Assessment ID
330597
Taxon name
Anthus spinoletta
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
330596
Taxon name
Anthus cervinus
Uploaded by
National Red List Database
Scientific name
Anthus cervinus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Anthus
Species
cervinus
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
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.
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 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.
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 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.
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).
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
330595
Taxon name
Anthus campestris
Uploaded by
National Red List Database
Scientific name
Anthus campestris
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Anthus
Species
campestris
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
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.
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 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
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
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 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
330594
Taxon name
Motacilla cinerea
Uploaded by
National Red List Database
Scientific name
Motacilla cinerea
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Motacilla
Species
cinerea
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
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.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers are highest 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.
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 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.
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.
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
330593
Taxon name
Motacilla citreola
Uploaded by
National Red List Database
Scientific name
Motacilla citreola
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Motacilla
Species
citreola
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
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.
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. 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.
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 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.
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.
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
330592
Taxon name
Motacilla alba
Uploaded by
National Red List Database
Scientific name
Motacilla alba
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Motacilla
Species
alba
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
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.
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 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
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
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 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
330591
Taxon name
Gymnoris xanthocollis
Uploaded by
National Red List Database
Scientific name
Gymnoris xanthocollis
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
passeridae
Genus
Gymnoris
Species
xanthocollis
Taxonomic notes and synonyms listed
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).
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The 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.
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 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).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species is found in open 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).
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).
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.
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
330590
Taxon name
Passer hispaniolensis
Uploaded by
National Red List Database
Scientific name
Passer hispaniolensis
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
passeridae
Genus
Passer
Species
hispaniolensis
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
Critically Endangered
Abbreviated status
CR
Qualifying criteria (if given)
A2a+4a; D
Criteria system used
IUCN
(see Assessment details)
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.
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 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.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
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).
Threats listed in assessment
The threats that have driven this decline are essentially unknown.
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.
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
Uploaded by
National Red List Database
Scientific name
Cinnyris asiaticus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
nectariniidae
Genus
Cinnyris
Species
asiaticus
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).
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 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.
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 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
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
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 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
Uploaded by
National Red List Database
Scientific name
Galerida cristata
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
alaudidae
Genus
Galerida
Species
cristata
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 very large resident population within the UAE, which is suspected to be potentially increasing. Therefore, it is listed here 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 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
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
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 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