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.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
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 |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type | Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 437,000 km2 | medium |
Severely fragmented? | no | - |
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 | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Indonesia | extant | native | yes | |||
Timor-Leste | extant | native | yes |
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 |
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 |
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 | ||||||
|
|||||||||
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 | ||||||
|
|||||||||
Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Causing/Could cause fluctuations | Unknown | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
|||||||||
Transportation & service corridors | Roads & railroads | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Causing/Could cause fluctuations | Unknown | ||||||
|
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.