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| Subspecies: | Unknown |
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| Est. World Population: | 119000-860000 |
| CITES Status: | NOT LISTED |
| IUCN Status: | Least Concern |
| U.S. ESA Status: | NOT LISTED |
| Body Length: | |
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| Jumping Ability: | (Horizontal) |
| Life Span: | in the Wild |
| Life Span: | in Captivity |
| Sexual Maturity: | (Females) |
| Sexual Maturity: | (Males) |
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Habitat:
Behaviour All populations of this species undergo post-breeding dispersal movements (del Hoyo et al. 1992) and are considerably nomadic (Snow and Perrins 1998). In addition northern breeding populations are fully migratory (del Hoyo et al. 1992) and may travel on a broad front (e.g. across the Sahara) (Brown et al. 1982). Northern and southern breeding populations breed during the local spring, whilst breeding elsewhere coincides with the rains (del Hoyo et al. 1992). The species nests in mixed-species colonies, either in small groups (e.g. 5-100 pairs in Africa) (Brown et al. 1982) or in large aggregations of thousands of pairs, and during the winter or dry seasons the species usually forages in small flocks (Hancock et al. 1992, del Hoyo et al. 1992) of up to 30 indivduals (Brown et al. 1982). It often roosts communally at night in large groups (sometimes thousands of individuals) with other species, occasionally in trees far from wetland feeding sites (Brown et al. 1982). Habitat The species feeds in very shallow water (Hancock et al. 1992) and nests in freshwater or brackish wetlands with tall dense stands of emergent vegetation (e.g. reeds or rushes) and low trees or bushes (Marchant and Higgins 1990, del Hoyo et al. 1992). It shows a preference for marshes at the edges of lakes and rivers (Hancock et al. 1992), as well as lagoons, flood-plains, wet meadows (Marchant and Higgins 1990, del Hoyo et al. 1992), swamps (del Hoyo et al. 1992), reservoirs (Hancock et al. 1992), sewage ponds, rice-fields and irrigated cultivation (Marchant and Higgins 1990, del Hoyo et al. 1992). It less often occurs in coastal locations such as estuaries, deltas, saltmarshes (Hancock et al. 1992) and coastal lagoons (del Hoyo et al. 1992). Roosting sites are often large trees that may be far from water (Brown et al. 1982, del Hoyo et al. 1992). Diet The diet of the species varies seasonally depending on what is available (Hancock et al. 1992). It takes adult and larval insects (e.g. aquatic beetles, dragonflies, grasshoppers, crickets, flies and caddisflies), worms, leeches, molluscs (e.g. snails and mussels), crustaceans (e.g. crabs and crayfish) and occasionally fish, frogs, tadpoles, lizards, small snakes and nestling birds (del Hoyo et al. 1992). Breeding site The nest is a platform of twigs and vegetation usually positioned less than 1 m above water (occasionally up to 7 m) in tall dense stands of emergent vegetation (e.g. reeds or rushes), low trees or bushes over water (del Hoyo et al. 1992).
Conservation:
Conservation Actions Underway
The species is listed on Annex I of the EU Birds Directive, Annex II of the Bern Convention and Annex II of the Convention on Migratory Species, under which it is covered by the African-Eurasian Waterbird Agreement (AEWA).
Conservation Actions Proposed
The following information refers to the species's European range only: Sustainably manage river valleys and wet grasslands; Abandonment of pastoral grassland, afforestation of farmland and drainage of wet meadows and inland wetlands in key breeding areas should be stopped.
The species is listed on Annex I of the EU Birds Directive, Annex II of the Bern Convention and Annex II of the Convention on Migratory Species, under which it is covered by the African-Eurasian Waterbird Agreement (AEWA).
Conservation Actions Proposed
The following information refers to the species's European range only: Sustainably manage river valleys and wet grasslands; Abandonment of pastoral grassland, afforestation of farmland and drainage of wet meadows and inland wetlands in key breeding areas should be stopped.




