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Assessment ID
330124
Taxon name
Eragrostis cilianensis
(All.) Jaunchen
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Eragrostis cilianensis
(All.) Jaunchen
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
poales
Family
poaceae
Genus
Eragrostis
Species
cilianensis
Species authority
(All.) Jaunchen
Taxonomic notes and synonyms listed
Not aquatic.
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 relatively widespread in the UAE: occurring along the Arabian Gulf coast and in the Hajar Mountains. In addition, it appears to utilise a range of habitats and is known to occur in at least one protected area within its distribution. Its ability to persist in a range of habitats may well provide some resistance to potential threats. As such, it is assessed as Least Concern.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
In the UAE this species is recorded from along the Arabian Gulf coast and in the northern Hajar Mountains, including Jebel Hafeet (Jongbloed et al. 2003, Al Mehairbi et al. 2019). Globally, the native range of this species spans across the Old World (Board of Trustees, RBG Kew 2019).
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 annual grass species grows within sand, in addition to plantation and garden habitats (Jongbloed et al. 2003, Brown et al. 2007, Mahmoud et al. 2018), disturbed areas, farms, roadsides, plantations and gardens (Al Mehairbi et al. 2019). Eragrostis cilianensis was also recorded from a gravel slope and terrace in the Wadi Wurayah National Park (Feulner 2016). It can grow up to 0.4 m in height, has flat, lance-shaped leaves and a pyramid-shaped inflorescence spray which flowers between February and April (Jongbloed et al. 2003). This plant also has an unpleasant smell which lends itself to the common name 'stinkgrass' (Jongbloed et al. 2003).
Threats and conservation measures listed
Threats listed in assessment
Grazing by goats may impact this species in parts of its range (Shahid 2017). Within its range along the Arabian Gulf coast, ongoing development could have negatively impacted the species.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330114
Taxon name
Medicago polymorpha
L.
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Medicago polymorpha
L.
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
fabales
Family
fabaceae
Genus
Medicago
Species
polymorpha
Species authority
L.
Taxonomic notes and synonyms listed
Medicago polymorpha L. is a tertiary wild relative of alfalfa (Medicago sativa L. subsp. sativa) (Singh and Jauhar 2005).
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
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.
Assessment details
Year assessed
2019
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
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).
Is there a map available in assessment?
Not possible
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
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.
Threats and conservation measures listed
Threats listed in assessment
This species is likely to be affected by grazing, although it is not clear whether this constitutes a major threat.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330113
Taxon name
Medicago laciniata
(L.) Mill.
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Medicago laciniata
(L.) Mill.
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
fabales
Family
fabaceae
Genus
Medicago
Species
laciniata
Species authority
(L.) Mill.
Taxonomic notes and synonyms listed
Medicago laciniata (L.) Mill. is a tertiary wild relative of <span class=""msoins0"">alfalfa (M. sativa L.) (Singh and Jauhar 2005).
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 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.
Assessment details
Year assessed
2019
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 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).
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 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).
Threats and conservation measures listed
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).
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330112
Taxon name
Diplotaxis harra
(Forssk.) Boiss.
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Diplotaxis harra
(Forssk.) Boiss.
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
brassicales
Family
brassicaceae
Genus
Diplotaxis
Species
harra
Species authority
(Forssk.) Boiss.
Taxonomic notes and synonyms listed
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.
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 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.
Assessment details
Year assessed
2019
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 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).
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
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).
Threats and conservation measures listed
Threats listed in assessment
There is no information available.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330111
Taxon name
Epipactis veratrifolia
Boiss. & Hohen.
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Epipactis veratrifolia
Boiss. & Hohen.
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
asparagales
Family
orchidaceae
Genus
Epipactis
Species
veratrifolia
Species authority
Boiss. & Hohen.
Taxonomic notes and synonyms listed
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.
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
D1
Criteria system used
IUCN

(see Assessment details)

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).
Assessment details
Year assessed
2019
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 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).
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 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).
Threats and conservation measures listed
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.
History
This species is restricted to specific types of habitats, and the situation has remained relatively to similar to that in 1996.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330110
Taxon name
Tripidium ravennae
(L.) H.Scholz
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Tripidium ravennae
(L.) H.Scholz
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
poales
Family
poaceae
Genus
Tripidium
Species
ravennae
Species authority
(L.) H.Scholz
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 widespread in the eastern UAE and assessed as Least Concern.
Assessment details
Year assessed
2019
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 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).
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
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).
Threats and conservation measures listed
Threats listed in assessment
There is no information available.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330109
Taxon name
Halodule uninervis
(Forssk.) Boiss.
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Halodule uninervis
(Forssk.) Boiss.
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
alismatales
Family
cymodoceaceae
Genus
Halodule
Species
uninervis
Species authority
(Forssk.) Boiss.
Taxonomic notes and synonyms listed
Halodule pinifolia is sometimes confused with this species.
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 is the most common species of seagrass in the UAE, where it occurs along the Arabian Gulf coast. Large areas of this species are found in inshore areas and around most, if not all, islands in Abu Dhabi Emirate, from the Abu Dhabi Islands to Ra's Hanjurah, extending eastwards to at least Umm Al Quwain. This species is susceptible to coastal development and water quality decline but can recover quickly if disturbance ceases and conditions improve. It is assessed as Least Concern.
Assessment details
Year assessed
2019
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 is the most common species of seagrass in the UAE. In the Arabian Gulf, there are large areas of this species in inshore areas and around most, if not all, islands in Abu Dhabi Emirate, from the Abu Dhabi Islands to Ra's Hanjurah, with a total area of c.55 km<sup>2</sup> estimated and representing c. 60% of seagrass bed content (EAD 2017); seagrass was found to be much more abundant in eastern Abu Dhabi, with the highest densities occurring north of Abu Dhabi Island around Al Samaliyah Island (EAD 2008). There is estimated to be around 4,000 km<sup>2</sup> of this species within Abu Dhabi Emirate (H.S. Das pers. comm. 2019). The species also occurs in Dubai Emirate, with records of extensive seagrass beds containing this species in the Jebel Ali area, particularly between Ras Hasyan and Ras Ghantoot, with their distribution primarily linked to areas of unconsolidated, deep sand (CBD 2016), and offshore from Jumeirah Beach. The species occurs eastwards to at least Umm Al Quwain. This species has a wide Indo-Pacific distribution. In the Pacific, it is found in southern Japan, Taiwan, the Philippines, Malaysia, Indonesia, throughout the Gulf of Thailand and along the coast of Vietnam and southern China. It occurs throughout insular Southeast Asia, northeast to the Northern Mariana Islands, Micronesia, and southeast to the Fiji Islands, as well as across northern Australia and the Great Barrier Reef. In the Indian Ocean, it is found from Geographe Bay in Western Australia extending across the Timor Sea, the south coast of Indonesia, and to the Andaman Sea and extending around the Bay of Bengal and around India to the Malabar Coast. It ranges from the Persian Gulf to the Red Sea, south to the east coast of South Africa to Madagascar and the islands of the western Indian Ocean.
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 sublittoral seagrass found from the mid-intertidal to a depth of 20 m. It is the least habitat-specific species of the seagrasses that occur in the UAE, being found in inter-tidal and sub-tidal zones, shallow sandy bays, in mangrove flats of fine mud and sand, in sheltered habitats with high levels of organic matter sediments, and in shallow open coast (EAD 2008). It is very fast growing, colonizes rapidly, and can flower prolifically, and some locations have very large seed banks. It can form dense meadows at some sites, whilst patchy and intermixed with other seagrass species (Short et al. 2010). In the Arabian Gulf, it tolerates extreme conditions with salinity varying from 38-70 ppt and temperatures of 10-“39'°C (inshore) and 19-33'°C (offshore; Short et al. 2010). Halodule uninervis is one of favoured foods of the Dugong and often heavily grazed (H.S. Das pers. comm. 2019).
Threats and conservation measures listed
Threats listed in assessment
This species is particularly susceptible to coastal development but can recover quickly if disturbance ceases and conditions improve. It can also be affected by siltation and sedimentation (Short et al. 2010, Erftemeijer and Shuail 2012). In the UAE, the species is impacted by coastal dredging and land reclamation and development, fish trawling activities, oil spills and oil pollution, oil extraction developments, coastal water eutrophication and salinisation (from water desalination plants), siltation, and other forms of pollution (Erftemeijer and Shuail 2012). Given its shallow water habitat, this species may also be threatened by climate change and the associated increase in storm activity, water temperature, and/or sea-level rise (Short et al. 2010).
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330108
Taxon name
Halophila stipulacea
(Forssk.) Asch.
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Halophila stipulacea
(Forssk.) Asch.
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
alismatales
Family
hydrocharitaceae
Genus
Halophila
Species
stipulacea
Species authority
(Forssk.) Asch.
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
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
B2ab(iii)
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This seagrass species occurs along the Arabian Gulf coastline of the UAE, in Abu Dhabi, Dubai and Ras al-Khaimah. The estimated AOO is under 2,000 km<sup>2</sup> and there are considered to be more than ten threat-based locations. Halophila stipulacea is currently undergoing a decline in the extent and quality of its habitat due to multiple threats including oil-related activities, pollution, dredging, coastal development and fishing culture. Therefore, this species is assessed as Near Threatened.
Assessment details
Year assessed
2019
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 UAE, this species is known to occur along the Arabian Gulf coast (Phillips et al. 2002). The maximum AOO of this species is estimated to be under 2,000 km<sup>2</sup>, incorporating the area of this species found in Abu Dhabi and Ras al-Khaimah (H.S. Das pers. comm. 2019). Due to the occurrence of multiple seagrass meadows along the UAE coastline, there are estimated to be greater than ten threat-based locations. The native range of this species encompasses Egypt to India and the West Indian Ocean (Board of Trustees, RBG Kew 2019).
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 perennial herb is a seagrass species (Norton et al. 2009, Phillips et al. 2002). It can grow at depths between 2-8 m (H.S. Das pers. comm. 2019).
Threats and conservation measures listed
Threats listed in assessment
This species is particularly susceptible to coastal development but can recover quickly if disturbance ceases and conditions improve. It can also be affected by siltation and sedimentation (Short et al. 2010, Erftemeijer and Shuail 2012). In the UAE, the species is impacted by coastal dredging and land reclamation and development, fish trawling activities, oil spills and oil pollution, oil extraction developments, coastal water eutrophication and salinisation (from water desalination plants), siltation, and other forms of pollution (Erftemeijer and Shuail 2012). Given its shallow water habitat, this species may also be threatened by climate change and the associated increase in storm activity, water temperature, and/or sea-level rise (Short et al. 2010).
History
Coastal development within the UAE has been increasing in frequency and intensity since 1996, reducing the extent and quality of available habitat for this species.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330105
Taxon name
Aegilops kotschyi
Boiss.
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Aegilops kotschyi
Boiss.
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
poales
Family
poaceae
Genus
Aegilops
Species
kotschyi
Species authority
Boiss.
Taxonomic notes and synonyms listed
Based on the interpretation of the bread wheat gene pool of van Slageren (1994), Aegilops kotschyi Boiss. is a secondary wild relative of Bread Wheat, Triticum aestivum L. subsp. aestivum, Durum Wheat, T. turgidum subsp. durum (Desf.) Husn., and a number of other cultivated wheats - including Emmer Wheat, T. turgidum subsp. dicoccon (Schrank) Thell., Einkorn Wheat, T. monococcum L. subsp. monococcum, Spelt, T. aestivum subsp. spelta (L.) Thell., and Sanduri Wheat, T. timopheevii (Zhuk.) Zhuk. subsp. timopheevii.
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 occurs at high elevations within the Ru'us al-Jibal. Although it is not as common as other species in the north of this area, this may be due to being overlooked and as a result of occurring at particularly high altitudes. It is, however, described as locally common within the south of the region. As such, it is assessed as Least Concern.
Assessment details
Year assessed
2019
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 UAE, this species has been recently recorded from the Ru'us al-Jibal (Feulner 2011). It is thought to generally grow at high elevations within this area, between 1,200 and 1,350 m (Feulner 2011). Globally, this species' native range spans from Tunisia to Afghanistan (Board of Trustees, RBG Kew 2019).
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 a crop wild relative of wheat, Triticum aestivum (Kameswara Rao 2013). It is recorded as growing on rocky slopes of the Ru'us al-Jibal (Feulner 2011).
Threats and conservation measures listed
Threats listed in assessment
There is no information available.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330104
Taxon name
Avena barbata
Pott ex Link
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Avena barbata
Pott ex Link
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
poales
Family
poaceae
Genus
Avena
Species
barbata
Species authority
Pott ex Link
Taxonomic notes and synonyms listed
Avena barbata Link is a secondary wild relative of oats, Avena sativa L. and A. byzantina K. Koch. (A. Katsiotis pers. comm. 2010). Five subspecies are native to Europe: A. barbata Link subsp. barbata, A. barbata subsp. castellana Romero Zarco, A. barbata subsp. hirtula (Lag.) Tab. Morais, A. barbata subsp. lusitanica (Tab. Morais) Romero Zarco and A. barbata subsp. wiestii (Steud.) Mansf.<span style=""background-color: yellow;""> (Valdés and Scholz; with contributions from Raab-Straube and Parolly 2009).<span style=""background-color: yellow;""><span style=""background-color: yellow;""><span style=""background-color: yellow;"">Romero Zarco (pers. comm. 2015) considers Avena saxatilis to be valid as a subspecies of Avena barbata (as Avena barbata subsp. castellana Romero Zarco), a situation that Euro+Med (2015, citing Valdés and Scholz 2009) agree with. Similarly, Loskutov and Rines (2011) consider A. saxatilis to be a form of Avena barbata. However, The Plant List (2015) considers Avena saxatilis to be a valid taxon).
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
This species is known from one site within the Ru'us al-Jibal. The species occurs at high elevations and are relatively undisturbed sites, which this plant appears to prefer. In addition, it is generally described as rare and detailed distribution data is lacking for this species. It would benefit from further research into its tolerance of threats, including disturbance, in addition to confirming its overall distribution in the UAE to be able to accurately assess it. For now, it is assessed as Data Deficient and further research is needed for this species.
Assessment details
Year assessed
2019
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
Avena barbata occurs in the Ru'us al-Jibal mountains in the north of the UAE (Jongbloed et al. 2003, Feulner 2011). Within this area, it has been recorded from one confirmed locality in the UAE at 900 m elevation, above bedrock on a ridge. A second record at 1,500 m elevation (Feulner 2011) may not be within the UAE. The origin and distribution of the species in the UAE requires confirmation; it may be native or be present here as a result of natural introduction, or may have been introduced alongside agriculture. Globally, this species occurs in northern, middle, east, south-east and south-west Europe, temperate Asia, Macaronesia, northern Africa and the Indian Subcontinent, and is naturalized in the Azores, Australia and the Americas (Duarte et al. 2011, Board of Trustees, RBG Kew 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
Avena barbata is a tall and thin grass (Jongbloed et al. 2003) known to occur in one site in the Ru'us al-Jibal in the UAE. Globally, Avena barbata has been reported to be very successful in undisturbed sites, preferring shallow stony hillsides, open parkland, pastures and cultivated land. It does not favour shrubby or forested sites (Duarte et al. 2011). In the UAE, it was found in silt amongst rock, on bedrock on ridge, c. 0.2 km above cultivation (Feulner 2011, G.R. Feulner pers. comm. 2019). This species is a crop wild relative of the oat crop, Avena sativa (Kameswara Rao 2013).
Threats and conservation measures listed
Threats listed in assessment
There is no information available.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.