email a friend
printable version
VU
Dusky Friarbird Philemon fuscicapillus

Justification
This species is classified as Vulnerable because it has a small population which is likely to be experiencing on-going declines owing to forest loss. It may be endemic to a single island, but identification difficulties mean that it is difficult to determine its true distribution, abundance, and hence its status.

Taxonomic source(s)
Sibley, C. G.; Monroe, B. L. 1990. Distribution and taxonomy of birds of the world. Yale University Press, New Haven, USA.

Identification
30 cm. Large, drab, forest-dwelling friarbird. Dark brown throughout, slightly paler below. Pink bare orbital skin. Heavy black bill with indistinct knob at base of culmen. Similar spp. Dusky-brown Oriole Oriolus phaeochromus almost identical, but smaller, with blunter bill, darker underparts and without bare pinkish skin around eye. Voice Probably gives variety of loud, coarse and nasal notes, although potentially mimicked by O. phaeochromus.

Distribution and population
Philemon fuscicapillus may be endemic to the island of Morotai (doubts have been raised over previous reports from Halmahera from where no specimens originate and no records can be traced to Bacan) in North Maluku, Indonesia (BirdLife International 2001). It was considered "very common" on Morotai in 1945. Assessment of its true status on Halmahera is severely hampered owing to visual mimicry by O. phaeochromus, and the possibility that it is largely overlooked in the canopy of tall trees.

Population justification
The population is estimated to number 2,500-9,999 mature individuals based on an assessment of known records, descriptions of abundance and range size. This is consistent with recorded population density estimates for congeners or close relatives with a similar body size, and the fact that only a proportion of the estimated Extent of Occurrence is likely to be occupied. This estimate is equivalent to 3,750-14,999 individuals, rounded here to 3,500-15,000 individuals.

Trend justification
Owing to this species's preference for lowland forest, habitat loss is suspected to be driving a moderate decline in its population.

Ecology
The species has been recorded in the canopy of primary and logged forest. It has also been found commonly in "secondary vegetation (bush)" and coconut plantations. Most records appear to be from the extreme lowlands (below 120 m), although it ascends rarely to 600 m.

Threats
Although it may be tolerant of quite severe habitat degradation, the primary threat is presumed to be forest loss, especially given its predilection for low elevations. It was reported in the 1990s that most of North Maluku, including around 90% of Halmahera and Bacan, remained forested. However, forest loss and fragmentation has accelerated greatly, through exploitation of economically valuable trees, and most remaining forest is now under timber concession. In addition, plans for agricultural development threaten further losses of original habitat.

Conservation Actions Underway
No direct measures are known. However, it may occur in the Lalobata and Ake Tajawe proposed protected area, which embraces c.3,550 km2 of all forest-types on the north-east peninsula of Halmahera, or the Gunung Sibela Strict Nature Reserve on Bacan, although this site is seriously threatened by agricultural encroachment and gold prospecting. Conservation Actions Proposed
Identify and record its vocalisations to aid its detection (if they differ significantly from those of O. phaeochromus). Conduct extensive surveys (especially within proposed or established protected areas) to establish its distribution, status, ecological requirements and altitudinal limits. Support the establishment and management of a protected area at Lolobata-Ake Tajawi (Halmahera) and Gunung Sibela Strict Nature Reserve (Bacan), should the species be found to occur there. Initiate conservation awareness campaigns to solicit local support for forest conservation.

References
BirdLife International. 2001. Threatened birds of Asia: the BirdLife International Red Data Book. BirdLife International, Cambridge, U.K.

Further web sources of information
Detailed species accounts from the Threatened birds of Asia: the BirdLife International Red Data Book (BirdLife International 2001).

Explore HBW Alive for further information on this species

Search for photos and videos, and hear sounds of this species from the Internet Bird Collection

Text account compilers
Benstead, P., Bird, J., Butchart, S., Taylor, J., Tobias, J.

Contributors
Bishop, K.

IUCN Red List evaluators
Butchart, S., Symes, A.

Recommended citation
BirdLife International (2014) Species factsheet: Philemon fuscicapillus. Downloaded from http://www.birdlife.org on 21/08/2014. Recommended citation for factsheets for more than one species: BirdLife International (2014) IUCN Red List for birds. Downloaded from http://www.birdlife.org on 21/08/2014.

This information is based upon, and updates, the information published in BirdLife International (2000) Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004) Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.

To provide new information to update this factsheet or to correct any errors, please email BirdLife

To contribute to discussions on the evaluation of the IUCN Red List status of Globally Threatened Birds, please visit BirdLife's Globally Threatened Bird Forums.

Key facts
Current IUCN Red List category Vulnerable
Family Meliphagidae (Honeyeaters)
Species name author (Wallace, 1862)
Population size 2500-9999 mature individuals
Population trend Decreasing
Distribution size (breeding/resident) 2,280 km2
Country endemic? Yes
Links to further information
- Additional Information on this species