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Taxon ID: 12,199 Total records: 39,143

Chlidonias hybrida

Classification

Kingdom Animalia (COL)
Phylum Chordata (COL)
Class Aves (COL)
Order Ciconiiformes (COL)
Family Laridae (COL)

Taxonomy

Genus Chlidonias Reference
SubGenus Vernacular Name
Species hybrida IUCN Threat Status-Year Least Concern, 2012
SubSpecies Nat'l Threat Status-Year Not Evaluated, 2000
Infraspecies Reason for Change
Infraspecies Rank CITES
Taxonomic Group Birds Native Status Native
Scientific Name Author Pallas, 1811 Country Distribution Myanmar
Citation Description Geographic Range [top] Countries occurrence: Native: Afghanistan; Albania; Algeria; Angola (Angola); Armenia (Armenia); Australia; Austria; Azerbaijan; Bahrain; Bangladesh; Belarus; Bosnia and Herzegovina; Botswana; Brunei Darussalam; Bulgaria; Cambodia; Central African Republic; Chad; China; Côte dIvoire; Croatia; Cyprus; Czech Republic; Egypt; Equatorial Guinea; Ethiopia; France; Gambia; Germany; Ghana; Greece; Guam; Guinea; Guinea-Bissau; Hong Kong; Hungary; India; Indonesia; Iran, Islamic Republic of; Iraq; Israel; Italy; Japan; Jordan; Kazakhstan; Kenya; Korea, Republic of; Kuwait; Lao Peoples Democratic Republic; Latvia; Lebanon; Liberia; Libya; Lithuania; Macedonia, the former Yugoslav Republic of; Madagascar; Malawi; Malaysia; Mali; Mauritania; Micronesia, Federated States of ; Moldova; Mongolia; Montenegro; Morocco; Mozambique; Myanmar; Namibia; Nepal; Niger; Nigeria; Northern Mariana Islands; Oman; Pakistan; Palau; Palestinian Territory, Occupied; Papua New Guinea; Philippines; Poland; Portugal; Qatar; Romania; Russian Federation; Saudi Arabia; Senegal; Serbia (Serbia); Sierra Leone; Singapore; Slovakia; Somalia; South Africa; South Sudan; Spain; Sri Lanka; Sudan; Swaziland; Switzerland; Syrian Arab Republic; Taiwan, Province of China; Tajikistan; Tanzania, United Republic of; Thailand; Timor-Leste; Togo; Tunisia; Turkey; Turkmenistan; Uganda; Ukraine; United Arab Emirates; Uzbekistan; Viet Nam; Western Sahara; Yemen; Zambia; Zimbabwe Vagrant: Barbados; Belgium; Burkina Faso; Burundi; Cameroon; Cape Verde; Christmas Island; Congo, The Democratic Republic of the; Denmark; Djibouti; Eritrea; Finland; Gibraltar; Iceland; Ireland; Lesotho; Luxembourg; Maldives; Malta; New Zealand; Norway; Rwanda; Seychelles; Sweden; United Kingdom; United States Continuing decline in area of occupancy (AOO): Unknown Extreme fluctuations in area of occupancy (AOO): No Estimated extent of occurrence (EOO) - km2: 10000000 Continuing decline in extent of occurrence (EOO): Unknown Extreme fluctuations in extent of occurrence (EOO): No Continuing decline in number of locations: Unknown Extreme fluctuations in the number of locations: No Upper elevation limit (metres): 2000 Range Map: Click here to open the map viewer and explore range. Population [top] Population: The global population is estimated to number c.300,000-1,500,000 individuals (Wetlands International 2006), while national population estimates include: c.10,000-100,000 breeding pairs and c.1,000-10,000 individuals on migration in China; c.50-10,000 wintering individuals in Taiwan; < c.1,000 individuals on migration in Korea; c.50-1,000 individuals on migration and < c.50 wintering individuals in Japan and c.100-10,000 breeding pairs and c.50-1,000 individuals on migration in Russia (Brazil 2009). Trend Justification: The overall population trend is fluctuating, although some populations are stable and others have unknown trends (Wetlands International 2006). Current Population Trend: Stable Additional data: ?Continuing decline of mature individuals: Unknown ?Extreme fluctuations: No ?Population severely fragmented: No ?Continuing decline in subpopulations: Unknown ?Extreme fluctuations in subpopulations: No ?All individuals in one subpopulation: No Habitat and Ecology [top] Habitat and Ecology: Behaviour Northern breeding populations of this species are fully migratory whilst tropical breeders are more nomadic or locally dispersive (del Hoyo et al. 1996). The species breeds from May to early-June (Richards 1990) in monospecific colonies of 10-100 pairs (del Hoyo et al. 1996). After breeding it departs for the wintering grounds from late-July to September, returning again between April and May (Richards 1990). The species sometimes forages singly, but is more common in small groups or larger mixed-species flocks on passage and in the winter (Snow and Perrins 1998). Habitat The species utilises a variety of wetland habitats but shows a preference for freshwater marshlands with scattered pools, particularly where the surrounding vegetation is grazed by cattle or horses (Richards 1990). It frequents inland lakes, rivers, marshes, temporary pans (e.g. in Africa), artificial fish-ponds and drainage-ponds covered with water-lilies (e.g. in Italy) (del Hoyo et al. 1996), swamps, river pools, reservoirs, large dams, sewage-ponds, flooded saltmarshes, arable fields (e.g. in Australia) (Higgins and Davies 1996, del Hoyo et al. 1996) and rice-fields (del Hoyo et al. 1996). In Australia the species also occurs along the coast on estuaries, coastal lagoons, creeks in mangrove swamps (Snow and Perrins 1998) and tidal mudflats (del Hoyo et al. 1996). Diet Its diet consists of terrestrial and aquatic insects (del Hoyo et al. 1996) (e.g. Dytiscidae, adult and larval Odonata, Orthoptera, flying ants (del Hoyo et al. 1996) and mosquitoes (Richards 1990)), spiders, frogs, tadpoles, small crabs (del Hoyo et al. 1996), shrimps (Richards 1990) and small fish (del Hoyo et al. 1996). Breeding site The nest is a heap of aquatic vegetation (Richards 1990, del Hoyo et al. 1996) or dry grass (del Hoyo et al. 1996), placed either on floating and emergent vegetation over water 60-80 cm deep or resting on the bottom of very shallow water (del Hoyo et al. 1996). The species nests in colonies, neighbouring pairs spaced between 1 and 5 m apart (del Hoyo et al. 1996), and may forage up to 9 km away from breeding sites (more usually within 1 km) (del Hoyo et al. 1996). Systems: Terrestrial; Freshwater; Marine Continuing decline in area, extent and/or quality of habitat: Unknown Generation Length (years): 9.9 Movement patterns: Full Migrant Congregatory: Congregatory (and dispersive) Threats [top] Major Threat(s): The species suffers nest destruction from the invasive rodent species Myocastor coypus in Italy (Arduin 1997). Utilisation Large numbers of eggs are collected for sale and local consumption in India (this may be causing population declines in some areas) (del Hoyo et al. 1996), and fishermen collect eggs in Ukraine (del Hoyo et al. 1996). Citation: BirdLife International. 2012. Chlidonias hybrida. The IUCN Red List of Threatened Species 2012: e.T22694764A38900337. http://dx.doi.org/10.2305/IUCN.UK.2012-1.RLTS.T22694764A38900337.en. Downloaded on 30 March 2016. Disclaimer: To make use of this information, please check the . 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Additional Info

Synonyms


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Chlidonias hybridus (Pallas, 1811)
Common Names


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Localities


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No Locality records in database.
Species Record Updated By: Carlos Aurelio Callangan