NT
Black-faced Pitta Pitta anerythra



Taxonomy

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.

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(ii,iii)
2016 Vulnerable D1
2012 Vulnerable D1
2008 Vulnerable D1
2004 Vulnerable
2000 Vulnerable
1996 Vulnerable
1994 Vulnerable
1988 Threatened
Species attributes

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

Estimate Data quality
Extent of Occurrence (breeding/resident) 18,000 km2 medium
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 2500-10000, 6500 mature individuals poor estimated 2022
Population trend decreasing poor suspected 2016-2027
Rate of change over the past 10 years/3 generations (longer of the two periods) 1-9% - - -
Rate of change over the future 10 years/3 generations (longer of the two periods) 1-9% - - -
Rate of change over the past & future 10 years/3 generations (longer of the two periods) 1-9% - - -
Generation length 3.89 years - - -
Number of subpopulations 2-100 - - -
Percentage of mature individuals in largest subpopulation 1-89% - - -

Population justification: This species is poorly understood, with recent records mostly from Tirotonga Village where it is described as fairly common (Dutson 2011). The species is protected in this area with a density of approximately five calling birds per 1.5 km2 block, although it is suspected to be scarce across most of its range (J. Bergmark in litt. 2022). Based on this density and assuming that 50% of suitable habitat is occupied, the species’ population size is estimated to number approximately 6,500 mature individuals and is tentatively placed here in the range 2,500-10,000. There is much uncertainty surrounding this population estimate however and it may be much lower; density is high around Tirotonga village where the species is actively protected but it is suspected to be very scarce across the remainder of its range (J. Bergmark in litt. 2022).
It is described as uncommon at the headwaters of the Kolosita River on Santa Isabel, with up to five individuals reported daily around 600 m (DeCicco et al. 2019). It was formerly reasonably common, at least on Bougainville, where 40 specimens were collected before 1938 (Erritzoe and Erritzoe 1998). It was then not recorded until 1994 when it was found to be fairly common at Tirotonga on Santa Isabel (Gibbs 1996), with up to three birds heard calling simultaneously (D. Gibbs in litt. 1994, Gibbs 1996, G. Dutson pers. obs. 1998). Searches and interviews on Choiseul and Bougainville have been unsuccessful (D. Gibbs in litt. 1994, K. D. Bishop in litt. 1997, G. Dutson pers. obs. 1998) until it was recorded on Choiseul in 2014 (Boseto and Pikacha 2015), although is possibly extirpated on Bougainville (Hadden 2004, Woxvold and Novera 2021).

Trend justification: There are no data on population trends; however, the species is suspected to be declining owing to forest loss and degradation. In the three generations (11.7 years; Bird et al. 2020) to 2021, remote sensing data indicate that 5-7% of forest was lost in the species' range (Global Forest Watch 2022, using data from Hansen et al. [2013] and methods disclosed therein) and this may accelerate slightly (to an equivalent rate of 7-9%) in the future based on losses in 2016-2021. The rate of population decline is tentatively placed here in the range 1-9% within three generations.


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Papua New Guinea possibly extant native yes
Solomon Islands extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Solomon Islands Kolombangara Upland Forest
Solomon Islands Mount Maetambe - Kolombangara River

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Artificial/Terrestrial Rural Gardens suitable resident
Forest Subtropical/Tropical Moist Lowland major resident
Shrubland Subtropical/Tropical Moist suitable resident
Altitude 0 - 600 m Occasional altitudinal limits  

Threats & impact
Threat (level 1) Threat (level 2) Impact and Stresses
Biological resource use Logging & wood harvesting - Unintentional effects: (large scale) [harvest] Timing Scope Severity Impact
Ongoing Majority (50-90%) Slow, Significant Declines Medium Impact: 6
Stresses
Ecosystem degradation, Ecosystem conversion
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Canis familiaris Timing Scope Severity Impact
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Species mortality
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Felis catus Timing Scope Severity Impact
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Species mortality
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Named species Timing Scope Severity Impact
Ongoing Minority (<50%) Negligible declines Low Impact: 4
Stresses
Reduced reproductive success

Recommended citation
BirdLife International (2024) Species factsheet: Black-faced Pitta Pitta anerythra. Downloaded from https://datazone.birdlife.org/species/factsheet/black-faced-pitta-pitta-anerythra 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.