Red Owl Tyto soumagnei Scientific name definitions
- VU Vulnerable
- Names (20)
- Monotypic
Text last updated December 3, 2015
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Species names in all available languages
Language | Common name |
---|---|
Bulgarian | Мадагаскарска забулена сова |
Catalan | òliba de Madagascar |
Czech | sova madagaskarská |
Dutch | Madagaskargrasuil |
English | Red Owl |
English (United States) | Red Owl |
French | Effraie de Soumagne |
French (France) | Effraie de Soumagne |
German | Malegasseneule |
Japanese | マダガスカルメンフクロウ |
Norwegian | okerslørugle |
Polish | płomykówka madagaskarska |
Russian | Мадагаскарская сипуха |
Serbian | Crvena kukuvija |
Slovak | plamienka oranžová |
Spanish | Lechuza Malgache |
Spanish (Spain) | Lechuza malgache |
Swedish | madagaskartornuggla |
Turkish | Madagaskar Peçeli Baykuşu |
Ukrainian | Сипуха мадагаскарська |
Tyto soumagnei (Grandidier, 1878)
Definitions
- TYTO
- soumagnei
The Key to Scientific Names
Legend Overview
Field Identification
27–30 cm; 323–435 g (1). Plumage suffused orange-red, darker (ochre-yellow to reddish-ochre) above and paler (more ochre) below , with fine black spots; tail relatively long (1); heart-shaped facial disc greyish-buff , darker around eyes and on rim (1); eyes blackish, bill pale grey, toes smoky grey (1). Sexes similar. Could be confused with sympatric race of Common Barn-owl (T. alba affinis), but latter is larger (wing length 290–325 mm versus 196–222 mm in present species (2) ) and has much paler underparts and wing coverts (1). Juvenile similar to adult, but initially brighter.
Systematics History
Subspecies
Distribution
N & E Madagascar.
Habitat
Traditionally linked with undisturbed rainforest at 800–1300 m (3). However, recent studies indicate forest edge, rice paddies and other cultivation important, at least for hunting, and day roosts found in small ravines among palms (4), bananas (Masu sp.) and secondary growth, but also recently in a sinkhole (5); dry deciduous forest (6) also added as a ‘new’ habitat type and overall altitudinal range recorded as sea-level to 2000 m (7). Radio-tagged bird frequented lowland secondary growth and open areas subjected to human disturbance, roosting during day in secondary vegetation, sometimes just 50 m from habitation (4) and 3–5 m (mean 3·7 m) above ground (4). Forages in forest and nearby open areas.
Movement
Apparently sedentary; radio-tagged bird was sedentary over 15 months within range of 210 ha (1), nesting 2 km from original roosting area of a year earlier.
Diet and Foraging
Almost exclusively small native mammals (insectivores and rodents), especially shrewlike tenrecs (Microgale talazaci (4), M. cowani) (8), rice tenrecs (Oryzorictes hova) (8) and tuft-tailed rats (Eliurus webbi, E. minor) (4), in size range 13–72 g; also occasional rats (Rattus ratus) (8), small lemurs (Microcebus rufus) (8), reptiles (Uroplatus sp.) (8) and old report of frogs. In dry deciduous forest diet (studied via pellet analysis over several years) slightly different, though still heavily biased towards native fauna, with frogs (Laliostoma sp., Mantidactylus spp., Aglyptodactylus sp., Boophis sp., Ptychadena madagascariensis, Mantella spp., Anodontohyla sp., Cophyla sp., Stumpffia sp.) (6), a primate (Microcebus tavaratra) (6) and insects (Coleoptera, Dictyoptera, Orthoptera) (6) present in pellets in some years; however, mammals (especially Suncus madagascariensis and Eliurus antsingy, but also Microgale brevicaudata) constituted the greatest proportion of prey items with geckos (Homopholis boivini, Uroplatus fimbriatus, U. henkeli, U. ebenaui, U. sikorae, Paroedura homalorhina, P. stumpffi, P. karstophila, P. oviceps, Geckolepis spp., Hemidactylus spp.) being important in one year (6). No records of predation on chameleons (9). Captive bird was successfully fed beef (!), frogs, rats, cockroaches and grasshoppers (3). There is apparently very little overlap in prey selected by this species and the sympatric race of T. alba on Madagascar (8), with, for example, the latter feeding on bats and birds in dry deciduous forest study mentioned above (6). No information on feeding behaviour; strictly nocturnal, and recorded singly or in pairs.
Sounds and Vocal Behavior
Loud, eerie, hissing screech, “shreeee”, dropping toward end and lasting c. 1·5 seconds (4), similar to that of T. alba but higher-pitched, downward-inflected (1) and more vigorous; also “wok wok wok” or “wac-wac-wac-...” calls, and a single, explosive call or brief resonant alarm.
Breeding
Only one nest described: site c. 23 m above ground in natural tree cavity in isolated Weinmannia 500 m from edge of main forest block; two recently hatched young Sept; natal down white, developing noticeable facial disc at one month; fledged Nov–Dec at ten weeks, and remained in natal area for at least c. 4 months. Might also breed in rock cavities, given that the species is known to roost in them (6).
Conservation Status
VULNERABLE. CITES I. Restricted-range species: present in East Malagasy Wet Forests EBA. Previously listed as Endangered. Current population estimated at fewer than 10,000 mature individuals within overall range of 52,200 km2. Old records from several areas including Sihanaka forest and Masoala Peninsula; sighting in Mar 1973 near Andasibe was first record in wild since 1934; one found in captivity in Aug 1993 at Andapa, in Anjanaharibe Sud Special Reserve, c. 475 km (3) N of known range. Old specimen record comes either from within or close to Analamazaotra Special Reserve (3), while more recently it has been found in Bemanevika New Protected Area (where described as common and four individuals are being radio-tracked), Kalambatritra Special Reserve (extending the species’ known range 500 km southwards) (7), in Ankarana Special Reserve in far N of country (5) and at Tsitongambarika in the SE lowlands. Additional protected areas known to harbour the species include: Mantadia National Park, Marotandrano Special Reserve, Masoala National Park, Montagne d’Ambre National Park, Tsaratanana Strict Reserve and Zahamena National Park. Individual trapped in Oct 1994 in Masoala Peninsula was radio-tagged and monitored until Dec 1995 using radio telemetry; had home range of 210 ha; in Sept 1995 it nested and raised two young, one of which was fitted with a transmitter and observed through Mar 1996, four months after it had fledged. Probably always uncommon within restricted range, much of which is threatened by habitat destruction; true distribution and status, however, possibly clouded by confusion with T. alba, which is widespread and relatively common throughout Madagascar. Although seems able to hunt over degraded habitats, its diet is heavily geared towards indigenous and endemic fauna, which must also be at risk from continued and ongoing habitat degradation (6). Intensive research and conservation urgently required.