NT
Barred Eagle-owl Bubo sumatranus



Taxonomy

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
Critically Endangered Endangered Vulnerable
- - -

Red List history
Year Category Criteria
2022 Near Threatened A2cd+3cd+4cd
2016 Least Concern
2012 Least Concern
2009 Least Concern
2008 Least Concern
2004 Least Concern
2000 Lower Risk/Least Concern
1994 Lower Risk/Least Concern
1988 Lower Risk/Least Concern
Species attributes

Migratory status not a migrant Forest dependency medium
Land-mass type Average mass -
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 4,270,000 km2
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size unknown - - -
Population trend decreasing - suspected 2016-2038
Rate of change over the past 10 years/3 generations (longer of the two periods) 20-29% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 20-29% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 20-29% - - -
Generation length 7.31 years - - -

Population justification: The global population of this species remains un-estimated. In oil palm plantations it appears to be too rare to generate reliable population densities (see Yahya et al. 2020) while in primary forest it has been recorded at densities of c.1.16 birds/km2 in southern Thailand (Kempt et al. 2009). The species is often described as common or uncommon (del Hoyo et al. 1999, Wells 1999, Eaton et al. 2021) and appears relatively adaptable to habitat modification, occurring too in isolated park fragments in cities (eBird 2021).

Trend justification: Using a previous three-generation length period (27.9 years), and based on forest loss between 2000 and 2012, Tracewski et al. (2016) estimated this species to have lost 26% of its habitat. Although the three-generation period is now shorter (22 years; Bird et al. 2020), the rate of forest loss in the range of this species has accelerated since 2012, such that forest cover (with a canopy cover greater than 30%) is estimated to have been reduced by 24-28% over the last three generations (based on data between 2000 and 2020) (Global Forest Watch [2021], using Hansen et al. [2013] and methods disclosed therein). Much of this forest cover loss has been the result of complete clearance and conversion to oil palm plantations. Although this species does occur in oil palm (e.g. Yahya et al. 2020), it does so at lower densities than in primary forest (see Kemp et al. 2009 vs Yahya et al. 2020). It does, however, appear tolerant of fragmentation and can persists in heavily degraded areas, including urban parks (eBird 2021). For these reasons, population reductions are suspected to be at a lower rate than that of forest loss: suspected here to be 15-20%. This species is also affected by capture for the pet trade (Nijman & Nekaris 2017, Siriwat et al. 2020). Using assigned probability curves according to expert opinion on trade desirability in conjunction with accessibility to determine likely rates of population loss over the next three generations (they used a previous value of 34.8 years), Symes et al. (2018) estimated loss from hunting amounted to 16.5%, but this analysis had no term to account for reproduction and the species remains comparatively rare in market surveys in most of its range (Nijman & Nekaris 2017) with no indication the species is getting more desirable. Adjusting this rate for the current three-generation period and acknowledging that the species still appears rare in markets, hunting is suspected to be causing declines of 5-10%. Accumulating threats, the species is suspected to have declined 20-29% over the past three generations; this rate of decline is suspected to continue at the same rate into the future.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Brunei extant native yes
Indonesia extant native yes
Malaysia extant native yes
Myanmar extant native yes
Singapore extinct native yes
Thailand extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Malaysia Bako-Buntal Bay
Malaysia Bau Limestone
Malaysia Belum-Temenggor
Malaysia Bintang Range
Malaysia Central Titiwangsa Range
Malaysia Danum Valley Conservation Area
Malaysia Endau-Rompin
Malaysia Gunung Pueh
Malaysia Kabili-Sepilok
Malaysia Kelabit Highlands
Malaysia Klias peninsula
Malaysia Krau Wildlife Reserve
Malaysia Lambir Hills National Park
Malaysia Lanjak Entimau Wildlife Sanctuary
Malaysia Niah National Park
Malaysia Panti forest
Malaysia Pondok Tanjung Forest Reserve
Malaysia Similajau National Park
Malaysia South-east Pahang peat swamp forest
Malaysia Tabin Wildlife Reserve
Malaysia Taman Negara National Park
Malaysia Tanjung Datu-Samunsam Protected Area
Malaysia Tawau Hills Park
Thailand Bala Sector, Hala-Bala Wildlife Sanctuary
Thailand Khao Nor Chuchi

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 Moist Lowland major resident
Forest Subtropical/Tropical Moist Montane suitable resident
Altitude 0 - 1600 m Occasional altitudinal limits (max) 2000 m

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Agriculture & aquaculture Annual & perennial non-timber crops - Shifting agriculture Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Wood & pulp plantations - Agro-industry plantations Timing Scope Severity Impact
Ongoing Majority (50-90%) Rapid Declines Medium Impact: 7
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Wood & pulp plantations - Small-holder plantations Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
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%) Slow, Significant Declines Medium Impact: 6
Stresses
Species mortality

Utilisation
Purpose Scale
Food - human subsistence, national, international
Pets/display animals, horticulture national, international

Recommended citation
BirdLife International (2024) Species factsheet: Barred Eagle-owl Bubo sumatranus. Downloaded from https://datazone.birdlife.org/species/factsheet/barred-eagle-owl-bubo-sumatranus on 23/12/2024.
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 23/12/2024.