The IUCN Red List of Threatened Species™ ISSN 2307-8235 (online) IUCN 2008: T3038A47437046 Bradypus variegatus, Brown-throated Sloth Assessment by: Moraes-Barros, N., Chiarello, A. & Plese, T. View on www.iucnredlist.org Citation: Moraes-Barros, N., Chiarello, A. & Plese, T. 2014. Bradypus variegatus. The IUCN Red List of Threatened Species 2014: e.T3038A47437046. http://dx.doi.org/10.2305/IUCN.UK.20141.RLTS.T3038A47437046.en Copyright: © 2015 International Union for Conservation of Nature and Natural Resources Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale, reposting or other commercial purposes is prohibited without prior written permission from the copyright holder. For further details see Terms of Use. 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THE IUCN RED LIST OF THREATENED SPECIES™ Taxonomy Kingdom Phylum Class Order Family Animalia Chordata Mammalia Pilosa Bradypodidae Taxon Name: Bradypus variegatus Schinz, 1825 Common Name(s): • English: • French: • Spanish: Brown-throated Sloth, Bolivian Three-toed Sloth, Brown-throated Three-toed Sloth Aï De Bolivie, Bradype, Paresseux Tridactyle, Paresseux Tridactyle De Bolivie Guasa, Perezoso Bayo, Perezoso Grisaceo, Perezoso Tridáctilo Taxonomic Notes: According to Gardner (2007) seven subspecies are recognized: B. v. boliviensis (Gray, 1871); B.v. brasiliensis Blainville, 1840; B.v. ephippiger R.A. Philippi, 1870; B.v. gorgon O. Thomas, 1926; B.v. infuscatus Wagler, 1831; B.v. trivittatus Cornalia, 1849; and B.v. variegates Schinz, 1825. Assessment Information Red List Category & Criteria: Least Concern ver 3.1 Year Published: 2014 Date Assessed: October 6, 2013 Justification: Bradypus variegatus is listed as Least Concern in view of its wide distribution including a large part of the Amazon forest, presumed large population, its occurrence in a number of protected areas, and because it is unlikely to be declining fast enough to qualify for listing in a threatened category. Previously Published Red List Assessments 2013 – Least Concern (LC) 2008 – Least Concern (LC) 2006 – Least Concern (LC) 1996 – Lower Risk/least concern (LR/lc) Geographic Range Range Description: Bradypus variegatus ranges from Honduras in the north, through southern Central America. In South America, it ranges from Colombia into western and southern Venezuela, and south into Ecuador, eastern Peru and Bolivia, into Brazil and northern Argentina (where it is now considered to be extirpated). Its distribution overlaps with B. torquatus in the central part of the Atlantic forest (Hirsch and Chiarello 2012). In Brazil, the species currently occurs in forested areas of the Amazon, Atlantic forest, and © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 1 possibly in the contact zones between these biomes and Cerrado. There are historical records of B. variegatus in the Caatinga biome (Moraes-Barros unpublished data 2010). There are no confirmed records for B. variegatus in the Pantanal biome of Brazil, but the species might occur in the contact zones between this biome and the Amazon forest to the north. Additional field studies are necessary in order to properly define the current species distribution in the Cerrado, Caatinga and Pantanal. The southernmost distribution of this sloth in Brazil was reported by Cabrera (1957) as the state of Rio Grande do Sul, which could, however, not be confirmed (Gardner 2007). It is historically absent from the state of Santa Catarina (Brazil) and northeastern Argentina; the southernmost confirmed record of the species is near Londrina, in the state of Paraná, Brazil, but today it is considered extinct in this state (Mikich and Bernils 2004). The last record from Argentina was collected in Jujuy province and dates back to 1916 (Vizcaíno et al. 2006), but field studies specifically aiming at this species are lacking from this country. Bradypus variegatus is found from sea level to at least 2,400 m asl (Ureña et al. 1986). Country Occurrence: Native: Bolivia, Plurinational States of; Brazil (Acre, Alagoas, Amazonas, Bahia, Brasília Distrito Federal, Ceará, Espírito Santo, Goiás, Maranhão, Mato Grosso, Mato Grosso do Sul, Minas Gerais, Pará, Paraíba, Paraná, Pernambuco, Piauí, Rio de Janeiro, Rio Grande do Norte, Rondônia, Roraima, São Paulo, Sergipe, Tocantins); Colombia; Costa Rica; Ecuador; Honduras; Nicaragua; Panama; Peru; Venezuela, Bolivarian Republic of Possibly extinct: Argentina (Jujuy) © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 2 Distribution Map © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 3 Population Population densities of B. variegatus have been estimated at 2.2 to 6.7 animals per hectare in the Brazilian Amazon (Queiroz 1995), 8.5 animals per hectare in Panama (Montgomery and Sunquist 1975), 0.6 to 4.5 animals per hectare in the tropical dry forest of Colombia (Acevedo and Sanchez 2007) and 0.7 animals per hectare on Isla Palma, Valle, Colombia (Carvajal-Nieto et al. 2013). No demographic information is available from the remaining area of distribution. Bradypus variegatus is commonly found in public squares, where densities can reach 12.5 animals per hectare (Manchester and Jorge 2009). Recent phylogeographic studies reveal that B. variegatus from the Central American, Western Amazon and Atlantic forests constitute distinct and unique evolutionary units that are distinguishable by molecular and morphological traits. Current Population Trend: Unknown Habitat and Ecology (see Appendix for additional information) Bradypus variegatus has been recorded from a number of forest types including seasonal mesic tropical forest, semi-deciduous forest (inland Atlantic Forest), cloud forest, and lowland tropical forest. It inhabits cacao (Theobroma cacao) plantations in Costa Rica (Vaughan et al. 2007, Ramirez et al. 2011). This sloth species produces one litter of one infant at intervals of at least 19 months (T. Plese pers. comm. 2010). Mating period varies depending on the year and geographical region, but occurs mainly in spring (i.e., from July to November in South America and from February to May in Central America). Systems: Terrestrial Use and Trade (see Appendix for additional information) In Brazil, especially in the northeastern region and in the Amazon, and in Colombia the common sloth is hunted and sold in public markets as food, medicine, and as a pet species. In several touristic sites, B. variegatus is used by locals to entertain visitors. Threats (see Appendix for additional information) It appears that there are no major threats to B. variegatus at the global level. Nevertheless, some subpopulations, especially in Colombia and the Atlantic Forest in Brazil, are declining due to deforestation leading to severe habitat degradation and fragmentation. The lowest levels of genetic diversity of the species were observed in the Atlantic Forest; they were similar to the levels observed in the Critically Endangered Bradypus pygmaeus (Silva 2013). Furthermore, they are hunted by local indigenous communities. Wild-caught individuals, especially offspring, are sold as pets to tourists in Colombia (Moreno and Plese 2006). This illegal trade is increasing and represents a cause of concern due to its impact on the wild populations. Mortality on roads also occurs. Conservation Actions (see Appendix for additional information) Bradypus variegatus is present in many protected areas. It is included in CITES Appendix II. Credits © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 4 Assessor(s): Moraes-Barros, N., Chiarello, A. & Plese, T. Reviewer(s): Abba, A.M. & Superina, M. Contributor(s): González-Maya, J.F. Facilitators(s) and Compiler(s): Superina, M. © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 5 Bibliography Acevedo, J.F. and Sanchez, D.P. 2007. Abundancia y preferencia de hábitat de Bradypus variegatus y Choloepus hoffmanni, durante la época seca en Arboletes, Antioquia. Universidad de Antioquia. Anderson, R.P. and Handley Jr., C.O. 2001. A new species of three-toed sloth (Mammalia: Xenarthra) from Panama, with a review of the genus Bradypus. Proceedings of the Biological Society of Washington 114: 1-33. Anderson, R.P. and Handley Jr., C.O. 2002. Dwarfism in insular sloths: biogeography, selection, and evolutionary rate. Evolution 56: 1045–1058. Baillie, J. and Groombridge, B. (comps and eds). 1996. 1996 IUCN Red List of Threatened Animals. IUCN, Gland, Switzerland and Cambridge, UK. Bezerra, B.M., Souto, A.S., Halsey, L.G. and Schiel, N. 2008. 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University of Florida Press, Gainesville, FL, USA. Eisenberg, J.F. 1989. Mammals of the Neotropics. The Northern Neotropics. The University of Chicago Press, Chicago, USA and London, UK. Eisenberg, J.F. and Redford, K.H. 1999. Mammals of the Neotropics: The Central Neotropics. The University of Chicago Press, Chicago, USA. Emmons, L.H. and Feer, F. 1997. Neotropical Rainforest Mammals: A Field Guide, Second edition. University of Chicago Press, Chicago, IL, USA. Ferreira, F.S., Fernandes-Ferreira, H., Léo Neto, N.A., Brito, S.V. and Alves, R.R.N. 2013. The trade of medicinal animals in Brazil: current status and perspectives. Biodiversity and Conservation 22: 839-870. Gardner, A.L. 1993. Order Xenarthra. Smithsonian Institution Press, Washington, DC, USA. Gardner, A.L. 2005. Order Pilosa. The Johns Hopkins University Press, Baltimore, Maryland, USA. Gardner, A.L. 2007. Magnorder Xenarthra. In: A.L. Gardner (ed.), Mammals of South America, pp. 127176. The University of Chicago Press, Chicago. Gilmore, D., Duarte, D.F. and Peres da Costa, C. 2008. The physiology of two- and three-toed sloths. In: S.F. Vizcaíno and W. J. Loughry (eds), The biology of the Xenarthra, pp. 130-142. University Press of Florida, Gainesville. Hall, E.R. 1981. The Mammals of North America. John Wiley and Sons, New York, USA. © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 6 Hayssen, V. 2010. Bradypus variegatus (Pilosa: Bradypodidae). Mammalian Species 42(850): 19-32. Hirsch, A. and Chiarello, A.G. 2012. The endangered maned sloth (Bradypus torquatus) of the Brazilian Atlantic forest: a review and update of geographical distribution and habitat preference. Mammal Review 42: 35-54. IUCN. 2014. The IUCN Red List of Threatened Species. Version 2014.1. Available at: www.iucnredlist.org. (Accessed: 12 June 2014). Lord, R. 2000. Wild mammals of Venezuela. Armitano Editores, C. A., Caracas, Venezuela. Losada, T. 2007. Conocimiento local y uso sobre los perezosos por la comunidad indígena Jusy Monilla Amena, Amazonas - Colombia. Facultad de Estudios Ambientales y Rurales, Pontificia Universidad Javeriana. Manchester, A. and Jorge, W. 2009. Biological data of a population of sloths (Bradypus variegatus) in a square of Teófilo Otoni, Minas Gerais, Brazil. Naturalia 32: 81-86. Medri, I.M., Mourão, G.M. and Rodrigues, F.H. 2006. Ordem Xenarthra. In: Reis, N. R., Perachi, A. L., Petro, W. A. and Lima, I. P. (eds), Mamíferos do Brasil, pp. 71-99. Universidade Estadual de Londrina, Londrina. Mikich, S.B. and Bernils, R.S. 2004. Livro Vermelho do Fauna Ameaçada no Estado do Paraná. Instituto Ambiental do Paraná, Curitiba, Brazil. Montgomery, G.G. and Sunquist, M.E. 1975. Impact of sloths on Neotropical forest energy flow and nutrient cycling. In: F.B. Golley and E. Medina (eds), Tropical ecological systems; trends in terrestrial and aquatic research, pp. 69-98. Springer-Verlag, Berlin. Moraes-Barros, N., Giorgi, A.P., Silva, S. and Morgante, J. S. 2010. Reevaluation of the geographical distribution of Bradypus tridactylus Linnaeus, 1758 and B. variegatus Schinz, 1825. Edentata 11(1): 5361. Moraes-Barros, N., Miyaki, C.Y. and Morgante, J.S. 2002. Genetic diversity in different populations of sloths assessed by DNA fingerprinting. Brazilian Journal of Biology 62: 503-508. Moraes-Barros, N., Miyaki, C.Y. and Morgante, J.S. 2007. Identifying management units in nonendangered species: the example of the sloth Bradypus variegatus Schinz, 1825. Brazilian Journal of Biology 67(4): 829-837. Moraes-Barros, N., Silva, J.A.B., Miyaki, C.Y. and Morgante, J.S. 2006. Comparative phylogeography of the Atlantic forest endemic sloth (Bradypus torquatus ) and the widespread three-toed sloth (Bradypus variegatus) (Bradypodidae, Xenarthra). Genetica 126: 189-198. Moreno, S. and Plese, T. 2005. Distribución actual e histórica, uso de hábitat y estimación del estado de conservación del perezoso de tres uñas (Bradypus variegatus) en el área de jurisdicción de Corantioquia. Fundación UNAU, Corantioquia, Medellín. Moreno, S. and Plese, T. 2006. The illegal traffic in sloths and threats to their survival in Colombia. Edentata 6: 10-18. Noss, A., Cuéllar, E., Tarifa, T., Vargas, J. and Aliaga-Rossel, E. 2010. Myrmecophagidae, Cyclopedidae, Bradypodidae y Megalonychidae. In: R.B. Wallace, H. Gómez, Z.R. Porcel and D. I. Rumiz (eds), Distribución, ecología y conservación de los mamíferos medianos y grandes de Bolivia, pp. 213-234. Centro de Ecología Difusión Simón I. Patiño, Santa Cruz de la Sierra, Bolivia. Pacheco, V., de Macedo, H., Vivar, E., Ascorra, C.F., Arana-Cardó, R. and Solari, S. 1995. Lista anotada de © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 7 los mamíferos peruanos. Occasional Papers in Conservation Biology 2: 1-35. Queiroz, H.L. de. 1995. Preguiças e Guaribas: Os mamíferos folívoros arborícolas do Mamirauá. Conselho Nacional de Desenvolvimento Cientifico e Tecnológico e Sociedade Civil Mamirauá, Brasília e Tefé, Brazil. Ramirez, O., Vaughan, C., Herrera, G. and Guries, R. 2011. Temporal and spatial resource use by female three-toed sloths and their young in an agricultural landscape in Costa Rica. Revista de Biologia Tropical 59: 1743-1755. Redford, K.H. and Eisenberg, J.F. 1992. Mammals of the Neotropics, The Southern Cone: Chile, Argentina, Uruguay, Paraguay. University of Chicago Press, Chicago, USA. Reid, F. 1997. A field guide to the mammals of Central America and southeast Mexico. Oxford University Press, New York, USA. Romero, M., Cabrera, E. and Ortiz, N. 2008. Informe sobre el estado de la biodiversidad en Colombia 2006-2007. Instituto de Investigación Alexander Von Humboldt, Bogotá, Colombia. Silva, S. 2013. Contribuições para a conservação de Bradypus variegatus (preguiça comum): processos históricos e demográficos moldando a diversidade nuclear. Universidade de São Paulo. Taube, E., Keravec, J., Vié, J.-C. and Duplantier, J.-M. 2001. Reproductive biology and postnatal development in sloths, Bradypus and Choloepus: review with original data from the field (French Guiana) and from the captivity. Mammalian Review 31(3): 173-188. Tirira, D. 1999. Mamiferos del Ecaudor. Museo de Zoologia, Centro de Biodiversidad y Ambiente, Pontifica Universidad Católica del Ecaudor and Sociedad para la Investigación y Monitoreo de la Biodiversidad Ecuatoriana, Quito, Ecuador. Tirira, D.G. 2007. Guía de Campo de los Mamíferos del Ecuador. Ediciones Murciélago Blanco. Publicación especial sobre los mamíferos del Ecuador 6, Quito, Ecuador. Ureña, H.M., Chacón, C.R., Faerrón, A.S. and Lizano, S.T. 1986. Hallazgo de Bradypus griseus y Choloepus hoffmanni (Edentata: Bradypodidae) en tierras altas de Costa Rica. Revista de Biología Tropical 34: 165166. Vaughan, C., Ramirez, O., Herrera, G. and Guries, R. 2007. Spatial ecology and conservation of two sloth species in a cacao landscape in Limón, Costa Rica. Biodiversity and Conservation 16: 2293-2310. Vizcaíno, S.F., Abba, A.M. and García Esponda, C.M. 2006. Magnaorden Xenarthra. In: R.M. Barquez, M.M. Díaz and R.A. Ojeda (eds), Los mamíferos de Argentina: sistemática y distribución, pp. 46-56. Sociedad Argentina para el estudio de los Mamíferos (SAREM), San Miguel de Tucumán, Argentina. Citation Moraes-Barros, N., Chiarello, A. & Plese, T. 2014. Bradypus variegatus. The IUCN Red List of Threatened Species 2014: e.T3038A47437046. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en Disclaimer To make use of this information, please check the Terms of Use. External Resources © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 8 For Images and External Links to Additional Information, please see the Red List website. © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 9 Appendix Habitats (http://www.iucnredlist.org/technical-documents/classification-schemes) Habitat Season Suitability Major Importance? 1. Forest -> 1.6. Forest - Subtropical/Tropical Moist Lowland Resident Suitable Yes 1. Forest -> 1.7. Forest - Subtropical/Tropical Mangrove Vegetation Above High Tide Level Resident Suitable No 1. Forest -> 1.8. Forest - Subtropical/Tropical Swamp Resident Suitable No 1. Forest -> 1.9. Forest - Subtropical/Tropical Moist Montane Resident Suitable No 14. Artificial/Terrestrial -> 14.3. Artificial/Terrestrial - Plantations Resident Suitable No Use and Trade (http://www.iucnredlist.org/technical-documents/classification-schemes) End Use Local National International Food - human Yes Yes No Medicine - human & veterinary Yes No No Pets/display animals, horticulture Yes Yes No Threats (http://www.iucnredlist.org/technical-documents/classification-schemes) Threat Timing Scope Severity Impact Score 2. Agriculture & aquaculture -> 2.1. Annual & perennial non-timber crops -> 2.1.2. Small-holder farming Ongoing Minority (50%) - - Stresses: 1. Ecosystem stresses -> 1.1. Ecosystem conversion 1. Ecosystem stresses -> 1.2. Ecosystem degradation Ongoing Minority (50%) Stresses: 1. Ecosystem stresses -> 1.1. Ecosystem conversion 1. Ecosystem stresses -> 1.2. Ecosystem degradation Ongoing - Stresses: 1. Ecosystem stresses -> 1.1. Ecosystem conversion 1. Ecosystem stresses -> 1.2. Ecosystem degradation 2. Agriculture & aquaculture -> 2.1. Annual & perennial non-timber crops -> 2.1.3. Agro-industry farming 2. Agriculture & aquaculture -> 2.3. Livestock farming & ranching -> 2.3.2. Small-holder grazing, ranching or farming © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en - - - - 10 2. Agriculture & aquaculture -> 2.3. Livestock farming & ranching -> 2.3.3. Agro-industry grazing, ranching or farming 4. Transportation & service corridors -> 4.1. Roads & railroads 5. Biological resource use -> 5.1. Hunting & trapping terrestrial animals -> 5.1.1. Intentional use (species is the target) Ongoing Minority (50%) - Stresses: 1. Ecosystem stresses -> 1.1. Ecosystem conversion 1. Ecosystem stresses -> 1.2. Ecosystem degradation Ongoing Minority (50%) Stresses: 2. Species Stresses -> 2.1. Species mortality Ongoing Minority (50%) Stresses: 2. Species Stresses -> 2.1. Species mortality Negligible declines Unknown - Low impact: 4 Unknown Conservation Actions in Place (http://www.iucnredlist.org/technical-documents/classification-schemes) Conservation Actions in Place In-Place Research, Monitoring and Planning Action Recovery plan: No Systematic monitoring scheme: No In-Place Land/Water Protection and Management Conservation sites identified: Yes, over entire range Occur in at least one PA: Yes Area based regional management plan: No Invasive species control or prevention: No In-Place Species Management Harvest management plan: No Successfully reintroduced or introduced beningly: No Subject to ex-situ conservation: No In-Place Education Subject to recent education and awareness programmes: Yes Included in international legislation: Unknown Subject to any international management/trade controls: Yes Conservation Actions Needed (http://www.iucnredlist.org/technical-documents/classification-schemes) © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 11 Conservation Actions Needed 2. Land/water management -> 2.1. Site/area management Research Needed (http://www.iucnredlist.org/technical-documents/classification-schemes) Research Needed 1. Research -> 1.1. Taxonomy 1. Research -> 1.2. Population size, distribution & trends 1. Research -> 1.3. Life history & ecology 3. Monitoring -> 3.1. Population trends Additional Data Fields Distribution Continuing decline in area of occupancy (AOO): Yes Estimated extent of occurrence (EOO) (km²): 10000000 Continuing decline in extent of occurrence (EOO): Unknown Lower elevation limit (m): 0 Upper elevation limit (m): 2400 Population Population severely fragmented: No Habitats and Ecology Continuing decline in area, extent and/or quality of habitat: Unknown Generation Length (years): 6 © The IUCN Red List of Threatened Species: Bradypus variegatus – published in 2014. http://dx.doi.org/10.2305/IUCN.UK.2014-1.RLTS.T3038A47437046.en 12 The IUCN Red List Partnership The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership. 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