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

Pomadasys commersonnii | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

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
Yes
Habitat
Habitat details as listed in assessment
This species inhabits shallow coastal areas and estuaries (Smith and Heemstra 2003). Spawning occurs at sea and juveniles settle in estuaries (Whitfield 1998). Adults inhabit full marine habitats, but also travel to estuaries for feeding (Day et al. 1981, Dames et al. 2017). Its maximum standard length is at least 70 cm (Nodo et al. 2017), longevity is 15 years and sexual maturity occurs at 3 years of age and 30-40 cm total length (Day et al. 1981). A study conducted in Oman reported lengths at 50% maturity of 44.2 cm for males and 42 cm for females (Al-Nahdi et al. 2010). When applying an age at first reproduction of 3 years and longevity of 15 years, its estimated generation length is 9 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Taxon
Taxa
Pomadasys commersonnii | (Lacepède, 1801)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is restricted to the Western Indian Ocean where it occurs from South Africa and Madagascar to the Arabian Gulf to India and the Seychelles (Smith and Heemstra 2003). Its estimated depth range is 0-50 m.
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 inshore, marine and estuarine species occurs throughout UAE waters. Fishing activity is not known to be causing declines in the UAE. It can be impacted by estuarine degradation (e.g., South Africa). There are no known major threats; therefore, it is listed as Least Concern in the UAE.
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
Fishing activity is not known to be driving declines in the UAE at this time. Anthropogenic modification of estuarine habitats, which is pervasive in the Arabian Gulf region, may impact this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Pastinachus sephen | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

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
Yes
Habitat
Habitat details as listed in assessment
The Cowtail Ray is benthic in coastal habitats and occurs over soft substrates, often near coral reefs (Last et al. 2016) to depths of 60 m. Maximum size and biology is poorly known due to confusion amongst Pastinachus spp. This species reaches at least 89 cm disc width (Last et al. 2016). Generation length is estimated at 20 years based on age data from Maculabatis astra (Jacobsen 2007).
Taxon
Taxa
Pastinachus sephen | (Forsskål, 1775)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Cowtail Ray occurs throughout UAE waters. It is possibly endemic to the Arabian Sea region, although its exact distribution is uncertain due to confusion amongst Pastinachus species, and recent taxonomic changes within the genus (Last et al. 2016).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
A2cd
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 Cowtail Ray occurs throughout UAE coastal waters. The exact distribution is uncertain due to confusion amongst Pastinachus species and recent taxonomic changes. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980 and recent surveys have detected it in the area. Cowtail rays are regularly discarded in the Arabian Gulf and Sea of Oman. A large part of the species' regional distribution (namely, India and Pakistan) is under extremely intense and increasing demersal fishing pressure. It is not known how individuals occupying the UAE are connected with the broader population of the Arabian Seas region, and there is no information available to suggest that its population status differs in the UAE as compared to other parts of its range in the region. Given the threats faced by this species in other parts of the Arabian Seas region, and ongoing threats from discarding and habitat loss in the UAE, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 60 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
Criteria system
Criteria system specifics
IUCN v3.1
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
No
Endemism Notes
Is an endemic?: No
Endemism specifics: Possibly endemic to Arabian Sea region
Conservation
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Pastinachus ater | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

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
Yes
Habitat
Habitat details as listed in assessment
The Broad Cowtail Ray is benthic in coastal habitats. Maximum size and biology is poorly known due to confusion amongst other cowtail rays. Reaches ~200 cm disc width (Last et al. 2016). Generation length is estimated at 20 years based on age data from Maculabatis astra (Jacobsen 2007).
Taxon
Taxa
Pastinachus ater | (Macleay, 1883)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Recently, molecular data confirmed that the single, widespread Indo-“Pacific species, Pastinachus sephen consists of two species, the widespread P. ater and a more restricted P. sephen (Last et al. 2016a).
Taxon distribution as listed in assessment
The Broad Cowtail Ray occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific, although its exact distribution is uncertain due to confusion amongst Pastinachus species and recent taxonomic changes within the genus.
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
A2cd
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 Broad Cowtail Ray occurs throughout UAE coastal waters. The exact distribution is uncertain due to confusion amongst Pastinachus species and recent taxonomic changes. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980 and recent surveys have detected it in the area. Cowtail rays are regularly discarded in the Arabian Gulf and Sea of Oman. A large part of the species' regional distribution (namely, India and Pakistan) is under extremely intense and increasing demersal fishing pressure. It is not known how individuals occupying the UAE are connected with the broader population of the Arabian Seas region, and there is no information available to suggest that its population status differs in the UAE as compared to other parts of its range in the region. Given the threats faced by this species in other parts of the Arabian Seas region, and ongoing threats from discarding and habitat loss in the UAE, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 60 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
Criteria system
Criteria system specifics
IUCN v3.1
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
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Carcharhinus dussumieri | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

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
Yes
Habitat
Habitat details as listed in assessment
The Whitecheek Shark is a small species of carcharhinid shark that is common in inshore waters over soft substrates at depths of 0-100 m (Weigmann 2016). It reaches a maximum size of 114 cm total length (TL) (Raeisi et al. 2017). Size at birth is around 28-40 cm TL. This species is placental viviparous and produces litters of 2-5 each year. A study conducted off Iran in the Arabian Gulf reported a longevity of 8 and 13 years for males and females, and both females and males matured at lengths between 60 to 68 cm (Raeisi et al. 2017). Age at maturity data are not available for this species, but the Atlantic Sharpnose Shark (Rhizoprionodon terraenovae), which reaches a similar maximum size of 96 cm TL (Carlson and Baremore 2003), is applied as a proxy for age at maturity (3-4 years for females and 2-3.5 years for males). When applying an age at first reproduction of 3 years and longevity of 13 years, its estimated generation length is 8 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Taxon
Taxa
Carcharhinus dussumieri | (Müller & Henle, 1839)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Carcharhinus dussumieri is part of the Carcharhinus seali-dussumieri group that has been revealed to consist of five species: C. dussumieri and C. sealei have recently been re-described, C. coatesi and C. tjutjot have been resurrected as valid species, and a new species, C. humani has been described (White 2012, White and Weigmann 2014).
Taxon distribution as listed in assessment
The Whitecheek Shark occurs throughout UAE waters. Globally, it occurs from the northern Arabian Sea in the Arabian Gulf to the southeast coast of India. Bonfil (2003) reported this species from the lower Red Sea and Gulf of Aden, but these records may have been of Human's Whaler Shark (Carcharhinus humani), which was only recently described from this area (White and Weigmann 2014).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
A2cd
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 Whitecheek Shark is common throughout UAE inshore waters. Little specific data are available for this species in the UAE. It has a relatively low reproductive capacity, which causes it to be susceptible to over-exploitation, but it remains common in the Arabian Gulf. It is apparently highly migratory, and has slow life history characteristics including low fecundity and a low annual rate of population increase. Considering this, the species has a low capacity to recover from even moderate levels of exploitation. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 50-70% over the past three generation lengths, or about 24 years. It is listed as Endangered A2cd.
Criteria system
Criteria system specifics
IUCN v3.1
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
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. Marine habitats in the Arabian Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Gerres macracanthus | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

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
Yes
Habitat
Habitat details as listed in assessment
This species inhabits shallow, inshore waters over sandy bottoms and in estuaries. It occurs singly or in schools (Iwatsuki et al. 1996). The maximum length is 30 cm (Kuiter and Tonozuka 2001).
Taxon
Taxa
Gerres macracanthus | Bleeker, 1854
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is distributed throughout UAE waters (Iwatsuki et al. 2015). Globally, it is widespread in the Indo-Pacific (Venkataraman and Badrudeen 1975, Kottelat et al. 1993).
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 demersal, inshore species occurs throughout UAE waters. Fishing activity is not known to be causing population declines at this time. There are no known major threats; therefore, it is listed as Least Concern in the 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
Fishing activity is not known to be driving declines in the UAE at this time.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Commicarpus helenae | UAE National Red List of Vascular Plants

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 perennial species can grow up to 40 cm in height (Jongbloed et al. 2003). It has round to triangular leaves, club-like fruit and pink or red-purple flowers which are present between March and June (Jongbloed et al. 2003). The plant is generally recorded as growing within wadis and plantations, in addition to the foothills of mountains (Jongbleod et al. 2003, MEW 2010).
Taxon
Taxa
Commicarpus helenae | (Romer & Schultes) Meikle
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
The taxonomy of this widespread species across the global range may merit some revision. Specimens from Oman appear to differ substantially in leaf form from those found on St Helena.
Taxon distribution as listed in assessment
Within the UAE, this species is known to occur in east coast plantations in addition to Masafi, Khatt and Wadi Hiluw in the north and the north-east of the UAE (Jongbloed et al. 2003). Globally, this species is native to Africa, western Asia, the Arabian Peninsula and India (Board of Trustees, RBG Kew 2019).
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 is generally described as rare, it appears to have a somewhat widespread distribution within the north and northeast of the UAE, in addition to along the east coast. Therefore, it is currently assessed as Least Concern, pending further detailed distribution data and investigation into potential threats to this species - this may warrant a change in category.
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 is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Dodonaea viscosa | UAE National Red List of Vascular Plants

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
The species is found in wadis, wadi banks, and on hillsides. In the Ru'us al-Jibal, it is found in flat wadis and stunted among rocks on open plateaux and gentle slopes (Feulner 2011). It is a perennial small shrub that can grow to more than 2.0 m in height (Feulner 2016) but 0.5 m is more common (Jongbloed et al. 2003).
Taxon
Taxa
Dodonaea viscosa | Jacq.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is common and widespread in the eastern parts of the UAE, in the Hajar Mountains and the Ru'us al-Jibal, and also found south to Jebel Hafeet (Jongbloed et al. 2003, MEW 2010, Feulner 2011; <a href=""http://data.rbge.org.uk/herb/E00436646"">RBGE Herbarium</a>). The species is a common ornamental and landscaping plant, and may also have been planted for medicinal use. The species is found across the southern hemisphere (Board of Trustees, RBG Kew 2019).
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 is widespread and common in northeastern parts of the UAE. Therefore, it qualifies 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
It is not known to be browsed by goats and camels (Jongbloed et al. 2003). The current threats to this species are currently unknown.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Strix butleri | 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
There is no information available on the habitat requirements and ecology of this species in the UAE. In Oman, it occurs in rocky wadis with scattered trees, surrounded by cliffs and steep mountain slopes (Robb et al. 2013). It is likely that is requires cliffs for nesting (Robb et al. 2013).
Taxon
Taxa
Strix butleri | (Hume, 1878)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Strix butleri;was previously listed as;S. omanensis;in del Hoyo and Collar (2014) based on the description under this name by Robb;et al. (2013).;S hadorami;(Kirwan, Schweizer & Copete, 2015) was previously listed as;S. butleri;in del Hoyo and Collar (2014) and before.Recent genetic and morphological analyses have revealed that the type specimen of S. butleri -;the geographical provenance of which is open to doubt - differs significantly from all other specimens previously ascribed to this species, indicating (despite the lack of vocal data definitively linked to the same population as the type) that two species are involved, principally because the degree of molecular differentiation is close to that in other taxa of Strix traditionally recognised as species, which led to populations of this species from S Oman to the Levant and E Egypt, which share the same morphology and vocalizations, being described as a separate species, Desert Tawny Owl S. hadorami.
Taxon distribution as listed in assessment
The status of this species in the UAE is not clear. Individuals were heard calling in Wadi Wurayah National Park (Fujairah Emirate) on several occasions in March 2015 and March 2017, suggesting that there might be a small resident population in the area (Pedersen et al. 2017).
Assessed status
Asessment status in full
Critically Endangered
Assessment status abreviation
CR
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
This recently rediscovered and little-known species is suspected to have a tiny population size within the UAE and so despite more research into this species being needed, it is listed here as Critically Endangered under criterion D.
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 is apparently no information available on potential threats to this little-known species.
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

Gallinula chloropus | 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 all kinds of permanent wetland sites (Jennings 2010). It particularly prefers freshwater marshy pools and lakes with abundant vegetation cover along the borders, floating and emergent vegetation, dense reeds and wet bushy areas near watercourses offering abundant hiding places (Richardson 1990, Jennings 2010, Aspinall and Porter 2011, R. Khan pers. comm.). Occasionally, it occurs in eutrophic water near dump sites, in saline habitats or mangroves. Recently, populations became established in artificial waterbodies (S. Alam (Dubai Municipality) pers. comm. 2019, R. Khan (Dubai Safari, Dubai Municipality) pers. comm. 2019). When foraging, it may venture into open water or dry habitats, such as crop fields and gardens near wetlands (Jennings 2010). There is no information available about its diet in the UAE; elsewhere it is omnivorous and opportunistic, its diet consisting of earthworms, crustaceans, molluscs, insects, spiders, small fish, tadpoles and occasionally birds eggs, as well as plant matter such as filamentous algae, moss and the vegetative parts of reeds and aquatic plants, as well as berries and fruits (del Hoyo et al. 1996). While the species forms small flocks during the non-breeding season, it becomes territorial and aggressive with the onset of the breeding season in early spring. The breeding season is very long; eggs have been recorded from January in the UAE until August on the Saudi Arabian coast of the Arabian Gulf, the majority of chicks have been observed between April and July (Jennings 2010). The nest is a bulky cup constructed from twigs and waterside vegetation, which is placed on floating or partially submerged objects on water, in reed beds or adjacent to water (del Hoyo et al. 1996, Jennings 2010). Clutches contain around eight, seldom up to 13 eggs (Jennings 2010). Part of the population in the UAE is migratory; individuals breed from eastern Europe to central Asia and move south towards the UAE or from September to December and return again from March to May (del Hoyo et al. 1996, Jennings 2010).
Taxon
Taxa
Gallinula chloropus | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Gallinula chloropus and G. galeata (del Hoyo and Collar 2014) were previously lumped as G. chloropus following Sibley and Monroe (1990, 1993).
Taxon distribution as listed in assessment
A breeding population recently colonised the country; the first successful breeding attempts were confirmed in April 1989 in Sharjah Emirate near Kalba and Sharjah City. Breeding has further been confirmed in Hatta Wadi and Al Marmoom Conservation Reserve (S. Alam (Dubai Municipality) pers. comm. 2019). The species has since been breeding regularly, but it is localised (Pedersen et al. 2017). The species also visits the UAE as a wintering species and migrant individuals occur on passage to and from the breeding grounds (Pedersen;et al. 2017). It is common at wetlands throughout the country, from the mountains at the border to Oman;to permanent water sites along the east and west coasts, as well as artificial lakes (Jennings 2010, Pedersen;et al. 2017, S. Alam in litt. 2019).
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 large and increasing breeding population in the UAE and it is assessed 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
In UAE the main threat to the species is development and infilling of wetland habitats (Aspinall 1996).The species is susceptible to avian influenza (Melville and Shortridge 2006, Gaidet et al. 2007) and avian botulism (Rocke 2006) and may be threatened by future outbreaks of these diseases.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
Aspinall (1996) listed 20-200 mature individuals, qualifying as CR, adjusted by one category to EN. There were very much fewer areas of suitable habitat at that time.
Verified entry
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Gelochelidon nilotica | 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 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).
Taxon
Taxa
Gelochelidon nilotica | (Gmelin, 1789)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
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).
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).
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
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.
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 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.
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