LC
Assessment ID
330062
Taxon name
Scincus mitranus
Uploaded by
National Red List Database
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
330061
Taxon name
Diplometopon zarudnyi
Uploaded by
National Red List Database
Scientific name
Diplometopon zarudnyi
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
trogonophidae
Genus
Diplometopon
Species
zarudnyi
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
Within the United Arab Emirates, this species is found throughout the sandy deserts from Ras al Khaimah to western Abu Dhabi. It is listed as Least Concern in view of its wide distribution, presumed large population with no major threats 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).
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is found throughout the sandy deserts from Ras al Khaimah to western Abu Dhabi, including the Liwa area (Gardner 2013, Burriel-Carranza et al. in press). Occurs from sea level to 300 m asl. Globally, this species ranges from western Iran (a limited small dune area), southern Iraq and Kuwait, into the Arabian Peninsula where it is found in northern and central Saudi Arabia, Oman and the United Arab Emirates (Sindaco and Jeremäenko 2008). It is found from sea level to around 1,000 m asl.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species is found on sand sheets and dunes including the upper shoreline of sandy beaches (Gardner 2013).It is a nocturnal and fossorial species that spends most of its life under the sand. At night, they may surface and move considerable distances whilst foraging (Gardner 2013). They are predators which are presumed to consume arthropods and perhaps small geckos (Gardner 2013). They are able to tolerate a wide range of temperature while maintaining a mean selected body temperature within a narrow range (Gardner 2013). Very little is known about the species reproduction, although it may be similar to the observation made in Saudi Arabia, where the breeding season was recorded from early April to late June (Al-Sadoon et al. 2014). Females lay 6-9 eggs with an average egg diameter of 1.5 mm (Al-Sadoon et al. 2014).
Threats listed in assessment
There appear to be no major threats to this species as a whole, although coastal habitats will be impacted by development.
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
330060
Taxon name
Pseudocerastes persicus
Uploaded by
National Red List Database
Scientific name
Pseudocerastes persicus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
viperidae
Genus
Pseudocerastes
Species
persicus
Taxonomic notes and synonyms listed
We provisionally treat Pseudocerastes fieldi Schmidt, 1930 as a distinct species (Uetz and Hallermann 2010, Uetz et al. 2018, Šmíd and Tolley 2019), although in some accounts it is treated as a subspecies of P. persicus (Leviton et al. 1992).Pseudocerastes bicornis Wall, 1913, described from a single locality on the Pakistan-Afghanistan border at the eastern range limit for the genus, has long been considered a junior synonym of P. persicus (Sindaco et al. 2013), and this scheme is followed here, but is listed as a valid species without comment by Khan (2006).Recent studies have confirmed that Pseudocerastes persicus from Oman and the United Arab Emirates (the) are genetically the same as those from Iran (de Pous et al. 2016).
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The species is listed as Least Concern in view of its wide distribution and no known widespread threats that may cause a decline in the population to qualify for listing in a more threatened category. The species was previously listed in 2012 as Vulnerable for the Arabian Peninsula (Cox et al. 2012) due to its restricted range, however, since then, more data have been obtained on the species distribution which expanded its known range within the Hajar Mountains of the United Arab Emirates. 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).
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is presumed to be widespread throughout the Hajar Mountains from 300 m to 1,400 m asl, including Jebel Hafeet in Abu Dhabi Emirate (Cunningham 2002, de Pous et al. 2016, Burriel-Carranza et al. in press).Globally, this species ranges from northeast Iraq, northwest Iran and southern Azerbaijan, south to the Arabian Peninsula, and eastwards to western Pakistan. The species is widespread in Iran (Latifi 1991). In Pakistan, it ranges as far east as Manguli in southwestern Kalat (Minton 1966). It is also reported to occur in Afghanistan, however this may be based on a record taken close to the Afghan border in Pakistan and it is still correct, as observed by Leviton and Anderson (1970), that no documented records of this species appear to exist from Afghanistan (Wagner et al. 2016). This species is unlikely to occur in southeast Turkey, from where reports of this species are considered to be erroneous (Sindaco et al. 2013), or in northwestern Azerbaijan, and presence in these areas needs to be confirmed. Khan (2006) reports that it occurs up to 2,200 m asl.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
The species is found in vegetated rocky mountains and mountain wadis (Gardner 2013).They are predominantly nocturnal but may be active or bask among rocks during the day in the cooler months or at twilight (Gardner 2013). They prey on small mammals, lizards and birds (Gardner 2013). They are oviparous, laying 11-21 eggs, and the embryos are well-advanced and hatch after about 30 days incubation (Gardner 2013). Very little further is known about the ecology of this species.
Threats listed in assessment
Because of its habit of congregating in smaller areas of suitable habitat in the winter, it is relatively easy to extirpate local populations or to collect for trade. In the United Arab Emirates, it may be threatened by increasing levels of quarrying in some parts of its range.
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
330057
Taxon name
Cerastes gasperettii
Uploaded by
National Red List Database
Scientific name
Cerastes gasperettii
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
viperidae
Genus
Cerastes
Species
gasperettii
Taxonomic notes and synonyms listed
Originally assessed for the UAE as the nominate subspecies, Cerastes gasperettii ssp. gasperettii Leviton & Anderson, 1967, but assessment moved to the species-level as only the nominate subspecies is present in the UAE. Indeed, the status of subspecies Cerastes gasperettii ssp. mendelssohni has been under dispute and the general consensus is that it might not be valid (J. Els pers. comm. 2018).
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
Within the United Arab Emirates, the species is widespread throughout the sandy regions from Ras al Khaimah to the Saudi Arabian border. The species is listed as Least Concern in view of its wide distribution, large population, presence in several Protected Areas throughout its range, and as 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).
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is widespread throughout the sandy regions from Ras al Khaimah to the Saudi Arabian border (Gardner 2013, Burriel-Carranza et al. in press) from sea level to 400 m asl.Globally, the species distribution range includes the United Arab Emirates, Yemen, Oman, Israel, Jordan, Iraq, Kuwait, Saudi Arabia, western Iran and Iraq.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species is found in desert and semi-desert areas, preferably with some sand (Gardner 2013).It is a nocturnal and terrestrial animal that may bask on winter days. It often partially buries itself in soft sand by shuffling sand to the sides with its flattened body until only the eyes, horns and snout show above the surfaces. It moves by sidewinding and may cover distances of up to one kilometre a night in search of food (Gardner 2013). Its diet includes rodents such as jerboas and gerbils, lizards and birds (Gardner 2013). Its oviparous with females laying 4-20 eggs which are round shaped and soft leathery, with an incubation period of 60-65 days. Not all individuals have a single enlarge scale (horn) above each eye, this occurrence is not limited to any specific locality as both horned and non-horned specimens can be found within the same area.
Threats listed in assessment
There are no major threats to the species, although parts of its distribution range are subject to urban and road development, and it may be persecuted as with all snakes.
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
330054
Taxon name
Stenodactylus slevini
Uploaded by
National Red List Database
Scientific name
Stenodactylus slevini
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
gekkonidae
Genus
Stenodactylus
Species
slevini
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is listed as Least Concern in view of its wide distribution, 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).
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is known from the Lisaili, Ras Ghanada, Taweelah and Sweihan areas, and then westwards through Baynunah and Ruwais to the edge of the Sabkhat Matti (Gardner 2013, Burriel-Carranza et al. in press). It occurs from sea level to 300 m asl. This species has been recorded from northwestern Saudi Arabia, Bahrain, southern Iraq, scattered records in parts of the United Arab Emirates, Jordan and Yemen (Sindaco and Jeremäenko 2008). It is found from sea level to around 1,000 m asl.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species prefers hard substrates such as consolidated sand and alluvial or gravel plains from sea level to 300 m asl (Gardner 2013). It is a ground-dwelling and nocturnal species that digs burrows in firm ground near or under vegetation and can be found under construction debris (Gardner 2013).
Threats listed in assessment
There are no major threats to this species, although urbanisation impacts some 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
Assessment ID
330053
Taxon name
Rhagerhis moilensis
Uploaded by
National Red List Database
Scientific name
Rhagerhis moilensis
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
psammophiidae
Genus
Rhagerhis
Species
moilensis
Taxonomic notes and synonyms listed
This species is widely known under the generic name Malpolon (although it was included in the genus Scutophis by Geniez et al. 2004). Kelly et al. (2008) found that this species is genetically distinct from other members of Malpolon, but took no taxonomic action. Investigating the nomenclatural history of this snake, Böhme and de Pury (2011) resurrected the genus Rhagerhis for this taxon, a name previously (and erroneously) considered to be unavailable. Rhagerhis appears to be nested within Malpolon (Figueroa et al. 2016), but Uetz et al. (2019) notes that this apparent synonymy not been widely adopted.Rhamphiophis maradiensis, described from Niger, is now understood to be a junior synonym of R. moilensis (Trape and Mané 2006, I. Ineich pers. comm. 2013), although this treatment has been disputed (L. Chirio pers. comm. in Uetz et al. 2019).
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is widespread in the northern parts of the United Arab Emirates, although absent from the Hajar Mountains. It is listed as Least Concern in view of its wide distribution, presumed large population size, and because it is adaptable 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).
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species has a wide distribution from Ras al Khaimah in the north towards Sila in Abu Dhabi in the south and further inland to Al Ain (Gardner 2013, Burriel-Carranza et al. in press). It occurs from sea level to 300 m asl., and is not found in the Hajar Mountains.This widespread species ranges from Mauritania, Western Sahara and Morocco in the west, through much of northern and Saharan Africa to the Red Sea coast of Egypt, Sudan (where it has been recorded from Suakin; Largen 1997) and Eritrea (Hasmet; Largen 1997), Israel, southeastern Jordan, southern Syria, Iraq, southern Iran (Khuzestan Province and Hormozgan Province) and most of the Arabian Peninsula. In West Africa, it has a seemingly disjunct distribution in parts of Mauritania, central and northern Mali, and Niger, with a marginal occurrence in northwest Nigeria (Trape and Mané 2006). It can be found up to 1,500 m asl.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Found in gravel and stony deserts, sandy plains, desert margins, sandy coastal regions, and in cultivated and urban areas (Gardner 2013). Apparently absent from the deep sand deserts and mountains (Gardner 2013). It is normally diurnal but crepuscular or nocturnal during the summer.This species is capable of moving large amounts of sand by active shovelling with the head and neck, pushing the sand aside with sideways movements with the head bent downwards, and can thus make shelters under stones or logs (Gardner 2013). When disturbed, the snake threatens by lifting the front third of the body off the ground and flattening the neck into a narrow hood. It predates on lizards, small mammals and other snakes (Gardner 2013). Breeding is during summer and spring, with females laying a clutch of 4-18 eggs (Gardner 2013). The species is known to polish its scales with an oily secretion from the outside of the nasal flap beside the nostrils (Gardner 2013), the purpose of which is unknown but presumed to reduce water loss or act as a chemical communication.
Threats listed in assessment
There appear to be no major threats to this species as a whole. Some animals are killed in residential areas or accidentally on roads. The species may be persecuted as with all snakes.
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
329913
Taxon name
Varanus griseus
Uploaded by
National Red List Database
Scientific name
Varanus griseus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
varanidae
Genus
Varanus
Species
griseus
Taxonomic notes and synonyms listed
The morphological diversity of this species complex is not adequately reflected in current subspecific divisions (Auliya and Koch 2020). This species is divided into three subspecies which occupy distinct geographical regions and can be identified by size, tail shape, and the number of bands on the body and tail. Varanus griseus griseus has a rounded tail and highest number of bands, Varanus griseus caspius reaches the largest size and has a laterally compressed tail, while Varanus griseus koniecznyi is the smallest subspecies and has the fewest bands (Stanner 2004).
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
Within the United Arab Emirates, this species is widespread throughout all of the mainland desert regions excluding the Hajar Mountains. It is listed as Least Concern in view of its wide distribution, presumed large population, presence in several Protected Areas, it is unlikely to be declining fast enough to qualify for listing in a more threatened category.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is widespread throughout all of the mainland desert regions excluding the Hajar Mountains (Gardner 2013, Burriel-Carranza et al. in press). It occurs from sea level to 300 m asl. Globally, this is a widespread species of arid areas of North Africa, West and Central Asia (Corkill 1928, Martens and Kock 1992, Stanner 2004, Trape et al. 2012). In northern Africa, this species ranges from Western Sahara, Mauritania, northern Mali, and Niger in the west, throughout the Saharan desert region, to Egypt and Sudan in the east. From Egypt, the species ranges northwards through the southern and eastern Levant and into Turkey (southeastern Anatolia), Iraq and Iran. The species is present throughout the Arabian Peninsula.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Within the UAE, this species is found in desert regions including sandy and harder substrates, dry wadis, and hills. They also use agricultural areas, irrigated forestry plots (Gardner 2013) and waste disposal sites.
Threats listed in assessment
Urban development is the main known threat to the species in some parts of its distribution range within the United Arab Emirates. The species is also persecuted, and it is likely to be impacted by recreational driving on dunes and sandy 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
Assessment ID
329903
Taxon name
Duttaphrynus dhufarensis
Uploaded by
National Red List Database
Scientific name
Duttaphrynus dhufarensis
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Amphibians
Kingdom
Animalia
Phylum
chordata
Class
amphibia
Order
anura
Family
bufonidae
Genus
Duttaphrynus
Species
dhufarensis
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The species is listed as Least Concern in view of its moderately wide distribution within the UAE, tolerance of a degree of habitat modification, 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).
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is found throughout the Hajar Mountains south to Al Ain (Gardner 2013, Soorae et al. 2013, Burriel-Carranza et al. in press), from sea level to 1,500 m asl.Globally, the species ranges from the western mountains of Arabia from around Mecca, Saudi Arabia southwards; around southern peripheral Arabia, including Yemen, southern and northern Oman, and the United Arab Emirates (Gardner 2013, Soorae et al. 2013). Apparently introduced into the Riyadh area of Saudi Arabia.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
The species is found throughout the Hajar Mountains (Burriel-Carranza et al. in press) on gravel plains, dry wadis and on mountain ridges. It is also encountered in gardens, oases, plantations and irrigation canals. The species is highly adapted to arid environments and in the UAE it is mainly nocturnal. During dry conditions, they are typically found as single individuals (Soorae et al. 2013) aestivating in burrows underground or under flat rocks until the rainy season. After rainfall, they appear in high densities and form breeding groups, which continue by day and night (Cunningham and Feulner 2001, 2005; Gardner 2013). They are able to breed successfully even in puddles or potholes away from permanent water. They feed on insects and other invertebrates.
Threats listed in assessment
There are no known widespread threats to this species; much of its range is undeveloped. The amphibian disease chytridiomycosis, caused by the chytrid fungus Batrachochytrium dendrobatidis, was not detected in a survey of wild populations in the UAE in 2012 (Soorae et al. 2012, Chaber et al. 2016).
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
329902
Taxon name
Sclerophrys arabica
Uploaded by
National Red List Database
Scientific name
Sclerophrys arabica
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Amphibians
Kingdom
Animalia
Phylum
chordata
Class
amphibia
Order
anura
Family
bufonidae
Genus
Sclerophrys
Species
arabica
Taxonomic notes and synonyms listed
According to Stöck et al. (2001), the taxonomy and nomenclature of this species requires aData deficientitional research, since the specimen considered the holotype by Balletto et al. (1985) is not that one described by Heyden (1827). Bufo hadramautinus Cherchi 1963 was synonymized with Bufo arabicus by Schätti and Desvoignes (1999). This species was under the generic name Duttaphrynus but is now treated under Sclerophrys (Frost 2016).
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
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 moderately wide distribution, tolerance of a broad range of habitats, 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).
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is found in association with surface water throughout the Hajar Mountains and is especially common in areas with permanent water (Cunningham and Feulner 2005). It is recorded from sea level to 1,100 m asl within the United Arab Emirates (Gardner 2013, Soorae et al. 2013, Burriel-Carranza et al. in press).The species lays eggs in artificial or treated sewage water-fed drains and falaj system in Al Ain Zoo and dry wadis nearby (M.A.R. Khan pers. comm. 2018), however, it is unclear if these populations are natural or introduced. The species were introduced in the Ruwais area of Abui Dhabi where it was recorded from artificial ponds within a residential complex (G.R. Feulner pers. comm. 2018).Globally, the species ranges from northwestern Saudi Arabia, through the western mountains south to Yemen, northern Oman (absent from southern Oman) and the United Arab Emirates (Heyden 1827, Balletto et al. 1985, Schätti and Desvoignes 1999, Stöck et al. 2001, Frost 2016).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This is an opportunistic species that is present where there are water sources available; this includes garden courtyards, oases, permanent springs, irrigation canals and permanent small rivers. Breeding takes place in stagnant and slow-moving water. These toads are active by day as well as by night. Eggs are laid throughout the year in permanent water pools and following rain in temporary pools (Gardner 2013).There is no overall decline in habitat extent and quality, however, over-utilisation of surface water (for agriculture for example) will impact the species.
Threats listed in assessment
There are no widespread threats to this species and much of its range is undeveloped. However, over-utilisation of surface water (for agriculture for example) will impact the species. The amphibian disease chytridiomycosis, caused by the chytrid fungus Batrachochytrium dendrobatidis, was not detected in a survey of wild populations in the UAE in 2012 (Soorae et al. 2012, Chaber et al. 2016).
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
330691
Taxon name
Gazella arabica
Uploaded by
National Red List Database
Scientific name
Gazella arabica
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Mammals
Kingdom
Animalia
Phylum
chordata
Class
mammalia
Order
cetartiodactyla
Family
bovidae
Genus
Gazella
Species
arabica
Taxonomic notes and synonyms listed
The taxonomy of genus Gazella is complex and several different arrangements have been proposed, but several issues remain unresolved. Gazella arabica was originally described from a single specimen: a skin and a skull obtained on the Farasan Islands off the coast of Saudi Arabia (or at least labelled as such). This became something of a mystery taxon and is different from the gazelles currently found there. Bärman et al. (2012) extracted DNA from the type specimen and showed that this was not a single specimen, assigning the skin to G. g. cora and the skull to gazelles of the northern type (G. g. gazella). Wronski et al. (2010) showed that Gazella gazella, in fact, consists of two monophyletic lineages, a northern clade (represented by samples from the Golan Heights) and a southern clade (based on samples from the Arabian Peninsula including the southern Arava Valley), based on mtDNA markers. Lerp et al. (2012) produced similar conclusions using nuclear markers and including samples from Central Israel. A morphological and genetic study of genus Gazella (Bärmann et al. 2013), and a genetic study of gazelles in the southern Levant (Hadas et al. 2015) all further support the existence of two monophyletic lineages: a northern clade (Gazella gazella), and a southern clade (provisionally named G. arabica on the basis that this name takes precedence over cora). This arrangement is now followed by the IUCN SSC Antelope Specialist Group, with G. gazella replacing G. g. gazella in the former arrangement, and the name G. arabica provisionally retained for the southern clade, pending a ruling by the International Commission on Zoological Nomenclature (ICZN). So G. arabica, as understood here, comprises all the gazelles formerly considered under G. gazella, from the southern Negev through the Arabian Peninsula. Several subspecies have been named under G. gazella and have previously been evaluated for The IUCN Red List: acaciae; in the southern Arava Valley; cora in most of the Arabian Peninsula; farasani on the Farasan Islands; and muscatensis on the Batinah coast of Oman. Genetic research by scientists at King Khaled Wildlife Research Centre (Saudi Arabia) and Zoological Society of London (ZSL) has confirmed the existence of some intraspecific variation, but there is no agreement on the validity of these named subspecies and they are not assessed separately for the time being, until a definitive analysis has been produced. All of the above are included in G. arabica here. The relationship between G. arabica (as here) and two other 'mystery' species, G. erlangeri and G. bilkis awaits confirmation.
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The species was formerly widespread in the UAE but its range and population size are much reduced, however, conservation efforts, captive breeding and releases have resulted in the population stabilising and now increasing. As a conservative estimate, the population is estimated to contain over 1,500 mature individuals and the population is stable or increasing, so the species does not qualify for a threatened category or Near Threatened and is assessed as Least Concern. No regional adjustment is made to the Least Concern assessment.
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.
URL (link) of redlist assessment or publication
https://www.moccae.gov.ae/assets/download/b352eff1/UNRL%20of%20Mammals%20-%20Report%202019.pdf.aspx?view=true
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Formerly widespread in UAE but then its range became reduced. Around 15-25 years ago it was known from a few sites in the Hajar Mountains and large areas of desert between Jebel Ali and Sweihan (Hornby 1996, Aspinall et al. 2005). Sites in the mountains include Gulfa Wadi (Masfut), Wadi Jabsah (Fujairah), and on the ridges above Wadi Awsaq, on the southern edge of the Musandam (in the mid-1990s). At the same time, gazelles were present in neighbouring Oman in Wadi Qahfi (near the so-called Hatta Pools); in several wadis with permanent water along the mountain front south of the Hatta road; and in the remote high Musandam, east of Jebel Harim). Musandam records from the late 2000s in the area near the watershed between Wadi Bih and Wadi Khabb Shamsi are believed to represent releases (a pair of animals was found in the same locality at ca. 1,200 m in two successive years). Some of the remaining desert subpopulations have also been supplemented by releases from captive breeding programmes, in some cases, such as the Dubai Desert, since the mid-1990s. The Al Marmoom Conservation Area and adjacent areas of the Dubai Desert hold one of the largest current subpopulations. This area also holds Oryx leucoryx and Gazella marica. The area is provisioned by the Dubai Municipality and the Ruler's Office with alfafa and water, but oryx tend to dominate the feeding points while the gazelles range widely over the whole area. Mountain Gazelles have also been released in the Dubai Desert Conservation Reserve, on Siniyyah Island, Arabian Oryx Protected Area and at other sites in Abu Dhabi Emirate. Based on the known habitat preferences, it is assumed that historically G. marica occupied desert areas and G. arabica the mountains and their fringes, but releases may now have obscured the original pattern. The species is endemic to the Arabian Peninsula, where it was once widely distributed. The largest remaining subpopulations are found in Oman and on the Farasan islands in Saudi Arabia. It has been reintroduced to the Uruq Bani Ma'arid, Mahazat as Sayd, and Ibex Reserves in Saudi Arabia. There is a small introduced subpopulation on Farur Island, Iran (IUCN SSC Antelope Specialist Group 2017a).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Arabian Gazelle occurs in deserts, semi-deserts, hills, mountains and coastal plains, often being associated with Acacia. It is generally seen singly or in small groups.
Threats listed in assessment
Uncontrolled hunting is considered responsible for the decline of the species across its regional range. Overgrazing is also a major factor in many areas (IUCN SSC Antelope Specialist Group 2017a). The increasing construction of roads and fences has likely had a serious impact on the habitat through fragmentation and preventing access to the limited supplies of water. There may be a risk of infectious diseases such as PPR, brucellosis, through contact with domestic livestock.
History
Over the last 15-25 years, captive breeding, releases and reinforcement, and the establishment of a network of protected areas has resulted in a large and stable population. Hornby (1996) listed Gazella gazella cora as Vulnerable and the backcasted 1996 assessment for this species is also Vulnerable under criteria C2a(i); D1.
Publication
Mallon, D., Hilton-Taylor, C., Allen, D., & Harding, K. (2019). UAE National Red List of Mammals: Marine and Terrestrial. A report to the Ministry of Climate Change and Environment, United Arab Emirates (p. 41). IUCN Global Species Programme. https://bit.ly/2RdZCQR