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Baudo Guan Penelope ortoni
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This species qualifies as Endangered because of continued intensive habitat loss and hunting, from which very rapid population declines are suspected.

Taxonomic source(s)
del Hoyo, J.; Collar, N. J.; Christie, D. A.; Elliott, A.; Fishpool, L. D. C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Barcelona, Spain and Cambridge UK: Lynx Edicions and BirdLife International.
SACC. 2006. A classification of the bird species of South America. Available at: #

66 cm. Shy, drab, medium-sized , long-tailed cracid. All rich brown with greyish-brown tinge to neck and head and fine whitish edging to foreneck and breast. Bare blue ocular area, prominent red dewlap, and dull red legs. Similar spp. Smaller and duller than other sympatric Penelope spp.. Similar-sized Sickle-winged Guan Chamaepetes goudotii lacks red dewlap and whitish breast streaks. Voice Call at dawn a far-carrying guttural bawling waou (Jahn et al. 2002, Jahn et al. in press). Mates and family members warn each other of an approaching human with low, soft, and prolonged rising whistles (Jahn et al. in press). Rarely heard alarm call is a repeated and agitated konh-konh-konh-konh (resembling other Penelope species) (Jahn et al. 2002, Jahn et al. in press).

Distribution and population
Penelope ortoni has been recorded locally along the west Andean foothills and slopes throughout west Colombia and in Ecuador, south to Naranjal, Guayas (Vaurie 1968, Hilty and Brown 1986), and possibly to Buenaventura, El Oro (P. Coopmans in litt. 1998). In Colombia, recent reports are from Chocó (B. López-Lanús in litt. 2000), Valle del Cauca (N. Gómez in litt. 1999, A. Cortés per E. Fierro in litt. 2012) and Nariño (Hellmayr and Conover 1942, Salaman and Giles 1995). In Ecuador, there are no confirmed recent records south of Pichincha, where it occurs in the Mindo-Nambillo area, but the majority of modern records are from Esmeraldas (Best et al. 1996, Velasco-Abad 1997, Sharpe 1999, Jahn and Mena 2002, Jahn et al. 2002, Idrobo-Medina et al. 2006, Jahn in press, Jahn et al. in press). Its range and population have undoubtedly contracted greatly.

Population justification
The Ecuadorian population was estimated at 2,500-7,500 mature individuals in 2002. On the basis of extensive visual and auditory transect-mapping samples (1997-2006) in Esmeraldas, Ecuador, extrapolated global population size was estimated at 7,000-21,000 mature individuals, roughly equivalent to 10,000-32,000 individuals in total. In remote premontane forest, about 0.5-1.5 territories were counted per transect kilometre. However, the species is usually extirpated within about 2-5km around human settlements (O. Jahn in litt. 2007, P. Mena Valenzuela in litt. 2007). Transects in Ensenada de Utria in 2010 estimated a total density of 0.56 individuals / km2 (O. Cortes in litt. 2012).

Trend justification
A very rapid population decline is suspected to have occurred over the last three generations on the basis of rates of habitat loss and hunting pressure.

It inhabits early to late successional stage humid and wet forest from the tropical to the temperate zone, mostly between 70-1,500m (Hellmayr and Conover 1942, Delacour and Amadon 1973, Hilty and Brown 1986, Jahn et al. in press), with wanderers recorded up to 3,100 m (Idrobo-Medina et al. 2006, O. Jahn  in litt. 2007). In Esmeraldas and Azuay, it has been recorded on the coastal plain and in rolling lowland hills, but only near the base of the Andes (Delacour and Amadon 1973, (Hellmayr and Conover 1942, Paynter 1993, Jahn 2001, Jahn in press). However, due to hunting pressure it is now usually restricted to steep slopes adjacent to level ground and mountain ridges (Idrobo-Medina et al. 2006, O. Jahn  in litt. 2007, P. Mena V. in litt. 2007). The guan's daily activities include all forest strata (Idrobo-Medina et al. 2006, O. Jahn  in litt. 2007, P. Mena V. in litt. 2007): at dawn it vocalizes and performs courtship displays from the canopy; around noon it tends to stay at medium levels, hiding from predators such as eagles, and it feeds on fruits and seeds from the ground level up to the canopy. Breeding pairs are territorial, and post-breeding birds live in family groups, usually numbering around four individuals, exceptionally more (Idrobo-Medina et al. 2006). Available data suggest this species breeds between July and September, with the clutch numbering two eggs (Haffer 1968, Salaman 1994, Salaman et al. 2000, Jahn and Mena 2002, Jahn et al. 2002, Idrobo-Medina et al. 2006, Jahn et al. in press).

This species is extremely sensitive to habitat modification and hunting (Jahn 2001, P. Salaman in litt. 2003, O. Cortes in litt. 2012). It usually does not flee if approached by humans, making it an easy bag for hunters (Jahn and Mena 2002). Large parts of its range have long since been deforested and plans to colonise and develop more remote regions are progressing through the rapid expansion of the road network (Dodson and Gentry 1991, Salaman 1994, Salaman and Stiles 1996, WWF and IUCN 1994-1997, Jahn in press). Colonisation is in turn increasing the impact of small-scale agriculture, illegal coca plantations, selective logging, hunting for food and gold mining (Salaman 1994, Salaman and Giles 1995, Salaman and Stiles 1996, WWF and IUCN 1994-1997, Idrobo-Medina et al. 2006, P. G. W. Salaman in litt. 1999, 2000), which is already affecting some key protected areas (Jahn and Mena 2002, Idrobo-Medina et al. 2006, Jahn in press, O. Jahn  in litt. 2007). Industrial-scale logging and intensive agriculture, especially oil palm and banana plantations and cattle-farming are major threats (Salaman 1994, Salaman and Stiles 1996, P. Coopmans in litt. 1998, Bowen-Jones et al. 1999, Sharpe 1999, P. G. W. Salaman in litt. 1999, 2000), and have already transformed over 90% of the Ecuadorian landscape below 900 m (Dodson and Gentry 1991). Large tracts of its western Ecuadorian range are being purchased from local communities, denuded of forest and converted to industrial oil palm plantations (Sharpe 1999). New legislation and the transfer of land-rights to local communities has been exploited by large businesses, for whom it has become cheap and easy to buy land (Bowen-Jones et al. 1999, P. G. W. Salaman in litt. 1999, 2000). The construction of pipelines and hydroelectric dams is also a potential threat (E. Gallo-Cajiao in litt. 2007). Despite the existence of protected areas within its range, some threats may operate even inside of such areas and their buffer zones (Jahn and Mena 2002).

Conservation Actions Underway
It occurs in Cotacachi-Cayapas Ecological Reserve (Esmeraldas) (Jahn and Mena 2002, O. Jahn  in litt. 2007), Awacachi Corridor (Esmeraldas) (P. Mena V. in litt. 2007), Canandé Reserve (Esmeraldas) (Idrobo-Medina et al. 2006), Mindo-Nambillo Protection Forest (Pichincha) (Idrobo-Medina et al. 2006), Farallones de Cali (Valle de Cauca) and Ensenada de Utría (Chocó) National Parks (Velasco-Abad 1997, B. López-Lanús in litt. 2000), and in the small El Pangán Nature Reserve (Nariño) (P. G. W. Salaman in litt. 1999, 2000, R. Strewe in litt. 1999). Historical specimens from the vicinity of Munchique National Park, Colombia, suggest that fieldwork at appropriate altitudes would probably find the species (P. G. W. Salaman in litt. 1999, 2000, R. Strewe in litt. 1999). In Ecuador the species is protected by law (Jahn and Mena 2002). Conservation Actions Proposed
Implement population monitoring programs (Jahn and Mena 2002). Survey appropriate habitats, especially in poorly-known areas. Extend and improve the network of protected areas in Nariño and Esmeraldas (Salaman 1994, Bowen-Jones et al. 1999, P. G. W. Salaman in litt. 1999, 2000, Sharpe 1999, Jahn and Mena 2002, Idrobo-Medina et al. 2006). Designate the Awá reserve, Cotacachi-Cayapas Ecological Reserve, Awacachi corridor, Gran Reserva Chachi, and Canandé Reserve, including the Río Santiago, Cayapas, Ónzole, and Hoja Blanca drainages, as a biosphere reserve (Jahn and Mena 2002, Jahn in press). Sustainably manage the buffer zones of the Awá Ethnic Reserve and Cotacachi-Cayapas Ecological Reserve (Jahn and Mena 2002, Jahn in press).

Best, B. J.; Checker, M.; Thewlis, R. M.; Best, A. L.; Duckworth, W. 1996. New bird breeding data from southwestern Ecuador. Ornitologia Neotropical 7(1): 69-73.

del Hoyo, J. 1994. Cracidae (Chachalacas, Guans and Curassows). In: del Hoyo, J.; Elliott, A.; Sargatal, J. (ed.), Handbook of the birds of the world, pp. 310-363. Lynx Edicions, Barcelona, Spain.

Delacour, J.; Amadon, D. 1973. Curassows and related birds. American Museum of Natural History, New York.

Dodson, C. H.; Gentry, A. H. 1991. Biological extinction in western Ecuador. Annals of the Missouri Botanical Garden 78: 273-295.

Haffer, J. 1968. Notes on the wing and tail molt of the screamers, the sunbittern and immature guans. The Auk 85: 633-638.

Hellmayr, C. E.; Conover, B. 1942. Catalogue of birds of the Americas, Part I, number 1. Field Museum of Natural History Zoological Series 13(Publ. 514).

Hilty, S. L.; Brown, W. L. 1986. A guide to the birds of Colombia. Princeton University Press, Princeton.

Idrobo-Medina, C. J.; Gallo-Cajiao, E.; Jahn, O. 2006. Baudó Guan (Penelope ortoni). In: Brooks, D. M. (ed.), Conserving cracids: the most threatened family of birds in the Americas, pp. 46-49. Misc. Publ. Houston Mus. Nat. Sci. no. 6.

Jahn, A.E., Saavedra, A.M., Horn, R.I., Dobbs, R.C., Porzecanski, A.L., Weicker, J.J. and Davis, S.E. 2008. A comparison of gallery and dry forest avian communities in the Gran Chaco of Bolivia. Ornitologia Neotropical 19(1): 1-14.

Jahn, O. 2001. Integrating biological data into development projects: threatened bird species and management plans for sustainable forestry in the Province of Esmeraldas, Ecuador. In: Rhoades, R. E.; Stallings, J. (ed.), Integrating conservation and development in Tropical America: experiences and lessons in linking communities and policies, pp. 39-54. SANREM CRSP and CARE, Athens, GA, USA.

Jahn, O. in press. Bird communities of the Ecuadorian Chocó: a case study for conservation. Bonner Zoologische Monographien 56.

Jahn, O.; Moore, J. V.; Valenzuela, P. M.; Krabbe, N.; Coopmans, P.; Lysinger, M.; Ridgely, R. S. 2002. The Birds of Northwest Ecuador Volume II: the lowlands and lower foothills. John V. Moore Nature Recordings, San Jose, USA.

Paynter, R. A. 1993. Ornithological gazetteer of Ecuador. President and Fellows of Harvard College, Harvard.

Salaman, P. G. W. 1994. Surveys and conservation of biodiversity in the Chocó, south-west Colombia. BirdLife International, Cambridge, U.K.

Salaman, P. G. W.; Donegan, T. M.; Cuervo, A. M.; Ochoa, J. M. 2000. Notas sobre historia natural de crácidos en los Andes colombianos. Bulletin of the IUCN/Birdlife/WPA Cracid Specialist Group 11: 14-18.

Salaman, P. G. W.; Giles, O. A. R. 1995. Notes on threatened bird from Colombia between July--December 1994.

Salaman, P. G. W.; Stiles, F. G. 1996. A distinctive new species of vireo (Passeriformes: Vireonidae) from the Western Andes of Colombia. Ibis 138: 610-619.

Sharpe, C. J. 1999. A rapid biodiversity assessment of the San Lorenzo - Ventanas area, Esmeraldas, north-west Ecuador, 27 November - 14 December 1998. Fauna and Flora International.

Vaurie, C. 1968. Taxonomy of the Cracidae (Aves). Bulletin of the American Museum of Natural History 138: 131-260.

Velasco-Abad, E. 1997. Status, distribución y población de Cracidae en el Valle de Cauca, Colombia. In: Strahl, S.D.; Beaujon, D.; Brooks, D.M.; Begazo, A.J.; Sedaghatkish, G.; Olmos, F. (ed.), The Cracidae: their biology and conservation, pp. 283-285. Hancock House Publishers, Surrey, Canada and Blaine, USA.

WWF/IUCN. 1994-1997. Centres of plant diversity. A guide and strategy for their conservation. IUCN, Cambridge, UK.

Further web sources of information
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Text account compilers
Benstead, P., Symes, A., Jahn, O., Sharpe, C J, Symes, A.

Sharpe, C J, Jahn, O., Gomez, N., Williams, R., Salaman, P., Gallo-Cajiao, E., Strewe, R., Coopmans, P., López-Lanús, B., Williams, R., Strewe, R., Fierro, E., Cortés, A., Cortes, O.

IUCN Red List evaluators
Butchart, S., Symes, A.

Recommended citation
BirdLife International (2016) Species factsheet: Penelope ortoni. Downloaded from on 23/10/2016. Recommended citation for factsheets for more than one species: BirdLife International (2016) IUCN Red List for birds. Downloaded from on 23/10/2016.

This information is based upon, and updates, the information published in BirdLife International (2000) Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004) Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.

To provide new information to update this factsheet or to correct any errors, please email BirdLife

To contribute to discussions on the evaluation of the IUCN Red List status of Globally Threatened Birds, please visit BirdLife's Globally Threatened Bird Forums.

Additional resources for this species

ARKive species - Baudo guan (Penelope ortoni) 0

Key facts
Current IUCN Red List category Endangered
Family Cracidae (Guans, Chachalacas, Curassows)
Species name author Salvin, 1874
Population size 7000-21000 mature individuals
Population trend Decreasing
Distribution size (breeding/resident) 52,400 km2
Country endemic? No
Links to further information
- Additional Information on this species