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

Himantura uarnak | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

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
Yes
Habitat
Habitat details as listed in assessment
The Reticulate Whipray is often found near sandy beaches, in sandy areas of coral reefs, in shallow estuaries and lagoons, and may even enter freshwater (Vaudo and Heithaus 2009, Gutteridge 2012). This species also occurs offshore to depths of at least 50 m (White et al. 2006). Tracking data for the Reticulate Whipray suggests that within sandy, shallow water areas, the species is a highly resident mesopredator, though the home range for individuals can be relatively restricted (Vaudo and Heithaus 2012). Himanura species exhibit a strong association with shallow waters of the western region where complex habitats such as coral assemblages and seagrass beds are most prevalent (Last et al. 2016 Rays of the World book). Its reproductive mode is viviparous with histotrophy. This species reaches 160 cm disc width (DW) (Last and Stevens 2009). Males mature at 82-84 cm DW and size at birth is 21-28 cm DW (Manjaji 2004, White et al. 2006, White and Dharmadi 2007). Fecundity is assumed to be low, as a single pregnant female observed possessed two embryos (B.M. Manjaji-Matsumoto pers. obs.).As there is no information on this species' maximum age and age at maturity, generation length was inferred as 20 years based on data for the congener, the Blackspotted Whipray (Himantura astra). Female Blackspotted Whiprays are reported to have a maximum age of 29 years and an age at maturity of nine years (Jacobsen and Bennett 2011). These were used to calculate a generation length of 19 years based on the equation: generation length = (((29-9)/2)+9). The maximum size of the Reticulate Whipray is considerably larger (~160 cm DW) than that of the Blackspotted Whipray (80 cm DW), so it is possible the generation length of the Reticulate Whipray is greater than 20 years.
Taxon
Taxa
Himantura uarnak | (Gmelin, 1789)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Himantura uarnak was recently split from other Himantura species (Last et al. 2016a). The new distribution no longer includes Australia and Papua New Guinea (Last et al. 2016b). There is some continued taxonomic uncertainty with the Himantura genus and this assessment should be updated if the current distribution changes.
Taxon distribution as listed in assessment
The Reticulate Whipray occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Last et al. 2016).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
A2cd
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
The Reticulate Whipray occurs throughout UAE coastal waters. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980 and recently conducted surveys indicate it remains common in the area; however, Himantura species are discarded from catches in the UAE and it is unknown how this impacts the species. A large part of the species distribution in the Arabian Sea region (namely, India and Pakistan) is under extremely intense and increasing demersal fishing pressure. In contrast, Himantura species are regularly discarded in the Arabian Gulf and Sea of Oman, and they remain common there. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. Given the intense fishing pressures faced by this species in other parts of the broader Arabian Seas region, and ongoing threats from discard and habitat loss in the UAE, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 30% over the past three generation lengths, or about 60 years. It is listed as Vulnerable A2cd.
Criteria system
Criteria system specifics
IUCN v3.1
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
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Aetobatus flagellum | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

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
Yes
Habitat
Habitat details as listed in assessment
The Longhead Eagle Ray occurs primarily inshore on the inner continental shelf, and is associated with estuarine habitats (Last et al. 2016), especially where it occurs in the Arabian Gulf (Bishop et al. 2016). It attains a maximum size of 90 cm disc width (DW) with males mature at 50 cm DW and females at 75 cm DW (White and Moore 2013). Size at birth is unknown but the smallest free-swimming individual examined was 23 cm DW. Little else is known of the biology of this species. However, it is suspected to exhibit low fecundity as with other myliobatids which bear litters of up to four offspring (Compagno and Last 1999). As there is no information on this species' maximum age and age at maturity, generation length was inferred as ~15 years based on data for the Bat Ray (Myliobatis californicus) which are reported to have a maximum age of 24 years and an age at maturity of five years (Martin and Cailliet 1988). However, it is noted that the Longhead Eagle Ray reaches a smaller maximum size than this species.
Taxon
Taxa
Aetobatus flagellum | (Bloch & Schneider, 1801)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
This species was previously considered to be conspecific with Aetobatus narutobiei, but the species have since been shown to differ genetically and morphologically (White and Moore 2013).
Taxon distribution as listed in assessment
The Longhead Eagle Ray occurs throughout UAE waters. Globally, it is patchily distributed in the Indo-West Pacific from the Arabian Sea region to Indonesia and Malaysia (Last et al. 2016).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
A2d
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 inshore eagle ray occurs throughout UAE waters, but little is known on its population there. It may be taken as bycatch in inshore gillnet fisheries. Most of the distribution of the species in the Arabian Sea region is under extremely intense and increasing demersal fishing pressure, especially off India. Furthermore, the loss and modification of coastal habitats in the Arabian Gulf is a significant concern, especially since this species is known to rely on estuaries during part of its life history. Its relative rarity, large size, and low productivity makes this species particularly susceptible to population decline. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. Given the intense fishing pressures faced by this species throughout the Arabian Seas, and ongoing threats from bycatch and habitat loss, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation, it is suspected to have declined by at least 50% over the past three generation lengths, or about 45 years. It is listed as Endangered A2d.
Criteria system
Criteria system specifics
IUCN v3.1
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
Information pertaining to threats to this species in UAE waters are unavailable. Generally, the Longhead Eagle Ray is highly susceptible to a variety of inshore demersal fisheries, including trawls and gill nets. In the Arabian Sea region, it occurs in areas of intense demersal trawl activity. Marine habitats in the Arabian Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010), which is likely to impact this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Scoliodon laticaudus | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

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
Yes
Habitat
Habitat details as listed in assessment
The Spadenose Shark is common in coastal and estuarine waters, preferring muddy and sandy substrates at depths up to 80 m. It attains a maximum size of 91 cm total length (TL) and males mature at 24-36 cm TL and females at 33-35.8 cm TL (Devadoss 1979, Compagno et al. 2005, Sen et al. 2018). Breeding occurs throughout the year (Devadoss 1979) and females probably mate at least once each year. This shark is placentally viviparous, with arguably the most advanced reproductive mode of the elasmobranchs. Litter sizes range from 6-20, with a mean of 13 (Devadoss 1979). Young are born throughout the year, with size at birth around 12-15 cm TL, after a gestation period of five or six months (Compagno et al. 2005). Age and growth data are limited, but the generation length is estimated at about 3.75 years (Nair 1976, Compagno et al. 2005).
Taxon
Taxa
Scoliodon laticaudus | Müller & Henle, 1838
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
The genus Scoliodon, represented by S. laticaudus, was previously considered monotypic but now consists of three species with S. macrorhynchus resurrected from the junior synonym of S. laticaudus (White et al. 2010).
Taxon distribution as listed in assessment
The Spadenose Shark occurs in UAE waters on the Sea of Oman coast, and potentially the Arabian Gulf coast. Its presence in the Arabian Gulf is unclear, but historic records suggest it may occur there (Wright et al. 1990). Extensive market and fishery surveys have failed to identify it there (Moore et al. 2012, Jabado et al. 2015). Globally, it is widespread in the Indo-West Pacific (Ebert et al. 2013).
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
The Spadenose Shark occurs in UAE waters on the Sea of Oman, but is very poorly known there. It is reported as a dominant species in landings in Pakistan and India and is particularly susceptible to inshore fisheries. Due to its limited fecundity, concern exists that ongoing increases in catches will lead to recruitment overfishing. Intensive and increasing fishing means that, like many other species, populations have likely declined. Little is known on the population of this species in UAE waters and given that its distribution there remains uncertain, it is listed as Data Deficient.
Criteria system
Criteria system specifics
IUCN v3.1
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
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. Marine habitats in the region have experienced high levels of disturbance and are quickly deteriorating due to major impacts from development activities (Sheppard <em style=""font-variant-ligatures: normal;font-variant-caps: normal;orphans: 2; text-align:start;widows: 2;-webkit-text-stroke-width: 0px;text-decoration-style: initial; text-decoration-color: initial;word-spacing:0px"">et al. 2010).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Ficus salicifolia | 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 tree species is known to grow within wadi environments (Mahmoud et al. 2018). It can grow up to 15 m in height and has smooth grey bark (Jongbloed et al. 2003). The tree produces a milky sap, has alternating, lance-shaped leaves and round orange fruits (Jongbloed et al. 2003). It flowers between May and December (Jongbloed et al. 2003). Typically, it grows within wadi banks and gorges at low elevations (Jongbloed et al. 2003) and is described as 'more prominent on rock debris, especially near wadis' (Perry 2008). This fig tree is also reported to be the most drought-tolerant of the Ficus species found within Arabia (Jongbloed et al. 2003).
Taxon
Taxa
Ficus salicifolia | Vahl
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Although the African Plant Database (APD 2020) maintains Ficus cordata subsp. salicifolia as a subspecies of F. cordata, we follow Bhanumas et al. 2013 and Plants of the World online (Board of Trustees, RBG Kew 2020) in considering Ficus salicifolia as a valid species.
Taxon distribution as listed in assessment
Within the UAE, this species is widespread throughout the Hajar Mountain range and the Ru'us al-Jibal (as Ficus cordata subsp. salicifolia; Jongbloed et al. 2003). It typically occurs at low elevations and is rarely found above 500 m altitude (Jongbloed et al. 2003). Globally, the native range of this species is given as from the western Cape Province to Cameroon, and east to the Arabian Peninsula (Board of Trustees, RBG Kew 2019), although Bhanumas et al. (2013) consider the distribution in Africa to generally be more northerly (Algeria, Niger, Libya, Congo, South Africa, Botswana, Egypt, Sudan, Zimbabwe, Uganda, Eritrea, Ethiopia, Kenya, Tanzania, Djibouti, Somalia, and Arabia (Saudi Arabia, Yemen, United Arab Emirates, and Oman). Bordbar and Mirtadzadini (2019) recorded the species for Iran.
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 in the UAE, in addition to the Ru'us al-Jibal. Within this range, it is known to occur in at least one protected area. It is generally considered to be common and 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:

Verified entry
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Vachellia flava | 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 much branched, tall shrub or small tree (2-7 m tall), which grows in dry semi-desert areas on sandy and clay soil and on stony screes. The species is one of the most drought-tolerant among the common African acacias occurring in the rainfall belts 50-400 mm. Its distribution differs from that of Acacia seyal, as the latter is a typical Sahelian and Sudanian species occurring in rainfall belts between 400 and 800 mm, on fine-textured soils only. The species is also known to occur in many ecoregions (WWF Ecoregions), such as Sahara desert, Sahelian Acacia savanna, southwestern Arabian foothills savanna, Red Sea Nubo-Sindian tropical desert and semi-desert, Arabian Desert and East Sahero-Arabian xeric shrublands and South Iran Nubo-Sindian desert and semi-desert.
Taxon
Taxa
Vachellia flava | (Forssk.) Kyal. & Boatwr.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, it is known from foothills of the Hajar Mountains, Al Marmoum, Jebel Hafeet, Arabian Oryx Protected Area, and Hilli. It is absent from the west of the UAE, but has been planted as a landscape tree, for example in parts of Dubai (G.R. Brown pers. comm. 2020). The estimated EOO for this species is 19,222 km<sup>2</sup>. The species is found in the northern Sahel and the southern and central Sahara, extending to eastern Africa and east to the Arabian Peninsula.
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
B1ab(iii)
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
The species is an important legume species for indigenous populations (it is used to feed animals, such as goats, sheep and camels, to produce high quality honey, for charcoal, as herbal medicine etc.), it is therefore important to ensure that this species is not over-exploited in the future leading to a population decline and to a threatened category. At present, the estimated EOO for this species is 19,222 km<sup>2</sup> and it is experiencing a decline in habitat extent and quality due to over-grazing and development. However, it is anticipated to occur at more than ten locations, meaning it is assessed as Near Threatened.
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 over-grazed and is at threat from development. There is no known natural regeneration for this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
There were fewer threats in the past decades which may have meant this species was at lower risk of extinction. However, it is still likely to have been categorised as Near Threatened.
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Chesneya parviflora | 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
The original records of this species by A.S. Gardner were from natural sites within the zone of mixed sedimentary rocks southeast of Dibba. It was subsequently recorded growing in silt at the base of a cliff, adjacent to cultivation (Feulner 2011). It is described as a perennial species (Board of Trustees, RBG Kew 2019).
Taxon
Taxa
Chesneya parviflora | Jaub. & Spach
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species has been recorded from a single locality at low altitude in the southeast of the Ru'us al-Jibal (Feulner 2011). There are reportedly other scattered specimens within the adjacent Dibba zone, although the plant does not seem to generally occur in the Hajar Mountains (Feulner 2011). Present in northern Oman at c. 2,500 m (Ghazanfar pers. comm. 2019). Globally, this species occurs from Pakistan to Iran (Board of Trustees, RBG Kew 2019). Plants of the World Online does not list the UAE as a native country of occurrence for this species, but its occurrence in the Hajar Mountains is consistent with an Oman-Makran distribution, characteristic of many other species of regional plants and animals.
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
There is limited information regarding Chesneya parviflora and its distribution within the UAE. Although this species has been recorded from the southern edge of the Ru'us al-Jibal and the Dibba zone, detailed distribution data is lacking. Furthermore, the threats to this species are currently unknown and there is more to learn about its habitat and ecology. Therefore, this species is currently assessed as 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
There is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Fagonia ovalifolia | 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
Fagonia ovalifolia is a perennial shrublet that is found on sandy plains.
Taxon
Taxa
Fagonia ovalifolia | Hadidi
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
The species is found across the sandy plains of the UAE, but is absent from the north-east of the country (Jongbloed et al. 2003, MEW 2010).Globally, its native range is considered to span across northern Africa, to the Arabian Peninsula 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 is widespread the southern emirates in the UAE. Although data are lacking on the population size and trend, the species is assessed as Least Concern as it is thought unlikely that it will approach the thresholds for a threatened category.
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
Grazing by livestock and feral animals may impact the species in parts of its range.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Cyanthillium cinereum | 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 species is an annual herb with slender stems that can reach up to 45 cm in height (Jongbloed et al. 2003). It has small, oval leaves and fruits with white tufts of hair, in addition to small purple-white flower-heads that can be seen between December and May (Jongbloed et al. 2003). This plant is generally found in plantations and fields (Jongbloed et al. 2003).
Taxon
Taxa
Cyanthillium cinereum | (L.) H.Rob.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
MEW (2010) considered this species to be widespread in the Hajar Mountains and in the Ru'us al Jibal in plantations, and Jongbloed et al. (2003) also reported the species from east coast plantations. However, the species seems to be absent from Feulner's (2011) study of the Ru'us al-Jibal. The global range of this species is across much of Africa, through the Arabian Peninsula, to East Asia and the Pacific (Board of Trustees, RBG Kew 2019). GRIN (2019) considers the species to be native to only Oman and Yemen in the Arabian Peninsula.
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 reported to be widespread through the Hajar Mountains and along the east coast in plantations. It is currently unclear as to whether it exists within the Ru'us al-Jibal. 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
There is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Bromus pectinatus | 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 perennial grass species can reach up to 80 cm in height (Jongbloed et al. 2003, Feulner 2014, El-Keblawy et al. 2016). It has coarse, narrow leaves and flower spikelets (Jongbloed et al. 2003, Feulner 2014). This plant grows within sandy habitats according to MEW (2010), however this requires confirmation.
Taxon
Taxa
Bromus pectinatus | Thunb.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species has been recorded from just below the summit of Jebel Al-Iyeli (c.1,000 m elevation) and from Wadi Helo (Feulner 2014, El-Keblawy et al. 2016), two nearby localities in the Olive Highlands. The global range of this species is Sahara to Kenya, Madagascar according to Plants of the World online (Board of Trustees, RBG Kew 2019), whilst Naderi and Rahiminejad (2015) give the distribution as South Africa, Kenya, Uganda, Ethiopia, Sudan, Morocco and Yemen. However, Plants of the World Online does not list the UAE as a native country of occurrence of this species.
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
Although this species has been recorded from two specific localities within the UAE, detailed data on its distribution in the country is required. For now, it is assessed as 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
There is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Centaurea pseudosinaica | 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
The species is found in coastal sands and sandy plains (Jongbloed et al. 2003, Sakkir and Brown 2014).
Taxon
Taxa
Centaurea pseudosinaica | Czerep.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
The species is found throughout the northern Emirates (MEW 2010), including Jebel Hafeet (Fawzi and Ksiksi 2007, Sakkir and Brown 2014) and Al Ain (Jongbloed et al. 2003), from at least the Taweela sands (Abu Dhabi Emirate; Brown et al. 2007) eastwards. The native range of this species is Iraq and southern Iran to the Arabian Peninsula (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 is widespread in northern parts of the UAE. Whilst subpopulations will have undergone a significant decline as a result of coastal development, it is thought that the species still qualifies 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
Grazing by livestock may impact the species in parts of its range, and impacts from coastal development are likely to have been significant.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off