LC
Cinnamon-banded Kingfisher Todiramphus australasia



Taxonomy

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.

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

Red List history
Year Category Criteria
2022 Least Concern
2016 Near Threatened C1+2a(i)
2012 Near Threatened C1+2a(i)
2008 Near Threatened C1; C2a(i)
2004 Near Threatened
2000 Lower Risk/Near Threatened
1994 Lower Risk/Near Threatened
1988 Threatened
Species attributes

Migratory status not a migrant Forest dependency high
Land-mass type Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 437,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 9250-18500, 12000-18000 mature individuals medium estimated 2020
Population trend decreasing poor suspected -
Generation length 3.6 years - - -
Number of subpopulations 5-10,10 - - -
Percentage of mature individuals in largest subpopulation 1-89% - - -

Population justification: The global population size of this species has not previously been quantified, although it is generally described as uncommon (Eaton et al. 2021) but maintains healthy populations in many areas (see Trainor and Verbelen 2013, eBird 2022). In 2020, the area of tree cover, excluding plantations, in its range was estimated at c.16,000 km2 (Global Forest Watch 2022, based on Hansen et al. 2013) and on Sumba, a density of 4.4 individuals/km2 was recorded (Jones et al. 1995). Assuming an occupancy of 20-40%, the population is estimated at 14,000-28,000 individuals, roughly equating to 9,250-18,500 mature individuals. Recognising that this species is tolerant of degraded habitats (at least on some islands), the best estimate is set at 12,000-18,000 mature individuals.

Trend justification: Data trends on this species are lacking. However, ongoing forest loss (albeit at a comparatively slow rate) in its range is suspected of causing slow population declines. Over the past three generations (10.8 years; Bird et al. 2020), forest loss in this species' mapped range has been c.4-6% (Global Forest Watch 2022, using data from Hansen et al. [2013] and methods disclosed therein). This species is somewhat tolerant of degradation, however, and consequently tree cover loss is thought to be causing only slow declines.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Indonesia extant native yes
Timor-Leste extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Indonesia Bipolo
Indonesia Camplong
Indonesia Gunung Arnau
Indonesia Gunung Mutis
Indonesia Gunung Rinjani
Indonesia Gunung Timau
Indonesia Kateri - Maubesi
Indonesia Kepulauan Lemola
Indonesia Laiwanggi Wanggameti
Indonesia Luku Melolo
Indonesia Manipo
Indonesia Manupeu Tanadaru
Indonesia Poronumbu
Indonesia Pulau Babar
Indonesia Pulau Damar
Indonesia Pulau Romang
Indonesia Yawila
Timor-Leste Lore
Timor-Leste Monte Mak Fahik - Sarim
Timor-Leste Mount Paitchau and Lake Iralalaro
Timor-Leste Tilomar

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Artificial/Terrestrial Plantations suitable resident
Artificial/Terrestrial Rural Gardens suitable resident
Forest Subtropical/Tropical Dry major resident
Forest Subtropical/Tropical Moist Lowland major resident
Altitude 0 - 700 m Occasional altitudinal limits  

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%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
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
Stresses
Ecosystem degradation
Energy production & mining Mining & quarrying Timing Scope Severity Impact
Ongoing Unknown Causing/Could cause fluctuations Unknown
Stresses
Ecosystem degradation, Ecosystem conversion
Natural system modifications Fire & fire suppression - Increase in fire frequency/intensity Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation
Transportation & service corridors Roads & railroads Timing Scope Severity Impact
Ongoing Unknown Causing/Could cause fluctuations Unknown
Stresses
Ecosystem degradation, Ecosystem conversion

Recommended citation
BirdLife International (2024) Species factsheet: Cinnamon-banded Kingfisher Todiramphus australasia. Downloaded from https://datazone.birdlife.org/species/factsheet/cinnamon-banded-kingfisher-todiramphus-australasia on 22/11/2024.
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 22/11/2024.