Taxonomic note
Chloebia gouldiae (del Hoyo and Collar 2016) was previously placed in the genus Erythrura following Christidis & Boles (2008); Sibley & Monroe (1990, 1993).
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., Fishpool, L.D.C., Boesman, P. and Kirwan, G.M. 2016. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Volume 2: Passerines. Lynx Edicions and BirdLife International, Barcelona, Spain and Cambridge, UK.
Critically Endangered | Endangered | Vulnerable |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2022 | Least Concern | |
2016 | Near Threatened | D1 |
2013 | Near Threatened | D1 |
2012 | Near Threatened | D1 |
2008 | Endangered | C2a(ii) |
2006 | Endangered | |
2004 | Endangered | |
2000 | Endangered | |
1996 | Endangered | |
1994 | Endangered | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | does not normally occur in forest |
Land-mass type |
Australia |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 1,780,000 km2 | medium |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 5000-50000, 25000 mature individuals | poor | estimated | 2020 |
Population trend | stable | poor | estimated | - |
Generation length | 2.64 years | - | - | - |
Number of subpopulations | 1-2 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: The population size of Gouldian Finches has been estimated using a number of methods: Legge et al. (2021) based their estimate on the product of three suspected AOO values: the minimum AOO is based on the number of 2x2 km squares encompassing all records since 1990, the best estimate is ten times this, and the maximum double the latter. These AOO values are applied to a density estimated for Mornington Wildlife Sanctuary, Western Australia (500–1,000 adult birds in 200 km2; Legge et al. 2021). Although using genetic techniques, the effective population size (Ne) was estimated to be 1,600 (611–20,000) in 2016 (Bolton et al. 2016), the ratio of Ne to the actual number of mature individuals can vary by two orders of magnitude (Palstra and Fraser 2012) and tends to decline as populations increase (Waples et al. 2018). On eBird (2021) the sum of the maximum number of birds in any count at 113 sites (each ≥10 km apart) reported during 2018–2019 was 3,915 mature individuals. Such counts are prone to some inflation from recounting the same individuals as they come and go from the field of view and >80% of birds in flocks are usually juveniles (Woinarski and Tidemann 1992, Franklin et al. 1998), so the number of mature individuals is much smaller than the numbers counted in flocks. Given these uncertainties, the estimate used here is set at 5,000-50,000 mature individuals, with a best estimate of 25,000.
Trend justification: Consistent with analyses undertaken in 2015 (TSSC 2016), there was zero trend in reporting rate from 2000–2019 for both 2-ha 20-min surveys and 500-m radius area surveys (BirdLife Australia 2020). Count data from standardised waterhole counts conducted at sites in the Northern Territory (1996–2004; O'Malley 2006) also showed no decline, while the known AOO expanded by 36% between 1999-2009 and 2010-2020, although there remains uncertainty whether this constitutes an expansion in range of survey effort.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Australia | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Australia | Keep River |
Australia | Mornington Sanctuary |
Australia | Wyndham |
Australia | Yinberrie Hills |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
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Grassland | Subtropical/Tropical Dry | major | resident |
Savanna | Dry | suitable | resident |
Shrubland | Subtropical/Tropical Dry | suitable | resident |
Altitude | 0 - 370 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
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Agriculture & aquaculture | Livestock farming & ranching - Agro-industry grazing, ranching or farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
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Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Minority (<50%) | Slow, Significant Declines | Past Impact | ||||||
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Climate change & severe weather | Habitat shifting & alteration | Timing | Scope | Severity | Impact | ||||
Future | Whole (>90%) | Unknown | Unknown | ||||||
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Climate change & severe weather | Other impacts | Timing | Scope | Severity | Impact | ||||
Future | Majority (50-90%) | Unknown | Unknown | ||||||
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Energy production & mining | Mining & quarrying | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Negligible declines | Low Impact: 4 | ||||||
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Bos taurus | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Negligible declines | Low Impact: 5 | ||||||
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Equus caballus | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Negligible declines | Unknown | ||||||
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Invasive and other problematic species, genes & diseases | Invasive non-native/alien species/diseases - Sus scrofa | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Negligible declines | Unknown | ||||||
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Invasive and other problematic species, genes & diseases | Problematic native species/diseases - Unspecified species | Timing | Scope | Severity | Impact | ||||
Past, Unlikely to Return | Unknown | Slow, Significant Declines | Past Impact | ||||||
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Natural system modifications | Fire & fire suppression - Trend Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Causing/Could cause fluctuations | Medium Impact: 6 | ||||||
|
Purpose | Scale |
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Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Gouldian Finch Chloebia gouldiae. Downloaded from
https://datazone.birdlife.org/species/factsheet/gouldian-finch-chloebia-gouldiae 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.