Please note, this National Red List website contains a subset of data whilst we transition to national focal point driven data uploads. We thank you for your patience with this and welcome national contributors to get in touch to update their national dataset. Terms of Use including citation guidance are found here.

The previous dataset is available via: https://archive.nationalredlist.org/. This site is no longer updated but can help with most enquiries whilst we focus on redevelopment.

NRLD - 330530 | Hydroprogne caspia

Assessment ID
330530
Taxon name
Hydroprogne caspia
(Pallas, 1770)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Hydroprogne caspia
(Pallas, 1770)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
laridae
Genus
Hydroprogne
Species
caspia
Species authority
(Pallas, 1770)
Taxonomic notes and synonyms listed
Hydroprogne caspia (del Hoyo and Collar 2014) was previously placed in the genus Sterna.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Critically Endangered
Abbreviated status
CR
Qualifying criteria (if given)
D
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species has a very small breeding and non-breeding population in the UAE, which qualifies it for listing as Critically Endangered and Endangered respectively. On a global scale, the species is increasing. Therefore, breeding populations outside of the country may have a large rescue effect. The population is stable within the country; however, wetland habitats within the UAE are likely to be deteriorating due to land conversion. Therefore, with the breeding population taking precedence, the species is precautionarily retained as Critically Endangered at the national level.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). It is common during winter along the coast, but has been recorded during all months (Pedersen et al. 2017).It has bred at Khor al Udayd near the border with Qatar (Richardson 1990, Pedersen et al. 2017) and also breeds in small numbers (1-2 pairs) on islands off Sila and most of the western islands, Sir Bu Nair Island in Sharjah, all in small numbers. In total, there are no more than 20 nesting pairs in the UAE.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
This species is mainly coastal, occurring over shallow waters up to 100 m from the shore (Jennings 2010). It frequents open coasts, sheltered lagoons, inshore islands and occasionally inland wetlands (Richardson 1990, Aspinall and Porter 2011). It feeds on fish, which it captures by plunge-diving (Jennings 2010). Elsewhere, it also takes eggs and young of other birds, carrion, aquatic invertebrates, flying insects and earthworms (Flint;et al.;1984, Urban;et al.;1986, del Hoyo;et al.;1996, Shuford and Craig 2002). It is not a highly gregarious species outside of the breeding season, but may aggregate into flocks on passage, and during the winter it may feed in loose congregations;in rich fishing areas or at nightly roost sites (Urban;et al. 1986, del Hoyo;et al.;1996, Snow and Perrins 1998). The species nests either in colonies or as single pairs on flat islands with sparse vegetation, on sandy or shingle beaches, on sand dunes, flat rock surfaces or sheltered reefs (Flint;et al.;1984, Higgins and Davies 1996, del Hoyo;et al.;1996, Snow and Perrins 1998, Jennings 2010). The species is believed to double-brood in the Arabian Gulf; eggs have been recorded between April and July and between September and January (Jennings 2010). The nest is a shallow depression scraped in sandy ground (Jennings 2010). Clutches contain one egg, rarely two (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
Within the UAE, the species is threatened by oil pollution and marine debris (plastics). The population within the UAE is likely to be impacted by the global threats described below, however, the extent to which these threats impact individuals that visit the UAE is uncertain.Globally, human disturbance represents a significant threat to this species. Caspian Tern colonies are especially vulnerable to disturbance during the early courtship and incubation stages, during which human visitation results in the flushing of the whole colony, potentially leading to nest or colony abandonment (Cuthbert and Wires 1999 per Shuford and Craig 2002). The effect of disturbance during research activities has been well quantified, with activities such as ringing and cannon-netting representing a large proportion of the reproductive failure in colonies studied (Shuford and Craig 2002). Disturbance due to recreational activities are less well quantified but likely also significant (Shuford and Craig 2002). Much of the loss of reproductive success due to human disturbance occurs through gull predation of chicks during the few seconds of panic flight in which the eggs and chicks of a nest are left exposed (Shuford and Craig 2002). Historically, overexploitation within parts of its global range has resulted in large population declines through the collection of eggs and adults for food and feathers (Shuford and Craig 2002) - shooting of birds is still thought to occur, but on a much smaller scale than in the past;(Shuford and Craig 2002).
History
As the species was not a regular breeder in 1996, it would not have been assessed then. For an assessment of whether a genuine change has taken place or not, we therefore have used the non-breeding population, It is assessed that in 1996, the national Red List status of this species's non-breeding population would have been the same as in this assessment.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates