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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
330118
Taxon name
Hydrophis cyanocinctus
Daudin, 1803
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Hydrophis cyanocinctus
Daudin, 1803
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
elapidae
Genus
Hydrophis
Species
cyanocinctus
Species authority
Daudin, 1803
Taxonomic notes and synonyms listed
In the Australian region, most people call this species H. pacificus and they may be the same species (A. Rasmussen pers. comm. 2008). Sometimes treated under the genus Leioselasma.
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Within UAE waters, this species is not well known and is less common than some other sea snake species. In the Arabian Gulf, it is only known from coastal strandings. On the east coast, it is known from more records, mostly from south of Fujairah city, but is less common than some other sea snake species. Nothing is known of the population size or trend, and further research is required. The species is considered Data Deficient for the UAE at present because the available data are inadequate to assign the species to either Least Concern or a threatened category, and research into this and other sea snakes should be a priority.
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
This species is confirmed from United Arab Emirates waters (Soorae et al. 2006, Egan 2007, Gardner 2013, Buzás et al. 2018), where it is found in the Arabian Gulf (stranding records only, including the Dubai coast) and shallow waters in the Gulf of Oman (Buzás et al. 2018). The species appears less common than other sea snakes along the east coast, found up to 7.2 km from the shore (Géczy et al. 2017, Buzás et al. 2018). Recent museum specimens for the UAE are available in the Al Mayya Sanctuary, Fujairah). The first museum specimen in the region was collected from Das Island (Arabian Gulf, UAE) by M.B. Bailey in 1963 (Gasperetii 1988). Museum specimens from Muscat, Oman (Boulenger 1887), Arabian Gulf and Iran (Gasperetti 1988). Globally, this species is found in the Arabian Gulf east to Indonesia, the Philippines, and China, with the range extending south to northern Australia and Papua New Guinea (Culotta and Pickwell 1993); the species is also possibly present in Japan (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
In the UAE, this species is found up to 6-7 km off the east coast, at depths of up to 50 m, where the bottom is sandy (Géczy et al. 2017, Buzás et al. 2018). The habitat requirements in the UAE require further research. In the Arabian Gulf, there have been significant declines in suitable habitats (seagrass, coral reefs etc), but specific utilisation of these habitats is uncertain. In the Arabian Gulf, strandings increase when the weather is colder, and with rough seas. The species is recorded all year round on the east coast (Buzás et al. 2018).Globally, this species can be found in shallow seas over muddy bottoms (Stuebing and Voris 1989). It feeds mostly on eels (Voris and Voris 1983, Das 2007), but also gobies and marine invertebrates (Das 2007).
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. 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). Coastal development and reclamation may impact coastal habitats such as mangrove areas.Globally this species is commonly caught as bycatch by trawlers in many parts of its range. Mangrove habitats are likely to be impacted by urban development and other threats.
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
330117
Taxon name
Hydrophis schistosus
Daudin, 1803
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Hydrophis schistosus
Daudin, 1803
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
elapidae
Genus
Hydrophis
Species
schistosus
Species authority
Daudin, 1803
Taxonomic notes and synonyms listed
This species has been placed in several different genera in the past, however, 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.
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Presence of this species is confirmed within the United Arab Emirates marine territorial waters, however on the east coast, this was the least common species found in surveys, only known from one specimen out of c.250 individuals collected, and on the Arabian Gulf, it is known from a single known stranding record from the Dubai coast.This species may be vagrant within UAE waters, or occurrence be the result of accidental transport. It is considered Data Deficient.
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, Castilla et al. 2017, Buzás et al. 2018). On the east coast, this was the least common species found in surveys, only known from one specimen (collected 6.3 km offshore) out of c.250 individuals collected (Géczy et al. 2017, Buzás et al. 2018). On the Arabian Gulf, it is known from a single available stranding record from the Dubai coast (M.A.R. Khan pers. comm. 2018). Recorded from the Arabian Gulf and from the Gulf of Oman (Gasperetti 1988, Rezaie-Atagholipur et al. 2016) including breeding pair photographed (Rezaie-Atagholipur et al. 2016). It is not known from museum records from the UAE. Museum specimens include those from Muscat, Oman (Boulenger 1887), Arabian Gulf and Iran (Gasperetti 1988).Globally, this species is found from the Arabian Gulf of Pakistan, India, and Sri Lanka, east to Australia and Papua New Guinea and north to Viet Nam (Culotta and Pickwell 1993, 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
In the UAE, the species is known from a very small number of records and nothing is known of its habitat use. It may not be resident in the UAE, and occurrence may be vagrant or the result of transport in fishing gear or ship ballast disposal.This species occurs (Rasmussen et al. 2010) in shallow open seas, river mouths, estuaries, coastal lagoons, and in mangrove forests (Limpus 1975, Lim and Sawai 1975, Murthy 1977, Murthy and Rama Rao 1988, Venkateswarlu et al. 1995). It is found from 3.7-22.2 m (Redfield et al. 1978). It occurs over soft substrates such as mud and sand (Limpus 1975). It is also found in freshwater lakes in Cambodia and India and can travel up rivers. It is common in near-shore shallow waters and estuaries, especially in the soft bottom marine environments where its preferred prey, catfish, occur in high abundances (Rasmussen et al. 2010). Animals are active during the night and day and prefers water depths from less than 5 m to a maximum of 30 m (Leviton et al. 2003).
Threats and conservation measures listed
Threats listed in assessment
Occurrence in the UAE is very low and little is known of potential threats. Impacts from oils spills are likely, but there are no records of bycatch.
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
330116
Taxon name
Hydrophis spiralis
(Shaw, 1802)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Hydrophis spiralis
(Shaw, 1802)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
elapidae
Genus
Hydrophis
Species
spiralis
Species authority
(Shaw, 1802)
Taxonomic notes and synonyms listed
This species has also been treated under the genus Leioselasma but is maintained in Hydrophis by Uetz 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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Within UAE waters, this species is not well known and there are few records. Nothing is known of the population size or trend, and further research is required. The species is considered Data Deficient for the UAE at present because the available data are inadequate to assign the species to either Least Concern or to a threatened category, and research into this and other sea snakes should be a priority.
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 (Egan 2007, Soorae et al. 2006, Buzás et al. 2018). It is found from both the Arabian Gulf and the Gulf of Oman. On the east coast, it is found up to 3.2-6.5 km (Géczy et al. 2017, Buzás et al. 2018). The depth range is not certain; it is probably a bottom-dwelling species. There is a record from Khor Kalba on the east coast, and recent museum records are available for the UAE in the Al Mayya Sanctuary, Fujairah. Museum specimens from the region are available for Muscat (Oman; Boulenger 1887), Arabian Gulf and Iran (Gasperetti 1988).Globally, this species is found in the Arabian Gulf, east to Indonesia and the Philippines (Culotta and Pickwell 1993, Heatwole 1999). It has also been found in 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 the UAE, the species has been found on sandy-bottoms.Little is known about the life history of this species. It has been reported to occur in relatively deeper water habitats (Smith 1926) down to 50 m (Rasmussen et al. 2010). Feeds on eels. Records suggest that this species attains very large sizes of up to 2.75 m (Smith 1943). However, most specimens collected rarely ever even reach 2 m (Rasmussen et al. 2010). The largest specimen recorded in the UAE was a 186 cm long gravid female found stranded in Ras Al-Khaimah in 2014 January (Buzás et al. 2018). Based on post mortem data of the same specimen, the clutch size is up to 15 (B. Buzás and Cs. Géczy pers. comm. 2018).
Threats and conservation measures listed
Threats listed in assessment
They have the potential for entanglement in marine litter, including abandoned fish traps (garghoor), and pollution. The impact of oil spills and other marine pollution requires further study.
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
330115
Taxon name
Hydrophis viperinus
(Schmidt, 1852)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Hydrophis viperinus
(Schmidt, 1852)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
elapidae
Genus
Hydrophis
Species
viperinus
Species authority
(Schmidt, 1852)
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.There are three forms of this species (Smith 1926).
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
Not Applicable
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species is known from adjacent areas of both the Gulf of Oman and the Arabian Gulf, however, there are no confirmed records from the territorial waters of the UAE. The species is considered Not Applicable at present for the UAE national Red List, and surveys are needed to confirm the occurrence of the species in the UAE.
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
This species has been reported as present within the United Arab Emirates marine territorial waters (Gasperetti 1988, Soorae et al. 2006, Egan 2007, Castilla et al. 2017), however, there are no known confirmed records from UAE waters in the Arabian Gulf. There is a single known museum specimen collected in UAE waters, from near Sir Abu Nu'ayr (Arabian Gulf, Emirate of Abu Dhabi, UAE) by the crew of the HMS Dalrymple (British Royal Navy) around 1963 (Gasperetti 1988), however, the identity of this record requires confirmation. It is possible that the species occurs only in the northern parts of the Arabian Gulf, but Rezaie-Atagholipour et al. (2016) reported no records from Iranian waters. There are no records from the east coast of the UAE (Géczy et al. 2017, Buzás et al. 2018), although the species is recorded from adjacent waters near Muscat in Oman (Rezaie-Atagholipour et al. 2016). The first museum specimen from the region was collected in Muscat, Oman by A.S.G. Jayakar and is the type specimen of the Hydrophis jayakari (Boulenger, 1887), a synonym of H. viperinus.Globally, this species is known from the Arabian Gulf of Pakistan, around India and Sri Lanka, south to Indonesia (including Borneo) and east to Bangladesh, southeast Asia and southern China (Culotta and Pickwell 1993, Heatwole 1999). There are no records from the Philippines (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
There are no confirmed records from UAE waters.Globally, the species generally occurs in slightly deeper waters (15 - 30 m) in muddy soft bottom habitats (Rasmussen et al. 2010). The maximum size is approximately 97 cm TL (captured in a trawl in Goa, India; Rasmussen et al. 2010). Feeds on spiny flatheads in India (Rasmussen et al. 2010) and on eels and gobies (Voris and Voris 1983). An average of 3-4 large young and high reproductive effort (Lemen and Voris 1981).
Threats and conservation measures listed
Threats listed in assessment
There are no confirmed records from UAE waters.
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
330107
Taxon name
Indotyphlops braminus
(Daudin, 1803)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Indotyphlops braminus
(Daudin, 1803)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Reptiles
Kingdom
Animalia
Phylum
chordata
Class
reptilia
Order
squamata
Family
typhlopidae
Genus
Indotyphlops
Species
braminus
Species authority
(Daudin, 1803)
Taxonomic notes and synonyms listed
The species has also been recently placed in the typhlopid genera Typhlops and Typhlina (see Wallach 2009 for a complete synonymy). Following Wallach (2009), Typhlops khoratensis is considered a junior synonym of Indotyphlops braminus. Typhlops fletcheri has widely been treated as a junior synonym of Indotyphlops braminus, but examination of the holotype suggests that it is likely to represent a distinct species (A. Wynn pers. comm. to P. Uetz, in Uetz 2019). It is treated as valid (as I. fletcheri) without comment by Hedges et al. (2014), but as it has not been formally resurrected this account follows Pyron and Wallach (2014) in retaining it within I. braminus pending further taxonomic research.
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
Not Applicable
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Within the United Arab Emirates, this species has only been recorded from Dubai and Abu Dhabi cities, where it is restricted to urban gardens. The species is considered Not Applicable for the UAE national Red List as a non-native introduction.
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 has been recorded from urban areas of Dubai (Gardner 2013, Burriel-Carranza et al. in press) and Abu Dhabi, where it is considered to be introduced. It occurs from sea level to 100 m asl. This species is native to tropical Asia (possibly Sri Lanka or southern India), but is invasive in many parts of the world and is now known from approximately 84 countries worldwide (Lever 2003, Wallach 2009). This cosmopolitan distribution includes Old World tropical and subtropical regions, with encroachment into the northern Hemisphere of the New World and adjacent temperate areas (Wallach 1999, 2009). It is found at a wide range of elevations.
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 fossorial species is a human commensal and found in and around human habitation, also in gardens, loose soil, refuse heaps, decaying logs and trees, gutters and drainage ditches, and under leaf litter, heaps of stones and piled up bricks, flower pots.
Threats and conservation measures listed
Threats listed in assessment
There are no 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
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