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EN

Assessment ID
330470
Taxon name
Anas acuta
Linnaeus, 1758
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Anas acuta
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
anseriformes
Family
anatidae
Genus
Anas
Species
acuta
Species authority
Linnaeus, 1758
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)
D
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species has a restricted non-breeding population in the UAE, which qualifies it for listing as Endangered. The population;within the country;is uncertain, however, recent data suggest that there may be a decline. In addition, there is a decline at the global level (although still considered;Least Concern).;The species is precautionarily retained as Endangered at the national level.
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 commonly occurs throughout the UAE during winter or on passage to and from its sub-Arctic breeding grounds (Pedersen et al. 2017). Occasionally individuals remain in the country over summer (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
This species occurs along sheltered coasts, at estuaries and tidal lagoons, as well as at fresh and brackish shallow ponds further inland and at water treatment plants (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere, this species is omnivorous and opportunistic, its diet consisting of algae, seeds, tubers, and the vegetative parts of aquatic plants, sedges and grasses, as well as aquatic invertebrates, amphibians and small fish (Johnsgard 1978, Brown et al. 1982, del Hoyo et al. 1992, Hockey et al. 2005). The species is migratory. Individuals wintering in the UAE breed in solitary pairs or loose groups between April and June in sub-Arctic regions (Madge and Burn 1988, Richardson 1990, del Hoyo et al. 1992). The species is highly gregarious in winter and on passage, often forming enormous concentrations (Madge and Burn 1988, Scott and Rose 1996). It feeds nocturnally; flocks roost by day on open water (Brown et al. 1982, Hockey et al. 2005). The species is shy and rarely remains at the same site over the winter (Richardson 1990).
Threats and conservation measures listed
Threats listed in assessment
The most relevant threats within UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown. Wetland habitat loss, petroleum pollution and reclamation of coastal areas for industrial development also pose a threat to this species in other parts of its range (Scott and Rose 1996, BirdLife International 2015).Additionally, individuals of this species that visit UAE are threatened by a range of other threats that operate outside of the country. For instance, the species is threatened by wetland drainage, peat-extraction, changing wetland management practices (decreased grazing and mowing in meadows leading to scrub over-growth) and the burning and mowing of reeds in Russia (Grishanov 2006). Over-exploitation is a concern in large parts of its global range (Baldassarre and Bolen 1994, Kear 2005, Balmaki and Barati 2006, Schmidt 2006).;Pintails are predated by feral cats Felis catus and rats Rattus norvegicus on islands (del Hoyo et al. 1992), and the species is susceptible to avian botulism (Rocke 2006) and avian influenza (Melville and Shortridge 2006, Gaidet et al. 2007) so may be threatened by future outbreaks of these diseases.
History
In 1996, the species was recorded in reasonable numbers at some localities, with a lower recording effort. It is likely to also qualify as Endangered, reduced by one category to Vulnerable (D1) based on potential rescue from the global population, which assumed to have been in better status at that time.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates
Assessment ID
330466
Taxon name
Alectoris chukar
(Gray, 1830)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Alectoris chukar
(Gray, 1830)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
galliformes
Family
phasianidae
Genus
Alectoris
Species
chukar
Species authority
(Gray, 1830)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Due to a presence of a large number of released birds both the population size and trend are uncertain, although it is suspected that the naturally wild population of this species in UAE is fewer than 250 mature individuals. It is therefore listed here as Endangered under criterion D.
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 native to the northern Hajar Mountains (Fujairah and Ras al-Khaimah emirates) north of Dibba and Masafi, where it is an uncommon resident (Pedersen et al. 2017). It was first recorded in the UAE in Fujairah in April 1987 (Pedersen et al. 2017). Birds outside of the Hajar Mountains are of feral origin and likely not self-sustaining: In 2012, 500 birds were released near Al Ain on Jebel Hafeet (Abu Dhabi Emirate); further releases took place on Jebel Buhays and Qarn Nizwa (Sharjah Emirate) as well as on several islands in the Arabian Gulf (Das, Sir Bani Yas, Marawa, Abu al-Abyad) (Jennings 2010, Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
Habitat details as listed in assessment
This species occurs on arid and semi-arid rocky slopes and hillsides with low vegetation cover and occasional stunted trees and bushes (Watson 1962, Papaevangelou 1980, Jennings 2010, Aspinall and Porter 2011). It is found mainly between 500 and 1,500 m, but ranges down to 200 m during foraging trips, when it also occurs on agricultural land (Pantelis 1980, Papaevangelou 1980, Serez 1992, Khan et al. 2009, Aspinall and Porter 2011). There is little known about the diet of the species in the UAE, but individuals in Musandam (Oman) have been observed feeding on berries (Jennings 2010). Elsewhere in the Middle East, the species also takes seeds of grasses and weeds, leaves and insects (Jennings 2010). Availability of water influences population density, even though birds will move up to 10 km to access water (Watson 1962), and likely limits a range expansion in eastern Arabia (Jennings 2010). There is no information available on the breeding behaviour of the species in the UAE. In Musandam (Oman), nests were made of twigs and placed in shallow depressions on gravelly ground, hidden under bushes at the edge of cultivated or grassy fields (Jennings 2010). These nests contained eggs in February and March, while juveniles were recorded in June (Jennings 2010). It is unclear if there is competition for feeding sources and nesting sites with Sand Partridge Ammoperdix heyi (Jennings 2010).
Threats and conservation measures listed
Threats listed in assessment
Released birds pose a threat to this species through genetic contamination from non-native populations;(Panayides et al. 2011).
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates
Assessment ID
330977
Taxon name
Aetobatus flagellum
(Bloch & Schneider, 1801)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Aetobatus flagellum
(Bloch & Schneider, 1801)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
aetobatidae
Genus
Aetobatus
Species
flagellum
Species authority
(Bloch & Schneider, 1801)
Taxonomic notes and synonyms listed
This species was previously considered to be conspecific with Aetobatus narutobiei, but the species have since been shown to differ genetically and morphologically (White and Moore 2013).
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2d
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This inshore eagle ray occurs throughout UAE waters, but little is known on its population there. It may be taken as bycatch in inshore gillnet fisheries. Most of the distribution of the species in the Arabian Sea region is under extremely intense and increasing demersal fishing pressure, especially off India. Furthermore, the loss and modification of coastal habitats in the Arabian Gulf is a significant concern, especially since this species is known to rely on estuaries during part of its life history. Its relative rarity, large size, and low productivity makes this species particularly susceptible to population decline. 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 throughout the Arabian Seas, and ongoing threats from bycatch and habitat loss, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation, it is suspected to have declined by at least 50% over the past three generation lengths, or about 45 years. It is listed as Endangered A2d.
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
The Longhead Eagle Ray occurs throughout UAE waters. Globally, it is patchily distributed in the Indo-West Pacific from the Arabian Sea region to Indonesia and Malaysia (Last et al. 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
The Longhead Eagle Ray occurs primarily inshore on the inner continental shelf, and is associated with estuarine habitats (Last et al. 2016), especially where it occurs in the Arabian Gulf (Bishop et al. 2016). It attains a maximum size of 90 cm disc width (DW) with males mature at 50 cm DW and females at 75 cm DW (White and Moore 2013). Size at birth is unknown but the smallest free-swimming individual examined was 23 cm DW. Little else is known of the biology of this species. However, it is suspected to exhibit low fecundity as with other myliobatids which bear litters of up to four offspring (Compagno and Last 1999). As there is no information on this species' maximum age and age at maturity, generation length was inferred as ~15 years based on data for the Bat Ray (Myliobatis californicus) which are reported to have a maximum age of 24 years and an age at maturity of five years (Martin and Cailliet 1988). However, it is noted that the Longhead Eagle Ray reaches a smaller maximum size than this species.
Threats and conservation measures listed
Threats listed in assessment
Information pertaining to threats to this species in UAE waters are unavailable. Generally, the Longhead Eagle Ray is highly susceptible to a variety of inshore demersal fisheries, including trawls and gill nets. In the Arabian Sea region, it occurs in areas of intense demersal trawl activity. Marine habitats in the Arabian 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), which is likely to impact this species.
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
330684
Taxon name
Aetomylaeus milvus
(Valenciennes, 1841)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Aetomylaeus milvus
(Valenciennes, 1841)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
myliobatidae
Genus
Aetomylaeus
Species
milvus
Species authority
(Valenciennes, 1841)
Taxonomic notes and synonyms listed
Aetomylaeus milvus is considered to be distinct from A. maculatus (Last et al. 2016).
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)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Ocellate Eagle Ray occurs throughout UAE inshore waters. Little is known on the population of this species in UAE waters. It is taken as bycatch in trawl and gill net fisheries, and fishing effort is intense and increasing in much of the Arabian Sea region. The loss and degradation of coastal habitats in the Gulf is a significant concern for inshore species such as this. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. 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. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 50% over the past three generation lengths, or about 45 years. It is listed as Endangered A2cd.
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
The Ocellate Eagle Ray occurs throughout UAE waters. It is restricted to the Arabian Sea region from Oman to India (Gujarat), including the Arabian Gulf (Last et al. 2016). Until recently, this species was confused with the Mottled Eagle Ray (A. maculatus) and possibly the Ornate Eagle Ray (A. vespertilio). Further research is needed to confirm its full distribution.
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
The biology of the Ocellate Eagle Ray is poorly known, but it likely inhabits inshore areas over soft bottoms to depths of 90 m (Last et al. 2016, Weigmann 2016). This eagle ray displays aggregating behaviour. It reaches a maximum size of 123 cm disc width (DW), and males mature at 50 cm DW (R.W. Jabado pers. comm. 09/02/2017). Female maturity and size at birth are unknown. The species is suspected to have low fecundity similar to other eagle rays, which bear litters of up to four offspring (Compagno and Last 1999, Last and Stevens 2009). As there is no information on this species' maximum age and age at maturity, generation length was inferred as ~15 years based on data for the Bat Ray (Myliobatis californicus) which are reported to have a maximum age of 24 years and an age at maturity of five years (Martin and Cailliet 1988). However, it is noted that the Ocellate Eagle Ray reaches a smaller maximum size than this species.
Threats and conservation measures listed
Threats listed in assessment
This species is impacted by fisheries in the UAE and forms a relatively large portion of all landed batoids. It is impacted by bycatch fisheries that are active elsewhere in its range as well. 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).
History
This is the first assessment for this species.
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
330655
Taxon name
Carcharhinus dussumieri
(Müller & Henle, 1839)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carcharhinus dussumieri
(Müller & Henle, 1839)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Carcharhinus
Species
dussumieri
Species authority
(Müller & Henle, 1839)
Taxonomic notes and synonyms listed
Carcharhinus dussumieri is part of the Carcharhinus seali-dussumieri group that has been revealed to consist of five species: C. dussumieri and C. sealei have recently been re-described, C. coatesi and C. tjutjot have been resurrected as valid species, and a new species, C. humani has been described (White 2012, White and Weigmann 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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Whitecheek Shark is common throughout UAE inshore waters. Little specific data are available for this species in the UAE. It has a relatively low reproductive capacity, which causes it to be susceptible to over-exploitation, but it remains common in the Arabian Gulf. It is apparently highly migratory, and has slow life history characteristics including low fecundity and a low annual rate of population increase. Considering this, the species has a low capacity to recover from even moderate levels of exploitation. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net, longline and trawl fisheries that operate within its range outside and surrounding UAE waters. Some management measures are now in place in the Arabian Sea region, although domestic fisheries are likely to continue. 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. It is inferred that declines reported in the Arabian Sea region are representative of its status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 50-70% over the past three generation lengths, or about 24 years. It is listed as Endangered A2cd.
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
The Whitecheek Shark occurs throughout UAE waters. Globally, it occurs from the northern Arabian Sea in the Arabian Gulf to the southeast coast of India. Bonfil (2003) reported this species from the lower Red Sea and Gulf of Aden, but these records may have been of Human's Whaler Shark (Carcharhinus humani), which was only recently described from this area (White and Weigmann 2014).
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
The Whitecheek Shark is a small species of carcharhinid shark that is common in inshore waters over soft substrates at depths of 0-100 m (Weigmann 2016). It reaches a maximum size of 114 cm total length (TL) (Raeisi et al. 2017). Size at birth is around 28-40 cm TL. This species is placental viviparous and produces litters of 2-5 each year. A study conducted off Iran in the Arabian Gulf reported a longevity of 8 and 13 years for males and females, and both females and males matured at lengths between 60 to 68 cm (Raeisi et al. 2017). Age at maturity data are not available for this species, but the Atlantic Sharpnose Shark (Rhizoprionodon terraenovae), which reaches a similar maximum size of 96 cm TL (Carlson and Baremore 2003), is applied as a proxy for age at maturity (3-4 years for females and 2-3.5 years for males). When applying an age at first reproduction of 3 years and longevity of 13 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.
Threats and conservation measures listed
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. Marine habitats in the Arabian 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).
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
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
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
330207
Taxon name
Lethrinus nebulosus
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Lethrinus nebulosus
(Forsskål, 1775)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
lethrinidae
Genus
Lethrinus
Species
nebulosus
Species authority
(Forsskål, 1775)
Taxonomic notes and synonyms listed
Lethrinus nebulosus may represent a complex of species, and further taxonomic work is required (K. Carpenter pers. comm. 2015). A cryptic species under L. nebulosus was detected in a study off southeastern Africa, but further study is required to resolve the taxonomy and distribution (Healey et al. 2018).
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 inshore, reef-associated species occurs throughout UAE waters. It is heavily exploited in the UAE, and stock assessments conducted for Abu Dhabi in 2006, 2010 and 2018 reported it as overfished. Based on catch data and stock assessments, this species has undergone an inferred declined of at least 52-78% 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. 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 in the UAE and Arabian Gulf region, especially for coral reefs, is expected to continue. The population in UAE is inferred to have some level of connectivity with those in surrounding countries, and declines have been reported from Saudi Arabia, Qatar and Kuwait. It is listed as Endangered A2bcd+A4bcd. In addition to improvements needed in fisheries management, taxonomic research is also recommended.
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. As is currently understood on the global-level, it is widespread in the Indo-West Pacific (Carpenter and Allen 1989). Its depth range is 0 to 90 m (R. Myers pers. comm. 2015).
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 nearshore and offshore coral reefs, coralline lagoons, seagrass beds, mangrove swamps, coastal sand and rock areas to depths of 75 m (Carpenter and Allen 1989). It is occasionally observed in small aggregations (Randall 1995), but adults typically occur singly. It primarily consumes molluscs, crustaceans, echinoderms and less often polychaetes and fishes (Carpenter and Allen 1989). The maximum total length is 87 cm (Assadi and Dehghani 1997). This species undergoes a protogynous sex change that occurs over a wide range of year groups starting with age 1, well before maturity (McPherson et al. 1985). Longevity is estimated to be 14-26 years (Mathews and Samuel 1991, Edwards and Shaher 1991, Dalzell et al. 1996, Grandcourt 2006, Ebisawa and Ozawa 2009). Off the Ryukyu Islands of Japan, the age of 50% ovarian maturity was 4 years (Ebisawa and Ozawa 2009). This species forms spawning aggregations (Salem 1999). In the southern Arabian Gulf, spawning occurs between April to May, the mean size and age at first sexual maturity for males and females to be 19.4 cm and 0.5 years for males and 28.9 cm and 2.7 years for females, and maximum age was 11 years (Grandcourt et al. 2006 and 2010). 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 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
330097
Taxon name
Scomberomorus commerson
(Lacepède, 1800)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Scomberomorus commerson
(Lacepède, 1800)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
scombridae
Genus
Scomberomorus
Species
commerson
Species authority
(Lacepède, 1800)
Taxonomic notes and synonyms listed
A revision of Scomberomorus was conducted by Collette and Russo (1985).
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
A2bd
Criteria system used
IUCN

(see Assessment details)

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.
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 (Ben Souissi et al. 2006).
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 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.
Threats and conservation measures listed
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).
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
330092
Taxon name
Acanthopagrus bifasciatus
(Forsskål, 1775)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Acanthopagrus bifasciatus
(Forsskål, 1775)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
sparidae
Genus
Acanthopagrus
Species
bifasciatus
Species authority
(Forsskål, 1775)
Taxonomic notes and synonyms listed
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).
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 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.
Assessment details
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Further information
Endemism (according to assessment)
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is restricted to the Western Indian Ocean where it occurs from 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).
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 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.
Threats and conservation measures listed
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.
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.