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

Scomber australasicus | 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 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.
Taxon
Taxa
Scomber australasicus | Cuvier, 1832
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
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.
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.
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 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.
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
Threats are poorly understood.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Rastrelliger kanagurta | 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 common, coastal pelagic species forms large schools in bays, harbors and deep lagoons, usually in some turbid plankton-rich waters. It feeds on phytoplankton (diatoms) and small zooplankton (cladocerans, ostracods, larval polychaetes, etc.). There are many reports on life history and other information for this species compared to other Rastrelliger species (Noble and Geetha 1992). Size at first maturity is approximately 17-“20 cm (Tampubolon and Merta 1987, Sivadas et al. 2006), and longevity is estimated to be approximately four years (Mehanna 2001). This is a fast-growing species, and age at first maturity is expected to occur during the first year (Jayabalan et al. 2016). When applying an age at first reproduction of 1 years and longevity of 4 years, its estimated generation length is 2.5 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
Rastrelliger kanagurta | (Cuvier, 1816)
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, itis widely distributed in the Indo-West Pacific (Collette 1970).
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 pelagic, coastal species occurs throughout UAE waters. It is taken in UAE fisheries, and catch has been increasing with effort over the past decade in Abu Dhabi. Fishing activity is not known to be causing declines in the UAE or surrounding areas 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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Scomberomorus commerson | 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 pelagic and oceanodromous species occurs from near the edge of the continental shelf to shallow coastal waters, often of low salinity and high turbidity. Juveniles inhabit estuaries and nearshore habitats. It is also found in drop-offs, and shallow or gently sloping reef and lagoon waters, and is more frequently caught in waters shallower than 100 m depth (Collette 2001). It undertakes lengthy long-shore migrations, but permanent resident populations also seem to exist. It occurs in small schools and primarily consumes small fishes like anchovies, clupeids and carangids, but also squid and penaeid shrimps. It spawns off reef slopes and edges, and forms spawning aggregations in specific areas. Depending on temperature regime, the spawning season may be more or less extended. Off Iran, spawning occurs mostly from June to September (Darvishi et al. 2011) and in May and June off Oman (Claereboudt et al. 2005). It possibly migrates from Omani waters to the Iranian coast in the Gulf during spawning season (Claereboudt et al. 2005, Darvishi et al. 2011). It has an age at first maturity of about 2 years (Devaraj 1981, Mackie et al. 2003, Claereboudt et al. 2005, Grandcourt et al. 2005). In north Queensland, Australia the oldest male was 10 years at 127 cm and the oldest female was 14 years and 155 cm. This species may live up to 15 years (IOTC 2006), 16 years (Grandcourt et al. 2005), and maybe as long as 22 years (Mackie et al. 2003). 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.
Taxon
Taxa
Scomberomorus commerson | (Lacepède, 1800)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
A revision of Scomberomorus was conducted by Collette and Russo (1985).
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, itis widely distributed in the Indo-West Pacific (Ben Souissi et al. 2006).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
A2bd
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 coastal, pelagic species occurs throughout UAE waters. It is heavily exploited by all levels of fisheries throughout the Arabian Gulf and Sea of Oman, and is considered overexploited according to stock assessments conducted in several countries of this region, including off Abu Dhabi where it is considered collapsed. Several management measures have been implemented in UAE waters, but fisheries management remains inadequate in other countries. Given the migratory nature of the species, it is considered a single stock across the Arabian Gulf, and possibly connected to the Sea of Oman as well. Effort is not quantified, but has either remained constant or increased across the region over time. Catch in the GCC countries, which represents a single stock, declined by about 68% since 1988. According to catch data, stock assessments and fish market observations, it is inferred this species declined by at least 50-70% over the past three generation lengths (27 years), or since about 1988. It is listed as Endangered A2bd.
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
Overfishing is a major threat to this species in the UAE and throughout the Arabian Gulf and Sea of Oman region (Grandcourt et al. 2005, Grandcourt et al. 2014). In addition, warming waters in the Gulf due to climate change are expected to impact this species in that region (Wabnitz et al. 2018). 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

Sarda orientalis | 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 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.
Taxon
Taxa
Sarda orientalis | (Temminck & Schlegel, 1844)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
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.
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 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.
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 a potential threat, but this is poorly understood.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Scomberomorus guttatus | 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 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.
Taxon
Taxa
Scomberomorus guttatus | (Bloch & Schneider, 1801)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
A revision of Scomberomorus was conducted by Collette and Russo (1985).
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, itis widely distributed in the Indo-West Pacific.
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 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.
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
Overfishing is a potential major threat in the UAE.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Katsuwonus pelamis | 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 pelagic and oceanodromous species is found in offshore waters to depths of 260 m. It exhibits a strong tendency to school in surface waters with birds, drifting objects, sharks, and whales. It feeds on fish, crustaceans, cephalopods, and molluscs and is preyed upon by large pelagic fishes (Kailola et al. 1993). In the western Atlantic, it is commonly found in mixed schools with Blackfin Tuna, Thunnus atlanticus.This species is very fast-growing, short-lived, and very fecund. Its maximum fork length is 111 cm (Bayliff 1988) and longevity is estimated to be between 6-“8 years (Garcia-Coll et al. 1985, Collette 2010). The age of first maturity is estimated to be 1.5 years (Maunder and Harley 2005) with a fork length at first maturity of 40-“55 cm, depending on the area (Collette and Nauen 1983, Matsumoto et al. 1984, Cayre and Farrugio 1986, Wild and Hampton 1994, Stequert and Ramcharrun 1996, Schaefer 2001). This species spawns several times per season in batches (Erdman 1977, Collette 2010). When applying an age at first reproduction of 1.5 years and longevity of 7 years, its estimated generation length is 4.25 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
Katsuwonus pelamis | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Some authors have included Skipjack Tuna in the genus Euthynnus, but recent authors agree with its placement in the monotypic genus Katsuwonus (Collette and Graves 2019).
Taxon distribution as listed in assessment
In the UAE, this species only occurs in the Sea of Oman. It does not occur in the Arabian Gulf. Globally, it is circumglobal in seas warmer than 15'°C.
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 species occurs in UAE waters in the Sea of Oman only, and its presence in fish markets has declined in recent years, but quantified data are limited. It is targeted by tuna fisheries in the Sea of Oman off Pakistan, Iran and Oman. The population in UAE waters is connected with the Indian Ocean stock, and its status should reflect that fisheries' reports. According to a stock assessment by the IOTC in 2017, it is considered to be not overfished, and historically not overfished. Fishing activity is not known to be driving population declines approaching a Near Threatened or threatened level at this time; therefore, it is listed as Least Concern.
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 expected to be causing population declines at this time.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Acanthopagrus berda | 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 is an estuarine-dependent species found mainly on sandy and muddy grounds in shallow coastal waters to 50 m depth (Fischer and Bianchi 1984, Garratt 1993). Juveniles inhabit protected bays and estuaries (Carpenter 2001). This species enters freshwaters in Zimbabwe, South Africa and Madagascar. It feeds on worms, molluscs, crustaceans, echinoderms and small fish (Fischer et al. 1990). The maximum length is 90 cm (Smith and Smith 1986). This species is a protandrous hermaphrodite (Allsop and West 2003).
Taxon
Taxa
Acanthopagrus berda | (Forsskål, 1775)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
This species was previously confused with Acanthopagrus vagus in South Africa (Heemstra and Heemstra 2004, Iwatsuki and Heemstra 2010).
Taxon distribution as listed in assessment
In UAE waters, this species only occurs in the Sea of Oman. It is not likely to occur in the Arabian Gulf, and reports from there are probably misidentifications of Acanthopagrus randalli (Y. Iwatsuki pers. comm. 2013). Globally, it is restricted to the Indian Ocean where it occurs from South Africa, Madagascar to the Red Sea, India, Phuket and Malaysia (Iwatsuki and Heemstra 2010). This species occurs to 50 m depth.
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 the UAE, this coastal and estuarine species occurs only in the Sea of Oman. It is apparently naturally rare in UAE waters. The impact from the ongoing degradation of estuaries in the region may require further investigation. 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
Fishing activity is not known to be driving population declines at this time, but habitat degradation, especially of estuaries, may be impacting this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Acanthopagrus bifasciatus | 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 associated with reefs in shallow coastal waters and also occurs in estuaries and bays (Sommer et al. 1996, Y. Iwatsuki pers. comm. 2009). Prey items consist mainly of molluscs and other benthic invertebrates (Masuda and Allen 1993). It occurs in small schools (Lieske and Myers 1994) and can attain 50 cm total length (Sommer et al. 1996). It is suspected to be protogynous and spawning in the southern Arabian Gulf occurs from January to April. Spawning aggregations have been observed off Oman (Y. Iwatsuki pers. comm. 2009). Sexual maturity is attained at 26.4 cm fork length or 4.6 years for females and 21.9 cm or 2.4 years for males (Grandcourt et al. 2004). It has been recorded to a maximum age of 19-21 years (Samuel and Mathews 1987, Grandcourt et al. 2004). When applying an age at first reproduction of 4.5 years and longevity of 20 years, its estimated generation length is 12.25 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
Acanthopagrus bifasciatus | (Forsskål, 1775)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Two colour morphs of this species have been observed, and further taxonomic study is needed (Y. Iwatsuki pers. comm. 2009). A northern and southern population were originally both described as Acanthopagrus bifasciatus in the Indian Ocean. Iwatsuki and Heemstra (2011) determined that both populations were two valid species, the northern population (Red Sea to the Arabian Gulf) is described as A. bifasciatus, while the southern population (southern Oman to South Africa) is described as A. catenula (Lacepède 1801).
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 the Gulf of Aden to Pakistan, including the Red Sea and Arabian Gulf (Iwatsuki and Heemstra 2011). This species occurs to 30 m depth (Sommer et al. 1996).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
A2bcd+4bcd
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 coastal and estuarine species occurs throughout UAE waters. It is heavily exploited in the commercial trap fisheries of the UAE and Arabian Gulf region. Despite stock assessment results indicating it is underexploited in Abu Dhabi as of 2004 and 2014, catch has declined by 91% over the past 16 years, or a little more than one generation length. Based on these data, and fish market observations, it is inferred that the species has undergone declines of at least 50% and possibly more over the past generation length. Its population status in areas neighboring the UAE is not known, but it is heavily exploited elsewhere as well. 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; however, effort in this fishery in surrounding Emirates where management measures are not stringent may increase or remain the same. 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 are expected to continue. In addition, degradation of coastal habitats, especially for coral reefs is ongoing in the UAE and Arabian Gulf region. It is listed as Endangered A2bcd+A4bcd.
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
Overfishing is a major threat to this species. Coastal development in the UAE and Arabian Gulf region, which includes destruction and degradation of coral reefs and estuaries, may also impact this species given its habitat preferences.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Argyrops spinifer | 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 wide range of bottoms to 150 m depth, usually 5-100 m (Smith and Smith 1986, Sommer et al. 1996). Young fish occur in very shallow waters of sheltered bays (Sommer et al. 1996) and larger individuals occur in deeper water. It occurs in estuaries along the Iranian Sea of Oman coast (Kamrani et al. 2016). It feeds on benthic invertebrates, mainly mollusks (Fischer et al. 1990, Salini et al. 1994). The spawning season in the Arabian Sea occurs from September to January, with a peak around October-November. In the southern Arabian Gulf, spawning occurs from January to April (Grandcourt et al. 2004). In Qatari waters, spawning occurs from November to March, with a peak in December (Abdallah et al. 2012). There is some evidence of large aggregations forming during autumn in the Gulf of Aden (Mann and Fennessy 2000). Its maximum total length is 75 cm (S. Alam pers. comm. 2013). The fork length at first maturity in Oman is 28.6 and 26.4 cm for females and males, respectively (McIlwain et al. 2006). Age and length at first maturity off Abu Dhabi is estimated as 26.9 cm and 2.4 years for males and 26.7 cm and 2.4 years for females (Grandcourt et al. 2004). In the Arabian Sea off Oman, longevity was estimated as 25 years and size and age at maturity as 36.5 cm and 5 years for males and 37.2 cm and 5.6 years for females (Al Mamry et al. 2009). In Iran, the maximum recorded ages for females and males was 21 and 25 years, respectively (Ghanbarzadeh et al. 2017). When applying an age at first reproduction of 3 years and longevity of 25 years, its estimated generation length is 14 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
Argyrops spinifer | (Forsskål, 1775)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Argyrops spinifer may represent three unique species in the Arabian Gulf (Y. Iwatsuki pers. comm. 2013). Iwatsuki and Heemstra (2018) recently described A. flavops from Mutrah, Oman and Karachi, Pakistan and A. caeruleops from the Gulf of Oman, southern Oman, Socotra and Pakistan. Further study of additional specimens is required to determine the extent of their distributions in the western Indian Ocean/Arabian Seas region.
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Bauchot and Smith 1984).
Assessed status
Asessment status in full
Critically Endangered
Assessment status abreviation
CR
Assessment status criteria
A2bd+4bd
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 coastal species occurs throughout UAE waters. It is targeted by commercial fisheries in the UAE and surrounding countries of the Arabian Gulf and Sea of Oman and is considered overexploited in Abu Dhabi. Based on catch data, stock assessments and fish market observations, this species is inferred to have declined by at least 80% over the past generation length, or 14 years. Its population status in areas neighboring the UAE is not known, but it is heavily exploited elsewhere as well. 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; however, effort in this fishery in surrounding Emirates where management measures are not stringent may increase or remain the same. 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 are expected to continue. It is listed as Critically Endangered A2bd+A4bd. As this species may be confused with two other recently described species from the region (Argyrops flavops and A. caeruleops), further taxonomic work is recommended.
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
Overfishing is a major threat to this species in the UAE (Grandcourt et al. 2014). Coastal development has been pervasive in the UAE and Arabian Gulf region, and this may impact the inshore habitats this species utilizes.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Pagellus affinis | 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 bottom types, but prefers hard bottoms to at least 100 m depth (Carpenter et al. 1997b). It consumes small invertebrates (Sivasubramaniam and Ebrahim 1982). It commonly occurs to 15-25 cm length, with a maximum total length of 37 cm (Sivasubramaniam and Ebrahim 1982, Sommer et al. 1996).
Taxon
Taxa
Pagellus affinis | Boulenger, 1888
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs in the Sea of Oman waters of the UAE, but does not occur on the Arabian Gulf coast. Globally, it is restricted to the northwestern Indian Ocean from the Gulf of Aden, Arabian Gulf to Pakistan (Y. Iwatsuki pers. comm. 2013).
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 coastal species occurs only on the Sea of Oman coast. It is taken in small quantities by fishers there and likely elsewhere in waters neighboring the UAE. Fishing activity is not known to be driving population declines at this time; therefore, it is listed as Least Concern.
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off