Giant Anteater, Myrmecophaga Tridactyla
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Giant anteater, Myrmecophaga tridactyla Compiler: Vinicius Alberici Contributors: Arnaud L.J. Desbiez, Adriano G. Chiarello, Davi Teles. Suggested citation: Alberici, V. et al. (2020). Survival Blueprint for the conservation of the giant anteater, Myrmecophaga tridactyla, in the Brazilian Cerrado. An output from the Anteaters & Highways Project, Brazil, and EDGE of Existence fellowship, Zoological Society of London, London, UK. 1. STATUS REVIEW 1.1 Taxonomy: Class: Mammalia Order: Pilosa Suborder: Vermilingua Family: Myrmecophagidae Genus: Myrmecophaga Species: Myrmecophaga tridactyla Linnaeus, 1758 There are three sub-species recognized by Gardner (2007): Myrmecophaga tridactyla artata Osgood, 1912 Myrmecophaga tridactyla centralis Lyon, 1906 Myrmecophaga tridactyla tridactyla Linnaeus, 1758 Common name(s): Giant Anteater (English) Oso Hormiguero (Spanish) Tamanduá-bandeira (Portuguese) 1.2 Distribution and population status: 1.2.1 Global distribution: The giant anteater (Myrmecophaga tridactyla) is endemic to the Neotropical region, occurring throughout South and Central America, but absent from North America (Wetzel 1985; Emmons and Feer 1997; Einsenberg and Redord 1999; Gardner 2005). According to Shaw and McDonald (1987), the species was more widely distributed in the early Pleistocene – a fossil found in Sonora (Mexico) indicates that the giant anteater participated in the Great American Exchange, after the formation of the Isthmus of Panama, which allowed the migration of numerous species between North and South America, previously isolated. Subsequently, there was a reduction in the species’ range, probably due to climate and habitat changes associated with the retraction of glaciers (McCain, 2001). Currently, records of giant anteaters in Central America are historical, rare, or anecdotal and it is more likely that the species is extinct from most of its original extent. While occurring throughout most part of South America, the giant anteater has also been suffering from local extinctions, especially in the southern limits of its range. Population estimate Population trend Country Distribution Notes (plus references) (plus references) There is a successful reintroduction program Formosa, in Iberá Natural Jujuy, Misiones, Salta, Reserve, in Corrientes Possibly extinct in Santa Fé, Santiago del (Di Blanco et al 2015) Chaco, Córdoba, Argentina Estero, Tucumán (Miranda Decreasing Corrientes, Entre Ríos et al 2014); Mostly open See also: Jimeno, (Miranda et al 2014) areas, but also found in Amaya (2009); forests (Gallo et al 2017) Fonseca, Aguiar (2004); Bauni et al (2013) Possibly extinct Belize - - - (Miranda et al 2014) Pando, Beni, northern Cochabamba, Santa Cruz and eastern Tarija and probably eastern Chuquisaca (Anderson 1997), Chiquitano forests, Pantanal (Brooks et al 2001), Chiquitan and Bolivia Unknown Decreasing - Chaco transition zones (Koysdar et al 2014), Noël Kempff National Park (Emmons et al 2014), Gran Chacho Kaa-Iya National Park in Santa Cruz, Madidi National Park in La Paz (Quiroga et al 2016) Acre, Alagoas, Amapá, Amazonas, Bahia, Ceará, Goiás, Maranhão, Mato Grosso, Mato Grosso Possibly extinct in do Sul, Minas Gerais, Pará, Espírito Santo, Rio de Paraíba, Paraná, Brazil Janeiro, Rio Grande Decreasing - Pernambuco, Piauí, Rio do Sul, Santa Catarina Grande do Norte, (Miranda et al 2014) Rondônia, Roraima, São Paulo, Sergipe, Tocantins (Miranda et al 2014) Mainland (Miranda et al Figel et al (2015) 2014), mainly present in documented an the east of Andes expansion of c. 430 (Orinoquía and Amazonia km in the species’ regions), but also in the distribution limits, Colombia Unknown Caribe, Pacífica and Decreasing including populations Andina regions (Sandoval- that inhabit the Gomez et al 2012; López et Magdalena river al 2013; Rojano-Bolaño et valley, between the al 2015; Pacheco et al central and eastern 2017) Andes Sighting reports are from the late 1970s and early 1980s, all in Mainland (Miranda et al protected and forested 2014); Corcovado National areas (Timm et al Park, Rincón de La Vieja Costa Rica Unknown Decreasing 2009). Martínez et al National Park, La Selva (2017) documents that Biological Station (Timm et the species was never al 2009) common in the country, with isolated records Mainland (Miranda et al Ecuador Unknown 2014); Yasuni Biosphere Decreasing - Reserve (Blake et al 2012) Not included in the Possibly extinct latest checklist of land El Salvador - - (Miranda et al 2014) mammals (Owen, Girón 2012). Paracou Research Station in Cayenne (Voss et al French Unknown 2001); forested areas in Decreasing - Guiana Saint-Laurent-du-Maroni (De Thoisy et al 2008) Possibly extinct Guatemala - - - (Miranda et al 2014) Rupununi river region Guiana Unknown Decreasing - (Fragoso et al 2016) First known record is Mainland (Miranda et al from 1996, when an 2014); Río Plátano adult giant anteater Biosphere Reserve (RBRP) was captured by (McCain, 2011; Gonthier, Honduras Unknown Decreasing Miskitos in RBRP to Castañeda, 2013; Martinez be sold in Asia, but et al 2020), Colón, Gracias then was released a Dios, Olancho (Reyes et back into the wild al 2010) (McCain 2001) Miskito people do not Mainland (Miranda et al consume giant 2014); Forests (Genoways, anteaters, but some Nicaragua Unknown Timm 2003); Bosawas Decreasing animals are killed Biosphere Reserve (Koster because they et al 2008) represent a threat to domestic hunting dogs Although it is present in Goldman’s Mammals of Panama (1920), the giant Panama Unknown Unknow Decreasing anteater was considered rare by Handley’s checklist (1966) Historically, the giant anteater was present throughout the country, but according to Smith (2007), it has suffered local extinctions due to Chaco and Pantanal Paraguay Unknown Decreasing hunting pressure regions (Smith 2007) mainly in the east. Abba and Vizcaíno (2008) list eight specimens in Paraguay, but all of them with imprecise locations Amazon region (Grimwood 1968); Tambopata (Naughton-Treves et al 2003); Manu Biosphere Peru Unknown Reserve, Madre de Dios Decreasing - (Boddicker & Amanzo 2002); San Martin and Amazonas (Allgas et al 2015) Kwamalasamutu region See Husson (1978) Suriname Unknown Decreasing (Gajapersad et al 2012) First record is from late 1990s, in Cerro Largo, followed by others in Rivera and Tacuarembó, all in the Possibly extinct Uruguay - - north of the country. It (Miranda et al 2014) is now considered extinct (Fallabrino, Castiñeira 2006). See also: Ameneiros et al (2015) See Allen (1904) and Mainland (Miranda et al Venezuela Unknown Decreasing Montgomery and 2014); Llanos Lubin (1977) Figure 1. Global distribution of the giant anteater (Myrmecophaga tridactyla), according to the latest assessment by IUCN (Miranda et al 2014). Figure 2. Presence records (in red) of the giant anteater (Myrmecophaga tridactyla) throughout Central and South America (Santos et al 2019). 1.2.2 Local distribution: Although historically the giant anteater occurred in all Brazilian biomes (Paglia et al., 2012), today the taxon is considered possibly extinct in the Pampas and almost extinct in the Atlantic Forest and Caatinga (Miranda et al 2015). Although relatively stable in the Pantanal and Amazon, their population has been drastically reduced in the Cerrado, one of the strongholds for giant anteaters. Figure 3. Local distribution of the giant anteater (Myrmecophaga tridactyla) in Brazil (Miranda et al 2015). The table below indicate some strictly protected areas (IUCN categories I-III) in the Brazilian states within the Cerrado, where the presence of the giant anteater has been confirmed. It is important to note, however, that the species is also present outside protected areas, where information about its occurrence and abundance is very scarce. Country Region / Population Site Level of Protection Reference(s) Notes /Region province size Boqueirão da Onça, Chapada Diamantina National Park, Campos et al Brazil / Grande Sertao Strictly protected areas 2019; Dias et Bahia Unknown Cerrado Veredas (IUCN categories I-III) al 2019 National Park, Serra das Confusões National Park Diniz, Brito Distrito Brasilia National Strictly protected area 2013; Unknown Federal Park (IUCN category III) Lacerda et al 2009. Bechara et al., 2002; Collevatti et Density of 0.2 al., 2007; ind. / km² Emas National Redford, (Miranda et al Park, Chapada Strictly protected area 1985; Silveira 2006) and 0.64 Goiás Unknown dos Veadeiros (IUCN category III) et al., 1999; ind. / km² National Park Silveira et al, (Silveira et al 2003; Vynne 1999) in Emas et al., 2009; National Park Zimbres et al., 2012. Gurupi Biological Reserve, Elildo Chapada das Strictly protected area Carvalho- Maranhão Mesas National Unknown (IUCN category I-III) Junior 2015 Park, Pers. Comm. Nascentes do Rio Parnaíba National Park Rio das Mortes Xavante Leeuwenberg Mato Reserve, Strictly protected area 1997; Prada, Unknown Grosso Chapada dos (IUCN category I-III) Marinho- Guimarães Filho 2004. National Park Nascimento, Campos 2011; Emas National Rodrigues et Mato Park, Serra da Strictly protected area al 2002; Grosso Unknown Bodoquena (IUCN category III) Anteaters do Sul National Park, and Highways Project; Ascensão 2017; 2019 Serra da Canastra National Park, Schneider et Grande Sertão Density of 1-2 al 2000; Veredas ind./km² for Shaw et al Minas National Park, Strictly protected area Serra da Unknown 1987; Young, Gerais Sempre-Vivas (IUCN category I-III) Canastra Coelho 2003; National Park, National Park Nascimento, Rio Preto State (Saw et al Campos Park, Veredas