Taxonomic note
Laniellus albonotatus (del Hoyo and Collar 2016) was previously listed as Crocias albonotatus.
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 |
---|---|---|
- | - | - |
Year | Category | Criteria |
---|---|---|
2024 | Near Threatened | B1ab(iii) |
2016 | Near Threatened | B1ab(i,ii,iii,iv,v) |
2012 | Near Threatened | B1ab(i,ii,iii,iv,v) |
2008 | Near Threatened | B1a+b(i,ii,iii,iv,v) |
2004 | Near Threatened | |
2000 | Lower Risk/Near Threatened | |
1994 | Lower Risk/Near Threatened | |
1988 | Near Threatened |
Migratory status | not a migrant | Forest dependency | high |
Land-mass type |
shelf island |
Average mass | - |
Estimate | Data quality | |
---|---|---|
Extent of Occurrence (breeding/resident) | 19,000 km2 | medium |
Area of Occupancy (breeding/resident) | 3,252 km2 | |
Number of locations | 11-50 | - |
Severely fragmented? | no | - |
Estimate | Data quality | Derivation | Year of estimate | |
---|---|---|---|---|
Population size | unknown | - | - | - |
Population trend | unknown | poor | - | - |
Generation length | 3.8 years | - | - | - |
Number of subpopulations | 6 | - | - | - |
Percentage of mature individuals in largest subpopulation | 1-89% | - | - | - |
Population justification: The global population size has not been quantified. Described as uncommon by Eaton et al. (2021), although Marsden et al. (2023) found them along 77 transects at 21 sites, with an encounter rate similar to other montane endemic passerines. Nijman et al. (2021) estimated that c.1,200-1,500 birds were sold in markets each year, somewhat sustainably. It is unclear what percentage of these are wild-caught; if a majority, this would suggest that the population of L. albonotatus numbers at least several thousand birds.
Trend justification: There are no robust data on the trends of this species. Habitat loss in its range has been minimal over the past two decades, although at the lower elevations of its range there is evidence of some clearance and additional degradation (Global Forest Watch 2024, using data from Hansen et al. [2013] and methods disclosed therein), the impact of which is unknown. The price of L. albnonotatus has remained relatively stable in the past 12 years suggesting that supply of birds is not decreasing (Nijman et al. 2021); however, it is unclear whether all of these birds are wild-caught, nor whether this is strictly a reliable indicator of trend. The trend is therefore considered unknown.
Country/Territory | Presence | Origin | Resident | Breeding visitor | Non-breeding visitor | Passage migrant |
---|---|---|---|---|---|---|
Indonesia | extant | native | yes |
Country/Territory | IBA Name |
---|---|
Indonesia | Gunung Ceremai |
Indonesia | Gunung Gede - Pangrango |
Indonesia | Gunung Halimun |
Indonesia | Gunung Manglayang |
Indonesia | Gunung Masigit-Kareumbi |
Indonesia | Gunung Papandayan-Kamojang |
Indonesia | Gunung Salak |
Indonesia | Gunung Slamet |
Indonesia | Gunung Tilu-Simpang |
Indonesia | Telaga Warna-Cibulao |
Habitat (level 1) | Habitat (level 2) | Importance | Occurrence |
---|---|---|---|
Forest | Subtropical/Tropical Moist Montane | major | resident |
Altitude | 1400 - 2500 m | Occasional altitudinal limits | (min) 900 m |
Threat (level 1) | Threat (level 2) | Impact and Stresses | |||||||
---|---|---|---|---|---|---|---|---|---|
Agriculture & aquaculture | Annual & perennial non-timber crops - Agro-industry farming | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
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Biological resource use | Hunting & trapping terrestrial animals - Intentional use (species is the target) | Timing | Scope | Severity | Impact | ||||
Ongoing | Majority (50-90%) | Unknown | Unknown | ||||||
|
|||||||||
Biological resource use | Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
|||||||||
Natural system modifications | Fire & fire suppression - Increase in fire frequency/intensity | Timing | Scope | Severity | Impact | ||||
Ongoing | Minority (<50%) | Unknown | Unknown | ||||||
|
Purpose | Scale |
---|---|
Pets/display animals, horticulture | subsistence, national |
Recommended citation
BirdLife International (2024) Species factsheet: Spotted Crocias Laniellus albonotatus. Downloaded from
https://datazone.birdlife.org/species/factsheet/spotted-crocias-laniellus-albonotatus 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.