EN
Assessment ID
330212
Taxon name
Rumex limoniastrum
Uploaded by
National Red List Database
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330000
Taxon name
Pupalia lappacea
Uploaded by
National Red List Database
Scientific name
Pupalia lappacea
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
caryophyllales
Family
amaranthaceae
Genus
Pupalia
Species
lappacea
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
This species is considered to be very rare: it is known from few records and has a restricted distribution. The number of mature individuals is estimated to not exceed 200-300. In addition, it doesn't appear to occur in any protected areas and is not cultivated in any way. It is also unclear whether this species is currently threatened. The species is assessed as Endangered on the basis of the restricted number of mature individuals. There not known to be any adjacent populations in Oman, and no rescue effect is inferred; the seed is burred and presumed to be transported by larger animals.
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
In the UAE, this species is found in Wadi Naqab and in the Ru'us al-Jibal Mountains in the UAE (Jongbloed et al. 2003, Feulner 2011). Karim and Fawzi (2007) recorded it from Wadi Sha'am. The extent of occurrence (EOO) of this species is estimated at less than 294 km<sup>2</sup>. This species is widespread in the tropics of the Old World. It occurs in tropical Africa from Egypt to South Africa and Madagascar (APD 2019), through the Arabian Peninsula (Yemen, Oman, the UAE) to Pakistan, India and Sri Lanka, and Southeast Asia (Board of Trustees, RBG Kew 2018). It is introduced in Australia.
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 an annual or perennial amaranth that grows up to 150 cm (Jongbloed et al. 2003). It grows in silt among rocks and produces round leaves in addition to flowers from February to April (Jongbloed et al. 2003). It is typically found in shaded, sheltered and relatively mesic conditions. The species appears to be long lived as known individuals have survived in the same locality for over a decade (G.R. Feulner, in litt, MEW 2010).
Threats listed in assessment
The species appears to be grazed, however, it is not clear to what extent this poses a threat to the species.
History
The situation in 1996 is thought to be similar to the current situation, including a relatively small population size.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330680
Taxon name
Anthus richardi
Uploaded by
National Red List Database
Scientific name
Anthus richardi
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Anthus
Species
richardi
Taxonomic notes and synonyms listed
Anthus richardi and A. cinnamomeus (del Hoyo and Collar (2016) were previously lumped as A. richardi following AERC TAC (2003); Dowsett and Forbes-Watson (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
Retained in this Red List assessment due to its regional listing as Vulnerable as a breeding bird in the Arabian Peninsula, this species has a very small non-breeding population within the UAE. It is listed here as Endangered under Criterion D, having been adjusted down by one category because it has a relatively small population size in UAE compared to the regional and global population. Further research is required to identify whether the species may be being impacted by factors such as habitat loss.
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 or migrant individuals on passage to and from the breeding grounds. Numbers are highest between mid-September and mid-April, occasionally to early May, when the species is fairly common to common throughout the country (Pedersen et al. 2017). Individuals wintering in or migrating through the UAE breed in central-eastern 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 grassland, irrigated grassland, marshes, scrubland and cultivations (Richardson 1990, Richardson and Aspinall 1998, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere it is insectivorous and feeds mainly on beetles and grasshoppers (Tyler 2019). The species is a long-distance migrant and breeds between April and July in grasslands of Siberia and Kazakhstan (Tyler 2019).
Threats listed in assessment
Symes et al. (2015) does note that its habitat could be declining (with no first level threat described) in the wider Arabian Peninsula, although pesticide use is potentially a key threat in its wider range. Within the UAE itself, overgrazing in areas outside of Protected Areas could potentially be an issue for this species too.
History
It is considered 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
330675
Taxon name
Alauda arvensis
Uploaded by
National Red List Database
Scientific name
Alauda arvensis
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
alaudidae
Genus
Alauda
Species
arvensis
Taxonomic notes and synonyms listed
Alauda arvensis (AERC TAC [2003]; AOU [1998 and supplements]; Christidis and Boles [2008]; Cramp et al. [1977-1994]; Dowsett and Forbes-Watson [1993]; Sibley and Monroe [1990, 1993]; Turbott [1990]) and A. japonica (Sibley and Monroe [1990, 1993]) have been lumped into A. arvensis following del Hoyo and Collar (2016).
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
This species has a very small non-breeding population. There was a suggestion that it was in decline in the late-1990s, but recent records instead suggest that the population is stable. The small population size does, however, mean it meets the threshold for listing as Endangered under criterion D.
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 individuals (Pedersen et al. 2017). Numbers are highest in November to mid-March, when the species is fairly common in open areas near the coast (Richardson 1990, Pedersen et al. 2017). The species is rare in April and October (Pedersen et al. 2017). Individuals wintering in the UAE breed in north-eastern Europe and central Russia (Richardson 1990).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species occurs in a variety of open habitats, including high and low grasslands, scrubland, cultivated fields, golf courses and large parks (Richardson 1990, Aspinall and Porter 2011). It avoids deserts (Richardson 1990). There is no information available about its diet in the UAE; elsewhere during winter, it is primarily herbivorous and feeds on seeds and other plant material (Donald and Garcia 2014). During winter, it forms flocks of more than 20 individuals (Richardson 1990). The species is migratory and breeds from late March to August and September throughout Eurasia.
Threats listed in assessment
Predation by cats,;Felis catus,;has been noted to cause local declines in Crested Larks on the Arabian Peninsula (Symes;et al.;2015), and it is plausible that this would be an potential threat to this species within the UAE. Overgrazing outside of Protected Areas could be be an additional threat within UAE.The main cause of global decline in this species is agricultural intensification. Recent research indicates the principal causes are changes in management of cereal-growing and grassland in its breeding range (leading to reduced nesting and foraging opportunities, and reduction of food resources [Donald and Garcia 2014]). In grasslands high fertiliser applications lead to vegetation that is too tall and dense for nesting. High hunting pressure in some countries poses an additional threat (Donald and Garcia 2014). However, it is uncertain to what extent these global threats impact the individuals that visit UAE, especially as records suggest the visiting population is stable (per R. Sheldon in litt. 2019).
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
330649
Taxon name
Gelochelidon nilotica
Uploaded by
National Red List Database
Scientific name
Gelochelidon nilotica
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
laridae
Genus
Gelochelidon
Species
nilotica
Taxonomic notes and synonyms listed
Gelochelidon nilotica and G. macrotarsa (del Hoyo and Collar 2014) were previously placed in the genus Sterna and lumped as S. nilotica 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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a very small non-breeding population in the UAE, which qualifies it for listing as Endangered. The population trend within the country is not known, but wetland habitats within the UAE are likely to be deteriorating due to land conversion. Therefore, the species is retained as Endangered at the national level.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The majority of occurrences of this species are likely to be of winter visitors and of migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). The species is found at wetlands along the coast (Aspinall and Porter 2011).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species occurs along sheltered coasts and is only rarely found at sea or far from land (Jennings 2010, Aspinall and Porter 2011). It inhabits a variety of habitats along the coast, including bays, mudflats, coastal creeks, brackish lagoons and mangroves, and further inland, including fish farms, sewage treatment plants, rubbish dumps and well-vegetated sites (Jennings 2010). It is largely insectivorous and takes terrestrial and aquatic insects or molluscs, which it catches from surface water, on the ground or during flight (Jennings 2010). The species is migratory, dispersing widely after breeding before travelling southwards to the wintering grounds (del Hoyo et al. 1996). The population migrating through or wintering in the UAE breeds from Europe to central Asia and winters in Africa, the Middle East and India (Jennings 2010).
Threats listed in assessment
The most relevant threats within UAE are changes in coastal land-use and the possibility of oil pollution and marine debris, but the severity of these threats towards this species is unknown.Outside of the UAE, this species has also been identified as particularly susceptible to abandonment of breeding sites due to human disturbance (Molina et al. 2014), although early dispersal from breeding sites appears to be a behavioural trait of the species that may mitigate the impact of disturbance.
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
330648
Taxon name
Bubo africanus
Uploaded by
National Red List Database
Scientific name
Bubo africanus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
strigiformes
Family
strigidae
Genus
Bubo
Species
africanus
Taxonomic notes and synonyms listed
Bubo africanus and B. cinerascens (del Hoyo and Collar 2014) were previously lumped as B. africanus 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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a very small resident population, which would qualify it for listing as Critically Endangered. However, on one hand, the species has probably colonised the country from Oman (although it is tentatively suspected that the species was in the country prior to 1996), and there remains large potential of immigration into the UAE across the border. On the other hand, the species has only recently been discovered in the UAE, which suggests that it is highly restricted in the country. It has been tentatively decided, though, to regionally adjust the species's category, dropping it down one category. It is therefore classified here as Endangered in the UAE.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is a rare, inconspicuous resident of the Hajar Mountains in northern UAE. It was first recorded in November 2017 and by May 2018, ten territories had been confirmed (Pedersen et al. 2017). Further records include a juvenile donated to the Dubai Zoo in 2003, which was caught in the Dibba Mountains in Fujairah Emirate (R. Khan per Pedersen et al. 2017) and an undated photograph of an adult in the Hatta Mountains in Dubai Emirate (K. Al Dhaheri per 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
There is no information available about the species's ecology and habitat requirements in the UAE; the following information comes from elsewhere in Arabia and Africa, but likely also applies to the population in the UAE. The species inhabits well-vegetated, wooded wadis and is often found near human sites (Jennings 2010). It feeds mainly on invertebrates like beetles, mantids and grasshoppers, but likely takes also small birds, small mammals, reptiles, amphibians, molluscs and crustaceans, which are captured by pouncing from perches or searching on the ground (Jennings 2010). The species is entirely nocturnal; during the day it retreats to rocks, bushes and palm trees (Jennings 2010). Pairs remain together for life (Jennings 2010). The breeding period lasts from March to June or July (Jennings 2010). Nests are placed in scrapes on the ground, in crevices in rocks or cliffs, or in holes in a tree or building (Jennings 2010). Clutches contain two to four eggs (Jennings 2010).
Threats listed in assessment
Given how recently the species has been discovered in UAE it is difficult to assess the threats to this species, although given that one was captured and donated to the Dubai Zoo in 2003 (R. Khan;per;Pedersen;et al. 2017);this could represent a very minor threat. Otherwise threats may be similar as for B. ascalaphus, namely persecution to discourage nesting near human habitation (Aspinall 1996), and collisions with vehicles and powerlines (Aspinall 1996). However, further work is required to get a better view of the species's threats 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
330617
Taxon name
Sula dactylatra
Uploaded by
National Red List Database
Scientific name
Sula dactylatra
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
suliformes
Family
sulidae
Genus
Sula
Species
dactylatra
Taxonomic notes and synonyms listed
Sula dactylatra;(AOU 1998 + updates) and;Sula tasmani;(Christidis and Boles 1994) have been lumped as;S. dactylatra;following Christidis and Boles (2008).
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
This species has a very small non-breeding population in the UAE, which might qualify it for listing as Critically Endangered. The breeding population of the Arabian Peninsula is considered to be stable, and; there is potentially a high rescue effect from individuals outside of the country. Therefore, the species's status has undergone a regional adjustment down one category and is classified as Endangered at the national level.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is rare in the UAE, where it is found between April and November offshore. It was first recorded in May 1973 off Sha'am (Ras al-Khaimah Emirate). Since 2010, single individuals or very small groups have been recorded on 25 occasions along the coasts of Sharjah (mostly near Khor Kalba, Luluyah Beach) and Fujairah (Fujairah City, Dibba, Al Aqah) emirates;(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 strictly marine species can be found over pelagic waters far from land (Jennings 2010, Aspinall and Porter 2011). It feeds on large species of shoaling fish, especially flying fish, but will also take large squid (del Hoyo et al. 1992). It forages by plunge-diving, followed by pursuits under water (Jennings 2010). It breeds year-round on rocky coasts and offshore islands on the southern end of the Arabian Peninsula (del Hoyo et al. 1992, Jennings 2010). While adults usually remain close to the colony, particularly young birds disperse over large distances across the Indian Ocean, the Gulf of Oman and occasionally into the Arabian Gulf (del Hoyo et al. 1992, Jennings 2010, Pedersen et al. 2017).
Threats listed in assessment
While the most relevant potential threat to the species in UAE waters is from oil spills, breeding colonies may be affected by a range of threats, which in turn could impact individuals that visit UAE. Collection of eggs and hunting of adults from breeding colonies (Carboneras et al. 2018) is thought to be causing slow and significant declines. Masked Boobies are sensitive to human disturbance, with visitors passing within 10-20 m causing birds to leave their nest (Borsa et al. 2010); however, this is not believed to be significantly affecting the population in the UAE. Invasive species, primarily House Rats Rattus rattus, also could pose a threat as has been noted in some parts of its range;(for example on Clipperton Island, following the eradication of feral cats Felis catus;[Pitman et al. 2005]).
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
330616
Taxon name
Larus cachinnans
Uploaded by
National Red List Database
Scientific name
Larus cachinnans
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
laridae
Genus
Larus
Species
cachinnans
Taxonomic notes and synonyms listed
L. michahellis and L. armenicus (del Hoyo and Collar 2014) were previously lumped as L. michahellis following a review by the BirdLife Taxonomic Working Group. Prior to that, L. armenicus had been split and;L. cachinnans (del Hoyo and Collar 2014) had been lumped with L. michahellis as L. cachinnans 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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species potentially has a very small non-breeding population in the UAE, which qualifies it for listing as Endangered. Land conversion is likely to be impacting its wetland habitats within the UAE, and so the species is precautionarily retained as Endangered at the national level.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Between September and April, this species is uncommon to locally fairly common along the coast of the UAE (Richardson 1990, Pedersen et al. 2017). The majority of occurrences of this species are likely to be of migrant individuals on passage to and from the breeding grounds as well as of wintering birds (Pedersen et al. 2017). Taxonomic confusion and difficult identification makes the precise distribution uncertain.
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 coastal waters and is found at fishing harbours and lagoons. Occasionally, it forages further inland in cultivated fields, along rivers and especially at refuse dumps and sewage treatment plants (Richardson 1990, del Hoyo et al. 1996, Snow and Perrins 1998, Olsen and Larsson 2003). There is not much known about the species ecology in the UAE; thus most of the following information refers to its global distribution range during the non-breeding season. Its diet consists of fish, invertebrates, reptiles, small mammals, refuse, offal, and bird eggs and chicks (del Hoyo et al. 1996, Snow and Perrins 1998, Olsen and Larsson 2003). Outside of the breeding season, the species is gregarious. It is fully migratory. It returns to the breeding grounds in central Asia around April, where it breeds colonially (Richardson 1990, del Hoyo et al. 1996).
Threats listed in assessment
The most relevant threats to this species within UAE are potentially from wetland land-use changes, and possibly oil pollution at coastal sites, bycatch and marine debris (plastic) at sea, although the severity of these threats is essentially unknown.Individuals that visit UAE may also be impacted upon by other threats. It has been reported that colonies in the east of the global range are frequently raided for eggs and the species is hunted in the Ukraine (Rudenko 2006, Burger et al. 2018). It has also, previously been culled to protect other Larus species, however this has not been recorded recently. Numerous small oil spills have been reported to cause mortality in the species, for example in Azerbaijan (Burger et al. 2018), though this appears to have minimal impact on the population trend.
History
The population size is thought to have been the same in 1996, and so it would have received the same Red List status.
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
330615
Taxon name
Cursorius cursor
Uploaded by
National Red List Database
Scientific name
Cursorius cursor
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
glareolidae
Genus
Cursorius
Species
cursor
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
This species has a small breeding population in the UAE, which qualifies it for listing as Endangered. The breeding population in the wider Arabian Peninsula is likely to be in decline, so if there is immigration from outside of the UAE, it is possible that it will be decreasing. The species is therefore retained as Endangered at the national level.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is an uncommon breeding resident in the arid plains of the northern half of the UAE (Jennings 2010, Pedersen et al. 2017). After the breeding season, flocks disperse widely over dry, flat country (Pedersen et al. 2017). The population is supplemented by wintering birds and 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 breeds on arid, gravelly plains interspersed with sandy areas and scanty scrub vegetation, often away from water (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). It avoids sand-sea desert and mountainous or rocky regions, and is only rarely seen at freshwater or saltwater margins (Jennings 2010). Outside of the breeding season, it is found on open plains in a wider variety of habitats, including short grassland, irrigated fields, cropland, cattle enclosures and rubbish sites, but also in the outskirts of towns, in parks and gardens, as well as on golf courses (Jennings 2010, Aspinall and Porter 2011). It forages on the ground or in low vegetation, occasionally digging with its bill for food items (Jennings 2010). Its diet includes invertebrates like grasshoppers, spiders, beetles, cockroaches, bugs, termites, maggots and caterpillars, but also seeds and vegetable matter (Jennings 2010). Even though it is occasionally observed drinking at pools or dripping pipes, it likely obtains most of its liquids from food. During the hottest part of the day, the species retreats to shady spots (Jennings 2010). Breeding pairs form in January and February; eggs are laid between February and April, occasionally until June. The nest consists of an unlined patch of gravel in a sandy spot. Two eggs are placed directly on the bare ground (Jennings 2010). After the breeding season, individuals congregate in large groups (Jennings 2010). During winter, a migratory population occurs in the UAE, which most likely migrates from breeding grounds in Iraq, Syria and Iran (Jennings 2010).
Threats listed in assessment
Desert encroachment and development is likely impacting suitable breeding habitat for the species (Aspinall 1996), while the increase in desert activities such as dune driving could negatively impact the availability and quality of its habitat (R. Sheldon;in litt. 2019). Failure of rain is also expected to exert a negative impact on the population (S. Alam in litt. 2019).;Outside of the UAE, in the wider Arabian Peninsula, hunting is considered to be a significant threat (Symes et al. 2015), but the degree of impact on the individuals that visit the UAE is uncertain.
History
The species is thought to have also;qualified as EN in 1996.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates
Assessment ID
330614
Taxon name
Ixobrychus minutus
Uploaded by
National Red List Database
Scientific name
Ixobrychus minutus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
pelecaniformes
Family
ardeidae
Genus
Ixobrychus
Species
minutus
Taxonomic notes and synonyms listed
Ixobrychus minutus;and;I. dubius;(del Hoyo and Collar 2014) were previously lumped as;I. minutus;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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species may have a very small breeding population in the UAE, which might qualify it for listing as Critically Endangered. However, as the breeding population of the Arabian Peninsula seems to be increasing, there is high potential for immigration. Therefore, the species's status has undergone an adjustment down one category and is listed as Endangered at the national level. The species may be in the process of expanding its breeding range in the UAE.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are likely to be of migrant individuals on passage to and from the breeding grounds. Numbers are highest between March and June and between August and November, when the species is uncommon to fairly common at freshwater sites throughout the country, but it has occasionally been recorded during other months (Pedersen et al. 2017). The first record of breeding was in 1995 in Ruwais (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 well-vegetated rivers, brackish and freshwater ponds and lakes, reed beds and irrigation ditches (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). It often perches in trees or bushes (Jennnings 2010). There is no information available about its diet in the UAE; elsewhere it is mainly insectivorous and takes insects such as crickets, grasshoppers, caterpillars and beetles (del Hoyo et al. 1992, Kushlan and Hancock 2005). Other food items include spiders, molluscs, crustaceans, fish, frogs, tadpoles, small reptiles and birds (del Hoyo et al. 1992, Kushlan and Hancock 2005). It it is mainly a crepuscular feeder (del Hoyo et al. 1992, Kushlan and Hancock 2005). The migratory population breeds between May and July in Europe and Asia (del Hoyo et al. 1992, Jennings 2010). The species's breeding behaviour in the UAE is unknown, but elsewhere in Arabia it breeds between April and June in reed beds and possibly mangroves (Jennings 2010). Only one nest has been described in Arabia, which was made of dry stems lined with leaves and placed in reeds about 25 cm above the water level. It is suspected that clutches contain five eggs (Jennings 2010).
Threats listed in assessment
Changes in wetland land-use could affect this species in UAE, but the severity of such a threats towards this species is unknown.The species also faces a range of threats globally, which could impact individuals that visit the country. Since 1970, European populations have fallen, most likely due to habitat destruction and pollution, however these alone do not explain its overall European decline. Recreational activities such as fishing and swimming are also a threat as is the intensive commercial use of water areas (e.g. reed cutting, fish farming), river regulation measures and eutrophication (Bauer et al. 2006).
History
The first breeding was confirmed in 1995 (Aspinall 1996). The species is assessed as CR in 1996 without any regional revision.
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