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

Triaenodon obesus | 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
Whitetip Reef Sharks are closely associated with coral reefs in clear, tropical waters. This species is primarily nocturnal, sheltering in caves by day, often communally. Maximum size is around 200 cm total length (TL), but adults are very rare over 160 cm. Maturity is attained at about 105 cm TL, although a mature male of 95 cm TL and a pregnant female of 102 cm TL have been recorded in the Maldives (Anderson and Ahmed 1993). Mating has been recorded in the wild by Tricas and Le Feuvre (1985) and pups are born at 52-60 cm TL after a gestation period of at least five months. Litter size has been recorded as 2-3 in Madagascar (Fourmanoir 1961, Last and Stevens 1994) and 1-5 elsewhere (Randall 1977, Last and Stevens 1994). Growth is slow in the wild, estimated at 2.1-4.2 cm year<sup>-1</sup> (Randall 1977), and it may attain sexual maturity at eight to nine years and live to about 16 years (Randall 1977, Smith et al. 1998). Generation length is estimated to be 12.25 years (Randall 1977).
Taxon
Taxa
Triaenodon obesus | (Rüppell, 1837)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Whitetip Reef Shark may occur in UAE waters on the Sea of Oman coast, but this is not yet confirmed. It is excluded from the Arabian Gulf (Al Jufaili et al. 2010). Globally, it is widespread in the tropical Indo-West Pacific (Last and Stevens 2009).
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
In the UAE, the Whitetip Reef Shark possibly occurs only in coastal waters of the Sea of Oman, but this is not yet confirmed. The species exhibits moderately slow life history characteristics, and is impacted by extensive fishing pressure and habitat loss and degradation throughout the Arabian Sea region. Little is known on the population of this species in UAE waters and given 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 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:

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Prionace glauca | 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 Blue Shark is oceanic and pelagic, found from the surface to depths of 1000 m (Weigmann 2016). It occasionally occurs close inshore when the continental shelf is narrow. This species reaches a maximum size of about 380 cm total length (TL). About 50% of males in the Atlantic are sexually mature by 218 cm, although some may reach maturity as small as 182 cm TL. Females are sub-adult from 173-221 cm TL and fully mature from 221 cm TL (Pratt 1979), although pregnant specimens as small as 183 cm TL have been recorded from the eastern Pacific (Williams 1977).Blue Sharks are placentally viviparous, producing litters averaging about 35 pups (maximum recorded 135) after a gestation period of 9-12 months. At birth, pups measure 35-50 cm TL. Reproduction has been reported as seasonal in most areas, with the young often born in spring or summer (Pratt 1979, Stevens 1984, Nakano 1994) although the periods of ovulation and parturition may be extended (Hazin et al. 1994). Ageing studies suggest a longevity of about 20 years with males maturing at 4-6 and females at 5-7 years (Stevens 1975, Cailliet et al. 1983, Nakano 1994). Smith et al. (1998) estimated the intrinsic rate of population increase at MSY to be 0.061.Generation length is estimated to be 10.5 years based on study of Blue Shark in the Northwest Pacific by Nakano (1994).
Taxon
Taxa
Prionace glauca | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Blue Shark may occur in UAE waters on the Sea of Oman coast, but is not yet confirmed from there. It is excluded from the Arabian Gulf. Globally, it occurs throughout tropical and temperate seas from latitudes of about 60'°N to 50'°S (Last and Stevens 2009).
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
In UAE waters, the Blue Shark may occur only in offshore waters of the Sea of Oman, though this remains unconfirmed. This species is considered productive, as it is relatively fast-growing and fecund. Around the world, the Blue Shark is taken in large numbers (an estimated 20 million individuals annually), mainly as bycatch, but there are no population estimates and many catches are unreported. IOTC fishery assessments suggest a wide range of stock statuses ranging from 'underexploited' to 'overfished with overfishing' occurring. Little is known on the population of this species in UAE waters. Given that its distribution in UAE waters (the Sea of Oman) remains uncertain, this species 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
Given the lack of clarity around the species occurrence in UAE waters, threats are poorly understood. 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. 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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Galeocerdo cuvier | 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 Tiger Shark inhabits reef and slope habitats, is sometimes associated with coral reefs, and occasionally makes longer-distance excursions into the pelagic zone. It regularly dives to depths greater than 1000 m and has been noted to move hundreds to thousands of kilometres (Holmes et al. 2014, Werry et al. 2014). It attains a maximum size of at least 550 cm total length (TL). In the north-west Hawaiian Islands, Tiger Sharks with a precaudal length of 200 cm were estimated to be about five years old and one of 300 cm was about 15 years old (De Crosta et al. 1984). Branstetter et al. (1987) estimated that initial growth was very fast, but that the rate of growth of very large animals is 5-10 cm year<sup>-1</sup>; thus, individuals of 400-450 cm TL would be 20-25 years of age. Branstetter et al. (1987) reported a maximum age of 45-50 years. Smith et al. (1998) estimated the intrinsic rate of increase of a tiger shark population at MSY to be 0.043 year<sup>-1</sup>. Randall (1992) summarised that the size at maturity of males is 226-290 cm TL and females 250-350 cm TL.The Tiger Shark is the only species in the Carcharhinidae family that is lecithotrophic viviparous. Litter sizes are large, with between 10-82 embryos reported from a single female. Mean litter sizes of 30-35 have been reported (Tester 1969, Bass et al. 1975, Simpfendorfer 1992). The size at birth is 51-90 cm TL (Randall 1992, Simpfendorfer 1992). Clark and von Schmidt (1965) reported the gestation period as 13-16 months. There have been few other estimates of gestation period. Mating is reported to take place in the Northern Hemisphere in spring, with pupping the following spring to summer. Mating occurs before full-term females have given birth to young, indicating that litters are produced every two years or less. Based on data from the North West Atlantic, generation length is estimated at 17.5 years (Natanson et al. 1999).
Taxon
Taxa
Galeocerdo cuvier | (Péron & Lesueur, 1822)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Tiger Shark occurs throughout UAE waters. Globally, it is widespread in tropical waters (Last and Stevens 2009).
Assessed status
Asessment status in full
Critically Endangered
Assessment status abreviation
CR
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
The Tiger Shark occurs throughout UAE waters. In the UAE, this species has historically been impacted by both targeted fishing and by-catch as well as habitat degradation and loss from coastal development. Catch in the UAE has declined by about 90% over the past three generation lengths. A series of conservation measures have been put in place to reduce shark fishing effort in UAE waters since 2008. 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. Elsewhere in the Arabian Sea region, this species has also experienced documented declines (e.g., Iran, the Red Sea, Yemen, Pakistan and India). Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Based on fish market surveys, fisher interviews, recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 80% over the past three generation lengths, or about 52 years. It is listed as Critically Endangered A2bcd. Monitoring of the species population trend moving forward should be a priority.
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, this species has historically been impacted by both targeted fishing and by-catch, habitat degradation and loss from coastal development. Finning has been banned in the UAE, yet surveys indicate that some trade in the fins and meat of this species still occurs. Sharks are impacted by high levels of largely unmanaged and unreported mortality in target (for fins and their valuable meat) and bycatch fisheries. 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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Carcharhinus melanopterus | 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 Blacktip Reef Shark is found in inshore habitats, especially associated with coral reefs and sandy areas to depths of 100 m. Adults reach total lengths of up to 180 cm total length (TL) and mature between 90-110 cm TL (Compagno 1984, Stevens 1984, Last and Stevens 1994). Size at birth has been reported at 30-52 cm TL. Information on reproductive biology is limited and conflicting. Blacktip Reef Sharks are viviparous with a yolk sac placenta and give birth to 2-4 pups (usually four) (Compagno 1984, Lyle 1987, Last and Stevens 1994). Data from Sudan suggests a 9 month gestation period in the region (I. Elhassan pers.comm. 09/02/2017). The only age data available is from Australia (Chin et al. 2013). Females mature at 8.5 years and reach a maximum age of at least 15 years. This yields a generation length of 11.5 years. During the breeding season (November and March (Mourier and Planes 2013).
Taxon
Taxa
Carcharhinus melanopterus | (Quoy & Gaimard, 1824)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Blacktip Reef Shark occurs throughout UAE waters. Globally, it is widespread in the tropical Indo-West and Central Pacific (Last and Stevens 2009).
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 Blacktip Reef Shark occurs throughout UAE inshore waters. It appears to be a resilient shark, persisting long after other species have been overfished, although it is threatened by extensive fishing pressure as well as habitat loss and degradation throughout the Arabian Sea region. Although there are limited data on its status, other Carcharhinus species in the Arabian Gulf have undergone significant declines due 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 and decline in habitat quality, it is suspected to have declined by 30-50% over the past three generation lengths, or about 34 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
In the UAE, sharks have been impacted by targeted fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). Sharks continue to be impacted by bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018). Inshore fisheries are generally intensive throughout the Arabian Sea region, and in some areas, fishing effort is increasing. Marine habitats in the Gulf, including the UAE, are experiencing high levels of disturbance 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
Off

Carcharhinus longimanus | 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 Oceanic Whitetip is one of the most widespread sharks, ranging across entire oceans in tropical and subtropical waters. It is an oceanic-epipelagic shark, usually found far offshore in the open sea in waters 230 m deep, between about 30'°N and 35'°S in all oceans; it is normally found in surface waters, although it has been recorded to 1082 m (Weigmann 2016). It has occasionally been recorded inshore, but is more typically found offshore or around oceanic islands and areas with narrow continental shelves (Compagno et al. 2005, Last and Stevens 1994). Temperatures of waters in which it regularly occurs are 18 to 28'°C, with water above 20'°C preferred.The Oceanic Whitetip Shark attains a maximum size of 400 cm total length (TL) (Stevens 1984, Seki et al. 1998). Males mature at about 168 to 198 cm TL and females at 170 to 200 cm TL (Seki et al. 1998). This species is born at about 57 to 77 cm TL after a gestation period of about 10 to 12 months (Compagno et al. 2005), with 15 foetuses recorded from a female of 245 cm TL from the Red Sea (Gohar and Mazure 1964) and larger females appear to carry more young, although there may be regional variation (Bass et al. 1973). Development is viviparous and embryos have a yolk sac placenta that attaches to the uterine wall of the mother (Bigelow and Schroeder 1948). Seki et al. (1998) studied the age, growth and reproduction of the Oceanic Whitetip Shark in the north Pacific. Both male and female Oceanic Whitetip Sharks matured at 4 to 5 years of age. In the western North Pacific, the size and age at first maturity was 190-193.4 cm TL and 8-5-8.8 years for females and 172-194.4 cm TL and 6.8-8.9 years for males (Joung et al. 2016). Smith et al. (1998) investigated the intrinsic rebound potential of Pacific sharks and found that oceanic whitetips to be among a moderate rebound potential, because of their relatively fast growth and early maturation. The species is estimated from a lifetable model created based on the WCPFC stock assessment to have a generation length of 16.4 years (M. J. Juan Jordá unpubl. data - based on the WCPFC stock assessment).
Taxon
Taxa
Carcharhinus longimanus | (Poey, 1861)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Oceanic Whitetip Shark may occur in UAE waters on the Sea of Oman coast, but has not been confirmed there. It is excluded from the Arabian Gulf. Globally, it is one of the most widespread of pelagic shark species, ranging across entire oceans in tropical and subtropical waters, usually found far offshore between about 30'°N and 35'°S in all oceans (Last and Stevens 2009).
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
In UAE waters, the Oceanic Whitetip Shark may occur only in offshore waters of the Sea of Oman, though this remains unconfirmed. Only a single record of the species was taken for Oman from extensive landing site surveys and it is not known if that individual was caught from the Sea of Oman. This formerly abundant large oceanic shark is subject to fishing pressure virtually throughout its range. It is frequently caught as a bycatch in pelagic fisheries. While there is limited species-specific information available, its large size, valuable fins and intensive fisheries mean that, like many other large carcharhinids, it has certainly declined. Capture of this species is totally banned in the UAE. Little is known on the population of this species in UAE waters, including the impact from the likely major threat of overexploitation. Given that its distribution in UAE waters (the Sea of Oman) remains uncertain, this species 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
In the UAE, sharks are impacted by both targeted and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018) though catch data are not species specific. 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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Carcharhinus leucas | 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 Bull Shark occurs in inshore and offshore waters, usually near the bottom, from the surfline to a depth of at least 152 m (Ebert et al. 2013). This species is euryhaline, with nursery areas in rivers, although within the Arabian Seas region, neonates have been recorded in areas without rivers and estuaries (Jabado et al. 2016). It attains a maximum size of about 340 cm total length (TL) with males mature at around 157-226 cm TL and females mature around 180-230 cm TL (Ebert et al. 2013, Jabado et al. 2016, Moore et al. 2012). Females produce litters of 1-13 every second year (Smith 1997) and size at birth is about 55-81 cm TL (Ebert et al. 2013). Ageing data from northern Australia indicate that females mature around 10 years and reach a maximum of at least 27 years (Tillett et al. 2011). Based on these data, generation length is estimated at 18.25 years.
Taxon
Taxa
Carcharhinus leucas | (Müller & Henle, 1839)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Bull Shark occurs throughout UAE waters. Elsewhere, it is circumglobal in tropical waters (Last and Stevens 2009). It is likely to have been widely misidentified as the Pigeye Shark (Carcharhinus amboinensis) where their distributions overlap (i.e. Gulf of Aden and eastwards).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
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 Bull Shark occurs throughout UAE inshore and offshore waters. Little specific data are available for this species in the UAE. Although there are limited data on its status, other Carcharhinus species in the Arabian Gulf have undergone significant declines due to exploitation. It has a relatively low reproductive capacity, which causes it to be susceptible to over-exploitation. 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. In addition, degradation of estuarine habitat is pervasive in the Arabian Gulf region. 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 and decline in habitat quality, it is suspected to have declined by 50-80% over the past three generation lengths, or about 55 years. It is listed as Endangered 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 target (for fins and their valuable meat) and 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). The reliance on rivers and estuaries by juveniles means that this species faces significant threats from habitat degradation due to damming, agriculture and coastal development (Moore 2018), which is pervasive in the Arabian Gulf region.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Carcharhinus leiodon | 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 in coastal waters on continental and insular shelves. Its maximum size is 165 cm total length (TL) (Weigmann 2016). Females are mature by at least 131 cm TL and demonstrate placental viviparity with litters of 4-6 embryos. In the northwestern Gulf, there is evidence that parturition occurs in spring when embryos are 35-51 cm TL. Further records of the Smoothtooth Blacktip Shark from the western Arabian Sea indicate that adults are present in this region throughout the year.No ageing data are available for the Smoothtooth Blacktip Shark. Generation length is estimated to be 8.25 years based on the Spottail Shark from Australia, which has a similar maximum size. The Spottail Shark matures at 2-3 years and reaches a maximum age of 14 years (Davenport and Stevens 1988).
Taxon
Taxa
Carcharhinus leiodon | Garrick, 1985
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Smoothtooth Blacktip Shark occurs throughout UAE waters. Globally, it is restricted to the Arabian Sea region from the Arabian Gulf, the Sea of Oman to Yemen.
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
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 Smoothtooth Blacktip Shark occurs throughout UAE inshore waters and is endemic to the Arabian Sea region. Little specific data are available for this species in the UAE. On the global-level, a limited number of specimens have been reported, in part due to probable confusion with other very similar and more common Carcharhinus species. Although there are limited data on its status, other Carcharhinus species in the Arabian Gulf have undergone significant declines due to exploitation. It has a relatively low reproductive capacity, which causes it to be susceptible to over-exploitation. 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 and decline in habitat quality, it is suspected to have declined by 50-80% over the past three generation lengths, or about 25 years. It is listed as Endangered 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
No
Endemism Notes
Is an endemic?: No
Endemism specifics: Endemic to the Arabian Sea region
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 et al. 2010). One of the known centres of abundance around Kuwait is also subject to habitat degradation (Moore et al. 2013) and the species was recently found to harbor high levels of mercury there (Moore et al. 2015).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Carcharhinus falciformis | 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 Silky Shark is a circumtropical oceanic and coastal-pelagic species, most often found near the edge of continental and insular shelves at depths of 200 m or more in the epipelagic zone. It is often associated with islands, insular slopes and deepwater reefs preferring warmer waters (about 23'°C) although it also occurs from the surface to a depth of at least 500 m offshore (Last and Stevens 2009). Smaller sharks are often found in coastal nurseries and adults further offshore over deeper water. In pelagic habitats, the Silky Shark is often associated with drifting materials on the surface (Filmalter et al. 2013). Life history parameters of this species vary considerably among regions (Clarke et al. 2015a). The maximum size varies from 229-371 cm total length (TL) with a size at maturity from 180-230 cm TL for males and 180-246 cm TL for females (Clarke et al. 2015). Age at maturity ranges from 5-13 years for males and 6-15 years for females with maximum ages of 8-28.6 years for males and 11-35.8 years for females. The Silky Shark gives birth to live young, averaging 5-7 pups per litter with a range of 2-18 pups per litter (Clarke et al. 2015a). Size at birth ranges from 65-81 cm TL and the gestation period ranges from 9-12 months depending on location and study (Clarke et al. 2015). Anderson and Ahmed (1993) report juveniles of 56-63 cm TL captured off the Maldives. Fecundity increases with increasing size of females, and females give birth every 1-2 years (Clarke et al. 2015). In the eastern Arabian Sea, total length and age at maturity for males is 201-“223 cm (TL) and 10 years, and 224-“231 cm and 11 years for females (Varghese et al. 2016). Generation length is estimated to be 15 years based on the average age of maturity of females as 9 years old and average maximum age of 21 years old (excluding outliers). This is in close agreement with generation length of 16 years in Dulvy et al. (2008).
Taxon
Taxa
Carcharhinus falciformis | (Bibron, 1839)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Silky Shark occurs throughout UAE waters. Elsewhere, it is circumglobally distributed in tropical waters (Last and Stevens 2009).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
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 Silky Shark occurs throughout UAE inshore and offshore waters. Little specific data are available for this species in the UAE. There has been a total ban on fishing for this species in UAE waters since 2019. This species is valued for its meat and fins across the Arabian Sea region. It is one of the dominant species in landings across the Arabian Sea region, and both adults and juveniles are landed. 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 pelagic tuna longline and purse seine 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 and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 45 years. It is listed as Near Threatened and nearly meets the thresholds for 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 target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. 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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Carcharhinus brevipinna | 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 Spinner Shark occurs in inshore and offshore waters on continental and insular shelves to depths of 75-100 m (Jabado and Ebert 2015). It is most common shallower than 30 m and also occurs in bays and off river mouths. It attains a maximum size of about 283 cm total length (TL). Males mature at ~177 cm TL, females mature at around 159 cm TL (Jabado and Ebert 2015). The species has an 11-15 month gestation period and is placentally viviparous, producing 3-20 pups (usually 7-11) with a size at birth of 48-55 cm TL. The reproductive cycle is two years (Castro 1993). There are no age data from the region, but generation length is suspected to be around 13 years based on work in South Africa (Allen and Wintner 2002) suggesting maturity at about 9 years and maximum age at about 17 years. In the Tasman Sea, age at maturity for females and males was 10.1 and 8.5 years, respectively (Geraghty et al. 2015).
Taxon
Taxa
Carcharhinus brevipinna | (Müller & Henle, 1839)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Spinner Shark occurs throughout UAE waters (Jabado and Ebert 2015). Globally, it is widespread in the tropical Indo-West Pacific and Atlantic Oceans (Last and Stevens 2009).
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 Spinner Shark occurs throughout UAE inshore and offshore waters. Little specific data are available for this species in the UAE. 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. Both juveniles and adults are valued for meat and fins. 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 and decline in habitat quality, it is suspected to have declined by 30-50% over the past three generation lengths, or about 39 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 target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. 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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Carcharhinus amboinensis | 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 Pigeye Shark occurs in inshore and offshore waters to depths of at least 100 m and juveniles are known to occur in estuaries (Ebert et al. 2013). Data on the life history of this species in the region is limited. Maximum reported size is 303 cm TL (Henderson et al. 2004). Size at birth is 57-72 cm TL, males mature at 195-227 cm TL, females mature at less than 195-224 cm TL (Moore et al. 2012, Ebert et al. 2013). Litter sizes reported include 11 from the Red Sea (I. Elhassan unpubl. data). In other parts of the range, litter sizes range from 3-13 (Bass et al. 1973). In Australia, females mature at 13 years and live to more than 30 years, while males mature at 12 years and live to more than 26 years (Tillett et al. 2011). Based on these data, generation length is estimated at 21.5 years.
Taxon
Taxa
Carcharhinus amboinensis | (Müller & Henle, 1839)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Pigeye Shark occurs throughout UAE waters. Globally, it is widespread but patchy in the Indo-West Pacific and Eastern Atlantic Oceans (Last and Stevens 2009). It is likely to have been widely misidentified as the Bull Shark (Carcharhinus leucas) where their distributions overlap (Gulf of Aden and eastwards).
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 Pigeye Shark occurs throughout UAE inshore and offshore waters. It is likely to have often been confused with the Bull Shark (Carcharhinus leucas), which causes difficulty when interpreting landings data. Little specific data are available for this species in the UAE. 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 and longline fisheries that operate within its range outside and surrounding UAE waters. In addition, degradation of rivers and estuaries in the Arabian Gulf region is likely a significant threat, particularly to juveniles. 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 and decline in habitat quality, it is suspected to have declined by 30-50% over the past three generation lengths, or about 65 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 target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. 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). Specifically, juveniles utilize rivers and estuaries, which are known to have undergone serious degradation in the Arabian Gulf region due to damming, agriculture and coastal development.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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