Current view: Data table and detailed info
Taxonomic note
Mulleripicus funebris and M. fuliginosus (del Hoyo and Collar 2014) were previously lumped as M. funebris following Sibley and Monroe (1990, 1993).
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.
IUCN Red List criteria met and history
Red List criteria met
Red List history
Migratory status |
not a migrant |
Forest dependency |
high |
Land-mass type |
|
Average mass |
164 g |
Population justification: The global population size has not been quantified, although it is considered rare (Allen 2020) and has undoubtedly been reduced in number over the past three generations. Despite increasingly comprehensive survey effort, this species has not been discovered at many sites (eBird 2023). Records from Samar are especially scarce and the species may now be confined (or functionally so) to Samar Island Natural Park, where habitat degradation is ongoing (Hutchinson 2021). On Mindanao, records from PICOP have decreased in frequency over the past two decades, and the population at this site may no longer be particularly large (eBird 2023). The only other site of frequent observation is Pasonanca Natural Park (Zamboanga), and sightings elsewhere are typically in small and increasingly fragmented areas of mountain foothill forest. No single subpopulation is suspected of numbering more than 1,000 mature individuals, and precautionarily the global population size is suspected of being fewer than 10,000 mature individuals
Trend justification: The population is inferred to be declining due to forest loss and degradation. There are no empirical survey data from which to derive rates of population decline, thus forest cover loss is used as a proxy. Over the past three generations (16 years: 2006-2022), forest cover loss in this species has been 13-19%, depending on the assumptions used (Global Forest Watch 2023, based on data from Hansen et al. [2013] and methods disclosed therein). Rates of forest loss appear to have accelerated since c. 2014, equivalent to a rate of 17-23% over three generations. However, rates of forest cover loss are believed to (perhaps significantly) underestimate population declines. First, forest losses over the past three generations appear spatially biased towards areas of primary forest from which this species is known (despite effort elsewhere), suggesting that M. fuliginosus is being disproportionately affected. Moreover, selective logging is thought to be having a significant impact on this species (probably via the removal of suitable nesting trees); this is evidenced by it becoming more difficult to see at some points, for example, at PICOP, where its detection rate has undoubtedly dropped in recent years (eBird 2023) at a rate that appears to have exceeded net forest loss. Over the past three generations, the rate of population decline is therefore suspected to have been in the range of 15-29%, with an acceleration in both the current and projected future rates of loss, set precautionarily at 20-35%.
Country/territory distribution
Important Bird and Biodiversity Areas (IBA)
Recommended citation
BirdLife International (2024) Species factsheet: Southern Sooty Woodpecker Mulleripicus fuliginosus. Downloaded from
https://datazone.birdlife.org/species/factsheet/southern-sooty-woodpecker-mulleripicus-fuliginosus 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.