This species has been uplisted to Near Threatened on the basis that increasing human disturbance and dam construction projects are expected to drive a moderately rapid population decline over the next three generations.
Sibley, C. G.; Monroe, B. L. 1990. Distribution and taxonomy of birds of the world. Yale University Press, New Haven, USA.
Distribution and populationSterna aurantia
The BirdLife Taxonomic Working Group is aware that phylogenetic analyses have been published which have proposed generic rearrangements which may affect this species, but prefers to wait until work by other taxonomists reveals how these changes affect the entire groups involved.
occurs across a wide range in southern Asia, being found in Pakistan
and southern China
(Yunnan) (del Hoyo et al
. 1996), with vagrant records from Iran and Afghanistan, although it is generally resident over most of its range. The global population is estimated at between 50,000 and 100,000 individuals (Delaney and Scott 2006). It has reportedly declined in abundance in Thailand, where it is now considered very rare (del Hoyo et al
.1996). The species has also declined in Laos since the early 20th century (Thewlis et al
. 1998), and is very close to being extirpated from the country (W. Duckworth in litt
. 2011). It is said to be declining throughout its range in Cambodia (F. Goes in litt
. 2011), with sharp declines noted in the number of pairs in the largest breeding colony on the Mekong, and the number of breeding locations, during the period 2007-2011 (A. Claassen in litt
. 2011). In view of its historical and recent precipitous decline in Cambodia, the species is said to be heading towards extinction there in 5-10 years if no specific conservation action is carried out (A. Claassen in litt
. 2011). The species is now a rare and very local visitor in Nepal, with a maximum population of 20 individuals estimated in 2011, having rapidly declined since the 1990s (C. Inskipp and H. S. Baral in litt
. 2011). The species is described as uncommon along the Dayingjiang river in south-western Yunnan (Yang Liu in litt
. 2011). In contrast to declines noted in South-East Asia, the species is now more regular in southern India than was once thought, having probably benefitted from the development of reservoirs (Praveen J. in litt
. 2012). Likewise, the species is described as having increased in Andhra Pradesh over the past 10 years (S. Riyazuddin in litt
. 2012).Population justification
The population in India has been estimated to number more than 50,000 individuals, thus the global population is put at 50,000-100,000 individuals (Delany and Scott 2006).Trend justification
Precipitous declines have occurred in parts of South-East Asia, whilst local increases have been noted in India, making the deciphering of past population trends difficult. The species is expected to undergo a moderately rapid reduction over the next three generations, as threats, such as dam construction and disturbance, increase in prevalence.Ecology
It inhabits rivers and freshwater lakes, also occurring rarely on estuaries, and breeds on sandy islands (del Hoyo et al
. 1996). It has been recorded up to 600 m in Nepal. It feeds predominantly on fish, small crustaceans and insects. Breeding occurs mainly in February-May (del Hoyo et al
Nesting areas are vulnerable to flooding, predation and disturbance (del Hoyo et al
. 1996). The negative population trend in Laos is probably due mainly to excessive human disturbance on sandbars (Thewlis et al
. 1998). The multitude of dam construction projects completed, underway or planned in South-East Asia (e.g. along the Mekong river [F. Goes in litt
) may also threaten the species through changes to flow regime and flooding of nest-sites. Its habitat may be threatened by the construction of dams in the Dayingjiang region of south-western Yunnan (Yang Liu in litt
. 2011).Conservation Actions Underway
The species occurs in a number of protected areas.Conservation Actions Proposed
Carry out regular surveys to monitor the population throughout its range. Conduct education activities to help alleviate human pressures on river and lake habitats. Lobby against high-risk dam projects, especially in South-East Asia.
del Hoyo, J.; Elliott, A.; Sargatal, J. 1996. Handbook of the Birds of the World, vol. 3: Hoatzin to Auks. Lynx Edicions, Barcelona, Spain.
Delany, S.; Scott, D. 2006. Waterbird population estimates. Wetlands International, Wageningen, The Netherlands.
Thewlis, R. M.; Timmins, R. J.; Evans, T. D.; Duckworth, J. W. 1998. The conservation status of birds in Laos.
Text account compilers
Butchart, S., Ekstrom, J., Taylor, J.
Baral, H., Claassen, A., Duckworth, W., Goes, F., Inskipp, C., Praveen, J., Riyazuddin, S., Thewlis, R., Yang, L.
IUCN Red List evaluators
Butchart, S., Symes, A.
BirdLife International (2014) Species factsheet: Sterna aurantia. Downloaded from
http://www.birdlife.org on 18/04/2014.
Recommended citation for factsheets for more than one species: BirdLife International (2014) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 18/04/2014.
This information is based upon, and updates, the information published in BirdLife International (2000)
Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004)
Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.
To provide new information to update this factsheet or to correct any errors, please email BirdLife
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