Taxonomic source(s)
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 |
---|---|---|
B1ab(v); C2a(i,ii); D | B1ab(v); C2a(i,ii); D | B1ab(v); C2a(i,ii); D1+2 |
Year | Category | Criteria |
---|---|---|
2021 | Critically Endangered | B1ab(v); C2a(i,ii); D |
2018 | Critically Endangered | B1ab(v);C2a(i,ii);D |
2016 | Critically Endangered | B1ab(v);C2a(i,ii);D |
2015 | Critically Endangered | B1ab(v);C2a(i,ii);D |
2013 | Critically Endangered | B1ab(v);C2a(i,ii);D |
2012 | Critically Endangered | B1ab(v);C2a(i,ii);D |
2010 | Critically Endangered | B1a+b(v); C2a(ii); D1 |
2009 | Critically Endangered | B1a+b(v); C2a(ii); D1 |
2008 | Critically Endangered | |
2006 | Critically Endangered | |
2004 | Critically Endangered | |
2000 | Critically Endangered | |
1996 | Critically Endangered | |
1994 | Critically Endangered | |
1988 | Threatened |
Migratory status | not a migrant | Forest dependency | medium |
Land-mass type |
shelf island |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 38 km2 | medium |
Number of locations | 1 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | 1-49 mature individuals | medium | estimated | 2009 |
Population trend | decreasing | good | inferred | - |
Generation length | 6.2 years | - | - | - |
Number of subpopulations | 1 | - | - | - |
Percentage of mature individuals in largest subpopulation | 100% | - | - | - |
Population justification: At the release site in West Bali National Park, c.50 individuals were estimated in 2008 (G. Dijkman in litt. 2008). At the release site on Nusa Penida Island, the population was recorded as 65 adults and 62 juveniles in 2009 (C. Kenwrick in litt. 2009). In February and March 2015, staff of Begawan Foundation and Wildlife Reserves Singapore undertook an audit on Nusa Penida and Nusa Lembongan Islands, which only found 12 adults and a possible 2 birds in nests (Halaouate 2015). At least at one other release site, the species appears to be doing well (Marsden 2017). In April 2019, 191 individuals were counted at Bali Barat National Park, following at least 100 birds being released in November 2018, although many were immature individuals (T. Squires in litt. 2019). However, as IUCN stipulates that re-introduced individuals must have produced viable offspring before they are counted as mature individuals, the population size is precautionarily assumed to be fewer than 50 mature individuals, although this may warrant revising upwards if there is continued evidence of breeding success.
Trend justification: The wild population has been maintained only by release of captive birds, so is essentially gradually declining. The trend of the introduced colonies is difficult to determine; while the two major populations on Nusa Penida Island and in West Bali National Park initially increased to over 50 individuals each in 2008-2009 (G. Dijkman in litt. 2008; C. Kenwrick in litt. 2009), further increasing to 120 birds on Nusa Penida Island by 2012-2013 (Nijman et al. 2017), the colonies on both Nusa Penida and Nusa Lembongan Islands decreased to less than 20 birds by 2015 due to illegal trapping, with a reported 85% decline on Nusa Penida alone (M. Halaouate in litt. 2013; Halaouate 2015; Nijman et al. 2017).
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Indonesia | extant | native | yes |
Country/Territory | IBA Name |
---|
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Artificial/Terrestrial | Plantations | possible | resident |
Forest | Subtropical/Tropical Dry | major | resident |
Savanna | Dry | major | resident |
Shrubland | Subtropical/Tropical Dry | suitable | breeding |
Altitude | 0 - 175 m | Occasional altitudinal limits |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Scale Unknown/Unrecorded | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Rapid Declines | Medium Impact: 7 | ||||||
|
|||||||||
Agriculture & aquaculture | Wood & pulp plantations - Agro-industry plantations | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
|||||||||
Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Whole (>90%) | Rapid Declines | High Impact: 8 | ||||||
|
|||||||||
Invasive and other problematic species, genes & diseases | Problematic native species/diseases | Timing | Scope | Severity | Impact | ||||
Ongoing | Unknown | Unknown | Unknown | ||||||
|
|||||||||
Residential & commercial development | Housing & urban areas | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Slow, Significant Declines | Medium Impact: 6 | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | international |
Recommended citation
BirdLife International (2024) Species factsheet: Bali Myna Leucopsar rothschildi. Downloaded from
https://datazone.birdlife.org/species/factsheet/bali-myna-leucopsar-rothschildi on 22/12/2024.
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 22/12/2024.