United Arab Emirates

Official name
United Arab Emirates
ISO alpha-2 code
AE
ISO alpha-3 code
ARE
ISO numeric-3 code
784
Continent
Asia

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

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
In 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).
Taxon
Taxa
Hydrophis ornatus | (Gray, 1842)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxonomic Notes
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.
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).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

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

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
In the 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).
Taxon
Taxa
Hydrophis cyanocinctus | Daudin, 1803
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxonomic Notes
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.
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).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

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

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
In the 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).
Taxon
Taxa
Hydrophis schistosus | Daudin, 1803
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxonomic Notes
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.
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).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

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

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
In the 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).
Taxon
Taxa
Hydrophis spiralis | (Shaw, 1802)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxonomic Notes
This species has also been treated under the genus Leioselasma but is maintained in Hydrophis by Uetz et al. (2018).
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).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

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

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
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).
Taxon
Taxa
Hydrophis viperinus | (Schmidt, 1852)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxonomic Notes
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).
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).
Assessed status
Asessment status in full
Not Applicable
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There are no confirmed records from UAE waters.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Medicago polymorpha | UAE National Red List of Vascular Plants

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Not possible
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
It is an annual herb species (Fawzi and Ksiksi 2012) and is found in lawns and gardens, in addition to grassy cultivated areas. This species is a crop wild relative of alfalfa, Medicago sativa (Kameswara Rao 2013). It has a distinctive spiral seed pod.
Taxon
Taxa
Medicago polymorpha | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Medicago polymorpha L. is a tertiary wild relative of alfalfa (Medicago sativa L. subsp. sativa) (Singh and Jauhar 2005).
Taxon distribution as listed in assessment
A detailed description of the distribution of Medicago polymorpha within the UAE is lacking, however it is known to occur within the country according to R. Western. According to Fawzi and Karim (pers. comm. 2019), this species has been recorded from Hatta and Ras al-Khaimah, in addition to Abu Dhabi Island (S. Sakkir pers. comm. 2019). Globally, the native range of this species encompasses northern and eastern Africa, Europe, the Arabian Peninsula and western and central Asia (Board of Trustees, RBG Kew 2019).
Assessed status
Asessment status in full
Data Deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
Medicago polymorpha is considered to grow relatively well within certain areas of the UAE, however its exact range in the country is still not well defined, and it is not clear if it is subject to any major threats. Given the lack of information on the species, it is considered Data Deficient.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
This species is likely to be affected by grazing, although it is not clear whether this constitutes a major threat.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Medicago laciniata | UAE National Red List of Vascular Plants

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This annual herb species is known to grow within gravel plain environments in low montane areas, along with garden and plantation habitats (Jongbloed et al. 2003, Mahmoud et al. 2018). The stems can grow up to 30 cm and the leaves have blunt tips with toothed edges (Jongbloed et al. 2003). In addition, the plant produces yellow flowers between February and April, while the seed pod has the form of a small prickly globe (Jongbloed et al. 2003). It is considered to be an important contributor to biomass in dune and stabilised sand environments (Ghazanfar and Fisher 1998). It is a crop wild relative of alfalfa, Medicago sativa (Kameswara Rao 2013).
Taxon
Taxa
Medicago laciniata | (L.) Mill.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Medicago laciniata (L.) Mill. is a tertiary wild relative of <span class=""msoins0"">alfalfa (M. sativa L.) (Singh and Jauhar 2005).
Taxon distribution as listed in assessment
Within the UAE, this species was recently recorded from Jebel Hafeet and is also known from the Ru'us al-Jibal (Feulner 2011, Sakkir and Brown 2014). It is generally found within the Hajar Mountains, although localities may be scattered (Jongbloed et al. 2003). Globally, the native range of this species encompasses southern Africa, in addition to Macaronesia to Ethiopia and Tanzania, and on to India (Board of Trustees, RBG Kew 2019).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species occurs throughout the Hajar Mountains and the Ru'us al-Jibal, in addition to scattered localities around the UAE. It has also been recently described from Jebel Hafeet. It is generally considered to be common within the country and is known to occur in at least one protected area. Although grazing may have an impact on this species, it is not currently known whether this poses a major threat, as the structure of the plant's seed pod may deter grazers. As a result, it is assessed as Least Concern.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
This species may be affected by grazing of goats within areas of its range (Norton et al. 2009, Shahid 2017). However, the bristly fruit of this species may provide a slight deterrent to potential browsers (Norton et al. 2009).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Diplotaxis harra | UAE National Red List of Vascular Plants

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
It is thought to be a foodplant for a subspecies of the Desert Blacktip, Elphinstonia carlona amseli (Gillett 1997). This dwarf shrub species has been reported from abandoned fields, gravel plains and slopes within low mountain habitats (Western 1991, Jongbloed et al. 2003, Mahmoud et al. 2018). This is an annual species, although sometimes perennial, which can grow up to 50 cm in height (Jongbloed et al. 2003). It has fleshy, oval-shaped leaves with toothed edges, in addition to yellow flowers which are present between February and May (Jongbloed et al. 2003). Diplotaxis harra has been recorded as flowering regularly and profusely within its first season while still surviving for long periods (Batanouny 2001). This plant also has hairs which help to absorb moisture when conditions are humid (Batanouny 2001). It is also a crop wild relative of Brassica species, which includes cabbage, mustard, rapeseed and turnip, among others (Kameswara Rao 2013).
Taxon
Taxa
Diplotaxis harra | (Forssk.) Boiss.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Diplotaxis harra (Forssk.) Boiss. is a wild relative of brassica crops as well as being related to cultivated perennial wall rocket, D. tenuifolia (L.) DC. Three subspecies are native to Europe: D. harra ssp. crassifolia (Raf.) Maire, D. harra ssp. intricata (Willk.) O.Bolà²s & Vigo and D. harra ssp. lagascana (DC.) O.Bolà²s & Vigo.
Taxon distribution as listed in assessment
Within the UAE, it occurs within the Hajar Mountain range and in the Ru'us al-Jibal (Jongbloed et al. 2003, Feulner 2011, 2014). In the Ru'us al-Jibal, this species has been recorded from up to at least 1,650 m altitude (Feulner 2011). Globally, the native range of this species includes Somalia and northern Africa, through to the Arabian Peninsula and Pakistan (Board of Trustees, RBG Kew 2019).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species appears to be fairly widespread within the UAE and is generally considered to be common within rocky areas. It also occurs within at least one protected area. It is therefore assessed as Least Concern.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Epipactis veratrifolia | UAE National Red List of Vascular Plants

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This is a perennial species with a creeping rhizome (Jongbloed et al. 2003). It is found in moist and shady places along wadi banks and rock walls, and near irrigation channels in plantations, and is dependent on near-surface water or seepages. The flowering period for this species is from February to April (Jongbloed et al. 2003). In Wadi Wurayah the species is typically found around water seepages on shaded rock walls, as well as amongst tall grasses and sedges at the base of the pipeline waterfall (Feulner 2016). This species tends to grow in association with the fern Adiantum capillus-veneris (Jongbloed et al. 2003, Feulner 2011).
Taxon
Taxa
Epipactis veratrifolia | Boiss. & Hohen.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Shifman (2015) divided the species into two 'northern' and 'southern' subspecies; the former is found in the eastern Mediterranean and the Irano-Turanian regions, from Cyprus and Israel to Turkey, the southern Caucasus, Iran and Afghanistan. The latter is also present on Cyprus but is more limited to tropical habitats in the Saharo-Arabian and Sudanian regions.
Taxon distribution as listed in assessment
This species is widespread but very scattered in the Hajar Mountains (Jongbloed et al. 2003), including Wadi Wurayah National Park (WWNP; Feulner 2016), and was recorded in 2018 from Jebel Hafeet (Sakkir et al. 2018). Feulner (2011) found this species at only one site (a spring, 'Ayn as-Sih) in the Ru'us al-Jibal, not in the UAE, but reported the species to be occasional in the Hajar Mountains near springs and seeps, typically among Adiantum capillus-veneris ferns. The species has also been recorded from the base of the waterfall in WWNP. Without detailed locality records (aside from Jebel Hafeet), it has not been possible to estimate the EOO and AOO. The distribution of this species is from the eastern Mediterranean and the Caucuses, through the Arabian Peninsula to eastern Africa, and east to China (Board of Trustees, RBG Kew 2018).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This is the only orchid known to be present in the UAE. It is widespread in suitable habitat in the Hajar Mountains (Jongbloed et al. 2003), including Wadi Wurayah (Feulner 2016), and was recorded in 2018 from Jebel Hafeet (Sakkir et al. 2018). The species is found near springs and seepages, typically among Adiantum capillus-veneris ferns, and also along irrigation channels in plantations. Without detailed locality records (aside from Jebel Hafeet), it has not been possible to accurately estimate the extent of occurrence (EOO) and area of occupancy (AOO), however the AOO is inferred to be less than 500 km<sup>2</sup> based on suitable natural habitat; the extent of distribution within irrigated habitats is not known. Several subpopulations are within protected areas (e.g. Jebel Hafeet and Wadi Wurayah). Some subpopulations may be vulnerable to impacts from disturbance by tourism and recreational activities, and the species may also be impacted by stochastic events such as flash-floods, however these threats are localised and it is assumed that the species occurs in more than ten locations. The species is restricted to specific habitats, and the number of mature individuals is suspected to be less than 1,000 in the UAE, and the species therefore qualifies as Vulnerable (VU D1).
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Some subpopulations may be vulnerable to impacts from disturbance by tourism and recreational use of the area, such as in some parts of Wadi Wurayah, however it also occurs in areas where such impacts are low. The species may also be vulnerable to grazing. The species may also be impacted by stochastic events such as flash-floods e.g., Feulner (2014) noted the absence of this species from the area below the main waterfall following heavy rain in November 2014.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
This species is restricted to specific types of habitats, and the situation has remained relatively to similar to that in 1996.
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Tripidium ravennae | UAE National Red List of Vascular Plants

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
Tripidium ravennae is a perennial grass that grows up to 450 cm. They grow in wadis or near water in the mountains (Jongbloed et al. 2003).
Taxon
Taxa
Tripidium ravennae | (L.) H.Scholz
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is widespread throughout the Hajar Mountains in the UAE (Jongbloed et al. 2003), including records from Wadi Wurayah National Park (Feulner 2016). Globally, this species occurs in North Africa, Southern Europe, the Middle East, Central Asia and Myanmar (Board of Trustees, RBG Kew 2018).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species is widespread in the eastern UAE and assessed as Least Concern.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off