VU
Javan Myna Acridotheres javanicus



Taxonomy

Taxonomic note

Acridotheres grandis and A. javanicus (del Hoyo and Collar 2016) were previously lumped as A. grandis following Sibley & Monroe (1990, 1993).

 

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.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - A2d+3d+4d

Red List history
Year Category Criteria
2020 Vulnerable A2d+3d+4d
2016 Vulnerable A2d+3d+4d
2012 Not Recognised
2008 Not Recognised
2004 Not Recognised
2000 Not Recognised
1994 Not Recognised
1988 Not Recognised
Species attributes

Migratory status not a migrant Forest dependency does not normally occur in forest
Land-mass type Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 188,000 km2
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 2500-9999 mature individuals poor estimated 2016
Population trend decreasing - inferred 2014-2024
Rate of change over the past 10 years/3 generations (longer of the two periods) 30-49% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 30-49% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 30-49% - - -
Generation length 2.9 years - - -
Number of subpopulations 2-100 - - -
Percentage of mature individuals in largest subpopulation 1-89% - - -

Population justification: The population size is preliminarily estimated to fall in the band 2,500-9,999 mature individuals based on recent records for wild populations within Java and Bali. Introduced populations are considerably larger. In Singapore, although there have been fluctuations, the population was estimated as 168,000 individuals in 2000 (Yap 2003) and in Taiwan an estimate of over 20,000 was made in 1999 (Lin Rueyshing 2001). Furthermore, during the ‘Big Month’ citizen science event in January 2020 (comprising 22,054 checklists) across Java and Bali, the species was recorded in 121 (1.5%) of the 7,935 tetrads (2×2 km squares) visited (T. Squires and S. Marsden in litt. 2020).

Trend justification: Within the native wild range of the species the population has declined rapidly within the recent past to the point where this formerly abundant bird is very infrequently seen, and many recent records appear to derive from escaped captive birds (Eaton et al. 2015). Very large numbers have previously been trapped within the native range to supply the cage bird trade (Chng et al. 2015). The emergence of bird-farms to supply the market within the last few years, which are now the source of many traded individuals (Burung Indonesia in litt. 2016), appears to be a response to supply problems and coincided with the sudden difficulty of observing the species in the wild on Java. Supply from wild-caught birds is continuing as evidenced by the recent seizures of illegally traded birds coming into Java from Kalimantan and Sumatra (S. Chng in litt. 2016), which are considered to come from the large introduced populations of the species outside of the native range. Thus, the species is inferred to be undergoing a rapid decline of 30-49% over three generations.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Indonesia extant native yes
Japan possibly extant introduced yes
Malaysia extant introduced yes
Puerto Rico (to USA) extant introduced yes
Singapore extant introduced yes
Thailand extant introduced yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Artificial/Terrestrial Pastureland major resident
Artificial/Terrestrial Rural Gardens suitable resident
Grassland Subtropical/Tropical Dry major resident
Wetlands (inland) Bogs, Marshes, Swamps, Fens, Peatlands suitable resident
Altitude   Occasional altitudinal limits  

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
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
Stresses
Species disturbance, Hybridisation, Species mortality
Pollution Agricultural & forestry effluents - Herbicides and pesticides Timing Scope Severity Impact
Ongoing Unknown Unknown Unknown
Stresses
Species mortality

Utilisation
Purpose Scale
Pets/display animals, horticulture national, international

Recommended citation
BirdLife International (2024) Species factsheet: Javan Myna Acridotheres javanicus. Downloaded from https://datazone.birdlife.org/species/factsheet/javan-myna-acridotheres-javanicus on 27/12/2024.
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 27/12/2024.