EN
Assessment ID
330563
Taxon name
Ardenna carneipes
Uploaded by
National Red List Database
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
Assessment ID
330562
Taxon name
Bulweria fallax
Uploaded by
National Red List Database
Scientific name
Bulweria fallax
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
procellariiformes
Family
procellariidae
Genus
Bulweria
Species
fallax
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The UAE is situated on the edge of the species range, and occurrence and numbers may be somewhat variable as a result. Nevertheless, counts of this species on pelagic bird trips suggest that the non-breeding visiting population of this species may be very small (100-600 mature individuals). This qualifies the species for listing as Endangered under criterion D.
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
Bulweria fallax is a poorly known species of the northwest Indian Ocean, occurring widely offshore in the Arabian Sea and Gulfs of Aden and Oman, where it is often the commonest pelagic seabird (Porter et al. 1996). It occurs commonly east of 58'°E in the Arabian Sea as far as the Maldive Ridge, regularly east to southern India and Sri Lanka, and regularly, albeit at low densities, to the eastern Indian Ocean in the Bay of Bengal and off north-western Australia (Van den Berg et al. 1991, Ryan et al. 2013, Lavers et al. 2014). During the summer monsoon (May-September) it congregates off the Socotra archipelago (Yemen), where a breeding colony of at least c.50 pairs was discovered (Taleb 2002) and where c.3,000 pairs are now estimated to nest locally on mainland cliffs (Al Saghier et al. unpublished), and also off the Hallaniyat Islands (southern Oman), where it may nest (or on the Arabian mainland adjacent) (Gallagher 1985).;Similar sea-cliffs within its range on the coast of Somalia deserve investigation for breeding colonies (PERSGA/GEF 2003). A population of unidentified Bulweria petrels, most likely B. fallax, was discovered around Comoro archipelago (Shirihai et al. 2015), with most birds being in active moult, but not all. These individuals, however, show plumage characteristics that do not match with B. fallax.In recent years, work in UAE waters off the Gulf of Oman has revealed erratic influxes of up to 600 birds in Sept -“ Dec (see Campbell;et al.;2017); the species is either very rare or absent for much of the rest of the year.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
It frequents open sea all-year-round, only approaching land during the breeding season, at dusk and after dark (Taleb 2002, PERSGA/GEF 2003). Its foraging areas are poorly known, but presumably related to highly productive areas of oceanic upwelling (PERSGA/GEF 2003). It flies low, taking food from the surface of sea, probably mainly plankton e.g. fish eggs, ctenophores and polychaete worms (PERSGA/GEF 2003).
Threats listed in assessment
Seabirds, including this species, were formerly exploited for food and medicinal use (at a subsistence level [Al-Saghier et al. 2000]) on the Halaaniyaat islands (Gallagher 1985) and Socotra (Al-Saghier et al. 2000, Porter et al. in prep.), but this practice appears to be discontinued due to the availability of cheap poultry and the danger of climbing the cliffs (Taleb 2002). Non-native predators (e.g. rats Rattus spp. and Feral Cats Felis catus) are probably a limiting factor on the species' breeding population size (Al-Saghier et al. 2000), although their impact on the Socotran subpopulation may have stabilised long ago, given the long period (over 2,000 years) of coexistence. Mortality and ecosystem degradation resulting from marine oil spills are potential threats.
History
It is assessed that in 1996, the national Red List status of this species 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
Assessment ID
330558
Taxon name
Nycticorax nycticorax
Uploaded by
National Red List Database
Scientific name
Nycticorax nycticorax
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
pelecaniformes
Family
ardeidae
Genus
Nycticorax
Species
nycticorax
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a tiny breeding and non-breeding population, both of which are thought to be increasing within the UAE. The breeding population size is low enough that it would trigger listing as Critically Endangered under Criterion D, while the non-breeding population size would trigger a listing as Endangered. Based on the regional criteria, however, the breeding population warrants a regional adjustment due to the likelihood of a rescue effect. The non-breeding population is precautionarily not thought to warrant such a change. The breeding status takes precedence and so the species is listed as Endangered under Criterion D.
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 in autumn, when it is fairly common at freshwater sites throughout the country (Richardson 1990, Pedersen et al. 2017). Some individuals stay in the country over summer (Pedersen et al. 2017). Breeding has been recorded near Dubai City in 1992, 2013 and 2015, but it has been suggested that the species breeds annually (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 inland wetlands including rivers, freshwater and brackish lakes, densely vegetated marshes, reservoirs, irrigation ponds and sewage treatment plants (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). During migration, it may also be found in wadis (Richardson 1990). Its diet in the UAE is not well known; elsewhere it is an opportunistic feeder taking fish, frogs, tadpoles, turtles, snakes, lizards, insects, spiders, crustaceans, molluscs, leeches, small rodents, bats and the eggs and chicks of other bird species (del Hoyo et al. 1992, Kushlan and Hancock 2005). The species is largely crepuscular and nocturnal, but may feed diurnally, especially during the breeding season (del Hoyo et al. 1992). It breeds during mid to late summer; nesting sites may be used in consecutive years (Jennings 2010). There is not much known about its breeding biology in the UAE or in Arabia. Usually, the nest is platform constructed of sticks and vegetation placed 2-50 m above water or on dry ground near water in trees, bushes, reedbeds, on cliff ledges and on the ground in protected sites (del Hoyo et al. 1992, Snow and Perrins 1998, Kushlan and Hancock 2005). The species nests close together in single- and mixed-species colonies (del Hoyo et al. 1992).
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 potentially threatened by a range of threats that operate outside of the country. The species is threatened by wetland drainage and destruction (del Hoyo et al. 1992, Kushlan and Hancock 2005) and by droughts in wintering areas (Hafner and Kushlan 2002). It is highly susceptible to pesticides (del Hoyo et al. 1992, Kwon et al. 2004, Kushlan and Hancock 2005) such as organophosphates, carbamates (Kwon et al. 2004) and DDE (a breakdown product of DDT), which negatively affect hatching success (Kushlan and Hancock 2005). There are also cases of genetic damage to chicks as a result of petroleum contamination (Custer 2000). The species is susceptible to avian influenza (Melville and Shortridge 2006) and Newcastle disease so may be threatened by future outbreaks (Kuiken et al. 2006). It is also persecuted (anti-predation killing) at aquaculture facilities due to its depredation on fish stocks (Kushlan and Hancock 2005), and has suffered declines due to the exploitation of chicks from nesting colonies in the past (del Hoyo et al. 1992).
History
The species first bred in the UAE in 1992. The species would have qualified as CR (D) under its breeding population, but without rescue effect since it was just becoming established. Its successful colonisation of the country is likely related to increases in suitable artificial habitats.
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
Assessment ID
330552
Taxon name
Phaethon aethereus
Uploaded by
National Red List Database
Scientific name
Phaethon aethereus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
phaethontiformes
Family
phaethontidae
Genus
Phaethon
Species
aethereus
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a small breeding population in the UAE, which qualifies it for listing as Endangered under criterion D.The breeding population in Saudi Arabia seems to be in decline, although there is still high potential for immigration from stable breeding populations throughout the Arabian Peninsula (Symes et al. 2015). The species has been retained as Endangered at the national level on a precautionary basis pending confirmation of the status of the breeding population.
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 ranges across the Arabian Gulf and the Gulf of Oman. It rarely visits mainland shores, but breeds on offshore islands in the Arabian Gulf; Qarnyan, Zirku and Arzanah islands (Javed et al. 2008, Pedersen et al. 2017), and nesting is possible on Sir Bu Nair, but this requires confirmation. There is no nesting at present on Sir Bu Nair, although it did occur there in the past. There has been no breeding on Qarnayn in the last two years (2018-2019); however, it has not been possible to visit Zirku and Arzanah islands, and so nesting birds may have moved to these two islands. It is a rare visitor off the east coast, where it was recorded once;near Khor Kalba (Sharjah Emirate) in October 2017 (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 almost entirely pelagic and only comes ashore to breed. It forages solitarily (Jennings. 2010). There is no information available about its diet in the UAE; elsewhere it feeds primarily on small fish, especially flying fish, but will also take squid. Most prey is caught by plunge-diving, but flying-fish are sometimes taken in flight (del Hoyo et al. 1992). It breeds colonially on rocky cliffs or slopes on islands, and only very rarely on the mainland (Aspinall and Porter 2011). There is no nest produced from any materials; instead, one egg is laid directly on the bare sand, stone or rock. In Arabia, the species generally nests in long, natural rock cavities with only one entrance, in caves or under overhangs in areas which are free of vegetation (Jennings 2010). The species's breeding biology in the Arabian Gulf is not well known. Birds return to their breeding sites in October and November, with eggs being recorded between December and June. It has been suggested that late breeding records come from inexperienced, young breeders using low-quality nesting sites (Jennings 2010). Breeding colonies are abandoned after breeding when individuals disperse over large distances; radio-tracking revealed that bird breeding on Qarnyan Island travelled to the Kerala coast of India (Jennings 2010).
Threats listed in assessment
The most pressing threats to this species in UAE are the presence of rats and cats on breeding islands, which cause rapid population declines (see Aspinall 1996). Birds of prey can also have an impact (Environment Agency - Abu Dhabi 2016). The presence of oil companies on Zirku and Arzanah has also led to local declines (Aspinall 1996).
History
Even though islands were in a better condition in 1996, it is thought that the population size would have been similar in 1996. Therefore, it would have received the same Red List status then as it does now.
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
Assessment ID
330544
Taxon name
Clanga clanga
Uploaded by
National Red List Database
Scientific name
Clanga clanga
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
accipitriformes
Family
accipitridae
Genus
Clanga
Species
clanga
Taxonomic notes and synonyms listed
Clanga clanga;(del Hoyo and Collar 2014);was previously placed in the genus Aquila.
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a very small non-breeding population in the UAE, which qualifies it for listing as Endangered. The population is increasing within the UAE. However, on a global scale, the species is listed as Vulnerable, as its small population is in rapid decline. Therefore, breeding populations outside of the country may not have a large rescue effect. Given the global situation, a regional adjustment has not been made and the species is retained as Endangered 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 in the UAE from late September to late April (Pedersen et al. 2017). Part of the population winters along the coast, while another part only passes through the country during migration to and from the breeding grounds, when it also occurs further inland (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
This species is found near coastal wetlands during winter, e.g. in mangroves, on inshore islands, in lagoons and mudflats (Richardson 1990, Aspinall and Porter 2011), it may also occur in agricultural areas (e.g. fodder fields and plantations). On passage, the species also occurs in wetlands further inland, such as marshes, but also near rubbish dumps (Richardson 1990). There is no information available on its diet in the UAE; elsewhere it feeds on unretrieved quarry, small mammals, waterbirds, frogs and snakes, hunting over swamps, wet meadows and over agricultural land(A. Làµhmus in litt. 1999); birds soar to c.100 m high when hunting. It is a migratory species. Birds breeding in central Asia winter in the UAE or migrate further south along the Arabian Peninsula until north-east Africa (del Hoyo et al. 1994). The species arrives at the non-breeding grounds in September and leaves again between February and April (Pedersen et al. 2017). The species migrates on a broad front, tending to pass in singles, twos and threes with the occasional larger group (Ferguson-Lees and Christie 2001). Individuals do not concentrate at bottleneck sites to the extent of many other raptors, such as Lesser Spotted Eagle Clanga pomarina (del Hoyo et al. 1994).
Threats listed in assessment
Within the UAE artificial habitats that favour this species within the UAE may be transient, so monitoring of such habitats will be important. However, as a migratory species, the key threats to Greater Spotted Eagle appear to come from outside of the UAE, and so threats from outside of the country need to be taken into account.;There is strong evidence of hybridisation between this species and Lesser Spotted Eagle Clanga pomarina (Bergmanis et al. 1997, Lohmus and Vali 2001, Dombrovski 2002, Vali et al. 2010). In some European countries mixed pairs can constitute 50% of Greater Spotted Eagle pairs (Maciorowski and Mizera 2010) or even more (Vali 2011). It is unclear whether this represents a new phenomenon or a conservation concern, but C. pomarina is far more numerous than C. clanga in the zone of overlap, and the range of C. pomarina appears to be spreading east, further into the range of C. clanga. Other key threats are habitat destruction and disturbance, also poaching and electrocution can be considered important. Suitable habitat mosaics have been lost as a result of afforestation and wetland drainage. In eastern Europe, agricultural intensification and the abandonment of traditional floodplain management have reduced habitat quality (A. Làµhmus in litt. 1999).;Birds are intolerant of permanent human presence in their territories. Forestry operations are a major cause of disturbance. Shooting, deliberate and accidental poisoning are a threat to this species in several areas across its global range, including Russia, the Mediterranean, South-East Asia and Africa (per;P. D. Round in litt. 1998, P. Mirski in litt. 2012). In Israel, poisoning and electrocution are major causes for casualties of wintering population (Perlman and Granit 2012).
History
This species has increased its population size since 1996 due to increasing availability of suitable irrigated habitat, and it is suspected that the population size may have been sufficiently small in 1996 that it would have warranted a listing as Critically Endangered under criterion D then, whereas now (2019) it is assessed as Endangered.
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
Assessment ID
330542
Taxon name
Circus macrourus
Uploaded by
National Red List Database
Scientific name
Circus macrourus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
accipitriformes
Family
accipitridae
Genus
Circus
Species
macrourus
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a very small non-breeding population in the UAE, which qualifies it for listing as Endangered. On a global scale, the species is listed as Near Threatened due to a moderately rapid population decline. Therefore, breeding populations outside of the country may not have a large rescue effect. The population trend within the country is not known. Given the global situation, the species is retained as Endangered 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 throughout the UAE during passage to and from the breeding grounds. A small population overwinters in the country, when it may occur over large parts of 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
This species is found in open habitat, favouring steppe, grassland, agricultural fields and sandy desert (Aspinall and Porter 2011). The species is migratory, with most birds wintering in sub-Saharan Africa or south-east Asia. Birds occur in the UAE between September and March, occasionally until April, and mainly breed in the steppes of southern Russia (Richardson 1990). Birds migrate on a broad front, with only minor concentrations at bottleneck sites (del Hoyo et al. 1994, Ferguson-Lees and Christie 2001). Although birds are most often seen singly, females and juveniles can form parties of 10-15 individuals on migration (Snow and Perrins 1998, Ferguson-Lees and Christie 2001). Birds fly at c.1-9 m above the ground when hunting (del Hoyo et al. 1994, Snow and Perrins 1998) and fly generally higher on migration, but tend to remain from c.1-15 m above the ground (Brown et al. 1982).
Threats listed in assessment
As a migratory species, the population of Pallid Harrier that visits UAE may be impacted by threats within the country and outside of it. Within its breeding range, the species is primarily threatened by the destruction and degradation of steppe grasslands through conversion to arable land, burning of vegetation, intensive grazing of wet pastures and the clearance of shrubs and tall weeds (Galushin et al. 2003, E. Bragin in litt. 2007). Fires are started by farmers, arsonists and dry thunderstorms(E. Bragin in litt. 2007). Outside of its breeding grounds, the species is thought to be negatively affected by the loss of grassland due to burning, cutting and overgrazing (Galushin;et al.;2003) and by the intensification of agriculture (R. Simmons in litt. 1999, Galushin et al. 2003), although this requires further research; and the latter is not deemed to be a particular threat within the UAE.
History
It is assessed that in 1996, the national Red List status of this species 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
Assessment ID
330524
Taxon name
Dromas ardeola
Uploaded by
National Red List Database
Scientific name
Dromas ardeola
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
dromadidae
Genus
Dromas
Species
ardeola
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
B1ab(iii)+2ab(iii)
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a fairly large breeding population, but a smaller non-breeding population. The breeding population is thought to be increasing, while the non-breeding population is assumed to be declining within the UAE.Nesting occurs on two small islands with a highly restricted extent of occurrence;(EOO) and area of occupancy (AOO). The;breeding population qualifies as Endangered under criterion B, presuming no rescue effect given that populations;within the Arabian Peninsula;are declining (Symes et al. 2015). The non-breeding population may warrant listing as EN under criteria C1+2a(ii). Based on regional criteria, neither of the two populations require a regional adjustment, as the breeding population in the wider Arabian Peninsula is thought to be in decline. The breeding population takes precedence here though, so the species is listed as Endangered under criteria B1ab(iii)+2ab(iii).
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 breeding resident occurring on Umm Amim and Abu Al Abyad islands in the Abu Dhabi Emirate (Environment Agency - Abu Dhabi 2016, Pedersen et al. 2017), although some of the population may disperse in the non-breeding season. About 1,500 breeding pairs have been recorded there in 2012 (Pedersen et al. 2017), but the new colony at Abu Al Abyad has recently seen rapid declines (Environment Agency - Abu Dhabi 2016).
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 zones like mudflats, coral reefs, mangroves and sheltered lagoons, but never occurs inland (Richardson 1990, Aspinall and Porter 2011). Breeding colonies are situated on sandbanks and islets low above the high tide mark or on sandy dunes (Hayman et al. 1986, del Hoyo et al. 1996, Jennings 2010). Outside of the breeding season, the species is found on open mudflats, sometimes in proximity to mangroves (Jennings 2010). During passage, it also occurs along creeks (Richardson 1990). Its diet consists predominantly (> 95%) of crabs and occasionally of small fish (del Hoyo et al. 1996, Jennings 2010). The species forages nocturnally mostly under semi-closed mangroves (Avicennia marina), but occasionally also on open intertidal flats (Jennings 2010). The breeding season starts in May, when nesting tunnels and burrows are excavated in moist sand (Jennings 2010, Aspinall and Porter 2011). These tunnels can be more than 2 m long and lead up to 1 m below the surface (del Hoyo et al. 1996, Jennings 2010). There is no other nesting material used (Jennings 2010). Clutches contain only one egg (Jennings 2010). Chicks hatch by mid-June and fledge in August (Jennings 2010). Juveniles remain with their parents for several months, including on the wintering grounds (Jennings 2010). The migratory movements are poorly understood. Individuals from the breeding colonies on Umm Amim and Abu al-Abyadh islands may disperse after the breeding season locally in response to food availability (Jennings 2010). However, individuals may also migrate southwards between August and November; one satellite-tagged bird from the UAE was found to winter in the Seychelles (Javed et al. 2011), while others may move to the East African coast or the eastern Indian Ocean (Jennings 2010). These individuals return northwards between March and April, although over much of its range the species is present in fluctuating numbers throughout the year (Hayman et al. 1986).
Threats listed in assessment
The species is threatened by future oil spills (Aspinall 1996, del Hoyo et al. 1996, Hockey et al. 2005) and the introduction of nest predators onto breeding islands (del Hoyo et al. 1996, Symes et al. 2015). Rat predation was first observed on Umm Amim;in 2005.;The planting of mangrove stands over bare substrates in some areas may also reduce the availability of nest sites (Hockey et al. 2005), while coastal development could also threaten existing colonies (Aspinall 1996, Symes et al. 2015, Environment Agency - Abu Dhabi 2016).;Eggs and young of the species used to be collected from nesting colonies in the wider Arabian region, a practice which may still occur (Hockey et al. 2005, Symes et al. 2015), while intrusions by people collecting the eggs of other species (e.g. Bridled Tern) can result in nest destruction (Aspinall 1996).
History
The species is considered to have been Endangered in 1996 on the basis of restricted nesting EOO and AOO, with rescue effect uncertain and therefore not applied.
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
Assessment ID
330523
Taxon name
Vanellus leucurus
Uploaded by
National Red List Database
Scientific name
Vanellus leucurus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
charadriidae
Genus
Vanellus
Species
leucurus
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a small breeding and non-breeding population in the UAE, which might qualify it for listing as Critically Endangered as a breeding species and Endangered in winter. However, since the first breed record in 1996, the population has increased within the country and it is stable in the wider Arabian Peninsula; thus, the potential for immigration from outside the UAE remains. Therefore, the species's status has been adjusted down by one category to Endangered as a breeding species and Vulnerable in winter. The breeding season takes precedence here, so it is listed as Endangered.
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 winter visitors and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). These individuals occur in the country mainly between August and April (Pedersen et al. 2017). In the 1990s, a resident breeding population became established in the country, with the first breeding confirmed in Ajman and possibly Sharjah emirates in 1996. These sites have been abandoned since, but since 1999 the species has been regularly breeding near Dubai City (Warsan Lake), and since 2009, east of Abu Dhabi City (Jennings 2010, 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 breeding season, this species inhabits eutrophic freshwater sites like marshes with effluent water input or nearby rubbish dumps, as well as pools with bare mud areas or tall reed beds (Jennings 2010, Aspinall and Porter 2011). During the non-breeding season, it prefers shallow coastal lagoons. During migration, it may be found at any type of freshwater body, including temporary rain pools, sewage lagoons, brackish coastal pools and tidal ponds (Jennings 2010). Its diet consists mainly of insects, but also of worms, molluscs and crustaceans, which it takes from soft mud and in shallow water (del Hoyo et al. 1996, Jennings 2010). At the beginning of the breeding season in February, the species establishes territories in loose colonies (Hayman et al. 1986, del Hoyo et al. 1996, Jennings 2010). The nest is a shallow scrape, lined with small sticks, stones or shells (del Hoyo et al. 1996, Jennings 2010). It is placed in muddy areas or close to bushes near water (del Hoyo et al. 1996, Jennings 2010). Eggs are laid between March and May (Jennings 2010). The species is partially migratory (del Hoyo et al. 1996). The migrant population in the UAE breeds in central Asia from Turkey to Pakistan and moves south during the non-breeding season, with parts of the population migrating further south to the eastern Sahel in Africa (Jennings 2010). Outside of the breeding season, the species occurs singly, in pairs or small groups, with small migratory flocks of 1-6 individuals and wintering flocks of 6-25 individuals (Urban et al. 1986, del Hoyo et al. 1996).
Threats listed in assessment
The loss of wetland habitats in Mesopotamia owing to drainage, and wetland destruction in Iraq (the core breeding and wintering areas) poses a threat to this species (Stroud;et al. 2005). Land-use changes and oil pollution of coastal sites within UAE could have an impact, but the severity of such threats is unknown.
History
The first breeding records was in 1996. The species is not backcast, as it would not have been considered to be regularly breeding or over-wintering (see Porter et al. 1996) in 1996 and would not have been assessed. It would also depend on timing of a “1996' assessment, as if done pre-breeding attempt then it wouldn't have been assessed.
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
Assessment ID
330513
Taxon name
Recurvirostra avosetta
Uploaded by
National Red List Database
Scientific name
Recurvirostra avosetta
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
recurvirostridae
Genus
Recurvirostra
Species
avosetta
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a very small breeding population in the UAE, which might qualify it for listing as Critically Endangered. However, the population is increasing rapidly within the country and is stable in the wider Arabian Peninsula; thus, the potential for immigration from outside the UAE remains very high. Therefore, the species's status has undergone a regional adjustment down one category, classifying it as Endangered.The non-breeding population is also relatively small, and would qualify as Endangered, but it could also rescued by breeding populations from outside the country. Therefore overall, the non-breeding population would be listed as Vulnerable at the national level after a regional adjustment, if the breeding population were not to take precedence for the final Red List status.
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 resident in the area of the Al Wathba Wetland Reserve, where up to eight pairs have been breeding almost annually since 1996 (Pedersen et al. 2017). Moreover, it is an uncommon passage migrant and wintering bird between September and March, with occasional records in other 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
The breeding population is restricted to open, swampy habitats like shallow waste water sites with rich invertebrate life (Jennings 2010). During migration, the species occurs at any kind of wetland on the coast or further inland, while wintering birds are usually found at shallow, sheltered coastal waters like brackish lagoons (Jennings 2010). Densely vegetated wetlands are not suitable as habitat nor as a foraging site (Jennings 2010). There is no information available about its diet in the UAE or in Arabia; elsewhere it feeds on aquatic invertebrates like insects and larvae, but also worms, crustaceans and occasionally fish, which are taken by scything the bill through the water while walking forward (Jennings 2010). The breeding season lasts from April until July (Jennings 2010). The species nests colonially on small islands in low vegetation near shallow water (Jennings 2010, Aspinall and Porter 2011). The nest is usually a scrape, sometimes with a raised rim and lined with plant material, which may be positioned in a variety of sites including on bare sand and dried mud (Johnsgard 1981, del Hoyo et al. 1996, Jennings 2010). Clutches contain three to four, sometimes up to six eggs (Jennings 2010). The species is partly migratory. Individuals wintering in the UAE or passing through the country on migration breed in central Eurasia (Jennings 2010). It is unclear whether the breeding population in Arabia is resident or if it migrates southward after breeding, to be replaced by wintering migrants from northern breeding grounds (Jennings 2010).
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 the species is unknown.Individuals of this species that visit UAE are threatened by a range of threats that operate outside of the country. For instance, the species is threatened in Europe by the pollution of wetlands with polychlorinated biphenyls (PCBs), insecticides, selenium, lead and mercury (del Hoyo et al. 1996).;The species is susceptible to avian botulism (Blaker 1967, Hubalek et al. 2005) and avian influenza (Melville and Shortridge 2006) so may be threatened by future outbreaks of these diseases.
History
There were no breeding records in 1996, and so the genuine change to be looked at here is for the non-breeding population.Wintering (non-breeding) population in 1996 is thought to have been c. 200 individuals, qualifying as EN, downlisted to VU, the same category as the non-breeding population would receive now if the breeding population did not take precedence.
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
Assessment ID
330509
Taxon name
Calidris falcinellus
Uploaded by
National Red List Database
Scientific name
Calidris falcinellus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Calidris
Species
falcinellus
Taxonomic notes and synonyms listed
Calidris falcinellus (del Hoyo and Collar 2014) was previously placed in the genus Limicola.
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2a; C1+2a(i,ii)
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a very small non-breeding population in the UAE, which is undergoing a rapid decline. Moreover, wetland habitats within the UAE are likely to be deteriorating due to land conversion. Therefore, the species could warrant listing as Critically Endangered at the national level. However, given the large and stable global populations, we downlist this assessment to Endangered for the UAE.
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 uncommon along the coast of the UAE (Pedersen et al. 2017). The majority of occurrences are likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). The most important wintering site is at Ras Al Khor Wildlife Sanctuary (J.N. Shah, NRCS,;pers comm. 2019). Numbers peak between July and October and are lowest in May and June (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
This species occurs mainly in coastal mudflats and tidal pools, but also in shallow fresh and brackish water and in wetlands further inland (Richardson 1990, del Hoyo et al. 1996, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere it is omnivorous and feeds mainly on marine nereid worms, small bivalves and snails, crustaceans, insects, as well as the seeds of aquatic plants (del Hoyo et al. 1996, Snow and Perrins 1998). The species is migratory. Birds wintering in the UAE breed in June in wet lowlands of subarctic Scandinavia (Richardson 1990, del Hoyo et al. 1996). Individuals leave the breeding grounds by July, and stop-over in substantial numbers in Sivash (southern Ukraine) and on the Caspian Sea or the Bulgarian seaboard, before arriving in wintering grounds in late July and August (Richardson 1990, del Hoyo et al. 1996). The species migrates singly or in small groups, although during the spring migration flocks of up to several hundred can occur (del Hoyo et al. 1996). The population departs the wintering grounds in spring in April or May (Richardson 1990, del Hoyo et al. 1996).A few non-breeding birds remain at the wintering sites during the summer (del Hoyo et al. 1996, Pedersen et al. 2017).
Threats listed in assessment
Changes in coastal land-use and the possibility of oil pollution could affect this species in UAE, but the severity of these threats towards this species is unknown. It is uncertain the extent to which factors affecting breeding populations (e.g. see BirdLife International 2015) could impact individuals that do pass-through/over-winter in UAE. Climate change is likely to have an effect on this species in the future, including sea level rise.
History
The population would have been at significantly larger in 1996, with counts of; > 500 individuals at Ras Al Khor in the 1990s, and the overall population would have been in excess of 1,000 individuals. Significant declines in habitat area and quality did not commence until after 1996, and the species is assessed as Least Concern in 1996.
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