Assessment ID
329879
Taxon name
Carcharhinus amblyrhynchoides
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
329876
Taxon name
Urogymnus asperrimus
Uploaded by
National Red List Database
Scientific name
Urogymnus asperrimus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
dasyatidae
Genus
Urogymnus
Species
asperrimus
Taxonomic notes and synonyms listed
Formerly, U. asperrimus was the only species within Urogymmus. Last et al. (2016) added five more species to the genus.
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Porcupine Ray occurs throughout UAE inshore waters, but is rarely observed. It is highly susceptible to a variety of fishing methods, and its life history characteristics cause it to be particularly susceptible to population decline in areas where fishing pressure is high. Significant declines of rays have been documented in parts of the Arabian Sea region (e.g., India), and the loss of coastal habitats across the region is also a concern. Though data specifically from the UAE are not available, and it is not known how individuals occupying the UAE are connected with the broader population of the Arabian Seas region, there is no information available to suggest that its population status differs in the UAE as compared to other parts of its range in the region. 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 30% over the past three generation lengths, or about 64 years. It is listed as Vulnerable 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 Porcupine Whipray occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The occurrence of this species appears to be patchy with localized hotspots (Chin 2014). Juveniles appear to be site-attached, and highly resident to small areas of shallow coastal mud and mangrove habitats (Cerutti-Pereyra et al. 2014). It has been recorded from coral reefs, sandy reef lagoons, beaches, mud flats and mangroves, at depths of ~1 m to at least 30 m (O'Shea 2013, Cerutti-Pereyra et al. 2014, Chin 2014).The Porcupine Ray reaches a maximum size of at least 115 cm disc width (DW) with females mature by ~100 cm DW and males at ~90 cm DW (Last and Stevens 2009). Little else is known of the biology of this species. Attempts to collect size-at-age data from vertebral counts have proved difficult due to the fragile nature of vertebra (O'Shea 2013). Using data from the Brown Stingray (Dasyatis lata), a related species from the Pacific as a proxy, generation length for the Porcupine Ray is inferred to be 21.5 years (Dale and Holland 2012).
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. Its small litter size and schooling behaviour in inshore areas causes it to be susceptible to rapid population declines when experiencing intense fishing activity. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
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
329875
Taxon name
Rhynchobatus djiddensis
Uploaded by
National Red List Database
Scientific name
Rhynchobatus djiddensis
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
rhinidae
Genus
Rhynchobatus
Species
djiddensis
Taxonomic notes and synonyms listed
Rhynchobatus djiddensis is part of the Indo-West Pacific Rhynchobatus djiddensis species-complex. The name R. djiddensis has previously been used widely, leading to poorly-defined taxonomy and distributions for members of the complex (in particular, R. australiae, R. djiddensis, and R. laevis). Further investigation into the taxonomy of 'whitespotted wedgefish' is required, and additional species are likely to be described in the future.
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)
A2bcd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Whitespotted Wedgefish occurs throughout UAE coastal waters. There has been a total ban on fishing for this species in UAE waters since 2019. Confusion amongst the species of Rhynchobatus that occur in the Arabian Sea causes a high level of uncertainty when interpreting catch data as well as an understanding of the extent of this species' range. It is taken as bycatch in gill net, longline and trawl fisheries and its fins are highly valued in international trade. Coastal development is causing habitat degradation, which may also be impacting this species. Significant declines in wedgefish populations are known in India, southern Oman, Pakistan and Iran. 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, 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, landings data and decline in habitat quality, it is suspected to have declined by 50-80% over the past three generation lengths, or about 39 years. It is listed as Endangered A2bcd.
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 Whitespotted Wedgefish occurs throughout UAE waters (Hellyer and Aspinal 2005, Jabado et al. 2015). Globally, it is widespread in the Western Indian Ocean, but may not be present in Pakistan, India, Sri Lanka and the Maldives (Last et al. 2016). It is apparently confirmed from the Red Sea, but with some uncertainty surrounding nomenclature (Giles et al. 2016). However, the difficulties in distinguishing between species of Rhynchobatus causes some of its distribution to be uncertain (Henderson et al. 2016).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Whitespotted Wedgefish inhabits coastal and continental shelf waters to depths of 70 m, but typically occurs in depths shallower than 35 m. It attains a maximum size of about 310 cm total length (TL), although it is typically smaller at around 175 cm TL, with males mature at about 150 cm TL (Last et al. 2016). Size at birth is about 60 cm TL. Maximum age for Rhynchobatus spp. in Australia is 5 years (males) and 12 years (females), but these data were not from the largest individuals (White et al. 2014) and are not reliable for the estimation of generation length. This is therefore estimated from the maximum age (19 years) and age at maturity (7 years) taken from the growth curve provided by White et al. (2014) for the Giant Guitarfish (Glaucostegus typus), which gives an estimated generation length of 13 years.
Threats listed in assessment
This species is impacted by target and bycatch fisheries in the UAE. 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
329874
Taxon name
Pristis zijsron
Uploaded by
National Red List Database
Scientific name
Pristis zijsron
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
pristidae
Genus
Pristis
Species
zijsron
Taxonomic notes and synonyms listed
Recent taxonomic work has confirmed that the Green Sawfish (Pristis zijsron) is a valid species with an Indo-West Pacific distribution (Faria et al. 2013).
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
Critically Endangered
Abbreviated status
CR
Qualifying criteria (if given)
A2bcd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Green Sawfish occurs throughout UAE inshore and offshore waters, and was historically relatively abundant there. Capture of this species has been banned in the UAE since 2008, but accidental captures, especially in gill net fisheries, still occur. According to fisher interviews conducted in the UAE, sightings of this species declined by 72% over at least the past 17 years and that it was historically more abundant around 20 years ago. The species is now very rarely sighted, with the last sighting occurring in Abu Dhabi in 2016. 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 and demersal 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. 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 fisher interviews, recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 80% over the past three generation lengths, or about 45 years. It is listed as Critically Endangered A2bcd. Based on the continuation of gill net fisheries and nearshore habitat degradation, the species remains under threat, though the ban of its capture in the UAE may have mitigated threats to some degree. Further research is needed on population trends and life history.
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 Green Sawfish occurs throughout UAE waters. Globally, it was historically widespread in the Indo-West Pacific, including throughout the Arabian Sea region from the Red Sea to India (Harrison and Dulvy 2014, Dulvy et al. 2016). Its current occurrence in much of this region is uncertain due to a lack of reliable data, but it is presumed to have been extirpated from much of its range due to severe impacts from intensive inshore gill net and trawl fisheries. It is currently known to be extant in Sudan, Eritrea and the UAE (Dulvy et al. 2016, Jabado et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
Green Sawfish are most common in shallow water coastal and estuarine areas, but occur to depths to over 70 m (Stevens et al. 2005). In the UAE, specimens of up to 600 cm TL were reported from shallow sandy areas with seagrass or further offshore by fishers (Jabado et al. 2017). A 350 cm total length (TL) female and a 250 cm TL male tracked in Australia remained in shallow water (mean depth <1.5 m) and within 200 m of a mangrove shoreline (Peverell and Pillans 2004, Stevens et al. 2008). The young are known to use nearshore and estuarine areas as nurseries, and adults occur more broadly and into deeper areas (Stephenson and Chidlow 2003).Green Sawfish may be the largest of the sawfishes, with reports of individuals up to 730 cm TL (Weigmann 2016). Mean size at birth in the Gulf of Carpentaria is 76 cm TL, and size at maturity at 340 to 380 cm TL (Peverell 2008, Last and Stevens 2009). Age and growth based on specimens from the Gulf of Carpentaria indicate that maturity is reached at about nine years, and maximum age may be >50 years (Peverell 2008). Little is known of its reproductive biology. Reproduction is aplacental viviparous and litter size is about 12. Demographic models based on life history data from the Gulf of Carpentaria indicate that the generation time is 14.6 years, the intrinsic rate of population increase is very low (0.02 yr<sup>-1</sup>), and population doubling time is ~28 years (Moreno Iturria 2012).
Threats listed in assessment
In the UAE, this species has been impacted by high levels of largely unmanaged and unreported mortality in target and bycatch fisheries. Fishers reported overfishing as the major cause for the observed decline in this species (Jabado et al. 2017). Though fishing for this species in the UAE has been banned since 2008, the species remains greatly threatened by accidental capture. Other threats include habitat loss (particularly loss of mangrove forest, intertidal areas, and coastal development), pollution, and climate change. Marine habitats in the Gulf, including the UAE, are experiencing high levels of disturbance due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). Suspected historical nurseries sites used by this species have been lost to coastal development (Al Hameli pers. comm. 2019). Across its range, continuing threats from mostly unregulated and unmanaged fisheries as well as habitat loss and degradation are resulting in the continual declines of remnant populations (Dulvy et al. 2016).
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
329870
Taxon name
Triaenodon obesus
Uploaded by
National Red List Database
Scientific name
Triaenodon obesus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Triaenodon
Species
obesus
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
Data Deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
In the UAE, the Whitetip Reef Shark possibly occurs only in coastal waters of the Sea of Oman, but this is not yet confirmed. The species exhibits moderately slow life history characteristics, and is impacted by extensive fishing pressure and habitat loss and degradation throughout the Arabian Sea region. Little is known on the population of this species in UAE waters and given its distribution there remains uncertain, it is listed as Data Deficient.
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 Whitetip Reef Shark may occur in UAE waters on the Sea of Oman coast, but this is not yet confirmed. It is excluded from the Arabian Gulf (Al Jufaili et al. 2010). Globally, it is widespread in the tropical Indo-West Pacific (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
Whitetip Reef Sharks are closely associated with coral reefs in clear, tropical waters. This species is primarily nocturnal, sheltering in caves by day, often communally. Maximum size is around 200 cm total length (TL), but adults are very rare over 160 cm. Maturity is attained at about 105 cm TL, although a mature male of 95 cm TL and a pregnant female of 102 cm TL have been recorded in the Maldives (Anderson and Ahmed 1993). Mating has been recorded in the wild by Tricas and Le Feuvre (1985) and pups are born at 52-60 cm TL after a gestation period of at least five months. Litter size has been recorded as 2-3 in Madagascar (Fourmanoir 1961, Last and Stevens 1994) and 1-5 elsewhere (Randall 1977, Last and Stevens 1994). Growth is slow in the wild, estimated at 2.1-4.2 cm year<sup>-1</sup> (Randall 1977), and it may attain sexual maturity at eight to nine years and live to about 16 years (Randall 1977, Smith et al. 1998). Generation length is estimated to be 12.25 years (Randall 1977).
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
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
329869
Taxon name
Prionace glauca
Uploaded by
National Red List Database
Scientific name
Prionace glauca
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Prionace
Species
glauca
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
Data Deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
In UAE waters, the Blue Shark may occur only in offshore waters of the Sea of Oman, though this remains unconfirmed. This species is considered productive, as it is relatively fast-growing and fecund. Around the world, the Blue Shark is taken in large numbers (an estimated 20 million individuals annually), mainly as bycatch, but there are no population estimates and many catches are unreported. IOTC fishery assessments suggest a wide range of stock statuses ranging from 'underexploited' to 'overfished with overfishing' occurring. Little is known on the population of this species in UAE waters. Given that its distribution in UAE waters (the Sea of Oman) remains uncertain, this species is listed as Data Deficient.
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 Blue Shark may occur in UAE waters on the Sea of Oman coast, but is not yet confirmed from there. It is excluded from the Arabian Gulf. Globally, it occurs throughout tropical and temperate seas from latitudes of about 60'°N to 50'°S (Last and Stevens 2009).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Blue Shark is oceanic and pelagic, found from the surface to depths of 1000 m (Weigmann 2016). It occasionally occurs close inshore when the continental shelf is narrow. This species reaches a maximum size of about 380 cm total length (TL). About 50% of males in the Atlantic are sexually mature by 218 cm, although some may reach maturity as small as 182 cm TL. Females are sub-adult from 173-221 cm TL and fully mature from 221 cm TL (Pratt 1979), although pregnant specimens as small as 183 cm TL have been recorded from the eastern Pacific (Williams 1977).Blue Sharks are placentally viviparous, producing litters averaging about 35 pups (maximum recorded 135) after a gestation period of 9-12 months. At birth, pups measure 35-50 cm TL. Reproduction has been reported as seasonal in most areas, with the young often born in spring or summer (Pratt 1979, Stevens 1984, Nakano 1994) although the periods of ovulation and parturition may be extended (Hazin et al. 1994). Ageing studies suggest a longevity of about 20 years with males maturing at 4-6 and females at 5-7 years (Stevens 1975, Cailliet et al. 1983, Nakano 1994). Smith et al. (1998) estimated the intrinsic rate of population increase at MSY to be 0.061.Generation length is estimated to be 10.5 years based on study of Blue Shark in the Northwest Pacific by Nakano (1994).
Threats listed in assessment
Given the lack of clarity around the species occurrence in UAE waters, threats are poorly understood. In the UAE, sharks have been impacted by targeted commercial fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). Sharks continue to be impacted by artisanal and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018), though catch data are not species-specific. Marine habitats in the region have experienced high levels of disturbance and are quickly deteriorating due to major impacts from development activities (Sheppard <em style=""font-variant-ligatures: normal;font-variant-caps: normal;orphans: 2; text-align:start;widows: 2;-webkit-text-stroke-width: 0px;text-decoration-style: initial; text-decoration-color: initial;word-spacing:0px"">et al. 2010).
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
329868
Taxon name
Galeocerdo cuvier
Uploaded by
National Red List Database
Scientific name
Galeocerdo cuvier
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Galeocerdo
Species
cuvier
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
Critically Endangered
Abbreviated status
CR
Qualifying criteria (if given)
A2bcd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Tiger Shark occurs throughout UAE waters. In the UAE, this species has historically been impacted by both targeted fishing and by-catch as well as habitat degradation and loss from coastal development. Catch in the UAE has declined by about 90% over the past three generation lengths. A series of conservation measures have been put in place to reduce shark fishing effort in UAE waters since 2008. It is apparently highly migratory, and has slow life history characteristics including low fecundity and a low annual rate of population increase. Considering this, the species has a low capacity to recover from even moderate levels of exploitation. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Elsewhere in the Arabian Sea region, this species has also experienced documented declines (e.g., Iran, the Red Sea, Yemen, Pakistan and India). Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Based on fish market surveys, fisher interviews, recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 80% over the past three generation lengths, or about 52 years. It is listed as Critically Endangered A2bcd. Monitoring of the species population trend moving forward should be a priority.
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 Tiger Shark occurs throughout UAE waters. Globally, it is widespread in tropical waters (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 Tiger Shark inhabits reef and slope habitats, is sometimes associated with coral reefs, and occasionally makes longer-distance excursions into the pelagic zone. It regularly dives to depths greater than 1000 m and has been noted to move hundreds to thousands of kilometres (Holmes et al. 2014, Werry et al. 2014). It attains a maximum size of at least 550 cm total length (TL). In the north-west Hawaiian Islands, Tiger Sharks with a precaudal length of 200 cm were estimated to be about five years old and one of 300 cm was about 15 years old (De Crosta et al. 1984). Branstetter et al. (1987) estimated that initial growth was very fast, but that the rate of growth of very large animals is 5-10 cm year<sup>-1</sup>; thus, individuals of 400-450 cm TL would be 20-25 years of age. Branstetter et al. (1987) reported a maximum age of 45-50 years. Smith et al. (1998) estimated the intrinsic rate of increase of a tiger shark population at MSY to be 0.043 year<sup>-1</sup>. Randall (1992) summarised that the size at maturity of males is 226-290 cm TL and females 250-350 cm TL.The Tiger Shark is the only species in the Carcharhinidae family that is lecithotrophic viviparous. Litter sizes are large, with between 10-82 embryos reported from a single female. Mean litter sizes of 30-35 have been reported (Tester 1969, Bass et al. 1975, Simpfendorfer 1992). The size at birth is 51-90 cm TL (Randall 1992, Simpfendorfer 1992). Clark and von Schmidt (1965) reported the gestation period as 13-16 months. There have been few other estimates of gestation period. Mating is reported to take place in the Northern Hemisphere in spring, with pupping the following spring to summer. Mating occurs before full-term females have given birth to young, indicating that litters are produced every two years or less. Based on data from the North West Atlantic, generation length is estimated at 17.5 years (Natanson et al. 1999).
Threats listed in assessment
In the UAE, this species has historically been impacted by both targeted fishing and by-catch, habitat degradation and loss from coastal development. Finning has been banned in the UAE, yet surveys indicate that some trade in the fins and meat of this species still occurs. Sharks are impacted by high levels of largely unmanaged and unreported mortality in target (for fins and their valuable meat) and bycatch fisheries. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
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.