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Assessment ID
330632
Taxon name
Siganus canaliculatus
(Park, 1797)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Siganus canaliculatus
(Park, 1797)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
siganidae
Genus
Siganus
Species
canaliculatus
Species authority
(Park, 1797)
Taxonomic notes and synonyms listed
There is some uncertainty about the taxonomic validity of Siganus fuscescens versus S. canaliculatus.
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2bd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This coastal species occurs throughout UAE waters. It is targeted by commercial fisheries in the UAE and elsewhere in the Arabian Gulf and Sea of Oman. Stock assessments conducted for Abu Dhabi in 2004, 2013 and 2018 considered this species overexploited. Catch in Abu Dhabi declined by 75% since at least 2006, or over the past 13 years. Its population status in areas neighboring the UAE is not known, but it is heavily exploited elsewhere as well. Based on catch data and stock assessments, it is inferred this species has undergone a decline of at least 70% over the past three generation lengths, or 15 years. It is listed as Endangered A2bd.
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 (Woodland 1984, 2001). Its depth range is about 0-50 m (Woodland 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 species schools in shallow, coastal waters to 40 m depth (Woodland 1984). It usually observed on rocky and sandy seaweed bottoms (Carpenter et al. 1997a), in and around the mouths of rivers in turbulent waters (Woodland 2001), and on hard-bottom structures (E. Abdulqader pers. comm. 2014). School size decreases with age, and juveniles often occur in very large schools in shallow bays and coral reef flats. This species feeds by scraping algae from rocks and corals, and to a lesser extent on seagrasses (Woodland 1984, 2001). The maximum total length is 30 cm (Randall 1995). Spawning appears to be synchronized with the lunar cycle and it is a multiple spawner (Hoque et al. 1999). Longevity is estimated as 7.8 years off UAE and mean size and age at first sexual maturity are 21.5 cm fork length and 1.9 years for males and 25.7 cm and 2.1 years for females (Grandcourt et al. 2007). When applying an age at first reproduction of 2 years and longevity of 8 years, its estimated generation length is 5 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Threats and conservation measures listed
Threats listed in assessment
Overfishing is a major threat to this species in the UAE (Grandcourt et al. 2014). A study conducted off Bahrain on this species found it to be susceptible to mass mortality events due to Streptococcus iniae bacterial infections (Yuasa et al. 1999). The pervasive level of coastal development within the UAE and Arabian Gulf region has degraded inshore habitats that this species utilizes. 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
330631
Taxon name
Plectorhinchus pictus
(Tortonese, 1936)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Plectorhinchus pictus
(Tortonese, 1936)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
haemulidae
Genus
Plectorhinchus
Species
pictus
Species authority
(Tortonese, 1936)
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, reef-associated species occurs throughout UAE waters. It is a relatively minor component of commercial fisheries in the Arabian Gulf; and is not directly targeted, but is taken in the shrimp trawl fishery and trap fishery. Catch in Abu Dhabi has been at relatively low levels since 2006, but did decline from 2 t in 2009 to zero since 2014. The status of population(s) outside the UAE are not well-understood, though declines have been reported from Bahrain, Kuwait and Iran. 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 occurs in the Indo-West Pacific from Yemen to the South China Sea (McKay 1984, 2001, Kemp 2000, Hassan Ali et al. 2016). Its depth range is 20-200 m (al Sakaff and Esseen 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 inhabits coastal rocky and coral reefs (Carpenter et al. 1997). Juveniles also inhabit mangrove areas (Shahraki and Fry 2016). Its maximum total length is 83 cm.
Threats and conservation measures listed
Threats listed in assessment
Overfishing is a potential major threat to this species in the Arabian Gulf. 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
330630
Taxon name
Diagramma pictum
(Thunberg, 1792)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Diagramma pictum
(Thunberg, 1792)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
haemulidae
Genus
Diagramma
Species
pictum
Species authority
(Thunberg, 1792)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2bcd+4bcd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species occurs throughout inshore waters of the UAE. It is targeted by commercial fisheries, and is considered overexploited in the UAE. Based on catch data and stock assessments, this species has undergone an inferred decline of at least 50% and possibly more over the past two generation lengths, or 14 years. 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. The population in UAE is inferred to have some level of connectivity with those in surrounding countries, and declines have been documented in Qatar and possibly Iran. It is listed as Endangered A2bcd+A4bcd.
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 (McKay 1984, Randall et al. 1997, McKay 2001, Seth and Sahoo 2014). Its depth range is 5-40 metres (Allen and Erdmann 2012).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This speciesinhabits shallow, coastal coral reefs and isolated coral heads of lagoons. It forms schools around isolated patch reefs. Juveniles generally occur in weedy areas (Smith and McKay 1986, Baillon and Kulbicki 1988, Wantiez and Kulbicki 1995). This species also occurs over mud, sand and silt bottoms in protected bays or estuaries, around outcrops, wreckage and debris (Kuiter and Tonozuka 2001, Allen and Erdmann 2012). It primarily consumes benthic invertebrates and fish (McKay 1984). The maximum fork length is 100 cm (Torres 1991). This species spawns between April to May and November in the southern Arabian Gulf (Grandcourt et al. 2006, 2011). Natural mortality was estimated at 0.13 year<sup>-1</sup> (Grandcourt et al. 2006). Estimated mean female fork length and age at first sexual maturity is 35.7 cm and 2.9 years for females and 26.7 cm and 0.5 years for males and longevity is about 11 years (Grandcourt et al. 2011). When applying an age at first reproduction of 3 years and longevity of 11 years, its estimated generation length is 7 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Threats and conservation measures listed
Threats listed in assessment
Overfishing is a major threat to this species in the UAE and off Qatar (Grandcourt et al. 2006). Coastal development in the UAE and Arabian Gulf region, which includes degradation of estuaries, may also impact 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
330629
Taxon name
Gerres longirostris
(Lacepède, 1801)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Gerres longirostris
(Lacepède, 1801)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
gerreidae
Genus
Gerres
Species
longirostris
Species authority
(Lacepède, 1801)
Taxonomic notes and synonyms listed
Gerres britannus, G. poieti, and G. acinaces, and four other species, are considered synonyms of G. longirostris (Iwatsuki et al. 2001).
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 in Abu Dhabi has declined by 87% since 2010, but a stock assessment conducted in 2015 concluded it was underexploited. Considering the catch declines cannot be explained at this time, and these information are conflicting, it is listed as Data Deficient in the UAE. Improvements in fisheries monitoring are needed.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific. Its depth range is 1 to 12 m (Allen and Erdmann 2012).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This species inhabits shallow waters over sandy bottoms, from coral reefs to seagrasses and brackish waters (Sommer et al. 1996). Adults are most often found in clear coastal waters, and juveniles are often observed in estuaries or lagoons influenced by freshwater (Iwatsuki et al. 2001). The species occurs singly or in groups and consumes small benthic invertebrates (Lieske and Myers 1994, Iwatsuki et al. 2001). Its maximum total length is 44.5 cm (Randall 1995, Allen and Erdmann 2012) and longevity is 9 years (Hashim and Salamah 1985). This species grows quickly. Off the UAE, the mean size and age at first sexual maturity is 16.3 cm and 1.1 years for males and 20.6 cm and 1.5 years for females (Grandcourt et al. 2006). In a study conducted in the Gulf off Saudi Arabia, size at first sexual maturity was 19.1 and 19.8 cm total length for females and males, and spawning occurred in late spring-early summer (Hosny and Al-Jaber 2017). When applying an age at first reproduction of 1.5 years and longevity of 9 years, its estimated generation length is 5.25 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 to this species in the UAE, but this is poorly understood. The large-scale anthropogenic modification of estuarine habitats in the UAE and elsewhere in the Gulf region may impact 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
330628
Taxon name
Uraspis uraspis
(Günther, 1860)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Uraspis uraspis
(Günther, 1860)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
carangidae
Genus
Uraspis
Species
uraspis
Species authority
(Günther, 1860)
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 speciesdoes not occur in the Arabian Gulf of the UAE and has not yet been confirmed from the eastern 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
This species is not confirmed to occur in the UAE, but may occur on the Sea of Oman coast. It is easily confused and misidentified as Uraspis helvola; due to this, it is not yet confirmed to occur in the Arabian Gulf (W. Smith-Vaniz pers. comm. 2013). Globally, it is widespread in the Indo-West Pacific (Masuda et al. 1984, Smith-Vaniz 1984, Paxton et al. 1989, Smith-Vaniz 1999). The depth range is 20 to 130 m (Mundy 2005).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This species forms small, demersal schools over the continental shelf (Paxton et al. 1989). The diet consists of epibenthic crustaceans and cephalopods (Myers 1999). The maximum fork length is 28 cm (Smith-Vaniz 1984).
Threats and conservation measures listed
Threats listed in assessment
Threats are unknown.
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
330627
Taxon name
Ulua mentalis
(Cuvier, 1833)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Ulua mentalis
(Cuvier, 1833)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
carangidae
Genus
Ulua
Species
mentalis
Species authority
(Cuvier, 1833)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore, pelagic speciesoccurs throughout UAE waters. Fishing activity is not expected to be causing population declines at this time. There are no known major threats; therefore, it is listed as Least Concern in the UAE.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Smith-Vaniz 1984, 1999, Motomura et al. 2007, R. Myers pers. comm. 2016). The depth range is 20 to 100 m (R. Myers unpublished data).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This speciesinhabits shallow, coastal waters near reefs and primarily feeds on crustaceans and fishes. The maximum total length is 100 cm (Smith-Vaniz 1984).
Threats and conservation measures listed
Threats listed in assessment
Fishing activity is not known to be driving declines in the UAE at this time. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
330626
Taxon name
Carangoides bajad
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carangoides bajad
(Forsskål, 1775)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
carangidae
Genus
Carangoides
Species
bajad
Species authority
(Forsskål, 1775)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Data deficient
Abbreviated status
DD
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore, pelagic speciesoccurs throughout UAE waters. It is common in UAE fish markets, and is heavily exploited by surrounding countries as well. A 2014 stock assessment for Abu Dhabi considered this species to be overfished. Abu Dhabi catch fluctuated with no clear trend between 2007-2018. An update to the stock assessment is expected in 2020, and until those results are available to compare to the 2014 assessment, its population status is poorly understood; therefore, it is listed as Data Deficient in the UAE. It is recommended to conduct life history studies to estimate generation length and improve fisheries monitoring.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Smith-Vaniz 1984, 1999). The depth range is 2 to 70 m (Allen and Erdmann 2012).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat
Habitat details as listed in assessment
This species schools in inshore coral and rocky reefs (Grandcourt et al. 2004). It feeds on nekton, crustaceans and finfish (Blaber et al. 1990, Masuda and Allen 1993). The estimated total length at first maturity for females is 24.7 cm and it spawns between May and September, with main spawning activity during June and September (Grandcourt et al. 2004). The maximum fork lengthis 55 cm (Smith-Vaniz 1984).
Threats and conservation measures listed
Threats listed in assessment
Overexploitation is a potential major threat in parts of its range. 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
330625
Taxon name
Sardinella sindensis
(Day, 1878)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Sardinella sindensis
(Day, 1878)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
clupeiformes
Family
clupeidae
Genus
Sardinella
Species
sindensis
Species authority
(Day, 1878)
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 speciesoccurs throughout UAE waters, but its population there is very poorly understood. It is presumably retained as bycatch in fisheries that also take Sardinella longiceps. It is heavily exploited in areas within close proximity of UAE waters, including Iran, and the status of those stocks is not known. Due to the lack of information regarding its population status, and potential major threat from exploitation, it is listed as Data Deficient in the UAE. Improvements in fisheries monitoring are needed.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is restricted to the western Indian Ocean from the Gulf of Aden to the Arabian Gulf to the Palk Strait between India and Sri Lanka (Lazarus 1980, Abdussamad et al. 2006). It occurs at latitudes between 30'°N and 10'°N and at longitudes between 42'°E and 74'°E. Its depth range is 0 to 50 metres (Whitehead 1985).
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-neritic species schools in coastal tropical waters to a depth of 50 m. It is also known to enter rivers in southern Iran (Coad 2017). Its maximum standard length is 17 cm, but is more common to 14 cm (Whitehead 1985). Off Qeshm Island, Iran, the maximum age is 3.5 years. Thisis a fast-growing species with a short life span (Dehghani et al. 2015).
Threats and conservation measures listed
Threats listed in assessment
This species may be negatively impacted in areas where it is heavily exploited (e.g., India, Pakistan and Iran).
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
330624
Taxon name
Sardinella gibbosa
(Bleeker, 1849)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Sardinella gibbosa
(Bleeker, 1849)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
clupeiformes
Family
clupeidae
Genus
Sardinella
Species
gibbosa
Species authority
(Bleeker, 1849)
Taxonomic notes and synonyms listed
Sardinella gibbosa is often confused with S. fimbriata in Indian waters (Whitehead 1985). There is at least one cryptic species present in the northern Philippines that has been called S. gibbosa (Thomas et al. 2014).
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore, pelagic speciesoccurs throughout UAE waters. Fishing activity is not expected to be causing population declines approaching a Near Threatened or threatened level at this time. Although, catch is apparently declining slightly on the eastern coast in recent years, and this requires further investigation. There are no known major threats; therefore, it is listed as Least Concern in the UAE.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Bleeker 1849, Russell and Houston 1989, Stern et al. 2015, Stern et al. 2016). Its depth range is 10 to 70 m (Pauly et al. 1996, FAO-FIGIS 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 pelagic, reef-associated species occurs in tropical waters between 10 to 70 m depth (Pauly et al. 1996, FAO-FIGIS 2005). It forms schools in coastal inshore waters, including estuaries and mangrove areas (Sousa and Dias 1981, Fischer et al. 1990, Shahraki et al. 2016). Its diet mainly consists of crustaceans and phytoplankton (Lazarus 1977). Its maximum standard length is 17 cm (Whitehead 1985) and the maximum reported age is 7 years (Sanders and Morgan 1989). The average size at first maturity has been reported as 13.7 cm (Bennet et al. 1992).
Threats and conservation measures listed
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. Declines due to overexploitation have been reported elsewhere, including Iran (Pauly and Zeller 2015). Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Publication
Ralph, G.M., Stump, E., Linardich, C., Bullock, R.W., Carpenter, K.E., Allen D.J., Hilton-Taylor, C., Al Mheiri, R., and Alshamsi, O. 2021. UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes. 2021. Ministry of Climate Change and Environment, Dubai, United Arab Emirates.
Assessment ID
330623
Taxon name
Nematalosa persara
Nelson & McCarthy, 1995
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Nematalosa persara
Nelson & McCarthy, 1995
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
clupeiformes
Family
clupeidae
Genus
Nematalosa
Species
persara
Species authority
Nelson & McCarthy, 1995
Taxonomic notes and synonyms listed
It is difficult to distinguish this species from Nematalosa nasus (Nelson and McCarthy 1995).
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore, pelagic species occurs throughout UAE waters. It has not been commonly recorded, and is easily misidentified as Nematalosa nasus. There are no known major threats; therefore, it is listed as Least Concern in the UAE.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is restricted to the northwestern Indian Ocean where it occurs from the Arabian Gulf to Pakistan. The distribution is based on specimens previously identified as Nematalosa nasus (Nelson and McCarthy 1995). Its depth range is about 0 to 8 m (FishNet2 database accessed June 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 coastal, pelagic species occurs in tropical marine waters. Its maximum standard length is 15.2 cm (Nelson and McCarthy 1995).
Threats and conservation measures listed
Threats listed in assessment
Fishing activity is not expected to driving declines in the UAE at this time.
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.