LC
Assessment ID
330498
Taxon name
Tringa totanus
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
330495
Taxon name
Limosa lapponica
Uploaded by
National Red List Database
Scientific name
Limosa lapponica
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Limosa
Species
lapponica
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a moderately sized non-breeding population in the UAE that is suspected to be stable at present, and qualifies as Least Concern.
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). The species is common to very common between July and April along the coast (Richardson 1990, Pedersen et al. 2017). A small number of non-breeding individuals may stay over summer in the country (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species occurs along the coast, where it frequents tidal mudflats, coastal creeks, sandy beaches and estuaries (Richardson 1990, Aspinall and Porter 2011). It is rarely found at freshwater sites (Richardson 1990). There is no information available about its diet in the UAE; elsewhere the diet consists of annelids, bivalves and crustaceans, although the species will also take cranefly larvae and earthworms on grasslands and occasionally larval amphibians and small fish (del Hoyo;et al.;1996). The species is migratory; birds start arriving in the UAE by mid-July from its breeding grounds in the tundra of northern Scandinavia and the Taymyr Peninsula in northern Russia (Richardson 1990). During the non-breeding season, the species is gregarious; flocks of over 1,000 individuals are regularly observed between August and April at Khor Dubai (Richardson 1990).
Threats listed in assessment
Within the UAE, the main threats to the species are likely to be due to coastal land use changes and potentially from oil spills, but the severity of these threats on the species there are uncertain.Individuals that visit the UAE are also impacted upon by a range of threats outside of the country. Threats on the breeding grounds include oil and gas exploration and associated infrastructure development, legal subsistence harvesting and illegal hunting, and increases in predator numbers (Brown et al. 2014). Climate change has the potential to affect vegetation and the extent of suitable breeding habitat (P. Battley in litt. 2016). The species is also threatened by the degradation of stopover and non-breeding sites due to land reclamation, shellfisheries, pollution, human disturbance, reduced river flows,;and in some areas the invasion of mudflats and coastal saltmarshes by mangroves (owing to sea-level rise and increased sedimentation and nutrient loads at the coast from uncontrolled development and soil erosion in upstream catchment areas) (del Hoyo;et al.;1996, Kelin and Qiang 2006, Straw and Saintilan 2006, Melville;et al.;2016).;Anthropogenic nutrient enrichment of wetland areas at non-breeding sites can also cause cyanobacterium blooms that may impact this species's prey species (Estrella;et al.;2011).;The species has also been susceptible to avian influenza in the past so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006).
History
With a similar population and a stable global population at the time, 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
330487
Taxon name
Spilopelia senegalensis
Uploaded by
National Red List Database
Scientific name
Spilopelia senegalensis
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
columbiformes
Family
columbidae
Genus
Spilopelia
Species
senegalensis
Taxonomic notes and synonyms listed
Spilopelia senegalensis (del Hoyo and Collar 2014) was previously placed in the genus Stigmatopelia.
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The resident population in the UAE is extremely large and stable. The species is therefore evaluated as Least Concern at the national level.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is an abundant and widespread resident across the UAE, including the islands in the Arabian Gulf (Jennings 2010, Pedersen et al. 2017). While it was restricted to the northern UAE prior to the 1970s, it spread southward following agricultural expansion and the increase in the irrigation of agricultural land and gardens (Jennings 2010). The subspecies that occurs in UAE is S. s. cambayensis;(Aspinall 1996).
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 closely associated with humans and is able to rapidly adapt to modified habitats (Jennings 2010). In the UAE, it mainly inhabits the outskirts of villages and palm groves, but also towns, gardens, parks, oases and agricultural land (Jennings 2010, Aspinall and Porter 2011). It is also found in natural habitats, like dense shrubby vegetation with scattered trees. It avoids very open habitat like desert or large cultivated fields, where it clusters around tree clumps and grain silos (Jennings 2010). It feeds on the ground, where it takes mostly seeds, but also human food scraps from rubbish bins; elsewhere it is known to feed on fruits, nectar, plant material and insects (Jennings 2010). It breeds year-round, but primarily between February and July (Jennings 2010). The nest is a frail, thin platform of roots, twigs and grasses placed in a bush or tree up to 15 m above the ground (Baptista et al. 1997, Jennings 2010). It may also nest on buildings under the eaves, on window ledges, drainpipes, beams, over doorways or in cracks in walls (Snow and Perrins 1998, Jennings 2010). Clutches contain almost always two eggs; only occasionally up to four eggs have been recorded. The species has multiple broods per year (Jennings 2010).
Threats listed in assessment
There are currently no known serious threats to this species (Aspinall 1996).
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
330484
Taxon name
Athene noctua
Uploaded by
National Red List Database
Scientific name
Athene noctua
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
strigiformes
Family
strigidae
Genus
Athene
Species
noctua
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The resident population is relatively large, and hence does not approach the thresholds for Vulnerable under the population size criterion. The population trend is not known, but the population is not believed to be decreasing and so would not trigger as listing under a threatened category. For these reasons the species is evaluated as Least Concern at the national level.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is a fairly common resident of northern emirates and the sand deserts of western Abu Dhabi Emirate (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 rocky country with scattered trees, in open wooded areas, stony wasteland, wadis, semi-desert, sandy desert with rocky outcrops and cultivated areas (Jennings 2010, Aspinall and Porter 2011). Its diet includes small vertebrates like rodents, bats, reptiles and birds, but also invertebrates like beetles, locusts, grasshoppers, ants, scorpions, spiders and solifugids (Jennings 2010). The species is monogamous and breeds mainly between March and June, but exceptionally breeding behaviour may be observed already in November (Jennings 2010). It nests in tree holes, preferably of Ghaf trees, caves, rock crevices, animal burrows and holes in abandoned buildings or vehicles (Jennings 2010, Aspinall and Porter 2011). No nesting material is used; instead the eggs are laid in a scrape in debris like droppings, feathers and prey remains (Jennings 2010). There is no information available about clutch size in the UAE; elsewhere usually, clutches are three to six eggs (Holt;et al.;2014).
Threats listed in assessment
At a very local level shifting land-use patterns in the desert areas of UAE may have an impact on individuals of this species, but the overall effect is deemed insignificant (Aspinall 1996).
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
330480
Taxon name
Apus pallidus
Uploaded by
National Red List Database
Scientific name
Apus pallidus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
caprimulgiformes
Family
apodidae
Genus
Apus
Species
pallidus
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The breeding population in the UAE is relatively large and stable. The species is therefore evaluated as Least Concern at the national level.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs in the UAE during the breeding season and during migration. The breeding population is very common between November and April/May and is found mainly along the coast of Abu Dhabi Emirate and in the north-eastern part of the country (Jennings 2010, Pedersen et al. 2017). The migrant population travels through the country on passage to and from the breeding grounds. From June to October, the species is very rare and uncommon in the UAE (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 aerial during the day, when it is found over a variety of habitats, including over ponds, sewage lagoons, irrigated cropfields, along busy roads, over coastal saltflats with scattered saltbush, over the sea and over coastal stacks (Jennings 2010). There is no information available about its diet in the UAE; elsewhere it takes flies, mosquitoes, ants and bees (Jennings 2010). Records of adults entering nest crevices suggest that the main breeding period lasts from February to July. Nest have not been described for the UAE, but elsewhere they consist of grass, feathers and debris, which are glued together with saliva (Jennings 2010). The preferred nesting sites include natural rock crevices, but also man-made sites like buildings and towers (Jennings 2010, Aspinall and Porter 2011). Clutches may contain two to three eggs (Jennings 2010). The species is migratory; immediately after breeding in the UAE or other parts in the Middle East, it returns to the wintering grounds in west and central Africa.
Threats listed in assessment
There are currently no known threats to this species in UAE (Aspinall 1996), and indeed urban development may even be aiding the species by providing new nesting sites.
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
330474
Taxon name
Upupa epops
Uploaded by
National Red List Database
Scientific name
Upupa epops
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
bucerotiformes
Family
upupidae
Genus
Upupa
Species
epops
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has increased rapidly since initially colonising the country in the late 1980's as a regular breeding species. The population size is now estimated to be 500-1,000 pairs (1,000-2,000 mature individuals), and this would warrant a listing of Near Threatened under criterion D1. The species is likely to continue to increase, and the possibility of rescue effect is good. Therefore, a regional adjustment has been made and it is listed as Least Concern here.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is a very common resident in the northern part of the UAE. Individuals will pass through the country on passage, and some may over-winter (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
Throughout the year, this species occupies open country such as well-watered meadows, grass patches on roadsides, damp areas near rivers and sewage lagoons, but also woodland, olive and palm groves, parks and gardens, or oases (Jennings 2010, Aspinall and Porter 2011). It requires the presence of features offering perches, drinking water, shade, nest-sites and accessible food. The species can tolerate hot, arid conditions, but only for short periods during migration (Jennings 2010). It feeds almost entirely on animal matter, primarily large insects and their larvae and pupae (Snow and Perrins 1998, Jennings 2010). While the species has no serious competitor for food resources, it may have to compete for nest sites with exotic species like mynas Acridotheres spp. or Common Starling Sturnus vulgaris (Jennings 2010). The species is monogamous, solitary and a territorial breeder. It breeds between January and August; nestlings have been reported in the UAE in February (Jennings 2010). It nests in natural holes in stumps, trees, walls, old buildings, cliffs, among boulders, in abandoned vehicles, drain pipes, wells, roof spaces and nest boxes, and occasionally in places like a lawn sprinkler cavity, a roll of carpet and a fountain, and may use the same site for several seasons (Jennings 2010, KriÅ¡tín;and Kirwan 2015). The nest may be unlined or lined with some debris from the crevice (Snow and Perrins 1998, Jennings 2010). In Arabia, clutches contain five to seven eggs (Jennings 2010).
Threats listed in assessment
This species has likely expanded thanks to the spread of suitable irrigated areas. These artificial habitats within the UAE may be transient, so monitoring of such habitats will be important.;Individuals that over-winter in country may face additional threats outside of the country, such as hunting (KriÅ¡tín;and Kirwan 2015).
History
The breeding population has been increasing over the past decades (R. Sheldon;in litt. 2019). The species had started breeding regularly by 1988 (R. Sheldon;in litt. 2019), but in the early 1990s, the species was still considered scarce - estimated at 10-100 pairs (Aspinall 1996). This would mean that in 1996 it warranted a listing as Critically Endangered under criterion D, but it would have undergone a regional adjustment to Endangered. Subsequent estimates increased to 100-200 pairs (Jennings 2010), and the population now is suspected to be 500-1,000 pairs, implying a population increase which might be due to the increase in the availability of suitable habitat (R. Sheldon;in litt. 2019).
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
330471
Taxon name
Anas crecca
Uploaded by
National Red List Database
Scientific name
Anas crecca
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
anseriformes
Family
anatidae
Genus
Anas
Species
crecca
Taxonomic notes and synonyms listed
Common Teal;A. crecca;(del Hoyo;et al.;2014) has been split into;Common Teal;A. crecca and Green-winged Teal;Anas carolinensis;(Handbook of the Birds of the World and BirdLife International 2020).;;This change follows a revision to the scoring of the;males' vertical white breast-side line, due to its role as a signal in display. As such the revised scoring is as follows:;male;A. carolinensis;differs from A. crecca;male in its vertical white breast-side line, replicated on rear flank (3),;lack of white horizontal scapular stripe (2), and lack of narrow buff supercilium (above broad green eyestripe) (1); various other very minor differences cannot be scored (plumage characters capped at three), differences in measurements do not exist, behavioural differences are matters of frequency rather than type, and genetic evidence, while suggesting paraphyly involving;A. flavirostris, indicates that hybridization is relatively widespread in Beringia (allow 1 for broad hybrid zone), indicating that;carolinensis;does warrant species status.;Aleutian race nimia remains treated as a synonym of a monotyic A. crecca.
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a large and increasing non-breeding population in the UAE, which qualifies it for listing as Least Concern. The population is stable within the region. Conditions outside of the UAE are considered unlikely to deteriorate, so there is a potentially very high rescue effect from individuals outside of the region.
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 common to very common passage migrant and winter visitor to the UAE (Pedersen et al. 2017). It occurs throughout the country between September and April, with numbers being highest from late October to mid-March (Richardson 1990).
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 in wetlands, from salt marshes to fresh and brackish inland ponds, lakes, ditches and standing water (Richardson 1990, Aspinall and Porter 2011), including dams in the Hajar Mountains. It is rarely found on tidal creeks and lagoons (Richardson 1990). There is no information available about its diet in the UAE; elsewhere during winter, the species mainly takes the seeds of aquatic plants (e.g. emergent and submerged macrophytes), grasses, sedges and agricultural grains (del Hoyo et al. 1992, Kear 2005). The species is migratory; individuals winter in the UAE between September and April before returning to their breeding grounds in Eurasia, where they breed from May onwards in single pairs or loose groups (Madge and Burn 1988, Richardson 1990, del Hoyo et al. 1992). Outside of the breeding season, the species forms large concentrations, with large flocks of 30-40 and sometimes hundreds of individuals gathering at winter roosting sites (Brown et al. 1982, Madge and Burn 1988).
Threats listed in assessment
The most relevant threats within UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown.Individuals of this species that visit UAE are also threatened by a range of threats that operate outside of the country: for instance, the species is threatened by lowland habitat loss and degradation (e.g. through wetland drainage) (Musil 2006) and by upland habitat loss due to afforestation and other land-use changes (Kear 2005). The species suffers mortality as a result of lead shot ingestion (Mondain-Monval et al. 2002), and is intensively hunted in its some areas (del Hoyo et al. 1992; e.g. Iran [Balmaki and Barati 2006]). The species is threatened by disturbance from human recreational activities (Pease et al. 2005),;and construction work (Burton et al. 2002). The species is susceptible to avian botulism (Rocke 2006) and avian influenza (Melville and Shortridge 2006, Gaidet et al. 2007) so may be threatened by future outbreaks of these diseases.
History
The species would also have qualified 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
330469
Taxon name
Spatula clypeata
Uploaded by
National Red List Database
Scientific name
Spatula clypeata
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
anseriformes
Family
anatidae
Genus
Spatula
Species
clypeata
Taxonomic notes and synonyms listed
Spatula clypeata;(del Hoyo and Collar 2014);was previously placed in the genus Anas.
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a large non-breeding population in the UAE, which qualifies it for listing as Least Concern.
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 locally common to very common migrant and winter visitor to the UAE, where it mainly occurs between August and March/April in the northern part of the country and in wetlands near Sharjah and Abu Dhabi cities (Richardson 1990, Pedersen et al. 2017). Occasionally, individuals are recorded in summer (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
The species is found in permanent shallow freshwater wetlands like marshes, lakes, ponds, reservoirs, but also in shallow coastal creeks and lagoons (Richardson 1990, Aspinall and Porter 2011). Usually, copious submerged aquatic vegetation sheltering abundant planktonic invertebrates is a valuable habitat characteristic (Johnsgard 1978). There is no information available on its diet in the UAE; elsewhere, it consists of small aquatic invertebrates such as adult and larval insects, molluscs, planktonic crustaceans, the seeds of emergent and aquatic plants, annelids, amphibian spawn, tadpoles, spiders, fish and the vegetative parts of aquatic plants (Johnsgard 1978, Brown et al. 1982, del Hoyo et al. 1992, Snow and Perrins 1998, Kear 2005). The species is highly migratory. Individuals wintering in the UAE mainly breed in solitary pairs or loose groups between April and June in central Asia (Madge and Burn 1988, del Hoyo et al. 1992). During autumn migration, migrant individuals pass through the UAE between August and October, travelling on a broad front (Richardson 1990, Scott and Rose 1996). In the UAE, the species usually occurs in flocks of more than 60 individuals at preferred sites (Richardson 1990, Richardson and Aspinall 1998); it generally often congregates when feeding or at stop-over sites on migration (Madge and Burn 1988, Kear 2005). It forages diurnally and roosts communally at night (Brown et al. 1982).
Threats listed in assessment
The most relevant threats within UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown.Individuals of this species that visit UAE are also threatened by a range of threats that operate outside of the country: For instance, the species is threatened by habitat loss from drainage and changing farmland practices (Hagemeijer and Blair 1997), and it is occasionally killed by collisions with power transmission lines (Malcolm 1982). It is susceptible to avian influenza (Melville and Shortridge 2006, Gaidet et al. 2007) and avian botulism (Forrester et al. 1980) so may be threatened by future outbreaks of these diseases. The species is frequently hunted in large proportion of its range (e.g. North America, Europe and Iran [Baldassarre and Bolen 1994, Balmaki and Barati 2006, BirdLife International 2015), but is rarely taken in large numbers (Kear 2005). The species suffers mortality as a result of lead shot ingestion (Camargue, Franceand Spain [Mateo et al. 1998, Mondain-Monval et al. 2002]).
History
In 1996, the species is likely to have qualified as Vulnerable (D1), downlisted to NT based on a regional assessment. This rate of increase is likely due to increased artificial wetland sites.
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
330468
Taxon name
Anas platyrhynchos
Uploaded by
National Red List Database
Scientific name
Anas platyrhynchos
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
anseriformes
Family
anatidae
Genus
Anas
Species
platyrhynchos
Taxonomic notes and synonyms listed
Anas platyrhynchos and A. fulvigula (incorporating diazi) (del Hoyo and Collar 2014) were previously treated as A. platyrhynchos (incorporating diazi) and A. fulvigula following Sibley and Monroe (1990, 1993).
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
Expert opinion at the UAE assessment workshop is that it is possible to differentiate between resident (non-native) and visiting wild populations. The population size is estimated to be at least 1,000 mature individuals, and it is assessed as Least Concern.
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 common migrant and winter visitor, which occurs throughout the UAE between October and March (Richardson 1990, Pedersen et al. 2017). Large populations of several hundred individuals are regularly found at Dubai Creek (Dubai Emirate) and in Ayn al Fayda near Al Ain (Abu Dhabi Emirate) (Richardson 1990). A population of resident, breeding birds was introduced in the 1980s in Dubai and Abu Dhabi cities and on Sir Bani Yas Island (Richardson and Aspinall 1998, Jennings 2010), but this introduced population would not count towards its Red List assessment.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
In the UAE, this species is most often found at estuaries, ponds, reservoirs, creeks, lagoons and water treatment plants (Richardson 1990, Aspinall and Porter 2011). It requires water less than 1 m deep for foraging (Snow and Perrins 1998). There is no information available about its diet in the UAE. In general, the species is omnivorous and opportunistic, feeding by dabbling in water and by grazing on the land (del Hoyo et al. 1992, Snow and Perrins 1998). Elsewhere, its diet consists of seeds and the vegetative parts of aquatic and terrestrial plants, as well as terrestrial and aquatic invertebrates such as insects, molluscs, crustaceans, worms and occasionally amphibians and fish (del Hoyo et al. 1992). The non-breeding population native to the UAE is migratory, leaving its breeding grounds in the western Palaeartic in September/October and returning in February/March (Richardson 1990). During migration and in winter, the species can be found in small to very large flocks numbering up to several hundred of individuals (Madge and Burn 1988, Richardson 1990, Richardson and Aspinall 1998, Snow and Perrins 1998). The species may also roost both nocturnally and diurnally in communal groups when not breeding (Brown et al. 1982).An introduced population breeds in early spring in various locations near human sites in Dubai and Abu Dhabi emirates (Richardson 1990, Richardson and Aspinall 1998, Jennings 2010), and chicks are present from late March on (Richardson 1990). While there is not much known about the breeding behaviour of the introduced population (Jennings 2010), usually the nest is a shallow depression or bowl of vegetation that can be situated in many different locations such as within vegetation on the ground, in natural tree cavities, under fallen dead wood, on tree stumps, under bushes and even in abandoned nests of other species (e.g. herons or crows) (Brown et al. 1982, Flint et al. 1984, del Hoyo et al. 1992, Snow and Perrins 1998). Nests are generally placed close to water (Kear 2005).
Threats listed in assessment
Within the UAE the main threats are likely to be from changes in wetland land-use, and potentially from oil pollution, but the severity of these on the population is uncertain - especially given the presence of a feral population here (which would not count to a Red List assessment).Outside of the UAE the species faces a range of threats, which could impact individuals that visit the country. The species is threatened by wetland habitat degradation and loss from pollution (e.g. petroleum [Grishanov 2006] and pesticides [Kwon et al. 2004]), wetland drainage, peat-extraction, changing wetland management practices (e.g. decreased grazing and mowing in meadows leading to scrub over-growth)and the burning and mowing of reedbeds (Grishanov 2006). The species is hunted over large areas (Kear 2005) and also suffers mortality as a result of lead shot ingestion (e.g. Mateo et al. 1999, Mondain-Monval et al. 2002). It is also susceptible to duck virus enteritis (DVE) (Friend 2006), avian influenza (Melville and Shortridge 2006) and avian botulism (Rocke 2006), so it may be threatened by future outbreaks of these diseases (although it may be able to withstand sporadic losses due to its high reproductive potential) (Rocke 2006).
History
The population in 1996 is thought to have also been moderately large (e.g., 1,000+ at Al Ain), with large visiting (= natural) populations. The species is considered to have been 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
330658
Taxon name
Pomadasys commersonnii
Uploaded by
National Red List Database
Scientific name
Pomadasys commersonnii
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
haemulidae
Genus
Pomadasys
Species
commersonnii
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This inshore, marine and estuarine species occurs throughout UAE waters. Fishing activity is not known to be causing declines in the UAE. It can be impacted by estuarine degradation (e.g., South Africa). There are no known major threats; therefore, it is listed as Least Concern in 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 occurs throughout UAE waters. Globally, it is restricted to the Western Indian Ocean where it occurs from South Africa and Madagascar to the Arabian Gulf to India and the Seychelles (Smith and Heemstra 2003). Its estimated depth range is 0-50 m.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
This species inhabits shallow coastal areas and estuaries (Smith and Heemstra 2003). Spawning occurs at sea and juveniles settle in estuaries (Whitfield 1998). Adults inhabit full marine habitats, but also travel to estuaries for feeding (Day et al. 1981, Dames et al. 2017). Its maximum standard length is at least 70 cm (Nodo et al. 2017), longevity is 15 years and sexual maturity occurs at 3 years of age and 30-40 cm total length (Day et al. 1981). A study conducted in Oman reported lengths at 50% maturity of 44.2 cm for males and 42 cm for females (Al-Nahdi et al. 2010). When applying an age at first reproduction of 3 years and longevity of 15 years, its estimated generation length is 9 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Threats listed in assessment
Fishing activity is not known to be driving declines in the UAE at this time. Anthropogenic modification of estuarine habitats, which is pervasive in the Arabian Gulf region, may impact this species.
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.