DD

Assessment ID
330442
Taxon name
Carangoides gymnostethus
(Cuvier, 1833)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carangoides gymnostethus
(Cuvier, 1833)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
carangidae
Genus
Carangoides
Species
gymnostethus
Species authority
(Cuvier, 1833)
Taxonomic notes and synonyms listed
This species is likely often misidentified as Carangoides fulvoguttatus (W. Smith-Vaniz pers. comm. 2015).
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This reef-associated, pelagic species possibly occurs throughout UAE waters, but has not been recorded there and is only confirmed from a single record in the northern Arabian Gulf. It is taken in fisheries at some level. Until it is confirmed from the UAE, this species is listed as Data Deficient.
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 has not been recorded in UAE waters, but may occur throughout based on the existence of records in the northern Arabian Gulf. Globally, it is widespread in the Indo-West Pacific (Randall and Anderson 1993, Randall 1995, Randall et al. 2003, Letourneur et al. 2004, Satapoomin 2011, R. Myers pers. comm. 2016). It occurs to 100 m depth (Allen and Erdmann 2012).
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 most commonly occurs over slightly deeper, offshore reefs (Smith-Vaniz 1984, Pereira 2000). Adults are generally solitary, while juveniles form small schools (Randall 1995). Its diet consists of small invertebrates and fishes (Carpenter et al. 1997b) and the maximum total length is 90 cm (Smith-Vaniz 1984).
Threats and conservation measures listed
Threats listed in assessment
Threats are 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
330441
Taxon name
Carangoides fulvoguttatus
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carangoides fulvoguttatus
(Forsskål, 1775)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
carangidae
Genus
Carangoides
Species
fulvoguttatus
Species authority
(Forsskål, 1775)
Taxonomic notes and synonyms listed
This species is likely often misidentified as Carangoides gymnostethus (W. Smith-Vaniz pers. comm. 2015).
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore, pelagic species occurs throughout UAE waters. It is a valued food fish in UAE fisheries, and is primarily taken in trap and handline fisheries. Catch in Abu Dhabi declined by at least 89% between 2007 to 2018, but the cause of these declines is very poorly understood. No stock assessments have been conducted or are scheduled. It is known that this is also a highly-desired species in Saudi Arabian fisheries, but the population status is also unknown. Based on the uncertainty regarding the population trend of this exploited species, it is listed as Data Deficient in UAE waters until updated data become available.
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 (Masuda et al. 1984, Randall 1995, Randall et al. 1997, Gell and Whittington 2002, Randall et al. 2003, R. Myers pers. comm. 2016). It occurs to 100 m depth (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 speciesoccurs in coastal waters near rocky and coral reefs as well as seagrass beds, and is occasionally found over offshore banks (Smith-Vaniz 1984, Gell and Whittington 2002). Itis often seen in small to large schools, but has also been observed singly. The maximum fork length is 120 cm (Torres 1991).
Threats and conservation measures listed
Threats listed in assessment
Overexploitation is a potential major threat to this species in the UAE.
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
330439
Taxon name
Carangoides equula
(Temminck & Schlegel, 1844)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carangoides equula
(Temminck & Schlegel, 1844)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
carangidae
Genus
Carangoides
Species
equula
Species authority
(Temminck & Schlegel, 1844)
Taxonomic notes and synonyms listed
In Hawaii, this species has been referred to as Carangoides dasson. Easter Island occurrences are likely conspecific with the Hawaiian fish (W. Smith-Vaniz pers. comm. 2015). Taxonomic clarification is needed on the disjunct populations reported for this species.
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In the UAE, this relatively deep-living species inhabits the continental shelf and slope on the Sea of Oman coast. Very little is known on its population; therefore, it is listed as Data Deficient in the UAE.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
In UAE waters, this species occurs only in Sea of Oman. In the Arabian Sea region, it is known only from northern Somalia, Oman and Iran (Sea of Oman). Records from Iraq (Jawad et al. 2018) require verification. Globally, it has a widespread, but patchy distribution in the Indo-West Pacific (Randall 1981, Larson et al. 2013). The depth range is 64 to 452 m (al Sakaff and Esseen 1999, Randall and Cea 2011, R. Myers pers. comm. 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 benthopelagic species occurs on the continental shelf and slope and is known to frequent deep reefs (Sommer et al. 1996, Mundy 2005, Randall and Cea 2011). The maximum fork length is 50 cm.
Threats and conservation measures listed
Threats listed in assessment
Threats are poorly understood.
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
330438
Taxon name
Carangoides coeruleopinnatus
(Rüppell, 1830)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carangoides coeruleopinnatus
(Rüppell, 1830)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
carangidae
Genus
Carangoides
Species
coeruleopinnatus
Species authority
(Rüppell, 1830)
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In UAE waters, this inshore, pelagic speciesoccurs only in the Sea of Oman, but very little is known, and has been recorded there very rarely. It is also easily confused with other Carangidae species; therefore, it is listed as Data Deficient in the UAE.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
In the UAE, this species only known from the Sea of Oman. Globally, it is widespread in the Indo-West Pacific (Smith-Vaniz 1986, Randall and Anderson 1993, Randall 1995, Naomi et al. 2011). The depth range is 10 to 25 m (Allen and Erdmann 2012).
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 speciesis commonly found over deeper coastal reefs, seagrass beds and coral reefs (Smith-Vaniz 1984, Letourneur et al. 2004, Satapoomin 2011). Due to its rather sluggish nature, this species is rarely found close to the shore (Smith-Vaniz 1984). Itis generally solitary (Kuiter and Tonozuka 2001). The maximum total lengthis 41 cm (Allen and Erdmann 2012).
Threats and conservation measures listed
Threats listed in assessment
Threats are poorly understood due to the lack of population information. It may occur in fisheries. 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
330436
Taxon name
Atule mate
(Cuvier, 1833)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Atule mate
(Cuvier, 1833)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
carangidae
Genus
Atule
Species
mate
Species authority
(Cuvier, 1833)
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore, pelagic speciesis common throughout UAE waters and is taken in fisheries. Catch on the eastern coast has declined significantly over at least the past decade or more. Catch in Abu Dhabi declined by 91% over the past 13 years, but this decline is expected to be caused at least partially by reduced fishing effort. A stock assessment conducted in 2012 for Abu Dhabi did not consider it overexploited at that time, and an update to the stock assessment was not able to be completed due to the lack of individuals available at the market to sample. It is taken in fisheries elsewhere in the Gulf and Sea of Oman region as well. Due to the potential major threat from overfishing and the very poor understanding of its population status in the UAE, it is listed as Data Deficient.
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 (Smith-Vaniz 1984, Gushiken 1984, Paxton et al. 1989, Graham and Wood 1997). The depth range is 1 to 80 m (Mundy 2005).
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 speciesforms schools in coastal waters, including bays, mangroves, estuaries and mud flats (Paxton et al. 1989). It is occasionally observed near reefs and can form very large seasonal aggregations (Carpenter et al. 1997a). The maximum total length is 30 cm (Smith-Vaniz 1984) and the size at first maturity is about 17 cm (Kasim 2003).
Threats and conservation measures listed
Threats listed in assessment
Fishing activity is not known to be driving declines in the UAE at this time. 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
330219
Taxon name
Pomadasys stridens
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Pomadasys stridens
(Forsskål, 1775)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
haemulidae
Genus
Pomadasys
Species
stridens
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore, marine and estuarine species occurs throughout UAE waters. It is apparently less common in the Arabian Gulf, than on the eastern coast. Its occurrence in fish markets has apparently declined over time on the eastern coast. It can be impacted by estuarine degradation (e.g., Egypt). Based on the uncertainty from impacts on estuarine degradation/pollution and the possibility for overfishing on the eastern coast, it is listed as Data Deficient in the UAE. Improvements in fisheries monitoring are needed.
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 restricted to the Western Indian Ocean where it occurs from South Africa to Mozambique (McKay 1984) and the Red Sea to the Arabian Gulf (B. Russell, K. Carpenter and Y. Iwatsuki pers. comm. 2013), Pakistan (Psomadakis et al. 2015) and questionably in western India (Smith and McKay 1986, Iwatsuki et al. 1995). Its depth range is 0-68 m.
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 speciesinhabits soft bottoms in coastal waters (Carpenter et al. 1997b), including estuaries (Kamrani et al. 2016). Its maximum total length is 21 cm (Safi et al. 2014). In Iran, the mean total length at first sexual maturity is 19.84 cm (Vahabnezhad et al. 2018).
Threats and conservation measures listed
Threats listed in assessment
Overfishing is a potential major threat. The inshore habitats, including estuaries, that this species is dependent on have experienced large-scale degradation in the UAE and surrounding areas. It is susceptible to deformities caused by adverse environmental conditions according to a study conducted off Iran (Alavi-Yeganeh 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
330206
Taxon name
Lethrinus microdon
Valenciennes, 1830
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Lethrinus microdon
Valenciennes, 1830
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
lethrinidae
Genus
Lethrinus
Species
microdon
Species authority
Valenciennes, 1830
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore, reef-associated species occurs throughout UAE waters. Despite an Abu Dhabi stock assessment reporting it as underexploited as of 2016, catch has declined by 75% over the past two generation lengths, or since 2009. This conflicting information cannot be clearly explained, in part due to the lack of information regarding fishing effort trends. It is also heavily exploited in areas outside the UAE. Based on the potential major threat from overfishing, this species is listed as Data Deficient in the UAE. Improvements in fisheries monitoring are needed.
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 (Carpenter and Allen 1989, Randall 1995). Its depth range is 10-80 m (Carpenter and Allen 1989).
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 speciesinhabits sandy areas near coral reefs as well as on seagrass beds. It shoals in small schools and actively feeds during the day and night on fishes, crustaceans, cephalopods and polychaetes (Carpenter and Allen 1989, Dorenbosch et al. 2005). The maximum total length is 80 cm (Kuiter and Tonozuka 2001). This species is fast-growing and short-lived with a high natural mortality rate. In the southern Arabian Gulf, spawning occurs between June and November and the mean age and size at sexual maturity is 3 years and 27.4 cm for males and 4.8 years and 29.1 cm for females (Grandcourt et al. 2010). A study conducted in the Red Sea off Egypt reported longevity of this species as 7 years (Mehanna et al. 2017). When applying an age at first reproduction of 5 years and longevity of 7 years, its estimated generation length is 6 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 potential major threat to this species in the UAE and surrounding areas. 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
330205
Taxon name
Lethrinus lentjan
(Lacepède, 1802)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Lethrinus lentjan
(Lacepède, 1802)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
lethrinidae
Genus
Lethrinus
Species
lentjan
Species authority
(Lacepède, 1802)
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore, marine species occurs throughout UAE waters. Catch declines of about 90% have occurred in Abu Dhabi over the past two generation lengths. Two recent stock assessments reported conflicting results - one assessed the stock as overfished, while the other assessed it as under-exploited. Due to this, the population status is poorly understood. With recent fisheries management measures implemented in Abu Dhabi, it is difficult to say whether fishing effort will continue to increase or decrease within the near future. Considering that other Emirates and surrounding countries that likely share this stock do not have management measures in place to reduce effort in the gargoor fishery, population declines may continue. The status of this species outside the UAE is not well-understood, but it is exploited elsewhere in the Gulf region. Due to the uncertainty regarding its population status, it is listed as Data Deficient in the UAE.
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 (Sato and Walker 1984, Carpenter and Allen 1989, Carpenter 2001). Its depth range is 0 to 50 m.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This species inhabits coastal, sandy areas, coral reefs, and deep lagoons to depths of 50 m. It primarily consumescrustaceans, molluscs, echinoderms, polychaetes and fishes (Sato and Walker 1984, Carpenter and Allen 1989). This species is a protogynous hermaphrodite and exhibits a protracted spawning season (Currey et al. 2013). In some areas, particularly Thailand, this species has been observed forming spawning aggregations (Tamelander et al. 2008). This is a fast-growing, short-lived species with high natural mortality. A study conducted in the southern Arabian Gulf reported its maximum age as 11 years, spawning occurs from April to June, and mean age and size at sexual maturity was 1.8 years and 24.6 cm for males and 2.4 years and 27.7 cm<sub> </sub>for females (Grandcourt et al. 2011). When applying an age at first reproduction of 2.5 years and longevity of 11 years, its estimated generation length is 6.75 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 potential major threat. Studies on this species in the UAE indicates it retains heavy metals sourced from nearshore pollution (Kosanovic et al. 2007). 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
330204
Taxon name
Lethrinus borbonicus
Valenciennes, 1830
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Lethrinus borbonicus
Valenciennes, 1830
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
lethrinidae
Genus
Lethrinus
Species
borbonicus
Species authority
Valenciennes, 1830
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore, reef-associated species occurs throughout UAE waters, and can be common in the Arabian Gulf. A 2010 stock assessment considered the Abu Dhabi stock to be overexploited, and in 2016, the stock was considered fully exploited. Catch in Abu Dhabi has declined by 81% over the past two generation lengths, or about 10-12 years. Fishing effort has declined in Abu Dhabi due to fisheries management to reduce the gargoor fishery since 2007, but catch declines are not fully explained by this. The status of population(s) outside the UAE are not well-understood. Based on the uncertainty regarding the population trend of this exploited species, it is listed as Data Deficient in UAE waters. Improvements in fisheries monitoring are needed.
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 restricted to the Western Indian Ocean where it occurs from South Africa, Madagascar, the Mascarenes and the Seychelles to the Red Sea, Arabian Gulf and Pakistan (Carpenter 1989, Carpenter and Allen 1989, Gaudian et al. 1995, Gillibrand 2007, K.E. Carpenter pers. comm. 2014). Its depth range is 1 to 40 m (Carpenter 1989).
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 marine species inhabits the sandy bottoms of seagrass beds and on or near coral reefs at depths of 1 to 40 m (Carpenter 1989, Khalaf et al. 2012). During the day, it is found to a depth of 40 m, occasionally occurring in small groups; however, at night, itis solitary and found over reef-flats and slopes as shallow as 1 m in depth. Itsdiet consists of echinoderms, mollusks and crustaceans. The maximum total length is 40 cm (Carpenter and Allen 1989). A study conducted in the southern Arabian Gulf, reported a maximum age of 9 years, spawning occurs from March to June, it is a short-lived, fast growing species with a high natural mortality rate, and the mean age and size at sexual maturity was 2 years and 22.1 cm for males and 1.3 years and 21.3 cm<sub> </sub>for females (Grandcourt et al. 2010). When applying an age at first reproduction of 2 years and longevity of 9 years, its estimated generation length is 5.5 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 Arabian Gulf (Grandcourt et al. 2010). According to a study conducted in the Red Sea, this species can retain relatively high levels of PAHs (Ali et al. 2014). 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
330158
Taxon name
Seriola dumerili
(Risso, 1810)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Seriola dumerili
(Risso, 1810)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
carangidae
Genus
Seriola
Species
dumerili
Species authority
(Risso, 1810)
Taxonomic notes and synonyms listed
This species is commonly misidentified as Seriola rivoliana and S. carpenteri, making market data unreliable (W. Smith-Vaniz pers. comm. 2013).
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
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This pelagic species occurs throughout UAE waters. It is a minor component of handline and trap fisheries off Abu Dhabi, but is considered valuable and highly desirable by commercial and recreational fishers. Catch in Abu Dhabi declined by about 80-90% over the past two generation lengths (about 12 years), but there is uncertainty associated with the effort trends, and catch in the recreational fishery are not recorded. Anecdotal observations of its presence in fish markets indicate it has declined on the eastern coast of the UAE. The status of population(s) outside the UAE is not well-understood, though it is also taken by fisheries elsewhere. Based on the uncertainty regarding the population trend of this exploited species, it is listed as Data Deficient in UAE waters until updated data become available. Improvements in fisheries monitoring are needed.
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. Elsewhere, it is circumglobally distributed except for the eastern Pacific (Smith-Vaniz 1984, Smith-Vaniz 2002).
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 epibenthic and pelagic species occurs over reefs or at deep offshore holes or drop-offs, usually in small or moderate-sized schools, but may be solitary (Smith-Vaniz 2002). It is also found over rocky outcrops and wrecks (Harris et al. 2007). Juveniles associate with Sargassum or flotsam in oceanic and offshore neritic waters (Bortone et al. 1977). Prey items include fish, invertebrates and sometimes live, dead, and artificial bait. Its maximum size is 188 cm total length, but common to about 70-110 cm fork length (Smith-Vaniz 2002). The fork length at 50% maturity is 64.6 cm for males and 73.3 cm for females. Several studies have estimated the maximum age using methods of varying accuracy, and in general, this fish is considered difficult to age (SEDAR9 2011). Estimates of maximum longevity range from 10-17 years, but an age of 15 years was used for this assessment as described in SEDAR33 (2014). This species is assumed to be fully mature by age two (SEDAR33 2014). The Hoenig maximum age natural mortality estimator recommended by the SEDAR33 (2014) is 0.28 year<sup>-1</sup>; however, it is unlikely that this parameter remains constant across all sizes and ages.The generation length was estimated to be 6 years using the equation 1/natural mortality + age of first reproduction. Using the equation age of first reproduction + [z * (length of the reproductive period)] where z = 0.5, generation length was estimated at 7 years. Therefore, the median of 6.5 years is applied.
Threats and conservation measures listed
Threats listed in assessment
Exploitation is a potential major threat to this species in the UAE. 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.