Current view: Data table and detailed info
Taxonomic note
Alcedo euryzona and A. peninsulae (del Hoyo and Collar 2014) were previously lumped as A. euryzona following Sibley and Monroe (1990, 1993).
Taxonomic source(s)
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.
IUCN Red List criteria met and history
Red List criteria met
Red List history
Migratory status |
not a migrant |
Forest dependency |
high |
Land-mass type |
|
Average mass |
- |
Population justification: Difficult to estimate, but population size thought to be very small. After a long period without records (Hume 2017), the species has since been found at several localities. There are a handful of records from Gunung Halimun-Salak National Park (Chan and Setiawan 2019) and, in 2000-2001, five birds were mist-netted here at Cikaniki Research Station (Noske et al. 2011) and the species was observed on several occasions 2017-2023 (eBird 2024). The species was rediscovered at Petungkriyono forest in Central Java in 2018 (Chan and Setiawan 2019) and has been observed on several occasions since (Rachmawati et al. 2022, eBird 2024). There have also been isolated photographed records from Puncak Simpe in November 2020 and Gunung Liman/Mt Wilis in September 2022 and November 2023 (eBird 2024). A broader survey of the Sengkarang watershed (which Petungkriyono forest is part of) covering 34.2 km of transects across the five main rivers found just c. 3 pairs (per Yayasan SwaraOwa unpublished data).
While this pattern of records suggests that the species is widespread (and is certainly more widespread than the paucity of records in the early 2000s suggested), the species is evidently very rare, patchily distributed, and occurs at low density due to its linear ranges. At each of the listed sites above, there is <20 km of suitable habitat, with none likely to support more than 10 pairs (except Gunung Halimun-Salak National Park, which could conceivably support 2-3x this number). Accordingly, the minimum population size is set at 50 mature individuals. The maximum figure, 250, represents a somewhat arbitrary upper bound, accepting that while numerous sites probably remain undiscovered given the search of sightings in recent years, there remains so little habitat on Java that it is unlikely to exceed this.
Trend justification: Trend poorly known due to the species' contemporary distribution only recently being understood. However, it is evidently highly sensitive to forest loss and disturbance, with all sightings made in good habitat along undisturbed rivers, and absences from degraded habitat that at one time would have been suitable and almost certainly hosted the species. While overall forest cover loss on Java has been minimal for c. 20 years (Global Forest Watch 2024), areas along rivers continue to be cleared and degraded (Hansen et al. 2013, Grantham et al. 2020, Global Forest Watch 2024). Accordingly, A. euryzona is precautionarily inferred to be declining, although monitoring data are urgently needed to confirm whether this is the case.
Country/territory distribution
Important Bird and Biodiversity Areas (IBA)
Recommended citation
BirdLife International (2024) Species factsheet: Javan Blue-banded Kingfisher Alcedo euryzona. Downloaded from
https://datazone.birdlife.org/species/factsheet/javan-blue-banded-kingfisher-alcedo-euryzona 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.