IUCN Red List Criteria
| Critically Endangered |
|
| Endangered |
|
| Vulnerable |
A4bcde |
IUCN Red List history
| Year |
Category |
| 2012 |
Vulnerable |
| 2010 |
Vulnerable |
| 2008 |
Vulnerable |
| 2005 |
Vulnerable |
| 2004 |
Vulnerable |
| 2000 |
Vulnerable |
| 1994 |
Not Recognised |
| 1988 |
Not Recognised |
Species attributes
| Migratory status |
full migrant |
Forest dependency |
Does not normally occur in forest |
| Land mass type |
shelf island
|
Average mass |
- |
Distribution
| |
Estimate |
Data quality |
| Extent of Occurrence breeding/resident (km2) |
44,800,000 |
medium |
| Area of Occupancy breeding/resident (km2) |
3,300 |
medium |
| Number of locations |
11-100 |
- |
| Fragmentation |
|
- |
Population & trend
| |
Estimate |
Data quality |
Derivation |
Year of estimate |
| No. of mature individuals |
3000000 |
medium |
Estimated |
2012 |
| Population trend |
Decreasing |
medium |
|
- |
| Number of subpopulations |
2-100 |
- |
- |
- |
| Largest subpopulation |
|
- |
- |
- |
| Generation length (yrs) |
24.7 |
- |
- |
- |
|
Population justification: A global population of 1,200,000 breeding pairs, down from 1,430,000 pairs in the 1980s, is estimated based on figures from 1985-2011. This equates to an estimated global population of c.3 million mature individuals, based on the estimated number of breeding pairs extrapolated according to a ratio from Brooke (2004). |
|
Trend justification: A decline is inferred from a drop in burrow occupancy of 28% over 20 years on Bird Island, South Georgia (Berrow et al. 2000), and declines of 86% during 1981-1993 at sea in Prydz Bay, Antarctica (Woehler 1996). Population monitoring on Marion Island between 1996-1997 and 1999-2000 recorded a 14.5% per annum decrease in the population. Data from the Crozet archipelago indicate a 37% decline in breeding pairs between 1983 and 2004, based on population models and field estimates from two surveys (Barbraud et al. in litt. 2008). Data from fisheries and a population model suggest that the population on the Kerguelen Islands may also be in decline (Barbraud et al. 2009). Data from at-sea surveys suggest a 35% decline in the Southern Indian Ocean during 1981-2007 (Péron et al. 2010a). Trend analysis from 1980-2054 (three generations, 74 years) predicts a 45% decline (BirdLife International unpublished data). For colonies without new data, this analysis assumed a stable population, however there is a need for more data, particularly from Kerguelen, as if this population were shown to be stable rather than increasing as is currently reported (200,000 pairs in 1987 and 234,000 in 2005, ACAP 2012), the overall rate of decline may be significantly higher. It is likely that 1987 figures are rough estimates, so new count data from Kerguelen to accurately assess the direction of population trends are required. |
Country/Territory distribution
| Country/Territory |
Occurrence status |
Extinct |
Breeding |
Non-breeding |
Passage |
| Antarctica |
Native |
No |
|
Yes |
|
| Argentina |
Native |
No |
|
Yes |
|
| Australia |
Native |
No |
Yes |
|
|
| Bouvet Island (to Norway) |
Unknown |
No |
|
|
|
| Brazil |
Native |
No |
|
Yes |
|
| Chile |
Native |
No |
|
Yes |
|
| Ecuador |
Unknown |
No |
|
|
|
| Falkland Islands (Malvinas) |
Native |
No |
|
|
|
| French Southern Territories |
Native |
No |
Yes |
|
|
| Heard Island and McDonald Islands (to Australia) |
Native |
No |
|
Yes |
|
| Madagascar |
Native |
No |
|
Yes |
|
| Mozambique |
Native |
No |
|
Yes |
|
| Namibia |
Native |
No |
|
Yes |
|
| New Zealand |
Native |
No |
Yes |
|
|
| Peru |
Native |
No |
|
|
|
| South Africa |
Native |
No |
Yes |
|
|
| South Georgia & the South Sandwich Islands |
Native |
No |
Yes |
|
|
| St Helena (to UK) |
Native |
No |
|
Yes |
|
| Uruguay |
Native |
No |
|
Yes |
|
Important Bird Areas where this species has triggered the IBA criteria
| Country/Territory |
IBA Name |
IBA link |
| Antarctica |
Indian Ocean, Antarctic and Southern 38 - Marine |
 |
| Antarctica |
Indian Ocean, Antarctic and Southern 45 - Marine |
 |
| Antarctica |
Indian Ocean, Antarctic and Southern 46 - Marine |
 |
| Argentina |
Islas Georgias del Sur |
 |
| Argentina |
Islas Malvinas |
 |
| Falkland Islands (Malvinas) |
Kidney Island Group |
 |
| Falkland Islands (Malvinas) |
New Island Group |
 |
| French Southern Territories |
Île de l'Est |
 |
| New Zealand |
Antipodes Islands |
 |
| New Zealand |
Auckland Islands |
 |
| New Zealand |
Campbell Island (and outliers) |
 |
| Peru |
Reserva Nacional de Paracas |
 |
| South Africa |
Prince Edward Islands Special Nature Reserve |
 |
| South Georgia & the South Sandwich Islands |
South Georgia - mainland, islands, islets and stacks |
 |
| Uruguay |
Atlantic Ocean and Rio de la Plata mouth |
 |
Habitats & altitude
| Habitat (level 1) |
Habitat (level 2) |
Importance |
Occurrence |
| Grassland |
Subantarctic |
major |
breeding |
| Marine Neritic |
Macroalgal/Kelp |
suitable |
non-breeding |
| Marine Neritic |
Macroalgal/Kelp |
suitable |
breeding |
| Marine Neritic |
Pelagic |
suitable |
breeding |
| Marine Neritic |
Pelagic |
suitable |
non-breeding |
| Marine Neritic |
Seagrass (Submerged) |
suitable |
non-breeding |
| Marine Neritic |
Seagrass (Submerged) |
suitable |
breeding |
| Marine Neritic |
Subtidal Loose Rock/pebble/gravel |
suitable |
breeding |
| Marine Neritic |
Subtidal Loose Rock/pebble/gravel |
suitable |
non-breeding |
| Marine Neritic |
Subtidal Rock and Rocky Reefs |
suitable |
breeding |
| Marine Neritic |
Subtidal Rock and Rocky Reefs |
suitable |
non-breeding |
| Marine Neritic |
Subtidal Sandy |
suitable |
non-breeding |
| Marine Neritic |
Subtidal Sandy |
suitable |
breeding |
| Marine Neritic |
Subtidal Sandy-Mud |
suitable |
non-breeding |
| Marine Neritic |
Subtidal Sandy-Mud |
suitable |
breeding |
| Marine Oceanic |
Epipelagic (0-200m) |
major |
non-breeding |
| Marine Oceanic |
Epipelagic (0-200m) |
major |
breeding |
|
Altitude
|
0 - 200 m
|
Occasional altitudinal limits
|
|
Threats & impact
| Threat (level 1) |
Threat (level 2) |
Impact and Stresses |
| Biological resource use |
Fishing & harvesting aquatic resources / Unintentional effects: (large scale) |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Majority (50-90%) |
Rapid Declines |
Medium Impact: |
| Stresses |
| Species mortality |
|
| Biological resource use |
Hunting & trapping terrestrial animals / Intentional use (species is the target) |
Timing |
Scope |
Severity |
Impact |
| Past, Unlikely to Return |
Minority (<50%) |
Slow, Significant Decline |
Past Impact |
| Stresses |
| Species mortality |
|
| Invasive non-native/alien species/diseases |
Problematic native species/diseases |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Minority (<50%) |
Negligible declines |
Low Impact: 4 |
| Stresses |
| Ecosystem degradation, Ecosystem conversion |
|
| Invasive non-native/alien species/diseases |
Problematic native species/diseases / Unspecified mammals |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Majority (50-90%) |
Negligible declines |
Low Impact: 5 |
| Stresses |
| Ecosystem degradation, Ecosystem conversion |
|
| Invasive non-native/alien species/diseases |
Invasive non-native/alien species/diseases / Black Rat (Rattus rattus) |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Minority (<50%) |
Slow, Significant Decline |
Low Impact: 5 |
| Stresses |
| Reduced reproductive success |
|
| Invasive non-native/alien species/diseases |
Invasive non-native/alien species/diseases / Brown Rat (Rattus norvegicus) |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Minority (<50%) |
Slow, Significant Decline |
Low Impact: 5 |
| Stresses |
| Reduced reproductive success |
|
| Invasive non-native/alien species/diseases |
Invasive non-native/alien species/diseases / Domestic Cat (Felis catus) |
Timing |
Scope |
Severity |
Impact |
| Ongoing |
Minority (<50%) |
Slow, Significant Decline |
Low Impact: 5 |
| Stresses |
| Species mortality |
|
Utilisation
| Purpose |
Primary form used |
Life stage used |
Source |
Scale |
Level |
Timing |
| Food (human) |
Whole |
Adults and juveniles |
Wild |
Subsistence, National |
Non-trivial |
Recent |
Recommended citation
BirdLife International (2013) Species factsheet: Procellaria aequinoctialis. Downloaded from
http://www.birdlife.org on 26/05/2013.
Recommended citation for factsheets for more than one species: BirdLife International (2013) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 26/05/2013.
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.