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

Jurinea berardioidea | 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 species is a perennial which grows in the form of a stemless leaf rosette, reaching up to 0.15 m in diameter (Jongbloed et al. 2003). It flowers between February and May and typically grows among rocks, but also in abandoned fields (Jongbloed et al. 2003).
Taxon
Taxa
Jurinea berardioidea | Diels
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs in the Ru'us al-Jibal Mountains in the UAE, typically above 800-900 m altitude (Jongbloed et al. 2003, Feulner 2011). The estimated EOO of this species is approximately 200 km<sup>2</sup>. Globally, this species occurs in the Middle East and Central Asia (Board of Trustees, RBG Kew 2018).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species occurs within a very restricted range in the UAE: the estimated Extent of Occurrence (EOO) is approximately 200 km<sup>2</sup>. The area of occupancy (AOO) is likely to be similarly restricted. In addition, it is only found at higher altitudes within this area and is considered to generally be rare, and subpopulations are small, perhaps with 20-30 individuals in a subpopulation. As such, any potential threats to this species could cause it to become threatened within a short space of time. The species is cautiously assessed as Near Threatened based on a presumed restricted population size and habitat availability in order to highlight threats or declines to this species.
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
Developmental expansion might impact the species in parts of its range.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
Whilst there are developmental threats in parts of the Ru'us al-Jibal that would not have been significantly present in 1996, these threats are generally at lower altitudes and are not significant. The species is thought have a similarly restricted population in 1996 and to have also qualified as NT at that time.
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Actiniopteris semiflabellata | 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 species is found in mountain areas, in silt between rocks (Jongbloed et al. 2003). It is a perennial species with creeping rhizomes, in addition to fan-shaped leaves with toothed edges (Jongbloed et al. 2003).
Taxon
Taxa
Actiniopteris semiflabellata | Pic.Serm.
Taxonomic Group
Plants
Taxonomic Group Level 2
Ferns and Allies
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is known from a single record in Wadi Limarit on the eastern slopes of the Hajar Mountains in Fujairah, southeast of Masafi; the locality given in Jongbloed et al. (2003) is incorrect (G.R. Feulner pers. comm. 2019). The distribution in the UAE is certainly under-recorded. Globally, this species has a wide distribution from southern Africa to Nepal (Board of Trustees, RBG Kew 2018). It occurs in adjacent parts of the Hajar Mountains in Oman (Jongbloed et al. 2003).
Assessed status
Asessment status in full
Data Deficient
Assessment status abreviation
DD
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 only known from a single locality in the Hajar Mountains within the UAE. However, detailed distribution data is lacking and the species is easily overlooked. As such, it is difficult to accurately assess this species. It is therefore categorised as Data Deficient.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There are no known threats.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Acridocarpus orientalis | 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
A perennial, woody, branched shrub, up to 2(-6) m in height that flowers in April-June in addition to October and November (Jongbloed et al. 2003). In its Arabian Peninsula range, the species is found in semi-desert bushland, in rocky places, particularly in wadis, from 100-700 m asl (Board of Trustees, RBG Kew 2019).
Taxon
Taxa
Acridocarpus orientalis | A.Juss.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species is restricted to a single wadi (Fawzi and Ksiksi 2012, Ksiksi et al. 2012): Wadi Tarabat, a valley in the northern foothills of Jebel Hafeet in Abu Dhabi Emirate (Jongbloed et al. 2003). The native range of this species is reported as north-east Somalia, the Arabian Peninsula, and Iran (Board of Trustees, RBG Kew 2019). Within Oman, the species is known from a number of localities in the Hajar Mountains, including Jebel Akhdar, Muscat and north to the Musandam Peninsula.
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
Within the UAE, this species is restricted to Wadi Tarabat in the northern foothills of Jebel Hafeet in Abu Dhabi Emirate. It has an extent of occurrence (EOO) and an area of occupancy (AOO) of less than 8 km<sup>2</sup>. Around 200 individuals are known, however, the population trend is not known, nor whether there is a decline in the number of mature individuals or habitat quality. Jebel Hafeet has been subject to habitat degradation as a result of livestock grazing, however fencing to restrict grazing in Wadi Tarabat was implemented in 2005, and again around 2017, and all known individuals of this species occur within this fenced area. The species is assessed as Endangered (EN D) as a result of its restricted population size (&lt;200 mature individuals). Further research is needed to understand the current situation for this species, and continued conservation action is required. The species potentially qualifies as CR as a result of the restricted EOO and AOO, if a continuing decline is shown. The species does occur as significant wadi and mountain slope populations in adjacent parts of Oman to the east and south. No immigration is known in recent years and therefore no regional adjustment is required.
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
Jongbloed et al. (2003) stated that the species is not grazed by livestock, however, the Jebel Hafeet area has been heavily degraded by livestock and introduced animal grazing.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
This species naturally occurs within a restricted distribution, which is not believed to have been altered between 1996 and the present.
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Achyranthes aspera | 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?
Incomplete
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This is a perennial species that flowers from December to April. It can be found in plantations and moist disturbed areas (Jongbloed et al. 2003, MEW 2010), in addition to oases. Across its range, it is common species of disturbed places, very variable, much-branched, 1-“6 ft. high, sometimes subscandent, sometimes woody (Board of Trustees, RBG Kew 2018). This species is also known to be spread by livestock and other animals.
Taxon
Taxa
Achyranthes aspera | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is found widespread in several scattered locations throughout the UAE (Jongbloed et al. 2003, MEW 2010). It is recorded from Abu Dhabi Emirate (Brown and Sakkir 2004). The species is globally distributed in the tropical and subtropical Old World and widely introduced in the Americas and in Europe (Board of Trustees, RBG Kew 2018). The origin of the species is uncertain, and it is possibly native to Southeast Asia and/or Africa (BioNET-EAFRINET 2011, CABI 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 found widespread in several scattered locations throughout the UAE (Jongbloed et al. 2003, MEW 2010, Brown and Sakkir 2004), although the full distribution is not well known. It occurs in agricultural land and in plantations, and is unlikely to face significant threats, and is considered Least Concern. However, further research is required to confirm the origin of this species in the UAE given the types of habitat that this species occurs in, and the medicinal and other uses of the species, suggesting that it may have been introduced through cultivation. The indigenous distribution of the species is uncertain, and it is possibly native to Southeast Asia and/or Africa.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There are no major threats.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Delphinus delphis | UAE National Red List of Mammals: Marine and Terrestrial

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
Mostly an offshore, deep-water species. Occurs in groups of 100 to over 3,000 individuals in the wider region. Feeds on small pelagic fish (Baldwin et al. 1999).
Taxon
Taxa
Delphinus delphis | Linnaeus, 1758
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
Taxonomic Notes
Until recently, two species were recognised in the genus Delphinus: the Short-beaked Common Dolphin (D. delphis) and the Long-beaked Common Dolphin (D. capensis), as described by Heyning and Perrin (1994). The morphological differences between D. delphis and D. capensis in the North Pacific (Heyning and Perrin 1994) were supported by molecular evidence from both mitochondrial and nuclear markers (Rosel et al. 1994). However, the genus exhibits a great deal of morphological variation globally and the criteria used to distinguish between the two species in the North Pacific appear not to apply elsewhere (Best 2007). In South Africa, Samaai et al. (2005) found that based on skull morphology the majority of specimens belonged to D. capensis, however two specimens were within the range for D. delphis from the North Pacific, and a third specimen fell between the ranges for D. delphis and D. capensis (Samaai et al. 2005). The same molecular markers that were used to differentiate the two sympatric species in the North Pacific failed to reveal any genetic distinction between the described morphotypes in South Africa (Best 2007). Subsequently, Cunha et al. (2015), in a global analysis of Delphinus which included nine specimens from the west coast of South Africa (eastern South Atlantic), concluded that all specimens analysed from the Atlantic Ocean belonged to D. delphis, and that D. capensis was not a genetically valid species. In 2016 the Society for Marine Mammalogy Committee on Taxonomy removed Delphinus capensis from its accepted list of marine mammal species and now recognises all Common Dolphins globally as belonging to a single species, Delphinus delphis (Committee on Taxonomy 2020). It recognises the following subspecies: <ul> <li>D. d. delphis Linnaeus, 1758. Common Dolphin</li> <li>D. d. bairdii Dall, 1873. Eastern North Pacific Long-beaked Common Dolphin</li> <li>D. d. ponticus Barabash, 1935. Black Sea Common Dolphin</li> <li>D. d. tropicalis van Bree, 1971. Indo-Pacific Common Dolphin</li> </ul> Cunha et al. (2015) noted that because the sympatric or parapatric Long-beaked and Short-beaked Common Dolphins off California in the eastern North Pacific appear not to interbreed, the Long-beaked Common Dolphins might eventually be described and recognised as a separate species, D. bairdii. Some researchers have considered the Long-beaked Common Dolphins in the Indo-Pacific, which has an exceptionally long beak, to constitute a separate species, D. tropicalis (Van Bree and Gallagher 1978; Rice 1998). However, another morphometric study concluded that that form should be considered a subspecies (Jefferson and Van Waerebeek 2002) and it is currently recognised as such, D. delphis tropicalis. The non-concordance of morphological and genetic data for Common Dolphins has caused much confusion and a rigorous global taxonomic study of the genus is needed. Further phylogenetic analyses are necessary to resolve the controversies surrounding the classification and nomenclature. More changes to Delphinus taxonomy should be expected.
Taxon distribution as listed in assessment
This species is relatively poorly known in the UAE. There are skeletal remains from western and eastern Abu Dhabi, though confirmed live sightings have not yet been recorded in the Arabian Gulf region of the UAE. There have been no remains found in the last 15 years, apart from an old skull from Umm Al Qawain in 2014/15 that was identified as this species by the <a href=""http://www.uaedolphinproject.org/"">UAE Dolphin Project</a>. It has been recorded on numerous occasions off the east coast of Fujairah during surveys in 2017-2018 by the Fujairah Whale and Dolphin Research Project, including relatively large groups (up to 100 individuals) in both shallower (50 m) and deep water (to at least 800 m). It is commonly recorded in other parts of the Gulf of Oman to the south of the UAE border (Baldwin 2005). A stranding has been reported from Khor Kalba, Sharjah. This species ranges in the Indo-Pacific from at least the Red Sea/Somalia to western Taiwan/southern China and Indonesia, including the Gulf of Thailand (Hammond et al. 2008a).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2018
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
There have been no sightings of live animals in the Arabian Gulf in recent years and no records of any strandings from Abu Dhabi in the past ten years, but there are numerous records of skeletal remains from the area. It is not clear if this means there has been a significant population reduction in the Gulf and over what time period that happened. The only confirmed recent records include multiple sightings of relatively large groups (up to 100 individuals) sighted in both shallower (50 m) and deep water (800 m) off the east coast of Fujairah. The population size and trend are unknown, hence this species is assessed as Data Deficient. No regional adjustment is made to the Data Deficient assessment.
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
The main threats to cetaceans in UAE waters include: incidental mortality in trawl, drift and anchored gill nets, depletion of prey populations (due in part to commercial overfishing); ship and boat strikes, disturbance due to underwater noise (including that from vessel traffic, drilling, piling, military operations and seismic activity related to offshore oil and gas exploration). Inshore and shallow-water species are further potentially threatened by entanglement in abandoned fishing gear, coastal development including port and harbour construction, dredging, land reclamation, residential and tourist development, and pollution (especially hydrocarbons). A lack of information (e.g. population size and trend, the location of critical habitats, and feeding ecology) hinders the development of appropriate conservation actions, but this should be used as an excuse for inaction.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The backcasted 1996 assessment for this species is Data Deficient which matches the listing given by Hornby (1996) albeit that this was based on a different taxonomic concept.
Verified entry
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Stenodactylus arabicus | UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species is found on soft windblown sand, in areas with dunes or sand sheets and sparse or scattered vegetation from sea level to 300 m asl (Gardner 2013). It is a ground-dwelling nocturnal species that is abundant in suitable habitat. Females lay clutches of a single oval egg during the warmer months from May to October (Gardner 2013). Arnold (1977) reports it from fine windblown sand, but that it is also found on firmer substrates. They predate on small insects. There is ongoing habitat loss in coastal areas, but this is not significant given the wide range in the UAE.
Taxon
Taxa
Stenodactylus arabicus | (Haas, 1957)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxonomic Notes
In a recent study, Nazarov et al. (2018) described a new species from Iran and proposed the validity of the genus Trigonodactylus Haas, 1957. However, since Stenodactylus is a monophyletic genus of similar age to the other geckos and the study by Nazarov et al. (2018) does not include S. pulcher, we consider that the new genus is not justified and therefore we use the taxonomy proposed by Metallinou et al. (2012) and Metallinou and Carranza (2013).
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is widespread throughout sandy desert areas of the UAE, from Ras al Khaimah to as far southwest as Jebel Dhanna in the Gharbia (Gardner 2013) and As Sila in the west, and inland as far as the edge of the mountains, including from the Al Khatim area and towards Um az Zumul on saline plains and sabkhas. It has also been recorded from Sir Bani Yas Island. It occurs from sea level to 300 m asl.This species is restricted to the Arabian Peninsula, present in Saudi Arabia, Qatar, central Yemen, southern Kuwait, southern and central Oman and the United Arab Emirates (Metallinou and Carranza 2013, Carranza et al. 2018). It is found from sea level to 500-600 m asl.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2018
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
Within the United Arab Emirates, this species is widespread from the sandy deserts of Ras al Khaimah to as far southwest as Jebel Dhanna in the Gharbia, and inland as far as the edge of the mountains. This species is listed as Least Concern in view of its wide range within the UAE, lack of significant threats, and presence in several protected areas throughout its range. This taxon is not a non-breeding visitor, and it is presumed that any immigration from populations outside the UAE is not significant, and therefore there is no adjustment to the Category according to the IUCN regional and national Guidelines (IUCN 2012).
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There are threats in coastal areas, but these are not significant.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Pristurus rupestris | UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles

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 rocky wadis, scree slopes, gravel plains, mountainsides, and is also able to thrive in proximity to humans, living in gardens, farming areas and orchards, and climbing on walls (Gardner 2013). It is a territorial diurnal species that perches on stones, walls or tree trunks near their refuge. Reproduction can occur throughout the year and females lay clutches of a single egg (Gardner 2013).
Taxon
Taxa
Pristurus rupestris | Blandford, 1874
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxonomic Notes
Badiane et al. (2014) found the taxon Pristurus rupestris to contain two genetically well-differentiated species: an eastern clade (=Pristurus rupestris rupestris) that occurs in coastal Iran and the Hajar Mountain range in northern Oman and the eastern UAE, and a western clade distributed from coastal central Oman, through Yemen, Saudi Arabia and up to southern Jordan, with two possible names available: Pristurus guweirensis Haas, 1943 (=P. r. guweirensis elevated to species) or Pristurus migiurtinicus Scortecci, 1933 (synonymized with P. rupestris by Loveridge (1947). Further comparison of material from the type localities of Pristurus guweirensis and Pristurus migiurtinicus is required to confirm which is the applicable name for the western clade taxon, and Badiane et al. (2014) refer to the western clade as Pristurus sp. 1.The resulting P. rupestris concept includes two nominal subspecies, P. r. rupestris (endemic to the Hajar Mountains) and P. r. iranicus (endemic to coastal Iran). P. r. iranicus is, however, morphologically identical to P. r. rupestris and recognizing it has been found to render P. r. rupestris paraphyletic, and it is possible that work in the near future may synonymize it within P. r. rupestris (S. Carranza pers. comm. 2018).Within the Hajar Mountains, populations are a species complex that requires further study, and the taxonomic identity of subpopulations are likely to change (Garcia-Porta et al. 2017, Carranza et al. 2018).
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is widespread throughout the Hajar Mountains and surrounding gravel plains from sea level to 1,300 m asl (Badiane et al. 2014, Burriel-Carranza et al. in press). It has been introduced to the offshore islands and populations were introduced incidentally to coastal areas, including Ras al Khaimah, Ajman, Sharjah, Dubai and Abu Dhabi city areas (Gardner 2013).Globally, this species is now considered to be endemic to the Hajar Mountains of UAE and Oman (P. r. rupestris) and coastal areas of southern Iran (P. r. iranicus (Badiene et al. 2014, Garcia-Porta et al. 2017, Carranza et al. 2018).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2018
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
Within the United Arab Emirates, the species is widespread throughout the Hajar Mountains and surrounding gravel plains, and it has been very widely introduced inadvertently elsewhere within the country. The species is listed as Least Concern in view of its wide distribution, presumed large population, the absence of threats, and ability to adapt to habitat modifications. Its population is not in decline and hence it does not qualify for listing in a threatened category. This taxon is not a non-breeding visitor, and it is presumed that any immigration from populations outside the UAE is not significant, and therefore there is no adjustment to the Category according to the IUCN regional and national Guidelines (IUCN 2012).The species should be reassessed when the taxonomic revision of this species complex is finalised.
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 appear to be no major threats to this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Trachydactylus hajarensis | UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles

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 mountainous and rocky areas, where it lives on stony plains, in wadi beds, and on scree slopes, from sea level to 1,000 m asl. The species is often encountered in and around cultivated land within its range and under construction debris. It is a nocturnal species that is mostly encountered on the ground, although they are excellent climbers and can be encountered climbing on trees. By day, they are most often encountered sheltering under stones. Breeding occurs throughout the warm season with females laying one or two, thin-shelled and slightly oval eggs at four-week intervals (Gardner 2013).
Taxon
Taxa
Trachydactylus hajarensis | (Arnold, 1980)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxonomic Notes
This species is genetically highly variable and may represent a species complex (De Pous et al. 2015).
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is widespread throughout the Hajar Mountain range from sea level to 1,000 m asl (Gardner 2013, Burriel-Carranza et al. in press).Globally the species is endemic to the Hajar Mountains from the Musandam Peninsula of Oman through the United Arab Emirates to the south of Oman (Pous et al. 2005, Gardner 2013, Carranza et al. 2018). It has also been recorded on Masirah Island, Oman (Carranza et al. 2018).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2018
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
Within the United Arab Emirates, this species is widespread throughout the Hajar Mountain range. The species is listed as Least Concern in view of its wide distribution range, presumed large population, and because it is unlikely to be declining fast enough to qualify for listing in a threatened category. This taxon is not a non-breeding visitor, and it is presumed that any immigration from populations outside the UAE is not significant, and therefore there is no adjustment to the Category according to the IUCN regional and national Guidelines (IUCN 2012).
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 species is likely to be impacted by construction in parts of its range.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Telescopus dhara ssp. dhara | UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
In the United Arab Emirates, the species is found in rocky, mountainous areas from sea level to 600 m asl. It is a crepuscular and nocturnal species that feeds on geckos, birds, bats and rodents (Gardner 2013). It has been recorded to be active and hunting on cold winter nights (Gardner 2013). The mating season is in summer and spring. Its oviparous with female laying a clutch of 6-20 eggs (Gardner 2013).
Taxon
Taxa
Telescopus dhara ssp. dhara | (Forskål, 1775)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Subspecies
Taxonomic Notes
Following Crochet et al. (2008), the distinct forms Telescopus dhara obtusus and T. d. somalicus, sometimes treated as full species, are provisionally retained as subspecies of T. dhara pending systematic treatment to clarify their appropriate status.
Taxon distribution as listed in assessment
In the United Arab Emirates, this subspecies is known from the Hajar Mountains (Gardner et al. 2009, Burriel-Carranza et al. in press), from sea level to 600 m asl.Globally, the subspecies range is restricted, following (Crochet et al. 2008) to the Arabian Peninsula, mostly in the mountainous periphery (Saudi Arabia, Oman (Carranza et al. 2018), UAE, Yemen), west to the Sinai Peninsula, north to Israel (close to the southern West Bank of Palestine) and Jordan.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2018
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
In the United Arab Emirates, this subspecies is known from the Hajar Mountains. The species is listed as Least Concern as there are no known significant direct threats to the species that may cause a decline in its population size presently or in the near future. The majority of the species' habitat in its range remains suitable and is unlikely to be altered in the near future. This taxon is not a non-breeding visitor, and it is presumed that any immigration from populations outside the UAE is not significant, and therefore there is no adjustment to the Category according to the IUCN regional and national Guidelines (IUCN 2012).
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There are limited threats to the species, which are restricted to the outer limits of its distribution range within the United Arab Emirates, with no known direct impact on the species. Potential threats to the species are quarrying and residential development. The species may be persecuted, as with all snakes.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Uromastyx aegyptia ssp. microlepis | UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles

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 subspecies is found in sandy or gravel plains, interdunal plains and flat wadi beds with scattered vegetation (Gardner 2013). They are more frequently encountered on cemented sandstone or on hard surface plains, and dependent on vegetation cover. A ground-dwelling and diurnal subspecies. They prefer high temperatures and are most active during summer, while on cool winter days they may not leave the burrows at all (Gardner 2013). Adults are vegetarian and are able to survive on poor quality forage (Gardner 2013). They feed on a broad range of plants, including grasses and herbs, but tend to avoid Tetraena qatarense despite its abundance (Gardner 2013). Individual lizards may move between several non-exclusive burrows (Gardner 2013). Mating occurs from spring to summer, and females lay a clutch of 12-30 eggs in the burrow.
Taxon
Taxa
Uromastyx aegyptia ssp. microlepis | Arnold, 1980
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Subspecies
Taxonomic Notes
Due to low levels of genetic differentiation between members of the Uromastyx aegyptia species group (considered to include U. aegyptia, U. leptieni, U. microlepis and U. occidentalis), Wilms et al. (2007) and Tamar et al. (2018) recognize U. aegyptia as a single species with three subspecies: U. a. aegyptia, U. a. leptieni and U. a. microlepis.The relationship of U. occidentalis, which was not included in the genetic analysis, to U. aegyptia remains in need of clarification, however Wilms et al. (2007) continue to recognize it as a full species due to its geographical separation from the remaining U. aegyptia-group taxa.
Taxon distribution as listed in assessment
In the United Arab Emirates, this subspecies is found in the south and west of the Abu Dhabi Emirate (Gardner 2013, Burriel-Carranza et al. in press). The subspecies occurs from sea level to 200 m asl. in the United Arab Emirates.The subspecies is widespread in the Arabian Peninsula including Saudi Arabia, Yemen, Oman, Qatar, Bahrain and Kuwait, extending eastwards to Iraq and coastal Iran, and north to Jordan and Syria.
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
A2abcd+4abcd
About the assessment
Assessment year
2018
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
In the United Arab Emirates, this subspecies is found in the south and west of the Abu Dhabi Emirate. The extent of occurrence (EOO) is moderately large, approaching 45,375 km<sup>2</sup>, however, the area of occupancy (AOO) is restricted, at just 324 km<sup>2</sup>. Its primary habitat, sandy or gravel plains, is impacted by a range of threats such as urban development, oil and gas exploitation, etc, which may result in local extirpations. As a result, the subspecies is assessed as Vulnerable (VU A2abcd+4abcd) based on observed and inferred (declines in AOO and habitat quality, and levels of exploitation) population decline in the past and ongoing that exceeds 30%. The population is suspected to have undergone a decline of at least 30% in the previous three generations (30 years) as a result of habitat loss, and a future decline of at least 10% is suspected as a result of ongoing habitat loss. The subspecies faces a wide range of threats in addition to urban development, including loss of vegetation cover, and persecution. The subspecies is unlikely to be declining fast enough for this subspecies to qualify for listing in a more threatened category and viable populations are present in several Protected Areas. This taxon is not a non-breeding visitor, and it is presumed that any immigration from populations outside the UAE is not significant, and therefore there is no adjustment to the Category according to the IUCN regional and national Guidelines (IUCN 2012).Conservation actions are required for this subspecies. Education is required to ensure that the existing Federal Law of the United Arab Emirates that prohibits the hunting, collection, and disturbance of the species is implemented, and habitat protected. Further research is required, including habitat and population monitoring.
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
Although a widespread the subspecies, it is not evenly distributed over its range, being dependent on sandy or gravel plains for its burrows, and generally avoiding soft sand or dunes (Gardner 2013). As a result, it makes the subspecies vulnerable to threats such as urban development, road construction, oil and gas exploitation etc, which may result in local extirpations. Over-grazing on the plains leads to the loss of vegetation cover, whilst tree-planting impacts the subspecies elsewhere. The subspecies is also subject to persecution.The combination of extended drought duration and over-grazing (even in protected areas), leading to the loss of essential vegetation cover, is hard to estimate but may be significant.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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