Phylogeography of Four Frog Species in Forest Fragments of Northeastern Brazil—A Preliminary Study1
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INTEGR.COMP.BIOL., 42:913±921 (2002) Phylogeography of Four Frog Species in Forest Fragments of Northeastern BrazilÐA Preliminary Study1 ANA CAROLINA O. Q. CARNAVAL2 The University of Chicago and The Field Museum of Natural History, 1025 East 57th Street (Culver Hall), Suite # 402, Chicago, Illinois 60637 SYNOPSIS. I contrast mitochondrial DNA genealogies based on 612 bp of the cytochrome b gene across four co-distributed species of frogs in Northeastern Brazil. They are Hyla albomarginata, Hyla branneri, Proceratophrys boiei, and Scinax nebulosus. Samples were collected from the core or edge of six rainforest remnants in the states of Pernambuco and Alagoas. Three fragments are located within the humid Atlantic Forest morphoclimatic domain (municipalities of Cabo de Santo Agostinho, Ibateguara, and Jaqueira), two Downloaded from https://academic.oup.com/icb/article/42/5/913/659735 by guest on 29 September 2021 are located in the transition zone between the Atlantic Forest domain and the semi-arid Caatinga (Caruaru and TimbauÂba), and one is found within the Caatinga (Brejo da Madre de Deus). Results show that local patterns and levels of genetic diversity are in¯uenced by taxon-speci®c habitat requirements. Populations of the montane, closed-canopy species P. boiei show strong geographical structure, re¯ecting barriers to gene ¯ow that predate human-driven habitat destruction. Species occurring along forest edges, such as H. albom- arginata and S. nebulosus, show genetic patterns similar to those of P. boiei, but lower levels of genetic divergence. The more generalist Hyla branneri shows no geographic pattern. The data are in agreement with distribution and fossil data gathered for other groups of organisms, suggesting that mesic forests occupied the currently arid Caatinga in the recent past. INTRODUCTION The tools of phylogeography (Avise et al., 1987) The Atlantic Rainforest is an extraordinarily diverse are central to conservation and can be informative for and complex ecosystem found along the coast of Bra- the preservation of the Atlantic Rainforest. This area zil. Home to approximately 21,361 species of plants of molecular biology investigates the spatial distribu- and tetrapod vertebrates, of which ca. 8,567 occur no- tion of evolutionary lineages and their phylogenetic where else in the planet, it ranks among the top priority relationships (Bermingham and Moritz, 1998). Phylo- areas for conservation in the world (Myers et al., geographic studies not only document the amount of 2000). Human-driven landscape changes have strongly current genetic diversity within and among geograph- impacted this area (Morellato and Haddad, 2000). Lo- ical areas, but also assess the phylogenetic distinctive- cal deforestation began with the arrival of European ness of populations, providing insight on how organ- colonizers in the sixteenth century and has increased isms have historically responded to local landscape dramatically ever since (Coimbra-Filho and CaÃmara, changes (Moritz and Faith, 1998). Comparative phy- 1996). Today's remnants of this ecosystem barely add logeographic analyses are yet more powerful. By con- up to 8% of its original extent (Myers et al., 2000). trasting gene trees of co-distributed species, these Causes of habitat destruction were many and syner- methods enable one to search for common historical gistic, involving agricultural practices, cattle ranching, events that might have affected multiple taxa in a giv- and urban growth (CaÃmara, 1992; FundacËaÄo SOS Mata en area (e.g., Patton et al., 1996; Schneider et al., AtlaÃntica, 1992; Sales et al., 1998). 1998; Bates, 2000, 2002; Stuart-Fox et al., 2001; To adequately preserve what is left of this biodi- SchaÈuble and Mortiz, 2001). Phylogeographic studies versity hotspot, it is imperative to deepen our knowl- involving taxa from the Brazilian Atlantic Forest are edge about the history of the Atlantic Forest and in- relatively few and recent, and most available data re- vestigate the consequences of habitat patchiness for late to species of mammals (Mustrangi and Patton, local populations. Distribution patterns of extant taxa 1997; Ditch®eld, 2000; Lara and Patton, 2000). provide clues about local historical processes and in- I contrast mitochondrial DNA genealogies based on form conservation in this system (Vanzolini, 1981; 612 bp of the cytochrome b gene of four species of Heyer and Maxson, 1983; Costa et al., 2000). How- amphibians that co-occur in or along Atlantic Forest ever, it is desirable to go beyond interspeci®c analyses remnants in Northeastern Brazil. They are Hyla albom- and study patterns of genetic diversity within local arginata Spix, Hyla branneri Cochran, Procerato- taxa. Are remnant populations still managing to ex- phrys boiei (Wied-Neuwied), and Scinax nebulosus change genes? If not, how divergent are they? Are they (Spix). These taxa differ in aspects of their natural genetically structured? If so, how? Ultimately, why? history, such as habitat requirements and reproductive biology. Field data and literature records indicate that 1 From the Symposium Integrated Approaches to Biogeography: Proceratophrys boiei is a forest-associated species that Patterns and Processes on Land and in the Sea presented at the Annual Meeting of the Society for Integrative and Comparative Bi- occurs in closed-canopy areas, breeding in slow-mov- ology, 2±6 January 2002, at Anaheim, California. ing waters such as side pools along streams (Cochran, 2 E-mail: [email protected] 1955; Izecksohn et al., 1979). Hyla albomarginata and 913 914 ANA CAROLINA O. Q. CARNAVAL in the transition zone between these two biomes. The term Brejos de Altitude or forest enclaves is used to denote such remnants of the Atlantic Forest found in the middle of the Caatinga and in transition areas un- der considerable Caatinga in¯uence (Andrade-Lima, 1982) (Fig. 1). The Brejos occur on mountains of ap- proximately 500±1,100 m of altitude that are exposed to humid winds, and it has been proposed that they represent extant refuges formally connected to Atlantic and Amazonian forests (Vanzolini, 1981; Andrade- Lima, 1982). The origin of the Brejos has been asso- ciated with humid paleoclimates established after the middle Tertiary, especially during interglacial phases Downloaded from https://academic.oup.com/icb/article/42/5/913/659735 by guest on 29 September 2021 of the Pleistocene (Bigarella et al., 1975; Bigarella and Andrade-Lima, 1982). It is hypothesized that both the FIG. 1. South American morphoclimatic domains, modi®ed from Atlantic Forest and Amazonia were able to expand and Ab'Saber, 1977. Triangles depict forest enclaves (Brejos) in the Caa- connect during such humid phases, extending their tinga and in the Caatinga-Atlantic Forest transition zone (based on Andrade-Lima, 1982). limits into what now is the semi-arid Caatinga. Today, lower temperatures and higher precipitation enable the maintenance of a forested environment in the Brejos, Scinax nebulosus are commonly found along forest and they persist in slopes of the Borborema, Araripe edges, breeding in standing water adjacent to forest and Ibiapaba plateaus (Andrade-Lima, 1982). borders (Cochran, 1955; Lutz, 1973; Arzabe et al., Field work for this study was conducted in the 1998). Hyla branneri is reported to be more resistant northeastern states of Alagoas (AL) and Pernambuco to open areas, occurring along forest edges (Arzabe et (PE). Samples of the target species were collected al., 1998) but also in drier, more remote zones of from the core or edge of six forest remnants in the Northeastern Brazil (Andrade et al., 2000). municipalities of Brejo da Madre de Deus (PE), Cabo By contrasting patterns of genetic diversity among de Santo Agostinho (PE), Caruaru (PE), Ibateguara these four co-distributed species of amphibians, I hope (AL), Jaqueira (PE), and TimbauÂba (PE) (Fig. 2). to improve our understanding of the history of the At- Three of the fragments are located within the Atlantic lantic Rainforest in Northeastern Brazil and inform Rainforest morphoclimatic domain. They are Cabo de conservation of its remnant populations. I speci®cally Santo Agostinho, Ibateguara, and Jaqueira. Brejo da address the following questions: What do genetic pat- Madre de Deus is located further inland in Northeast- terns exhibited by multiple lineages suggest about the ern Brazil, within the savanna-like, semi-arid Caatin- history of these forest remnants? Are populations ga. Caruaru and TimbauÂba are situated in the transition found in or along fragments genetically structured? zone between the Atlantic Forest coastal domain and How? Does habitat selection in¯uence levels and pat- the dry Caatinga (FundacËaÄo Instituto Brasileiro de terns of genetic diversity in the target taxa? If so, one Geogra®a e EstatõÂstica, 1988). Forests in both Brejo would predict that genetic differentiation among pop- da Madre de Deus and Caruaru are representatives of ulations should be higher in the most specialized, Brejos in the state of Pernambuco (Andrade-Lima, closed-canopy dependent Proceratophrys boiei, while 1982; Sales et al., 1998) intermediate among populations of forest-edge taxa such as Hyla albomarginata and Scinax nebulosus, About the target species and little or nonexistent among those of the more gen- Proceratophrys boiei (Fig. 3) is a medium-sized eralist Hyla branneri. frog whose adults live under leaves and stones in for- ested mountains of up to approximately 1,000 m along STUDY SYSTEM the Brazilian coast (Cochran, 1955;