|Scientific Name:||Eutriorchis astur|
|Species Authority:||(Sharpe, 1875)|
|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. Lynx Edicions BirdLife International.|
|Identification information:||66 cm. A medium-sized, secretive forest eagle. Rather dull, pale earth-brown above, with narrow, blackish barring in crown, nape, some ear-coverts, and wider black barring on the tertials, secondaries and primaries. Whitish below with wide irregular dark brown barring. Long tail, barred dark with paler margins to dark bars. Yellow eyes, stout bill but lacking tooth. Long, powerful, yellowish, heavily-scaled legs. Similar spp. Differs from Henst's Goshawk Accipiter henstii by paler earth-brown upperparts combined with horizontal breast-barring, inconspicuous dark bars in upperparts (especially tertials and on head), rather long tail, rather bulging head-shape with slight nape crest, and call. Voice Loud call, a far-carrying and measured wah...wah...wah...wah..., often followed by a lower rugh.|
|Red List Category & Criteria:||Endangered C2a(i) ver 3.1|
|Reviewer(s):||Taylor, J. & Butchart, S.|
|Contributor(s):||Hawkins, F., Réné De Roland, L. & Thorstrom, R.|
|Facilitator/Compiler(s):||Benstead, P., Ekstrom, J., Evans, M., Shutes, S., Starkey, M., Symes, A., Taylor, J.|
This species's known range is considerably larger than once thought, and the use of playback techniques has demonstrated that it is not as rare as previously thought. Nevertheless, the species has a very small population, which is suspected to be undergoing a continuing decline as a result of the increasing destruction and fragmentation of its habitat through deforestation, and for these reasons it is listed as Endangered.
|Previously published Red List assessments:||
Eutriorchis astur is a rare inhabitant of the eastern rainforests of Madagascar from Zahamena in the south to Marojejy in the north, and in the central high plateau at Anjozorobe and Bemanevika (L.-A. Rene de Roland in litt. 2012). Apart from inconclusive reports of its presence in Marojejy Reserve in the 1960s and 1970s, and despite considerable search-effort within its habitat, it was not definitely recorded between 1930 and 1993 (R. Thorstrom and L.-A. Rene de Roland in litt. 2007). Since the clarification of the species's territorial call in 1995, it has been discovered at several new sites. Amongst other localities, it is most commonly observed in Masoala National Park, where at least 16 individuals have been recorded from nine sites (Wilcove 1999) and nesting attempts have been recorded, and at Makira forest (R. Thorstrom and L.-A. Rene de Roland in litt. 2007). The population is almost certainly greater than 250 individuals (F. Hawkins in litt. 2003).
|Continuing decline in area of occupancy (AOO):||Yes|
|Extreme fluctuations in area of occupancy (AOO):||No|
|Estimated extent of occurrence (EOO) - km2:||17300|
|Continuing decline in extent of occurrence (EOO):||Unknown|
|Extreme fluctuations in extent of occurrence (EOO):||No|
|Number of Locations:||11-100|
|Continuing decline in number of locations:||Unknown|
|Extreme fluctuations in the number of locations:||No|
|Upper elevation limit (metres):||1500|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||The population is estimated at 66-1,660 individuals (0.04-1 individuals/km2 x 1,660 km2), but is perhaps best placed in the band 250-999 mature individuals. This equates to 375-1,499 individuals in total, rounded here to 350-1,500 individuals. Hawkins (in litt. 2003) suggests the total population is certainly not less than 250 individuals, and L.-A. Rene de Roland in litt. (2012) suggests 250-650 individuals. Assuming a body mass of 800-1,200 g, data in Newton (1979) suggests a breeding density of c. 0.04-1 birds/km2, however the body mass has since been estimated to average 700 g for males and 800 g for females (L.-A. Rene de Roland in litt. 2012).
Trend Justification: Hawkins in litt (2003) suggests that the population decrease cannot be more than 30% over the past ten years.
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||An elusive and wary denizen of lowland and mid-altitude primary rainforest, it rarely, if ever, ventures beyond the forest edge (Langrand 1990, Morris and Hawkins 1998, Horstrom and Watson 1997). It is known to feed on lizards (chameleons and geckos, which make up 83% of its diet) and frogs (Thorstrom and de Roland 2000). It flies between subcanopy perches, hunting for food on the ground, possibly also taking reptiles in the subcanopy. It is also known to glide over the canopy and use foot-thrusting to flush prey in epiphytes and under leaf litter on the ground (R. Thorstrom and L.-A. Rene de Roland in litt. 2007). Between 1997-2005 a total of five nests were located on the Masoala Peninsula, all of which were placed inside epiphytic ferns, however at Bemanevika New Protected Area nests observed in 2007-2012 were constructed from sticks and placed in a tree fork 20-23 m above ground, with a clutch size of two (Peregrine Fund 1997, L.-A. Rene de Roland in litt. 2012). In one studied nest at Masoala the clutch size was one, incubation 40+ days, nestling period 62 days, and the young dispersed at 15 weeks of age. The species exhibits low productivity, producing one offspring every one or two years (R. Thorstrom and L.-A. Rene de Roland in litt. 2007).
|Continuing decline in area, extent and/or quality of habitat:||Yes|
|Generation Length (years):||12.9|
|Movement patterns:||Not a Migrant|
Its forest habitat is being reduced by extensive clearance for subsistence slash-and-burn agriculture and also commercial logging activities. Other threats include uncontrolled bush fires and poor mining practices. The species dependence on pristine lowland forest makes it particularly susceptible to disturbance. Human persecution may also be a problem in some areas (Thorstrom and Watson 1997). Much of the eastern coastal plain has either already been cleared or is covered by highly degraded forest; remaining habitat is under pressure from the increasing human population (Du Puy and Moat 1996). If present trends continue, the remaining forest, especially at the lower altitudes preferred by this species, will disappear within decades (Du Puy and Moat 1996). It is possible that numbers of Uroplatus geckos, a key prey species, are being reduced by capture for the exotic pet trade, but this has not been confirmed (Eames 2010).
Conservation Actions Underway
CITES Appendix II. The species has been found in several protected areas, including four National Parks, one Strict Reserve, two Special Reserves and one Classified Forest, as well as at 10 of the 30 Important Bird Areas in eastern Madagascar (ZICOMA 1999). It may occur in other protected areas further south. It is the subject of an ongoing research program in the Masoala peninsula (Thorstrom and de Roland 2000). Conservation Actions Proposed
Establish whether it is present in the southern half of the eastern rainforest belt, including Ranomafana and Midongy-South National Parks (ZICOMA 1999). Refine population estimates (ZICOMA 1999). Improve the management and conservation of protected areas in the east coast rainforest belt.
|Citation:||BirdLife International. 2012. Eutriorchis astur. The IUCN Red List of Threatened Species 2012: e.T22695336A38184521. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22695336A38184521.en . Downloaded on 06 October 2015.|
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