LC

Assessment ID
330604
Taxon name
Charadrius alexandrinus
Linnaeus, 1758
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Charadrius alexandrinus
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
charadriidae
Genus
Charadrius
Species
alexandrinus
Species authority
Linnaeus, 1758
Taxonomic notes and synonyms listed
Charadrius alexandrinus, C. dealbatus and C. nivosus (del Hoyo and Collar 2014) were previously lumped as C. alexandrinus following Sibley and Monroe (1990, 1993).
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species has a relatively large breeding and non-breeding population, and both are thought to be stable. Also in the wider Arabian Peninsula, the population is assumed to be stable, and thus the likelihood of a rescue effect is very high. Therefore, the species is listed as Least Concern.
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 in coastal UAE (Pedersen et al. 2017). Outside of the breeding season, the population is supplemented by migrants (particularly in March-May and August-October) and wintering birds from the Balkans, Turkey and southeastern Russia (Richardson 1990, 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 the coastline on shingle, sandy and muddy beaches, shallow tidal mudflats, saline wetlands and lagoons (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). It is occasionally found further inland at pools of brackish or freshwater, reservoirs, sewage treatment plants and near livestock enclosures (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). It feeds on invertebrates like ants, bees, beetles, flies, maggots, decapod crustaceans and shrimps, which it takes from decaying algal mats or other marine detritus on the shore or from irrigated crop fields (Jennings 2010). In the UAE, the species breeds in spring and early summer, with most eggs laid in April and May; however, the breeding season may start earlier, with one record of chicks already in December (Jennings 2010). Preferred nesting sites include dry sandy or shingle patches near the coast or wetlands, where territories are established and aggressively defended (Jennings 2010). The nest is a shallow scrape in the sand or shingle, sometimes paved with small pebbles or shell and plant material arranged around it (Jennings 2010). Clutches contain usually three eggs (Jennings 2010). Eggs and nestlings suffer high rates of predation by rodents, foxes and terns (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
Within the UAE coastal development and urbanisation is reducing the amount of available habitat for the species (Aspinall 1996), and as such these threats are likely to be the most pressing issues for the population within the country. Oil spills may also have an effect on coastal ecosystems, but it is uncertain whether these have any effect on this species. The species is susceptible to avian botulism, so may be threatened by future outbreaks of the disease (Blaker 1967).
History
The species would also have been Least Concern in 1996 based on Aspinall (1996), which gives a;breeding population estimated at 2,600 individuals in 1996 (Aspinall 1966).
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
330603
Taxon name
Coracias benghalensis
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Coracias benghalensis
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
coraciiformes
Family
coraciidae
Genus
Coracias
Species
benghalensis
Species authority
(Linnaeus, 1758)
Taxonomic notes and synonyms listed
Coracias benghalensis and C. affinis (del Hoyo and Collar 2014) were previously lumped as C. benghalensis following Sibley and Monroe (1990, 1993).
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species has a relatively large resident population in the UAE, which is increasing steadily. Therefore, the species is listed as Least Concern 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
This species is a very common resident in the northern part of the UAE and around Al Ain (Abu Dhabi Emirate) (Pedersen et al. 2017). The range is expanding westward to the islands of Zarka, Sir Bani Yas and Das, as well as southward to the Liwa region (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
The species inhabits fertile, well-vegetated wadis with good availability of water. It is increasingly found in open cultivated country with scattered trees, such as irrigated fields and grass meadows, but also plantations, parks, gardens and even golf courses (Jennings 2010). It mainly feeds on the rich invertebrate fauna found in these habitats, which it takes by pouncing from lookout posts (Jennings 2010). In the UAE, cases of kleptoparasitism have been recorded (Jennings 2010). Pairs are monogamous, territorial and stay together throughout the year. Territories are defended by display flights, which include almost vertical flights and high dives, which are performed by the male or the pair together (Jennings 2010). Breeding takes place between April and June. Clutches contain three to four eggs (Jennings 2010). The nest is a thin pad made of grass, twigs, rags and feathers. It is placed in a tree cavity at least 2 m above the ground, particularly on old Ghaf Prosopis cinerea trees and date palms (Jennings 2010). The species competes for nest holes with exotic species like Rose-ringed Parakeet Psittacula krameri and mynas Acridotheres spp. (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
The species is considered to not be under any serious threat in UAE and is increasing rapidly (Aspinall 1996, Symes et al.;2015). However, the potential for declines in invertebrate populations as a result of agricultural intensification and future declines in water availability requires further research.
History
It is assessed that in 1996, after regional adjustment, 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
330602
Taxon name
Merops cyanophrys
(Cabanis & Heine, 1860)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Merops cyanophrys
(Cabanis & Heine, 1860)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
coraciiformes
Family
meropidae
Genus
Merops
Species
cyanophrys
Species authority
(Cabanis & Heine, 1860)
Taxonomic notes and synonyms listed
Merops orientalis, M. viridissimus and M. cyanophrys (del Hoyo and Collar 2014) were previously lumped as M. orientalis following Sibley and Monroe (1990, 1993).
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The species's population size within the UAE is large enough that it would not approach the thresholds for listing under a threatened category due to small population size alone. The population has been considered to be increasing, although there is some uncertainty now due to some noted localised declines, but it is not considered to be likely to be declining in the country as a whole. The population in the wider Arabian Peninsula is stable or increasing; thus, the potential for immigration from outside the UAE remains very high. Therefore, the species is listed as Least Concern 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
This species is a common to very common resident in the northern part of the UAE. Following agricultural and afforestation projects, its range is expanding southwards and westwards (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 rocky wadis with scattered acacia trees, in coastal plains and open country with trees, semi-desert, mountain sides, cultivations, parks and gardens (Jennings 2010, Aspinall and Porter 2011). It is not able to tolerate very dry environments (Jennings 2010). It feeds on aerial prey (bees, wasps, flies, locusts, moths and butterflies) by chasing them in short flights (Jennings 2010). Pairs form in winter and early spring, but pairs may stay together throughout the year (Jennings 2010). The breeding period lasts from February to July, with most activity occurring in April and May (Jennings 2010). Pairs are territorial and breed solitarily, excavating a nesting tunnel horizontally into a bank of sand, silk or earth, including artificial banks and trenches (Jennings 2010). Eggs are placed directly into a brood chamber at the end of the tunnel. In the UAE, pairs raise two to three juveniles (Jennings 2010). There is evidence that the species has two broods per season in the UAE (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
There have been localised declines in some areas, e.g. at Al Wathba, and these are suspected to be potentially be associated with land-use changes. The potential for declines in invertebrate populations as a result of agricultural intensification and future declines in water availability requires further research.
History
It is assessed that in 1996, after regional adjustments, 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
330598
Taxon name
Euodice malabarica
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Euodice malabarica
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
estrildidae
Genus
Euodice
Species
malabarica
Species authority
(Linnaeus, 1758)
Taxonomic notes and synonyms listed
Euodice malabarica (del Hoyo and Collar 2016) was previously placed in the genus Lonchura following AERC TAC (2003); AOU (1998 and supplements); Cramp and Simmons (1977-1994); Sibley and Monroe (1990, 1993).
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species has increased its population size over recent years and is expanding its range into anthropogenic habitats. As such it is not thought to approach the threshold for Vulnerable under any criterion, and is listed here as Least Concern.
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 very common resident in the UAE. As it is a popular pet in the country, some occurrences might be of individuals released from cages (Pedersen et al. 2017). It is unclear whether the species is indeed native to the country; it might have colonized the UAE and Oman during the first half of the 20<sup>th</sup> century from Iran, spreading westward across the Arabian Peninsula (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 uses a wide variety of habitats from wadis and hills, even in dry desert areas, but also occupies to grassland and scrub, cultivated land, palm groves and gardens (Richardson 1990, Aspinall and Porter 2011). It tolerates hot, dry conditions (Jennings 2010). The home range spans at least 3 km<sup>2</sup>, but is likely larger in rural populations (Jennings 2010). It forages in flocks, mainly taking seeds of reed (Phragmites sp.) and grass (Panicum turgidum, Pennisetum divisum) and in urban areas also visits bird tables (Jennings 2010). Occasionally, it forms mixed flocks with House Sparrow Passer domesticus and Spanish Sparrow Passer hispaniolensis (Jennings 2010). Nesting activity has been observed year-round (Jennings 2010), but seems to peak in January/February (Richardson 1990). Nests are ball-like structures consisting of grass, plant fibers and leaves, which are placed in a bush or tree (Jennings 2010). Occasionally, pairs occupy abandoned nests of other species (Jennings 2010). There is no information on clutch size in the UAE; elsewhere clutches contain three to eight eggs (Payne 2019). The species is a popular cagebird; some isolated populations likely originate from escaped or released cagebirds (Richardson 1990). Some individuals in these colonies had been colour-dyed, which is a common practice to make them more attractive for the pet trade (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
This species is caught for the cagebird trade, but this is not deemed to be a significant threat by Aspinall (1996). There is a risk that escapes from captivity could lead to introductions of disease into the wild population (Aspinall 1996). Some artificial habitats that favour this species within the UAE may be transient, so monitoring of such habitats will be important.
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
330597
Taxon name
Anthus spinoletta
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Anthus spinoletta
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Anthus
Species
spinoletta
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species has a small non-breeding population size within the UAE that could warrant listing as Near Threatened under Criterion D1. However, there is no strong evidence to support any deterioration and it is likely that there is a rescue effect from outside the country. Therefore, a regional adjustment has been made and the species is listed here as Least Concern.
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 common within the UAE during winter and on passage to and from the breeding grounds. Numbers are highest between late October and early April (Pedersen et al. 2017). Individuals wintering in or migrating through the UAE breed in south-central Eurasia.
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 a variety of open habitats, including lowland grasslands, large open gardens, wetlands, lakesides, sewage works and water treatment plants (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere it feeds mainly on invertebrates but also takes some plant material. The species is a short-distance migrant and breeds between late April and early July on mountain slopes and pastures in south-central Eurasia.
Threats and conservation measures listed
Threats listed in assessment
Within the UAE land-use changes may have an impact on this species, but the severity of such a threat is essentially unknown. Artificial habitats that favour this species within the UAE may be transient, so monitoring of such habitats will be important. Individuals visiting the country are likely to be impacted by other threats. For instance, in some areas, grazing animals have been shown to have a significant negative impact on the nesting success of this species (Pavel 2004). It is also thought to be threatened by climate change (Ebenhöh 2003, Melendez and Laiolo 2014).
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 (accounting for regional adjustments) may have been sufficiently small in 1996 that it would have warranted a listing as Near Threatened under criterion D1 then, whereas now (2019) it is assessed as Least Concern.
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
330595
Taxon name
Anthus campestris
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Anthus campestris
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Anthus
Species
campestris
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Although this species has a relatively small non-breeding population size within the UAE, there is no strong evidence to support any deterioration in the population (and it is likely that there is a rescue effect from outside the country). Therefore, the species is listed here as Least Concern as it does not approach the thresholds for listing as threatened.
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 very common during migration and winter in open country throughout the UAE. Numbers are highest between mid-September and late April. The species is uncommon between May and August (Pedersen et al. 2017). Individuals wintering in or migrating through the UAE breed in western-central Asia.
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 a wide variety of open country, including sparsely vegetated plains, grassland, desert scrub, cultivations, parks and rubbish dumps (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere it mainly feeds on insects, although other invertebrates and seeds are also taken, as well as rarely small vertebrates (Tyler and Christie 2016). The species often occurs in groups (Richardson 1990). It is migratory and breeds between mid-April and mid-August.
Threats and conservation measures listed
Threats listed in assessment
Overgrazing outside of Protected Areas potentially could have an impact on this species, while climate change may also have an impact (Tyler and Christie 2016).
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 (accounting for regional adjustments) may have been sufficiently small in 1996 that it would have warranted a listing as Near Threatened under criterion D1 then, whereas now (2019) it is assessed as Least Concern.
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
330592
Taxon name
Motacilla alba
Linnaeus, 1758
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Motacilla alba
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Motacilla
Species
alba
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Although this species has a relatively small non-breeding population size within the UAE, there is no strong evidence to support any deterioration in the population (and it is likely that there is a rescue effect from outside the country). Therefore, the species is listed here as Least Concern.
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 very common migrant and winter visitor in the UAE. It occurs throughout the country between mid-September and April (Pedersen et al. 2017). Individuals wintering in or migrating through the UAE breed throughout Eurasia.
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 a wide variety of non-forested, open habitats, including parks, large gardens, cultivations, livestock enclosures, damp grassland, sewage treatment plants, roadsides and roundabouts (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere it feeds on a wide range of small invertebrates, as well as fish fry, crumbs and other household scraps. At dusk, the species forms flocks to roost (Richardson 1990). The species is migratory and breeds between early April and August.
Threats and conservation measures listed
Threats listed in assessment
Climate change is thought to affect the timing of migration for this species (Ahas and Aasa 2006,;Sokolov and Gordienko 2008,;Kullberg;et al.;2015), but it is unknown whether this is having significant impacts on the population trend within UAE. Artificial habitats that favour this species within the UAE may be transient, so monitoring of such habitats will be important.
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
330589
Taxon name
Cinnyris asiaticus
(Latham, 1790)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Cinnyris asiaticus
(Latham, 1790)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
nectariniidae
Genus
Cinnyris
Species
asiaticus
Species authority
(Latham, 1790)
Taxonomic notes and synonyms listed
Cinnyris asiaticus (del Hoyo and Collar 2016) was previously placed in the genus Nectarinia and listed as N. asiatica following Sibley and Monroe (1990, 1993).
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The species has a large resident population, which is increasing within the UAE. Hence it is not believed to approach the threshold for Vulnerable, and as such it is listed as Least Concern.
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 breeding resident in the UAE (Pedersen et al. 2017). It is expanding its range southwards following intense afforestation efforts in the Abu Dhabi Emirate (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 a wide variety of habitats, only avoiding the most arid zones. It is found in coastal dunes and salt flats, in mountains, wadis and sandy deserts, thorn scrub and dry forest, but also in gardens and cultivations (Jennings 2010, Aspinall and Porter 2011). It feeds only on nectar, preferring the desert bush Calotropis procera. This plant's adaptation to arid conditions enable Purple Sunbird to survive even several years of drought (Jennings 2010). The species is nomadic in summer, when it leaves the breeding areas in response to declines in food availability (Jennings 2010). Between July and September, it is not found in urban and suburban parks and gardens (Jennings 2010). It has been hypothesized that the species is undergoing seasonal altitudinal migrations, moving from below 500 m, where the density of its preferred feeding bushes is highest, uphill to breed (Jennings 2010). The breeding season starts in March. The nest is a bottle-shaped construction the size of a tennis ball, made from grasses, spider's webs, and pieces of paper and plastic. It is attached to a branch using palm or nylon fibers (Jennings 2010). The clutch consists of two to three eggs, which are mainly incubated by the female (Jennings 2010). A pair may breed two or three times per breeding season (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
There are no known significant threats to this species within UAE (Aspinall 1996), although some artificial habitats that favour this species within the UAE may be transient, so monitoring of such habitats will be important.
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
330588
Taxon name
Galerida cristata
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Galerida cristata
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
alaudidae
Genus
Galerida
Species
cristata
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species has a very large resident population within the UAE, which is suspected to be potentially increasing. Therefore, it is listed here as Least Concern.
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 very common, abundant resident occurring almost across the entire country (Pedersen et al. 2017). It has colonised Qarnayn, Abu al-Abyad and Das islands in the 1990s, as well as remote desert areas in the south and west of the UAE (Richardon 1990, 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 grassy or arid country and semi-desert, given that sufficient vegetation cover is present (Jennings 2010). It is particularly numerous near human settlements, on farmlands, gardens and cultivated areas, as well as along roadsides (Jennings 2010, Aspinall and Porter 2011). The species generally becomes scarcer with increasing aridity and distance from human habitations (Jennings 2010). It feeds on the ground, occasionally digging into the surface with the bill (Jennings 2010). It feeds on invertebrates and plant material, such as seeds. Elsewhere, it also feeds on human food scraps, such as bread, fruits and plant shoots (Jennings 2010). The availability of drinking water is important for this species (Jennings 2010). The breeding behaviour is not well explored. In Arabia, the breeding period peaks between May and June, but nesting may already occur from January on (Jennings 2010). The species is monogamous and usually lays a clutch of one to five eggs. The nest is a depression on the ground with an untidy lining of grass or other vegetation (de Juana and Suárez 2004), which placed in the shade of a clump of grass or other plants (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
In Europe the use of pesticides has negatively affected populations (Tucker and Heath 1994), but this may not be a significant threat to this species within UAE. Predation by cats,;Felis catus,;has been noted to cause local declines on the Arabian Peninsula (Symes et al. 2015). Overgrazing outside of Protected Areas could be be an additional threat within 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
330586
Taxon name
Ammomanes deserti
(Lichtenstein, 1823)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Ammomanes deserti
(Lichtenstein, 1823)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
alaudidae
Genus
Ammomanes
Species
deserti
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species has a relatively large resident population in the UAE. The breeding population in the wider Arabian Peninsula is stable; thus, the potential for immigration from outside the UAE remains very high. Therefore, the species is listed as Least Concern 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
This species is a common resident, occurring in the mountains and plains of northeastern UAE as well as locally along the coast of western Abu Dhabi 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 on arid hills and along sparsely vegetated stony or rocky slopes (Jennings 2010). It avoids flat and sandy landscapes. The species can survive long periods without drinking water and shows several behavioural and morphological adaptations to hot and arid conditions: It is most active around sunrise and sunset, it moves slowly, avoids long flights and pants in hot weather. Moreover, its plumage has wide bar gaps between feathers (Jennings 2010). The species feeds on seeds and invertebrates, which it takes by systematically searching rocks and vegetation. Occasionally, it visits human habitations where it picks up discarded food (Jennings 2010). The highest breeding activity in Arabia has been recorded in March (Jennings 2010). The nest is made from grass stems and other fine plant material, lined with softer material and with a rampart of small stones on the exposed side, or surrounded by small stones when in an open site. It is always placed on the ground in the shade of a rock or plant (Jennings 2010). Clutches mostly contain three eggs (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
Development within its range could be leading to the loss and degradation of its habitat.
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