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

Epinephelus areolatus | 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 continental shelf species is usually found in turbid water in seagrass beds or silty sand bottoms around isolated small rock outcrops, as well as near dead coral or soft coral as deep as 200 metres (Randall and Ben-Tuvia 1983, Leis 1987, Randall and Heemstra 1991). Juveniles are common to depths of 80 m (Kailola et al. 1993). It has also been observed on artificial reefs in Hong Kong (AFCD 2001). It feeds on fish and benthic invertebrates, primarily prawns and crabs (Parrish 1987, Randall and Heemstra 1991, Salini et al. 1994, Kulbicki et al. 2005). It is thought to spawn during seasonal periods and form spawning aggregations (Shapiro 1987). Maximum total length is 47 cm and maximum weight is 1.4 kg (Moran et al. 1988). The maximum reported age for this species is 15 years (Shapiro 1987), but a study conducted in northern Oman recorded a maximum age of 39 years and total length of 48 cm (J. McIlwain unpublished data). The length and age at first sexual maturity is 22.8 cm and 2 years for males and 23.5 cm and 2 years for females, respectively (Mahmoud 2009). When applying an age at first reproduction of 2 years and longevity of 39 years, its estimated generation length is 20 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
Epinephelus areolatus | (Forsskål, 1775)
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 (Russell and Houston 1989, Randall and Heemstra 1991, Randall et al. 2003). Its depth range is 2 to 200 metres.
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 species inhabits both soft and hard bottom habitats throughout UAE waters. It is exploited by grouper fisheries, and it appears likely that this species is overfished in the UAE. During the period from 2005-2016, a 67% decline in landings of this species occurred off Abu Dhabi. In addition, due to severe declines in Gulf coral reefs, this species may also be impacted by habitat degradation. The status of population(s) outside the UAE is not well-understood, though it is also heavily exploited elsewhere, especially off Oman and Iran. Based on fish market observations and catch data, it is inferred that this species has declined by at least 50-60% in the UAE since about 1995, or a little over one generation length (29 years). Fishing effort is expected to remain the same or increase in the future time period over the next two generations. Therefore, it is listed as Endangered A2bcd+4bcd.
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
Overexploitation is a major threat to this species in the UAE. Its occurrence in the trap (gargoor) fishery as ghost fishing may also cause mortality in this species. 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:

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Cephalopholis hemistiktos | 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 coral reefs and adjacent areas (Carpenter et al. 1997a). In the Red Sea, it is more often found on patchy open reef areas rather than on well-developed coral reefs. In Oman, it is abundant, but patchily distributed on shallow coastal reefs and rocky reef substrata (J. McIlwain pers. comm. 2015). Its maximum total length is 35 cm. It is a diurnal, ambush predator that feeds throughout the day on fishes and crustaceans (Craig et al. 2011). This is a monogamous species and pairs jointly defend a territory of up to 62 m'² (Shpigel and Fishelson 1991). Spawning occurs off Abu Dhabi from July to November and the mean age and total length at first sexual maturity for femalesis 13 years and 25.3 cm (Grandcourt et al. 2013). These data are not available for the Red Sea population. Longevity is at least 28 years in Oman, 24 years in the Red Sea (Priest et al. 2016) and 20 years in the Arabian Gulf (Grandcourt et al. 2013). We utilized the following data to estimate the generation length: natural mortality of 0.21 year<sup>-1</sup> and age at first maturity of 13 years (Grandcourt et al. 2013). The generation length equation (1/natural mortality) + age at first reproduction), estimates the generation length as 17.8 years, with three generation lengths being 53.4 years. However, this may be modified if the age at first maturity is found to be an overestimate.
Taxon
Taxa
Cephalopholis hemistiktos | (Rüppell, 1830)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Recent genetic and demographic evidence suggests that the population of Cephalopholis hemistiktos in the Red Sea and Gulf of Aden may be a distinct species from the population in the Arabian Gulf and Gulf of Oman (Priest et al. 2016).
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it has a disjunct distribution in the northwestern Indian Ocean, with one subpopulation in the Red Sea to Socotra Island (Yemen) and northern Somalia, and the second subpopulation in northern Oman (Sea of Oman), the Arabian Gulf and Pakistan. Recent research suggests these may represent two distinct species (Priest et al. 2016); however, until a formal description is published, both subpopulations are treated as one species. Its depth range is 2 to 55 metres.
Assessed status
Asessment status in full
Critically Endangered
Assessment status abreviation
CR
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 reef-associated species occurs throughout UAE waters. It is a long-lived species (26 years) that reaches sexual maturity late in life (13 years), and the generation length is estimated at about 17 years. A stock assessment conducted in 2013 in the Gulf considered this species overexploited. It was common in UAE fish markets from 1980s until about 1995, but declined thereafter. Despite fishing effort remaining at a stable level, catch of this species has remained very low to the present day. Effort is likely to increase for this species, especially as larger grouper species, such as Epinephelus coioides, continue to be depleted in this region. In addition, due to severe declines in Gulf coral reefs, this species may also be impacted by habitat degradation. Based on fish market observations, scientific survey data and catch data, it is inferred that this species has declined by at least 50% and likely more than 80% in the UAE since about 1995, or over the past one and a half generation lengths (29 years). Fishing effort is expected to remain the same or increase in the future time period over the next one and a half generations. The status of population(s) outside the UAE is not well-understood, though it is also heavily exploited elsewhere, especially off Oman and Saudi Arabia. Therefore, it is listed as Critically Endangered A2bcd+4bcd. Improvements in fisheries management 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
Overexploitation is a major threat. In addition, 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:

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Epinephelus polylepis | 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 occurs on rock and boulder slopes and also in areas with high coral cover (M. Samoilys pers. comm. 2016). Off southern Oman and eastern Yemen, it is frequently observed on coral reefs between 10 to 15 m depth (J. Kemp pers. comm. 2007). Off Muscat, Oman its preferred habitat is small rocky outcrops at 70-155 m depth. It has also been collected from trawls operating between 33-100 m depth on sandy bottoms (Randall and Heemstra 1991). This species may be a diandric protogynous hermaphrodite (J. McIlwain pers. comm. 2007), but this is not yet confirmed. Peak spawning in Oman occurs from August to October and may also extend into June-July (J. McIlwain pers. comm. 2007). Maximum total length is 120 cm (Bagley et al. 2009). In Oman, it has been aged to 40 years (J. McIlwain unpublished data). Age at first maturity is likely about 3-4 years (H. Choat pers. comm. 2007). When applying an age at first reproduction of 3-4 years and longevity of 40 years, its estimated generation length is 21-22 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
Epinephelus polylepis | Randall & Heemstra, 1991
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Prior to this species' formal description in 1991, it was identified as Epinephelus chlorostigma, particularly in India.
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is restricted to the northwest Indian Ocean where it occurs from the northern Gulf of Aden (Yemen and Djibouti) to the Arabian Gulf to southwestern India (Randall and Heemstra 1991, M. Samoilys pers. comm. 2016). It is not known to occur in the Maldives (Anderson pers. comm. 2007). Its depth range is 10-155 metres.
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 reef-associated species occurs throughout UAE waters. In the UAE, it is infrequently observed in markets, and is not recorded in fisheries statistics. It is heavily exploited in much of its range, and fishing pressure has been increasing and is expected to continue increasing. The relatively poor understanding of its' population status is in part due to it being historically misidentified as Epinephelus chlorostigma until its formal description in 1991 (only about 25 years ago). There are anecdotal reports of declining catch per unit effort in Oman, but landings quantified in the Arabian Gulf over the past 15 years have not declined, possibly due to increases in effort. The status of population(s) outside the UAE are not well-understood, though it is also taken by fisheries elsewhere. 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 potential major threat to this species, although declines have not yet been quantified and only anecdotal reports of declining catch per unit effort are known. Given that fishing effort has been increasing in the fisheries that take this species throughout its range, there is concern that declines are either occurring or will occur. 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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Epinephelus multinotatus | 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 coral and rocky reef, including drop-offs and banks (Randall 1995, Stephenson et al. 2001, J. Robinson pers. comm. 2007). Juveniles can be more common on coral reefs at least in the Gulf, while adults are often found in deeper waters around sandy or rocky substrates (Carpenter et al. 1997a). In general, younger individuals are found in the shallower portion of its range while adults occur deeper (Allen and Erdmann 2012). Spawning aggregations have been reported during peak reproductive months (Wheeler and Ommanney 1953, Robinson et al. 2004), and non-aggregating spawning likely occurs at other times during the year (J. Robinson pers. comm. 2007). Its maximum total length is 90 cm (Allen and Erdmann 2012) and its maximum age is 30 years (Grandcourt 2005). In Australia, females mature at about 41 cm and the species has been aged to at least 22 years (Bray 2016).
Taxon
Taxa
Epinephelus multinotatus | (Peters, 1876)
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 has a disjunct distribution in the Indian Ocean with one subpopulation occurring in the western part from Mozambique and Madagascar to the Gulf of Aden, Arabian Gulf, Sea of Oman and the Maldives and Chagos Archipelago, and the second subpopulation occurring in the east from northwestern Australia to Indonesia (Aru, Kei, and Tanimbar Islands). Its depth range is 10-110 metres (Allen and Erdmann 2012).
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 reef-associated species occurs throughout UAE waters. It is harvested in the Arabian Gulf and Sea of Oman, and landings, while fluctuating, show a modest downward trend off Saudi Arabia, Bahrain, Kuwait and possibly Oman. In the UAE, it is infrequently observed in markets, and is not recorded in fisheries statistics. The status of population(s) outside the UAE are not well-understood, though it is also taken by fisheries elsewhere, and some level of localised declines have been noted. 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 threat to this species in parts of its range(Craig et al. 2011, Chabanet et al. 2016). Reef degradation may also negatively impact this species (Pistorius and Taylor 2009). 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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Epinephelus latifasciatus | 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
Adults of this species inhabit coarse sand or rocky bottoms, while juveniles inhabit silty-sand and mud bottoms (Carpenter et al. 1997). It seems to prefer continental localities and low-relief bottoms. Its maximum standard length is 137 cm (Randall and Heemstra 1991). In India, the spawning season for this species occurs from November to March and lengths of males and females at 50% maturity are 66 and 61 cm total length, respectively (Sujatha Shrikanya 2013).
Taxon
Taxa
Epinephelus latifasciatus | (Temminck & Schlegel, 1842)
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 (Heemstra and Randall 1993). Its depth range is 20-230 metres.
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 demersal species inhabits soft and hard bottoms throughout UAE waters. Fishing activity is not known to be causing population declines at this time. There are no known major threats; therefore, it is listed as Least Concern 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
Fishing activity is not known to be causing population declines in the UAE at this time.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Olea europaea | 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
A tree that grows to at least 3-4 m in height in the UAE (G.R. Feulner pers. comm. 2019). The species is generally found along ridge tops, summit cliffs, and north and east-facing slopes and ravines of the Hajar Mountains above 800 m as well as, occasionally, in ravine beds in wadi bottoms at Wadi Hayl and Wadi Mayy (Feulner 2014).
Taxon
Taxa
Olea europaea | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Olea taxonomy is far from being clearly understood. Some molecular studies (Balboni et al. 2006, Besnard et al. 2009, Besnard et al. 2013) strongly suggest that there have been successive episodes of cross-breeding among wild, feral and cultivated forms of Olea europaea, throughout the Mediterranean region for several centuries. As the cultivated forms were brought from the eastern to the western Mediterranean, they also crossbred with spontaneous Olea subspecies and then became feral. As centuries passed, this process resulted in the gradual dilution of oriental haplotypes into the western haplotypes. However, it is considered that some of the conclusions presented in the above molecular studies are not robust, since they may lack some taxonomic accuracy regarding the sampled taxa (with different taxa sampled as the same taxon) (J. Capelo pers. comm. 2016) and therefore molecular studies are not yet conclusive in terms of the taxonomy of this species; we follow the classical taxonomic treatment from Green (2002). Four subspecies and one variety of Olea europaea L. are considered native to Europe (WCSP 2016):<ul><li>O. europaea subsp. cerasiformis G.Kunkel & Sunding</li><li>O. europaea subsp. europaea</li><li>O. europaea subsp. guanchica P.Vargas, J.Hess, Muñoz Garm. & Kadereit</li><li>O. europaea var. sylvestris Brot.</li></ul>These taxa are related to cultivated Olive.
Taxon distribution as listed in assessment
The species is found at higher elevations along connected high elevation ridges in the 'Olive Mountains' of the UAE. This species was first recorded for the UAE in 1997 at sites including the summit of Jebel Qitab (at c. 1,000 m asl), and above Wadi al-Iyeli; at each of these localities approximately two dozen specimens were present in adjacent ravines, and observations suggested that limited numbers were present in the intervening area (Feulner 1997). In general, it is restricted to the highest ridges of the Hajar Mountains southwest of Fujairah above 600 m (G.R. Feulner, in litt, MEW 2010, Feulner 2014). Records from the ""Olive Highlands"" area include the higher ridges above Wadi Mayy, Wadi Hayl and Wadi Saham, on north-facing cliffs of Jebel Al-Iyeli and on the northern slopes and ravines of Jebel Sfai (Feulner 2014). Individual small specimens have been found at wadi level in Wadi Hayl (M.A.R. Khan pers. comm. in Feulner 2014). The only other records are of two small trees (&lt;1.5 metres tall) on the northern slopes of Jebel Jabsah, and north of Wadi Ham on the outskirts of Fujairah city (Feulner 2014). The species is absent from Wadi Wurayah National Park (Feulner 2016) and from the Ru's al-Jibal (Feulner 2011). The EOO is less than 200 km<sup>2</sup>. The AOO has not been measured as detailed locality records are not available, but it is likely to also be 200 km<sup>2</sup>. It is considered to be native to the UAE. The species has been very widely cultivated so it is difficult to determine its full native range, but currently it is considered native to parts of Africa, Europe and western Asia.
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species was first recorded for the UAE in 1997 and is now known to be largely restricted to the 'Olive Highlands' area of the Hajar Mountains in eastern UAE, with additional records from northern slopes of Jebel Jabsah and north of Wadi Ham on the outskirts of Fujairah city. The extent of occurrence (EOO) is less than 200 km<sup>2</sup>. The area of occupancy (AOO) has not been measured as detailed locality records are not available, but it is likely to be less than 200 km<sup>2</sup>. The impact of current and potential threats are not known, however grazing by livestock and feral animals may account for the poor regeneration that was observed in the early 2000's. The species is assessed as Vulnerable (VU D1) because there are thought to be c. 500 mature individuals. No rescue effect is applied as, although the species occurs in Oman, no young trees have been seen. Conservation action and research is required for this species in order to protect significant subpopulations, and to understand the impacts of hybridisation and climate change in the mountains.
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 is at the northern extent of its range in these mountains. Individuals in wadi beds and the lower parts of ravines are vulnerable to grazing, development (housing, roads etc), and other threats. Grazing by livestock and feral animals might be the cause of the poor regeneration observed by G.R. Feulner (in litt, MEW 2010). There has been localised loss of individuals as a result of development (radio mast construction). In parts of the Olive Highlands, introduced (e.g., from Spain and Italy) olive plantations have been developed. Hybridisation between wild olives and planted olive trees is highly likely by pollinators and wind pollination.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
Same population size, although the individual trees were in better condition as a a result of higher rainfall.
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Varanus griseus | UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
Within the UAE, this species is found in desert regions including sandy and harder substrates, dry wadis, and hills. They also use agricultural areas, irrigated forestry plots (Gardner 2013) and waste disposal sites.
Taxon
Taxa
Varanus griseus | (Daudin, 1803)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxonomic Notes
The morphological diversity of this species complex is not adequately reflected in current subspecific divisions (Auliya and Koch 2020). This species is divided into three subspecies which occupy distinct geographical regions and can be identified by size, tail shape, and the number of bands on the body and tail. Varanus griseus griseus has a rounded tail and highest number of bands, Varanus griseus caspius reaches the largest size and has a laterally compressed tail, while Varanus griseus koniecznyi is the smallest subspecies and has the fewest bands (Stanner 2004).
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species is widespread throughout all of the mainland desert regions excluding the Hajar Mountains (Gardner 2013, Burriel-Carranza et al. in press). It occurs from sea level to 300 m asl. Globally, this is a widespread species of arid areas of North Africa, West and Central Asia (Corkill 1928, Martens and Kock 1992, Stanner 2004, Trape et al. 2012). In northern Africa, this species ranges from Western Sahara, Mauritania, northern Mali, and Niger in the west, throughout the Saharan desert region, to Egypt and Sudan in the east. From Egypt, the species ranges northwards through the southern and eastern Levant and into Turkey (southeastern Anatolia), Iraq and Iran. The species is present throughout the Arabian Peninsula.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
Within the United Arab Emirates, this species is widespread throughout all of the mainland desert regions excluding the Hajar Mountains. It is listed as Least Concern in view of its wide distribution, presumed large population, presence in several Protected Areas, it is unlikely to be declining fast enough to qualify for listing in a more 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
Urban development is the main known threat to the species in some parts of its distribution range within the United Arab Emirates. The species is also persecuted, and it is likely to be impacted by recreational driving on dunes and sandy areas.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Lutjanus argentimaculatus | 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 reef-associated species often occur in groups around coral reefs and sometimes extends to depths in excess of 100 m. Juveniles and young adults occur in mangrove estuaries, as well as the lower reaches of freshwater streams and tidal creeks (Lieske and Myers 1994, Sommer et al. 1996, Russell et al. 2003). This nocturnal species consumes fishes and crustaceans (Anderson and Allen 2001). The maximum total length is 150 cm (Torres 1991). The natural mortality for this species is measured at 0.158 (Russell et al. 2003). In a cooler part of its range, off eastern Australia, it has been aged at up to 57 years old (Piddocke et al. 2015). Spawning occurs off Abu Dhabi from September to October, longevity is estimated to be 37 years and the mean age and size at first sexual maturity is 14 years and 56.4 cm fork length for females and 13 years and 55.8 cm for males (Grandcourt et al. 2013). When applying an age at first reproduction of 14 years and longevity of 37 years, its estimated generation length is 25.5 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
Lutjanus argentimaculatus | (Forsskål, 1775)
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 widely distributed in the Indo-West Pacific (Anderson and Allen 2001). Its depth range is 1 to 120 m (Lieske and Myers 1994).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
A2bcd
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 reef and estuarine-associated species occurs throughout UAE waters. It is heavily exploited and very highly-valued in the Arabian Gulf, including the UAE. A 2013 Abu Dhabi stock assessment concluded it is overexploited, especially due to the high rate of juvenile retention, which has led to growth overfishing. Though catch quantity has been relatively low over the time period from 2009-2018, it has virtually disappeared from fisheries catch on both coasts of the UAE. In addition, mangrove and estuarine degradation in the Arabian Gulf region is serious, and a likely additional threat to nursery habitat for this species. The status of population(s) outside the UAE is not well-understood, but it is exploited elsewhere as well. Based on stock assessment, catch data and fish market observations, this species is inferred to have declined by at least 50% or possibly more than 80% over at least half of a generation length, or the past decade. Three generation lengths is about 75 years, but data are not available to calculate a decline over this period. Considering this species is particularly long-lived and late to maturity, it is intrinsically susceptible to declines from overexploitation. Assuming that the population was stable previous to 2009, we suspect a decline of at least 50% with an expected continuing decline due to fishing effort trends. It is listed as Endangered A2bcd.
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 UAE (Grandcourt et al. 2013). In addition, juveniles are dependent on mangroves and associated freshwater-influenced areas, which is a habitat that has been destroyed or severely degraded in the Arabian Gulf region as a result of coastal development (A. Al-Kuwari, E. Abdulqader, F. Kaymaram, K. Al-Khalaf, J. Bishop, Q. Alghawzi, S. Alam, S. Hartmann pers. comm. 2013). Historically, mangrove area declined on the Arabian Gulf coast of the UAE, but since the 1990s, mangrove area has increased somewhat in part due to restoration efforts. The percent decline over the entire time period of three generation lengths is poorly understood. 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:

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Isurus paucus | 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 Longfin Mako is a poorly-known epipelagic, tropical and warm-temperate shark, and its full depth range is unknown (Compagno 2001). It attains a maximum size of at least 427 cm total length (TL). Both males and females have been reported to mature at &gt;245 cm TL with the smallest mature male observed at 225 cm TL (Varghese et al. 2017). It is aplacental viviparous with oophagy and uterine cannibalism, and a pregnant female may have 2 to 8 embryos per litter. Size at birth is recorded at 97 to 120 cm TL (Compagno 2001). It has been suggested that females may approach land to pup (Compagno 2001). The generation length is suspected to be around 25 years, based on that of the Shortfin Mako (Isurus oxyrinchus) (Natanson et al. 2006).
Taxon
Taxa
Isurus paucus | Guitart, 1966
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Longfin Mako occurs in UAE waters on the Sea of Oman coast. It is excluded from the Arabian Gulf (Golani and Bogorodsky 2010). Globally, it is likely circumglobal in tropical and warm temperate waters. However, records are sporadic and the complete distribution remains unclear in part due to confusion with the more common Shortfin Mako (Isurus oxyrinchus) (Compagno 2001).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
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
In UAE waters, the Longfin Mako occurs only in offshore waters of the Sea of Oman. Little is known on the population of this species in UAE waters. It is caught incidentally in pelagic longline fisheries, but comprises much lower proportions of the catch than the Shortfin Mako (Isurus oxyrinchus). Most catches of this species are inadequately recorded and likely underestimated. Its apparent rarity, large size, low fecundity and continued occurrence as bycatch in fisheries is concerning. It is apparently highly migratory, and has slow life history characteristics including low fecundity and a low annual rate of population increase. Considering this, the species has a low capacity to recover from even moderate levels of exploitation. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. 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. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation, it is suspected to have declined by 20-30% over the past three generation lengths, or about 75 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable 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
In the UAE, sharks have been impacted by targeted commercial fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). Sharks continue to be impacted by artisanal and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018), though catch data are not species-specific. This species is impacted by bycatch fisheries that are active elsewhere in its range.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Mobula thurstoni | 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 Bentfin Devil Ray is usually pelagic or epipelagic in shallow, productive, neritic waters of &lt;100 m depth (Notarbartolo di Sciara 1988, Croll et al. 2016), although it is also caught in offshore pelagic waters (Mas et al. 2015), and around seamounts in the Mid-Atlantic Ridge (Mendonça et al. 2012). Segregation by size and sex is seasonal, with all size classes and sexes appearing together during the summer months (Notarbartolo di Sciara 1988). The species is observed either solitarily or in small groups (2-“6 individuals); it is not a schooling species (Notarbartolo di Sciara 1988). Maximum size is reported to at least 189 cm disc width (DW) and both females and males are estimated to mature at around 154 cm disc width (DW), while size at birth is estimated at 65-“85 cm DW (Notarbartolo di Sciara 1988, Last et al. 2016). Size at 50% maturity was estimated at 153.8 cm DW for males (White et al. 2006b). The mode of reproduction is matrotrophic viviparity. Embryos obtain nutrients initially via yolk, then through absorption of enriched uterine fluid from the mother (Wourms 1977). Only the left ovary is functional and litter size is one pup after a 12-month gestation period (Wourms 1977, Notarbartolo di Sciara 1988). It is estimated that the maximum intrinsic population growth rate (r<sub>max</sub>) of devil rays is similar to manta rays, and these productivity rates are among the lowest of all chondrichthyans (Dulvy et al. 2014, Pardo et al. 2016). Mating, parturition, and early life history are reported to take place in the shallow water during summer and perhaps early autumn (Notarbartolo di Sciara 1988).For the Spinetail Devil Ray (up to 310 cm DW), Cuevas-Zimbrón (2012) estimated age at maturity to be 5-“6 years and a minimum lifespan of 14 years, giving a generation length of 10 years. While accurate age at maturity and longevity information is unavailable for the Bentfin Devil Ray, it can be inferred according to the smaller maximum size that it would be close to but slightly shorter than that of its congener. As there are not enough data to estimate an exact generation length for this species, an approximate, suspected generation length is used. A midway point of 7.5 years between a very conservative low of five years, and the larger Spinetail Devil Ray's 10-year generation length is suspected to be the approximate generation length for the Bentfin Devil Ray until more accurate information becomes available.
Taxon
Taxa
Mobula thurstoni | (Lloyd, 1908)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Bentfin Devil Ray occurs in UAE waters on the Sea of Oman coast. It is excluded from the Arabian Gulf. Elsewhere, it is distributed in tropical, subtropical, and temperate waters of the Indian Ocean from the Red Sea to India, Sri Lanka, and the Maldives (Couturier et al. 2012, Notarbartolo di Sciara et al. 2017).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
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
In UAE waters, the Bentfin Devil Ray occurs only in the Sea of Oman in inshore and offshore waters. This species is not targeted or valued in markets of the UAE and capture of this species is totally banned in the UAE. When captured in the Sea of Oman, it is typically discarded alive, and significant declines are not suspected there at this time. It is a component of the bycatch in several fisheries (e.g., Pakistan), and is directly targeted in Sri Lanka and India. Its low productivity causes it to be susceptible to rapid population declines, and declines have recently been confirmed from Pakistan (over the past three years). It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. 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. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. There is no information to confirm that this species is breeding in the UAE and no information confirming the likelihood of a cease in immigration from outside the region, despite ongoing threats and recorded declines. Based on recorded levels of exploitation, it is suspected to have declined by 30-50% over the past three generation lengths, or about 23 years. It is listed as Vulnerable 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 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. Manta rays are easy to target because of their large size, slow swimming speed, aggregation behaviour and predictable habitat use.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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