EN
Assessment ID
329875
Taxon name
Rhynchobatus djiddensis
Uploaded by
National Red List Database
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329873
Taxon name
Sphyrna zygaena
Uploaded by
National Red List Database
Scientific name
Sphyrna zygaena
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
sphyrnidae
Genus
Sphyrna
Species
zygaena
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2d
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
In UAE waters, the Smooth Hammerhead occurs only in the Sea of Oman. Capture of this species is totally banned in the UAE. It is sometimes confused with the more abundant Scalloped Hammerhead (Sphyrna lewini). This species is caught in both coastal and oceanic fisheries, and its low productivity causes it to be susceptible to rapid population declines from exploitation. Its fins are highly valued, and this is driving increased targeted fishing in some areas. Despite the lack of data, the similar ecology, low productivity, and presence of intensive fisheries, mean that this species, like other large sharks in the Arabian Sea region, has likely undergone significant declines. 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 at least 50% over the past three generation lengths, or about 72 years. It is listed as Endangered A2d.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Smooth Hammerhead occurs in UAE waters on the Sea of Oman coast. It is apparently excluded from the Arabian Gulf (Last and Stevens 1994). Records from the Gulf may be misidentifications of Sphyrna mokarran (Ali et al. 2018). Globally, it occurs in all coastal and open ocean temperate and tropical waters (Ebert et al. 2013). The full extent of this species' range in tropical waters may be incompletely known at present due to confusion with the more abundant Scalloped Hammerhead (Sphyrna lewini).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Smooth Hammerhead is a coastal-pelagic and semi-oceanic species that occurs on the continental shelf, to at least 200 m depth, with large individuals often found over deep reefs on the edge of the shelf (Smale 1991, Ebert et al. 2013). Despite its widespread occurrence, there are only limited published biological data on this species. It attains a maximum size of 370-400 cm total length (TL) (Ebert et al. 2013, Weigmann 2016). Stevens (1984) reported that off the east coast of Australia males mature at about 250-260 cm TL and females at about 265 cm TL with parturition and ovulation occurring between January and March. The gestation period off eastern Australia would appear to be 10-11 months. Castro and Mejuto (1995) reported 21 gravid females with a mean litter size of 33.5 from the waters of western Africa. Off eastern Australia, Stevens (1975) reported litter sizes between 20-49 (mean 32). The sex ratio of embryos is 1:1 (Stevens 1984, Castro and Mejuto 1995). Compagno (1984) and Compagno et al. (2005) gave the size at birth as 50-61 cm. Smale (1991) and Doño (2008) reported juveniles with open umbilical scars from South Africa at sizes between 59 and 63 cm, and from Uruguay between 49 and 55 cm TL, respectively. Although maximum age has yet to be determined for this species, it is thought that the lifespan of the Smooth Hammerhead may be 20 years or longer (FLMNH 2008). Generation length is estimated at 24 years based on that for the Scalloped Hammerhead (S. lewini), which reaches a similar size (Drew et al. 2015).
Threats listed in assessment
This species is impacted by target and bycatch fisheries across its range. Finning and discarding of carcasses has also been reported, especially in offshore and high seas fisheries (Anderson and Simpfendorfer 2005). This species is being increasingly targeted in some areas in response to increasing demand for the fins (Jabado et al. 2015).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329872
Taxon name
Sphyrna mokarran
Uploaded by
National Red List Database
Scientific name
Sphyrna mokarran
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
sphyrnidae
Genus
Sphyrna
Species
mokarran
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2d
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Great Hammerhead occurs throughout UAE inshore and offshore waters, and is unlikely to be abundant wherever it occurs. Capture of this species is totally banned in the UAE. It is particularly susceptible to capture in gill net and longline fisheries and is highly valued for its fins. It suffers very high bycatch mortality, which causes it to be susceptible to population decline. While there is limited information available on this species in the region, its large size, valuable fins, and intensive fisheries mean that, like many other large sharks, it has undergone significant declines. 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 at least 50% over the past three generation lengths, or about 75 years. It is listed as Endangered A2d.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Great Hammerhead occurs throughout UAE waters (Tourenq et al. 2008). Globally, it ranges widely throughout the tropical waters of the world from latitudes 40'°N to 35'°S (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Great Hammerhead is a coastal-pelagic and semi-oceanic tropical hammerhead shark occurring close inshore and well offshore, over continental shelves, island terraces, and in passes and lagoons of coral atolls, as well as over deep water near land, at depths ranging from near-surface to over 80 m (Compagno et al. 2005). The maximum total size is 550-610 cm total length (TL) (Weigmann 2016), though 400 cm TL is more common for a mature adult (Compagno et al. 2005, Last and Stevens 1994). Males mature at about 225 to 269 cm TL, and reach at least 341 cm TL, and females mature at about 225 to 300 cm TL and reach 482 to 549 cm TL (Compagno et al. 2005) In the UAE the largest recorded specimen was 3.82 m (Jabado et al. 2016 biological data sharks uae paper). The Great Hammerhead is viviparous, with a yolk-sac placenta. Litter size ranges from 6 to 42 pups after 11 months' gestation (Ebert et al. 2013). Size at birth is 50 to 70 cm TL with females breeding once every two years (Stevens and Lyle 1989). Generation length is estimated at 24-25 years based on Piercy et al. (2010) and Harry et al. (2011).
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). Low survival at capture makes this species very vulnerable to fishing pressure, whether directed or incidental. Finning and discarding of carcasses has also been reported, especially in offshore and high seas fisheries (Anderson and Simpfendorfer 2005). This species is being increasingly targeted in some areas in response to increasing demand for the fins (Jabado et al. 2015). 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).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329871
Taxon name
Sphyrna lewini
Uploaded by
National Red List Database
Scientific name
Sphyrna lewini
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
sphyrnidae
Genus
Sphyrna
Species
lewini
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2d
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Scalloped Hammerhead occurs throughout UAE inshore and offshore waters, and is apparently infrequently captured there. Capture of this species is totally banned in the UAE. All life-stages of this species are vulnerable to capture in both targeted and incidental fisheries that occur in both coastal areas as well as oceanic. Although there are limited data on its status, other shark species in the Arabian Gulf have undergone significant declines due to 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. There is evidence that a distinct subpopulation of this species occurs in the Arabian Sea region. Based on recorded levels of exploitation, it is suspected to have declined by at least 50% over the past three generation lengths, or about 72 years. It is listed as Endangered A2d.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Scalloped Hammerhead occurs throughout UAE waters. Elsewhere, it is circumglobally distributed in coastal warm temperate and tropical seas (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Scalloped Hammerhead is a coastal and semi-oceanic pelagic shark, found over continental and insular shelves and in deep water ranging from intertidal areas and the surface to at least 1,000 m depth (Compagno et al. 2005). Horizontal migration is observed from inshore bays to a pelagic habitat as this species grows. It has been observed to be highly faithful to particular diurnal core areas (Holland et al. 1993) and sometimes form large schools which migrate to higher latitudes in summer (Stevens and Lyle 1989). This species segregates by sex, with females migrating offshore earlier and at smaller sizes than males. Adults spend most of the time offshore in midwater and females migrate to the coastal areas to have their pups (Bass et al. 1975, Klimley and Nelson 1984, Branstetter 1987, Klimley 1987, Chen et al. 1988, Stevens and Lyle 1989). Nursery areas are found in shallow inshore waters, while the adults are found offshore (Compagno 1984, Holland et al. 1993, Kotas et al. 1995, Lessa et al. 1998). Neonates and juveniles are known to shoal in confined coastal pupping areas for up to two years before moving out to adult habitat (Holland et al. 1993). The species is viviparous with a yolk-sac placenta. Only the right ovary is functional. In Taiwanese (POC) waters, ovum development takes approximately 10 months and ova reach a maximum diameter of 40-45 mm. The number of oocytes in the ovarium can be as many as 40-50 per female (Chen et al. 1988). The gestation period is around 9-12 months, with birth in spring and summer. The average number of embryos in the uterus ranges from 12-41 and females pup every year. Newborn size ranges from 31-57 cm (Castro 1983, Compagno 1984, Branstetter 1987, Chen et al. 1988, Stevens and Lyle 1989, Chen et al. 1990, Oliveira et al. 1991, 1997, Amorim et al. 1994, White et al. 2008). Maximum size is reported by several studies, 370-420 cm total length (TL) (Ebert et al. 2013) and ranged from 219-340 cm TL for males and 296-346 cm TL for females (Bass et al. 1975b, Schwartz 1983, Klimley and Nelson 1984, Stevens 1984, Branstetter 1987, Chen et al. 1988, Stevens and Lyle 1989, Chen et al. 1990). Males mature between 140-198 cm TL and females at around 200-250 cm TL (Compagno 1984b, Branstetter 1987, Chen et al. 1990, Carrera and Martinez 2007, White et al. 2008). Branstetter's (1987) growth study in the Gulf of Mexico found asymptotic length for both sexes of 329 cm TL and 253 cm fork length (FL), with an index of growth rate of k = 0.073 y<sup>-1</sup>. Piercy et al.'s (2007) more recent study used FL rather than TL and suggested faster growth, with asymptotic length of 214.8 cm FL for males and 233.1 cm FL for females, with an index growth rate of k=0.13 year<sup>-1</sup> for males and k=0.09 year<sup>-1</sup> for females. It is unclear whether these differences are related to sample size, methodology or changes resulting from a density-dependent compensatory response to population depletion. The nearest studies on life history traits of this species have been undertaken in the Eastern Indian Ocean. White et al. (2008) estimated females and males to mature at 228.5 cm TL and 175.6 cm TL, respectively. Age at maturity was estimated at 13.2 for females and 8.9 years for males (Drew et al. 2015). Based on these data, generation length was estimated at 24 years.
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. Finning and discarding of carcasses has also been reported, especially in offshore and high seas fisheries (Anderson and Simpfendorfer 2005). This species is being increasingly targeted in some areas in response to increasing demand for the fins (Jabado et al. 2015). Furthermore, aggregating behaviour and low survival at capture causes this species to be very susceptible to fishing pressure, and the recolonisation of depleted areas is expected to be a slow and complex process (Maguire et al. 2006, Drew et al. 2015).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329865
Taxon name
Carcharhinus leucas
Uploaded by
National Red List Database
Scientific name
Carcharhinus leucas
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Carcharhinus
Species
leucas
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
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.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
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).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
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.
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.
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329864
Taxon name
Carcharhinus leiodon
Uploaded by
National Red List Database
Scientific name
Carcharhinus leiodon
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Carcharhinus
Species
leiodon
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
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.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
No
Endemism Notes
Endemism Notes
Endemic to the Arabian Sea region
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.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
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).
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).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329860
Taxon name
Carcharhinus amblyrhynchos
Uploaded by
National Red List Database
Scientific name
Carcharhinus amblyrhynchos
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Carcharhinus
Species
amblyrhynchos
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Grey Reef Shark occurs throughout UAE inshore waters, often near coral reefs. 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 fisheries that operate within its range outside and surrounding UAE waters. In addition, coral reef loss and degradation have been severe across the UAE. 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. This species faces intense fishing pressures throughout the Arabian Sea. 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 36 years. It is listed as Endangered A2cd.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Grey Reef Shark occurs throughout UAE waters. Globally, it is widespread in the tropical Indo-West and Central Pacific (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Grey Reef Shark is found in clear tropical waters often from 10 m to around 140 m and is common around coral reefs, particularly near drop-offs and fringing reefs. It attains a maximum size of 255 cm total length (TL). Males mature at 110-145 cm TL; females at about 120-142 cm TL (Wetherbee et al. 1997, Ebert et al. 2013) at around seven years. Litters are small with up to six pups measuring 48-49 cm TL (Compagno 1984, Anderson and Ahmed 1993, Last and Stevens 1994, Wetherbee et al. 1997). Smart et al. (2016) provide age data from Australia where the females mature at 9 years and reach a maximum age of at least 15 years. A study conducted on an unfished population of this species reported an estimated length at maturity of 116.7-“123.2 cm TL for males and a maximum lifespan of 18.1 years for both sexes, and an annual survival rate of 0.74 year<sup>-1</sup> (Bradley et al. 2017). When applying an age at first reproduction of 9 years and longevity of 18 years, its estimated generation length is 13.5 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.
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). 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).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329852
Taxon name
Thunnus albacares
Uploaded by
National Red List Database
Scientific name
Thunnus albacares
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
scombridae
Genus
Thunnus
Species
albacares
Taxonomic notes and synonyms listed
Although several geographic populations have been named as species, morphological and genetic data show there is one world-wide panmictic species (Gibbs and Collette 1967, Scoles and Graves 1993).
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2bd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
In the UAE, this pelagic species occurs only in the Sea of Oman where it is taken in both commercial and recreational fisheries. It is heavily targeted by commercial fisheries that operate throughout the Indian Ocean, including the Sea of Oman. Due in part to its highly migratory behavior, the Indian Ocean is considered a single stock by the Indian Ocean Tuna Commission (IOTC). According to the 2018 IOTC stock assessment, this species is overfished with overfishing occurring. Catch has been increasing since 2009, and is currently at an unsustainable level, but effort data are largely lacking, and the 2017 spawning stock biomass (SSB) was at 30% of unfished levels. As of 2009, SSB had declined by 45% over the previous decade (1999-“2008). Assuming this decline continued to the present due to increasing catch levels since 2009, a linear regression of estimated adult biomass indicates that the Indian Ocean stock is suspected to have declined by 61% over the past three generation lengths (1999-2019 or 20 years); therefore, it is listed as Endangered A2bd.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
In UAE waters, this species occurs only in the Sea of Oman, and is excluded from the Arabian Gulf. Elsewhere, it is circumglobally distributed in tropical and subtropical waters.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
This open-water pelagic and oceanic species inhabits waters between 18-“31'°C and occurs above and below the thermocline to at least 400 m depth. It schools primarily by size, either in monospecific or multi-species groups. Larger fish frequently school with porpoises and are also associated with floating debris and other objects. It feeds on fishes, crustaceans and squids. Maximum fork length is 240 cm. In the Indian Ocean, longevity is 9 years, length at 50% maturity for males and females is 100 cm and age at first maturity is 3-5 years (IOTC 2018). When applying an age at first reproduction of 4 years and longevity of 9 years, its estimated generation length is 6.5 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.
Threats listed in assessment
Overfishing is a major threat to this species in the UAE in part due to its overfished status across the Indian Ocean stock, in which the Sea of Oman is included (IOTC 2018).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329844
Taxon name
Rhincodon typus
Uploaded by
National Red List Database
Scientific name
Rhincodon typus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
orectolobiformes
Family
rhincodontidae
Genus
Rhincodon
Species
typus
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2d
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Whale Shark occurs throughout UAE pelagic and coastal waters, and conducts seasonal migrations. Capture of this species is totally banned in the UAE. It is taken as bycatch in gill net fisheries in the UAE, but is not particularly valued there. It may be impacted by vessel strikes, especially in the vicinity of busy shipping lanes in the Gulf. Elsewhere, where it has been historically exploited, large-scale declines have occurred (e.g., India, the Maldives). Protective measures are in place, and directed fisheries mostly no longer exist, though the species is retained when taken as bycatch. It exhibits 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 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 50-80% over the past three generation lengths, or about 75 years. It is listed as Endangered A2d.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Whale Shark occurs throughout UAE waters (Hellyer and Aspinall 2005, Jabado et al. 2014). Elsewhere, it is circumglobally distributed in tropical and warm temperate seas.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
Whale Sharks are found in both coastal and oceanic habitats (Rowat and Brooks 2012). This species is highly mobile, with mean daily movement rates of 24-“28 km based on tethered geopositioning tags (Hueter et al. 2013). Whale Sharks spend the majority of time in the epipelagic zone, but dive to at least 1,928 m in depth (Tyminsky et al. 2015). Most sightings occur at a small number of known coastal feeding areas for the species, where the sharks aggregate on the surface to exploit seasonal productivity such as fish spawning events or zooplankton blooms (Rowat and Brooks 2012, Robinson et al. 2013). A degree of inter-annual site fidelity has been documented in many locations (Cagua et al. 2015, Norman et al. in press). Sexual- and size-based segregation is typical in these locations, with a bias towards juvenile males from 4-“8 m total length (TL) (Rohner et al. 2015, Norman et al. 2017, Robinson et al. 2016). The largest recorded Whale Sharks are approximately 20 m TL (Chen et al. 1997) and 42 t in mass (Hsu et al. 2014) as reported from Taiwan. An individual extrapolated to be 18.8 m TL was caught in India (Borrell et al. 2011). Estimates of TL at maturity for males vary between 7-9.2 m TL (Norman and Stevens 2007, Ramírez-Macías et al. 2012, Rohner et al. 2015). Size at maturity in females is approximately 9 m TL, based on visual and laser photogrammetric estimates (Acuña-Marrero et al. 2014, Ramírez-Macías et al. 2012). Whale Shark reproductive ecology is poorly known. Pregnant female sharks are seasonally found in the Eastern Pacific, particularly off Darwin Island in the Galapagos Archipelago (Acuña-Marrero et al. 2014) and the Gulf of California (Eckert and Stewart 2001, Ramírez-Macías et al. 2012), but rarely sighted outside this region. The single pregnant female that has been physically examined, from Taiwan, had 304 pups in various stages of development, establishing that this species is lecithotrophic viviparous (Joung et al. 1996, Schmidt et al. 2010). The largest size class of embryos, 58-“64 cm TL, appeared close to fully developed (Joung et al. 1996). Size at birth is presumed to be around that size although a 46 cm TL specimen was the smallest free-swimming neonate found in the Philippines (Aca and Schmidt 2011). Age and growth data on Whale Sharks are sparse. Based on biannual band-pairs, it is estimated that that male sharks begin maturing at ~17 years and females at 19-“22 years in the Indo-Pacific with generation length estimated at 25 years (Hsu et al. 2014).
Threats listed in assessment
The major threats to the Whale Shark include fisheries (both directed and incidental) and vessel strikes. Where shipping lanes are located close to Whale Shark feeding areas, vessel strikes are more common (Motta et al. 2010, Gleiss et al. 2013). Propeller injuries are commonly recorded during monitoring programs (Rowat et al. 2006, Speed et al. 2008, Fox et al. 2013). Areas where Whale Sharks appear to be at particular risk include the Gulf waters, where a high frequency of serious propeller injuries are observed during monitoring (D. Robinson unpubl. data). Coastal development may be particularly problematic in the Gulf region as Whale Sharks can be attracted to and become entrapped in ports and suffer from extended exposure to warm temperatures (D. Robinson pers. obs.).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
329815
Taxon name
Carcharhinus plumbeus
Uploaded by
National Red List Database
Scientific name
Carcharhinus plumbeus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Carcharhinus
Species
plumbeus
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Sandbar Shark occurs throughout UAE inshore and offshore waters. It is caught with longlines, hook-and-line, and set bottom nets and the fins are generally considered to be of high value. While there is limited information available on this species in the region, its large size, valuable fins and intensive fisheries mean that, like many other large carcharhinids in the region, it has declined significantly. In addition, this is one of the least biologically productive sharks, with high intrinsic vulnerability, and information from other parts of its global range have demonstrated that it is quickly overfished even with moderate levels of fishing. Little specific data are available for this species in the UAE. 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 at least 50% over the past three generation lengths, or about 86 years. It is listed as Endangered A2cd.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Sandbar Shark occurs throughout UAE waters. Elsewhere, it is broad ranging but patchily distributed (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Terrestrial
No
Freshwater
No
Marine
Yes
Habitat details as listed in assessment
The Sandbar Shark occurs in coastal, often shallow waters and is associated with sandy or muddy flats, bays, estuaries and harbours (Grubbs et al. 2007). The species also occurs further offshore, particularly on banks, near islands, flat reefs and other topographic features in open waters from the surface to 280 m depth, but is typically found in waters less than 100 m depth (Compagno et al. 2005). It attains a maximum size of at least 240 cm total length (TL) (Ebert et al. 2013). Size at maturity in females ranges from 129-158 cm TL and from 123-156 cm TL in males. This species is viviparous with a yolk sac placenta with a gestation period estimated at 9-12 months (McAuley et al. 2007). Females apparently have young only every two or three years. Litter size is variable and depends in part on the size of the mother, and ranges from 1-10 (Tester 1969, McAuley et al. 2007). Size at birth varies slightly by region but does not follow the same geographic pattern. New born pups range from 40-65 cm TL (Capapé 1984, McAuley et al. 2007).Sandbar Sharks are slow-growing K-selected species (Hoff and Musick 1987, Sminkey and Musick 1995). Wild populations grow very slowly and mature at a relatively late age (Lawler 1976, Casey et al. 1985, Sminkey and Musick 1995). Maturity in these studies was estimated at 13-16 years. The ages at which 50% of female and male sharks were mature was estimated to be 16.2 and 13.8 years, respectively (McAuley et al. 2006) and longevity is 35-41 years (McAuley et al. 2006). In the Tasman Sea, age at maturity for females and males was 9.5 and 7 years, respectively (Geraghty et al. 2015). Generation length is therefore estimated as 28.5 years.
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. Studies show that sandbar sharks are a long-lived species with low fecundity and are very susceptible to overfishing (Springer 1960, Casey et al. 1985, Sminkey and Musick 1995, 1996; McAuley et al. 2005, 2006). 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). 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).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
