Taxonomic source(s)
del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 1: Non-passerines. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.
SACC. 2005 and updates. A classification of the bird species of South America. Available at: https://www.museum.lsu.edu/~Remsen/SACCBaseline.htm.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | A2cd+3cd+4cd; C2a(i) |
Year | Category | Criteria |
---|---|---|
2023 | Vulnerable | A2cd+3cd+4cd |
2016 | Endangered | C2a(i) |
2013 | Endangered | C2a(i) |
2012 | Endangered | C2a(i) |
2008 | Endangered | C2a(i) |
2004 | Vulnerable | |
2000 | Vulnerable | |
1996 | Endangered | |
1994 | Endangered | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
continent |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 143,000 km2 | medium |
Area of Occupancy (breeding/resident) | 14,000 km2 | |
Number of locations | 11-100 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 3500-12500 mature individuals | poor | inferred | 2015 |
Population trend | decreasing | poor | inferred | 2010-2037 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
Rate of change over the future 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
Rate of change over the past & future 10 years/3 generations (longer of the two periods) | 30-49% | - | - | - |
Generation length | 9 years | - | - | - |
Number of subpopulations | 5-100 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: Formerly common, this species is now generally rare and occurs at low densities (Wege and Long 1995, Silva 1999). Based on observed densities of 4.8 individuals/km2 in Tamá National Natural Park, the population in Colombia is estimated at c.10,900 individuals, though this may be an overestimate; the population is therefore placed in the band 2,500-9,999 mature individuals (Renjfo et al. 2014). The population in Venezuela is suspected to number 1,000-2,499 mature individuals (Rojas-Suárez et al. 2015). The global population may therefore number roughly 3,500-12,500 mature individuals.
Trend justification: Once common across its range, the population has declined considerably; it is reportedly observed less frequently in recent years and has even suffered local extinctions (Renjifo et al. 2014, Rojas-Suárez et al. 2015, del Hoyo and Kirwan 2020, T. Donegan in litt. 2023). The principal drivers of the decline are thought to be intense hunting pressure and habitat loss (del Hoyo and Kirwan 2020).
The rate of decline has not been quantified across the range. Within its altitudinal range, about 6% of tree cover has been lost since 2000 (Global Forest Watch 2022, using Hansen et al. [2013] data and methods disclosed therein), which roughly equates to a decline of 8% over the past three generations (27 years). Given the species' strict dependence on interior forest and sensitivity to fragmented and edge habitat, habitat loss may have caused population declines at a higher rate than tree cover loss alone suggests. By now, the species is largely restricted to protected areas (Rojas-Suárez et al. 2015). The impact of hunting has not been quantified; hunting pressure is however described as intense and ongoing even within protected areas (Renjifo et al. 2014, Rojas-Suárez et al. 2015). In Colombia, it is suspected that the population has declined by >50% over 40 years (Renjifo et al. 2014), which is equivalent to a decline of 37% over three generations. Assuming that this rate is representative for the entire range, it is suspected that the combined impacts of hunting and habitat loss are causing overall population declines at a rate of 30-49% over three generations, though an accurate quantification of the population trend is urgently required.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Colombia | extant | native | yes | |||
Venezuela | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Colombia | Parque Nacional Natural El Cocuy |
Colombia | Parque Nacional Natural Tamá |
Colombia | Serranía de los Yariguíes |
Venezuela | Dinira National Park and surrounding areas (Refugio de Fauna Silvestre y Reserva de Pesca Parque Nacional Dinira IBA) |
Venezuela | Henri Pittier National Park (Parque Nacional Henri Pittier IBA) |
Venezuela | Parque Nacional El Ávila and surrounding areas |
Venezuela | Parque Nacional El Tamá |
Venezuela | Parque Nacional Guaramacal |
Venezuela | Parque Nacional Guatopo |
Venezuela | Parque Nacional Macarao |
Venezuela | Parque Nacional Páramos Batallón y La Negra and surrounding areas |
Venezuela | Parque Nacional Perijá |
Venezuela | Parque Nacional San Esteban |
Venezuela | Parque Nacional Sierra La Culata |
Venezuela | Parque Nacional Sierra Nevada |
Venezuela | Parque Nacional Tapo-Caparo |
Venezuela | Parque Nacional Terepaima |
Venezuela | Parque Nacional Yacambú |
Venezuela | Zona Protectora San Rafael de Guasare |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 500 - 2260 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Agro-industry farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Agriculture & aquaculture | Annual & perennial non-timber crops - Small-holder farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Agriculture & aquaculture | Livestock farming & ranching - Agro-industry grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Purpose | Scale |
---|---|
Food - human | subsistence, national |
Handicrafts, jewellery, etc. | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Helmeted Curassow Pauxi pauxi. Downloaded from
https://datazone.birdlife.org/species/factsheet/helmeted-curassow-pauxi-pauxi on 23/11/2024.
Recommended citation for factsheets for more than one species: BirdLife International (2024) IUCN Red List for birds. Downloaded from
https://datazone.birdlife.org/species/search on 23/11/2024.