• Summary
• Text account
• Data table and detailed info
• Distribution map
• Reference and further resources

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.

Red List criteria met

Critically Endangered	Endangered	Vulnerable
-	-	-

Red List history

Year	Category	Criteria
2023	Least Concern
2016	Near Threatened	C1
2012	Near Threatened	C1
2008	Near Threatened	C1
2004	Near Threatened
2000	Lower Risk/Near Threatened
1994	Lower Risk/Least Concern
1988	Lower Risk/Least Concern

Migratory status	nomadic	Forest dependency	high
Land-mass type		Average mass	24 g

	Estimate	Data quality
Extent of Occurrence (breeding/resident)	102,000 km2	medium
Severely fragmented?	no	-

	Estimate	Data quality	Derivation	Year of estimate
Population size	unknown	-	-	-
Population trend	stable	poor	suspected	-
Generation length	3.2 years	-	-	-
Number of subpopulations	7-20	-	-	-
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 common above 1000 m on Bougainville, Kolombangara and Guadalcanal, but rarer on other islands (del Hoyo et al. 1997, Dutson 2011, Collar and Boesman 2021). Buckingham et al. (1990) recorded 17 contacts/km² in old-growth hill forest, 220 in primary montane forest (> about 500 m) and 640 in primary moss forest (> about 1200 m) on Kolombangara, and flocks of 3–8+ were recorded daily above 1,450 m at Kukupi, Bougainville (Woxvold and Novera 2021). The population likely numbers above 10,000 mature individuals (G. Dutson in litt. 2023).

Trend justification: There are no data on population trends, however forest loss is low within the range, equivalent to c.2% within the ten years to 2021 (Global Forest Watch 2022, using Hansen et al. [2013] data and methods disclosed therein). In the absence of evidence for any declines or substantial threats, the species is suspected to be stable overall.

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

Country/Territory	IBA Name
Solomon Islands	East Makira
Solomon Islands	Guadalcanal Watersheds
Solomon Islands	Kolombangara Upland Forest
Solomon Islands	Malaita Highlands

Habitat (level 1)	Habitat (level 2)	Importance	Occurrence
Artificial/Terrestrial	Plantations	suitable	resident
Forest	Subtropical/Tropical Moist Lowland	suitable	resident
Forest	Subtropical/Tropical Moist Montane	major	resident
Altitude	1000 - 1200 m	Occasional altitudinal limits	0 - 1700 m

Threat (level 1)	Threat (level 2)	Impact and Stresses
Biological resource use	Logging & wood harvesting - Unintentional effects: (subsistence/small scale) [harvest]	Timing		Scope		Severity		Impact
		Ongoing		Minority (<50%)		Negligible declines		Low Impact: 4
		Stresses Ecosystem degradation

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Recommended citation
BirdLife International (2024) Species factsheet: Meek's Lorikeet Charmosyna meeki. Downloaded from https://datazone.birdlife.org/species/factsheet/meeks-lorikeet-charmosyna-meeki on 23/11/2024.
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 23/11/2024.