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

Teucrium stocksianum | 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 shrublet species grows on hillsides and within wadis (Jongbloed et al. 2003, Mahmoud et al. 2018). It has a perennial life cycle and can reach up to 25 cm in height (Jongbloed et al. 2003). The plant is woolly, has oval leaves with scalloped edges, small nutlet fruits and pink-cream flowers which are present between February and May (Jongbloed et al. 2003).
Taxon
Taxa
Teucrium stocksianum | Boiss.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, it occurs throughout the Hajar Mountains and in the Ru'us al-Jibal (Jongbloed et al. 2003, Judas 2016). It is considered to grow at all elevations (Jongbloed et al. 2003). Globally, the native range of this species spans from the Arabian Peninsula 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 described as growing throughout the Hajar Mountain range in the UAE, in addition to occurring in at least one protected area within its range. It is described as common and can grow at a wide range of altitudes. Although this species may be affected by grazing, the extent of this threat is currently unclear. Therefore, 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
Grazing by goats may impact this species in parts of its range (Feulner 2011).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Saccharum kajkaiense | 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 wadi-bed species that is more dependent on permanent or regular access to near-surface water than S. griffithii, and it is always found close to water or where the soil remains moist even in the summer (Feulner and Karki 2009), such as near streams and springs. The species does not exceed c. 1.5 m in height (Feulner and Karki 2009). The seed dispersal mechanisms for this species are not known, but potentially include wind, water, by animals (epizoochorously or endozoochorously), as well as by human transport. Seed dormancy in the seedbank is also not known.
Taxon
Taxa
Saccharum kajkaiense | (Melderis) Melderis
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species has a restricted distribution in the UAE, where it is known from two sites in the Hajar Mountains. Feulner and Karki (2009) undertook fieldwork to search for the species in suitable habitat in northern Oman and in the UAE, finding the species at just two sites in the UAE; Wadi Shawka and Wadi Wurayah National Park (a single location above the Wadi Wurayah waterfall; Feulner 2016). G.R. Feulner (pers. comm. 2019) also found the species at Wadi Hala (Ras al Khaimah). Saccharum kajkaiense has also been recorded from a locality south-east of Shawqa (Dave Aplin pers. comm. 2019). Given the records from adjacent parts of Oman to the west, south, and southeast of Hatta (including at Wadi Qahfi, part of the 'Hatta Pools'), the presence of the species in suitable habitat (permanent water) within the UAE around Hatta might be expected, but it was not found during surveys by Feulner and Karki (2009). The species may occur at other sites with permanent water, as it is difficult to identify S. kajkaiense amongst the large background populations of S. griffithii (G.R. Feulner pers. comm. 2019). Based on the four currently known localities, the AOO is 16 km<sup>2</sup> using a 2x2 km grid, although the actual area where this species occurs is very much less, just a few square meters. It is considered to occur at four threat-based locations. The altitude range in the UAE is c. 200 - 450 m asl, but it is found to above 1,000 m in neighbouring parts of Oman. R.A. Western (<a href=""http://data.rbge.org.uk/herb/E00240941"">RBG Edinburgh Herbarium specimen</a>) collected the species in 1990 from Wadi Rayy in Oman, just south of Hatta in the UAE and Cock (2009) collected the species from east of Hatta (Wadi Qahfi), also in Oman. Feulner and Karki (2009) summarise the known records for the UAE and northern Oman. The global distribution of this species is from Afghanistan, Pakistan, and Iran, to the Arabian Peninsula (Oman and the United Arab Emirates; Cope 2007, Feulner and Karki 2009).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
B1ab(iii)+2ab(iii); 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 species has a very restricted known distribution in the UAE, where it is currently known from a few locations in the Hajar Mountains. Given the records from adjacent parts of Oman, the presence of the species in suitable habitat around Hatta within the UAE might be expected, but it was not found during surveys by Feulner and Karki (2009). Based on the currently known localities, the area of occupancy (AOO) is very much less than 50 km<sup>2</sup> measured using the required 2x2 km grid, however, the actual area represented by the two localities is probably just a few square meters. The extent of occurrence (EOO) is around 280 km<sup>2</sup>. In addition, the species occurs in four threat-based locations and is thought to be undergoing a continuing decline in the extent and quality of habitat. As a result, the restricted distribution meets the threshold for Endangered under Criterion B1 and B2. Overall, the three known localities in the UAE comprise c.100 plants (inferred here to equal mature individuals). Both sites are subject to heavy recreational use. Therefore, the species also qualifies as Endangered under Criterion D, due to the small number of mature individuals. Whilst the seed dispersal mechanisms for this species are not known, the potential for dispersal from adjacent populations in Oman (by wind, water, by animals (especially water birds), as well as by human transport) is considered to be high. As a result, the category is downgraded by one category from Endangered to Vulnerable (VU B1ab(iii)+2ab(iii); D) for this UAE national assessment. Monitoring is essential for this species, and it should be reassessed if new data become available on, for example, new records for the UAE, population size or trend, or the potential for seed immigration from Oman.
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
The habitat of this species is prone to change and damage. The exploitation of water resources (e.g. the Wadi Shawka dam) is a potential threat.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assumed that the species occurred with a similar distribution and population size in 1996.
Verified entry
Off

Lethrinus nebulosus | 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
This species inhabits nearshore and offshore coral reefs, coralline lagoons, seagrass beds, mangrove swamps, coastal sand and rock areas to depths of 75 m (Carpenter and Allen 1989). It is occasionally observed in small aggregations (Randall 1995), but adults typically occur singly. It primarily consumes molluscs, crustaceans, echinoderms and less often polychaetes and fishes (Carpenter and Allen 1989). The maximum total length is 87 cm (Assadi and Dehghani 1997). This species undergoes a protogynous sex change that occurs over a wide range of year groups starting with age 1, well before maturity (McPherson et al. 1985). Longevity is estimated to be 14-26 years (Mathews and Samuel 1991, Edwards and Shaher 1991, Dalzell et al. 1996, Grandcourt 2006, Ebisawa and Ozawa 2009). Off the Ryukyu Islands of Japan, the age of 50% ovarian maturity was 4 years (Ebisawa and Ozawa 2009). This species forms spawning aggregations (Salem 1999). In the southern Arabian Gulf, spawning occurs between April to May, the mean size and age at first sexual maturity for males and females to be 19.4 cm and 0.5 years for males and 28.9 cm and 2.7 years for females, and maximum age was 11 years (Grandcourt et al. 2006 and 2010). When applying an age at first reproduction of 3 years and longevity of 11 years, its estimated generation length is 7 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Taxon
Taxa
Lethrinus nebulosus | (Forsskål, 1775)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Lethrinus nebulosus may represent a complex of species, and further taxonomic work is required (K. Carpenter pers. comm. 2015). A cryptic species under L. nebulosus was detected in a study off southeastern Africa, but further study is required to resolve the taxonomy and distribution (Healey et al. 2018).
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. As is currently understood on the global-level, it is widespread in the Indo-West Pacific (Carpenter and Allen 1989). Its depth range is 0 to 90 m (R. Myers pers. comm. 2015).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
A2bcd+4bcd
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, reef-associated species occurs throughout UAE waters. It is heavily exploited in the UAE, and stock assessments conducted for Abu Dhabi in 2006, 2010 and 2018 reported it as overfished. Based on catch data and stock assessments, this species has undergone an inferred declined of at least 52-78% over the past two generation lengths, or 14 years. With recent fisheries management measures implemented in Abu Dhabi, it is difficult to say whether fishing effort will continue to increase or decrease within the near future. Considering that other Emirates and surrounding countries that likely share this stock do not have management measures in place to reduce effort in the gargoor fishery, population declines are expected to continue. In addition, degradation of coastal habitats in the UAE and Arabian Gulf region, especially for coral reefs, is expected to continue. The population in UAE is inferred to have some level of connectivity with those in surrounding countries, and declines have been reported from Saudi Arabia, Qatar and Kuwait. It is listed as Endangered A2bcd+A4bcd. In addition to improvements needed in fisheries management, taxonomic research is also recommended.
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
Overfishing is a major threat to this species in the Arabian Gulf. 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
Off

Lethrinus microdon | 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
This speciesinhabits sandy areas near coral reefs as well as on seagrass beds. It shoals in small schools and actively feeds during the day and night on fishes, crustaceans, cephalopods and polychaetes (Carpenter and Allen 1989, Dorenbosch et al. 2005). The maximum total length is 80 cm (Kuiter and Tonozuka 2001). This species is fast-growing and short-lived with a high natural mortality rate. In the southern Arabian Gulf, spawning occurs between June and November and the mean age and size at sexual maturity is 3 years and 27.4 cm for males and 4.8 years and 29.1 cm for females (Grandcourt et al. 2010). A study conducted in the Red Sea off Egypt reported longevity of this species as 7 years (Mehanna et al. 2017). When applying an age at first reproduction of 5 years and longevity of 7 years, its estimated generation length is 6 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Taxon
Taxa
Lethrinus microdon | Valenciennes, 1830
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Carpenter and Allen 1989, Randall 1995). Its depth range is 10-80 m (Carpenter and Allen 1989).
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
This inshore, reef-associated species occurs throughout UAE waters. Despite an Abu Dhabi stock assessment reporting it as underexploited as of 2016, catch has declined by 75% over the past two generation lengths, or since 2009. This conflicting information cannot be clearly explained, in part due to the lack of information regarding fishing effort trends. It is also heavily exploited in areas outside the UAE. Based on the potential major threat from overfishing, this species is listed as Data Deficient in the UAE. Improvements in fisheries monitoring are needed.
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
Overfishing is a potential major threat to this species in the UAE and surrounding areas. 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
Off

Lethrinus lentjan | 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
This species inhabits coastal, sandy areas, coral reefs, and deep lagoons to depths of 50 m. It primarily consumescrustaceans, molluscs, echinoderms, polychaetes and fishes (Sato and Walker 1984, Carpenter and Allen 1989). This species is a protogynous hermaphrodite and exhibits a protracted spawning season (Currey et al. 2013). In some areas, particularly Thailand, this species has been observed forming spawning aggregations (Tamelander et al. 2008). This is a fast-growing, short-lived species with high natural mortality. A study conducted in the southern Arabian Gulf reported its maximum age as 11 years, spawning occurs from April to June, and mean age and size at sexual maturity was 1.8 years and 24.6 cm for males and 2.4 years and 27.7 cm<sub> </sub>for females (Grandcourt et al. 2011). When applying an age at first reproduction of 2.5 years and longevity of 11 years, its estimated generation length is 6.75 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Taxon
Taxa
Lethrinus lentjan | (Lacepède, 1802)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Sato and Walker 1984, Carpenter and Allen 1989, Carpenter 2001). Its depth range is 0 to 50 m.
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
This inshore, marine species occurs throughout UAE waters. Catch declines of about 90% have occurred in Abu Dhabi over the past two generation lengths. Two recent stock assessments reported conflicting results - one assessed the stock as overfished, while the other assessed it as under-exploited. Due to this, the population status is poorly understood. With recent fisheries management measures implemented in Abu Dhabi, it is difficult to say whether fishing effort will continue to increase or decrease within the near future. Considering that other Emirates and surrounding countries that likely share this stock do not have management measures in place to reduce effort in the gargoor fishery, population declines may continue. The status of this species outside the UAE is not well-understood, but it is exploited elsewhere in the Gulf region. Due to the uncertainty regarding its population status, it is listed as Data Deficient 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
Overfishing is a potential major threat. Studies on this species in the UAE indicates it retains heavy metals sourced from nearshore pollution (Kosanovic et al. 2007). 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
Off

Lethrinus borbonicus | 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
This marine species inhabits the sandy bottoms of seagrass beds and on or near coral reefs at depths of 1 to 40 m (Carpenter 1989, Khalaf et al. 2012). During the day, it is found to a depth of 40 m, occasionally occurring in small groups; however, at night, itis solitary and found over reef-flats and slopes as shallow as 1 m in depth. Itsdiet consists of echinoderms, mollusks and crustaceans. The maximum total length is 40 cm (Carpenter and Allen 1989). A study conducted in the southern Arabian Gulf, reported a maximum age of 9 years, spawning occurs from March to June, it is a short-lived, fast growing species with a high natural mortality rate, and the mean age and size at sexual maturity was 2 years and 22.1 cm for males and 1.3 years and 21.3 cm<sub> </sub>for females (Grandcourt et al. 2010). When applying an age at first reproduction of 2 years and longevity of 9 years, its estimated generation length is 5.5 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Taxon
Taxa
Lethrinus borbonicus | Valenciennes, 1830
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is restricted to the Western Indian Ocean where it occurs from South Africa, Madagascar, the Mascarenes and the Seychelles to the Red Sea, Arabian Gulf and Pakistan (Carpenter 1989, Carpenter and Allen 1989, Gaudian et al. 1995, Gillibrand 2007, K.E. Carpenter pers. comm. 2014). Its depth range is 1 to 40 m (Carpenter 1989).
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
This inshore, reef-associated species occurs throughout UAE waters, and can be common in the Arabian Gulf. A 2010 stock assessment considered the Abu Dhabi stock to be overexploited, and in 2016, the stock was considered fully exploited. Catch in Abu Dhabi has declined by 81% over the past two generation lengths, or about 10-12 years. Fishing effort has declined in Abu Dhabi due to fisheries management to reduce the gargoor fishery since 2007, but catch declines are not fully explained by this. The status of population(s) outside the UAE are not well-understood. Based on the uncertainty regarding the population trend of this exploited species, it is listed as Data Deficient in UAE waters. Improvements in fisheries monitoring are needed.
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
Overfishing is a major threat to this species in the Arabian Gulf (Grandcourt et al. 2010). According to a study conducted in the Red Sea, this species can retain relatively high levels of PAHs (Ali et al. 2014). 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
Off

Elagatis bipinnulata | 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
This pelagic species occurs mainly near the surface, over reefs and sometimes offshore (Berry 1969). It may form large schools and prey items include invertebrates and fish. The maximum size is 107 cm fork length, but is common to 80 cm (Smith-Vaniz 2002). Its depth range is 1-150 m (Lieske and Myers 1994). Spawning is thought to occur throughout the year in the Indo-Pacific and Western Atlantic (Okiyama 1970, Aprieto 1974, Yesaki 1979).
Taxon
Taxa
Elagatis bipinnulata | (Quoy & Gaimard, 1825)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
In UAE waters, this species occurs only in the Sea of Oman. There are no confirmed records from the Arabian Gulf (W. Smith-Vaniz pers. comm. 2013). Elsewhere, it is circumtropically distributed in tropical waters (Smith-Vaniz 2002, Simon et al. 2013, Friedlander et al. 2014, Smith-Vaniz 2016). The depth range is 1-150 m (Lieske and Myers 1994).
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
In the UAE, this pelagic speciesoccurs only in the Sea of Oman. It is commercially and recreationally exploited in UAE waters, but little information on catch is available. It is frequently taken as bycatch in tuna purse seine fisheries in the Sea of Oman. Fishing is not known to be causing large-scale declines at this time; therefore, it is listed as Least Concern in the UAE. It is recommended to improve fisheries monitoring of this species.
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
Fishing activity is not known to be driving declines approaching a Near Threatened or threatened level in the UAE at this time. 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
Off

Saccharum griffithii | 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 usually found on gravel near water in wadis (MEW 2010, Feulner 2011). It is a perennial tussock-forming grass that grows to c. 2 m in height, with flower spikes that can grow up to one metre above that (Feulner and Karki 2009). Brown (<a href=""http://data.rbge.org.uk/herb/E003"">RBGE specimen</a>) recorded the species in slow-flowing water in a wadi, and in a saline pool (<a href=""http://data.rbge.org.uk/herb/E00358630"">RBGE specimen</a>).
Taxon
Taxa
Saccharum griffithii | Munro ex Aitch.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is widespread in the Hajar Mountains in suitable habitat (near water in wadis; MEW 2010). It has also been recorded from Abu Dhabi and Al Wagan (A.R. Western, U. Deil and F. Karim; Jongbloed et al. 2003). The species is recorded from Wadi Wurayah (Feulner 2016, Judas 2016). The species is absent or rare in the Ru'us al-Jibal (Feulner 2011). RBG Edinburgh holds specimens from; 1. <a href=""http://data.rbge.org.uk/herb/E00358631"">Wadis around Hatta</a>, (300 m asl), 2. <a href=""http://data.rbge.org.uk/herb/E00358628"">fringing the oasis at Qidfa'</a> (Fujairah), 3. Wadi Ham between Masati and Fujairah, and 4. <a href=""http://data.rbge.org.uk/herb/E00358630"">Abu Dhabi to Al Ain roa</a>d at al Khanza south; this latter record is a long way outside the otherwise known distribution of the species in the UAE, and is discounted here. Globally, this species occurs through the Arabian Peninsula to Iran, the western Himalaya and Bangladesh (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 the Hajar Mountains of the UAE. Whilst subpopulations may have been impacted by livestock grazing, 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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Juncus socotranus | 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 that is found in wadis where water is close to the surface (G.R. Feulner in lit., MEW 2010), and submerged in freshwater (Al Meharibi et al. 2019).
Taxon
Taxa
Juncus socotranus | (Buchenau) Snogerup
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is widespread in the Hajar Mountains (Jongbloed et al. 2003, Al Meharibi et al. 2019). The global distribution of this species is from Socotra to Iran (Kirschner 2002, 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 found in the Hajar Mountains in the eastern UAE. It is common in suitable habitat, and whilst its freshwater-dependent habitat is susceptible to over-abstraction of groundwater and declines in rainfall, the species is considered Least Concern 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
The species would be susceptible to the over-abstraction of ground and surface water, however, the scope and impact of this within the range of the species in the UAE are not known. Long term declines in rainfall as a result of climate change are likely to impact the species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Vernonia arabica | 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 on wadi banks and mountain slopes (Jongbloed et al. 2003). In the WWNP, the species is typically found on stony slopes and in gulleys, as well as along the wadi floor, more common at higher elevations (Feulner 2016). It is a perennial herb with woody stems (up to 0.35 m in height) that flowers between February and April (Jongbloed et al. 2003).
Taxon
Taxa
Vernonia arabica | F.G.Davies
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
The species is widespread in the Hajar Mountains and the Ru'us al-Jibal, and has also been recorded from Jebel Hafeet (Jongbloed et al. 2003). In the Ru'us al-Jibal, the species occurs at low to moderate elevations (c.150-950 (1,250 m) in the southern and (outside the UAE) eastern Ru'us al-Jibal (Feulner 2011). the species occurs in Wadi Wurayah National Park (WWNP; Feulner 2016). The native range of this species spans across north-east Africa (Somalia) and the Arabian Peninsula (Yemen to the UAE) (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 northeastern parts of the UAE and 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
In the Ru'us al-Jibal, Feulner (2011) observed that the species was heavily impacted by grazing at lower altitudes.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off