Circus maillardi 

Scope: Global
Language: English

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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Accipitriformes Accipitridae

Scientific Name: Circus maillardi
Species Authority: Verreaux, 1862
Common Name(s):
English Reunion Marsh-harrier, Malagasy Marsh Harrier, Réunion Harrier
Spanish Aguilucho Lagunero Malgache
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, Barcelona, Spain and Cambridge, UK.
Identification information: 54 cm. Large harrier. Male has mainly black head and dark back, contrasting with light grey primaries/secondaries, unbarred tail, and white rump, belly, and underwings. Female and immature dark brown, with barred tail. Whitish rump at all ages. Voice Grating kiay kioo near breeding site, kai pi-pi-pi-pi-pi by male during display flights. Hints Search in forested habitat.

Assessment Information [top]

Red List Category & Criteria: Endangered B1ab(iii);D ver 3.1
Year Published: 2016
Date Assessed: 2016-10-01
Assessor(s): BirdLife International
Reviewer(s): Butchart, S. & Symes, A.
Contributor(s): Bretagnolle, V., Le Corre, M., Safford, R., Grondin, V. & Thiollay, J.
Facilitator/Compiler(s): Ekstrom, J., Pilgrim, J., Stattersfield, A., Symes, A., Taylor, J. & Westrip, J.
This species is classified as Endangered since it has an extremely small population and a very small range, within which habitat continues to be lost and degraded.

Previously published Red List assessments:

Geographic Range [top]

Range Description:Circus maillardi is confined to Réunion (to France). Current population estimates range from less than 100 pairs to 125-130 (Bretagnolle et al. 2000), 130-170 pairs (M. Le Corre in litt. 1999), and 150 confirmed or probable pairs (Grondin & Philippe 2011). A population of around 130 pairs probably equates to a total population close to or exceeding 500 individuals (V. Bretagnolle in litt. 2007, estimated by Grondin & Philippe (2011) at at least 564 individuals. The range appears to have been stable from the late 1970s to the present (Bretagnolle et al. 2000), and numbers were believd to be at least stable and probably increasing as a consequence of protection (Cheke 1987c, M. Le Corre in litt. 2000, V. Bretagnolle in litt. 2007). However, a decrease in population density was observed in some areas between 2000 and 2010, while some areas were occupied in 2010 that were unoccupied in 2000, making the overall trend difficult to determine (Grondin & Philippe 2011). Most suitable habitat is occupied, albeit with varying densities (M. Le Corre in litt. 2000).

Countries occurrence:
Additional data:
Continuing decline in area of occupancy (AOO):Unknown
Extreme fluctuations in area of occupancy (AOO):NoEstimated extent of occurrence (EOO) - km2:2100
Continuing decline in extent of occurrence (EOO):UnknownExtreme fluctuations in extent of occurrence (EOO):No
Number of Locations:1Continuing decline in number of locations:Unknown
Extreme fluctuations in the number of locations:No
Upper elevation limit (metres):1800
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:Population estimates range from fewer than 100 pairs to 125-130 (Bretagnolle et al. 2000), 130-170 pairs (M. Le Corre in litt. 1999), and most recently 564 adults recorded in 2009-2010, including c.150 confirmed or probable pairs, with the total number perhaps higher (Grondin & Philippe 2011) giving a range of 200-560 mature individuals.

Trend Justification:  The range seems to have been stable since the late 1970s (Bretagnolle et al. 2000), and the population was believed to be at least stable (V. Bretagnolle in litt. 2007) and probably increasing following the introduction of protection measures (Cheke 1987c; M. Le Corre in litt. 2000; V. Bretagnolle in litt. 2007). Subsequent surveys found a decrease in population density in some areas between 2000 and 2010, however some areas were occupied in 2010 that were unoccupied in 2000 (Grondin & Philippe 2011). The overall trend is difficult to determine, but the species is suspected to have undergone a slow decline between 2000-2010.
Current Population Trend:Decreasing
Additional data:
Number of mature individuals:200-560Continuing decline of mature individuals:Unknown
Extreme fluctuations:NoPopulation severely fragmented:No
No. of subpopulations:1Continuing decline in subpopulations:Unknown
Extreme fluctuations in subpopulations:NoAll individuals in one subpopulation:Yes
No. of individuals in largest subpopulation:100

Habitat and Ecology [top]

Habitat and Ecology:When breeding, it largely occupies indigenous and degraded forests (Clouet 1978, V. Bretagnolle in litt. 1999, M. Le Corre in litt. 1999) - although rarely tall, dense forest - mostly between 300 and 700 m. It forages in most habitats, but particularly in wooded and forested habitats (65%), as well as cultivated (sugarcane) fields and pastures (20%) and open grasslands and savannas (15%) (Bretagnolle et al. 2000). Its original diet was probably entirely birds and insects, but now c.50% consists of introduced mammals such as rats, mice and tenrec Tenrec ecaudatus (Clouet 1978). Reptiles, particualrly Oriental garden lizard Calotes versicolor, are also commonly taken (V. Grondin in litt. 2012). It will also take carrion. Its fecundity is poor for a member of the Circus genus and is probably related to the lack of natural predators and low benefits of dispersion (Clouet 1978). The nest is built on the ground.

Continuing decline in area, extent and/or quality of habitat:Yes
Generation Length (years):7.8
Movement patterns:Not a Migrant

Threats [top]

Major Threat(s): Poaching (M. Le Corre in litt. 1999) and persecution (it is believed to be a predator of chickens and, formerly at least, was considered a bird of ill omen) (Jakubek et al. 1997) continue, despite protective legislation, and together with secondary poisoning from rodenticides constitute the most serious current threats (Grondin & Philippe 2011). Increasing urbanisation and road construction bring disturbance further into the breeding habitat. Below 1,300 m, cultivation and urbanisation have eliminated native forest from all but the steepest of slopes. Cyclones, heavy rains and fires may possibly degrade remaining habitat (Bretagnolle et al. 2000) that is already increasingly degraded by exotic plants (Macdonald et al. 1991). Other possible threats include agricultural pesticide use, silvicultural management of some forests, collisions with electrical cables and wind turbines, and human hunting pressure on some prey species (e.g. larger birds) (Bretagnolle et al. 2000, Grondin & Philippe 2011).

Conservation Actions [top]

Conservation Actions: Conservation Actions Underway
CITES Appendix II. It has been protected since 1966, with protection strengthened in 1974, leading to an increase in numbers (Cheke 1987c), and is protected by a 1989 Ministerial Decree. Ongoing public awareness campaigns and conservation action aim to stop poaching and to rescue and release poached birds (M. Le Corre in litt. 1999). Between 1997-2009 103 individuals were taken into care, many in a critical condition, of which 43 were successfully released back into the wild (Grondin & Philippe 2011). Advice has been given on minimising secondary poisoning occurring as a result of rodent control. A Species Action Plan was published in 2011 (Grondin & Philippe 2011).

Conservation Actions Proposed
Monitor its population trends. Continue developing public awareness campaigns to stop poaching and persecution. Protect remaining habitat. Ensure that rodent control methods minimise the risk of secondary poisoning (M. Le Corre in litt. 1999, Grondin & Philippe 2011). Develop a strategy to decrease collisions with cables and wind turbines, and improve care of birds brought to SEOR care centre (V. Grondin in litt. 2012).

Citation: BirdLife International. 2016. Circus maillardi. The IUCN Red List of Threatened Species 2016: e.T22728310A94979400. . Downloaded on 16 January 2017.
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