NT
Togian Boobook Ninox burhani



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.
Indrawan, M.; Somadikarta, S. 2004. A new hawk-owl from the Togian Islands, Gulf of Tomini, central Sulawesi, Indonesia. Bulletin of the British Ornithologists' Club 124: 160-171.

IUCN Red List criteria met and history
Red List criteria met
Critically Endangered Endangered Vulnerable
- - -

Red List history
Year Category Criteria
2023 Near Threatened B1b(iii)+2b(iii); C1
2016 Near Threatened C2a(i)
2012 Near Threatened C2a(i)
2008 Near Threatened C2a(i)
2007 Near Threatened
2006 Not Evaluated
2004 Not Recognised
2000 Not Recognised
1994 Not Recognised
1988 Not Recognised
Species attributes

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

Estimate Data quality
Extent of Occurrence (breeding/resident) 1,700 km2 medium
Area of Occupancy (breeding/resident) 1,080 km2
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 2100-8100 mature individuals poor inferred 2022
Population trend decreasing - suspected 2016-2029
Rate of change over the past 10 years/3 generations (longer of the two periods) 5-15% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 10-20% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 10-20% - - -
Generation length 4.39 years - - -
Number of subpopulations 3-5 - - -
Percentage of mature individuals in largest subpopulation 1-89% - - -

Population justification: The population size of this species has never been formally estimated, although it is described as 'fairly common' by Eaton et al. (2021). Citizen science data (eBird 2023) affirm this description and suggest it occurs at relatively high density in areas for which it has been searched. Remote sensing data indicate that c.600 km2 of forest remains in its range (per Global Forest Watch 2023), and most of this is suspected to be occupied given this species' apparent tolerance of degradation (Eaton et al. 2021). Few robust densities for Ninox owls are available, although Jakosalem et al. (2013) recorded densities of up to 20 mature individuals/km2 for Ninox rumseyi of Cebu. However, these data were based on home ranges from satellite-tracking that the authors acknowledged yielded territory sizes that were probably too small due to the short time the birds were followed for. The estimated home ranges were, for example, up to ten times smaller than that of Ninox boobook sensu stricto (Olsen et al. 2011). Assuming a density of 5-15 mature individuals/km2, and an occupancy of 70-90%, the population size of Ninox burhani is inferred to be 2,100-8,100 mature individuals.

Trend justification: The population trend of this species has not been directly assessed although it is suspected to be declining in response to forest cover loss, which appears to be accelerating. In the three generations (13.2 years; Bird et al. 2020) to 2021, approximately 10% of forest cover was lost in this species' mapped range. Between 2016 and 2021, this accelerated to a rate equivalent to c.13%. However, this species is evidently tolerant of some habitat degradation (Eaton et al. 2021, eBird 2023) and it therefore may not be declining in parallel with forest losses. To account for this uncertainty, it is suspected to have declined by 5-15% in the past three generations, and (precautionarily assuming 2016-2021 rates of loss continue) by 10-20% in the next three generations.


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 Rural Gardens suitable resident
Artificial/Terrestrial Subtropical/Tropical Heavily Degraded Former Forest marginal resident
Forest Subtropical/Tropical Moist Lowland major resident
Shrubland Subtropical/Tropical Moist suitable resident
Altitude 0 - 400 m Occasional altitudinal limits  

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Agriculture & aquaculture Annual & perennial non-timber crops - Small-holder farming Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation

Recommended citation
BirdLife International (2024) Species factsheet: Togian Boobook Ninox burhani. Downloaded from https://datazone.birdlife.org/species/factsheet/togian-boobook-ninox-burhani 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.