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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
Assessment ID
330565
Taxon name
Puffinus persicus
Hume, 1873
Uploaded by
National Red List Database
Scientific name
Puffinus persicus
Hume, 1873
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
procellariiformes
Family
procellariidae
Genus
Puffinus
Species
persicus
Species authority
Hume, 1873
Taxonomic notes and synonyms listed
Puffinus lherminieri (incorporating baroli), P. bannermani, P. persicus, P. subalaris and P. bailloni (del Hoyo and Collar 2014) were previously lumped as P. lherminieri and baroli was subsumed under P. assimilis, following Brooke (2004), before which P. bannermani and P. persicus where split following Sibley and Monroe (1990, 1993).
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
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The non-breeding population size is extremely large. The population trend is not known, but it is not believed to be decreasing sufficiently rapidly to approach the threshold for listing as threatened under the population trend criterion. For these reasons the species is evaluated as Least Concern at the national level.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is fairly common to common off the east coast of the UAE, but is only rarely observed along the west coast and in the Arabian Gulf. It occurs in UAE waters throughout the year. The largest groups were recorded off the coast of Khor Kalba (Sharjah Emirate), with 3,000 individuals counted in April 2011 and over 4,200 individuals in May 2013 (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species is marine; it occurs in offshore waters, but also closer to the shore near breeding colonies (Aspinall and Porter 2011, del Hoyo et al. 2019). Its diet consists of fish, squid and crustaceans, which are caught by plunge-diving, pursuits and surface-seizing (del Hoyo et al. 2019). It breeds on cliffs and slopes on barely vegetated, rocky offshore islands. There is not much known about its breeding biology; it presumably breeds during summer. While adult individuals are thought to be largely sedentary, immature birds disperse into the Gulf of Oman and occasionally into the Arabian Gulf (del Hoyo et al. 2019).
Threats listed in assessment
The main threat to this species likely occur outside of UAE waters - globally, population size has been historically limited by humans taking chicks for food, a practice which continues on a local basis today at breeding sites. Little is known about the level of impact, but;caution should be exerted since the cause for the overall global decline in this species is unknown (Brooke 2004).
History
The species was first recorded in the early 1990s (907 birds off Ras Dibba). The species is considered to also have been Least Concern in 1996.
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
Assessment ID
330555
Taxon name
Ardea cinerea
Linnaeus, 1758
Uploaded by
National Red List Database
Scientific name
Ardea cinerea
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
pelecaniformes
Family
ardeidae
Genus
Ardea
Species
cinerea
Species authority
Linnaeus, 1758
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
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a moderately sized non-breeding population in the UAE, which qualifies it for listing as Vulnerable. The population is increasing within the region, with the breeding population in the wider Arabian Peninsula stable or increasing; therefore, any breeding population outside of the region will likely have a large rescue effect. Therefore, the species is downlisted by two categories to Least Concern at the national level.
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.
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). Numbers are highest between late July and May, when the species is very common at coastal wetlands, e.g. at Khor Dubai (Richardson 1990, Pedersen et al. 2017). Some non-breeding individuals may stay in the country over summer (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species inhabits any kind of wetland, from open, sandy coasts and lagoons to sheltered creeks, ponds, lakes, reservoirs, sewage treatment plants and ornamental ponds in cities (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). It is an opportunistic feeder; it takes predominantly fish, but also insects, reptiles and small birds (Jennings 2010). It occasionally establishes feeding territories, where it hunts by stalking or standing still to wait for prey (Jennings 2010). It feeds at any time of the day or at night, but is most active at dawn or dusk, typically roosting communally or solitary during the middle of the day and at night (Brown et al. 1982, Kushlan and Hancock 2005). The species is migratory. Individuals wintering in or migrating through the UAE breed during spring in Siberia, where they may form large colonies (Kushlan and Hancock 2005, Jennings 2010). Most migratory movements occur nocturnally in small parties or larger flocks of 200 to 250 individuals (Brown et al. 1982).
Threats listed in assessment
The most relevant threats to this species within UAE are potentially from wetland land-use changes and possibly oil pollution at coastal sites, although the severity of these threats is essentially unknown.;Individuals that visit UAE may also be impacted upon by other threats outside of the country. In Europe, the species was heavily persecuted in the nineteenth century due to its consumption of fish, which resulted in competition with fishermen and fish farmers (Kushlan and Hancock 2005). Although killing at aquaculture farms has not reduced the global population so far (possibly because it is mostly young birds being killed) (Kushlan and Hancock 2005), large numbers have been killed (Carss 1994, Kushlan and Hancock 2005). Timber harvesting is a threat throughout much of the species's range by removing trees used by nesting colonies and/or disturbing nearby colonies (Kushlan and Hancock 2005). The species is also susceptible to avian influenza (Melville and Shortridge 2006) and avian botulism (van Heerden 1974), so may be threatened by future outbreaks of these diseases.
History
The population would have been a little smaller but still moderately sized, sufficient to qualify as Vulnerable, adjusted down by two categories to LC.
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
Assessment ID
330537
Taxon name
Onychoprion anaethetus
(Scopoli, 1786)
Uploaded by
National Red List Database
Scientific name
Onychoprion anaethetus
(Scopoli, 1786)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
laridae
Genus
Onychoprion
Species
anaethetus
Species authority
(Scopoli, 1786)
Taxonomic notes and synonyms listed
Onychoprion anaethetus (del Hoyo and Collar 2014) was previously placed in the genus Sterna.
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
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a very large, stable breeding population in the UAE. Therefore, it is listed as Least Concern here.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The species is a common breeding visitor along the southwestern coast of the UAE and on the islands in the Arabian Gulf (Jennings 2010, Pedersen et al. 2017). The population is supplemented by migrant individuals on passage to and from the breeding ground (Pedersen et al. 2017). It is most common between late March and mid-November, and uncommon to rare between December and February (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species is very rarely observed in coastal waters (Jennings 2010, Aspinall and Porter 2011). At sea, it is often associated with patches of macroalgae (e.g. Sargassum spp.) or flotsam which it uses for perching (del Hoyo et al. 1996, Haney et al. 1999, Jennings 2010). Its diet consists predominantly of squid and surface-schooling fish less than 6 cm long as well as crustaceans and occasionally aquatic insects or molluscs (del Hoyo et al. 1996, Higgins and Davies 1996, Jennings 2010). During the breeding season from April to July, the species forms colonies on rocky or sandy islands and on the mainland coast, where enough low vegetation is present (Jennings 2010, Aspinall and Porter 2011). When nesting, the species often associates with nesting White-cheeked Tern Sterna repressa or Lesser Crested Tern Thalasseus bengalensis (Jennings 2010). One single egg is laid directly on the ground, in a small scrape or depression in shingle or sand (Higgins and Davies 1996, Jennings 2010). Nests are placed in concealed locations and always in the shade, like under a bush, in a rock crevice or on a ledge (Jennings 2010). The species is migratory and dispersive; it abandons its breeding site at the end of the breeding season to overwinter at sea (Higgins and Davies 1996, Haney et al. 1999). Its detailed migratory movements are largely unknown however (del Hoyo et al. 1996), but it is assumed that the Arabian population winters in the Indian Ocean east of Africa (Jennings 2010). Away from the breeding grounds, the species is entirely pelagic (del Hoyo et al. 1996, Haney et al. 1999).
Threats listed in assessment
Aspinall (1996) identifies the main threats to the species within the UAE as egg collecting, introduced mammals (such as cats), land development, disturbance, oil pollution and nest site competition from feral pigeons. Changes in habitat structure have also been thought to affect nesting (Environment Agency - Abu Dhabi 2016).
History
It is considered that in 1996, the national Red List status of this species would have been the same as in this assessment.
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
Assessment ID
330534
Taxon name
Sterna hirundo
Linnaeus, 1758
Uploaded by
National Red List Database
Scientific name
Sterna hirundo
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
laridae
Genus
Sterna
Species
hirundo
Species authority
Linnaeus, 1758
Taxonomic notes and synonyms listed
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.
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
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a small non-breeding population in the UAE, which might qualify it for listing as Near Threatened. However, the population is increasing rapidly within the country. Moreover, in the wider Arabian Peninsula, the species is stable. Therefore, breeding populations outside of the country may have a large rescue effect. Therefore, the species has undergone a regional adjustment and is listed as Least Concern at the national level.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The majority of occurrences of this species are likely to be of wintering birds and of migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers are highest during passage between August and September and between February and May, when it is very common at coastal and inland waters (Richardson 1990, Aspinall and Porter 2011, Pedersen et al. 2017). The species is common in winter, but has been recorded during all months (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species is found along the coast and in inland wetlands (Aspinall and Porter 2011). It winters on sheltered coastal waters, estuaries and along large rivers, occupying harbours, jetties, piers, beaches and coastal wetlands including lagoons, rivers, lakes, swamps and saltworks, mangroves and saltmarshes (del Hoyo et al. 1996, Higgins and Davies 1996). During this season, it roosts on unvegetated sandy beaches, shores of estuaries or lagoons, sandbars and rocky shores (Higgins and Davies 1996). There is no information available about its diet in the UAE; elsewhere the species is opportunistic, its diet consisting predominantly of small fish and occasionally planktonic crustaceans and insects (del Hoyo et al. 1996). It forages in flocks over freshwater as well as marine habitats, and often follows predatory fish, waiting for panicking baitfish to surface. It is gregarious throughout the year (Snow and Perrins 1998). The species is strongly migratory (del Hoyo et al. 1996, Snow and Perrins 1998). It breeds between April and June in solitary pairs or colonially in groups (of up to several thousand pairs in central Asia) (del Hoyo et al. 1996). Individuals migrate south after breeding between August and October, returning to the breeding grounds in March or April (del Hoyo et al. 1996).
Threats listed in assessment
Globally, during the breeding season, the species is vulnerable to human disturbance at nesting colonies (Buckley and Buckley 1984, Blokpoel and Scharf 1991), with sources of disturbance including off-road vehicles, recreation, motor-boats, personal watercraft and dogs (van Halewyn and Norton 1984, Hyde 1997, Burger 1998, Gochfeld et al. 2018). The flooding of nest sites as a result of naturally fluctuating water levels can also result in complete breeding failure of the affected colony (Buckley and Buckley 1984, Hyde 1997, Gochfeld et al. 2018). Previously, this species has experienced significant declines due to egg collecting, hunting and the millinery trade (Gochfeld et al. 2018). Although in most places populations have recovered, hunting remains a significant problem in some areas (Gochfeld et al. 2018). However, the extent to which all of these threats impact individuals that visit the UAE is uncertain. Within the UAE, an additional threat to the species comes from oil pollution.
History
Although there are few records from the 1996 period, it is considered likely to have been LC in 1996.
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
Assessment ID
330531
Taxon name
Thalasseus bengalensis
(Lesson, 1831)
Uploaded by
National Red List Database
Scientific name
Thalasseus bengalensis
(Lesson, 1831)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
laridae
Genus
Thalasseus
Species
bengalensis
Species authority
(Lesson, 1831)
Taxonomic notes and synonyms listed
Thalasseus bengalensis (del Hoyo and Collar 2014) was previously placed in the genus Sterna.
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
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a very large breeding population in the UAE, which is increasing rapidly. Therefore, the species is listed as Least Concern at the national level.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
During the breeding season from April to September, this species is common on islands in the Arabian Gulf, particularly Qarnayn Island (Richardson 1990, Jennings 2010, Pedersen et al. 2017). Additionally, the species is a very common passage migrant and wintering bird in the coastal areas of the country (Aspinall and Porter 2011, Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species inhabits coastal waters (Aspinall and Porter 2011). It is gregarious throughout the year, foraging in single- or mixed-species flocks up to 400 individuals (del Hoyo et al. 1996, Snow and Perrins 1998). It forages in the surf and offshore waters by plunge-diving or surface-dipping (del Hoyo et al. 1996, Snow and Perrins 1998, Jennings 2010). Its diet consists predominantly of small pelagic fish, but it may also take crustaceans such as prawns and shrimps (Urban et al. 1986, del Hoyo et al. 1996, Jennings 2010). During the breeding season, it establishes large, densely packed colonies on sandy patches on islands up to 200 m from the coast (Jennings 2010, Aspinall and Porter 2011). Colony locations are often protected by low vegetation and shrubs from predators, e.g. introduced cats and dogs, mice or Sooty Gull Larus hemprichii (Jennings 2010). The breeding season lasts from early May to July (Jennings 2010). The nest is a shallow scrape in the sand, which may gradually get deeper during incubation (Jennings 2010). Clutches contain one egg (Jennings 2010). After the breeding season, the species disperses out into the Indian Ocean; the details of its movement are poorly known (del Hoyo et al. 1996, Jennings 2010).
Threats listed in assessment
Aspinall (1996) identifies the key threats to this species as egg collecting, invasive mammals, development, disturbance and pollution (e.g. from oil). The severity of these threats, however, is uncertain.
History
The 1996 population is assumed to have been lower but still large, and Least Concern.
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
Assessment ID
330529
Taxon name
Larus genei
Brème, 1839
Uploaded by
National Red List Database
Scientific name
Larus genei
Brème, 1839
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
laridae
Genus
Larus
Species
genei
Species authority
Brème, 1839
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
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a large non-breeding population in the UAE, which is stable at high numbers. Therefore, it is listed as Least Concern at the national level.
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.
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 migrant individuals on passage to and from the breeding ground or winter visitors (Pedersen et al. 2017). The species is particularly common between April and November along the coast (Richardson 1990). Individual birds may also occur during summer in the country (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
During the non-breeding season, this species is almost entirely coastal, frequenting shallow inshore waters and mudflats further inland (del Hoyo et al. 1996, Aspinall and Porter 2011). It forages in shallow water close to the shore and on sandy beaches, but also inland in flooded saltflats (Jennings 2010). It mainly feeds on small fish and marine invertebrates, which it takes by plunge-diving, surface-dipping or by wading in shallow pools (Jennings 2010). Individuals may oversummer in the UAE; however, they do not breed there. Instead, migratory populations breed in central Asia (Jennings 2010)
Threats listed in assessment
In UAE the most relevant threats are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown.Globally, the species considered to be threatened by pollution from oil (Cooper;et al.;1984, James 1984, del Hoyo;et al;1996), and there are a range of other factors that could impact individuals that visit UAE. These include disturbance caused by local people and tourists casually visiting breeding colonies, and by habitat loss resulting from tourism development (James 1984). The species is also susceptible to avian influenza, so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006, Gaidet;et al.;2007).
History
The species is considered to have had large and stable;numbers in 1996, and so it would have received the same national Red List category as it does now.
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
Assessment ID
330528
Taxon name
Larus ridibundus
Linnaeus, 1766
Uploaded by
National Red List Database
Scientific name
Larus ridibundus
Linnaeus, 1766
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
laridae
Genus
Larus
Species
ridibundus
Species authority
Linnaeus, 1766
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
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a large non-breeding population in the UAE, which is stable at very high numbers. Therefore, it is listed as Least Concern at the national level.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE is likely to be of wintering birds and of migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). The species is very common throughout the country between late November and early March (Richardson 1990, Pedersen et al. 2017). Individuals may stay during summer, but do not breed (Richardson 1990, Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
During the non-breeding season, this species is most common in coastal habitats and tidal inshore waters, showing a preference for inlets or estuaries with sandy or muddy beaches, and generally avoiding rocky or exposed coastlines (del Hoyo et al. 1996, Snow and Perrins 1998, Aspinall and Porter 2011). It may also occur inland during this season, frequenting ploughed fields, moist grasslands, urban parks, sewage treatment plants, refuse tips, reservoirs, ponds and ornamental waters, and roosts on sandy and gravel sites or on inland reservoirs (Richards 1990, Snow and Perrins 1998, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere, it feeds predominantly of aquatic and terrestrial insects, earthworms and marine invertebrates, although it may also take fish, rodents and agricultural grain (Flint et al. 1984, del Hoyo et al. 1996). The species generally remains gregarious throughout the year and may roost in large flocks during the winter (Richards 1990). The species breeds between April and May in Eurasia, where it forms dense colonies of up to several thousand pairs (del Hoyo et al. 1996, Snow and Perrins 1998). ;
Threats listed in assessment
The most relevant threat within UAE is the possibility of oil pollution (a threat also highlighted at the global level [Gorski et al. 1977]), but the severity of this threats towards this species is unknown.Individuals of this species that visit UAE are also threatened by a range of threats that operate outside of the country. The species is susceptible to avian influenza (Melville and Shortridge 2006) and avian botulism so may be threatened by future outbreaks of these diseases (Hubalek et al. 2005). It;has suffered local population declines in the past as a result of egg collecting (del Hoyo et al. 1996). In some areas of its breeding range the species may also suffer from reduced reproductive successes due to contamination with chemical pollutants (del Hoyo et al. 1996). None of these, however, are thought to be significant threats to the global population.
History
In 1996, populations will have been lower (no garbage dumps), but the species would still have been assessed as Least Concern.
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
Assessment ID
330526
Taxon name
Larus fuscus
Linnaeus, 1758
Uploaded by
National Red List Database
Scientific name
Larus fuscus
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
laridae
Genus
Larus
Species
fuscus
Species authority
Linnaeus, 1758
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
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a large non-breeding population in the UAE. Therefore, it is listed as Least Concern at the national level.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs during passage and winter along the coast of the UAE (Pedersen et al. 2017). The majority of the population is observed during September/October and February to April (Pedersen et al. 2017). Since 1993, single individuals or small groups have been recorded in Abu Dhabi (Al Sila'a, Al Dabb'iya Peninsula, Abu Dhabi City, Al Wathba Wetland Reserve, Al Futaisi Island, Ghantoot, Zakher Lake), Sharjah (Sharjah City, Khor Kalba), Fujairah (Fujairah City) and Dubai (Dubai City) emirates (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species's ecology and habitat requirements in the UAE are not well known; thus the following information refers to its global distribution range during the non-breeding season. The species inhabits inshore and offshore seas and islands, as well as lagoons, estuaries and harbours (Richardson 1990, Snow and Perrins 1998). Less frequently, it may also occur in inland habitats, such as large lakes and rivers (Urban;et al. 1986, Richardson 1990, Snow and Perrins 1998). It is often seen foraging in large flocks on arable land, pasture land, and on refuse dumps (Richards 1990, del Hoyo et al. 1996). The species is an omnivorous, opportunistic feeder that forages extensively at sea. Its diet consists of small fish, aquatic and terrestrial invertebrates, bird eggs and nestlings, carrion, offal, rodents, berries;and grain (Urban et al. 1986, del Hoyo;et al.;1996, BirdLife International 2000, Olsen and Larsson 2003). It often follows fishing fleets, feeding on discarded bycatch (BirdLife International 2000). Outside of the breeding season, the species is gregarious. The species is migratory and travels with many stopovers from its wintering grounds to the breeding grounds in northern Eurasia (del Hoyo;et al.;1996, Olsen and Larsson 2003). It breeds colonially, often with other gull species, in colonies ranging in size from a few pairs to several tens of thousands (Richards 1990, Snow and Perrins 1998,;Mitchell;et al.;2004).
Threats listed in assessment
The most relevant threats within UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown. Individuals of this species that visit UAE are also threatened by a range of threats that operate outside of the country: Declines in the most northerly breeding subspecies;L. f. fuscus;(a rare passage migrant to UAE; Pedersen et al. 2017) have been attributed in part to the high level of DDE residues accumulated during the non-breeding season, when this subspecies is found further south than the rest of the species (Bustnes 2006, Burger et al. 2018). High levels of PCBs have also been recorded with the potential to lead to mortality in chicks (Hario et al. 2000). Lesser Black-backed Gulls are also persecuted in some areas of its range, which may lead to displacement or even local declines. The species is susceptible to avian botulism, so may be threatened by future outbreaks of this disease (Mitchell;et al.;2004).
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
Assessment ID
330521
Taxon name
Vanellus indicus
(Boddaert, 1783)
Uploaded by
National Red List Database
Scientific name
Vanellus indicus
(Boddaert, 1783)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
charadriidae
Genus
Vanellus
Species
indicus
Species authority
(Boddaert, 1783)
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
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a small resident population in the UAE, which might qualify it for listing as Near Threatened. However, the population is increasing rapidly within the country and in the wider Arabian Peninsula; thus, the potential for immigration from outside the UAE remains very high. Therefore, the species's status has been adjusted down one category and it is listed as Least Concern at the national level.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is a very common breeding resident in the UAE (Pedersen et al. 2017). While until the 1970s, a few breeding pairs were restricted to the northern part of the country (Ras al-Khaimah Emirate), the species has since increased rapidly and spread its range southward to the wetlands near Abu Dhabi City, where it is now a regular breeder (Jennings 2010, Pedersen et al. 2017). In winter individuals occur outside of the breeding range, including western Abu Dhabi Emirate and Das Island (Jennings 2010).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species inhabits open country inland, usually near waterbodies (Jennings 2010, Aspinall and Porter 2011). It is found close to pools of fresh or brackish water, like ditches, water treatment plants, sewage dumps, reservoirs, pits, pools, wet wadis, as well as newly formed and temporary waterbodies (Richardson 1990, Jennings 2010). It also frequents irrigated land, agricultural areas and grass or meadows, including large gardens, golf courses and camel race tracks (Jennings 2010, Aspinall and Porter 2011). There is no information available about its diet in the UAE or Arabia; elsewhere it takes beetles and other insects, as well as molluscs, worms and crustaceans. It mainly forages around dusk and dawn and at night (Jennings 2010). The breeding period starts in February, with most clutches reported between April and May. The species is territorial. Even though it may nest in groups at the same site, it is not colonial (Jennings 2010). The nest is a shallow scrape, unlined or lined with small stones and debris, usually situated near water. Clutches contain usually four eggs; however, as eggs and chicks suffer high mortality, possibly due to predation by House Crow Corvus splendens, mostly only one or two chicks fledge (Jennings 2010).
Threats listed in assessment
Within the UAE the only factor that was deemed a potential threat to this species by Aspinall (1996) is from the infilling of wetland sites.
History
In 1996, the breeding population was 200 mature individuals (Aspinall 1996) which qualifies the species as Endangered. Although the species was not breeding elsewhere in the Arabian Peninsula at the time, the species was expanding and colonising from southwest Asia, and a regional adjustment of one category is made, to Vulnerable. The species is now listed as Least Concern, with the improvement in status being the result of natural colonization and range expansion, probably due to increased availability of suitable habitat.
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