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EN

Assessment ID
330524
Taxon name
Dromas ardeola
Paykull, 1805
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Dromas ardeola
Paykull, 1805
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
dromadidae
Genus
Dromas
Species
ardeola
Species authority
Paykull, 1805
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
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).
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
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
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
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 and conservation measures listed
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
(Lichtenstein, 1823)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Vanellus leucurus
(Lichtenstein, 1823)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
charadriidae
Genus
Vanellus
Species
leucurus
Species authority
(Lichtenstein, 1823)
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
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.
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 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
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
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 and conservation measures listed
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
Linnaeus, 1758
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Recurvirostra avosetta
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
recurvirostridae
Genus
Recurvirostra
Species
avosetta
Species authority
Linnaeus, 1758
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
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.
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
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
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
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 and conservation measures listed
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
(Pontoppidan, 1763)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Calidris falcinellus
(Pontoppidan, 1763)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Calidris
Species
falcinellus
Species authority
(Pontoppidan, 1763)
Taxonomic notes and synonyms listed
Calidris falcinellus (del Hoyo and Collar 2014) was previously placed in the genus Limicola.
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
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.
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
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
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
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 and conservation measures listed
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
Assessment ID
330501
Taxon name
Actitis hypoleucos
Linnaeus, 1758
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Actitis hypoleucos
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Actitis
Species
hypoleucos
Species authority
Linnaeus, 1758
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
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 in decline and breeding populations outside of the country may not have a large rescue effect. Therefore, the species is precautionarily retained as 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 of migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers are highest between late July and early May, when the species may be found on any freshwater wetland in the country, but individuals are recorded through the summer months as well (Richardson 1990, Pedersen et al. 2017).
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 occurs on the edges of freshwater wetlands, mostly at ponds, water treatment plants and in irrigated grassland (Richardson 1990, Aspinall and Porter 2011). It is rarely found in saline habitats like mudflats and only sometimes on shorelines and rocky coasts (Richardson 1990). There is no information available about its diet in the UAE; elsewhere it consists of adult and larval insects, spiders, molluscs, snails, crustaceans, annelids, and occasionally frogs, toads, tadpoles and small fish, as well as plant material (Urban et al. 1986, del Hoyo et al. 1996). It forages solitarily during the day (Richardson 1990, del Hoyo et al. 1996), but may aggregate at night into roosts of over 100 individuals (Johnsgard 1981, del Hoyo et al. 1996). The species is migratory (del Hoyo et al. 1996). It breeds between May and June on freshwater margins throughout Eurasia (del Hoyo et al. 1996, Snow and Perrins 1998). Immature individuals may also remain in the winter range throughout the summer breeding season (Snow and Perrins 1998, Pedersen et al. 2017).
Threats and conservation measures listed
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.
History
The population is thought to have been similar in 1996; significant impacts from development had not yet commenced, whilst wetland creation had also not started in a large way.
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
330492
Taxon name
Pterocles lichtensteinii
Temminck, 1825
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Pterocles lichtensteinii
Temminck, 1825
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
pterocliformes
Family
pteroclidae
Genus
Pterocles
Species
lichtensteinii
Species authority
Temminck, 1825
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species potentially has a very small resident population within the UAE, and is suspected to be declining. Therefore, it is listed here as Endangered.
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
This species is a fairly common resident in the mountains in the northern part of the UAE (Jennings 2010, Pedersen et al. 2017).
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 inhabits rocky, arid mountain hillsides, wadis, gravel plains and deserts, often interspersed with acacia (Jennings 2010, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere it takes seeds mainly of acacia, but also of Indigofera, Asphodelus, Salsola and Cassia bushes (Jennings 2010). Shortly before sunrise and after sunset, the species gathers in small groups of 10 to 15 birds at water sources (Jennings 2010). The species is probably more active during the night than during the day, when it retreats to shady places, e.g. under an acacia bush (Jennings 2010). It is well camouflaged and only flushes late, responding to disturbance with short-distance flights to hide behind some nearby vegetation or rock (Jennings 2010). It is likely that the species is generally not a good flier and only travels short distances to water sources (Jennings 2010). Pairs are regularly observed during January to October, with a peak between February and May (Jennings 2010). Egg-laying starts in February, and chicks are observed between March and August (Jennings 2010). The nest is scraped in stony or gravelly ground and unlined, and is sometimes placed next to a rock or bush (Jennings 2010). Both parents incubate the eggs and raise the young; families stick together until the chicks are fully grown (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
Its crepuscular/nocturnal habits mean it is likely not greatly threatened by human activity (Symes et al. 2015). However, given the suspected population declines there must be an unknown threat having an impact on the UAE population, unless the population has moved out of the country. Potential threats include development of montane areas, reduced water availability in some areas with fewer small ponds in montane areas, and the presence of feral dogs (e.g. at Jebel Hafeet).
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
330491
Taxon name
Pterocles exustus
Temminck, 1825
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Pterocles exustus
Temminck, 1825
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
pterocliformes
Family
pteroclidae
Genus
Pterocles
Species
exustus
Species authority
Temminck, 1825
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species potentially has a very small resident population within the UAE. It is difficult to assess the population trend, because the population can fluctuate considerably between years. But at the very least the species qualifies for listing as Endangered under Criterion D.
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
This species is a common resident particularly in the northern part of the country and along the coast, as well as on islands close to the mainland (Jennings 2010, Pedersen et al. 2017). In winter, the species undertakes seasonal movements (Jennings 2010).
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 occurs in lowland plains, preferably in sandy, but also in gravelly or bare country and scrubland (Jennings 2010, Aspinall and Porter 2011). It also frequents coastal dunes, beaches and inshore islands (Aspinall and Porter 2011). Even though it inhabits mostly arid zones, it needs daily access to water, for which it may fly more than 30 km one way (Jennings 2010). There is no information available on its diet in the UAE; elsewhere in Arabia and Africa it takes seeds, spilt grain, plant shoots and insects (Jennings 2010). The species is undergoing seasonal feeding movements, which are most likely triggered by food shortage in the area (Jennings 2010). The species breeds opportunistically when conditions are favourable and rainfall has been sufficient. Consequently, it may breed year-round, though most breeding activity has been recorded in April and May (Jennings 2010). The nest is scraped in the sand or gravel, often unshaded and in bare country, although there is usually some vegetation nearby (Jennings 2010). Clutches contain two to three eggs. Both adults assist in incubating the eggs and raising the young, which often stick to their parents until fully grown (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
In UAE this species is under threat from anthropogenic disturbance and loss of habitat due to land-use changes (Aspinall 1996, Symes et al. 2015). Feral dogs may also be a potential threat.
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
330489
Taxon name
Porphyrio porphyrio
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Porphyrio porphyrio
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
gruiformes
Family
rallidae
Genus
Porphyrio
Species
porphyrio
Species authority
(Linnaeus, 1758)
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
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, and the potential for immigration from outside the UAE remains very high. Therefore, the species's status has undergone a regional adjustment; down one category and is thus listed as Endangered at the national level, as the evidence for increase is not yet in place.
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
From 2002 on, this species occurred as a vagrant, but regularly, at Al Warsan Lakes near Dubai City, where up to eight pairs have been breeding annually since 2004. In 2013 and 2016, breeding was confirmed in the Al Wathba Wetland Reserve (Pedersen et al. 2017). Between 1984 and 2016, the species has been recorded at multiple locations in Dubai City (Jebel Ali Hotel, Al Warsan Lakes, Zabeel Ponds, Emirates Golf Club), Sharjah City (Ramtha Rubbish Tip), as well as in Ruwais Housing Complex and Ain Al Fayda in Abu Dhabi Emirate (Pedersen et al. 2017). Moreover, several birds have been released in the last decades: In 1997, 25 individuals were released in Abu Al Abyad Island; in 2004, 20 individuals were released near Mushrif National Park in Dubai, which were not found again in 2013; in 2012, several individuals were released near Al Ajban in Dubai Emirate (Pedersen et al. 2017). One individual of uncertain origin was recorded in 2013 near Al Madam in Sharjah Emirate (Pedersen et al. 2017).
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 occurs in brackish and freshwater habitats with dense vegetation cover, like swamps, reed beds and lake borders, but it may also be found in small temporary wetlands (Jennings 2010, Aspinall and Porter 2011). The species is mainly crepuscular and forages in the early-morning and late-evening (del Hoyo et al. 1996). There is no information available about its diet in the UAE; elsewhere the diet consists predominantly of plant matter including shoots, leaves, roots, stems, flowers and seeds (del Hoyo et al. 1996, Taylor and van Perlo 1998). It also takes animal matter including molluscs, leeches, small crustaceans, adult and larval insects, earthworms, spiders, fish and fish eggs, frogs and frog spawn, lizards, water snakes Natrix maura, adult birds, bird eggs and nestlings, small rodents and carrion (del Hoyo et al. 1996, Taylor and van Perlo 1998). Its breeding biology is not well studied; the timing of breeding is unknown and seems to be erratic, as chicks have been recorded in Dubai in October and April (Jennings 2010). No nest has been described from the UAE. Elsewhere, it breeds in solitary territorial pairs or in small communal groups containing several breeding males, breeding females and non-breeding helpers and the nest it is a shallow cup in a large substantial structure of vegetation built on a platform of vegetation floating on or standing in shallow water 30-120 cm deep and concealed in thick vegetation (del Hoyo et al. 1996, Taylor and van Perlo 1998).
Threats and conservation measures listed
Threats listed in assessment
The main threat to this species within UAE is likely to be from land-use changes. Globally the use of pesticides has been noted as a possible threat too, although this is unlikely to impact individuals in the UAE. The species is also susceptible to avian influenza (Melville and Shortridge 2006, Gaidet;et al.;2007) and avian botulism, so may be threatened by future outbreaks of these diseases (Galvin;et al.;1985).
History
The species was not breeding in the UAE in 1996; the first breeding record was in 2004. Therefore, it would not have been assessed 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
Assessment ID
330485
Taxon name
Caprimulgus aegyptius
Lichtenstein, 1823
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Caprimulgus aegyptius
Lichtenstein, 1823
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
caprimulgiformes
Family
caprimulgidae
Genus
Caprimulgus
Species
aegyptius
Species authority
Lichtenstein, 1823
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
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 and the potential for immigration from outside the UAE remains very high, as the species is stable in the wider Arabian Peninsula. Therefore, the species's status has undergone a regional adjustment down one category and is thus listed as 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 in the UAE are likely to be of migrant individuals. Between September and early May, the species is fairly common across the country (Pedersen et al. 2017). The species is a scarce breeding resident in Abu Dhabi Emirate; the first breeding was confirmed in June 2013, followed by two more records from March 2016 and April 2017 (Pedersen et al. 2017).
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 occurs in semi-deserts, often interspersed with palm or scrub (Aspinall and Porter 2011). The species is migratory; after breeding in south-central Asia, individuals winter in the UAE or pass through the country on their way to wintering grounds in the Sahel zone of Africa. There is no information available on its feeding habits, nor on its breeding behaviour in the UAE. Elsewhere it feeds singly or in small flocks low over the ground near water, bushes, over cultivated land or livestock enclosures, where it takes mainly insects (Cleere 2019). It breeds from spring to early summer. Eggs are laid directly on the ground in a depression among stones, sheltered by a small bush. Clutches contain one to two eggs (Cleere 2019).
Threats and conservation measures listed
Threats listed in assessment
Historically, this species appears to have been impacted by agricultural development and urbanisation within parts of its breeding range (del Hoyo et al. 1999). The degree to which this has affected the species over recent times is uncertain, but it is possible that habitat loss could be having an effect on the species within UAE.
History
This species would not have qualified to have been listed in a 1996 assessment of this species's Red List status in UAE. As such this species cannot be assessed for a genuine change.
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
330483
Taxon name
Bubo ascalaphus
Savigny, 1809
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Bubo ascalaphus
Savigny, 1809
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
strigiformes
Family
strigidae
Genus
Bubo
Species
ascalaphus
Species authority
Savigny, 1809
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
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 resident population in the UAE, which qualifies it for listing as Endangered. Given the long-term stability of the population, any immigration of mature individuals is not deemed significant. Therefore, the species's status has not undergone a regional adjustment and is retained as Endangered.
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
This species is a widespread resident particularly in the northern part of the UAE, with several records also from the Empty Quarter (Jennings 2010, Pedersen et al. 2017).
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 inhabits lithified sandy areas and arid, rocky areas like mountains and steppe in the lowlands below 1,000 m. It is found on cliffs, crags, rocky outcrops and small isolated hills on the plains, as well as in sandy deserts interspersed with trees and bushes, often near the coast (Jennings 2010, Aspinall and Porter 2011). It feeds mainly on rodents (Lepus, Rattus, Meriones, Jaculus and Gerbillus species), but also on birds, bats, lizards and large invertebrates (Jennings 2010). When available, it is drawn to troughs and wells for drinking water (Jennings 2010). It generally avoids proximity to humans (Jennings 2010). Being solitary between August and December, pairs form in December and begin breeding in late January. The species nests on the ground, under Leptadenia and Ghaf vegetation,;in rock cavities, protected by an overhang, in an unlined sandy depression, which may be used in consecutive years (Jennings 2010). Clutches contain two or three eggs. Juveniles in the nest have been recorded until June (Jennings 2010). Humans approaching the nest are chased off by angry distraction displays including hooting and screaming, bill snapping, flapping along the ground and tumbling down slopes (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
This species may face persecution to discourage nesting near human habitation (Aspinall 1996), while collisions with vehicles and powerlines can lead to the death of individuals (Aspinall 1996). There is also a risk that individuals may be taken from nest sites for trade (Symes et al. 2015) or because people accidentally think chicks have been abandonned. Nests may also be disturbed by photographers, and undisturbed nest site availability may be declining in certain areas.
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