NT
Assessment ID
330685
Taxon name
Brevitrygon walga
Uploaded by
National Red List Database
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
330657
Taxon name
Pastinachus sephen
Uploaded by
National Red List Database
Scientific name
Pastinachus sephen
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
dasyatidae
Genus
Pastinachus
Species
sephen
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
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Cowtail Ray occurs throughout UAE coastal waters. The exact distribution is uncertain due to confusion amongst Pastinachus species and recent taxonomic changes. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980 and recent surveys have detected it in the area. Cowtail rays are regularly discarded in the Arabian Gulf and Sea of Oman. A large part of the species' regional distribution (namely, India and Pakistan) is under extremely intense and increasing demersal fishing pressure. It is not known how individuals occupying the UAE are connected with the broader population of the Arabian Seas region, and there is no information available to suggest that its population status differs in the UAE as compared to other parts of its range in the region. Given the threats faced by this species in other parts of the Arabian Seas region, and ongoing threats from discarding and habitat loss in the UAE, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 60 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
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.
Endemic to region
No
Endemism Notes
Endemism Notes
Possibly endemic to Arabian Sea region
Taxon distribution as listed in assessment
The Cowtail Ray occurs throughout UAE waters. It is possibly endemic to the Arabian Sea region, although its exact distribution is uncertain due to confusion amongst Pastinachus species, and recent taxonomic changes within the genus (Last et al. 2016).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Cowtail Ray is benthic in coastal habitats and occurs over soft substrates, often near coral reefs (Last et al. 2016) to depths of 60 m. Maximum size and biology is poorly known due to confusion amongst Pastinachus spp. This species reaches at least 89 cm disc width (Last et al. 2016). Generation length is estimated at 20 years based on age data from Maculabatis astra (Jacobsen 2007).
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010). 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
330656
Taxon name
Pastinachus ater
Uploaded by
National Red List Database
Scientific name
Pastinachus ater
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
dasyatidae
Genus
Pastinachus
Species
ater
Taxonomic notes and synonyms listed
Recently, molecular data confirmed that the single, widespread Indo-“Pacific species, Pastinachus sephen consists of two species, the widespread P. ater and a more restricted P. sephen (Last et al. 2016a).
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
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Broad Cowtail Ray occurs throughout UAE coastal waters. The exact distribution is uncertain due to confusion amongst Pastinachus species and recent taxonomic changes. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980 and recent surveys have detected it in the area. Cowtail rays are regularly discarded in the Arabian Gulf and Sea of Oman. A large part of the species' regional distribution (namely, India and Pakistan) is under extremely intense and increasing demersal fishing pressure. It is not known how individuals occupying the UAE are connected with the broader population of the Arabian Seas region, and there is no information available to suggest that its population status differs in the UAE as compared to other parts of its range in the region. Given the threats faced by this species in other parts of the Arabian Seas region, and ongoing threats from discarding and habitat loss in the UAE, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 60 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Broad Cowtail Ray occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific, although its exact distribution is uncertain due to confusion amongst Pastinachus species and recent taxonomic changes within the genus.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Broad Cowtail Ray is benthic in coastal habitats. Maximum size and biology is poorly known due to confusion amongst other cowtail rays. Reaches ~200 cm disc width (Last et al. 2016). Generation length is estimated at 20 years based on age data from Maculabatis astra (Jacobsen 2007).
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010).
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
330017
Taxon name
Pateobatis jenkinsii
Uploaded by
National Red List Database
Scientific name
Pateobatis jenkinsii
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
dasyatidae
Genus
Pateobatis
Species
jenkinsii
Taxonomic notes and synonyms listed
Last et al. (2016) described the genus Pateobatis, consisting of five medium-size to very large, marine whiprays previously placed in Himantura (including jenkinsii).This species has probably been misidentified as Himantura (=Pateobatis) fai in the literature (W. White pers. obs). More specimens of both this species and of H. draco from South Africa need to be examined to resolve the taxonomic status of this species. Presently, H. draco is considered a synonym of P. jenkinsii. The South African species had dark spots along the posterior margin of the disc, but this form has also been reported from the Arafura Sea and off Sumatra in Indonesia. It is possible that these may in fact be colour forms of the same species. Examples of specimens with dark spots along the posterior margin of the disc are from the Arafura Sea, Sumatra (Last and Stevens 1994, Fahmi pers. obs. 2007), and from western Sri Lanka (Morón et al. 1998, Manjaji 2004), and the Sulu Sea (B.M. Manjaji-Matsumoto pers. obs. 2002).
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
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Jenkins' Whipray occurs throughout UAE inshore waters. It is very poorly known in the Arabian Sea region due to confusion with Pateobatis fai (the Pink Whipray) and results from a recent taxonomic revision. It is presumably taken incidentally in net and longline fisheries, and fishing pressure is intense and increasing in the Arabian Sea region, particularly in India and Pakistan. Whiprays are generally discarded as bycatch in the Arabian Gulf and Sea of Oman. Though data specifically from the UAE are not available, and it is not known how individuals occupying the UAE are connected with the broader population of the Arabian Seas region, there is no information available to suggest that its population status differs in the UAE as compared to other parts of its range in the region. Given the threats faced by this species in other parts of the Arabian Seas region, and ongoing threats from discarding and habitat loss in the UAE, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 60 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Jenkins' Whipray occurs throughout UAE waters. Globally, it is widespread but patchy in the Indo-West Pacific. Its distribution is not well defined due to recent taxonomic changes and the re-identification of stingrays (Dasyatidae) from the region (Last et al. 2016). Records from Pakistan, India and Sri Lanka need confirmation. Further taxonomic revisions and surveys in the Arabian Sea region are required to determine its distribution.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
This species is an inshore ray, usually found on sandy bottoms down to at least 90 m deep (Manjaji 2004, White et al. 2006, Last et al. 2016). It attains a maximum size of at least 150 cm disc width (DW) (~300 cm total length) (White et al. 2006, Last et al. 2016). Males mature at about 75-85 cm DW and size at birth is around 23 cm DW (White and Dharmadi 2007). Reproduction is viviparous with histotrophy (White et al. 2006). As there is no information on this species' maximum age and age at maturity, generation length was inferred as ~20 years based on data for Blackspotted Whipray (Maculabatis astra) (Jacobsen and Bennett 2011). However, it is noted that the Blackspotted Whipray grows to a much smaller maximum size (80 cm DW) than Jenkins' Whipray (150 cm DW).
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010).
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
330014
Taxon name
Pateobatis fai
Uploaded by
National Red List Database
Scientific name
Pateobatis fai
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
dasyatidae
Genus
Pateobatis
Species
fai
Taxonomic notes and synonyms listed
Last et al. (2016) described the genus Pateobatis, consisting of five medium-size to very large, marine whiprays previously placed in Himantura (including fai). This species is frequently misidentified as Himantura (=Pateobatis) jenkinsii.
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
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Pink Whipray occurs throughout UAE inshore waters, and is is apparently uncommon in the Arabian Gulf and Sea of Oman area. This species is incidentally captured in inshore fisheries and mostly discarded in UAE waters. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980, and recently conducted surveys have detected it in the area. In India, it is under extremely intense and increasing demersal fishing pressure. Though data specifically from the UAE are not available, and it is not known how individuals occupying the UAE are connected with the broader population of the Arabian Seas region, but there is no information available to suggest that its population status differs in the UAE, compared to other parts of its range in the region. Given the threats faced by this species in other parts of the Arabian Seas region, and ongoing threats from discarding and habitat loss in the UAE, it is inferred that declines reported in the Arabian Seas are representative of the status in the UAE. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by 20-30% over the past three generation lengths, or about 60 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Pink Whipray occurs throughout UAE waters. Globally, it is widespread in the Indo-West and Central Pacific (Kuiter and Debelius 1994, Anderson and Hafiz 1997, Golani and Bogorodsky 2010).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Pink Whipray is found on soft sandy bottoms and coral rubble on the inner continental shelf from the intertidal zone to 70 m depth (Last et al. 2016). The species attains a maximum size of at least 146 cm DW (disc width) with males maturing at around 112 cm disc width (DW) (Last et al. 2016). Size at maturity for females is unknown, but reproduction is viviparous with histotrophy (White et al. 2006). Little else is known of its biology. As there is no information on this species' maximum age and age at maturity, generation length was inferred as ~20 years based on data for Blackspotted Whipray (Maculabatis astra) (Jacobsen and Bennett 2011). However, it is noted that the Blackspotted Whipray grows to a much smaller maximum size (80 cm DW) than the Pink Whipray (146 cm DW).
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. This species is impacted by bycatch fisheries that are active elsewhere in its range. Marine habitats in the Gulf are experiencing high levels of disturbance and quickly deteriorating due to major impacts from development activities (including dredging and reclamation), desalination plants, industrial activities, habitat destruction through the removal of shallow productive areas and major shipping lanes (Sheppard et al. 2010).
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
330006
Taxon name
Rhinobatos annandalei
Uploaded by
National Red List Database
Scientific name
Rhinobatos annandalei
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
rhinobatidae
Genus
Rhinobatos
Species
annandalei
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
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Bengal Guitarfish occurs throughout UAE coastal waters. Due to confusion with the Spotted Guitarfish (Rhinobatos punctifer), population data can be uncertain. There has been a total ban on fishing for this species in UAE waters since 2019, but is still taken as bycatch in coastal net fisheries. Declines of several species of inshore guitarfish have been documented (e.g., India). Habitat degradation from coastal development is a concern for this species as well. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net 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 20-30% over the past three generation lengths, or about 15 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Bengal Guitarfish occurs throughout UAE waters. Globally, it has a poorly defined distribution in the Northern Indian Ocean from the Arabian Gulf (Iran, UAE) to India and possibly Sri Lanka (Bianchi 1985, Talwar and Jhingran 1991, Assadi and Dehghani 1997, Vossoughi and Vosoughi 1999). There has been some confusion as to the identification of this species, making its exact distribution difficult to define, with some previous studies have referred to it as the Spotted Guitarfish.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
Very little information is currently available on the habitat or biology of this guitarfish. It occurs from close inshore out to about 90 m deep and presumably occurs over soft substrates. Maximum total length is reported at approximately 87 cm (R.W. Jabado pers. obs.). Maturity for males is about 50-68 cm TL and for females it is around 60 cm TL (Raje 2006, Henderson et al. 2004, Last et al. 2016). Size at birth is about 19-20 cm TL. Fecundity is up to 3-20 pups (M. Khan pers. comm. 08/02/2016, Raje 2006) although females dissected from landings in Oman had between 3-5 pups (Henderson et al. 2004). Most pregnant and post-partum females in Indian and Pakistan waters occur in September and October (M. Khan pers. comm. 08/02/2016, Raje 2006) and in the summer and winter in Oman (Henderson et al. 2004). Generation length is inferred to be 5 years from the Lesser Guitarfish (Acroteriobatus annulatus) from southern Africa (Compagno et al. 1989).
Threats listed in assessment
This species has been impacted by target and bycatch fisheries. It may also being impacted by habitat degradation due to coastal development, especially nursery grounds. 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.<em style=""font-size: 12pt; font-family: Georgia;""> 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
330005
Taxon name
Rhinobatos punctifer
Uploaded by
National Red List Database
Scientific name
Rhinobatos punctifer
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
rhinobatidae
Genus
Rhinobatos
Species
punctifer
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
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Spotted Guitarfish occurs throughout UAE coastal waters. Due to confusion with the Bengal Guitarfish (Rhinobatos annandalei), population data can be uncertain. There has been a total ban on fishing for this species in UAE waters since 2019, but is still taken as bycatch in coastal net fisheries. Declines of several species of inshore guitarfish have been documented elsewhere. Habitat degradation from coastal development is a concern for this species as well. It is especially susceptible to exploitation (target and bycatch) in many largely unregulated gill net 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 20-30% over the past three generation lengths, or about 15 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Spotted Guitarfish occurs throughout UAE waters. Globally, it is restricted to the Arabian Sea region from the northern Red Sea to the Sea of Oman and Arabian Gulf (Bonfil and Abdallah 2004, Last et al. 2016). The species has been frequently misidentified in the literature, and sometimes confused with the Bengal Guitarfish (Rhinobatos annandalei).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
This species inhabits the inshore continental shelf to depths of 70 m on soft substrates (Weigmann 2016). Reproduction is viviparous and the species reaches at least 90 cm total length (TL) (Weigmann 2016). Maximum litter size is up to at least seven and size at birth is ~25 cm TL (A.C. Henderson unpubl. data). Data from Oman indicates that females taken during autumn off Muscat were all mature at less than 77 cm TL while males matured at less than 71 cm TL (Henderson et al. 2004). Generation length is inferred to be 5 years from the Lesser Guitarfish (Acroteriobatus annulatus) from southern Africa (Compagno et al. 1989).
Threats listed in assessment
This species has been impacted by target and bycatch fisheries. It may also being impacted by habitat degradation due to coastal development, especially nursery grounds. 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.<em style=""font-size: 12pt; font-family: Georgia;""> 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
330004
Taxon name
Mobula kuhlii
Uploaded by
National Red List Database
Scientific name
Mobula kuhlii
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
mobulidae
Genus
Mobula
Species
kuhlii
Taxonomic notes and synonyms listed
Combined morphological and molecular data led Last et al. (2016) and White et al. (2017) to conclude that M. eregoodootenkee is a junior synonym of M. kuhlii. However, Hosegood et al. (2019) suggested these were separate species, which was supported by Notarbartolo di Sciara et al. (2020), who also clarified the nomenclature as M. eregoodoo.
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
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2d
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Shortfin Devil Ray occurs throughout UAE waters and may be locally common there. This species is not targeted or valued in markets of the UAE and capture of this species is totally banned there. When captured in the Arabian Gulf and Sea of Oman, it is typically discarded alive, and significant declines are not suspected there at this time. It is a component of the bycatch in several fisheries (e.g., Pakistan), and is directly targeted in Sri Lanka and India. Its low productivity causes it to be susceptible to rapid population declines, and severe declines have recently been confirmed from Pakistan (over the past three years). 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, it is suspected to have declined by 20-30% over the past three generation lengths, or about 23 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2d.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Shortfin Devil Ray occurs throughout UAE waters. Globally, it is widespread in the tropical Indo-West Pacific (Notarbartolo di Sciara et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Shortfin Devil Ray is an uncommon inshore, primarily shelf pelagic species found in continental coastal areas but not extending into the epipelagic zone (Compagno and Last 1999). This species reaches a maximum size of about 119 cm disc width (DW) (White et al. 2006b). Males mature at 103-“119 cm (DW) (White et al. 2006b, Notarbartolo di Sciara et al. 2017) and size at birth is around 31 cm DW (Compagno and Last 1999). As with all Myliobatiformes, the reproductive mode of M. kuhlii is livebearing and histotrophic, with embryonic nutrition supplied from a protein- and lipid-rich histotroph from highly developed trophonemata. A single, relatively large pup is produced per litter (Compagno and Last 1999, White et al. 2006b). Intrinsically, Manta and Mobula rays have among the lowest productivity of any chondrichthyan (Pardo et al. 2016). Long resting periods may account for extended reproductive cycles in mobulid species. As there are not enough data to estimate an exact generation length for this species, an approximate, suspected generation length is used. A midway point of 7.5 years between a very conservative low of five years, and the larger Spinetail Devil Ray's 10-year generation length is suspected to be the approximate generation length for the Shortfin Devil Ray until more accurate information becomes available (Cuevas-Zimbron et al. 2013).
Threats listed in assessment
Information pertaining to threats specific to the UAE is unavailable. This species is impacted by target (for fins and their valuable meat) and bycatch fisheries that are active elsewhere in its range. Manta rays are easy to target because of their large size, slow swimming speed, aggregation behaviour and predictable habitat use.
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
330003
Taxon name
Chiloscyllium arabicum
Uploaded by
National Red List Database
Scientific name
Chiloscyllium arabicum
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
orectolobiformes
Family
hemiscylliidae
Genus
Chiloscyllium
Species
arabicum
Taxonomic notes and synonyms listed
This species was first described by Gubanov and Schleib (1980) but Dingerkus and DeFino (1983) described it as a separate species, Chiloscyllium confusum, without mention of C. arabicum. Compagno (1984) provisionally recognized C. arabicum but noted it was apparently very close to C. punctatum. Dingerkus and DeFino's account clearly establishes this species as separate from C. punctatum (Compagno 2001). This species has been widely misreported as C. griseum, at least in the Arabian Gulf, and the distribution of these two similar species requires clarification. There is a high need for taxonomic investigation regarding species in the genus Chiloscyllium in the Arabian Sea region (D. Ebert pers. comm. 2017).
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
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2cd+3cd
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The Arabian Carpetshark occurs throughout UAE coastal waters, and is common in the Arabian Gulf. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980 and recently conducted surveys frequently detected it in the area. It is not targeted in the Arabian Sea region, but appears to be a major component of bycatch in trawl (and other) fisheries, and is typically discarded due to its small size and low market value. It has a close association with coral reef and estuarine habitats, which are prone to degradation and loss in the Gulf due to coastal development and impacts to benthic communities from demersal trawling. 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 20-30% over the past three generation lengths, or about 27 years. It is listed as Near Threatened, nearly meeting the thresholds for Vulnerable A2cd.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
The Arabian Carpetshark occurs throughout UAE waters. Globally, it is restricted to the Arabian Sea region from the Arabian Gulf to India. Records from Oman require confirmation. Another Chiloscyllium species, which is similar to the Arabian Carpetshark and possibly undescribed, may occur in northwestern India (R.W. Jabado pers. comm. 07/02/2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
The Arabian Carpetshark occurs in coastal waters in coral reefs, lagoons, rocky shores, muddy bottoms and mangrove estuaries from 2-100 m. This shark is less than 10 cm total length (TL) at birth, but grows to a maximum length of 80 cm TL (Weigmann 2016). Females mature at 52 cm TL and males at about 55 cm TL (Moore and Peirce 2013). The species is oviparous, with single egg cases developing in each uterus. It appears to be closely associated with coral reefs. Age data are not available, but generation length is estimated as 9 years using data from the similar-sized White-spotted Bambooshark (C. plagiosum) (Chen et al. 2007).
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. The Arabian Carpetshark is known to have close association with coral reef habitats, which are particularly prone to anthropogenic degradation and the effects of climate change (Carpenter et al. 2008, Normile 2016). In the Gulf, habitat degradation threats include impacts from the damming of the Tigris-Euphrates river system in Turkey and draining of the Iraqi marshes (Al-Yamani et al. 2007), chronic and acute (e.g., war-related) releases of oil, rapid large-scale coastal development (e.g., megastructures in the UAE), and disturbance of benthic communities due to demersal trawling. Coastal land reclamation has accelerated in this area in recent years and, as a result, coastal reefs and other habitat have been destroyed. This has also resulted in the almost total loss of mangrove areas around Bahrain (Morgan 2006a). High levels of polycyclic aromatic hydrocarbons (PAHs) and benzo [a] pyrene have been reported from this species in Kuwait (Al-Hassan et al. 2000). 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
329946
Taxon name
Porites lobata
Uploaded by
National Red List Database
Scientific name
Porites lobata
Assessed taxon level
Species
Higher level taxonomic groupings
Invertebrates
Corals
Kingdom
Animalia
Phylum
cnidaria
Class
anthozoa
Order
scleractinia
Family
poritidae
Genus
Porites
Species
lobata
Taxonomic notes and synonyms listed
Porites baueri and Porites excavata are now synonyms of this species.
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
Assessed as
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
A2bc
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This stony coral is common and can be a dominant species along both coasts of the UAE. It can survive sedimentation and has low susceptibility to bleaching, but other species of Porites are particularly susceptible to disease and extensive reduction of coral reef habitat due to a combination of threats. This species is among the most common corals in Fujairah and occurs along the entire coast of the UAE, but becomes less common to the west. Species-specific population trend data are not available and therefore are based on the data available for the genus. Despite the relatively low susceptibility to bleaching, the most recent bleaching event (2017) resulted in over 75% mortality of Porites in shallow-water habitats of Abu Dhabi. Elsewhere, however, Porites are in better shape. For example, Porites species are relatively stable in Dubai. In Fujairah, Porites species are increasing, likely recovering from an earlier decline after a massive harmful algal bloom and cyclone in 2007-2008. Although recent (post-2011) data are limited, there have been no major disturbances since then. As this species is more abundant in areas that are improving in status, it is suspected that overall declines in the UAE are likely approaching but not exceeding 30% over three generations (1989-2019). Therefore, it is listed as Near Threatened under criterion A2bc. No regional adjustment is made to the Near Threatened listing.
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is reported from UAE waters in both the Gulf and Sea of Oman (Riegl et al. 2012, Grizzle et al. 2016).Elsewhere, this species is widely distributed in the Indo-Pacific.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Yes
Habitat details as listed in assessment
This species is frequently a dominant species of back reef margins, lagoons and some fringing reefs, and generally can be found to depths of 30 m. It is one of the predominant framework builders, sometimes building monospecific reef frameworks or contributing to pocilloporid reef building (Glynn 2001). It is a relatively slow-growing species with reported growth rates of 8.4 mm/year in Costa Rica and 8.1 mm/year in the Galápagos; however, it can grow as fast as 14 to 19 mm/year during the first few years (Guzmán and Cortes 1993, Cortés and Guzmán 1998, Guzmán and Cortés 1989). This species utilizes a gonochoristic reproductive strategy (except from Caño Island, Costa Rica), and is presumably a broadcaster spawner (Glynn et al. 1994). Glynn et al. (1994) suggested that eastern Pacific populations appeared to be reproductively active over multiple annual intervals, including periods of relatively low temperature. According to Glynn et al. (1994), fecundity can vary between regions; P. lobata has higher fecundities at Caño Island, Costa Rica, and Uva Island, Panama, than in the Galápagos Islands, where water temperatures are lower and more seasonally variable. Moreover, Glynn et al. (1994) suggest that P. lobata reproduces twice per year in thermally high and stable environments. Fecundity of this coral appears to benefit from moderate sea warming events, but may decline dramatically during unusually strong thermal anomalies (Glynn et al. 1994). After 1983, observations of sexual recruitment have been rare to infrequent in the eastern Pacific; however sexual recruitment has been observed in some areas of the Galápagos Islands (Glynn et al. 1994). The almost complete absence of sexual recruitment for this species in the eastern Pacific may be due to high larval mortality in the water column; as well as increased levels of competition with benthic alga, and increased densities of grazers and bioeroders following the 1982-83 El Niño event (Glynn et al. 1994).Porites lobata can also reproduce asexually by fragmentation (Guzmán and Cortés 1989, Cortés and Guzmán 1998, Cortés and Jiménez 2003). In the eastern Pacific the incidental feeding activities of the triggerfish Pseudobalistes naufragium can generate fragments that survive to form new colonies (Guzmán and Cortés 1989, Cortés and Guzmán 1998, Glynn et al. 1994). This form of fragmentation is common in Costa Rica and Panama, but uncommon in the Galápagos Islands (Glynn et al. 1994). Fragmentation also occurs by initial weakening of colonies by bioeroders; P. lobata colonies possess high densities of boring bivalves (Lithophaga spp.), which erode the skeletal structure, a process that can also lead to fragmentation (Cortés and Jiménez 2003, Glynn et al. 1994).At least eight fish species feed on live corals, with their feeding strategies ranging from removing mainly live tissue and causing little damage to the skeleton, to abrading or breaking apart colonies in the feeding process, such as during feeding of Arothron meleagris and Pseudobalistes naufragium (Guzmán and Cortes 1989, Glynn 2001). It is commonly grazed by the puffer Arothron meleagris (Guzmán and Robertson 1989, Glynn et al. 1994).The age of first maturity of most reef building corals is typically three to eight years (Wallace 1999) and therefore we assume that average age of mature individuals is greater than eight years. Total longevity is not known, but likely to be more than ten years. Furthermore, based on average sizes and growth rates, we assume that average generation length is 10 years, unless otherwise stated. Therefore, any population decline rates for the Red List assessment are measured over at least 30 years.
Threats listed in assessment
In the Gulf, the major threats to corals include extreme and increasing temperature variability due to climate change, as well as direct destruction and increased turbidity caused by coastal construction (Riegl et al. 2012). Although bleaching thresholds in the Gulf are the highest recorded in the world (Riegl et al. 2012), bleaching events in the UAE have resulted in significant mortality (such as in 1996-1998, 2002, 2010 and 2017) and slow recovery (Burt et al. 2008). In Abu Dhabi, the most recent coral bleaching event resulted in nearly 95% of corals bleaching, and by April 2018, mortality reached 73% (Burt et al. 2019). This event resulted in mass mortality of even the more stress-tolerant corals such as poritids and merulinids (Burt et al. 2019). Coastal development, particularly large-scale offshore real estate developments and sedimentation associated with reclamation, has directly buried coral reefs in the Gulf (Burt et al. 2008, 2013; Burt 2014; Burt and Bartholomew 2019). In the Sea of Oman, UAE reefs have experienced major hurricanes and harmful algal blooms that caused high coral mortality and shifted community structure (Bauman et al. 2010, Foster et al. 2011).The genus is not particularly susceptible to bleaching, but is more prone to disease than many other corals. Coral disease has emerged as a serious threat to coral reefs worldwide and is a major cause of reef deterioration (Weil 2006). The numbers of diseases and coral species affected, as well as the distribution of diseases have all increased dramatically within the last decade (Porter et al. 2001, Green and Bruckner 2000, Sutherland et al. 2004, Weil 2004). Coral disease epizootics have resulted in significant losses of coral cover and were implicated in the dramatic decline of acroporids in the Florida Keys (Aronson and Precht 2001, Porter et al. 2001, Patterson et al. 2002). In the Indo-Pacific, disease is also on the rise with disease outbreaks recently reported from the Great Barrier Reef (Willis et al. 2004), Marshall Islands (Jacobson 2006) and the northwestern Hawaiian Islands (Aeby et al. 2006). Increased coral disease levels on the Great Barrier Reef were correlated with increased ocean temperatures (Willis et al. 2004) supporting the prediction that disease levels will be increasing with higher sea surface temperatures. Escalating anthropogenic stressors combined with the threats associated with global climate change of increases in coral disease, frequency and duration of coral bleaching and ocean acidification place coral reefs in the Indo-Pacific at high risk of collapse.Globally, the major threat to corals is global climate change, in particular, temperature extremes leading to bleaching and increased susceptibility to disease, increased severity of ENSO events and storms, and ocean acidification. In addition to global climate change, corals are also threatened by a number of localized threats. Localized threats to corals include fisheries, human development (industry, settlement, tourism, and transportation), changes in native species dynamics (competitors, predators, pathogens and parasites), invasive species (competitors, predators, pathogens and parasites), dynamite fishing, chemical fishing, pollution from agriculture and industry, domestic pollution, sedimentation, and human recreation and tourism activities.
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.
