LC
Red-eared Fruit-dove Ramphiculus fischeri



Taxonomy

Taxonomic note

Ramphiculus fischeri was previously split as R. fischeri and R. meridionalis (del Hoyo and Collar 2014), prior to which they were previously placed in the genus Ptilinopus and lumped as P. fischeri following Sibley and Monroe (1990, 1993). Taxon meridionalis differs in its dark slate-grey vs dull emerald-green wing-coverts, secondaries, tertials, back and rump (3); mantle as dark grey as rest of wings and back vs whitish-grey shading to mid-grey before shading to the green of the upper back (ns1); white vs yellowish-white chin and upper throat (ns1); breast to mid-belly greyish-white vs mid-grey (2); mid-belly to vent greyish-white vs dull yellowish-grey (2). However, the form centralis sits between these two extremes and is intermediate in plumage, suggesting that differences may be clinal, and there is no indication of any vocal difference, so for now meridionalis is returned to a subspecies of R. fischeri. Formerly placed in genus Leucotreron. Closely allied to R. occipitalis. Three subspecies recognized.

Taxonomic source(s)
Handbook of the Birds of the World and BirdLife International. 2023. Handbook of the Birds of the World and BirdLife International digital checklist of the birds of the world. Version 8. Available at: https://datazone.birdlife.org/userfiles/file/Species/Taxonomy/HBW-BirdLife_Checklist_v8_Dec23.zip.

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

Red List history
Year Category Criteria
2023 Least Concern
2016 Not Recognised
2014 Not Recognised
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) 267,000 km2
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size unknown - - -
Population trend decreasing - suspected -
Generation length 5.61 years - - -
Number of subpopulations 3 - - -
Percentage of mature individuals in largest subpopulation 1-89% - - -

Population justification: The global population size has not been quantified, but the species is described as uncommon (Gibbs et al. 2001, Eaton et al. 2021).

Trend justification: Much of this species' range lies above the altitudes where forest loss is occurring, and remote sensing data indicates that tree cover loss is ongoing slowly at a rate equivalent to 3-4% in three generations (Global Forest Watch 2023 using data from Hansen et al. [2013] and methods disclosed therein). The environs of the Lompobattang massif are one of the most densely populated areas of Sulawesi and all forest below 1,000-1,500 m, and locally up to 1,700 m, has disappeared as a result of land clearance for transmigration settlements, commercial logging and both shifting and plantation agriculture, affecting subspecies meridionalis. Remaining forest continues to be threatened by human activities. However, records from recently logged forest (eBird 2023) suggest this species may be relatively adaptable and less seriously threatened by logging activities than many forest birds (del Hoyo et al. 2022). Precautionarily therefore, the species is suspected to be declining slowly as a result of ongoing forest loss, although the rate has not been quantified.


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
Indonesia Bogani Nani Wartabone
Indonesia Gunung Klabat
Indonesia Gunung Simbalang
Indonesia Karaeng - Lompobattang
Indonesia Lore Lindu
Indonesia Mekongga
Indonesia Morowali
Indonesia Pegunungan Latimojong

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Forest Subtropical/Tropical Moist Montane major resident
Altitude 1000 - 3000 m Occasional altitudinal limits  

Threats & impact
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%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
Agriculture & aquaculture Annual & perennial non-timber crops - Shifting agriculture Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Logging & wood harvesting - Unintentional effects: (large scale) [harvest] Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
Biological resource use Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest] Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion
Residential & commercial development Housing & urban areas Timing Scope Severity Impact
Ongoing Minority (<50%) Slow, Significant Declines Low Impact: 5
Stresses
Ecosystem degradation, Ecosystem conversion

Recommended citation
BirdLife International (2024) Species factsheet: Red-eared Fruit-dove Ramphiculus fischeri. Downloaded from https://datazone.birdlife.org/species/factsheet/red-eared-fruit-dove-ramphiculus-fischeri on 22/11/2024.
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 22/11/2024.