Taxonomic note
Following Kennedy and Spencer (2014) the genus Phalacrocorax has been divided into six genera, with P. auritus, P. brasilianus and P. harrisi moved into Nannopterum (HBW and BirdLife International 2018).
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.
Handbook of the Birds of the World and BirdLife International. 2018. Handbook of the Birds of the World and BirdLife International digital checklist of the birds of the world. Version 3. Available at: https://datazone.birdlife.org/userfiles/file/Species/Taxonomy/HBW-BirdLife_Checklist_v3_Nov18.zip.
Kennedy, Martyn & Spencer, Hamish. 2014. Classification of the Cormorants of the World. Molecular phylogenetics and evolution. 79: 249-257.
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 |
---|---|---|
- | - | D2 |
Year | Category | Criteria |
---|---|---|
2018 | Vulnerable | D2 |
2016 | Vulnerable | D2 |
2013 | Vulnerable | D2 |
2012 | Vulnerable | D2 |
2011 | Vulnerable | D2 |
2010 | Endangered | B1a+c(iv); B2a+c(iv) |
2008 | Endangered | B1a+c(iv); B2a+c(iv) |
2005 | Endangered | |
2004 | Endangered | |
2000 | Endangered | |
1996 | Vulnerable | |
1994 | Vulnerable | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | does not normally occur in forest |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 5,900 km2 | medium |
Extent of Occurrence (non-breeding) | 90 km2 | medium |
Area of Occupancy (breeding/resident) | 50 km2 | medium |
Number of locations | 2 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | good | estimated | 2013 |
Population trend | stable | good | estimated | 1978-2011 |
Rate of change over the past 10 years/3 generations (longer of the two periods) | 0% | - | - | - |
Generation length | 11.1 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: In 1971-1972, the population was estimated at 800 breeding pairs (Harris 1973). Between 1977 and 1985, it remained stable at around 650 to 850 mature individuals (Harris 1973, Valle 1986, Valle and Coulter 1987). However, during the severe El Niño event in 1983, the population declined drastically to 400 individuals, but recovered within a season (Valle and Coulter 1987). In 1986, the population was estimated at 1,000 mature individuals (Rosenberg et al. 1990). After the El Niño event in 1997-1998, growth in the cormorant population has been higher than ever before in the survey period (1977-2006). In 1999, a total of 900 individuals was counted during the census (H. Vargas and F. Cruz in litt. 2000). In 2006, a total of 1,396 individuals were counted. Still, results as of 2003 show a decrease in the rate of population growth and a low percentage of juveniles (3% in 2006), suggesting that the population is stabilizing at a new high (Jiménez-Uzcátegui and Vargas 2007). In 2013, the population was estimated to be 2,080 individuals (Jiménez-Uzcátegui 2013, Carrera-Játiva et al. 2014).
Trend justification: This species has undergone marked fluctuations since 1977, with the population estimate ranging from 400 individuals after the El Niño in 1983 (Valle and Coulter 1987) to 1,396 individuals in 2006 (Jiménez-Uzcátegui and Vargas 2007). From 2010 on, a different census methodology was used, and in 2013 the population was estimated in 2,080 individuals (Jiménez-Uzcátegui 2013, Carrera-Játiva et al. 2014). Currently, the population is thought to be stabilizing.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Ecuador | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Ecuador | Áreas costeras de Fernandina y del occidente de Isabela |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Marine Intertidal | Rocky Shoreline | major | breeding |
Marine Neritic | Macroalgal/Kelp | major | resident |
Marine Neritic | Pelagic | suitable | resident |
Marine Neritic | Seagrass (Submerged) | major | resident |
Marine Neritic | Subtidal Loose Rock/pebble/gravel | major | resident |
Marine Neritic | Subtidal Rock and Rocky Reefs | major | resident |
Marine Neritic | Subtidal Sandy | major | resident |
Marine Neritic | Subtidal Sandy-Mud | major | resident |
Altitude | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Biological resource use | Fishing & harvesting aquatic resources - Unintentional effects: (large scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Negligible declines | Medium Impact: 6 | ||||||
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Climate change & severe weather | Temperature extremes | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Causing/Could cause fluctuations | Medium Impact: 7 | ||||||
|
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Geological events | Volcanoes | Timing | Scope | Severity | Impact | ||||
Future | Unknown | Unknown | Unknown | ||||||
|
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Human intrusions & disturbance | Recreational activities | Timing | Scope | Severity | Impact | ||||
Future | Whole (>90%) | Negligible declines | Low Impact: 4 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Canis familiaris | Timing | Scope | Severity | Impact | ||||
Past, Likely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Felis catus | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Rapid Declines | Medium Impact: 6 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Named species | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Rapid Declines | Medium Impact: 6 | ||||||
|
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Toxoplasma gondii | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | No decline | Low Impact: 5 | ||||||
|
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Invasive and other problematic species, genes & diseases | Viral/prion-induced diseases - Unspecified species | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Unknown | Unknown | ||||||
|
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Pollution | Industrial & military effluents - Oil spills | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Rapid Declines | Low Impact: 5 | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Flightless Cormorant Nannopterum harrisi. Downloaded from
https://datazone.birdlife.org/species/factsheet/flightless-cormorant-nannopterum-harrisi 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.