Abstract Abstract
The Rhinella margaritifera species group consists of 17 species of toads distributed in tropical and subtropical South America and eastern Central America. The identity of some of its species is poorly understood and there are numerous undescribed cryptic species. Among them, the status of Rhinella margaritifera is one of the most problematic. Its range includes lowland rainforests separated by the Andes, the Chocoan rainforest to the west and the Amazonian rainforest to the east. This distribution is puzzling because the Andes are an old and formidable barrier to gene flow and therefore should generate vicariant speciation between disjunct lowland populations. Herein we clarify the taxonomy of populations of the Rhinella margaritifera complex from Central America and the Chocó region of South America. The morphological and genetic variation of Rhinella margaritifera was examined from 39 populations from Chocó, 24 from the upper Amazon region of Ecuador, and 37 from Panama, including the holotype of the Panamanian Rhinella alata. Phylogenetic analyses were performed based on mitochondrial genes 12S rRNA, 16S rRNA, and cytochrome c oxidase I (COI) and the nuclear gene Tyrosinase (Tyr). The genetic and morphological data show that Panamanian and Chocoan populations are conspecific. In the phylogeny, populations from Chocó and Panama form a well-supported clade. The morphology of the holotype of Rhinella alata falls within the variation range of Panamanian and Chocoan populations. Based on all this evidence, we assign the populations from western Ecuador and Panama to Rhinella alata and demonstrate that the unusual distribution pattern of “Rhinella margaritifera” on both sides of the Andes was an artifact of incorrectly defined species boundaries.
Keywords: Andes, Biogeography, Chocó, Morphology, Panama, Phylogeny, Rhinella alata
Introduction
Rhinella is a genus of bufonid frogs distributed from southern Texas, through southern Sonora (Mexico), south tropical Mexico, Central America, and South America. There are 87 recognized species of Rhinella (Frost, 2014) among which 17 belong to the Rhinella margaritifera species group (Lavilla et al. 2013, Moravec et al. 2014). Thirteen of these species are distributed throughout the Amazon Basin, the Guyanas and Central America, while Rhinella hoogmoedi Caramaschi & Pombal, 2006 occurs in the Brazilian Atlantic Forest, Rhinella scitula (Caramaschi & Niemeyer, 2003) and Rhinella ocellata (Günther, 1858) in the Brazilian Cerrado, and Rhinella paraguayensis Ávila, Pansonato & Strüssmann, 2010 in the Brazilian Pantanal (Caramaschi and Niemeyer 2003, Caramaschi and Pombal 2006, Lima et al. 2007, Fouquet et al. 2007a, Ávila et al. 2010, Frost 2014). They inhabit the forest floor and their cryptic coloration mimics the forest leaflitter. Morphologically they have been characterized by the presence of hypertrophied supra and postorbital crests, especially in females. Putative synapomorphies for the group are the expansion of the posterior ramus of the pterygoid and nasals that articulate laterally with the preorbital process of the maxilla (Pramuk 2006).
The Rhinella margaritifera species group (formerly Bufo typhonius or Bufo margaritifer group) has one of the most complex histories in the systematics of Neotropical anurans (Hoogmoed 1986, 1989, 1990, Hass et al. 1995, Fouquet et al. 2007b). The boundaries among its species member are poorly understood as a result of a highly variable intraspecific morphology and scant morphological differentiation between some species. In addition, some of the type material is unavailable or poorly preserved and several species descriptions lack details. Despite recent progress in the systematics of the group (i.e. Vélez-Rodriguez 2004, Pramuk 2006, Fouquet et al. 2007b, 2012b, Ávila et al. 2010, Lavilla et al. 2013, Moravec et al. 2014) a number of cryptic species still need to be identified, specially among Amazonian populations (Hoogmoed 1990, Hass et al. 1995, Vélez-Rodríguez 2004, Pramuk 2006, Fouquet et al. 2007b, Lavilla et al. 2013, Moravec et al. 2014).
Two species of the Rhinella margaritifera group have been reported west of the Andes (Chocó region, humid forests west of the Andes in Colombia and Ecuador) and in eastern Panama: Rhinella alata and Rhinella margaritifera. Rhinella alata was described by Thominot (1884) as Bufo alatus, based on an adult male collected at Obispo, Isthmus of Panama. Boulenger (1885) considered it a junior synonym of “Bufo typhonius”, and Hoogmoed (1986, 1989) suggested that it was, possibly, a synonym of Bufo acutirostris (Spix, 1824). La Marca (1997) reported populations of Rhinella alata from northern Venezuela. Gorzula and Señaris (1999) suggested that Rhinella margaritifera only occurs in southern Venezuela and Rhinella alata north of the Orinoco. However, Barrio-Amorós (1999 “1998”, 2004) disagreed with both reports and considered that Rhinella alata was not distributed in Venezuela.
Rhinella margaritifera was described by Laurenti in 1768. It occurs in eastern Panama (Frost 2014), the Chocoan lowlands of western Ecuador and western Colombia (e.g. Anderson 1945, Miyata 1982, Ruiz-Carranza et al. 1996, Ortega-Andrade et al. 2010, Ortiz et al. 2013, Ron et al. 2014), Amazonia and vicinities in Bolivia, Brazil, Colombia, Ecuador, French Guiana, Guyana, Peru, Surinam and Venezuela (Lavilla et al. 2013). A genetic study by Fouquet et al. (2007b), using two mitochondrial genes (12S and 16S) and the two nuclear genes (Tyrosinase and 18S), showed that Rhinella margaritifera was paraphyletic and contained up to 11 cryptic species. Populations from the Chocó region have been widely referred as Rhinella margaritifera although Solis et al. (2010) remarked that populations from the Ecuadorian Chocó might belong to a separate species. Unfortunately, they did not provide further details.
The distribution of Rhinella margaritifera in the humid lowlands west and east of the Andes is intriguing because, particularly for amphibians, the Andes represent a formidable barrier to gene flow (e.g. Santos et al. 2009). Despite similar environmental conditions, only four amphibian species are shared between the lowland rainforests of the Amazon basin and the Chocó: Rhinella margaritifera, Rhinella marina, Hypsiboas boans and Trachycephalus typhonius. Moreover, there is genetic and morphological evidence suggesting that populations on each side of the Andes of Rhinella marina and Trachycephalus typhonius represent separate species (Slade and Moritz 1998, Ron and Read 2011). Thus, the distribution of Rhinella margaritifera is suggestive of either an unusual biogeographic history or the existence of cryptic species.
Herein, genetic and morphological information were integrated to clarify the taxonomy of the populations of Rhinella margaritifera from Panama and the Chocoan region. Populations from the western and eastern Andean slopes were compared to test the role of the Andes as a dispersal barrier in shaping the evolution of the Rhinella margaritifera species complex.
Methods
Population sampling
Populations from Panama, the Ecuadorian Chocó, and the Amazon basin were sampled (Figs 1 and 2). Specimens examined morphologically are listed in Appendix 1; specimens analyzed genetically are listed in Table 1.
Figure 1.
Localities of the Rhinella margaritifera group from Chocó (triangles) and Amazon (squares). Gray for specimens analyzed morphologically, black for specimens analyzed both genetically and morphologically. Specimens (listed in Appendix 1 and Table 1) are deposited at the Museo de Zoología of Pontificia Universidad Católica del Ecuador (QCAZ), Centro de Ornitología y Biodiversidad (CORBIDI), and National Museum of Natural History (USNM).
Figure 2.
Panamanian populations of the Rhinella margaritifera group included in this study. White crosses for specimens analyzed morphologically, black crosses analyzed both morphologically and genetically. The type locality of Rhinella alata is shown with a triangle. Specimens (listed in Appendix 1 and Table 1) are deposited at American Museum of Natural History (AMNH), Muséum National d’Histoire Naturelle du Paris (MNHN), Círculo Herpetológico de Panama (CH), and the Museo de Vertebrados de la Universidad de Panama (MVUP).
Table 1.
GenBank accession numbers for DNA sequences used in the phylogenetic analysis.
| Museum No. | Species | Country | Locality | GenBank Accession No. | Reference | |||
|---|---|---|---|---|---|---|---|---|
| TYR | 16S | 12S | COI | |||||
| QCAZ10253 | Rhinella alata | Ecuador | Reserva La Chiquita | KR012523 | KR012615 | KR012605 | KR012568 | This study |
| QCAZ10254 | Rhinella alata | Ecuador | Reserva La Chiquita | KR012524 | KR012616 | KR012601 | KR012567 | This study |
| QCAZ10255 | Rhinella alata | Ecuador | Reserva La Chiquita | KR012525 | KR012617 | KR012602 | KR012570 | This study |
| QCAZ11598 | Rhinella alata | Ecuador | Reserva La Chiquita | KR012526 | KR012618 | KR012603 | KR012550 | This study |
| QCAZ13882 | Rhinella alata | Ecuador | Manta Real | KR012527 | KR012619 | KR012597 | KR012571 | This study |
| QCAZ13896 | Rhinella alata | Ecuador | Manta Real | - | DQ158471 | DQ158471 | - | Pramuk 2006 |
| QCAZ14607 | Rhinella alata | Ecuador | Borbón | KR012528 | KR012620 | KR012578 | KR012552 | This study |
| QCAZ37244 | Rhinella alata | Ecuador | Valle Hermoso | KR012539 | KR012632 | KR012592 | KR012576 | This study |
| QCAZ37248 | Rhinella alata | Ecuador | Valle Hermoso | KR012540 | KR012633 | KR012595 | KR012544 | This study |
| QCAZ 23161 | Rhinella alata | Ecuador | San Lorenzo | KR012534 | KR012626 | KR012577 | KR012562 | This study |
| QCAZ25023 | Rhinella alata | Ecuador | La Tortuga | KR012536 | KR012629 | KR012596 | KR012572 | This study |
| QCAZ25025 | Rhinella alata | Ecuador | La Tortuga | KR012537 | KR012630 | KR012582 | KR012573 | This study |
| QCAZ25032 | Rhinella alata | Ecuador | La Pedorrera | KR012538 | KR012631 | KR012604 | KR012569 | This study |
| CH9104 | Rhinella alata | Panama | Cana, Boca Cupé | KR012507 | KR012610 | KR012598 | KR012560 | This study |
| MVUP2299 | Rhinella alata | Panama | Río Chico Masambí, Parque Nacional Soberanía | KR012511 | KR012613 | KR012600 | KR012561 | This study |
| CH9192 | Rhinella alata | Panama | Parque Nacional Soberanía | KR012521 | KR012611 | KR012599 | KR012559 | This study |
| QCAZ11597 | Rhinella alata | Ecuador | Reserva La Chiquita | - | DQ15872 | DQ15872 | - | Pramuk 2006 |
| 104mc | Rhinella castaneotica | French Guyana | Tibourou | EF364355 | EF364289 | EF364263 | - | Fouquet et al. 2007b |
| 110pg | Rhinella castaneotica | French Guyana | Moint Saint Marcel | EF364353 | EF364285 | EF364259 | - | Fouquet et al. 2007b |
| QCAZ38477 | Rhinella dapsilis | Ecuador | Villano B | KR012513 | KR012634 | KR012586 | KR012554 | This study |
| QCAZ38512 | Rhinella dapsilis | Ecuador | Villano BII | KR012514 | KR012635 | KR012587 | KR012558 | This study |
| QCAZ38560 | Rhinella dapsilis | Ecuador | Villano B | KR012515 | KR012636 | KR012588 | KR012555 | This study |
| QCAZ38621 | Rhinella dapsilis | Ecuador | Villano K4 | KR012516 | KR012637 | KR012606 | KR012556 | This study |
| QCAZ38688 | Rhinella dapsilis | Ecuador | Villano K4 | KR012517 | KR012638 | KR012607 | KR012575 | This study |
| QCAZ38755 | Rhinella dapsilis | Ecuador | Villano BII | KR012518 | KR012639 | KR012589 | KR012548 | This study |
| QCAZ38892 | Rhinella dapsilis | Ecuador | Comunidad Kutintza 2 | KR012519 | KR012640 | KR012608 | KR012566 | This study |
| QCAZ38998 | Rhinella dapsilis | Ecuador | Comunidad Kurintza 3 | KR012520 | KR012641 | KR012590 | KR012549 | This study |
| MTR19199 | Rhinella hoogmoedi | Brazil | Bahia, Camacan | - | JN867571 | JN867545 | - | Fouquet et al. 2012a |
| 112bm | Rhinella lescurei | French Guyana | Litany | EF364343 | EF217473 | EF364279 | - | Fouquet et al. 2007b |
| 3027t | Rhinella lescurei | French Guyana | Mitaraka | JN692065 | EF364305 | EF364279 | - | Fouquet et al. 2012b |
| 108mc | Rhinella margaritifera | French Guyana | Kaw | EF364333 | EF364292 | EF364266 | - | Fouquet et al. 2007b |
| 136mc | Rhinella margaritifera | French Guyana | Crique Margot | EF364335 | EF364292 | EF364266 | - | Fouquet et al. 2007b |
| 389MC | Rhinella margaritifera | French Guyana | Camp Canopé | JN692029 | - | - | - | Fouquet et al. 2007b |
| 374MC | Rhinella margaritifera | French Guyana | Régina | JN692038 | JN691389 | JN690782 | - | Fouquet et al. 2007b |
| 390MC | Rhinella margaritifera | French Guyana | St Georges | JN692037 | JN691388 | JN690781 | - | Fouquet et al. 2007b |
| 2559T | Rhinella margaritifera | French Guyana | Pic Matecho | JN690780 | JN691387 | JN690780 | - | Fouquet et al. 2012b |
| 4482T | Rhinella margaritifera | French Guyana | Angoulème | JN692042 | JN691379 | JN690772 | - | Fouquet et al. 2012b |
| 163bm | Rhinella margaritifera | French Guayana | Guatemala | EF364320 | EF364292 | EF364266 | - | Fouquet et al. 2007b |
| 164bm | Rhinella margaritifera | French Guyana | Montagne des Singes | EF364321 | EF364292 | EF364266 | - | Fouquet et al. 2007b |
| 176bm | Rhinella margaritifera | French Guyana | Crique Grand Leblond | EF364323 | EF364292 | EF364266 | - | Fouquet et al. 2007b |
| 195mc | Rhinella margaritifera | French Guyana | Kaw | EF364325 | EF364292 | EF364266 | - | Fouquet et al. 2007b |
| 2034at | Rhinella margaritifera | French Guyana | Nouragues | JN692033 | EF364292 | EF364266 | - | Fouquet et al. 2007b |
| 204mc | Rhinella margaritifera | French Guyana | Saul | EF364328 | EF364295 | EF364269 | - | Fouquet et al. 2007b |
| 217mc | Rhinella margaritifera | French Guyana | Grant Santi | EF364329 | EF364299 | EF364273 | - | Fouquet et al. 2007b |
| 225mc | Rhinella margaritifera | French Guyana | Road St. Elie | EF364330 | EF364292 | EF364266 | - | Fouquet et al. 2007b |
| 284mc | Rhinella margaritifera | French Guyana | St Elie | EF364336 | EF364292 | EF364266 | - | Fouquet et al. 2007b |
| 288ag | Rhinella margaritifera | French Guyana | St Georges | JN692021 | JN691380 | JN690773 | - | Fouquet et al. 2012b |
| 294mc | Rhinella margaritifera | French Guyana | Camp Canope | JN692029 | EF364292 | EF364266 | - | Fouquet et al. 2012b |
| 2bm | Rhinella margaritifera | French Guyana | Cisame | EF364313 | EF364293 | EF364267 | - | Fouquet et al. 2007b |
| 307pg | Rhinella margaritifera | French Guyana | Lac Toponowini | JN692022 | EF364292 | EF364266 | - | Fouquet et al. 2012b |
| 361mc | Rhinella margaritifera | French Guyana | Lucifer | JN692031 | EF364292 | EF364266 | - | Fouquet et al. 2012b |
| 408pg | Rhinella margaritifera | French Guyana | Mont Kotika | JN692023 | EF364292 | EF364266 | - | Fouquet et al. 2012b |
| 66mc | Rhinella margaritifera | French Guyana | Monts Bakra | EF364334 | EF364298 | EF364272 | - | Fouquet et al. 2007b |
| 74af | Rhinella margaritifera | French Guyana | St Georges | JN692020 | EF364266 | EF364292 | - | Fouquet et al. 2012b |
| 92bm | Rhinella margaritifera | French Guyana | Cisame | EF364314 | EF364301 | EF364275 | - | Fouquet et al. 2007b |
| KU215143 | Rhinella margaritifera | Peru | Madre de Dios | - | AY819461 | AY819331 | - | Wiens et al. 2005 |
| 13872MTR | Rhinella margaritifera | Brazil | Amapá, Lourenço | JN692016 | JN691390 | JN690783 | - | Fouquet et al. 2012b |
| 13873MTR | Rhinella margaritifera | Brazil | Amapá, Lourenço | JN692017 | JN691391 | JN690784 | - | Fouquet et al. 2012b |
| 13874MTR | Rhinella margaritifera | Brazil | Amapá, Lourenço | JN692018 | JN691393 | JN690786 | - | Fouquet et al. 2012b |
| 13878MTR | Rhinella margaritifera | Brazil | Amapá, Lourenço | JN692019 | JN691392 | JN690785 | - | Fouquet et al. 2012b |
| MRT6313 | Rhinella margaritifera | Brazil | Pará, Serra do Kukoinhokren | JN692075 | JN691394 | JN690787 | - | Fouquet et al. 2012b |
| MRT6317 | Rhinella margaritifera | Brazil | Pará, Serra do Kukoinhokren | JN692076 | JN691395 | JN690788 | - | Fouquet et al. 2012b |
| KU215146 | Rhinella margaritifera | Peru | Madre de Dios | - | - | HM563858 | JN867978 | Mendelson et al. 2011 |
| CORBIDI5840 | Rhinella margaritifera | Peru | Curupa | KR012522 | KR012612 | KR012594 | KR012564 | This study |
| USNM268828 | Rhinella margaritifera | Peru | Madre de Dios | - | DQ158490 | DQ158490 | - | Pramuk 2006 |
| KU215145 | Rhinella cf. margaritifera | Peru | Madre de Dios | - | DQ158491 | DQ158491 | - | Pramuk 2006 |
| ZUEC-DCC3393 | Rhinella cf. margaritifera | Brazil | Rio de Janeiro, Santo Aleixo | - | - | AY680262 | - | Pauly et al. 2004 |
| QCAZ17775 | Rhinella margaritifera | Ecuador | 244 km of Indanza | KR012529 | KR012621 | KR012581 | KR012551 | This study |
| QCAZ17989 | Rhinella margaritifera | Ecuador | Estación Biológica JatunSacha | KR012530 | KR012622 | - | KR012565 | This study |
| QCAZ17990 | Rhinella margaritifera | Ecuador | Estación Biológica JatunSacha | KR012531 | KR012623 | KR012593 | KR012557 | This study |
| QCAZ17991 | Rhinella margaritifera | Ecuador | Estación Biológica JatunSacha | KR012532 | KR012614 | - | KR012543 | This study |
| QCAZ23632 | Rhinella margaritifera | Ecuador | 7Km North of Cosanga | KR012535 | KR012627 | KR012583 | KR012542 | This study |
| QCAZ23917 | Rhinella margaritifera | Ecuador | Gualaquiza-El Ideal | KR012512 | KR012628 | KR012591 | KR012547 | This study |
| QCAZ10601 | Rhinella margaritifera | Ecuador | Parque Nacional Yasuní | - | DQ15870 | DQ15870 | - | Pramuk 2006 |
| QCAZ18241 | Rhinella margaritifera | Ecuador | Shaime | KR012533 | KR012625 | KR012585 | KR012553 | This study |
| 10226MSH | Rhinella margaritifera | Brazil | Amazonas, Anavilhanas | JN692056 | JN691364 | JN690757 | - | Fouquet et al. 2012b |
| 10339MSH | Rhinella margaritifera | Brazil | Amazonas, Anavilhanas | JN692057 | JN601365 | JN69058 | - | Fouquet et al. 2012b |
| QCAZ42269 | Rhinella margaritifera | Ecuador | Reserva Yachana | KR012541 | KR012642 | KR012584 | KR012563 | This study |
| 111af | Rhinella martyi | French Guyana | Brownsberg | JN692045 | EF364303 | EF364277 | - | Fouquet et al. 2007b |
| 156mc | Rhinella martyi | French Guyana | Trijonction | EF364337 | EF364303 | EF364277 | - | Fouquet et al. 2007b |
| LAJ210 | Rhinella ocellata | Brazil | Tocantins, Lajeado | - | JN867572 | JN867546 | - | Fouquet et al. 2012a |
| MZUSP103261 | Rhinella ocellata | Brazil | Tocantins, Peixe | - | DQ158479 | DQ158479 | - | Pramuk 2006 |
| SMF88237 | Rhinella cf. paraguayensis | Bolivia | - | - | JF790186 | - | - | Jansen et al. 2011 |
| MNKA9691 | Rhinella cf. paraguayensis | Bolivia | - | - | JF790185 | - | - | Jansen et al. 2011 |
| ESTR00173 | Rhinella sp. | Brazil | Amazonas, Carolina | - | JN867574 | JN867548 | - | Fouquet et al. 2012a |
| AF7275337 | Rhinella sp. | Brazil | Mato Grosso, APM Manso | - | JN867575 | JN867549 | - | Fouquet et al. 2012a |
| Outgroup | ||||||||
| QCAZ50698 | Rhinella marina | Ecuador | Puerto Cayo | KR012508 | KR012643 | KR012579 | KR012545 | This study |
| QCAZ50702 | Rhinella marina | Ecuador | San Andrés de Rocafuerte | KR012509 | KR012644 | KR012580 | KR012546 | This study |
| QCAZ18203 | Rhinella festae | Ecuador | Estación Biológica Jatun Sacha | KR012510 | KR012624 | KR012609 | KR012574 | This study |
| KU217501 | Rhinella festae | Ecuador | Pastaza | - | DQ158423 | DQ158423 | - | Pramuk 2006 |
| MTD43789 | Rhinella chavin | Peru | Palma Pampa | - | DQ158441 | DQ158441 | - | Pramuk 2006 |
| UTA53310 | Rhinella nesiotes | Bolivia | La Paz | - | DQ158478 | DQ158478 | - | Pramuk 2006 |
Morphometric analyses were based on 120 adult specimens of Rhinella margaritifera from Panama (14 specimens from 10 populations), Ecuadorian Chocó (74 specimens, 37 populations), and the Ecuadorian Amazon (32 specimens, 18 populations). Qualitative morphological characters were examined in the same specimens and 28 additional individuals from 27 Panamanian populations (Figs 1 and 2; Appendix 1).
Genetic analyses were based on newly generated sequences of Rhinella margaritifera from 32 individuals and 19 populations: Rhinella margaritifera from the Ecuadorian Chocó (12 individuals, 7 populations); Rhinella margaritifera from Panama (3 individuals, 2 populations) and Rhinella margaritifera from the Amazon basin (17 individuals, 10 populations), and six sequences for the outgroups (see Table 1). Sequences of eight Rhinella dapsilis were generated, including all available homologous sequences for the Rhinella margaritifera species group from GenBank (http://www.ncbi.nlm.nih.gov/genbank; Table 1). Rhinella marina, Rhinella chavin, Rhinella nesiotes and Rhinella festae were included as outgroups. The morphometric and genetic analyses were based on the same individuals, when possible. Several specimens used in the morphological analyses lacked tissues and were not included in the genetic analyses. However, their identification was unambiguous based on geographic distribution and morphological characters.
Examined specimens are deposited at the Museo de Zoología, Pontificia Universidad Católica del Ecuador (QCAZ, Quito, Ecuador), the American Museum of Natural History (AMNH, New York, USA), Círculo Herpetológico de Panama (CH, Panama, Panama), Centro de Ornitología y Biodiversidad (CORBIDI, Lima, Perú) and Museo de Vertebrados de la Universidad de Panama (MVUP). We also examined photographs of the holotypes of Rhinella alata from Musée National d’Historie Naturelle (MNHN, Paris, France). Tissues were obtained from the QCAZ and CH collections. Tissues (liver or thigh muscle) were stored in 95% ethanol.
Morphological analyses
Morphological terminology and abbreviations follow Vélez-Rodriguez (2004) and Narvaes and Rodrigues (2009). Sexual maturity was determined by the presence of nuptial pads in adult males and convoluted oviducts or mature eggs in gravid females. Specimens from the QCAZ collection were euthanized with the anesthetic spray Roxicaine, fixed in 10% formalin, and preserved in 70% ethanol.
The goal of the morphological analyses was to compare three geographic regions: (1) Chocó (2) Panama, and (3) upper Amazon basin. Because the phylogeny showed that Panama and Chocó populations are conspecific, we also compared Chocó + Panama vs. upper Amazon. Morphometric analyses were based on adult and well-preserved specimens (Simmons 2002). We measured the following variables: (1) SVL (snout-vent length, from the tip of snout to the mid-vent); (2) TL (tibia length, from the outer edge of flexed knee to the heel); (3) FL (femur length, from the mid-venter to the outer edge of flexed knee); (4) HL (head length, from the posterior margin of tympanum to the tip of snout); (5) HW (head width, between knobs at angles of jaws, if present); (6) STCH (supratympanic crest height, the distance between the angle of the jaw and the highest point of the ridge above of the tympanum); (7) SOCH (supraorbital crest height, the distance between the angle of jaw and the highest point of the ridge at the mid-orbit); (8) NSD (nostril-snout distance, from the nostril to the tip of the snout); (9) IND (inter-nostril distance, distance between nostrils); (10) TD (tympanum diameter, from the posterior to the anterior edge of the tympanum); (11) FT (foot length, from the posterior edge of the metatarsal tubercle to the tip of the toe IV). Measurements were taken with digital calipers (to the nearest 0.01 mm). Two qualitative morphological characters were also analyzed: (1) vertebral apophyses (present/absent) and (2) bony knob at angle of jaws (present/absent).
Principal Components Analysis (PCA) and Discriminant Function Analysis (DFA) were used to assess morphometric differentiation between Chocó, upper Amazon, and Panama. To remove the effect of body size (SVL), the MANOVA and PCA were applied to the residuals from the linear regressions between the measured variables and SVL, for males and females separately. For the PCA, only components with eigenvalues > 1 were retained. All measurements were first subjected to the Shapiro-Wilk normality to test for normal distribution (Shapiro and Wilk 1965). Data not normally distributed were log-transformed. Levene’s test was used to determine if variables were homoscedastic (Levene 1960). Number of analyzed specimens were (1) Chocó: 43 males and 31 females, (2) Panama: 6 males and 8 females, (3) upper Amazon basin: 16 males and 16 females. All analyses were performed using JMP® 9.0.1 (SAS Institute 2010).
DNA extraction, amplification, and sequencing
Total DNA was extracted from muscle or liver tissue preserved in 95% ethanol or tissue storage buffer using standard guanidine thiocyanate protocol (M. Fujita, unpublished) with modifications. Polymerase Chain Reaction (PCR) was used to amplify the mitochondrial genes 12S rRNA, 16S rRNA, cytochrome c oxidase I (COI) and nuclear gene Tyrosinase (Tyr). PCR amplifications were carried out under standard protocols. Using standard primers developed by Bossuyt and Milinkovitch (2000), Goebel et al. (1999), Pauly et al. (2004), and Meyer et al. (2005). Amplicons were sequenced by Macrogen Inc., Seoul, Korea.
Phylogenetic analyses and genetic distances
Preliminary sequence alignment was done with Geneious Pro 5.4.6 (Drummond et al. 2011). The sequence matrix was imported to Mesquite 2.75 (Maddison and Maddison 2011) and the ambiguously aligned regions were adjusted manually to produce a parsimonious alignment. Phylogenetic trees were obtained using Bayesian Inference (BI) in MrBayes 3.1.2 (Ronquist and Huelsenbeck 2003) and Maximum Likelihood (ML) in Garli 2.0 (Zwickl 2006). The best-fit models of sequence evolution were selected under the Akaike information criterion (AIC) and the best partitioning scheme for the combined nucleotide data set and the models of character evolution for the BI and ML were estimated with PartitionFinder 1.0.1 (Lanfear et al. 2012). We ran three analyses: (1) the complete multi-locus data set, (2) only mitochondrial genes, (3) only the nuclear gene.
The Bayesian search consisted of two parallel runs each with 130 × 106 generations with four Markov chains. The convergence of the runs was assessed with Tracer 1.5 (Rambaut and Drummond 2007) evaluating the effective sample sizes and stopping when all post burn-in values were greater than 200. The first 10% of the sample was discarded as burn-in (Castañeda and Queiroz 2011).
For the ML analysis, we carried out 20 replicate searches and increased the setting “genthreshfortopoterm” until all searches resulted in similar likelihood values, indicating an efficient search (Zwickl 2006; final value was 200,000). Ten replicate searches started from stepwise trees and ten from random trees. The setting “limsprrange” was set to 10 (default = 6). Node support was assessed with non-parametric bootstrapping (Felsenstein 1983) with 100 pseudoreplicates with the same settings of the stepwise full search but with a single replicate per search. The 50% majority rule consensus for the bootstrap trees was obtained with Mesquite 2.75 (Maddison and Maddison 2011).
Uncorrected pairwise (p) genetic distances were obtained for gene 16S using software Mesquite 2.75 (Maddison and Maddison 2011). Missing and ambiguous sites were excluded. Genetic distances comparisons were based on gene 16S because it has been widely used as a barcode standard in amphibians (e.g. Vences et al. 2005). We assumed that genetic distances > 3% are suggestive of interspecific differentiation (Fouquet et al. 2007c). Genetic distances thresholds are problematic because they can lead to both false negatives and false positives in species identifications (Collins and Cruickshank 2013). We used the threshold only as a working hypothesis that was tested with morphological comparisons.
Results
Phylogenetic analyses
The complete matrix contained up to four genes and 3045 bp for 92 samples. For the complete data set, PartitionFinder chose seven partitions as the best strategy (best model in parenthesis): 12S (GTR + I + G), 16S (GTR + I + G), COI 1st position (TIMef + G), COI 2nd position (TVM + I + G), COI 3rd position (TrN + G), Tyr 1st and 2nd position (TrN + G), Tyr, 3rd position (TrN + I + G). For the mitochondrial analyses, the same five partitions were chosen, one for each ribosomal RNA gene and each codon position in COI. For the nuclear analysis, two partitions were chosen: Tyr, 1st and 2nd position and Tyr, 3rd position.
The tree topologies for the Maximum likelihood and Bayesian phylogenies were similar except for weakly supported nodes (posterior probability < 0.95 and bootstrap < 75). The Maximum Likelihood tree (Fig. 3) shows a basal divergence of Rhinella castaneotica, which is sister to two clades containing the remaining species of the Rhinella margaritifera species group. One clade is strongly supported in the Bayesian consensus (posterior probability = 1) although it has low bootstrap support (= 63). It contains three groups: Panama (posterior probability = 1.0, bootstrap = 100), Chocó (posterior probability = 1.0, bootstrap = 86) and upper Amazon (posterior probability = 1.0, bootstrap = 68). Chocó and Panama form clade sister to the upper Amazon clade. Both clades, which are on opposite sides of the Andes, are separated by pairwise genetic distances (uncorrected p for the mitochondrial gene 16S) ranging from 3.01 to 5.5% (average = 4.28, SD = 0.56). The genetic distances and the morphological differences (see next section) between the Chocó-Panama clade and the upper Amazon clade suggest that they are separate species. The 16S genetic distances between the Chocó and Panama clades range from 1.26 to 1.99% (average = 1.63, SD = 0.19). The relatively low genetic distances and the lack of morphological differences between their populations (see next section) indicate that they are conspecific. The Chocó populations further segregate latitudinally in two well-supported clades. One includes the populations in northern Ecuador (e.g. Reserva La Chiquita and Borbón) while the other includes central and southern populations (e.g. Manta Real and Valle Hermoso, Fig. 3).
Figure 3.
Maximum Likelihood phylogram depicting relationships within the Rhinella margaritifera species group. The phylogram was derived from the analysis of 3045 bp of mitochondrial (12S, 16S, COI) and nuclear (Tyr) genes. Numeric codes on terminals are individual collection numbers (associated data listed in Table 1). Posterior probabilities (above) and bootstrap values (below) are shown on branches except when they are < 0.50 and 50%, respectively. Abbreviations are: EC = Ecuador, FG = French Guyana, BR = Brazil, BO = Bolivia, PE = Peru, PA = Panama. Outgroups are not shown.
The sister clade to Chocó-Panama + Upper Amazon has weak support and includes other members of the Rhinella margaritifera group (Rhinella dapsilis, Rhinella hoogmoedi, Rhinella lescurei, Rhinella martyi, Rhinella ocellata, Rhinella paraguayensis and “Rhinella margaritifera”) from the Guiana region and Amazonian Brazil, Ecuador and Peru. Relationships among them are weakly supported on most branches.
The Maximum Likelihood tree based on mitochondrial genes (Fig. 4) has similar topology to the Maximum Likelihood tree derived from the analysis of the complete data set (Fig. 3). The Bayesian consensus tree, derived from the Tyrosinase gene, has definitely lower resolution (Appendix 2).
Figure 4.
Maximum Likelihood phylogram depicting relationships within the Rhinella margaritifera species group. The phylogram was derived from the analysis of 2495 bp of mitochondrial gene fragments (12S, 16S, COI). Numeric codes on terminals are individual collection numbers (associated data listed in Table 1). Bootstrap values appear above branches. The branches without numbers have bootstrap values < 50%. Abbreviations: EC = Ecuador, FG = French Guyana, BR = Brazil, BO = Bolivia, PE = Peru, PA = Panama. Outgroups are not shown.
Morphological analyses
Morphometric comparisons. Morphometric data from adults are summarized in Table 2. In the examined series, Amazonian males and females were significant larger than their counterparts from Chocó (Fig. 5; males Student’s t = -10.32, DF = 57 p < 0.001; females t = -13.12, DF = 45, p < 0.001) and Panama (males t = -8.7, DF = 22, p < 0.001; females t = -4.43, DF = 20, p < 0.001). There are no significant differences in SVL between Chocoan and Panamanian populations (males t = 1.37, DF = 47, p = 0.91; females t = -1.58, DF = 37, p = 0.06).
Table 2.
Descriptive statistics for morphometric measurements of adults from Rhinella margaritifera from Amazonian Ecuador and Rhinella alata from Chocó and Panama. Mean ± SD is given, with the range below. Abbreviations are: SVL = Snout-Vent Length; TL = Tibia Length; FL = Femur Length; HL= Head Length; HW = Head Width; STCH = Supratympanic Crest Height; SOCH = Supraorbital Crest Height; NSD = Nostril-Snout Distance; IND = Inter-Nostril Distance; TD = Tympanum Diameter; FT = Foot Length. All measurements are in mm.
| Rhinella margaritifera | Rhinella alata | |||||||
|---|---|---|---|---|---|---|---|---|
| Amazon | Chocó | Panamá | combined | |||||
| Morphometric measurements | Males (n = 16) |
Females (n = 16) |
Males (n = 43) |
Females (n = 31) |
Males (n = 6) |
Females (n = 8) |
Males (n = 49) |
Females (n = 39) |
| SVL | 45.6 ± 4.11 (54.36–39.88) |
68.90 ± 8.26 (77.97–55.42) |
36.66 ± 2.42 (43.25 –31.84) |
44.82 ± 4.42 (56.19–38.55) |
38.03 ± 0.59 (39.20–37.54) |
42.38 ± 3.82 (49.69–37.78) |
36.83 ± 2.31 (43.25–31.84) | 44.27 ± 4.37 (56.19–37.78) |
| TL | 18.73 ± 1.97 (23.13–15.14) |
29.36 ± 2.97 (34.26–24.01) |
15.98 ± 1.14 (18.72–13.69) |
18.26 ± 1.24 (20.73–16.22) |
15.86 ± 1.16 (18.12–15.09) |
17.79 ± 0.75 (18.99–16.41) |
15.97 ± 1.13 (18.72– 13.69) | 18.17 ± 1.16 (20.73–16.22) |
| FL | 19.67 ± 1.97 (23.84–16.15) |
29.33 ± 3.67 (35.34–22.75) |
15.69 ± 1.34 (19.28–13.09) |
18.16 ± 1.72 (22.04–15.18) |
16.39 ± 0.37 (17.01 –16.03) |
17.46 ± 0.67 (18.72–16.72) |
15.77 ± 1.27 (19.28–13.09) | 18.02 ± 1.58 (22.04–15.18) |
| HW | 16.9 ± 1.59 (19.93–14.77) |
25.88 ± 2.73 (30.69–21.01) |
12.57 ± 0.95 (15.14–10.31) |
15.10 ± 1.6 (18.94–12.49) |
12.98 ± 0.17 (13.3–12.8) |
14.90 ± 1.12 (17.23–13.79) |
12.63 ± 0.91 (15.14–10.31) | 15.06 ± 1.50 (18.94–12.49) |
| HL | 14.6 ± 1.28 (17.44–13.27) |
22.27 ± 2.71 26.51–17.94) |
11.61 ± 0.8 (13.88–10.29) |
13.67 ± 1.19 (16.84–11.85) |
11.85 ± 0.21 (12.2–11.54) |
13.18 ± 1.12 (15.45–11.77) |
11.64 ± 0.76 (13.88–10.29) | 13.57 ± 1.17 (16.84–11.77) |
| SOCH | 9.46 ± 0.86 (11.13–8.19) |
15.43 ± 2.02 (18.33–12.06) |
7.71 ± 0.59 (8.87–6.45) |
9.28 ± 0.86 (11.40–7.77) |
8.39 ± 0.21 (8.67–8.2) |
9.13 ± 0.49 (9.87–8.53) |
7.79 ± 0.59 (8.87–6.45) | 9.25 ± 0.79 (11.4–7.77) |
| STCH | 8.78 ± 1.55 (12.27–6.78) |
17.73 ± 3.26 (22.7–12.35) |
6.27 ± 0.54 (7.97–5.36) |
7.96 ± 0.68 (9.71–6.63) |
6.59 ± 0.31 (6.99–6.31) |
7.38 ± 0.39 (8.01–6.99) |
6.31 ± 0.52 (7.97–5.36) | 7.84 ± 0.67 (9.71–6.63) |
| NSD | 2.08 ± 0.44 (2.64–1.41) |
2.45 ± 0.42 (3.37–1.79) |
1.63 ± 0.29 (2.23–1.05) |
1.70 ± 0.21 (2.08–1.25) |
1.47 ± 0.17 (1.60–1.18) |
1.66 ± 0.16 (1.89–1.35) |
1.61 ± 0.28 (2.23–1.05) | 1.69 ± 0.20 (2.08–1.25) |
| IND | 3.35 ± 0.35 (3.89–2.70) |
3.12 ± 0.37 (3.73–2.59) |
2.50 ± 0.33 (3.23–1.86) |
2.80 ± 0.43 (3.98–2.16) |
2.41 ± 0.11 (2.59–2.31) |
2.42 ± 0.23 (2.63–2.08) |
2.48 ± 0.32 (3.23–1.86) | 2.72 ± 0.43 (3.98–2.08) |
| TD | 3.48 ± 0.24 (3.93–3.18) |
4.14 ± 0.21 (4.48–3.65) |
3.34 ± 0.47 (4.03–1.95) |
3.46 ± 0.59 (4.45–2.5) |
3.38 ± 0.20 (3.60–3.13) |
3.79 ± 0.25 (4.05–3.31) |
3.33 ± 0.45 (4.03–1.95) | 3.52 ± 0.55 (4.45–2.5) |
| FT | 16.87 ± 2.145 (21.85–13.76) |
24.87 ± 3.64 (28.86 –19.13) |
13.46 ± 1.12 (15.88–11.43) |
15.33 ± 1.52 (19.40–13.15) |
13.72 ± 0.68 (14.70–12.82) |
14.96 ± 0.76 (16.54–14.39) |
13.48 ± 1.07 (15.88–11.43) | 15.25 ± 1.39 (19.4–13.15) |
Figure 5.

Box and whisker plots showing snout-vent length variation in adult Rhinella margaritifera (upper Amazon) and Rhinella alata (Chocó and Panama). The central bar indicates the median, the interquartile range is shown by the box length, and the range is shown by the short horizontal lines (whiskers). SVL = snout-vent length. The black cross is the holotype of Rhinella alata.
Significant differences were observed in relative crest size between the Chocó-Panama and upper Amazon clades (Fig. 6). In the former, female supratympanic crest height had a range between 51.6 to 63.5% of head length (n = 39); in the later, range was 68.6 to 95.5% (n = 16). Ranges did not overlap and differences were significant (Wilcoxon’s Z = –5.77, p < 0.001). Male supratympanic crest height had a range between 49.3 to 59.8% of head length in Chocó-Panama (n = 49); in upper Amazon, range was 50.6 to 78.4% of head length (n = 16). Ranges overlapped but differences were significant (Wilcoxon’s Z = 3.11, p = 0.0018).
Figure 6.
Box and whisker plots showing relative size of supratympanic crests for adult Rhinella margaritifera (upper Amazon) and Rhinella alata (Chocó-Panama). The central bar indicates the median, the interquartile range is shown by the box length, and the range is shown by the short horizontal lines (whiskers). STCH = supratympanic crest height, HL = head length. The yellow cross is the holotype of Rhinella alata.
Three components with eigenvalues > 1.0 were extracted from the PCA for females (Table 3). The three components accounted for 67.3% of the total variation. The highest loadings of the PCA for females were supratympanic and supraorbital crest height, and tibia length for PC I, inter-nostril distance and tympanum diameter for PC II, and nostril-snout distance and inter-nostril distance for PC III. Three components with eigenvalues > 1.0 were extracted from the PCA in males (Table 3). The three components accounted for 63.3% of the total variation. The highest loadings for the PCA for males were head length and head width for PC I, inter-nostril distance and tympanum diameter for PC II, and tibia length and foot length PC III. The morphometric space of the Chocoan, upper Amazon, and Panamanian populations broadly overlaps in both males and females (Fig. 7).
Table 3.
Character loadings and eigenvalues for Principal Components (PC) Analysis. The analysis was based on ten size-corrected morphometric variables measured in Amazonian, Chocoan and Panamanian populations of the Rhinella margaritifera species group. Abbreviations are: TL = Tibia Length; FL = Femur Length; HL = Head Length; HW = Head Width; STCH = Supratympanic Crest Height; SOCH = Supraorbital Crest Height; NSD = Nostril-Snout Distance; IND = Inter-Nostril Distance; TD = Tympanum Diameter; FT = Foot Length. Bold figures indicate highest loadings.
| Variable | PCA Females | PCA Males | ||||
|---|---|---|---|---|---|---|
| PC I | PC II | PC III | PC I | PC II | PC III | |
| FL | 0.330 | 0.165 | 0.167 | 0.272 | 0.159 | 0.322 |
| FT | 0.334 | 0.214 | 0.418 | 0.061 | -0.038 | 0.661 |
| HL | 0.350 | -0.065 | 0.153 | 0.448 | -0.268 | -0.078 |
| HW | 0.343 | 0.132 | -0.288 | 0.446 | -0.222 | -0.045 |
| IND | -0.203 | 0.381 | 0.512 | 0.280 | 0.502 | -0.142 |
| NSD | 0.217 | 0.155 | -0.580 | 0.262 | 0.386 | -0.186 |
| SOCH | 0.368 | -0.067 | 0.190 | 0.423 | -0.071 | -0.082 |
| STCH | 0.411 | -0.154 | -0.039 | 0.409 | -0.290 | -0.045 |
| TD | 0.071 | 0.817 | -0.159 | 0.099 | 0.557 | -0.128 |
| TL | 0.368 | -0.200 | 0.232 | 0.134 | 0.228 | 0.610 |
| Eigenvalue | 4.411 | 1.192 | 1.128 | 2.800 | 1.947 | 1.585 |
| Cumulative variance (%) | 44.11 | 56.03 | 67.31 | 28.00 | 47.47 | 63.32 |
Figure 7.

Principal components extracted from the analysis of ten size-corrected morphological variables of adult Rhinella margaritifera (upper Amazon) and Rhinella alata (Chocó and Panama). The black cross is the holotype of Rhinella alata. See Table 3 for character loadings on each component.
In the DFA classification for females, 51 out of 55 females were assigned correctly to their geographic region. The four misclassified females from Ecuadorian Chocó were assigned to Panamanian populations. All specimens from the upper Amazon were correctly classified. In the DFA for males, 56 out of 65 males were correctly classified. The eight misclassified males from Ecuadorian Chocó were assigned to Panamanian populations and only one from upper Amazon to Panamanian populations. All males and females from Panama were correctly classified. The DFA analyses indicate that populations from the Ecuadorian Chocó are morphometrically very similar with those from Panama, both groups being markedly different from Rhinella margaritifera from the upper Amazon.
Finally, evidence of sexual dimorphism was found in relative crest size: females have larger cephalic crests than males (Fig. 6). The ratio supratympanic crest height/head length (STCH/HL) was significantly different between males and females in the Chocó-Panama clade (Wilcoxon’s Z = 5.15, p < 0.001) and the upper Amazon clade (Wilcoxon’s Z = -4.35, p < 0.001).
Qualitative morphological characters
The upper Amazon clade differs from the Chocó-Panama clade in having protruding vertebral apophyses in the dorsum and bony knobs at angle of jaws (both absent in the Chocó-Panama clade; Figs 8–10). The Chocó-Panama clade differs from other species of the Rhinella margaritifera group by a combination of an an absence of vertebral apophyses, an absence of bony knob at angle of jaws, low cranial crests, and the tympanum rounded or ovoid (see Systematic account section). A large number of specimens were examined (see Populations sampling section) and all conform to this characterization. Thus, it seems unlikely that there are additional species of the group in the Chocoan and Panamanian regions.
Figure 8.
Dorsolateral and ventral views of Rhinella alata from the Chocó region. A and C QCAZ 50568 (SVL 40.37 mm), adult female, La Concordia, Santo Domingo Province, Ecuador B and D QCAZ 37248 (SVL 40.23 mm), adult male, Valle Hermoso, El Oro Province, Ecuador. Not shown at the same scale. Photos by S.R. Ron.
Figure 10.
Dorsolateral views of Rhinella margaritifera from the Ecuadorian Amazon. Females: A QCAZ 55930 (SVL 80.15 mm) B QCAZ 55914 (SVL 72.49 mm), Lorocachi, Pastaza Province, Ecuador; males: C QCAZ 52343 (SVL 37.59 mm) D QCAZ 52344 (SVL 36.66 mm), Cascada San Rafael, Sucumbíos Province, Ecuador. Photos by S.R. Ron. Not shown at the same scale.
The holotype of Rhinella alata (Thominot, 1884) (Fig. 11) is an adult male with an SVL of 39.2 mm. It has poorly developed supratympanic crests and lacks bony knobs at the angle of jaws. The vertebral apophyses are inconspicuous. These characters and the location of its type locality (within 6 km of one of our examined populations) lead us to conclude that it is conspecific with the Panamanian and Chocoan populations examined herein.
Figure 11.
Dorsal (A), ventral (B), and lateral (C) views of the holotype of Rhinella alata. MNHN 84285, adult male, SVL = 39.2 mm.
Systematic account of Rhinella alata
Rhinella alata
(Thominot, 1884)
Bufo alatus Thominot, 1884. Holotype: MNHN 84285, adult male from Obispo, Panama.
Diagnosis.
Rhinella alata is a small-sized (Table 2; Figs 8 and 9) species of Rhinella having the following combination of characters: (1) average SVL of females 44.25 mm (SD = 4.36, n = 39), males 36.83 mm (SD = 2.31, n = 49); (2) bony knob at angle of jaws absent, corner of mouth angular; (3) supraorbital crests low and thick, continuous with preorbital crests; usually with crenulate texture on vertical surfaces; (4) supratympanic crests concave and small; their posterior edge usually next to the anterior border of parotoid glands; (5) canthus rostralis present but inconspicuous, sometimes continuous with preorbital crests; (6) parietal crests usually present, ill-defined; (7) heel reaching posterior margin of eye when hindlimbs adpressed; (8) vertebral apophyses no protruding; (9) snout subacuminate in dorsal view, from rounded to protruding in profile; (10) skin on dorsum bearing a mixture of warts, pustules, and minute tubercles; (11) mid-dorsal line from snout to vent often present; (12) spiculate tubercles on external border of shank, evident especially on females; (13) dorsolateral row of sharply pointed, conical tubercles between posterior border of parotoid glands and groin; (14) tympanic membrane and tympanic annulus distinct; moderately large, ovoid to round; (15) parotoid glands small, elongated posteriorly; (16) upper eyelid warty; (17) tarsal fold absent; (18) digits slender and long, with small knobs at tip; lateral fringes present; finger lengths 3 > 4 > 2 > 1; toe lengths 4 > 5 > 3 > 2 > 1; (19) nuptial pads present.
Figure 9.

Dorsolateral views of Rhinella alata. A Cerro Azul, Parque Nacional Chagres, Panama Province, Panama. Photo by Ángel Sosa B Cerro Bruja, Parque Nacional Portobelo, Colón Province, Panama. Photo by Ángel Sosa C Gamboa, Colón Province, Panama. Photo by Roberto Ibáñez.
Rhinella alata is most similar to Rhinella acutirostris. Both species differ from other members of the Rhinella margaritifera group by the absence of protruding vertebral apophyses, canthus rostralis not raised, snout projected, and low cranial crests. Rhinella acutirostris differs from Rhinella alata in having a bony knob at the angle of jaws (bony knob absent in Rhinella alata [Hoogmoed 1986, Lötters and Köhler 2000]). Rhinella alata differs from the holotype of Rhinella proboscidea (ZSM 1145/0) in having a less protruding snout and skin on dorsum bearing a mixture of warts, pustules, and minute tubercles (smooth skin in Rhinella proboscidea). Rhinella dapsilis is much larger than Rhinella alata (Rhinella dapsilis holotype SVL = 77 mm, adult male; Myers and Carvalho 1945) and has a fleshy proboscis in the snout (proboscis absent in Rhinella alata). Rhinella alata differs from Rhinella yunga in having tympanic membrane and annulus distinct (tympanic membrane and annulus absent in Rhinella yunga; Moravec et al. 2014). Rhinella hoogmoedi, Rhinella magnussoni, Rhinella martyi, Rhinella paraguayensis, Rhinella scitula, Rhinella sclerocephala, and Rhinella stanlaii have a bony knob at angle of jaws (Caramaschi and Pombal 2006, Lima et al. 2007, Fouquet et al. 2007a, Ávila et al. 2010, Caramaschi and Niemeyer 2003, Mijares-Arrutia and Arends-R 2001, Lötters and Köhler 2000; bony knob absent in Rhinella alata). Rhinella alata differs from Rhinella castaneotica, Rhinella margaritifera (sensu stricto) and Rhinella roqueana, by the absence of protruding vertebral apophyses (present in Rhinella castaneotica [Caldwell 1991], Rhinella margaritifera [Lavilla et al. 2013], and Rhinella roqueana [Melin 1941]).
Rhinella alata is most closely related to populations of Rhinella margaritifera from the upper Amazon basin in Ecuador and Peru. They can be easily distinguished by differences in body size (Fig. 5; see morphometric comparisons section) and relative size of cranial crests (Fig. 6).
Holotype.
The holotype is an adult male with SVL = 39.2 mm (Fig. 11). Descriptions of the holotype have been provided by Leavitt (1933) and Hoogmoed (1989). The bony knob at angle of jaws and vertebral apophyses are absent. The crests are low and thick. There is a dorsolateral row of conical tubercles from the posterior border of the parotoid gland to the groin. There is a clear mid-dorsal line from the snout to the vent. The tympanum is rounded.
Variation.
Variation in dorsal and ventral coloration of preserved specimens is shown in Figures 12 and 13. Background dorsal coloration varies from light gray (QCAZ 37244, AMNH 88689), light brown (QCAZ 14607, AMNH 104454) to dark gray (QCAZ 6733) or dark brown (QCAZ 11598, AMNH 52744), with irregular black and yellowish marks (QCAZ 4444, AMNH 88690). Some specimens have nearly uniform brown dorsum without marks (QCAZ 31603, 10296, AMNH 10296). A clear mid-dorsal line is often present (e.g. QCAZ 3502, QCAZ 12233).
Figure 12.

Rhinella alata from Ecuador showing variation in dorsal and ventral coloration of preserved specimens. Left to right, males: QCAZ 6733 (SVL 38.23 mm), QCAZ 10279 (SVL 35.08 mm); females, QCAZ 11598 (SVL 42.13 mm), QCAZ 14607 (SVL 50.95 mm), QCAZ 10439 (SVL 47.06 mm). See Appendix 1 for locality data. Not shown at the same scale.
Figure 13.
Rhinella alata from Panama showing variation in dorsal and ventral coloration of preserved specimens. Left to right, male: AMNH 89459 (SVL 37.54 mm); females, AMNH 88694 (SVL 41.21 mm), AMNH 55476 (SVL 41.19 mm), AMNH 104454 (SVL 49.69 mm), AMNH 88689 (SVL 42.75 mm), AMNH 20896 (SVL 42.98 mm). See Appendix 1 for locality data. Not shown at the same scale.
Ventral surfaces of preserved specimens have a cream to yellowish-cream background color with irregular darker marks arranged in diverse patterns; marks can be light gray (QCAZ 6734, AMNH 88689), light brown (QCAZ 6732, AMNH 104454), dark gray (QCAZ 31606) or dark brown (QCAZ 6733, AMNH 89459), and vary from being restricted to the anterior half of the body (QCAZ 31604, AMNH 89459) to being present over the entire venter (QCAZ 4445, AMNH 88694). A longitudinal mid-ventral cream thin stripe can be present in the gular region (QCAZ 31602, 31606) or from the gular region to the mid-venter (QCAZ 6731, 11598).
Head shape in dorsal view varies from elongated (QCAZ 11598, AMNH 89459) to subtriangular (QCAZ 4447, AMNH 55475); in lateral view it varies from rounded (QCAZ 31605, AMNH 52749) to protruding (QCAZ 11393, AMNH 55475). Canthal region coloration varies from light gray or light brown to dark gray or dark brown. In some individuals the area below the eye and tympanum is yellowish cream (QCAZ 4447, AMNH 20896) or brown (QCAZ 31603, AMNH 88694) and differs from the color of the dorsum. Cloacal tubercles vary from yellowish cream (QCAZ 4441, AMNH 20896), to gray (QCAZ 31606) or brown (QCAZ 31602, AMNH 88695).
Color in life.
Based on digital photograph of an adult female QCAZ 50568 (Fig. 8). Dark brown dorsum with irregular light brown and yellowish marks; there is a clear mid-dorsal line. Dorsal surfaces of tights and shanks are dark brown with transversal brown bands. Dorsal surfaces of forelimbs are dark brown with irregular light brown marks. Dark brown tubercles are abundant on the dorsum. Ventral surfaces vary from light brown to dark brown, with some irregularly distributed white and orange spots. The fingertips and the subarticular tubercles on fingers and toes are red-orange. Canthal region and tympanum are dark brown; iris greenish yellow with black reticulation.
Based on a digital photography of an adult male QCAZ 37248 (Fig. 8). Light brown dorsum with black spots and light brown and light gray marks. Dorsal surfaces of tights, shanks and forelimbs are light brown with transversal dark brown bands. Brown tubercles are abundant on the dorsum. Ventral surfaces are dark brown with irregularly distributed yellowish marks; the posterior part of the venter is cream. The subarticular tubercles of palms, soles, and fingertips are red-orange. Canthal region and tympanum are dark brown; iris greenish yellow with black reticulation.
Distribution and ecology.
Rhinella alata has been recorded at 37 localities in the Ecuadorian Chocó (Cañar, Carchi, El Oro, Esmeraldas, Manabí, Pichincha, and Santo Domingo Provinces; Fig. 1), one locality in the Colombian Chocó (Barbacoas, Nariño; see Taxonomic remarks) and 35 localities in Panama (Comarca Guna Yala and Provinces Coclé, Colón, Darién and Panama; Fig. 2). It has a wide elevation range, from 19 to 1500 m above sea level.
The examined specimens from Chocoan populations contain 21 gravid females (average SVL = 45.37 mm, SD = 4.05 mm): QCAZ 4262, QCAZ 4441, QCAZ 4442, QCAZ 4443, QCAZ 7065, QCAZ 10296, QCAZ 11597, QCAZ 11598 collected in January; QCAZ 50568 collected in February; QCAZ 11392, QCAZ 31601, QCAZ 31603, QCAZ 31605 collected in April; QCAZ 25023 collected in June; QCAZ 10439 collected in August; QCAZ 14607 collected in November; QCAZ 10301 collected in December. This suggests year round reproductive activity with a peak between January and April, a period that corresponds to the rainy season in the Ecuadorian Chocó.
In Panamanian populations gravid females were found in January (AMNH 104454), September (AMNH 55461), November (AMNH 88689), and December (AMNH 53699). In central Panama, Rhinella alata breeds in ponds and pools along permanent streams or swamps. Reproduction is explosive and most takes place from the middle of the rainy season to early dry season (Wells 1979, Ibáñez et al. 1999). Choruses last less than 24 hours with males usually calling at night and oviposition occurring by day, especially in the early afternoon (Wells 1979). Otherwise, individuals are primarily diurnal, found active on the leaf litter of the forest floor during daytime, and often found asleep on leaves of low vegetation at night (Ibáñez et al. 1999). Diet is specialized on ants (Toft 1981).
Most of the Ecuadorian specimens are from Reserva Mayronga and Reserva Ecológica Cotacachi-Cayapas. They were found in the leaf litter of secondary forest and in agricultural lands. Some adults were observed at night within the forest in vegetation above the ground and some were found in amplexus (QCAZ 10271, QCAZ 10274, QCAZ 10275 in November 1996, and QCAZ 31604, QCAZ 31605 in February 1996). All the specimens collected in Reserva Ecológica Cotacachi-Cayapas were found in secondary forest. At some collecting sites, the forest has been cleared for cacao plantations (QCAZ specimen database).
According to the classification of Sierra et al. (1999) the vegetation types for Ecuadorian localities are: (1) Lowland Evergreen Forest of Coastal Range, characterized by abundant epiphytes, climbers and herbaceous plants, with a canopy of 30 m (e.g. Reserva La Chiquita, Durango); (2) Semideciduous Lowland Forest of Coastal Range, defined by the presence of broad canopy trees up to 20 m and curved shafts; the tree stratum is characterized by the presence of spiny, deciduous species with epiphytes while the forest floor has herbaceous plants (e.g. Bilsa, La Tortuga); (3) Evergreen Foothill Forest of Coastal Range, characterized by a canopy that can reach 30 m or more and trunks of trees covered with orchids, bromeliads, ferns and aroids (e.g. Manta Real, Alto Tambo); (4) Deciduous Lowland Forest of Costal Range, characterized by losing leaves during part of the year with a great varieties of cactus and thorny plants; the most conspicuous trees are the family Bombacaceae have curved trunks and broad crown. (e.g. El Progreso); (5) Semideciduos Foothill Forest of Coastal Range, characterized by having slightly dispersed vegetation, with trees over 20 m and dense herbaceous layers of ferns (e.g. Valle Hermoso).
The main vegetation types for Panamanian localities are (following Hogan 2010): (1) Isthmian-Atlantic Moist Forests, characterized by tall tropical evergreen forest with buttressed canopy trees reaching 40 m and with an extremely rich epiphyte flora (e.g. Cruces Trail, Punta Rincón); (2) Eastern Panamanian Montane Forest, at elevations from 500 to 1800 m above sea level, includes marshes, swamp forests, semi-deciduous tropical moist forests, premontane wet forest, cloud forests and elfin forests (e.g. Cana, Cerro Tacarcuna); (3) Chocó-Darién Moist Forests, at elevations between 0 and 1000 m above sea level, between the Pacific Ocean and the western range of the Andes (e.g. Dad Nakue Dubpir, Udirbi).
Taxonomic remarks.
Based on morphological characters, Vélez-Rodriguez (2004) ascribed four populations from Panama and Colombia to Rhinella alata: Isthmus of Panama (Panama; 15 males, 10 females); Parque Nacional Los Katíos (Colombia; 12 males, 15 females); Gorgona and Güape Island (Colombia; 7 males, 8 females); Municipio Restrepo (Colombia; 7 males, 8 females). Based on data from Vélez-Rodriguez (2004), these populations differ from the holotype of Rhinella alata and populations of Rhinella alata in Ecuador and Panama (in parentheses) in having: (1) a canthus rostralis protruding in females and ill-defined in males (inconspicuous in males and females), (2) parietal crests well defined in females, ill-defined in males (ill-defined in males and females), (3) vertebral apophyses slightly visible externally (absent). The differences suggest that those specimens are not Rhinella alata and may belong to a different species. Alternatively, differences between Rhinella alata described by Vélez-Rodriguez (2004) and our study could be an artifact resulting from the use of distinct terminology for similar character states.
In contrast, Mueses-Cisneros and Moreno-Quintero (2012) reported two species of the Rhinella margaritifera group form Barbacoas, Nariño, Colombia (Rhinella sp. 9 and Rhinella sp. 10). Two photographs of live individuals (pp. 45) show morphological features that fall within the observed variation of Rhinella alata. We tentatively assign them to Rhinella alata but direct specimen examination is required to confirm this identification.
Discussion
The taxonomic status and phylogenetic position of populations traditionally ascribed to Rhinella margaritifera (= Bufo typhonius; e.g. Anderson 1945, Miyata 1982, Ortega-Andrade et al. 2010) from western Ecuador and Central America were reviewed. The examination of the holotype of Rhinella alata in combination with the morphological and genetic information from 72 populations from the Chocó region and Panama, indicate that those populations should be referred to Rhinella alata. The similarity between Chocoan and Panamanian populations was previously noted by Hoogmoed (1990).
Systematics and morphology
Hoogmoed (1990), Lescure and Marty (2000) and Fouquet et al. (2007b) considered that Rhinella margaritifera from French Guyana, with hypertrophied crests, corresponds to Rhinella margaritifera sensu stricto. In a recent review, however, Lavilla et al. (2013) assigned a neotype with the type locality in “Humaitá, State of Amazonas, Brazil”. In our phylogeny (Fig. 3), the sister clade of Rhinella ocellata include the closest localities to the new type locality for Rhinella margaritifera and are likely to contain populations of Rhinella margaritifera sensu stricto. Our phylogeny and previous reviews (e.g. Fouquet et al. 2007b) indicate that species diversity in the Rhinella margaritifera group is greatly underestimated. In our phylogeny, two Rhinella margaritifera from the southern Amazon in Ecuador (QCAZ 18241 and QCAZ 23917) are more closely related to Rhinella margaritifera from French Guyana and Rhinella dapsilis than to other Rhinella margaritifera from Amazonian Ecuador. They probably represent an undescribed species, characterized by the presence of vertebral apophyses, bony knobs at the angle of jaws, and poorly developed crests. More studies are needed to define the status of these populations, as well as that of Rhinella cf. paraguayensis from Bolivian and Brazilian Amazon and Rhinella cf. hoogmoedi from Brazilian Atlantic Forest.
The identity of the upper Amazon clade (Ecuador-Peru) remains unresolved. It was not possible to ascribe it unequivocally to any described species of the Rhinella margaritifera species group and it is unlikely to be Rhinella margaritifera sensu stricto (as defined by Lavilla et al. 2013). Thus, these populations may belong to an undescribed species characterized by having prominent supratympanic crests, conspicuous vertebral apophyses in the dorsum and bony knobs at angle of jaws (Fig. 10). We refrain from describing this species until genetic samples of Rhinella margaritifera sensu stricto are available and a comprehensive review of the group is carried out. For now, we suggest that these populations are referred as Rhinella margaritifera sensu lato.
These results raise some rather interesting questions. For instance, the complete distribution range of Rhinella alata is yet to be determined. Extensive and explicit studies are necessary to reveal whether the species is continuously distributed from Ecuador to Panama or if it consists one, two (or more) disjoint population nuclei. This would be an indispensable step before planning further studies on the evolutionary history or conservation status of the species. Moreover, future studies including a larger number of samples, more representative of the geographic range of each species within the Rhinella margaritifera group, from Colombia, Venezuela and Suriname, will help to clarify their evolutionary identity. It will also be necessary to re-evaluate, using molecular, morphological, ecological, behavioral, and phylogenetic analyses, the taxonomic status of species that have been previously described only morphologically such as Rhinella acutirostris, Rhinella magnussoni, Rhinella proboscidea, Rhinella roqueana, Rhinella sclerocephala, Rhinella scitula and Rhinella stanlaii. Integrative approaches like the one we pursued in this study will help to disentangle the complex evolutionary history, systematics, and taxonomy of this species group.
Biogeographic implications
Because all species in the Rhinella margaritifera species group are distributed in South America, it is reasonable to assume that the presence of Rhinella alata in Central America is the result of a single dispersal event from South America. The genetic distances between Chocoan and Panamanian populations are low (range 1.2–1.9%) and suggest that their divergence was recent and occurred after the closure of the Panamanian isthmus during the late Pliocene. Assuming a rate of evolution of the gene 16S of 0.00249–0.00277 substitutions per site per lineage per Myr (Evans et al. 2004; Lemmon et al. 2007), the divergence between these populations occurred ~ 2.16 to 3.42 Myr ago (under the 0.00277 rate) or ~ 2.41 to 3.81 Myr ago (under the 0.00249 rate). Thus, it is likely that the divergence between Panama and Chocó took place after the completion of the Panamanian Isthmus (~ 3.5 Myr ago; Coates et al. 1992, Coates and Obando 1996). These estimates of time of divergence, however, should be considered with extreme caution because they assume a molecular clock at a rate estimated for species in different families. Further explicit studies will be necessary to estimate divergence times with more confidence.
Rhinella alata is sister to populations of Rhinella margaritifera from the Ecuadorian and Peruvian Amazon and the eastern Andean slopes, up to 2000 m of elevation, forming altogether a robust clade. The two lineages are highly divergent from each other (uncorrected p distances 3.0–5.5%, mitochondrial gene 16S) and are morphologically distinctive. Therefore, both clades clearly represent separate species. Previously, Rhinella margaritifera was considered to occur on lowland rainforests east and west of the Andes of Ecuador. This distribution was atypical because out of 174 amphibian species inhabiting the Amazonian rainforests of Ecuador below 600 m of elevation, only three also occur in the rainforests of the Chocó region west of the Andes: Hypsiboas boans, Rhinella marina and Trachycephalus typhonius (Ron et al. 2014). Despite having similar environmental conditions and being geographically close (as low as 100 km of airline distance), rainforests on both sides of the Andes share few amphibian species, a result of the barrier effect of the Andes. Our results showing that Rhinella margaritifera only occurs on the eastern side demonstrate that their unusual distribution was an artifact of the incorrect delimitation of species boundaries. We suspect that the same problems could explain the disjunct distributions of Rhinella marina, Trachycephalus typhonius and Hypsiboas boans. Therefore, tropical rain forests of the Amazon and the Chocó may not share amphibian species.
Supplementary Material
Acknowledgments
This work was funded by Secretaría Nacional de Educación Superior, Ciencia, Tecnología e Innovación (Arca de Noé initiative) and Pontificia Universidad Católica del Ecuador. RI was supported by the Sistema Nacional de Investigación de Panama. We are particularly thankful to Annemarie Ohler, the Curator of Muséum National d’Histoire naturelle, who provided data and photos of the holotype of Rhinella alata. David Buckley for valuable comments on the text. Ángel Sosa and Mario Yánez-Muñoz shared photographs of Rhinella alata. Darrel Frost, Curator of AMNH, loaned specimens of Rhinella alata from Panama. Pablo Venegas, curator of CORBIDI, provided a tissue sample from Peru. Nadia Páez for help in taking measurements of specimens. We are thankful to Andrea Manzano and María Ordoñez for carrying laboratory work. For specimen collection and locality data, we are indebted to Néstor Acosta, Silvia Aldás, Alejandro Arteaga, Fernando Ayala, Alvaro Barragán, Paola Buitrón, David Cannatella, Edwin Carrillo, Luis Coloma, Rafael de Sa, Alexandra Endara, Jorge García, Stella de la Torre, Mireya Dimas, Sehoya Harris, César Jaramillo, Fidel Jaramillo, Diego Lombeida, Alfredo Lopez, Luis E. Lopez, Fernando Nogales, Giovanni Onore, Aida Ortiz, Alexandra Quiguango, Fabián Sáenz, Frank Solís, Samuel Sucre, Italo Tapia, Queti Tapia, Eduardo Toral, J. M. Touzet, Ana M. Velasco, and Tania Villegas.
Appendix 1
Examined material. Numbers in bold indicate specimens analyzed genetically and morphometrically.
Rhinella alata.— ECUADOR: PROVINCIA CAÑAR: Manta Real, Río Patul (2.5679°S, 79.3666°W), 350–400 m (QCAZ 3437, 3551, 4757–758); Manta Real (2.5537°S, 79.3642°W), 500 m (QCAZ 12778–779). PROVINCIA CARCHI: Vía Zumba–El Chota, 1500 m (QCAZ 12233). PROVINCIA EL ORO: Valle Hermoso, Parroquia Bella María (3.5019°S, 79.8172°W), 379 m (QCAZ 37244, 37248); El Progreso, vía Pasaje–Pan de Azúcar (3.2883°S, 79.7581°W), 180 m (QCAZ 10366). PROVINCIA ESMERALDAS: Lagarto, Mayronga Reserve (1.042°S, 79.28°W), 100 m (4262–4264, 4441–4451, 4709–4717, 6637–6642); Reserva Ecológica Bilsa (0.6202°S, 79.931°W), 534 m (QCAZ 6731–6743); Corriente Grande, Río Cayapas (0.6895°S, 78.9589°W), 70 m (QCAZ 10271, 10274–281, 10289, 10290, 10292, 10295–299, 10299, 10301); Reserva Ecológica Cotacachi Cayapas, Charco Vicente (0.6962°S, 78.9109°W), 60 m (QCAZ 3338–3339, 11391–396); Pichiyacu, Comunidad Chachi, Río Cayapas (0.9081°S, 78.998°W), 260 m (QCAZ 31602–609); Reserva Ecológica Cotacachi–Cayapas o Playa de Oro (0.8285°S, 78.722°W), 179 m (QCAZ 49381–382, 49387, 49391); Las Golondrinas near Río Canandé (QCAZ 12651–652); Durango, Río San José (1.054°S, 78.625°W), 33 m (QCAZ 24968–978); Río Onzole (0.712°S, 79.092°W), 110 m (QCAZ 10440–443); Comunidad Loma Linda, Río Onzole (0.8754°S, 79.0511°W), 95 m (QCAZ 10439); La Concordia (0.0022°S, 79.4105°W), 144 m (QCAZ 50573, 50568); San Lorenzo, Protectora La Chiquita (1.2333°S, 78.76°W), 60 m (QCAZ 10253, 10254–255, 11597, 11598); San Lorenzo, La pera del Guarapo (1.2684°S, 78.8067°W), 253 m (QCAZ 23161); La Pedorrera (0.4667°S, 79.9833°W), 53 m (QCAZ 25032); La Tortuga (0.591°S, 79.957°W), 86 m (QCAZ 25023); Borbón (1.0667°S, 79.05°W), 70 m (QCAZ 14607); Viche (0.6615°S, 79.5387°W), (QCAZ 4674); Durango (1.0427°S, 78.6245°W), (QCAZ 8549, 35250); 7 km western of Durango (1.0133°S, 78.6682°W) 220 m, (QCAZ 23164, 23623); Viruela, Rio Cayapas (1.1142°S, 78.9936°W), 45 m (QCAZ 10289); Al Tambo (0.9169°S, 79.5662°W) 253 m, (QCAZ 21138); El Milagro, La Mayronga (1.003°S, 79.326°W). PROVINCIA MANABÍ: El Carmen (0.274°S, 79.459°W). 300 m (QCAZ 7038–7039, 7065). PROVINCIA PICHINCHA: Reserva Forestal ENDESA (0.1667°S, 79,1667°W), 720 m (QCAZ 1659); Río Canoi (0.075°S, 79.051°W), 570 m (QCAZ 2745); 1 km E of Pedro Vicente Maldonado (0.0833°S, 79.039°W), 670 m, (QCAZ 2752); San Miguel de los Bancos (0.0166°S, 78.8833°W), (QCAZ 3813, 3815–818); San Miguel de los Bancos, Río Pitzará, 130 m (QCAZ 50846); km 9 San Miguel de los Bancos–Puerto Quito road (0.072°S, 78.9599°W), (QCAZ 5860); Puerto Quito, ENDESA (0.098°S, 79.117°W), (QCAZ 36827). PROVINCIA SANTO DOMINGO: Bosque Protector La Perla (0.057°S, 79.359°W), (QCAZ 3500–504); km 8 road to Santo Domingo (0.2005°S, 79.1924°W), 528 m (QCAZ 23621). PANAMA: COMARCA GUNA YALA: Dad Nakue Dubpir, Río Ogandí (9.2477°N, 78.1744°W), 150 m (CH 8842); Udirbi, Reserva Forestal (9.3167°N, 78.9833°W), 342 m (CH 1706); PROVINCIA COCLÉ: La Mina, Río Indio (8.9382°N, 80.1469°W), 48 m (CH 4922); near Río Tife cascade, Parque Nacional General de División Omar Torrijos Herrera (8.7065°N, 80.6352°W), 460 m (CH 0065); Obispo (9.1167°N, 79.6833°W) (MNHN 84285); Quebrada La Tiburcia, Cascajal (8.7158°N, 80.4605°W), 180 m (CH 5042); Quebrada La Varona, near Palmarazo (8.7342°N, 80.6565°W), 125 m (CH 5139). PROVINCIA COLÓN: Chitra, Santa Isabel (9.5186°N, 79.1534°W), 90 m (CH 7783); El Limón, Río Indio (8.9919°N, 80.1701°W), 19 m (CH 4967); Rinconcito, Punta Rincón (9.0135°N, 80.6884°W), 52 m (CH 1412); Río Caimito, Petaquilla (8.9706°N, 80.671°W), 54 m (CH 5476); Río Boquerón (9.3857°N, 79.4826°W), 150 m (AMNH 89459); Río Frijoles, Camino del Oleoducto, Parque Nacional Soberanía (9.1523°N, 79.7347°W), 67 m (CH 0307); road to Piña, after the represa Gatún (9.2603°N, 79.94°W), 34 m (CH 1679); Sta. Rosa and Guayabalito (9.1833°N, 79.65°W), 36 m (AMNH 55475); PROVINCIA DARIÉN: between Dos Bocas de Antaral and campsite on Serranía de Jingurudó (7.6564°N, 77.9986°W), <675 m (CH 4641); Cerro Tacarcuna, Río Pucuro (8.0011°N, 77.4852 °W), 640 m (AMNH 104454); Cana, trail to Boca de Cupé, Pinogana (7.7661°N, 77.6752°W), 518 m (CH 9104); Estación Pirre, Río Peresénico (8.0192°N, 77.7325°W), 90 m (CH 4057); Laguna Purriche (7.7222°N, 77.6555°W), 475 m (CH 6376); PROVINCIA PANAMA: Altos de Majé (AMNH 88689–8690, 88694); Barro Colorado (9.1636°N, 79.8378°W), 79 m (AMNH 20896, 5274, 55461–462); Parque Nacional Soberanía, Ancón (9.0764°N, 79.6594°W), 130 m (CH 9192); Chiva Chiva Road, Parque Nacional Camino de Cruces (9.0284°N, 79.5899°W), 41 m (CH 0491); Cruces trail (9.0453°N, 79.5892°W), 77 m (AMNH 55460); Finca Santa Bárbara, Nuevo Emperador, Arraiján (9.0011°N, 79.7235°W), 135 m (CH 1158); near Boquerón, Candelaria and Peluca (9.3671°N, 79.5546 °W) (AMNH 53699); near entrance to Chilibrillo Cave (9.1833°N, 79.6167°W) (AMNH 55476); Pacora (9.0833°N, 79.2833°W), 20 m (QCAZ 55481); Río Arraijancito (8.983°N, 79.6361°W), 110 m (CH 3980); Río Chico Masambí, Parque Nacional Soberanía, Ancón (9.0787°N, 79.6601°W), 135 m (MVUP 2299); Río Indio Arriba (8.6562°N, 80.1144°W), 645 m (CH 5005); San Juan de Pequení (9.3841°N, 79.5227°W), 100 m (CH 3702); stream near ACP Estación Río Chico (9.2636°N, 79.5097°W), 116 m (CH 6825); Tortí (8.9389°N, 78.4573°W), 95 m (MVUP 2256); Trinidad (8.7321°N, 79.9617°W), 420 m (CH 4313); Altos de Cerro Azul, Cerro Jefe (9.2284°N, 79.4046°W), 800 m (CH 3441).
Rhinella margaritifera.— ECUADOR: PROVINCIA ORELLANA: Parque Nacional Yasuní, Estación Científica Yasuní (0.6772°S, 76.4012°W), 230 m (QCAZ 8415, 17736, 17740, 41011); Parque Nacional Yasuní, Bloque 31 (0.942°S, 75.905°W), (QCAZ 11909); Parque Nacional Yasuní, Rio Yasuní (0.9248°S, 75.9152°W), 206 m (QCAZ 11940); Parque Nacional Yasuní, Via Pompeya-Iro (0.6536°S, 76.4536°W), 287 m (QCAZ 17216, 17329, 43011, 22401); Parque Nacional Yasuní, Apaika (0.8656°S, 75.9245°W), (QCAZ 33545); Estación Biológica Tiputini (0.0639°S, 76.1493°W), 250 m (QCAZ 10207); Nuevo Rocafuerte (0.8967°S, 75.437°W),186 m (QCAZ 39466); Añangu (0.5249°S, 76.3844°W), 255 m (QCAZ 43952–953); Chiroisla (0.58°S, 75.9177°W), 207 m (QCAZ 44318–319; Huiririma (0.7116°S, 75.6239°W), 194 m (QCAZ 44563–565). PROVINCIA PASTAZA: Río Bobonaza (1.8056°S, 77.3313°W), 250 m (QCAZ 10650); Kapawi Lodge (2.5387 °S, 76.8583°W), 239 m (QCAZ 25476, 25488–489); Pomona (1.625°S, 77.9072°W), 846 m (QCAZ 25631). PROVINCIA SUCUMBIOS: Reserva Limoncocha (0.4062°S, 76.6195°W), 261 m (QCAZ 43104, 43108); Pañacocha (0.4712°S, 76.0667°W), 255 m (QCAZ 44098–099). PROVINCIA NAPO: Reserva Yachana (0.8333°S, 77.1667 °W), 350 m (QCAZ 42269); Cascada de San Rafael (0.1036°S, 77.5808°W), 1300 m (QCAZ 31708). PROVINCIA MORONA SANTIAGO: Plan de Milagro (3.0011 °S, 78.5052°W), 1950 m (QCAZ 48242).
Appendix 2
Bayesian consensus phylogram depicting relationships within the Rhinella margaritifera species group. The phylogram was derived from the analysis of 550 bp of nuclear gene Tyrosinase. Museum catalog numbers are shown in Table 1. Abbreviations are: EC = Ecuador, FG = French Guyana, BR = Brazil, BO = Bolivia, PE = Peru, PA = Panama. Outgroups are not shown.
Citation
dos Santos SP, Ibáñez R, Ron SR (2015) Systematics of the Rhinella margaritifera complex (Anura, Bufonidae) from western Ecuador and Panama with insights in the biogeography of Rhinella alata. ZooKeys 501: 109–145. doi: 10.3897/zookeys.501.8604
References
- Ávila RW, Pansonato A, Strüssmann C. (2010) A new species of the Rhinella margaritifera group (Anura: Bufonidae) from Brazilian Pantanal. Zootaxa 2339: 57–68. [DOI] [PubMed] [Google Scholar]
- Anderson LG. (1945) Batrachians from East Ecuador collected 1937, 1938 by Wm. Clarke–MacIntyre and Rolf Blomberg. Arkiv för Zoologi 37: 1–88. [Google Scholar]
- Barrio–Amorós CL. (1999 “1998”) Sistemática y biogeografía de los anfibios (Amphibia) de Venezuela. Acta Biologica Venezuelica 18: 1–93. [Google Scholar]
- Barrio–Amorós CL. (2004) Amphibians of Venezuela. Systematic list. Distribution and references. Revista de Ecología Latino Americana 9: 1–48. [Google Scholar]
- Boulenger GA. (1885) Reptilia and Batrachia (1884). Zoological Record 21: 1–19. [Google Scholar]
- Bossuyt F, Milinkovitch MC. (2000) Convergent adaptive radiations in Madagascan and Asian ranid frogs reveal covariation between larval and adult traits. Proceedings of the National Academy of Sciences 97: 6585–6590. doi: 10.1073/pnas.97.12.6585 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Caldwell JP. (1991) A new species of toad in the genus Bufo from Para, Brazil, with an unusual breeding site. Papeis Avulsos de Zoologia 37: 389–400. [Google Scholar]
- Caramaschi U, Niemeyer H. (2003) Nova espécie do complexo de Bufo margaritifer (Laurenti, 1768) do Estado do Mato Grosso do Sul, Brasil (Amphibia, Anura, Bufonidae). Boletim do Museu Nacional 501: 1–16. [Google Scholar]
- Caramaschi U, Pombal Jr JP. (2006) A new species of Rhinella Fitzinger, 1826 from the Atlantic rain forest, eastern Brazil (Amphibia, Anura, Bufonidae). Papéis Avulsos de Zoologia 46(23): 251–259. doi: 10.1590/S0031-10492006002300001 [Google Scholar]
- Castañeda MR, de Queiroz K. (2011) Phylogenetic relationships of the Dactyloa clade of Anolis lizards based on nuclear and mitochondrial DNA sequence data. Molecular Phylogenetics and Evolution 61: 784–800. doi: 10.1016/j.ympev.2011.07.004 [DOI] [PubMed] [Google Scholar]
- Coates AG, Jackson JBC, Collins LS, Cronin TM, Dowsett HJ, Bybell LM, Jung P, Obando JA. (1992) Closure of the Isthmus of Panama: the near–shore marine record of Costa Rica and western Panama. Geological Society of America Bulletin 104: 814–828. doi: 10.1130/0016-7606(1992)104<0814:COTIOP>2.3.CO;2 [Google Scholar]
- Coates AG, Obando JA. (1996) The geologic evolution of the Central American Isthmus. In: Jackson JBC, Budd AF, Coates AG. (Eds) Evolution and Environment in Tropical America. University of Chicago Press, Chicago, 21–56. [Google Scholar]
- Collins RA, Cruickshank RH. (2013) The seven deadly sins of DNA barcoding. Molecular Ecology Resources 13: 969–975. doi: 10.1111/1755-0998.12046 [DOI] [PubMed] [Google Scholar]
- Drummond AJ, Ashton B, Buxton S, Cheung M, Cooper A, Duran C, Field M, Heled J, Kearse M, Markowitz S, Moir R, Stones–Havas S, Sturrock S, Thierer T, Wilson A. (2011) Geneious. Version 5.4. http://www.geneious.com/
- Evans BJ, Kelley DB, Tinsley RC, Melnick DJ, Cannatella DC. (2004) A mitochondrial DNA phylogeny of clawed frogs: phylogeography on sub–Saharan Africa and implications for polyploid evolution. Molecular Phylogenetics and Evolution 33(1): 197–213. doi: 10.1016/j.ympev.2004.04.018 [DOI] [PubMed] [Google Scholar]
- Felsenstein J. (1983) Statistical inference of phylogenies. Journal of the Royal Statistical Society 146: 246–272. doi: 10.2307/2981654 [Google Scholar]
- Fouquet A, Gaucher P, Blanc M, Vélez–Rodriguez CM. (2007a) Description of two new species of Rhinella (Anura: Bufonidae) from the lowlands of the Guiana Shield. Zootaxa 1663: 17–32. [Google Scholar]
- Fouquet A, Gilles A, Vences M, Marty C, Blanc M, Gemmell NJ. (2007c) Underestimation of species richness in neotropical frogs revealed by mtDNA analyses. PLoS Biology 2: . doi: 10.1371/journal.pone.0001109 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Fouquet A, Noonan BP, Rodrigues MT, Pech N, Gilles A, Gemmell NJ. (2012b) Multiple quaternary refugia in the eastern Guiana Shield revealed by comparative phylogeography of 12 frog species. Systematic Biology 61: 461–489. doi: 10.1093/sysbio/syr130 [DOI] [PubMed] [Google Scholar]
- Fouquet A, Recoder R, Teixeira M, Cassimiro Da Silva J, Amaro RC, Camacho Guerrero A, Damasceno R, Carnaval AC, Moritz C, Rodrigues MT. (2012a) Molecular phylogeny and morphometric analyses reveal deep divergence between Amazonia and Atlantic Forest species of Dendrophryniscus. Molecular Phylogenetics and Evolution 62: 826–838. doi: 10.1016/j.ympev.2011.11.023 [DOI] [PubMed] [Google Scholar]
- Fouquet A, Vences M, Salducci MD, Meyer A, Marty C, Blanc M, Gilles A. (2007b) Revealing cryptic diversity using molecular phylogenetics and phylogeography in frogs of the Scinax ruber and Rhinella margaritifera species groups. Molecular Phylogenetics and Evolution 43: 567–582. doi: 10.1016/j.ympev.2006.12.006 [DOI] [PubMed] [Google Scholar]
- Frost DR. (2014) Amphibian Species of the World: an Online Reference. Version 5.5. http://research.amnh.org/vz/herpetology/amphibia/
- Goebel AM, Donnelly JM, Atz M. (1999) PCR primers and amplification methods for 12S Ribosomal DNA, the Control Region, Cytochrome Oxidase I, and Cytochrome b in Bufonids and other frogs, and an overview of PCR primers which have amplified DNA in amphibians successfully. Molecular Phylogenetics and Evolution 11: 163–199. doi: 10.1006/mpev.1998.0538 [DOI] [PubMed] [Google Scholar]
- Gorzula S, Señaris JC. (1999 “1998”) Contribution to the herpetofauna of the Venezuelan Guayana, I: A data base. Scientia Guaianae 8: 1–129. [Google Scholar]
- Günther ACLG. (1858) Neue Batrachier in der Sammlung des britischen Museums. Archiv für Naturgeschichte, Berlin; 24: 319–328. [Google Scholar]
- Hass CA, Dunski JF, Maxson LR, Hoogmoed MS. (1995) Divergent lineages within Bufo margaritifera complex (Amphibia: Anura; Bufonidae) revealed by albumin immunology. Biotropica 2: 238–249. doi: 10.2307/2389000 [Google Scholar]
- Hogan MC. (2010) Ecoregions of Panama. In: Cleveland CJ. (Ed.) Encyclopedia of Earth. Environmental Information Coalition, National Council for Science and the Environment; http://www.eoearth.org/view/article/51cbed867896bb431f692a98/ [Google Scholar]
- Hoogmoed MS. (1986) Biosystematic studies of the Bufo “typhonius” group. A preliminary progress report. In: Rocek Z. (Ed.) Studies in Herpetology, Prague, 147–150. [Google Scholar]
- Hoogmoed MS. (1989) South American bufonids (Amphibia: Anura: Bufonidae), an enigma for taxonomists. Societat Catalana d’Ictiologia i Herpetologia 2: 167–180. [Google Scholar]
- Hoogmoed MS. (1990) Biosystematics of South American Bufonidae with special reference to the Bufo “typhonius” group. In: Peters G, Hutterer R. (Eds) Vertebrates in the Tropics. Museum Alexander Koenig, Bonn, Germany, 113–123. [Google Scholar]
- Ibáñez DR, Rand AS, Jaramillo ACA. (1999) Los Anfibios del Monumento Natural Barro Colorado, Parque Nacional Soberanía y Areas Adyacentes/The Amphibians of Barro Colorado Nature Monument, Soberanía National Park and Adjacent Areas. Editorial Mizrachi and Pujol, Panama. [Google Scholar]
- IUCN (2013) Conservation International and Nature Serve. Global Amphibian Assessment, 187 pp http://www.globalamphibians.org [Google Scholar]
- Jansen M, Bloch R, Schulze A, Pfenninger M. (2011) Integrative inventory of Bolivia’s lowland anurans reveals hidden diversity. Zoologica Scripta 40: 567–583. doi: 10.1111/j.1463-6409.2011.00498.x [Google Scholar]
- La Marca E. (1997) Lista actualizada de los anfibios de Venezuela. In: La Marca E. (Ed.) Vertebrados Actuales y Fósiles de Venezuela. Museo de Ciencia y Tecnología de Mérida; Mérida, Venezuela, 123–124. [Google Scholar]
- Lanfear R, Calcott B, Ho SYW, Guindon S. (2012) PartitionFinder: combined selection of partitioning schemes and substitution models for phylogenetic analyses. Molecular Biology and Evolution 29: 1695–1701. doi: 10.1093/molbev/mss020 [DOI] [PubMed] [Google Scholar]
- Laurenti JN. (1768) Specimen medicum, exhibens synopsin reptilium emendatam cum experimentis circa venena et antidota reptilium Austriacorum. Typ. Joan. Thom. Nob. de Trattnern, Caes. Reg. Aulae Typogr. et Bibliop, Viennæ, 214 pp. doi: 10.5962/bhl.title.5108 [Google Scholar]
- Lavilla EO, Caramaschi U, Langone J, Pombal JP, de Sá R. (2013) The identity of Rana margaritifera Laurenti, 1768 (Anura, Bufonidae). Zootaxa 3646: 251–264. doi: 10.11646/zootaxa.3646.3.4 [DOI] [PubMed] [Google Scholar]
- Leavitt BB. (1933) On three races of Bufo typhonius. Copeia 1933: 7–8. doi: 10.2307/1436176 [Google Scholar]
- Lemmon EM, Lemmon AR, Cannatella DC. (2007) Geological and climatic forces driving speciation in the continentally distributed trilling chorus frogs (Pseudacris). Evolution 61: 2086–103. doi: 10.1111/j.1558-5646.2007.00181.x [DOI] [PubMed] [Google Scholar]
- Lescure J, Marty C. (2000) Atlas des Amphibiens de Guyane. Collections Patrimoines Naturels 45: 1–388. [Google Scholar]
- Levene H. (1960) Robust Tests for Equality of Variances. In: Olkin I, Ghurye SG, Hoeffding W, Madow WG, Mann HB. (Eds) Contributions to Probability and Statistics: Essays in Honor of Harold Hotelling. Stanford University Press, 278–292. [Google Scholar]
- Lima AP, Menin M, Araújo MC. (2007) A new species of Rhinella (Anura: Bufonidae) from Brazilian Amazon. Zootaxa 1663: 1–15. [Google Scholar]
- Lötters S, Köhler J. (2000) A new toad of the Bufo typhonius complex from humid montane forests of Bolivia. Spixiana 23: 293–303. [Google Scholar]
- Maddison WP, Maddison DR. (2011) Mesquite: a modular system for evolutionary analysis. Version 2.75. http://mesquiteproject.org/
- Melin DE. (1941) Contributions to the knowledge of the Amphibia of South America. Göteborgs Kungl. Vetenskaps-och Vitterhets-samhälles. Handlingar. Serien B, Matematiska och Naturvetenskapliga Skrifter 1: 1–71. [Google Scholar]
- Mendelson III JR, Mulcahy DG, Williams TS, Sites JW. (2011) A phylogeny and evolutionary history of Mesoamerican toads (Anura: Bufonidae: Incilius) based on morphology, life history, and molecular data. Zootaxa 3138: 1–34. [Google Scholar]
- Meyer CP, Geller JB, Paulay G. (2005) Fine scale endemism on coral reefs: archipelagic differentiation in turbinid gastropods. Evolution 59: 113–125. doi: 10.1111/j.0014-3820.2005.tb00899.x [PubMed] [Google Scholar]
- Mijares-Urrutia A, Arends-R A. (2001) A new toad of the Bufo margaritifer complex (Amphibia: Bufonidae) from northwestern Venezuela. Herpetologica 57: 523–531. [Google Scholar]
- Miyata K. (1982) A checklist of the amphibians and reptiles of Ecuador with a bibliography of Ecuadorian herpetology. Smithsonian Herpetology 54: 1–70. doi: 10.5479/si.23317515.54.1 [Google Scholar]
- Moravec J, Lehr E, Cusi JC, Córdova JH, Gvoždík V. (2014) A new species of the Rhinella margaritifera species group (Anura, Bufonidae) from the montane forest of the Selva Central, Peru. ZooKeys 17(371): 35–56. doi: 10.3897/zookeys.371.6580 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Myers GS, de Carvalho AL. (1945) Notes on some new or little-known Brazilian amphibians, with an examination of the history of the Plata salamander, Ensatina platensis. Boletim do Museu Nacional 35: 1–24. [Google Scholar]
- Mueses-Cisneros JJ, Moreno-Quintero V. (2012) Fauna anfibia de la reserva natural biotopo selva húmeda, Barbacoas, Nariño, Colombia. Herpetotropicos 7: 39–54. [Google Scholar]
- Narvaes P, Rodrigues MT. (2009) Taxonomic revision of Rhinella granulosa species group (Amphibia. Anura. Bufonidae) with a description of a new species. Arquivos de Zoologia Museu de Zoologia da Universidade São Paulo 40: 1–73. doi: 10.11606/issn.2176-7793.v40i1p1-73 [Google Scholar]
- Ortega-Andrade HM, Bermingham J, Aulestia C, Paucar C. (2010) Herpetofauna of the Bilsa Biological Station, province of Esmeraldas, Ecuador. Check List 6: 119–154. [Google Scholar]
- Ortiz DA, Ron SR, Coloma LA. (2013) Rhinella margaritifera. In: Ron SR, Guayasamín JM, Yanez-Munoz M, Merino-Viteri A, Ortiz DA. (Eds) AmphibiaWebEcuador. Version 2014.0. Museo de Zoología, Pontificia Universidad Católica del Ecuador; http://zoologia.puce.edu.ec/vertebrados/anfibios/FichaEspecie.aspx?Id=1176/ [Google Scholar]
- Pauly GB, Hillis DM, Cannatella DC. (2004) The history of a Nearctic colonization: Molecular phylogenetics and biogeography of the Nearctic toads (Bufo). Evolution 58(11): 2517–2535. doi: 10.1554/04-208 [DOI] [PubMed] [Google Scholar]
- Pramuk JB. (2006) Phylogeny of South American Bufo (Anura: Bufonidae) inferred from combined evidence. Zoological Journal of the Linnean Society 146: 407–452. doi: 10.1111/j.1096-3642.2006.00212.x [Google Scholar]
- Rambaut A, Drummond AJ. (2007) Tracer–MCMC Trace Analysis Tool. Version v1.4. http://tree.bio.ed.ac.uk/software/tracer/
- Ron SR, Guayasamin JM, Yánez-Muñoz MH, Merino-Viteri A, Ortiz DA, Nicolalde DA. (2014) AmphibiaWebEcuador. Version 2014.0. Museo de Zoología, Pontificia Universidad Católica del Ecuador; http://zoologia.puce.edu.ec/Vertebrados/anfibios [accessed 15 June 2014] [Google Scholar]
- Ron SR, Read M. (2011) Trachycephalus typhonius. In: Ron SR, Guayasamín JM, Yanez-Munoz M, Merino-Viteri A, Ortiz DA. (Eds) AmphibiaWebEcuador. Version 2014.0. Museo de Zoología, Pontificia Universidad Católica del Ecuador; http://zoologia.puce.edu.ec/Vertebrados/anfibios/FichaEspecie.aspx?Id=1356 [Google Scholar]
- Ronquist F, Huelsenbeck JP. (2003) Mrbayes 3: Bayesian phylogenetic inference under mixed models. Bioinformatics 19(3): 1572–1574. doi: 10.1093/sysbio/sys029 [DOI] [PubMed] [Google Scholar]
- Ruiz-Carranza PM, Ardila-Robayo MC, Lynch JD. (1996) Lista actualizada de la fauna de Amphibia de Colombia. Revista de la Academia Colombiana de Ciencias 20: 365–415. [Google Scholar]
- Santos JC, Coloma LA, Summers K, Caldwell JP, Ree R, Cannatella DC. (2009) Amazonian amphibian diversity is primarily derived from late Miocene Andean lineages. PLoS Biology 7(3): 448–461. doi: 10.1371/journal.pbio.1000056 [DOI] [PMC free article] [PubMed] [Google Scholar]
- SAS Institute (2010) User guide. SAS Institute. Cary. Version 8.01. http://www.jmp.com/
- Shapiro SS, Wilk MB. (1965) An analysis of variance test for normality (Complete Samples). Biometrika 52: 591–611. doi: 10.1093/biomet/52.3-4.591 [Google Scholar]
- Sierra R, Cerón C, Palacios W, Valencia R. (1999) Mapa de vegetación del Ecuador Continental 1:1’000.000. Proyecto INEFAN/GEF–BIRF, Wildlife Conservation Society y Ecociencia, Quito, 174 pp. [Google Scholar]
- Simmons JE. (2002) Herpetological collecting and collection management. Herpetological Circular 31: 1–153. [Google Scholar]
- Slade RW, Moritz C. (1998) Phylogeography of Bufo marinus from its natural and introduced ranges. Proceedings of the Royal Society of London Series B-Biological Sciences 265(1398): 769–777. doi: 10.1098/rspb.1998.0359 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Solis F, Ibañez R, Jaramillo C, Fuenmayor Q, Silvano DL, Coloma LA, La Marca E, Ron SR, Hoogmoed MS. (2010) Rhinella margaritifera. IUCN Red List of Threatened Species. [accessed 15 January 2015]
- Spix JB. (1824) Animalia nova sive species novae testudinum et ranarum quas in itinere per Brasiliam annis MDCCCXVII–MDCCCXX jussu et auspiciis Maximiliani Josephi I Bavariae Regis. F. S. Hübschmann, München, 146 pp. [Google Scholar]
- Thominot A. (1884) Note sur un batracien despèce nouvelle provenant de Panama. Bulletin de la Société Philomathique de Paris 8: 151–152. [Google Scholar]
- Toft CA. (1981) Feeding ecology of Panamanian litter anurans: patterns in diet and foraging mode. Journal of Herpetology 15: 139–144. doi: 10.2307/1563372 [Google Scholar]
- Vélez–Rodríguez CM. (2004) Sistemática de los sapos neotropicales pertenecientes al grupo Bufo typhonius (Amphibia: Bufonidae). PhD Thesis, Universidad Austral de Chile, Valdivia, Chile. [Google Scholar]
- Vences M, Thomas M, van der Meijden A, Chiari Y, Vieites DR. (2005) Comparative performance of the 16S rRNA gene in DNA barcoding of amphibians. Front Zool 2: . doi: 10.1186/1742-9994-2-5 [DOI] [PMC free article] [PubMed] [Google Scholar]
- Wells KD. (1979) Reproductive behavior and male mating success in a Neotropical toad, Bufo typhonius. Biotropica 11: 301–7. doi: 10.2307/2387922 [Google Scholar]
- Wiens JJ, Fetzner JW, Parkinson CL, Reeder TW. (2005) Hylid frog phylogeny and sampling strategies for speciose clades. Systematic Biology 54: 719–748. doi: 10.1080/10635150500234625 [DOI] [PubMed] [Google Scholar]
- Zwickl DJ. (2006) Genetic algorithm approaches for the phylogenetic analysis of large biological sequence datasets under the maximum likelihood criterion. PhD Thesis, University of Texas at Austin, Austin, United States of America. [Google Scholar]
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