LC
Adelie Penguin Pygoscelis adeliae



Taxonomy

Taxonomic source(s)
Christidis, L. and Boles, W.E. 2008. Systematics and Taxonomy of Australian Birds. CSIRO Publishing, Collingwood, Australia.
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.
Turbott, E.G. 1990. Checklist of the Birds of New Zealand. Ornithological Society of New Zealand, Wellington.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - -

Red List history
Year Category Criteria
2020 Least Concern
2018 Least Concern
2016 Least Concern
2012 Near Threatened A3c
2009 Least Concern
2008 Least Concern
2004 Least Concern
2000 Lower Risk/Least Concern
1994 Lower Risk/Least Concern
1988 Lower Risk/Least Concern
Species attributes

Migratory status full migrant Forest dependency does not normally occur in forest
Land-mass type Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 21,000,000 km2 medium
Extent of Occurrence (non-breeding) 32,000,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 10000000 mature individuals medium estimated 2017
Population trend increasing - estimated -
Generation length 12.7 years - - -

Population justification:

The total global population was previously estimated at c.2.37 million breeding pairs (range 1.83-2.88 million pairs), equating to 4.74 million breeding individuals, based on survey data collated up to the mid-1990s (Woehler 1993, Woehler and Croxall 1997). More recently, Lynch and La Rue (2014) estimated the global breeding population to be 3.79 million pairs (range 3.52-4.10 million pairs) spread amongst 190-250 colonies (depending on the definition of a colony), equating to 7.58 million breeding individuals, based largely on satellite imagery of breeding colonies obtained between 2006 and 2011. These estimates do not include mature individuals that have skipped breeding in a season, which have been estimated to comprise up to 20% of the total breeding-age population (Southwell et al. 2017), nor pre-breeding individuals (the species not beginning to breed until an average of 4-5 years; Ainley 2002). The global population of breeding-aged individuals is thus likely to be around 10 million mature individuals; the total population including both mature and pre-breeding birds is around 14-16 million individuals (Southwell et al. 2017).

Trend justification: Lynch and LaRue (2014) reported that the global population had increased between the times of the two global estimates in the mid-1990s and 2014 (Woehler 1993, Woehler and Croxall 1997, Lynch and La Rue 2014), with 27% of the difference accounted for by increasing abundance at known colonies and 32% of the difference accounted for by colonies that had not previously been surveyed. Satellite imagery broadened the scope of assessing colony population size. Recent direct surveys in East Antarctica (Southwell et al. 2015a, b) and the Ross Sea (Lyver et al. 2014) have estimated a greater increase in these regions (e.g. average rate of increase in East Antarctica of 1.9% (1.3%-2.4%) per year over 30 years), indicating that the increase in the global population is probably greater than the 27%. The increase in numbers in the Ross Sea accelerated after about 2000 (Lyver et al. 2014).

Recent population increases were found in those regions where most of the world population breeds, including East Antarctica and Victoria Land in the Ross Sea (Lyver et al. 2014, Southwell et al. 2015a,b); the species has also been increasing on the southern Antarctic Peninsula south of 66°S (Sailley et al. 2013). In the northern Peninsula region, evidence indicates that some populations are beginning to stabilize after decades of significant decrease (Fountain et al. 2016); population decreases had previously occurred in parts of the northern Peninsula region (Fraser et al. 1992) and in the South Orkney Islands (Dunn et al. 2016). Modelling exercises now replicate some of the strongest signals in population change (Che-Castaldo et al. 2017). The net change in world population has been positive (Lynch and LaRue 2014). It should be noted that modelled projections in response to climate change, with associated inherent uncertainty, suggest that populations could decrease north of 70°S after the mid-21st century (Ainley et al. 2010, see also Cimino et al. 2016a), and such a change will necessitate a future re-examination of the Adélie Penguin’s status.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Antarctica extant native yes
Argentina extant vagrant
Australia extant vagrant
Falkland Islands (Malvinas) extant vagrant
French Southern Territories extant vagrant
Heard Island and McDonald Islands (to Australia) extant vagrant
New Zealand extant vagrant
South Georgia & the South Sandwich Islands extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Antarctica Antarctica Marine 1
Antarctica Antarctica Marine 13
Antarctica Antarctica Marine 18
Antarctica Antarctica Marine 29
Antarctica Antarctica Marine 30
Antarctica Antarctica Marine 32
Antarctica Antarctica Marine 35
Antarctica Antarctica Marine 39
Antarctica Antarctica Marine 41
Antarctica Antarctica Marine 44
Antarctica Antarctica Marine 45
Antarctica Antarctica Marine 47
Antarctica Antarctica Marine 48
Antarctica Antarctica Marine 49
Antarctica Antarctica Marine 52
Antarctica Antarctica Marine 53
Antarctica Antarctica Marine 54
Antarctica Antarctica Marine 58
Antarctica Antarctica Marine 59
Antarctica Antarctica Marine 60
Antarctica Antarctica Marine 61
Antarctica Avian Island
Antarctica Beaufort Island
Antarctica Cape Adare
Antarctica Cape Crozier, Ross Island
Antarctica Cape Jules
Antarctica Caughley Beach, Cape Bird
Antarctica Cotter Cliffs
Antarctica Danger Islands
Antarctica Eden Rocks
Antarctica Edwards Islands
Antarctica Ferrier Peninsula / Graptolite Island
Antarctica Franklin Island southwest
Antarctica Hop Island, Rauer Islands
Antarctica Hope Bay
Antarctica Lindsey Islands
Antarctica MacKellar Islands
Antarctica Paulet Island
Antarctica Pointe Géologie
Antarctica Possession Island
Antarctica Rookery Islands
Antarctica Rookery Lake / W Long Peninsula
Antarctica Scullin Monolith / Murray Monolith
Antarctica Seabee Hook, Cape Hallett
Antarctica Way Archipelago
South Georgia & the South Sandwich Islands South Sandwich Islands
South Georgia & the South Sandwich Islands South Sandwich Islands Marine North
South Georgia & the South Sandwich Islands South Sandwich Islands Marine South

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Marine Intertidal Rocky Shoreline major breeding
Marine Neritic Macroalgal/Kelp major non-breeding
Marine Neritic Macroalgal/Kelp major breeding
Marine Neritic Pelagic major non-breeding
Marine Neritic Pelagic major breeding
Marine Neritic Seagrass (Submerged) major non-breeding
Marine Neritic Seagrass (Submerged) major breeding
Marine Neritic Subtidal Loose Rock/pebble/gravel major non-breeding
Marine Neritic Subtidal Loose Rock/pebble/gravel major breeding
Marine Neritic Subtidal Rock and Rocky Reefs major non-breeding
Marine Neritic Subtidal Rock and Rocky Reefs major breeding
Marine Neritic Subtidal Sandy major non-breeding
Marine Neritic Subtidal Sandy major breeding
Marine Neritic Subtidal Sandy-Mud major non-breeding
Marine Neritic Subtidal Sandy-Mud major breeding
Marine Oceanic Epipelagic (0-200m) major non-breeding
Marine Oceanic Epipelagic (0-200m) major breeding
Marine Oceanic Mesopelagic (200-1000m) major non-breeding
Marine Oceanic Mesopelagic (200-1000m) major breeding
Rocky areas (eg. inland cliffs, mountain peaks) major breeding
Altitude   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) [harvest] Timing Scope Severity Impact
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Indirect ecosystem effects, Ecosystem degradation
Climate change & severe weather Habitat shifting & alteration Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Indirect ecosystem effects, Ecosystem degradation, Ecosystem conversion, Reduced reproductive success
Human intrusions & disturbance Recreational activities Timing Scope Severity Impact
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Species disturbance
Human intrusions & disturbance Work & other activities Timing Scope Severity Impact
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Species disturbance, Reduced reproductive success
Pollution Industrial & military effluents - Oil spills Timing Scope Severity Impact
Past, Likely to Return Minority (<50%) Slow, Significant Declines Past Impact
Stresses
Ecosystem degradation, Reduced reproductive success, Species mortality

Utilisation
Purpose Scale
Pets/display animals, horticulture international
Research international

Recommended citation
BirdLife International (2024) Species factsheet: Adelie Penguin Pygoscelis adeliae. Downloaded from https://datazone.birdlife.org/species/factsheet/adelie-penguin-pygoscelis-adeliae on 28/11/2024.
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 28/11/2024.