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EN

Assessment ID
329919
Taxon name
Epinephelus areolatus
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Epinephelus areolatus
(Forsskål, 1775)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
epinephelidae
Genus
Epinephelus
Species
areolatus
Species authority
(Forsskål, 1775)
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)
A2bcd+4bcd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species inhabits both soft and hard bottom habitats throughout UAE waters. It is exploited by grouper fisheries, and it appears likely that this species is overfished in the UAE. During the period from 2005-2016, a 67% decline in landings of this species occurred off Abu Dhabi. In addition, due to severe declines in Gulf coral reefs, this species may also be impacted by habitat degradation. The status of population(s) outside the UAE is not well-understood, though it is also heavily exploited elsewhere, especially off Oman and Iran. Based on fish market observations and catch data, it is inferred that this species has declined by at least 50-60% in the UAE since about 1995, or a little over one generation length (29 years). Fishing effort is expected to remain the same or increase in the future time period over the next two generations. Therefore, it is listed as Endangered A2bcd+4bcd.
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
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Russell and Houston 1989, Randall and Heemstra 1991, Randall et al. 2003). Its depth range is 2 to 200 metres.
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 continental shelf species is usually found in turbid water in seagrass beds or silty sand bottoms around isolated small rock outcrops, as well as near dead coral or soft coral as deep as 200 metres (Randall and Ben-Tuvia 1983, Leis 1987, Randall and Heemstra 1991). Juveniles are common to depths of 80 m (Kailola et al. 1993). It has also been observed on artificial reefs in Hong Kong (AFCD 2001). It feeds on fish and benthic invertebrates, primarily prawns and crabs (Parrish 1987, Randall and Heemstra 1991, Salini et al. 1994, Kulbicki et al. 2005). It is thought to spawn during seasonal periods and form spawning aggregations (Shapiro 1987). Maximum total length is 47 cm and maximum weight is 1.4 kg (Moran et al. 1988). The maximum reported age for this species is 15 years (Shapiro 1987), but a study conducted in northern Oman recorded a maximum age of 39 years and total length of 48 cm (J. McIlwain unpublished data). The length and age at first sexual maturity is 22.8 cm and 2 years for males and 23.5 cm and 2 years for females, respectively (Mahmoud 2009). When applying an age at first reproduction of 2 years and longevity of 39 years, its estimated generation length is 20 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Threats and conservation measures listed
Threats listed in assessment
Overexploitation is a major threat to this species in the UAE. Its occurrence in the trap (gargoor) fishery as ghost fishing may also cause mortality in this species. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
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
329912
Taxon name
Lutjanus argentimaculatus
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Lutjanus argentimaculatus
(Forsskål, 1775)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
lutjanidae
Genus
Lutjanus
Species
argentimaculatus
Species authority
(Forsskål, 1775)
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)
A2bcd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This reef and estuarine-associated species occurs throughout UAE waters. It is heavily exploited and very highly-valued in the Arabian Gulf, including the UAE. A 2013 Abu Dhabi stock assessment concluded it is overexploited, especially due to the high rate of juvenile retention, which has led to growth overfishing. Though catch quantity has been relatively low over the time period from 2009-2018, it has virtually disappeared from fisheries catch on both coasts of the UAE. In addition, mangrove and estuarine degradation in the Arabian Gulf region is serious, and a likely additional threat to nursery habitat for this species. The status of population(s) outside the UAE is not well-understood, but it is exploited elsewhere as well. Based on stock assessment, catch data and fish market observations, this species is inferred to have declined by at least 50% or possibly more than 80% over at least half of a generation length, or the past decade. Three generation lengths is about 75 years, but data are not available to calculate a decline over this period. Considering this species is particularly long-lived and late to maturity, it is intrinsically susceptible to declines from overexploitation. Assuming that the population was stable previous to 2009, we suspect a decline of at least 50% with an expected continuing decline due to fishing effort trends. It is listed as Endangered A2bcd.
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
This species occurs throughout UAE waters. Globally, it is widely distributed in the Indo-West Pacific (Anderson and Allen 2001). Its depth range is 1 to 120 m (Lieske and Myers 1994).
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 reef-associated species often occur in groups around coral reefs and sometimes extends to depths in excess of 100 m. Juveniles and young adults occur in mangrove estuaries, as well as the lower reaches of freshwater streams and tidal creeks (Lieske and Myers 1994, Sommer et al. 1996, Russell et al. 2003). This nocturnal species consumes fishes and crustaceans (Anderson and Allen 2001). The maximum total length is 150 cm (Torres 1991). The natural mortality for this species is measured at 0.158 (Russell et al. 2003). In a cooler part of its range, off eastern Australia, it has been aged at up to 57 years old (Piddocke et al. 2015). Spawning occurs off Abu Dhabi from September to October, longevity is estimated to be 37 years and the mean age and size at first sexual maturity is 14 years and 56.4 cm fork length for females and 13 years and 55.8 cm for males (Grandcourt et al. 2013). When applying an age at first reproduction of 14 years and longevity of 37 years, its estimated generation length is 25.5 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Threats and conservation measures listed
Threats listed in assessment
Overfishing is a major threat to this species in the UAE (Grandcourt et al. 2013). In addition, juveniles are dependent on mangroves and associated freshwater-influenced areas, which is a habitat that has been destroyed or severely degraded in the Arabian Gulf region as a result of coastal development (A. Al-Kuwari, E. Abdulqader, F. Kaymaram, K. Al-Khalaf, J. Bishop, Q. Alghawzi, S. Alam, S. Hartmann pers. comm. 2013). Historically, mangrove area declined on the Arabian Gulf coast of the UAE, but since the 1990s, mangrove area has increased somewhat in part due to restoration efforts. The percent decline over the entire time period of three generation lengths is poorly understood. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
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
329909
Taxon name
Glaucostegus granulatus
(Cuvier, 1829)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Glaucostegus granulatus
(Cuvier, 1829)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
glaucostegidae
Genus
Glaucostegus
Species
granulatus
Species authority
(Cuvier, 1829)
Taxonomic notes and synonyms listed
Changes to the systematics of Rhinobatos elevated the subgenus Glaucostegus to full generic status and placed this genus into a family of its own: Glaucostegidae (Compagno 2005, Last et al. 2016a). This species is often confused with Glaucostegus typus and Pacific Ocean records of G. granulatus are probably G. typus.
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 Sharpnose Guitarfish occurs throughout UAE coastal waters, and may be naturally uncommon there. It likely grows slowly and matures late, which causes it to have a low productivity and be particularly susceptible to declines when experiencing exploitation. It is commonly taken in gill net and trawl fisheries, and coastal development is a significant threat. Significant declines of wedgefishes and guitarfishes have been documented in India, Pakistan and Iran. There has been a total ban on fishing for this species in UAE waters in place since 2019. 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 50-80% over the past three generation lengths, or about 39 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 Sharpnose Guitarfish occurs throughout UAE waters. Globally, it is moderately widespread in the northern Indian Ocean from the Arabian Gulf to 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 Sharpnose Guitarfish commonly occurs in intertidal areas, but has been recorded to depths of 119 m (Compagno and Last 1999). It attains a maximum size of at least 229 cm total length (TL) (Last et al. 2016). Size at birth is believed to be around 39 cm TL (Moore et al. 2012), but little else is known of its biology. The estimation of generation length is 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 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. This species may also be impacted by coastal development and habitat degradation (Moore et al. 2012), especially since juveniles utilize inshore areas as 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 sea-filling), 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
329897
Taxon name
Rhynchobatus laevis
(Bloch & Schneider, 1801)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Rhynchobatus laevis
(Bloch & Schneider, 1801)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
rhinidae
Genus
Rhynchobatus
Species
laevis
Species authority
(Bloch & Schneider, 1801)
Taxonomic notes and synonyms listed
Rhynchobatus laevis 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). Rhynchobatus yentinensis Wang, 1933 (described from China) might be applicable to this species or may be a synonym of R. springeri. Further investigation into the taxonomy of 'whitespotted wedgefish' is required, and additional species are likely to be described in the future.
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)
A2bcd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Smoothnose Wedgefish occurs throughout UAE inshore waters in shallow bays and off river mouths. There has been a total ban on fishing for this species in UAE waters since 2019. The similarity of the three species of Rhynchobatus that occur in the region mean there are few reliable species-specific data available. It is commonly taken as bycatch in gillnet, 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 are known in India, southern Oman, Pakistan and Iran. Little is known on the population of this species in UAE waters. 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.
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 Smoothnose Wedgefish occurs throughout UAE waters. Globally, it has a poorly-defined distribution in the Indo-West Pacific due to difficulties in distinguishing between species of Rhynchobatus (Last et al. 2016). It is confirmed in the Arabian Gulf and Sea of Oman (Giles 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
This species occurs mainly near the coast in shallow bays and off river mouths (Last et al. 2016). Maximum size is unknown but it attains at least 200 cm total length (TL) with males mature at about 130 cm TL (Last et al. 2016). Size at birth is unknown, although the closely related R. djiddensis is born at about 60 cm total length (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 and conservation measures listed
Threats listed in assessment
This species is impacted by target and bycatch fisheries. This species 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
329896
Taxon name
Rhynchobatus australiae
Whitley, 1939
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Rhynchobatus australiae
Whitley, 1939
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
rhinidae
Genus
Rhynchobatus
Species
australiae
Species authority
Whitley, 1939
Taxonomic notes and synonyms listed
Rhynchobatus australiae 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.
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)
A2bcd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Bottlenose Wedgefish occurs throughout UAE inshore and offshore waters. There has been a total ban on fishing for this species in UAE waters since 2019. The similarity of the three species of Rhynchobatus that occur in the region mean there are few reliable species-specific data available. It is commonly 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 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.
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 Bottlenose Wedgefish occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Last et al. 2016, Giles et al. 2016). However, the difficulties in distinguishing between species of Rhynchobatus causes some of its distribution to be uncertain.
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 occurs in inshore and offshore waters over soft substrates to depths of 60 m or more (Last et al. 2016), but can also be associated with coral reefs. It attains a maximum size of about 300 cm total length (TL) with males mature at about 124 cm TL (Last et al. 2016). Size at birth is unknown, although the closely related R. djiddensis is born at 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 and conservation measures listed
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). 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
329892
Taxon name
Negaprion acutidens
(Rüppell, 1837)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Negaprion acutidens
(Rüppell, 1837)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Negaprion
Species
acutidens
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
The Sharptooth Lemon Shark occurs throughout UAE inshore and offshore waters. In the UAE and neighboring countries, it is a minor component of shark landings, and may be relatively rarely occurring in the area. It is at risk from extensive fishing pressure by longline and gill net fisheries that operate throughout the Arabian Sea region. Extensive habitat degradation and loss due to coastal development in the Arabian Gulf region may also be impacting the species. It is apparently highly migratory, and has slow life history characteristics including low fecundity and a low annual rate of population increase. Considering this, the species has a low capacity to recover from even moderate levels of exploitation. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. Though data specifically from the UAE are not available, individuals in the UAE are a component of a larger, interconnected and migratory population that occurs broadly in the north-western Indian Ocean. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 50% over the past three generation lengths, or about 49 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 Sharptooth Lemon Shark occurs throughout UAE waters. Globally, it is widespread in the Indo-West and Central 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 Sharptooth Lemon Shark occurs in shallow inshore and offshore waters near the bottom and is often found on and around coral reefs and on sandy plateaus near coral at depths to at least 30 m (Stevens 1984, Compagno 1998). It is also known to occur around and within the mangrove forests in certain areas of the UAE (Abu Dhabi) and Sudan (Suakin), which may be used as nursery grounds (Bonfil 2003, R. W. Jabado pers. comm. 06/02/2017). The maximum size reported is 340 cm total length (TL) with size at maturity around 220 cm TL for males and females (Compagno et al. 2005). The gestation period is recorded at 10 to 11 months, a reproductive periodicity of two years with a litter size average of 9.3 (6 to 12) and size at birth of 60 cm TL. Growth rates are reported at 12.5 to 15.5 cm per year. The generation length is suspected to be around 16.5 years, similar to that of the Lemon Shark (Negaprion brevirostris), which reaches a similar maximum size (Brown and Gruber 1988).
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). 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
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Rhynchobatus djiddensis
(Forsskål, 1775)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
rhinidae
Genus
Rhynchobatus
Species
djiddensis
Species authority
(Forsskål, 1775)
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.
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)
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.
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 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
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
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 and conservation measures listed
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
329873
Taxon name
Sphyrna zygaena
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Sphyrna zygaena
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
sphyrnidae
Genus
Sphyrna
Species
zygaena
Species authority
(Linnaeus, 1758)
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)
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.
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 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
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
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 and conservation measures listed
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
(Rüppell, 1837)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Sphyrna mokarran
(Rüppell, 1837)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
sphyrnidae
Genus
Sphyrna
Species
mokarran
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)
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.
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 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
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
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 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). 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
(Griffith & Smith, 1834)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Sphyrna lewini
(Griffith & Smith, 1834)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
sphyrnidae
Genus
Sphyrna
Species
lewini
Species authority
(Griffith & Smith, 1834)
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)
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.
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 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
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
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 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. 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.