United Arab Emirates

Official name
United Arab Emirates
ISO alpha-2 code
AE
ISO alpha-3 code
ARE
ISO numeric-3 code
784
Continent
Asia

Himantura leoparda | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
The Leopard Whipray is demersal on soft substrates and is mainly inshore and coastal, though it also occurs on the continental shelf to at least 70 m depth (White et al. 2006, Manjaji-Matsumoto and Last 2008). Himanura species exhibit a strong association with shallow waters of the western region where complex habitats such as coral assemblages and seagrass beds are most prevalent (Last et al. 2016 Rays of the World book). The biology of this species is poorly known, partly due to confusion with other species of the “uarnak' species-complex, especially the Reticulate Whipray (H. uarnak) and the Honeycomb Whipray (H. undulata) (Last and Stevens 2009). It attains about 140 cm disc width (DW); born at about 20 cm DW; males mature at 70-“94 cm DW (White and Dharmadi 2007, Last and Stevens 2009). Its reproduction is viviparous (White et al. 2006). It typically has1-4 young and reproduces year-round (Rastgoo et al. 2015). As there is no information on this species' maximum age and age at maturity, generation length was inferred as 20 years based on data for the congener, the Blackspotted Whipray (Himantura astra). Female Blackspotted Whiprays are reported to have a maximum age of 29 years and an age at maturity of nine years (Jacobsen and Bennett 2011). These were used to calculate a generation length of 19 years based on the equation: generation length = 9+((29-9)/2). The maximum size of the Leopard Whipray is considerably larger (~140 cm DW) than that of the Blackspotted Whipray (80 cm DW) so it is possible the generation length of the Leopard Whipray is greater than 20 years.
Taxon
Taxa
Himantura leoparda | Manjaji-Matsumoto & Last, 2008
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
The Leopard Whipray (Himantura leoparda) is a recently described (2008) species closely related and similar in shape and dorsal disc pattern to the Reticulate Whipray (H. uarnak) and Honeycomb Whipray (H. undulata). These three species are in the “uarnak' species-complex, a subgroup of mainly reticulated, ocellated or spotted whiprays. The Leopard Whipray can be distinguished by its unique arrangement of midscapular denticles and the leopard-like markings on the dorsal surface of adults and large specimens. Juveniles of the three species are born at different sizes and vary slightly in colour patterns and denticle shapes (Manjaji-Matsumoto and Last 2008, Last and Stevens 2009). Taxonomic work is currently ongoing to more clearly define the sister species relationships (P. Last pers. comm. 2010).Previously, this species has been misidentified as Dasyatis uarnak: Wallace 1967; Himantura fava: Compagno and Roberts 1982; Himantura sp. 1: Gloerfelt-Tarp and Kailola 1984; Himantura uarnak: Compagno 1986, Compagno et al. 1989; and Himantura undulata: Last and Stevens 1994, Last and Compagno 1999, White et al. 2006.
Taxon distribution as listed in assessment
The Leopard Whipray occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Last et al. 2016).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
A2cd
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
The Leopard Whipray occurs throughout UAE coastal waters. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980 and recently conducted surveys indicate it remains common in the area; however, Himantura species are discarded from catches in the UAE and it is unknown how this impacts the species. A large part of the species distribution in the Arabian Sea region (namely, India and Pakistan) is under extremely intense and increasing demersal fishing pressure. In contrast, Himantura species are regularly discarded in the Arabian Gulf and Sea of Oman, and they remain common there. 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. Given the intense fishing pressures faced by this species in other parts of the broader Arabian Seas region, and ongoing threats from discard and habitat loss in the UAE, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 30% over the past three generation lengths, or about 60 years. It is listed as Vulnerable A2cd.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Pomadasys kaakan | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This speciesinhabits coastal rocky and coral reefs (Valinassab et al. 2011). Juveniles also occur in turbid inshore waters and estuaries, including mangrove habitats over sand and mud bottoms (Van der Elst 1993). Its maximum total length is 80 cm, but occurs more commonly to 45 cm (McKay 2001). Its maximum age is 36 years (Al-Husaini et al. 2001). Itspawns from February to July (Al-Husaini et al. 2001) and forms shoals near river mouths during the winter.
Taxon
Taxa
Pomadasys kaakan | (Cuvier, 1830)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Pomadasys kaakan may be confused with P. argenteus in the literature.
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Hata et al. 2015). Its depth range is 0-75 metres (Smith and McKay 1986).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This inshore, reef-associated species occurs throughout UAE waters, but is naturally uncommon to rare on the Arabian Gulf coast. It is easily confused with Pomadasys argenteus. Population data from the UAE are limited. Anecdotal information indicates some level of decline may have occurred on the eastern coast. It is heavily exploited in parts of the Arabian Gulf and Sea of Oman, and declines have occurred in at least Kuwait and Iran, although it remains abundant off Iran. The status of population(s) outside the UAE are not well-understood, though declines have been reported from Kuwait and Iran. Estuarine degradation may also impact this species. 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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Fishing is causing declines in some areas of the Arabian Gulf and Sea of Oman, and may represent a major threat. It can also be impacted by estuarine degradation, a habitat that juveniles are dependent on, especially where freshwater flow has been altered (e.g., Kuwait; Al-Husaini 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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Plectorhinchus sordidus | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This speciesinhabits inshore and offshore rocky and coral reefs, as well as seagrass beds (McKay 1984, Gell and Whittington 2002). Its maximum total length is 30 cm (Psomadakis et al. 2015). This species has been observed on breakwaters and natural reefs in Dubai, with an apparent preference for natural reef (Burt et al. 2009, 2013). In Abu Dhabi, the maximum age is 14 years, and the mean age and size at sexual maturity was 1.8 years and 24.8 cm for males and 2.1 years and 26 cm for females (Grandcourt et al. 2011). When applying an age at first reproduction of 2 years and longevity of 14 years, its estimated generation length is 8 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.
Taxon
Taxa
Plectorhinchus sordidus | (Klunzinger, 1870)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Western Indian Ocean (Randall 1995, Carpenter et al. 1997a, Fricke et al. 2009, Psomadakis et al. 2015, Fricke et al. 2018). Its depth range is 2-25 m.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This demersal, reef-associated species occurs throughout UAE waters and can be common. Fishing activity is not known to be causing population declines at this time. There are no known major threats; therefore, it is listed as Least Concern in the UAE.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Fishing is not expected to be driving population 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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Plectorhinchus schotaf | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species is most commonly found in surf zones around rocky and coral reefs as well as in seagrass beds, and occasionally in rivers and estuaries (Roux 1986, Lieske and Myers 1994, Gell and Whittington 2002). Juveniles are found in tide pools (Smith and McKay 1986). This species is nocturnal and feeds on zooplankton and small fish (Dorenbosch et al. 2005). The maximum total length is 90 cm (McKay 2001).
Taxon
Taxa
Plectorhinchus schotaf | (Forsskål, 1775)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Two species, Plectorhinchus caeruleonothus and P. unicolor, have long been confused with P. schotaf (Johnson and Wilmer 2015).
Taxon distribution as listed in assessment
In the UAE, this species occurs on the Sea of Oman coast and possibly on the Arabian Gulf coast, but this requires further study. Globally, it is distributed in the Western Indian Ocean from South Africa (Transkei) north to the Red Sea, Arabian Gulf, Sea of Oman and Arabian Sea to Pakistan and India (Johnson and Wilmer 2015, Psomadakis et al. 2015). Its depth range is 1-80 m (Lieske and Myers 1994).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
In the UAE, this demersal, reef-associated species occurs on the Sea of Oman coast and possibly the Arabian Gulf coast. Fishing activity is not known to be causing population declines at this time. There are no known major threats; therefore, it is listed as Least Concern in the UAE.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Lutjanus ehrenbergii | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This reef-associated species inhabits very shallow coastal habitats, often forming large schools near freshwater run-offs (Kuiter and Tonozuka 2001). Adults inhabit coral reefs, while juveniles frequent inshore areas over sand, silt or coral rubble bottoms, occasionally in mangrove-lined streams and estuaries (Fischer et al. 1990). Its maximum total length is 35 cm (Allen 1985). Off Abu Dhabi, its mean age and size at sexual maturity is 1.7 years and 19.9 cm for males and 1.8 years and 20.4 cm for females and it has been aged up to 11 years (Grandcourt et al. 2011). When applying an age at first reproduction of 2 years and longevity of 11 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.
Taxon
Taxa
Lutjanus ehrenbergii | (Peters, 1869)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widely distributed in the Indo-West Pacific (Allen 1985). Its depth range is 1 to 20 m (Anderson and Allen 2001, R. Myers unpublished data).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This reef-associated species occurs throughout UAE waters. It is taken in fisheries throughout the Arabian Gulf, including the UAE. A 2011 stock assessment considered it to be sustainably exploited off Abu Dhabi, but the retention of juveniles was very high, which could lead to growth overfishing. The stock was assessed as fully exploited in 2018. Effort in the fishery that exploits this species has declined over time. The status of populations outside the UAE is not well-understood. Population declines are not known to be approaching a Near Threatened or threatened level in the UAE at this time; therefore, it is listed as Least Concern with a recommendation to continue fisheries monitoring.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Declines have not yet been documented in the Arabian Gulf, but exploitation is relatively high, and may represent a significant 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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
First assessment.
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Pinjalo pinjalo | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This schooling species inhabits coral and rocky reefs, including open ocean reefs. Its maximum total length is 80 cm, but is more common to 30 cm (Sommer et al. 1996, Psomadakis et al. 2015).
Taxon
Taxa
Pinjalo pinjalo | (Bleeker, 1850)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widely distributed in the Indo-West Pacific. Its depth range is 0-60 m (Allen 1985).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This reef-associated species occurs throughout UAE waters. Fishing activity is not known to be causing declines approaching a Near Threatened or threatened level in the UAE or surrounding areas at this time; therefore, it is listed as Least Concern in the UAE. As other exploited snapper species are in decline, there is concern that fishing effort towards this species will increase over time. As such, it is highly recommended to improve fisheries monitoring, and/or conduct a stock assessment.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Fishing activity is not known to be driving declines approaching a Near Threatened or threatened level 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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Pristipomoides multidens | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This deepwater, demersal species inhabits tropical and sub-tropical waters (Allen 1985). It schools in areas of hard, rocky and uneven sea floor near steep drop-offs (Parrish 1987). It consumes fishes, shrimps, crabs, lobsters, stomatopods, squids, gastropods and urochordates (Allen 1985). Its maximum total length is 90 cm (Anderson 1986). The maximum age is about 18.2 years, the age at maturity is 3.2 years, the reproductive lifespan is estimated at 15 years, and the natural mortality is 0.35 (Martinez-Andrade 2003). The maximum age from Australia is 30 years at 81 cm total length and age at 50% maturity is 8 years at 55 cm total length (Flood et al. 2014). When applying an age at first reproduction of 8 years and longevity of 30 years, its estimated generation length is 19 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.
Taxon
Taxa
Pristipomoides multidens | (Day, 1871)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters (Jawad et al. 2018). Globally, it is widely distributed in the Indo-Pacific (Allen 1985), but some exclude it from the Arabian Sea (R. Myers pers. comm. 2015). Its depth range is 40 to 245 m (Anderson and Allen 2001).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This relatively deep-living, reef-associated species occurs throughout UAE waters. Fishing activity is not known to be causing declines in the UAE. There are no known major threats; therefore, it is listed as Least Concern in the UAE.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
The protracted longevity, moderately slow growth and low natural mortality rates makes this species vulnerable to overfishing (Newman and Dunk 2002), but 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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Lutjanus fulviflamma | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species inhabits a variety of inshore habitats, including coral reefs. Juveniles are sometimes found in mangrove swamps and estuaries (Randall 2005). Adults typically school on coastal reefs and in deep lagoons (Kuiter and Tonozuka 2001). This species is often found in large aggregations with Lutjanus kasmira and L. lutjanus (Lieske and Myers 1994). It consumes fishes, shrimps, crabs and other crustaceans and its maximum total length is 35 cm (Allen 1985). The reproductive lifespan is estimated at 15.5 years (Martinez-Andrade 2003). Spawning in the southern Arabian Gulf occurs from April to June, maximum observed age was 14.3 years and the mean age and size at sexual maturity was 1.6 years and 16.7 cm for males and 1.9 years and 18.7 cm<sub> </sub>for females (Grandcourt et al. 2006). When applying an age at first reproduction of 2 years and longevity of 14.5 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.
Taxon
Taxa
Lutjanus fulviflamma | (Forsskål, 1775)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
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 0 to 35 m.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This reef-associated species occurs throughout UAE waters. According to a 2014 stock assessment, the stock of this species off Abu Dhabi was sustainably exploited. Catch declines are expected to reflect fishing effort declines. A stock assessment update expected in 2021 may better explain these declines. Fishing activity is not expected to be causing declines approaching a Near Threatened or threatened level in the UAE at this time; therefore, it is listed as Least Concern with a recommendation to continue fisheries monitoring.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Fishing activity is not known to be driving declines approaching a Near Threatened or threatened level 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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Lutjanus quinquelineatus | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This reef-associated species inhabits sheltered lagoons and exposed, outer slope coral reefs (Anderson and Allen 2001). It is frequently encountered in large aggregations of 100 or more individuals. Juveniles are solitary and inhabit shallow areas in protected bays with algae and rubble substrates (Kuiter and Tonozuka 2001). It feeds mainly on fishes and crustaceans (Allen 1984). It reaches a maximum total length of about 38 cm, but is more commonly seen to 20 cm (Anderson and Allen 2001). The maximum ageis 32 years off Australia (Anderson et al. 2003). The age at maturity is 2.9 years, the reproductive lifespan is estimated at 23.9 years and the natural mortality is 0.84 (Martinez-Andrade 2003).
Taxon
Taxa
Lutjanus quinquelineatus | (Bloch, 1790)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
This species has been referred to as Lutjanus spilurus (Allen 1985).
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widely distributed in the Indo-West Pacific (Allen 1985). Its depth range is 2 to 40 m (Anderson and Allen 2001).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This reef-associated species occurs throughout UAE waters. Fishing activity is not known to be causing declines in the UAE. There are no known major threats; therefore, it is listed as Least Concern in the UAE.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Fishing activity is not known to be driving population 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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Lutjanus coeruleolineatus | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
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.
Taxon
Taxa
Lutjanus coeruleolineatus | (Rüppell, 1838)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
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.
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).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off