VU
Sangkar White-eye Zosterops melanurus



Taxonomy

Taxonomic note
Oriental White-eye Zosterops palpebrosus has been split into Indian White-eye Z. palpebrosus, Hume's White-eye Z. auriventer and Sangkar White-eye Z. melanurus on the basis of thorough morphological comparisons (Wells et al. 2017a, b) and genetic differentiation, morphology and vocalisations (Round et al. 2017, Lim et al. 2019). 

The subspecies Z. m. buxtoni is here cautiously treated in line with Lim et al. (2019), who conclude: 'photographic evidence of populations in montane Sumatra strongly suggests the presence of a population of the montane species Hume’s White-eye, Zosterops auriventer … that has hitherto been misidentified (unpublished data), and we follow this preliminary evidence here in excluding montane Sumatran populations from the range of buxtoni.

Taxonomic source(s)
Handbook of the Birds of the World and BirdLife International. 2019. Handbook of the Birds of the World and BirdLife International digital checklist of the birds of the world. Version 4. Available at: https://datazone.birdlife.org/userfiles/file/Species/Taxonomy/HBW-BirdLife_Checklist_v4_Dec19.zip.
Lim, B.T., Sadanandan, K.R., Dingle, C., Leung, Y.Y., Prawiradilaga, D.M., Irham, M., Ashari, H., Lee, J.G. & Rheindt, F.E. 2019. Molecular evidence suggests radical revision of species limits in the great speciator white-eye genus Zosterops. Journal of Ornithology 160(1): 1-16.

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

Red List history
Year Category Criteria
2021 Vulnerable A2d+3d+4d
2019 Vulnerable A2d+3d+4d
2016 Not Recognised
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 medium
Land-mass type Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 189,000 km2
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size unknown - - -
Population trend decreasing - inferred 2018-2028
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 2.3 years - - -

Population justification: Quantitative population estimates do not exist for this species and, due to the presence of extensive trapping, a total population estimate cannot be calculated from population density estimates. However, the species is described as common on Java and Bali (Eaton et al. 2016). Weeklong ornithological surveys across 27 sites on nine mountains in West-Central Java between 2018 and 2020 for example found the species at 14 sites and on 7 mountains with a mean encounter rate of 0.39 groups/hour (range = 0.19 to 0.66 where present; C. Devenish, A. R. Junaid and S. Marsden in litt. 2020). During the ‘Big Month’ citizen science event (conducted in January 2020 comprising 22,054 checklists) across Java and Bali moreover, the species was recorded in 61 (0.77%) of the 7,935 tetrads (2 × 2 km squares) visited (T. Squires and S. Marsden in litt. 2020).

Trend justification: On the basis of the observed numbers in markets, it has been suggested that a '30% reduction in global population size over the past 10 years is a reasonable, if not conservative assumption' (Lim et al. 2019). As such, the species is assessed as having a decreasing population size. Judging the likely rate of population decline is difficult in this circumstance however. There are anecdotal reports of greatly reduced numbers at multiple sites across Java (including possibility of local extinction across Sukapua, Resmi Tinggal Village, Kertasari, and Bandung due to extensive trapping during 2009-2012; Akbar and van Balen 2020), where the species would be expected to be abundant (S. Mahood in litt. 2019; F. Rheindt in litt. 2019), coupled with inferred rising prices for the species in bird markets implying a reduction in availability and the strong impression that the numbers recorded in trade are far above a sustainable number (Lim et al. 2019). Symes et al. (2018) assigned probability curves according to expert opinion on trade desirability in conjunction with accessibility (based on a distance to forest edge from remote sensed forest data) to determine likely rates of population loss over the next three generation or ten year period: across the entire Sundaic range of the pre-split species, the estimated loss was 55%, but this analysis had no term to account for reproduction. While there is no direct data that can be used to estimate a rate of decline, it is suspected that a decline in excess of the threshold of 30% has been occurring over the past ten years, and this rate is not likely to diminish in the near future. There is a need for more field data that can be used to estimate the actual rate of decline, and for additional data to track numbers and prices at a sample of Javan markets.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Indonesia extant native yes

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

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Artificial/Terrestrial Plantations suitable resident
Artificial/Terrestrial Rural Gardens suitable resident
Artificial/Terrestrial Subtropical/Tropical Heavily Degraded Former Forest suitable resident
Artificial/Terrestrial Urban Areas suitable resident
Forest Subtropical/Tropical Mangrove Vegetation Above High Tide Level suitable resident
Forest Subtropical/Tropical Moist Lowland major resident
Forest Subtropical/Tropical Moist Montane suitable resident
Forest Subtropical/Tropical Swamp suitable resident
Introduced vegetation suitable resident
Shrubland Subtropical/Tropical Moist suitable resident
Altitude 100 - 2500 m Occasional altitudinal limits (min) 0 m

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Agriculture & aquaculture Annual & perennial non-timber crops - Scale Unknown/Unrecorded Timing Scope Severity Impact
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Hunting & trapping terrestrial animals - Intentional use (species is the target) Timing Scope Severity Impact
Ongoing Majority (50-90%) Rapid Declines Medium Impact: 7
Stresses
Species mortality

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

Recommended citation
BirdLife International (2024) Species factsheet: Sangkar White-eye Zosterops melanurus. Downloaded from https://datazone.birdlife.org/species/factsheet/sangkar-white-eye-zosterops-melanurus 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.