United Arab Emirates

Official name
United Arab Emirates
ISO alpha-2 code
AE
ISO alpha-3 code
ARE
ISO numeric-3 code
784
Continent
Asia

Euodice malabarica | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
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).
Taxon
Taxa
Euodice malabarica | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
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).
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).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Anthus spinoletta | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
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.
Taxon
Taxa
Anthus spinoletta | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
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.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
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.
Verified entry
Off

Anthus cervinus | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species occurs in humid areas and usually near water, favouring marshes, damp grassland, wet hollows, surface water margins and cultivations (Richardson 1990, Aspinall and Porter 2011). During winter, the species forms small flocks at its preferred locations (Richardson 1990). There is no information available about its feeding habits in the UAE; elsewhere it forages on the ground and its prey is mainly insects but also other invertebrates, and some vegetable matter (Tyler 2016). The species is migratory and breeds between late May and July in the arctic tundra.
Taxon
Taxa
Anthus cervinus | (Pallas, 1811)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs in the UAE during winter and on passage. Numbers are highest between mid-September and early May, when the species is common to very common in humid areas throughout the country (Pedersen et al. 2017). Individuals wintering in or migrating through the UAE breed in the Arctic.
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has a very small non-breeding population size within the UAE, small enough that it falls below the threshold for listing as Endangered under Criterion D. However, it is likely that there is the chance for a rescue effect for this population and so the category has undergone a regional adjustment. Therefore, the species is listed here as Vulnerable under Criterion D1.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Artificial habitats that favour this species may be transient, so monitoring of such habitats will be important. The species is also vulnerable to future climate change (Virkkala et al. 2008).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Anthus campestris | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
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.
Taxon
Taxa
Anthus campestris | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
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.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
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.
Verified entry
Off

Motacilla cinerea | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species occurs on inland freshwater sites, including wooded streams, mountain wadis near rivers, pools and pool margins, sewage treatment plants and wet grassland (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere it feeds mainly on insects, but also takes freshwater shrimps (Gammarus), terrestrial snails and spiders. The species is migratory and breeds between late March and August near watercourses in Eurasia.
Taxon
Taxa
Motacilla cinerea | Tunstall, 1771
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers are highest between late August and April, when the species is fairly common at freshwater sites throughout the country. The species is rarely observed in May (Pedersen et al. 2017). Individuals wintering in or passing through the UAE breed throughout Eurasia.
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
Retained in the UAE list because of its regional status as a breeding bird in the Arabian Peninsula, within the UAE this species has an extremely small non-breeding population size. This tiny population size meets the threshold for listing as Critically Endangered under Criterion D. However, after regional adjustment it is listed here as Vulnerable under Criterion D, as it has a relatively small population size in UAE compared to the regional and global population.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Symes et al. (2015) do not note any specific threats for this species despite it being considered Near Threatened as a breeding bird in the Arabian Peninsula due to a small population size; and indeed it has been suggested that stream pollution may not significantly impact the species (del Hoyo et al. 2004). Artificial habitats that favour this species may be transient, so monitoring of such habitats will be important.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Motacilla citreola | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species occurs near waterbodies or wet areas, including swampy and damp meadows or fields, marshes, exposed pond edges, river and lake margins, public parks, golf courses, lagoons, sewage ponds and water treatment plants (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere the diet includes a wide variety of invertebrates, often aquatic, and their larvae. The species is migratory and breeds from April to June in central Eurasian grasslands.
Taxon
Taxa
Motacilla citreola | Pallas, 1776
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
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. Numbers are highest between mid-August and April, when the species is common at wetlands throughout the country (Aspinall and Porter 2011, Pedersen et al. 2017). In other months, the species is rare (Pedersen et al. 2017). Individuals wintering in, or migrating through, the UAE breed throughout central Eurasia.
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has a non-breeding population size that is small enough to qualify as Endangered under Criterion D. However, the species is considered likely to receive a rescue effect from breeding populations outside of the country and so the species's category has undergone a regional adjustment. It is therefore listed as Vulnerable under Criterion D1.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There are currently no known significant threats to this species, however, artificial habitats that favour this species may be transient, so monitoring of such habitats will be important.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Motacilla alba | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
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.
Taxon
Taxa
Motacilla alba | Linnaeus, 1758
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
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.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Gymnoris xanthocollis | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species is found in open dry woodland, but sometimes also in cultivated areas with scattered trees or hedgerows, generally avoiding sandy desert (Jennings 2010, Aspinall and Porter 2011, Summers-Smith 2019). It has a strong preference for Ghaf (Prosopis cineraria) and acacia trees; however, during passage, almost any type of woodland is utilised, including mangroves, parks and large gardens (Jennings 2010). During the breeding season, the diet mainly consists of insects, in particular Orthoptera and Cicadidae, which are collected in the canopy of trees (Jennings 2010). Individuals on passage take nectar from flowering Eucalyptus and probably also Ghaf trees (Jennings 2010). Individuals arrive to the breeding grounds within the UAE from late March to April, when territories are established and males start singing. The breeding period is not known exactly, but it is assumed that three to four eggs are laid in April/May, which are incubated by the female, and juveniles fledge between mid-May and early July (Jennings 2010). Nests have not been described for the UAE. Elsewhere, they consist of; dry grass, wool and hair, lined with feathers. They are usually placed in a crevice in a tree or shrub in more than 2 m height. There might be competition for nest sites with other hole-breeders, including Common Myna (Acridotheres tristis) and Pallid Scops-owl (Otus brucei) (Jennings 2010).
Taxon
Taxa
Gymnoris xanthocollis | (Burton, 1838)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Gymnoris xanthocollis (del Hoyo and Collar 2016) was previously placed in the genus Petronia following AERC TAC (2003); Cramp and Simmons (1977-1994); Sibley and Monroe (1990, 1993).
Taxon distribution as listed in assessment
This species breeds in the northern and eastern UAE, where it is common but localized (Jennings 2010, Pedersen et al. 2017). Occurrences in the southern and western parts of the country as well as in islands during March/April and September/October are likely to be of migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
D
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
The population size of this species within the UAE is potentially very small, potentially as low as 100 mature individuals, and the population is suspected to be declining. Therefore, the species is assessed as Endangered, without applying a regional adjustment.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Loss of woodland (e.g. Acacia and Prosopis), would have an impact on this species (see Aspinall 1996). Development in certain areas would also likely pose a threat to this species. There is some trade in this species, but this is only thought to involve imported individuals rather than capture from the wild within the country (Aspinall 1996).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
This species breeding in Ghaf groves, which have declined since 1996 and it is possible that the species doesn't adapt to altered habitats; which means that this species is suspected to be undergoing a decline within the UAE. While the 1996 population estimate of Aspinall (1996) is considered to be an overestimate, it is still considered here that the species would have warranted a listing of Least Concern in 1996, whereas now it is assessed as Endangered.
Verified entry
Off

Passer hispaniolensis | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
In general, this species is found mainly in moist, humid areas near water with trees and shrubs and is normally associated with cultivation, extending in villages, farmland, plantations, date groves or reed beds (Jennings 2010). During winter, it is highly gregarious, with flocks ranging far into the desert during foraging trips. It feeds on the ground, mostly on vegetable matter, especially seeds of grasses, crops and low herbs, but it also takes invertebrates throughout year (Jennings 2010, Summers-Smith 2015). Breeding occurs in colonies and is highly synchronised (Jennings 2010). The nest is a loosely woven, roughly spherical structure 15-“30 cm in diameter and made of grass and other plant stems, lined with finer grasses and feathers. It is preferably attached to branches of tall trees more than 15-20 m high, e.g. Ghaf (Prosopis cinearia), but also placed in lower bushes if trees are absent (Jennings 2010). There is no information on clutch size in the UAE, but elsewhere clutches of two to six eggs have been reported (Summers-Smith 2015).
Taxon
Taxa
Passer hispaniolensis | (Temminck, 1820)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is scarce and uncommon in the UAE. It irregularly winters in the country between November and early March, when it can form in large flocks (Richardson 1990), or occurs there during passage to and from the breeding grounds (Aspinall and Porter 2011). It bred in Ras al-Khaimah (Al Hamraniyah) and Fujairah (Wamm Farms) at least between 1993 and 2008 (Pedersen et al. 2017). Since 2009, the species has been recorded in three localities in Abu Dhabi (Ruwais and Al Mirfa) and Fujairah (Wamm Farms); in 2012 it was recorded once in Fujairah (Wamm Farms), and in 2014 once in Abu Dhabi (Al Lulu Island) (Pedersen et al. 2017). However, breeding in the UAE has not been observed for potentially five years now.
Assessed status
Asessment status in full
Critically Endangered
Assessment status abreviation
CR
Assessment status criteria
A2a+4a; D
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has been estimated to have a breeding population of up to 100 pairs, but there have been no recorded breeding attempts for potentially five years now, and it is suspected that the species is no longer breeding in the country. More research is required to confirm its disappearance from the UAE as a breeding species though. Therefore, the species is listed here as Critically Endangered (Regionally Possibly Extinct) as a breeding species in UAE.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
The threats that have driven this decline are essentially unknown.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
In 1996 the population size was considered to be 10-100 pairs (Aspinall 1996), which would have meant that the species would have qualified as Critically Endangered under criterion D. The species has subsequently potentially disappeared from the UAE as a breeding species, although the reasons for this are essentially unknown.
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Cinnyris asiaticus | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
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).
Taxon
Taxa
Cinnyris asiaticus | (Latham, 1790)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
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).
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).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
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