VU
Montserrat Oriole Icterus oberi



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
- - D1+2

Red List history
Year Category Criteria
2024 Vulnerable D1+2
2016 Vulnerable D1+2
2015 Critically Endangered B1ab(i,ii,iii,iv)
2013 Critically Endangered B1ab(i,ii,iii,iv)
2012 Critically Endangered B1ab(i,ii,iii,iv,v)
2010 Critically Endangered B1a+b(i,ii,iii,iv,v)
2009 Critically Endangered B1a+b(i,ii,iii,iv,v)
2008 Critically Endangered
2004 Critically Endangered
2000 Critically Endangered
1994 Lower Risk/Near Threatened
1988 Threatened
Species attributes

Migratory status not a migrant Forest dependency high
Land-mass type Average mass 36 g
Range

Estimate Data quality
Extent of Occurrence (breeding/resident) 48 km2 medium
Area of Occupancy (breeding/resident) 48 km2
Number of locations 2 -
Severely fragmented? no -
Population
Estimate Data quality Derivation Year of estimate
Population size 460 mature individuals medium estimated 2012
Population trend stable medium estimated -
Generation length 4.97 years - - -
Number of subpopulations 2 - - -
Percentage of mature individuals in largest subpopulation 80% - - -

Population justification: In 2012 the total population was estimated at 690 individuals (Oppel et al. 2014a). This estimate comprises 546 individuals in the Centre Hills, and 143 individuals in the South Soufrière Hills. This roughly equates to 460 mature individuals, with 364 mature individuals in the Centre Hills subpopulation and 95 mature individuals in the South Soufrière Hills subpopulation. The population has remained roughly stable since, despite some inter-annual fluctuations (Oppel et al. 2014b, Kitchener 2020).

Trend justification: Prior to 1995, this species was widespread across Montserrat. In that year however, volcanic activity began in the Soufrière Hills: A major eruption in 1996 caused a 60% decrease in range and population, with further eruptions in 2001 and 2003 causing heavy ash falls on large areas of the Centre Hills, destroying nests and curtailing breeding (Arendt et al. 1999; G. Hilton in litt. 2000, 2003; Hilton et al. 2003). In December 1997, the estimated population was c. 4,000 individuals, and intensive monitoring indicated declines by 40-50% in 1997-2003 (Arendt et al. 1999; G. Hilton in litt. 2000, 2003; Hilton et al. 2003).
The rapid declines noted between 1996 and 2003 have now ceased: In 2012 the population was estimated at c. 690 individuals (Oppel et al. 2014a), and monitoring data shows that the population is now overall stable, despite some fluctuations (S. Oppel in litt. 2015, Kitchener 2020). It is however noted that the population levels remain well below those of 1997. Population modelling projects a continuation of the stable trends or small increases up until 2028, though with considerable uncertainty relating to environmental and demographic stochasticity (Oppel et al. 2014b).


Country/territory distribution
Country/Territory Presence Origin Resident Breeding visitor Non-breeding visitor Passage migrant
Montserrat (to UK) extant native yes

Important Bird and Biodiversity Areas (IBA)
Country/Territory IBA Name
Montserrat (to UK) Centre Hills
Montserrat (to UK) South Soufriere Hills

Habitats & altitude
Habitat (level 1) Habitat (level 2) Importance Occurrence
Artificial/Terrestrial Plantations marginal resident
Artificial/Terrestrial Subtropical/Tropical Heavily Degraded Former Forest suitable resident
Forest Subtropical/Tropical Moist Lowland suitable resident
Forest Subtropical/Tropical Moist Montane major resident
Altitude 100 - 900 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 Minority (<50%) No decline Low Impact: 4
Stresses
Ecosystem degradation
Geological events Volcanoes Timing Scope Severity Impact
Past, Likely to Return Whole (>90%) Very Rapid Declines Past Impact
Stresses
Indirect ecosystem effects, Ecosystem degradation, Ecosystem conversion, 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
Invasive and other problematic species, genes & diseases Invasive non-native/alien species/diseases - Sus domesticus Timing Scope Severity Impact
Future Minority (<50%) Slow, Significant Declines Low Impact: 3
Stresses
Ecosystem degradation
Invasive and other problematic species, genes & diseases Problematic native species/diseases - Margarops fuscatus Timing Scope Severity Impact
Ongoing Whole (>90%) No decline Medium Impact: 6
Stresses
Reduced reproductive success
Residential & commercial development Housing & urban areas Timing Scope Severity Impact
Ongoing Minority (<50%) No decline Low Impact: 4
Stresses
Ecosystem degradation, Ecosystem conversion

Utilisation
Purpose Scale
Pets/display animals, horticulture international

Recommended citation
BirdLife International (2024) Species factsheet: Montserrat Oriole Icterus oberi. Downloaded from https://datazone.birdlife.org/species/factsheet/montserrat-oriole-icterus-oberi on 24/12/2024.
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 24/12/2024.