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Assessment ID
330013
Taxon name
Alopias pelagicus
Nakamura, 1935
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Alopias pelagicus
Nakamura, 1935
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
lamniformes
Family
alopiidae
Genus
Alopias
Species
pelagicus
Species authority
Nakamura, 1935
Location and scope
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
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2bd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In UAE waters, the Pelagic Thresher Shark occurs only in the Sea of Oman. 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 and under-reported gillnet and longline fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region (i.e. through the IOTC), although domestic fisheries are likely to continue. A total ban of fishing for this species has been in place in UAE waters since 2019. 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 fisheries data and recorded levels of exploitation, it is suspected to have declined by at least 50% over the past three generation lengths, or about 57 years. It is listed as Endangered A2bd.
Assessment details
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Pelagic Thresher shark occurs in UAE waters on the Sea of Oman coast. It is likely excluded from the Arabian Gulf (Compagno 2001). An Alopias species was reported by a diver at an offshore wreck in Dubai. An archaeological study found four caudal vertebrae belonging to thresher shark species in Abu Dhabi (Beech 2004). Globally, it is wide-ranging in the Indo-Pacific.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Pelagic Thresher is epipelagic and mesopelagic from the surface to 300 m depth (Weigmann 2016). It attains a maximum size of 365 cm total length (TL). In the Arabian Sea, males are reported to mature at 245-270 cm TL while females mature between 268-286 cm TL (Varghese et al. 2017). The species is lecithotrophic viviparous with oophagy, and a litter size of only two very large (158-190 cm TL) pups. Age at maturity near Taiwan is estimated as 8-9.2 years in females and 7-8 years in males (Liu et al. 1999). Its potential annual rate of population increase under sustainable fishing is thought to be very low and has been estimated at 2-4% (Smith et al. 1998), or 0.033 (Dulvy et al. 2008), compared with the Common Thresher, which is between 4 and 7% (Smith et al. 1998) or 0.254 (Dulvy et al. 2008). Generation length is estimated at 18.6 years (Drew et al. 2015).
Threats and conservation measures listed
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. Thresher sharks are impacted by target (for fins and their valuable meat) and bycatch fisheries throughout their range. Finning and discarding of carcasses has also been reported, especially in offshore and high seas fisheries (Anderson and Simpfendorfer 2005, IOTC 2006). This species has the lowest intrinsic rebound potential and least resistance to fisheries of the genus (Chen et al. 1997). It has a particularly low (2-4%) annual rate of population increase.
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
330012
Taxon name
Maculabatis gerrardi
(Gray, 1851)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Maculabatis gerrardi
(Gray, 1851)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
dasyatidae
Genus
Maculabatis
Species
gerrardi
Species authority
(Gray, 1851)
Taxonomic notes and synonyms listed
Last et al. (2016) described the genus Maculabatis, comprised of nine medium to large, marine whiprays previously placed in Himantura (including gerrardi). Reports of the species are often confused with the Coach Whipray (Himantura uarnak).
Location and scope
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
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Whitespotted Whipray occurs throughout UAE inshore waters. Little is known on the population of this species in UAE waters, but it is taken as bycatch. It is taken as bycatch in trawl, gillnet, and longline fisheries in the Arabian Seas region and fishing pressure is intense and increasing in some areas, particularly in Iran, India and Pakistan, where batoid populations have declined. It is not known how individuals occupying UAE waters are connected with the broader population of the Arabian Seas region, though there is no information available to suggest that its population status differs in the UAE. Given the threats faced by this species in other parts of the Arabian Seas region, and ongoing threats from discarding and habitat loss in the UAE, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 50% over the past three generation lengths, or about 60 years. It is listed as Endangered A2cd.
Assessment details
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Whitespotted Whipray occurs throughout UAE waters. Globally, it is moderately widespread in the Northern Indian and Western Pacific Oceans (Last et al. 2016 ). In the Arabian Sea region, it inhabits waters from the Arabian Gulf to southern India and Sri Lanka.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Whitespotted Whipray occurs inshore on soft substrates to depths of at least 60 m (Last et al. 2016). This species attains a maximum size of 116 cm disc width (DW). Males are reported to mature at 48-58 cm DW, with females maturing at 63 cm DW. Litter size is reported as 2-4 pups with size at birth at 13-21 cm DW (Last et al. 2016). As there is no information on this species' maximum age and age at maturity, generation length was inferred as ~20 years based on data for Blackspotted Whipray (Maculabatis astra) (Jacobsen and Bennett 2011). However, it is noted that the Blackspotted Whipray grows to a smaller maximum size (80 cm DW) than the Whitespotted Whipray (116 cm DW).
Threats and conservation measures listed
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).
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
330011
Taxon name
Carcharhinus altimus
(Springer, 1950)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carcharhinus altimus
(Springer, 1950)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Carcharhinus
Species
altimus
Species authority
(Springer, 1950)
Taxonomic notes and synonyms listed
The Bignose Shark is morphologically distinct but genetically similar to the Sandbar Shark (Carcharhinus plumbeus) (Naylor et al. 2012, Duffy and Struthers 2017).
Location and scope
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
Conservation Status
Assessed as
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In UAE waters, the Bignose Shark occurs only in the Sea of Oman in deep 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 longline fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region (i.e. through the IOTC), 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 at least 30% over the past three generation lengths, or about 64 years. It is listed as Vulnerable A2cd.
Assessment details
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
In the UAE, the Bignose Shark occurs only on the Sea of Oman coast. It is excluded from the Arabian Gulf. Globally, it is widespread but patchy throughout the Indo-Pacific and Atlantic Oceans (Last and Stevens 2009). This species is possibly easily confused with Carcharhinus plumbeus (Henderson et al. 2016).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Bignose Shark occurs mainly on the edge of continental shelves in waters to 800 m deep, but is more common between 80 and 220 m with occasional captures in shallow water (Tester 1969). Individuals have been caught at night near the surface over deep water in the Maldives (Anderson and Ahmed 1993) and this species is thought to display diurnal vertical migrations (Anderson and Stevens 1996). It attains a maximum size of 282 cm total length (TL) with an average reproductive age of ~21 years (Compagno 1984, Kohler et al. 1995, Jensen et al. 1996). Males reach maturity at 216 cm TL and females at 226 cm TL. Females are reported to give birth to 1-13 pups per litter with size at birth around 70-90 cm TL.
Threats and conservation measures listed
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).
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
330010
Taxon name
Carcharhinus albimarginatus
(Rüppell, 1837)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carcharhinus albimarginatus
(Rüppell, 1837)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Carcharhinus
Species
albimarginatus
Species authority
(Rüppell, 1837)
Location and scope
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
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In UAE waters, the Silvertip Shark occurs only in the Sea of Oman in continental shelf habitats. 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 longline 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 (i.e. through the IOTC), 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 60-70% over the past three generation lengths, or about 64 years. It is listed as Endangered A2cd.
Assessment details
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Silvertip Shark occurs in UAE waters on the Sea of Oman coast. It is excluded from the Arabian Gulf. Globally, it is widespread, but patchy in the Indo-Pacific (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Silvertip Shark occurs on the continental shelf, offshore islands, coral reefs, and offshore banks, from surface waters to depths of 600-800 m (Compagno et al. 2005). It is also found inside lagoons, near drop-offs, and offshore (Compagno et al. 2005). The species appears to be relatively site-specific for long periods with limited dispersion, particularly at remote and isolated coral reef habitats around tropical islands or atolls (Barnett et al. 2012, Espinoza et al. 2015). On the continental shelf, larger individuals of the species tend to be more mobile and use larger areas than other common reef shark species (Barnett et al. 2012, Espinoza et al. 2015). The Silvertip Shark also exhibits strong diel behaviour, moving closer to coral reefs and using shallower habitats at night.This species reaches a maximum size of 300 cm total length (TL) (Compagno et al. 2005). Males are reported to mature at 160-180 cm TL and females at 160-199 cm TL (Compagno et al. 2005). White et al. (2006) report that males mature at 190-200 cm TL and females at ~195 cm TL. Reproduction is viviparous, with a yolk sac placenta (Compagno et al. 2005, White et al. 2006, White 2007). In a study conducted in Papua New Guinea, males matured at 175 cm TL and 10.5 years, while females matured at 209 cm TL and 14.8 years, and longevity was estimated as 18-32 years for females (Smart et al. 2017). Females give birth to 1-11 pups per litter (average six) biennially, after a 12 month gestation period (Compagno et al. 2005, White et al. 2006, Last and Stevens 2009). Size at birth is reported at 60-68 cm TL (Compagno et al. 2005) and 73-81 cm TL (White et al. 2006). Young are found in shallow water closer to shore, whereas adults are more wide-ranging (Compagno et al. 2005). Growth appears to be fairly slow at about 9 cm per year for juveniles (Last and Stevens 2009). No estimate of generation length is available for the species, although it can be inferred from its congener, the Pigeye Shark (C. amboinensis), which has a similar maximum size and an estimated generation length of 21.5 years (Tillett et al. 2011). When applying an age at first reproduction of 15 years and longevity of 18-32 years, its estimated generation length is 16.5-23.5 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 and conservation measures listed
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
330009
Taxon name
Paragaleus randalli
Compagno, Krupp & Carpenter, 1996
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Paragaleus randalli
Compagno, Krupp & Carpenter, 1996
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
hemigaleidae
Genus
Paragaleus
Species
randalli
Species authority
Compagno, Krupp & Carpenter, 1996
Location and scope
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
Conservation Status
Assessed as
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Slender Weasel Shark occurs throughout UAE inshore waters and may be uncommon there. It is poorly known in general, in part due to confusion with other species. It is caught in inshore gill net, trawl and line fisheries in the Arabian Sea region where inshore fishing pressure is intense and increasing. There is also an ongoing decline in habitat quality due to coastal development, particularly in the Gulf. 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 30-50% over the past three generation lengths, or about 24 years. It is listed as Vulnerable A2cd.
Assessment details
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Slender Weasel Shark occurs throughout UAE waters. Globally, it has a patchy distribution in the northern Indian Ocean from the Arabian Gulf, inner Sea of Oman, India and Sri Lanka.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Slender Weasel Shark is found inshore in shallow waters of the continental shelf to depths of 18 m (Compagno et al. 1996, Weigmann 2016). It reaches a maximum size of at least 85 cm with males reaching maturity at around 65 cm TL (Moore et al. 2012, Moore and Pierce 2013, Jabado et al. 2016). It is a viviparous species, giving birth to two pups per litter which are born at 35-40 cm TL. No age and growth data are available and generation length is estimated as 8 years based on data for the Hooktooth Shark (Chaenogaleus macrostoma) (Henderson et al. 2004).
Threats and conservation measures listed
Threats listed in assessment
In the UAE, sharks have been impacted by targeted commercial fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). Sharks continue to be impacted by artisanal and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018), though catch data are not species-specific. This species is impacted by bycatch fisheries that are active elsewhere in its range. 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).
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
330008
Taxon name
Iago omanensis
(Norman, 1939)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Iago omanensis
(Norman, 1939)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
triakidae
Genus
Iago
Species
omanensis
Species authority
(Norman, 1939)
Taxonomic notes and synonyms listed
The Bay of Bengal population may represent a separate dwarf Iago omanensis-like species (Fernando et al. 2019, Psomadakis et al. 2019).
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In UAE waters, the Bigeye Houndshark occurs only in deeper waters of the Sea of Oman. This species is not targeted or valued in markets of the UAE and trawling has been banned there since 1980. It is taken by gill net or trawl fisheries in Oman, Pakistan and India and utilized fresh for human consumption. It appears to be quite common in some areas of its range, such as Oman and northwestern India, but data specific to its status in the UAE are not available at this time. There is some evidence for declines in the Gulf of Aqaba (Red Sea) and India, especially where deep sea trawl fisheries have been recently expanding. There are no data to suggest that the part of the population that occupies the UAE is under any greater threat than in any other part of its range and that its status in the Arabian Seas region should be representative of its status in the UAE. Given its probable extensive refuge in deep waters, it is listed as Least Concern.
Assessment details
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Bigeye Houndshark occurs in UAE waters on the Sea of Oman coast. It is excluded from the Arabian Gulf. Its global range is poorly-defined due to taxonomic issues, but as presently known, it occurs throughout the Arabian Sea region with the exception of the Gulf, the Maldives, and Sri Lanka. There may be several species in India that remain to be described (K.K. Bineesh pers. comm. 07/02/2017). Further research is required, but the Bigeye Houndshark may be restricted to the western parts of the Arabian Sea region.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Bigeye Houndshark is most commonly found on continental shelves and slopes at depths from 110-1,000 m and possibly as deep as 2,195 m in the Red Sea. In the Gulf of Aqaba, males apparently inhabit deeper waters, whereas females prefer shallower waters (300 m) (Baranes 2005). The species attains a maximum size of 84 cm total length (TL) (Henderson and Reeve 2014) with females reaching maturity at ~40 cm TL and males at 31-32 cm TL. Reproduction is viviparous with yolk-sac placenta and gestation lasts for 10-12 months with two to six pups are produced per litter (Baranes 2007). Size at birth is at ~14 cm TL (Baranes 2007, Henderson and Reeve 2014). Preliminary ageing data indicates males live to 7 years and females to 9 years (Henderson et al. 2004) suggesting a generation length of 5.5 years.
Threats and conservation measures listed
Threats listed in assessment
Threat information specific to this species in the UAE is unavailable. 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.
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
330007
Taxon name
Mustelus mosis
Hemprich & Ehrenberg, 1899
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Mustelus mosis
Hemprich & Ehrenberg, 1899
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
triakidae
Genus
Mustelus
Species
mosis
Species authority
Hemprich & Ehrenberg, 1899
Location and scope
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
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Arabian Smoothhound occurs throughout UAE inshore and offshore waters, and may be relatively common there. It is taken as bycatch in some parts of its range, but remains common in landings. This species is not targeted in the UAE, trawling has been banned there since 1980 and it apparently remains common. Based on the lack of evidence for declines, continued importance in fisheries landings and relatively high biological productivity, this species is listed as Least Concern.
Assessment details
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Arabian Smoothhound occurs throughout UAE waters (Randall 1995, Environment Agency Abu Dhabi unpublished data). Globally, it is moderately widespread in the Northern Indian Ocean from the Red Sea to India and Sri Lanka. Taxonomic issues have confused the distribution of this species in eastern India and Sri Lanka, and the full distribution of the species remains to be resolved.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This is a bottom dwelling shark found inshore and offshore at depths of 0-250 m, sometimes in association with coral reefs (Compagno 1984). The species is reported to reach a maximum size of 150 cm total length (TL) but is rarely seen above 100 cm TL (Jabado et al. 2016, Moore et al. 2016). Males mature at 65-78 cm TL and females mature from about 73 cm TL. Reproduction is viviparous, and the species gives birth to 2-16 pups per litter (Moore et al. 2016). Size at birth is reported as 26-28 cm TL (Bass 1986). No ageing data is available. Generation length is estimated as 10 years based on the Narrownose Smoothhound (Mustelus schmitti) from Brazil which has a similar distribution and maximum size.
Threats and conservation measures listed
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. 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).
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
330006
Taxon name
Rhinobatos annandalei
Norman, 1926
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Rhinobatos annandalei
Norman, 1926
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
rhinobatidae
Genus
Rhinobatos
Species
annandalei
Species authority
Norman, 1926
Location and scope
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
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Bengal Guitarfish occurs throughout UAE coastal waters. Due to confusion with the Spotted Guitarfish (Rhinobatos punctifer), population data can be uncertain. There has been a total ban on fishing for this species in UAE waters since 2019, but is still taken as bycatch in coastal net fisheries. Declines of several species of inshore guitarfish have been documented (e.g., India). Habitat degradation from coastal development is a concern for this species as well. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net 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 20-30% over the past three generation lengths, or about 15 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
Assessment details
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Bengal Guitarfish occurs throughout UAE waters. Globally, it has a poorly defined distribution in the Northern Indian Ocean from the Arabian Gulf (Iran, UAE) to India and possibly Sri Lanka (Bianchi 1985, Talwar and Jhingran 1991, Assadi and Dehghani 1997, Vossoughi and Vosoughi 1999). There has been some confusion as to the identification of this species, making its exact distribution difficult to define, with some previous studies have referred to it as the Spotted Guitarfish.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
Very little information is currently available on the habitat or biology of this guitarfish. It occurs from close inshore out to about 90 m deep and presumably occurs over soft substrates. Maximum total length is reported at approximately 87 cm (R.W. Jabado pers. obs.). Maturity for males is about 50-68 cm TL and for females it is around 60 cm TL (Raje 2006, Henderson et al. 2004, Last et al. 2016). Size at birth is about 19-20 cm TL. Fecundity is up to 3-20 pups (M. Khan pers. comm. 08/02/2016, Raje 2006) although females dissected from landings in Oman had between 3-5 pups (Henderson et al. 2004). Most pregnant and post-partum females in Indian and Pakistan waters occur in September and October (M. Khan pers. comm. 08/02/2016, Raje 2006) and in the summer and winter in Oman (Henderson et al. 2004). Generation length is inferred to be 5 years from the Lesser Guitarfish (Acroteriobatus annulatus) from southern Africa (Compagno et al. 1989).
Threats and conservation measures listed
Threats listed in assessment
This species has been impacted by target and bycatch fisheries. It may also being impacted by habitat degradation due to coastal development, especially nursery grounds. 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.<em style=""font-size: 12pt; font-family: Georgia;""> 2010).
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
330005
Taxon name
Rhinobatos punctifer
Compagno & Randall, 1987
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Rhinobatos punctifer
Compagno & Randall, 1987
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
rhinobatidae
Genus
Rhinobatos
Species
punctifer
Species authority
Compagno & Randall, 1987
Location and scope
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
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Spotted Guitarfish occurs throughout UAE coastal waters. Due to confusion with the Bengal Guitarfish (Rhinobatos annandalei), population data can be uncertain. There has been a total ban on fishing for this species in UAE waters since 2019, but is still taken as bycatch in coastal net fisheries. Declines of several species of inshore guitarfish have been documented elsewhere. Habitat degradation from coastal development is a concern for this species as well. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net 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 20-30% over the past three generation lengths, or about 15 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
Assessment details
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Spotted Guitarfish occurs throughout UAE waters. Globally, it is restricted to the Arabian Sea region from the northern Red Sea to the Sea of Oman and Arabian Gulf (Bonfil and Abdallah 2004, Last et al. 2016). The species has been frequently misidentified in the literature, and sometimes confused with the Bengal Guitarfish (Rhinobatos annandalei).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This species inhabits the inshore continental shelf to depths of 70 m on soft substrates (Weigmann 2016). Reproduction is viviparous and the species reaches at least 90 cm total length (TL) (Weigmann 2016). Maximum litter size is up to at least seven and size at birth is ~25 cm TL (A.C. Henderson unpubl. data). Data from Oman indicates that females taken during autumn off Muscat were all mature at less than 77 cm TL while males matured at less than 71 cm TL (Henderson et al. 2004). Generation length is inferred to be 5 years from the Lesser Guitarfish (Acroteriobatus annulatus) from southern Africa (Compagno et al. 1989).
Threats and conservation measures listed
Threats listed in assessment
This species has been impacted by target and bycatch fisheries. It may also being impacted by habitat degradation due to coastal development, especially nursery grounds. 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.<em style=""font-size: 12pt; font-family: Georgia;""> 2010).
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
330004
Taxon name
Mobula kuhlii
(Müller & Henle, 1841)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Mobula kuhlii
(Müller & Henle, 1841)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
mobulidae
Genus
Mobula
Species
kuhlii
Species authority
(Müller & Henle, 1841)
Taxonomic notes and synonyms listed
Combined morphological and molecular data led Last et al. (2016) and White et al. (2017) to conclude that M. eregoodootenkee is a junior synonym of M. kuhlii. However, Hosegood et al. (2019) suggested these were separate species, which was supported by Notarbartolo di Sciara et al. (2020), who also clarified the nomenclature as M. eregoodoo.
Location and scope
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
Conservation Status
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2d
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Shortfin Devil Ray occurs throughout UAE waters and may be locally common there. This species is not targeted or valued in markets of the UAE and capture of this species is totally banned there. When captured in the Arabian Gulf and Sea of Oman, it is typically discarded alive, and significant declines are not suspected there at this time. It is a component of the bycatch in several fisheries (e.g., Pakistan), and is directly targeted in Sri Lanka and India. Its low productivity causes it to be susceptible to rapid population declines, and severe declines have recently been confirmed from Pakistan (over the past three years). It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation, it is suspected to have declined by 20-30% over the past three generation lengths, or about 23 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2d.
Assessment details
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.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Shortfin Devil Ray occurs throughout UAE waters. Globally, it is widespread in the tropical Indo-West Pacific (Notarbartolo di Sciara et al. 2017).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
The Shortfin Devil Ray is an uncommon inshore, primarily shelf pelagic species found in continental coastal areas but not extending into the epipelagic zone (Compagno and Last 1999). This species reaches a maximum size of about 119 cm disc width (DW) (White et al. 2006b). Males mature at 103-“119 cm (DW) (White et al. 2006b, Notarbartolo di Sciara et al. 2017) and size at birth is around 31 cm DW (Compagno and Last 1999). As with all Myliobatiformes, the reproductive mode of M. kuhlii is livebearing and histotrophic, with embryonic nutrition supplied from a protein- and lipid-rich histotroph from highly developed trophonemata. A single, relatively large pup is produced per litter (Compagno and Last 1999, White et al. 2006b). Intrinsically, Manta and Mobula rays have among the lowest productivity of any chondrichthyan (Pardo et al. 2016). Long resting periods may account for extended reproductive cycles in mobulid species. As there are not enough data to estimate an exact generation length for this species, an approximate, suspected generation length is used. A midway point of 7.5 years between a very conservative low of five years, and the larger Spinetail Devil Ray's 10-year generation length is suspected to be the approximate generation length for the Shortfin Devil Ray until more accurate information becomes available (Cuevas-Zimbron et al. 2013).
Threats and conservation measures listed
Threats listed in assessment
Information pertaining to threats specific to the UAE is unavailable. This species is impacted by target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. Manta rays are easy to target because of their large size, slow swimming speed, aggregation behaviour and predictable habitat use.
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.