserv Biol 12: 313-320.
  • Heyer WR, Rand AS, Cruz CAG and Peixoto OL. 1988. Decimations, extinctions, and colonizations of frog populations in southeast Brazil and their evolutionary implications. Biotropica 20: 230-235.
  • Houlahan JE, Findlay CS, Schmidt BR, Meyer AH and Kuzmin SL. 2000. Quantitative evidence for global amphibian population declines. Nature 404: 752-755.
  • Hurlbert AH and Jetz W. 2007. Species richness, hotspots, and the scale dependence of range maps in ecology and conservation. Proc Natl Acad Sci USA 104: 13384-13389.
  • IBGE. 2004. Mapa da vegetação do Brasil e Mapa de Biomas do Brasil. Available at: http://www.ibge.gov.br.
    » http://www.ibge.gov.br
  • IUCN. 2001. IUCN Red List Categories and Criteria, version 3.1. Gland, Switzerland and Cambridge, U.K.: Species Survival Commission, World Conservation Union, 32 p.
  • IUCN, Conservation International and Natureserve. 2006. Global Amphibian Assessment. Available at: http://www.globalamphibians.org.
    » http://www.globalamphibians.org
  • IUCN. 2012. IUCN Red List of Threatened Species, version 2012.1. Available at: http://www.iucnredlist.org.
    » http://www.iucnredlist.org
  • Izecksohn E and Carvalho-e-Silva SP. 2001. Anfíbios do município do Rio de Janeiro, 1a ed., Rio de Janeiro: Editora UFRJ, 148 p.
  • Juncá FA. 2001. Declínio mundial das populações de anfíbios. Sitientibus Sér Ci Biol 1: 84-87.
  • King DA. 2004. The scientific impact of nations. Nature 430: 311-316.
  • Kovach WL. 2004. MVSP: Multivariate Statistical Package, version 3.13m. Available at: http://www.kovcomp.co.uk/mvsp/.
    » http://www.kovcomp.co.uk/mvsp/
  • Lawler JJ et al. 2006. Conservation science: a 20-year report card. Front Ecol Environ 4: 473-480.
  • Lebboroni M, Ricchiardino G, Bellavita M and Chelazzi G. 2006. Potential use of anurans as indicators of biological quality in upstreams of central Italy. Amph-Rept 27: 73-79.
  • Lowe S, Browne M, Boudjelas S and De Poorter M. 2000. 100 of the world's worst invasive alien species - A selection from the global invasive species database. Auckland: School of Geography and Environmental Sciences, University of Auckland, 12 p.
  • Loyola R, Becker CG, Kubota U, Haddad CFB, Fonseca CR and Lewinsohn TM. 2008. Hung out to dry: choice of priority ecoregions for conserving threatened Neotropical anurans depends on life-history traits. PLoS ONE 3: e2120.
  • Magurran AE. 2004. Measuring biological diversity, 2nd ed., Oxford: Blackwell Publishing, 70 p.
  • Margules CR and Pressey RL. 2000. Systematic Conservation Planning. Nature 405: 242-253.
  • Margules CR and Sarkar S. 2007. Systematic Conservation Planning, 1st ed., Cambridge: Cambridge University Press, 278 p.
  • Massarani L. 2013. Brazil's science investment reaches record high. Nature News (01 August 2013): 13495.
  • MCT. 2010. Plano de ação em ciência, tecnologia e inovação: Principais resultados e avanços, Brasília: Ministério da Ciência e Tecnologia, 168 p.
  • Morais AR, Siqueira MN, Lemes P, Maciel NM, De Marco Jr P and Brito D. 2013. Unraveling the conservation status of Data Deficient species. Biol Conserv 166: 98-102.
  • Nystrom P, Hansson J, Mansson J, Sundstedt M, Reslow C and Brostrom A. 2007. A documented amphibian decline over 40 years: Possible causes and implications for species recovery. Biol Conserv 138: 399-411.
  • Oksanen J, Kindt R, Legendre P, O'Hara RB, Gavin L, Simpson GL, Solymos P, Stevens MH and Wagner H. 2009. Vegan: Community Ecology Package. R package version 1.15–4. Available at: http://CRAN.R-project.org/package=vegan.
    » http://CRAN.R-project.org/package=vegan
  • Pimenta BVS, Haddad CFB, Nascimento LB, Cruz CAG and Pombal Jr JP. 2005. Comment on “status and trends of amphibian declines and extinctions worldwide”. Science 309: 5743.
  • Pombal Jr JP and Haddad CFB. 1999. Frogs of the genus Paratelmatobius (Anura: Leptodactylidae) with descriptions of two new species. Copeia 4: 1014-1026.
  • R Development Core Team. 2009. R: A language and environment for statistical computing. Vienna: R Foundation for Statistical Computing. Available at: http://www.R-project.org.
    » http://www.R-project.org
  • Sarkar S and Illoldi-Rangel P. 2010. Systematic conservation planning: an updated protocol. Nat Conservação 8: 19-26.
  • Schiesari L, Grillitsch B and Grillitsch H. 2007. Biogeographic biases in research and their consequences for linking amphibian declines to pollution. Conserv Biol 21: 465-471.
  • Segalla MV, Caramaschi U, Cruz CAG, Garcia PCA, Grant T, Haddad CFB and Langone J. 2012. Brazilian amphibians – List of species, Sociedade Brasileira de Herpetologia. Available at: http://www.sbherpetologia.org.br.
    » http://www.sbherpetologia.org.br
  • Sewell D and Griffiths RA. 2009. Can a single amphibian species be a good biodiversity indicator? Diversity 1: 102-117.
  • Silva ET, Ribeiro-Filho OP and Feio RN. 2011. Predation of native anurans by invasive bullfrogs in southeastern Brazil: spatial variation and effect of microhabitat use by prey. South Am J Herpetol 6: 1-10.
  • Silvano DL and Segalla MV. 2005. Conservation of Brazilian Amphibians. Conserv Biol 19: 653-658.
  • Stuart SN, Chanson JS, Cox NA, Young BE, Rodrigues ASL, Fischman DL and Waller RW. 2004. Status and trends of amphibian declines and extinctions worldwide. Science 306: 1783-1786.
  • Toledo LF and Batista RF. 2012. Integrative Study of Brazilian Anurans: Geographic Distribution, Size, Environment, Taxonomy, and Conservation. Biotropica 44: 785-792.
  • Trindade-Filho J, Carvalho RA, Brito D and Loyola RD. 2012. How does the inclusion of Data Deficient species change conservation priorities for amphibians in the Atlantic Forest? Biodivers Conserv 21: 2709-2718.
  • Urbina-Cardona JN. 2008. Conservation of Neotropical herpetofauna: research trends and challenges. Trop Conserv Sci 1: 359-375.
  • Verdade VK et al. 2012. A leap further: The Brazilian amphibian conservation action plan. Alytes 29: 27-42.
  • Weygoldt P. 1989. Changes in the composition of mountainstream frog communities in the Atlantic mountains of Brazil: frogs as indicators of environmental deteriorations? Stud Neotrop Fauna Environ 243: 249-255.
  • Young B et al. 2001. Population declines and priorities for Amphibian conservation in Latin America. Conserv Biol 15: 1213-1223.

Publication Dates

  • Publication in this collection
    09 Dec 2014
  • Date of issue
    Dec 2014

History

  • Received
    7 Apr 2014
  • Accepted
    7 July 2014
Academia Brasileira de Ciências Rua Anfilófio de Carvalho, 29, 3º andar, 20030-060 Rio de Janeiro RJ Brasil, Tel: +55 21 3907-8100 - Rio de Janeiro - RJ - Brazil
E-mail: aabc@abc.org.br