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.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
D | D | D1 |
Year | Category | Criteria |
---|---|---|
2022 | Critically Endangered | D |
2016 | Endangered | B2ac(ii) |
2012 | Endangered | B1ab(ii,iii,iv,v)+2ab(ii,iii,iv,v);C2a(ii) |
2008 | Endangered | B1a+b(ii,iii,iv,v); B2a+b(ii,iii,iv,v); C2a(ii) |
2004 | Endangered | |
2000 | Endangered | |
1996 | Endangered | |
1994 | Endangered | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | low |
Land-mass type |
Australia |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 30,200 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 1-249, 1-49 mature individuals | poor | estimated | 2020 |
Population trend | unknown | poor | - | - |
Generation length | 3.1 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification:
This species is evidently extremely rare. Garnett et al. (2011) posited there may be 500 birds, although this was presented without evidence and there are probably fewer, possibly even none (Webster et al. 2021a). From 2001–2019 a search effort of 103 days (193 person-days) yielded a report of one female at Mareeba in 2005, one female on Lakefield National Park in 2009, and up to two pairs at Mount Mulligan in 2015 (Mathieson and Smith 2017, Webster et al. 2021a). However, these were not accompanied by any verifiable evidence. In a separate and more targeted search effort between 2018 and 2021, extensive surveys (over 200 person-days) including camera trapping, call playback, searches for platelets, flush surveys and automated recording units were undertaken across the species's range at all known historic sites and contemporary sites with reports; no T. olivii were found, but the adopted methods were successful in detecting T. varius, T. velox, T. oyrrhothorax and T. maculosus (Webster et al. 2021b). Despite occasional reports (both peer-reviewed and anecdotal) from the Wet Tropics and Einasleigh Uplands Bioregion since the 1980s (e.g. Mathieson and Smith 2017), no observations have been made with irrefutable evidence and Webster et al. (2021b) concluded that the last confirmed records date back to the early 1920s. Accepting this assertion, the average probability of extinction using the threats model of extinction (Keith et al. 2017) and the records and survey model (Thompson et al. 2017) is 0.48. Any extant population is therefore estimated to be tiny, and the population size is here estimated at 1-250 mature individuals, with a best estimate (following Webster et al. 2021a) of 1-49 mature individuals.
Trend justification:
Given the tremendous uncertainties regarding this species's population size, the trend is effectively inestimable. Although the paucity of verified records in recent decades suggests that it has declined since the 1920s, there is little indication of when this decline took place. Given how long the species has been rare for (with no verified sightings since the early 1920s), a continuing decline would probably mean the species is now Extinct. In the absence of more robust data therefore, the population trend is recorded as unknown.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Australia | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Australia | Iron and McIlwraith Ranges |
Australia | Morehead River |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Lowland | suitable | resident |
Grassland | Subtropical/Tropical Dry | major | resident |
Altitude | 0 - 500 m | Occasional altitudinal limits | (max) 800 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Livestock farming & ranching - Scale Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
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Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Slow, Significant Declines | Low Impact: 4 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Felis catus | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Rhinella marina | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Sus scrofa | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Unspecified species | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Problematic native species/diseases - Named species | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Unknown | Unknown | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Trend Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Slow, Significant Declines | Low Impact: 5 | ||||||
|
Recommended citation
BirdLife International (2024) Species factsheet: Buff-breasted Buttonquail Turnix olivii. Downloaded from
https://datazone.birdlife.org/species/factsheet/buff-breasted-buttonquail-turnix-olivii on 23/11/2024.
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 23/11/2024.