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LC

Assessment ID
330163
Taxon name
Pristurus minimus
Arnold, 1977
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Pristurus minimus
Arnold, 1977
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
sphaerodactylidae
Genus
Pristurus
Species
minimus
Species authority
Arnold, 1977
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species is listed as Least Concern as it is moderately widespread in the UAE and locally abundant and subject to no major threats. 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).
Assessment details
Year assessed
2018
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species occurs inland from Sharjah south to Abu Dhabi inwards to Al Ain (Gardner 2013) from sea level to 300 m asl, with an isolated record also known from the vicinity of Khor Fakkan on the east coast (Böhme and Leptien 1990, Gardner 2013, Burriel-Carranza et al. in press).Globally, the species is endemic to the Arabian Peninsula, where it has been recorded from the United Arab Emirates, Oman (including Masirah Island) and eastern Yemen (Arnold 1977, 1980; Carranza et al. 2018). There is a questionable record from the northern Empty Quarter in Saudi Arabia. It is very localised in Yemen, where only one record is known.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
The species is mostly found in sandy plains with clumps of grass or other low shrubby vegetation. It has also been recorded from a rocky hillside on the east coast of the United Arab Emirates (Gardner 2013).It is predominantly a diurnal species which may be active during the summer at night. It preys on small insects including termites and ants (Gardner 2013). Females lay a single egg and reproduction apparently occurs throughout the year (Gardner 2013).
Threats and conservation measures listed
Threats listed in assessment
There are no major threats to this species.
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE
Assessment ID
330161
Taxon name
Asaccus gallagheri
(Arnold, 1972)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Asaccus gallagheri
(Arnold, 1972)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
phyllodactylidae
Genus
Asaccus
Species
gallagheri
Species authority
(Arnold, 1972)
Taxonomic notes and synonyms listed
Populations from the Eastern Hajar Mountains in Oman are now referred to A. arnoldi (Simó-Riudalbas et al. 2018).
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In the United Arab Emirates, this species is restricted to the Hajar Mountains, with an extent of occurrence (EOO) of 3,165 km<sup>2</sup> and an area of occupancy (AOO) of 168 km<sup>2</sup>. Populations are thought to be stable, and there are no known widespread threats. The species is assessed as Least Concern. 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).
Assessment details
Year assessed
2018
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, the species occurs throughout the Hajar Mountains from sea level to 600 m asl (Gardner 2013, Burriel-Carranza et al. in press). Globally, the species is endemic to the central and western Hajar Mountains, ranging from the Musandam Peninsula in Oman through the United Arab Emirates to Jebel Akhdar in Oman (Gardner 2013, Carranza et al. 2018). It has been found from sea level up to 1,700 m asl.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
Rocky terrain in mountains and coastal wadis, and on small cliffs on open hillsides (Gardner 2013) from sea level to 600 m asl. The species has also been encountered on stony walls surrounding farms, on the external walls of houses and abandoned buildings within their distribution range. It is a small nocturnal species that predates on invertebrates. Breeding season is during spring and summer, with females laying a single egg that is glued to the surrounding surface at intervals of four weeks (Gardner 2013). The species is sexual dimorphic in that the adult males have a yellow tail and females a white tail with dark bands.
Threats and conservation measures listed
Threats listed in assessment
There are no major threats to the species, except for localised quarrying which will not have a significant impact on the population throughout its area of occurrence.
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE
Assessment ID
330160
Taxon name
Echis omanensis
Babocsay, 2004
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Echis omanensis
Babocsay, 2004
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
viperidae
Genus
Echis
Species
omanensis
Species authority
Babocsay, 2004
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Within the United Arab Emirates, this species occurs throughout the Hajar Mountains, and was recently recorded from Jebel Hafeet. The species is listed as Least Concern in view of its wide range and lack of significant threats. 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 population density may be increasing where irrigation projects occur.
Assessment details
Year assessed
2018
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species occurs throughout the Hajar Mountains (Babocsay 2004, Gardner 2013, Burriel-Carranza et al. in press) from sea level to 1,000 m asl. The species also occurs in Jebel Hafeet near Al Ain.This species is endemic to the Hajar Mountain of Oman and the United Arab Emirates (Egan 2007). The animals are seldom found above 800 m asl.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
This species is common in mountain wadis and surrounding rocky terrain, especially in areas having permanent or semi-permanent surface water. They are primarily nocturnal hunters but in cool weather they can be found on bedrock or gravel beside surface water or damp hollows, where they may bask, but also wait in ambush. Their diet consists of small vertebrates, particularly toads, and they emerge in wadi beds during or after light rain to feed on toads which emerge at the same time. Individual snakes have been observed to maintain territories and regular resting place over several years. They are presumably oviparous.
Threats and conservation measures listed
Threats listed in assessment
There are no widespread threats, although some populations may be impacted by localized quarrying and major infrastructure projects within their habitat. Over-extraction of water may have an impact on the species within certain parts of its range. It is persecuted throughout most of its range due to human fear of this venomous species.
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE
Assessment ID
330157
Taxon name
Trapelus flavimaculatus
Rüppell, 1835
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Trapelus flavimaculatus
Rüppell, 1835
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
agamidae
Genus
Trapelus
Species
flavimaculatus
Species authority
Rüppell, 1835
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Trapelus flavimaculatus is listed as Least Concern in view of its wide distribution within the UAE, presumed large population, and because it is unlikely to be declining fast enough to qualify for listing in a more 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).
Assessment details
Year assessed
2018
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
In the United Arab Emirates, this species has been recorded from the Sila area through the coastal deserts of Abu Dhabi to Ras Al Khaimah, and further inland around Sweihan and Al Ain (Gardner 2013, Burriel-Carranza et al. in press). The species has also been recorded along the east coast of the United Arab Emirates but is absent from the Hajar Mountains. The species is found from sea level to 400 m asl.This species is present in Saudi Arabia, Oman, Yemen, United Arab Emirates, Qatar, Bahrain and Kuwait.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
The species is found in open areas, where it basks in the branches of small Acacia and Prosopis trees, and on the ground in sandy areas. In the United Arab Emirates, this species occurs on stable sand and gravelly surfaces, usually with bushes and shrubs, on which it is found sunning itself (Arnold 1980, Gardner 2013). The species is also found in urban and rural gardens. In disturbed areas, heaps of stones and earth may be used for sunning (Arnold 1980). The breeding season is spring and summer. The females lay four to six eggs.
Threats and conservation measures listed
Threats listed in assessment
There are no widespread threats to this species, but there will be localised impacts from development, to which its habitat is particularly susceptible.
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE
Assessment ID
330121
Taxon name
Hydrophis lapemoides
(Gray, 1849)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Hydrophis lapemoides
(Gray, 1849)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
elapidae
Genus
Hydrophis
Species
lapemoides
Species authority
(Gray, 1849)
Taxonomic notes and synonyms listed
This species is sometimes treated under the genus Chitulia.
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Presence of this species is confirmed within the United Arab Emirates marine territorial waters, where it occurs in both the Arabian Gulf and in the Gulf of Oman. In contrast with some other sea snakes in UAE waters, this species appears to be relatively abundant, and it breeds in the UAE.Whilst more research and monitoring is required, this species is considered Least Concern as the known threats are unlikely to be causing a significant decline at present.
Assessment details
Year assessed
2018
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Presence of this species is confirmed within the United Arab Emirates marine territorial waters (Soorae et al. 2006, 2010; Buzás et al. 2018). It is found in both the Arabian Gulf and in the Gulf of Oman. Breeding has been confirmed in the waters off the east coast (Géczy et al. 2017, Buzás et al. 2018). On the east coast, it is found from 2.7-9.7 km offshore (Géczy et al. 2017, Buzás et al. 2018). The depth range is not certain, but likely to be found to c.45 m depth along the east coast. Museum records are available for the UAE in the Al Mayya Sanctuary, Fujairah. Recent museum specimens include those from Muscat, Oman (Boulenger 1887), Arabian Gulf and Strait of Hormuz (Gasperetti 1988). The first museum specimens for the region were collected in Dubai and Sharjah (Arabian Gulf, UAE) by M.D. Gallagher in 1972 (Gasperetii 1988).Globally, this species is found in the Arabian Gulf eastwards to India and Sri Lanka (Culotta and Pickwell 1993, Heatwole 1999), and to the west coast of peninsular Thailand, Melanesia and Singapore (Rasmussen et al. 2010).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
This is a shallow-water species found over open sandy substrates in shallow water up to 45 m depth. Feed possibly on eels, goboids, and flatfish. In captivity, a wide range of fish are accepted (Egan 2007). The species breeds in UAE waters.
Threats and conservation measures listed
Threats listed in assessment
There are no widespread threats. As with all sea snakes, this species is vulnerable to indirect threats from habitat loss and climate change throughout its range. The impact of oil spills and other marine pollution requires further study. They have the potential for entanglement in marine litter and abandoned fish traps (garghoor).
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE
Assessment ID
330120
Taxon name
Hydrophis platurus
(Linnaeus, 1766)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Hydrophis platurus
(Linnaeus, 1766)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
elapidae
Genus
Hydrophis
Species
platurus
Species authority
(Linnaeus, 1766)
Taxonomic notes and synonyms listed
A recent molecular phylogenetic study of 39 sea snake species in 15 genera recovered Hydrophis as broadly paraphyletic with respect to several other genera (Sanders et al. 2013). Instead of erecting multiple new genera, the authors recommended dismantling the mostly monotypic genera Pelamis, Enhydrina, Astrotia, Thalassophina, Acalyptophis, Kerilia, Lapemis and Disteira, and recognizing a single genus, Hydrophis, for these taxa (Sanders et al. 2013). This classification system avoids confusion and better reflects the history of recent and very rapid diversification of these snakes and are followed by most recent authors (e.g., Leviton et al. 2014, Lillywhite et al. 2014, Rasmussen et al. 2014, Ukuwela et al. 2014, D'Anastasi et al. 2016, Rezaie-Atagholipour et al. 2016, Udyawer et al. 2015, Mirtschin et al. 2017).A distinctive new subspecies of sea snake from inner-basin waters of Golfo Dulce, Costa Rica has been described (Bessesen and Galbreath 2017). The Yellow sea snake, Hydrophis platurus ssp. xanthos Bessesen & Galbreath, 2017 is diagnosed by a notably smaller body size and nearly uniform yellow colouration, which contrasts with the black and yellow striae and tail spots or bands typical of the species (Bessesen and Galbreath 2017).
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Presence of this species is confirmed within the United Arab Emirates marine territorial waters, where it occurs in both the Arabian Gulf and in the Gulf of Oman. In contrast with some other sea snakes in UAE waters, this species appears to be relatively abundant, at least on the east coast, and it breeds in the UAE marine area.Whilst more research and monitoring is required, this species is considered Least Concern as the known threats are unlikely to be causing a significant decline at present.
Assessment details
Year assessed
2018
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Presence of this species is confirmed within the United Arab Emirates marine territorial waters (Gasperetti 1988, Egan 2007, Soorae et al. 2006, Gardner 2013, Buzás et al. 2018), with confirmed records from the Arabian Gulf (from small numbers of strandings) and the Gulf of Oman, where it is primarily found up to 8.9 km offshore, but seen at 13.8, 34.5, 44 and 78 km offshore; as a pelagic species, it can be found anywhere within the EEZ (Géczy et al. 2017, Buzás et al. 2018). The depth range is not certain, but likely to be found to c.5 m depth, as this is a surface-dwelling species. Recent museum records are available for the UAE in the Al Mayya Sanctuary, Fujairah.Globally, this species is very widespread in the tropical parts of the Pacific and Indian Oceans between the 18-20'º C isotherms (Dunson and Ehlert 1971, Graham et al. 1971). It is known from the coasts of eastern Africa, north to the Arabian Gulf, east along the Asian coast of the Indian Ocean to the Pacific Ocean, northward to Japan and eastward to the western coasts of the Americas (Culotta and Pickwell 1993, Heatwole 1999). Currents occasionally carry the snakes into temperate waters, but these are almost certainly far from their breeding and feeding waters (Guinea et al. 2017). The species has been reported, from a small number of records, from Atlantic waters (Atlantic coast of Africa and the Caribbean coast of Columbia), which suggests that colonization of the Atlantic Ocean is a possibility (Lillywhite et al. 2018).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
This is a pelagic surface species, found to c.5 m depth in the UAE.Globally, this species is the most pelagic of the sea snakes, occurring in the open ocean well away from coasts and reefs, and may occur in coastal mangrove habitats (Guinea et al. 2017). This species is usually found in the 0-10 m range of the water column. In the open ocean, the snakes often occur in large numbers in association with long lines of debris.
Threats and conservation measures listed
Threats listed in assessment
As with all sea snakes, this species is vulnerable to indirect threats from habitat loss and climate change throughout its range (Rasmussen et al. in prep.). The impact of oil spills and other marine pollution requires further study. They have the potential for entanglement in marine litter. There are no known major threats to this species. Minor threats may include bycatch in fisheries, ghost fishing nets, and pollution, including oil spills (Guinea et al. 2017).
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE
Assessment ID
330119
Taxon name
Hydrophis ornatus
(Gray, 1842)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Hydrophis ornatus
(Gray, 1842)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
elapidae
Genus
Hydrophis
Species
ornatus
Species authority
(Gray, 1842)
Taxonomic notes and synonyms listed
This species has three subspecies: Hydrophis ornatus ornatus (Gray, 1942), Hydrophis ornatus godeffroyi Peters, 1873, and Hydrophis ornatus ocellatus Gray, 1849. The status of these subspecies is very uncertain, and the subspecies ocellatus is treated in this assessment as a separate distinct species (H. Cogger pers. comm. 2009). H. lamberti has been incorrectly considered a synonym of H. ornatus (Smith 1926). This species has also been treated under the genus Chitulia.
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Presence of this species is confirmed within the United Arab Emirates marine territorial waters, where it occurs in both the Arabian Gulf and in the Gulf of Oman. In contrast with some other sea snakes in UAE waters, this species appears to be relatively abundant, at least on the east coast, and it is assumed to breed in the UAE.Whilst more research and monitoring is required, this species is considered Least Concern as the known threats are unlikely to be causing a significant decline at present.
Assessment details
Year assessed
2018
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Presence of this species is confirmed within the United Arab Emirates marine territorial waters (Soorae et al. 2006, Buzás et al. 2018). It is found in both the Arabian Gulf and in the Gulf of Oman. Breeding is confirmed, as juveniles are found in the waters off the east coast (Géczy et al. 2017, Buzás et al. 2018). On the east coast, it is found up to 8 km offshore (Géczy et al. 2017, Buzás et al. 2018). The depth range is not certain, but likely to be found to c. 45 m depth along the east coast. Museum specimens from Muscat, Oman (Boulenger 1887), Arabian Gulf and Strait of Hormuz (Gasperetti 1988). Recent museum records are available for the UAE in the Al Mayya Sanctuary, Fujairah.Globally, this species is found in the Arabian Gulf, east to Indonesia, China, and Taiwan (Culotta and Pickwell 1993, Heatwole 1999), and south to New Caledonia and the Loyalty Islands (Ineich and Rasmussen 1997).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
In UAE waters this species is found up to 6-7 km offshore on the east coast, over sandy bottoms, sometimes associated with coral reefs. The habitat requirements in the UAE require further research. In the Arabian Gulf, there have been significant declines in coastal habitats, but specific utilisation of these habitats is uncertain.Globally, this species is found in coral reefs, turbid inshore waters, and estuaries (Heatwole 1999). It eats fish. The general reproductive strategy for the species includes small clutches (commonly 2-5 individuals). There is evidence of synchronized annual reproduction (Rasmussen 1989).
Threats and conservation measures listed
Threats listed in assessment
As with all sea snakes, this species is vulnerable to indirect threats from habitat loss and climate change throughout its range (Rasmussen et al. in prep.). The impact of oil spills and other marine pollution requires further study. They have the potential for entanglement in marine litter and abandoned fish traps (garghoor).
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE
Assessment ID
330078
Taxon name
Myriopholis macrorhyncha
(Jan, 1860)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Myriopholis macrorhyncha
(Jan, 1860)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
leptotyphlopidae
Genus
Myriopholis
Species
macrorhyncha
Species authority
(Jan, 1860)
Taxonomic notes and synonyms listed
This taxon is thought to be a complex of species that is in need of revision (Wallach et al. 2014; S. Baha El Din pers. comm.). West African members of this complex are no longer considered to belong to M. macrorhyncha (J.-F. Trape pers. comm. 2002), but the identity of populations from the MiData deficientle East, Pakistan and northwest India are still in need of clarification (Broadley and Wallach 2007). Adalsteinsson et al. (2009) assigned the species to their new genus, Myriopholis. These authors resurrected Leptotyphlops phillipsi from synonymy with M. macrorhyncha, however this action was apparently taken without examining specimens and as such this account treats this taxon as a junior synonym of M. macrorhyhncha pending resolution of this issue.
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Within the United Arab Emirates, this species is widespread throughout the sandy areas. The species is listed as Least Concern due to its presumed large population and because it is not thought to be subject to major threats throughout its extent of occurrence and area of occupancy. 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).
Assessment details
Year assessed
2018
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is widespread throughout the sandy deserts from sea level to 300 m asl (Gardner 2013, Burriel-Carranza et al. in press). It is more frequently recorded north of Abu Dhabi through the sandy deserts to Ras al Khaimah.Globally, this species ranges from Egypt, south through Sudan (but apparently absent from South Sudan; Broadley and Wallach 2007), Somalia and Ethiopia to Kenya and northern Tanzania, and east from Israel, Jordan, Syria and southeastern Turkey, through Iran (Khuzestan Province) and Iraq to the Arabian Peninsula, Pakistan and northwestern India. It is not present in Lebanon.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
The species is found on sand, sandy soil, cultivated land with some vegetation (Gardner 2013). The species is fossorial and only encountered occasionally during the night or after rains on the surface.It is a specialised termite eater and produces chemicals that prevent the soldier termites from attacking them (Gardner 2013). Their diet may also include ants and other small invertebrates, invertebrate eggs, larvae and pupae. Due to their small mouths, the soft abdomens of large termites are crushed and their contents squeezed out (Gardner 2013). They lay small clutches of tiny eggs (Gardner 2013).
Threats and conservation measures listed
Threats listed in assessment
There appear to be no major threats to this species.
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE
Assessment ID
330077
Taxon name
Cyrtopodion scabrum
(Heyden, 1827)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Cyrtopodion scabrum
(Heyden, 1827)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
gekkonidae
Genus
Cyrtopodion
Species
scabrum
Species authority
(Heyden, 1827)
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species is listed as Least Concern in view of its wide distribution, tolerance of a high degree of habitat modification, presumed large population, and the absence of significant threats. It has successfully colonized areas where it has been introduced and its population is increasing. 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).
Assessment details
Year assessed
2018
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is widespread throughout the sandy desert and gravel plains from sea level to 199 m asl. It is generally found in coastal areas and associated with man (Gardner 2013). Isolated records exist of the species at higher elevation from 900 to 1,000 m asl. It is also known from Dalma and Sir Bani Yas islands of the United Arab Emirates (Gardner 2013, Burriel-Carranza et al. in press). Within the UAE, this species also appears to be associated with development and urbanisation in parts of its range.The natural range of this species is not clear since it appears to have been introduced over much of its range (S. Baha El Din pers. comm. 2009). Populations on the African coast have almost certainly been introduced (Largen and Spawls 2010) and the only report from Eritrea is that of von Heyden (1827), so there is considerable doubt about whether the species still persists there. The current global range (Sindaco and Jeremäenko 2008) of this species is from Eritrea, through Sudan (where it was reported from Port Sudan; Loveridge 1947), Egypt (Flower 1933), Israel (introduced to Eilat; Hoofien 1995, Dolev and Perevelotsky 2002, Werner 1987), southwestern and northeastern Jordan (Sindaco et al. 1995, Disi et al. 2001, Disi 2002), eastern Syria (Disi and Böhme 1996, Martens 1997), Turkey (southeast Anatolia only; Baran and Atatür 1998, Sindaco et al. 2000), most of Iraq, western and southwestern Iran (Anderson 1999), northwestern, northern and eastern Saudi Arabia (with isolated central populations), southwestern Yemen, Kuwait, Qatar, northern United Arab Emirates, eastern and southern Oman (van der Kooij 2000, Carranza et al. 2018), eastwards to Afghanistan (Leviton and Anderson 1963), Pakistan (Baig 1998, Baig et al. 2008, Masroor 2009, Rais et al. 2015) and India (Pardeshi et al. 2010, Vyas 2011). It has also been introduced to the USA (Texas) where it is currently believed to be expanding its range. This species can be found from sea level to 1,800 m asl.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
This species is found in rocky coastal areas. It occurs in stony areas, on gravelly plains, moderately sandy desert with sparse vegetation, dry wadis and in dry grasslands. It can also be found in urban areas, villages and on building walls and ruins. In general, this is a very anthropophilic species. It is a nocturnal species that lacks adhesive pads on its toes. In the United Arab Emirates, it appears to be found predominantly associated with human habitation and gardens, and it is known to be an invasive colonist (Gardner 2013). Most populations are undoubtedly introduced as new settlements such as towns, farms and oil camps are established (Gardner 2013). Females lay two hard-shelled eggs in a clutch, and lay multiple clutches through the warmer months (Gardner 2013).
Threats and conservation measures listed
Threats listed in assessment
There appear to be no widespread threats to this species. The species may be preyed on by feral introduced species (cats, rats, etc).
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE
Assessment ID
330076
Taxon name
Ablepharus pannonicus
(Fitzinger, 1824)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Ablepharus pannonicus
(Fitzinger, 1824)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
scincidae
Genus
Ablepharus
Species
pannonicus
Species authority
(Fitzinger, 1824)
Taxonomic notes and synonyms listed
Barabanov and Milto (2017) give the authority of this species as 'Lichtenstein, 1823', however, the name Scincus pannonicus was reported in this source (correctly, Fitzinger in Lichtenstein, 1823) without an associated description, and is consequently considered a nomen nudum by Uetz et al. (2018). The correct authority is consequently 'Fitzinger, 1824', in which publication the species was formally described (P. Uetz pers. comm. 2018).
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Within the United Arab Emirates, this species is known from the Hajar Mountains between Asimah and Daftah, however, the distribution may extend further. The species is listed as Least Concern, despite its limited known area of occupancy (EOO) of 12 km<sup>2</sup> and extent of occurrence (EOO) 21 km<sup>2</sup>, which may be attributed to under-sampling due to its small size and semi-fossorial habits. It is able to adapt to habitat modification and appears to thrive within cultivated areas, and there are no known threats to the species which may cause it to decline in the near future 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).
Assessment details
Year assessed
2018
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is known from the Hajar Mountains between Asimah and Daftah (Gardner 2013, Burriel-Carranza et al. in press) and occurs at between 400-900 m asl. The species distribution might extend further, but due to its semi-fossorial habits, small size and difficulty to observe, it is under-sampled in surveys. This species is the most widely distributed member of its genus and has been recorded from southwestern Saudi Arabia, Yemen, southeast Kuwait, northern Oman, Iraq, northern and western Iran, southern Turkmenistan, southern Tajikistan, southeastern Uzbekistan, Kyrgyzstan, Afghanistan and Pakistan (from Quetta to Chitral; Minton 1966), reaching its eastern range limit in the Indian state of Jammu-Kashmir (Sahi and Duda 1986). In Afghanistan Sindaco and Jeremçenko (2008) mapped lowland localities along the borders of Pakistan, Iran and Turkmenistan, however, the records provided by Wagner et al. (2016) suggest that the species is confined to montane areas in this country. A single specimen has also been reported from Syria (Aleppo; Jeremäenko and Szczerbak 1986), but the occurrence in this country needs to be confirmed, as do reports of its occurrence in Azerbaijan and Georgia (Sindaco and Jeremäenko 2008). It can occur up to 2,500 m asl.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
The species is found in the Hajar Mountains especially in well-vegetated areas, oases, date gardens and orchards (Gardner 2013). It may also enter small crevices, hide under stones, leaves, or in cracks in the soil. It is a diurnal species with a semi-fossorial habit that preys on invertebrates such as ants, small beetles and crickets (Gardner 2013). It is presumed that the breeding season is during spring and summer. Females will lay a clutch of three to four eggs (Gardner 2013).
Threats and conservation measures listed
Threats listed in assessment
There appear to be no major threats to this species within its limited known area of occupancy. The species can adapt to habitat modifications and appear to thrive within cultivated areas.
Publication
Els, J., Allen, D., Hilton-Taylor, C., Harding, K. (2019). UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles. MOCCAE, UAE