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DD

Assessment ID
330140
Taxon name
Lutjanus coeruleolineatus
(Rüppell, 1838)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Lutjanus coeruleolineatus
(Rüppell, 1838)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
lutjanidae
Genus
Lutjanus
Species
coeruleolineatus
Species authority
(Rüppell, 1838)
Taxonomic notes and synonyms listed
This species has been referred to as Lutjanus aya by previous authors, but Rivas (1966) concluded that Bodianus aya is not a lutjanid, but probably a sciaenid.
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 reef-associated species occurs only in the Sea of Oman, and is relatively uncommon there. It is exploited by fisheries off Oman, and it is not known if exploitation in the Sea of Oman is impacting the UAE population. Based on the uncertainty regarding the population trend of this exploited species, 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
In UAE waters, this species occurs only in the Sea of Oman, and is apparently excluded from the Arabian Gulf. Although Grandcourt (2012) lists it as occurring in the Arabian Gulf, both Allen (1984, 1985) and Randall (1995) did not include the Gulf in its range. In addition, Field (2013) notes it only occurs around the Arabian peninsula. Globally, it is restricted to the Western Indian Ocean where it occurs from Somalia to the southern Red Sea to Pakistan, India and the Gulf of Mannar (Allen 1984, Allen 1985, Goren and Dor 1994, Zajonz et al. 2000, Manilo and Bogorodsky 2003, Wilkens 2005, Al-Jufaili et al. 2010, Golani and Bogorodsky 2010, Psomadakis et al. 2015, Joshi et al. 2016). Its depth range is 10 to 20 m (Lieske and Myers 1994, Manilo and Bogorodsky 2003, Wilkens 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 species inhabits clear, coastal coral and rocky reefs. It occurs singly or in small groups (Allen 1985, Wilkens 2005). The maximum total length is 40 cm (Randall 1995, Field 2013). Along the southern Omani coast, it has a prolonged breeding season (August to March) with peak spawning occurring in October and January. The total length and age at first maturity is 28.1 cm and 2.9 yrs for males and 29.7 cm and 4.3 years for females and it has been aged up to 18 years (Al-Mamari et al. 2017). When applying an age at first reproduction of 4.5 years and longevity of 18 years, its estimated generation length is 11.25 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
A potential threat from fishing 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
330137
Taxon name
Pristipomoides filamentosus
(Valenciennes, 1830)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Pristipomoides filamentosus
(Valenciennes, 1830)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
lutjanidae
Genus
Pristipomoides
Species
filamentosus
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
In UAE waters, this relatively deep-living, reef-associated species occurs only in the Sea of Oman. It is exploited in the UAE and surrounding waters of the Sea of Oman. Anecdotal observations reported by fishermen indicate catch of this species declined by about 80% over the past decade. The generation length is not known due in part to the lack of data on age at first maturity. In addition, fishing effort trends are poorly understood. Based on the concern for its population status in the face of possible ongoing overexploitation, and general lack of data, it is listed as Data Deficient. It is recommended to conduct life history studies and improve fisheries management.
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 the Sea of Oman. A report of this species occurring in the Arabian Gulf from Blegvad (1944) is questionable (Carpenter et al. 1997b). Globally, it is widely distributed in the Indo-Pacific (Anderson and Allen 2001, Williams et al. 2006). Its depth range is 40 to 360 m (Anderson and Allen 2001).
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, reef-associated species occurs over rocky bottoms (Sommer et al. 1996). At night, it migrates vertically to the upper part of its habitat to feed on small fishes, shrimps, crabs, amphipods, ascidians and salps (Opic et al. 1994, Anderson and Allen 2001). Its maximum total length is 100 cm (Anderson 1986), but more commonly occurs to 50 cm standard length (Anderson and Allen 2001). Female fork length at first maturity ranges from 36 to 38 cm (Mees 1993).The maximum reported age is 44 years (Andrews et al. 2012).
Threats and conservation measures listed
Threats listed in assessment
Overfishing is a 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.
Assessment ID
330134
Taxon name
Sphyraena barracuda
(Edwards, 1771)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Sphyraena barracuda
(Edwards, 1771)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
sphyraenidae
Genus
Sphyraena
Species
barracuda
Species authority
(Edwards, 1771)
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, coastal species occurs throughout UAE waters. Catch in Abu Dhabi has declined by 96% since 2011, and the cause of this decline is not known. Due to concerns for its population status, it is listed as Data Deficient in the UAE. Studies are needed to estimate life history parameters (age at sexual maturity and longevity) to calculate generation length. Improvements in fisheries management is also 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 nearly circumglobally distributed in tropical to warm temperate waters, but does not occur in the eastern Pacific (Carpenter et al. 1997b, Russell 2002, Simon et al. 2013, Friedlander et al. 2014, Wirtz et al. 2014). It occurs mainly at the surface, but can be found to 100 m depth (Russell 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 pelagic species is found on shallow reefs and deep reefs to the shelf-edge (Feitoza et al. 2005). Juveniles school in shallow waters over sandy, weedy bottoms and in mangroves. Young barracuda will spend their first summer in shallow nursery areas and move offshore to deeper water in late fall. In the second summer, young enter mangrove habitat or deeper weed beds. In its third year, it enters coral reef habitat (de Sylva 1963). Larger adults (>65cm standard length) are usually solitary and found over reef areas and offshore waters. Large schools have been observed and are probably associated with spawning behavior. Its maximum length is 200 cm (Robins and Ray 1986). It feeds mainly on littoral schooling and coral reef fishes, cephalopods, and shrimps (de Sylva 1981, Cervigon 1993). It can reach at least 14 years of age. Males mature by year three, and females by year four. Off Abu Dhabi, the mean age and size at sexual maturity for males was 1.3 years and 56.2 cm and 2.6 years and 80.1 cm for females (Grandcourt et al. 2012). When applying an age at first reproduction of 2.5 years and longevity of 14 years, its estimated generation length is 8.25 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. 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
330131
Taxon name
Crenimugil seheli
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Crenimugil seheli
(Forsskål, 1775)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
mugiliformes
Family
mugilidae
Genus
Crenimugil
Species
seheli
Species authority
(Forsskål, 1775)
Taxonomic notes and synonyms listed
The taxonomy of species in the Mugilidae family is complex, and under revision (Durand and Borsa 2015). This species is commonly referred to as Valamugil seheli in the literature. According to Eschmeyer's Catalog of Fishes, it is now valid as Crenimugil seheli.
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 species occurs throughout UAE waters. It is exploited throughout the UAE, and the stock in Abu Dhabi was considered fully exploited as of 2010. Since 2007, or over the past 11 years (approximately 1.5 generation lengths), catch declined by about 86%. Fishing effort trends are not well-understood. It is also exploited in areas neighboring the UAE. An updated stock assessment is expected to occur in 2020, and until then, the status of its population in the UAE is poorly understood; therefore, it is listed as Data Deficient. 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 widely distributed in the Indo-West Pacific (Harrison and Senou 1999).
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 schools in shallow coastal waters, and is known to enter lagoons, estuaries, and freshwater rivers to feed. Mass shoaling takes place at sea during spawning. It consumes various algae, diatoms, foraminiferans, and detritus associated with sand and mud (Harrison and Senou 1999). The maximum total length is 60 cm (Lieske and Myers 1994). Spawning occurs from February to April in the southern Arabian Gulf, age and size at sexual maturity for males and females are 4.5 years and 38 cm and 4 years and 41.8 cm, respectively, and the maximum age is 9 years (Grandcourt et al. 2010). When applying an age at first reproduction of 4 years and longevity of 9 years, its estimated generation length is 6.5 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Threats and conservation measures listed
Threats listed in assessment
Overfishing is a potential major threat to this species in the UAE and surrounding areas. In addition, estuaries and nearshore habitats have been seriously degraded in the Arabian Gulf region.
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
330106
Taxon name
Pomadasys argenteus
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Pomadasys argenteus
(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
argenteus
Species authority
(Forsskål, 1775)
Taxonomic notes and synonyms listed
Pomadasys argenteus was originally described as Sciaena argentea by Forsskål (1775) from Jeddah, Saudi Arabia, Red Sea.
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 demersal, inshore species occurs throughout UAE waters. Catch declines have been recorded in both Abu Dhabi and on the eastern coast, but the cause of this decline is poorly understood. The status of population(s) outside the UAE are not well-understood, though declines have been reported from Kuwait. 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 widespread in the Indo-West Pacific (Talwar and Jhingran 1991, al Sakaff and Esseen 1999, Bijukumar and Sushama 2000, Almatar et al. 2004, Rahman and Akhter 2009, B. Russell and Y. Iwatsuki pers. comm. 2013).
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 shallow, coastal inshore waters in open bays and estuaries (McKay 1984, 2001). It can also occur near reefs and occasionally mangroves. It spawns from mid May to early October and females spawn about six times in one season (Almatar et al. 2004). The maximum total length is 70 cm (Kuiter and Tonozuka 2001).
Threats and conservation measures listed
Threats listed in assessment
Overfishing is potential major threat to 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
330103
Taxon name
Auxis rochei
(Risso, 1810)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Auxis rochei
(Risso, 1810)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
scombridae
Genus
Auxis
Species
rochei
Species authority
(Risso, 1810)
Taxonomic notes and synonyms listed
Before 1960, many researchers thought that there was only one world-wide species in the genus Auxis, which was recorded as Auxis thazard (Collette and Aaland, 1996).The species contains two subspecies; A. rochei rochei (Risso, 1810) worldwide except for the eastern tropical Pacific where it is replaced by A. r. eudorax Collette and Aadland, 1996.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This pelagic, open ocean species is not yet confirmed to occur in the UAE, but may occur on the Sea of Oman coast. If it does range into UAE waters (Sea of Oman only), its presence there is apparently marginal. There has been some confusion with Auxis thazard in some nearby areas where exploitation occurs (e.g., Iran), and this confusion may contribute to the lack of confirmed records 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
In UAE waters, this species does not occur in the Arabian Gulf (B. Collette pers. comm. 2013), but may occur on the Sea of Oman coast, though records are not yet confirmed. Elsewhere, it is cosmopolitan in warm waters (Collette and Aadland 1996).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This is a pelagic, oceanodromous species that forms schools. It is an offshore predator feeding on whatever abundant resource is available with a preference for planktonic crustaceans, small cephalopods, and fish larvae (Mostarda et al. 2007). Its maximum fork length is 50 cm. Longevity is 5 years and maturity occurs around 2 years of age or about 35 cm fork length for both males and females, but this can vary by region (Muthiah 1985, Yesaki and Arce 1994, Niiya 2001a, b, Collette 2010). When applying an age at first reproduction of 5 years and longevity of 2 years, its estimated generation length is 3.5 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
Threats to this species in the UAE and neighboring area 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
330102
Taxon name
Thunnus tonggol
(Bleeker, 1851)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Thunnus tonggol
(Bleeker, 1851)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
scombridae
Genus
Thunnus
Species
tonggol
Species authority
(Bleeker, 1851)
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, but may be less common there due to its preference for deeper waters such as areas off Iran. It is targeted by commercial fisheries that operate throughout the Indian Ocean, including the Gulf and Sea of Oman, and the Indian Ocean is considered a single stock by the Indian Ocean Tuna Commission (IOTC). According to the 2018 IOTC stock assessment, this species is overfished with overfishing occurring due to unsustainable fishing pressure. A recent assessment conducted off Iran also reported it as overfished. Catch has been declining since 2012, or over the past five years, but effort data are largely unavailable. In addition, the lack of life history studies prevents an estimation of generation length at this time. Conservation measures are likely insufficient to reduce fishing effort. Due to the lack of population and life history data, and acknowledging the ongoing major threat from overfishing across the Indian Ocean and in Iran, this species is listed as Data Deficient in the UAE. It is recommended to improve fisheries monitoring and determine generation length, specifically age at first maturity.
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, itis widely distributed in the Indo-West Pacific.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This pelagic species primarily occurs on the continental shelf, but can also occur in the open-ocean, and avoids very turbid waters and areas with reduced salinity such as estuaries. It may form schools of varying size. It feeds on a variety of fishes, cephalopods, and crustaceans, particularly stomatopod larvae and prawns. This species probably spawns more than once a year and is reported to be confined to coastal waters (Nishikawa and Ueyanagi 1991). Maximum fork length (FL) is 145 cm. Very few life history studies have been conducted, but in the Indian Ocean, longevity is about 20 years, males and females reach maturity at about 40 cm fork length and age at first maturity is not known (IOTC 2018). In Australia, longevity is estimated to be about 10 years (Wilson 1981), and age at first maturity in Thailand is estimated to be 2 years (Boonragsa 1987). It may live as long as 18 years in the central Indo-Pacific (Griffiths et al. 2009). Natural mortality in a study conducted across Iranian waters was 0.49 year<sup>-1</sup> (Darvishi et al. 2018).
Threats and conservation measures listed
Threats listed in assessment
Overfishing is a major threat to this species in the UAE in part due to its overfished status across the Indian Ocean stock, in which the Arabian Gulf and Sea of Oman are included (IOTC 2018).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
330099
Taxon name
Scomber australasicus
Cuvier, 1832
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Scomber australasicus
Cuvier, 1832
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
scombridae
Genus
Scomber
Species
australasicus
Species authority
Cuvier, 1832
Taxonomic notes and synonyms listed
The population in the Red Sea and the Arabian Sea formerly considered to be Scomber japonicus were re-identified as Scomber australasicus (Baker and Collette 1998). This population was described as a separate species, Scomber indicus by Abdussamad et al. 2016 which is considered as a subspecies here.
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 is not yet confirmed to occur in UAE waters, but may occur on the Sea of Oman coast. Little is known on its distribution, population, ecology and potential threats in the UAE; therefore, 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
In UAE waters, this species does not occur in the Arabian Gulf (B. Collette pers. comm. 2013) and has not yet been confirmed from the Sea of Oman coast, but possibly occurs there. Elsewhere, it occurs in the Red Sea and widely in the western Pacific. It has been confused with Scomber japonicus.
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 pelagic species occurs in coastal and oceanic waters to 300 m depth (May and Maxwell 1986, Collette 1995). It forms schools by size, and schools may include Jack Mackerels and Pacific Sardines. It is a plankton feeder, filtering copepods and other crustaceans, but adults also feed on small fishes and squids. The maximum fork length is 40 cm. In Australia, age at first maturity is 2 years and longevity is 8 years (Stevens et al. 1984). However, this species is larger and longer lived in New Zealand, where longevity has been estimated to be as high as 24 years (Morrison et al. 2001) and length at first maturity is 28 cm and approximately 3 years (Manning et al. 2007). In Japan, the age at first maturity is 1 year and longevity is approximately 6 years (Uozumi pers. comm. 2009). Generation length in Japan, is therefore estimated to be 2-“3 years, but may be higher in Australia and New Zealand.
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
330096
Taxon name
Sarda orientalis
(Temminck & Schlegel, 1844)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Sarda orientalis
(Temminck & Schlegel, 1844)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
scombridae
Genus
Sarda
Species
orientalis
Species authority
(Temminck & Schlegel, 1844)
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 pelagic species occurs only in the Sea of Oman. It is taken in fisheries there, and catch has been in a general decline in recent years. Data on this species' population status are lacking in general, including in the UAE as well as directly outside. It is also exploited in Oman. Considering the potential threat from fishing and little data on its population in general, 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 the Sea of Oman. It does not occur in the Arabian Gulf (B. Collette pers. comm. 2013). Globally, this species is patchily, but widely distributed in the Indo-Pacific.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This coastal, pelagic species schools with small tunas to 30 m depth. It is also found around some islands (Collette 1995). It feeds on clupeoids, other fishes, squids, and decapod crustaceans. It occurs at temperatures of 13.5-“23'°C. Fork length at first maturity is about 54 cm (Silas 1964). Maximum fork length is 102 cm.
Threats and conservation measures listed
Threats listed in assessment
Fishing is a potential threat, but this is 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
330095
Taxon name
Scomberomorus guttatus
(Bloch & Schneider, 1801)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Scomberomorus guttatus
(Bloch & Schneider, 1801)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
scombridae
Genus
Scomberomorus
Species
guttatus
Species authority
(Bloch & Schneider, 1801)
Taxonomic notes and synonyms listed
A revision of Scomberomorus was conducted by Collette and Russo (1985).
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, coastal species occurs throughout UAE waters. It is taken in the highly-valued fishery that targets Scomberomorus commerson throughout the Arabian Gulf and Sea of Oman. It is easily confused with S. commerson, and as a result, species-specific data are not available. The population of S. commerson has declined by 50-70% over the past 30 years, and remains overexploited. In addition, fishing effort is increasing. Considering the uncertainty on its population status, and potential major threat from overfishing, it is listed as Data Deficient in the UAE. It is recommended to improve fisheries data collection for this species.
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, itis widely distributed in the Indo-West Pacific.
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This is a pelagic migratory fish inhabiting coastal waters to 200 m depth. It sometimes enters turbid estuarine waters, and is usually found in small schools. It feeds mainly on small schooling fishes (especially sardines and anchovies), squids and crustaceans. Adults can reach a maximum fork length of 76 cm. Maturity occurs at around 48-“52 cm total length or 1-“2 years in southern India, and about 40 cm in Thailand (Krishnarnoorthy 1958). This species may live to 16 years of age (Devaraj 1977). When applying an age at first reproduction of 2 years and longevity of 16 years, its estimated generation length is 9 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 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.