VU
Christmas Island Frigatebird Fregata andrewsi



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.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- C2a(ii) C1+2a(ii)

Red List history
Year Category Criteria
2022 Vulnerable C1+2a(ii)
2018 Critically Endangered B2ab(ii,iii,v)
2016 Critically Endangered B2ab(ii,iii,v)
2015 Critically Endangered B2ab(ii,iii,v)
2013 Critically Endangered B2ab(ii,iii,v)
2012 Critically Endangered B2ab(ii,iii,v)
2010 Critically Endangered B2a+b(ii,iii,v)
2009 Critically Endangered B2a+b(ii,iii,v)
2008 Critically Endangered
2007 Critically Endangered
2005 Critically Endangered
2004 Critically Endangered
2000 Critically Endangered
1996 Vulnerable
1994 Vulnerable
1988 Threatened
Species attributes

Migratory status full migrant Forest dependency medium
Land-mass type Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 40 km2 medium
Extent of Occurrence (non-breeding) 7,160,000 km2 medium
Area of Occupancy (breeding/resident) 40 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 2400-5000,3700 mature individuals medium estimated 2020
Population trend decreasing good estimated 1970-2025
Rate of change over the past 10 years/3 generations (longer of the two periods) 22-26% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 5-19% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 22-26% - - -
Generation length 18.4 years - - -
Number of subpopulations 1 - - -
Percentage of mature individuals in largest subpopulation 100% - - -

Population justification: There have been five estimates in the last three generations: 1,300 pairs in 1985 (Stokes 1988), 1,466±325 in 2003, 1,392±102 in 2004 (James 2014), 1,050 in 2016 and 1,200 in 2017 (J.C. Hennicke unpublished). Taking a different approach based on genetics, Morris-Pocock et al. (2012) estimated the population at 5,000 mature individuals. The best estimate of mature individuals is the mean of the two methods.

Trend justification: Historically, there were estimated to be 6,300 annual breeding pairs, but a loss of breeding habitat apparently owing to habitat clearance and dust fallout from phosphate mining, marine pollution, overfishing and bycatch in fishing gear has caused declines.  Although land-based threats are no longer thought to be prevalent, declines are projected to continue principally owing to the ongoing threat of persecution by fishing activities (Macgregor et al. 2021). Surveys from 2008-2013 show an ongoing declining trend in breeding numbers (Hennicke 2014). There have been five estimates in the last three generations: 1,300 pairs in 1985 (Golf Course 850 nests, Cemetery 350, Dryers 100; Stokes 1988), 1,466±325 in 2003, 1,392±102 in 2004 (James 2014), 1,050 in 2016 and 1,200 in 2017 (J. C. Hennicke unpublished, in Macgregor et al. 2021). This species breeds biennially, so the increase between 2016 and 2017 cannot be interpreted as an increase in mature individuals. Using the five estimates of breeding pairs, there was an approximate decline of c.20-25% over the last three generations (Macgregor et al. 2021).


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Australia extant vagrant yes
Brunei extant native yes
Cambodia extant native yes
China (mainland) extant native yes
Christmas Island (to Australia) extant native yes
Cocos (Keeling) Islands (to Australia) extant vagrant yes
Hong Kong (China) extant native yes
India extant vagrant yes
Indonesia extant native yes
Japan extant vagrant yes
Malaysia extant native yes
Philippines extant native yes
Singapore extant native yes
Sri Lanka extant native yes
Thailand extant native yes
Timor-Leste extant native yes
Vietnam extant vagrant yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Cambodia Koh Tang Archipelago
Christmas Island (to Australia) Christmas Island
Indonesia Pulau Dua
Indonesia Pulau Rambut
Indonesia Ujung Kulon
Malaysia Bako-Buntal Bay
Malaysia Mantanani islands
Malaysia Sipadan islands
Malaysia Tanjung Datu-Samunsam Protected Area
Malaysia Tempasuk plains
Thailand Hat Nopharat Thara - Mu Ko Phi Phi

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Moist Lowland major breeding
Marine Neritic Estuaries suitable resident
Marine Neritic Macroalgal/Kelp major resident
Marine Neritic Pelagic major 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
Marine Oceanic Epipelagic (0-200m) major resident
Marine Oceanic Mesopelagic (200-1000m) major resident
Altitude 0 - 200 m Occasional altitudinal limits (max) 357 m

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Agriculture & aquaculture Annual & perennial non-timber crops - Small-holder farming Timing Scope Severity Impact
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Fishing & harvesting aquatic resources - Unintentional effects: (large scale) [harvest] Timing Scope Severity Impact
Ongoing Whole (>90%) Slow, Significant Declines Medium Impact: 7
Stresses
Indirect ecosystem effects, Species mortality
Biological resource use Hunting & trapping terrestrial animals - Intentional use (species is the target) Timing Scope Severity Impact
Ongoing Majority (50-90%) Very Rapid Declines High Impact: 8
Stresses
Species mortality
Climate change & severe weather Habitat shifting & alteration Timing Scope Severity Impact
Ongoing Whole (>90%) Unknown Unknown
Stresses
Ecosystem degradation
Climate change & severe weather Storms & flooding Timing Scope Severity Impact
Future Whole (>90%) Unknown Unknown
Stresses
Ecosystem degradation
Energy production & mining Mining & quarrying Timing Scope Severity Impact
Past, Unlikely to Return Majority (50-90%) Slow, Significant Declines Past Impact
Stresses
Ecosystem degradation, Ecosystem conversion, Species mortality
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Anoplolepis gracilipes Timing Scope Severity Impact
Ongoing Whole (>90%) Unknown Unknown
Stresses
Indirect ecosystem effects
Pollution Garbage & solid waste Timing Scope Severity Impact
Ongoing Whole (>90%) Unknown Unknown
Stresses
Ecosystem degradation
Pollution Industrial & military effluents - Type Unknown/Unrecorded Timing Scope Severity Impact
Ongoing Whole (>90%) Unknown Unknown
Stresses
Ecosystem degradation

Utilisation
Purpose Scale
Food - human subsistence, national

Recommended citation
BirdLife International (2024) Species factsheet: Christmas Island Frigatebird Fregata andrewsi. Downloaded from https://datazone.birdlife.org/species/factsheet/christmas-island-frigatebird-fregata-andrewsi on 23/12/2024.
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 23/12/2024.