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VU

Assessment ID
329923
Taxon name
Epinephelus bleekeri
(Vaillant, 1878)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Epinephelus bleekeri
(Vaillant, 1878)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
epinephelidae
Genus
Epinephelus
Species
bleekeri
Species authority
(Vaillant, 1878)
Location and scope
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Conservation Status
Assessed as
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2bcd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This reef-associated species occurs throughout UAE waters. It is exploited by grouper fisheries, and is common in local markets in the Arabian Gulf, but apparently less common in UAE markets in general. It appears likely that this species is overfished in the UAE, based on the status of Epinephelus coioides, which this species (E. bleekeri) continues to be confused with in fishery statistics. Anecdotal observations of its occurrence in fish markets over the past 10-29 years indicate that population declines have occurred since about 1995, or a 24-year time period. Catch of E. coioides has declined by about 51% in Abu Dhabi over the past 12 years (since 2007), or approximately one and a half generation lengths. Applying data from a proxy species, three generation lengths is about 24 years. The status of population(s) outside the UAE is not well-understood, though it is also taken by fisheries elsewhere, including in the Sea of Oman. Based on catch data and fish market observations, this species has undergone a suspected decline of at least 30% and possibly more since about 1995, or over the past three generation lengths. Fishing effort is expected to remain the same or increase in the future. Therefore, it is listed as Vulnerable A2bcd. Further action is needed to improve fishery monitoring and data collection. Research on life history parameters is needed to improve the estimate of generation length.
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 (Heemstra and Randall 1993, K. Rhodes pers. comm. 2016). Its depth range is 3 to 104 metres.
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 demersal species inhabits mostly shallow coral and rocky banks, can be associated with non-reefal and turbid habitat, and is not known from well-developed coral reefs (Randall 1995). Juveniles can be commonly taken in estuaries. Its maximum standard length is 87 cm (Richu et al. 2018). Life history data are lacking, but due to similarities, Epinephelus maculatus is considered an appropriate proxy to estimate generation length. The age at first maturity for E. maculatus females is 2.8 years and males is 4 years and longevity is 13 years (Rhodes et al. 2016). 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. Off India, Richu et al. (2018) estimated the longevity as 9.7 years and Kandula et al. (2015) reported a total length at first sexual maturity of about 36 cm.
Threats and conservation measures listed
Threats listed in assessment
Overexploitation is a major threat to this species. Degradation of estuaries (juvenile habitat) has been severe in the UAE and the Arabian Gulf region due to coastal development and pollution. 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
329910
Taxon name
Mobula thurstoni
(Lloyd, 1908)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Mobula thurstoni
(Lloyd, 1908)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
mobulidae
Genus
Mobula
Species
thurstoni
Species authority
(Lloyd, 1908)
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2d
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In UAE waters, the Bentfin Devil Ray occurs only in the Sea of Oman in inshore and offshore waters. This species is not targeted or valued in markets of the UAE and capture of this species is totally banned in the UAE. When captured in the 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 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. There is no information to confirm that this species is breeding in the UAE and no information confirming the likelihood of a cease in immigration from outside the region, despite ongoing threats and recorded declines. Based on recorded levels of exploitation, it is suspected to have declined by 30-50% over the past three generation lengths, or about 23 years. It is listed as Vulnerable 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 Bentfin Devil Ray occurs in UAE waters on the Sea of Oman coast. It is excluded from the Arabian Gulf. Elsewhere, it is distributed in tropical, subtropical, and temperate waters of the Indian Ocean from the Red Sea to India, Sri Lanka, and the Maldives (Couturier et al. 2012, Notarbartolo di Sciara et al. 2017).
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 Bentfin Devil Ray is usually pelagic or epipelagic in shallow, productive, neritic waters of &lt;100 m depth (Notarbartolo di Sciara 1988, Croll et al. 2016), although it is also caught in offshore pelagic waters (Mas et al. 2015), and around seamounts in the Mid-Atlantic Ridge (Mendonça et al. 2012). Segregation by size and sex is seasonal, with all size classes and sexes appearing together during the summer months (Notarbartolo di Sciara 1988). The species is observed either solitarily or in small groups (2-“6 individuals); it is not a schooling species (Notarbartolo di Sciara 1988). Maximum size is reported to at least 189 cm disc width (DW) and both females and males are estimated to mature at around 154 cm disc width (DW), while size at birth is estimated at 65-“85 cm DW (Notarbartolo di Sciara 1988, Last et al. 2016). Size at 50% maturity was estimated at 153.8 cm DW for males (White et al. 2006b). The mode of reproduction is matrotrophic viviparity. Embryos obtain nutrients initially via yolk, then through absorption of enriched uterine fluid from the mother (Wourms 1977). Only the left ovary is functional and litter size is one pup after a 12-month gestation period (Wourms 1977, Notarbartolo di Sciara 1988). It is estimated that the maximum intrinsic population growth rate (r<sub>max</sub>) of devil rays is similar to manta rays, and these productivity rates are among the lowest of all chondrichthyans (Dulvy et al. 2014, Pardo et al. 2016). Mating, parturition, and early life history are reported to take place in the shallow water during summer and perhaps early autumn (Notarbartolo di Sciara 1988).For the Spinetail Devil Ray (up to 310 cm DW), Cuevas-Zimbrón (2012) estimated age at maturity to be 5-“6 years and a minimum lifespan of 14 years, giving a generation length of 10 years. While accurate age at maturity and longevity information is unavailable for the Bentfin Devil Ray, it can be inferred according to the smaller maximum size that it would be close to but slightly shorter than that of its congener. 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 Bentfin Devil Ray until more accurate information becomes available.
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. 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
329906
Taxon name
Rhinoptera javanica
Müller & Henle, 1841
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Rhinoptera javanica
Müller & Henle, 1841
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
rhinopteridae
Genus
Rhinoptera
Species
javanica
Species authority
Müller & Henle, 1841
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2d
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Javan Cownose Ray occurs throughout UAE coastal waters. Due to confusion with the Oman Cownose Ray (Rhinoptera jayakari), population data can be uncertain, but it is suspected this species is the rarer of the two that occur in the Arabian Sea region. Serious declines in cownose ray landings have been observed in Pakistan, and of batoids in general in India. It exhibits 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 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 at least 30% over the past three generation lengths, or about 45 years. There is no information to confirm that this species is breeding in the UAE and no information confirming the likelihood of a cease in immigration from outside the region, despite ongoing threats and recorded declines. It is listed as Vulnerable 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 Javanese Cownose Ray occurs throughout UAE waters. Globally, it has a wide range throughout the Indo-West Pacific (Spaet and Berumen 2015, 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
This species is benthopelagic and occurs over the continental shelf, often close inshore. It is typically solitary or small aggregations (not usually in the very large aggregations like other cownose rays) (Last et al. 2016). Litter size is 1-2 pups per litter (R. W. Jabado unpubl. data), but it is unknown if reproductive periodicity is annual or biennial. It reaches at least 165 cm disc width (DW) (Last et al. 2016). Generation length estimated to be ~15 years based on the smaller (110 cm DW) R. bonasus (Fisher et al. 2014).
Threats and conservation measures listed
Threats listed in assessment
This species is impacted by target and bycatch fisheries in the UAE as well as elsewhere in its range. Marine habitats in the Arabian Gulf are experiencing high levels of disturbance 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
329900
Taxon name
Epinephelus coioides
(Hamilton, 1822)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Epinephelus coioides
(Hamilton, 1822)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
actinopterygii
Order
perciformes
Family
epinephelidae
Genus
Epinephelus
Species
coioides
Species authority
(Hamilton, 1822)
Taxonomic notes and synonyms listed
This species is frequently mis-identified as Epinephelus malabaricus or E. tauvina in aquaculture and fisheries literature (Heemstra and Randall 1993).
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2bcd+4bcd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This demersal species inhabits nearshore habitats from estuaries (juveniles) to coral reefs (adults) throughout UAE waters. It is heavily targeted by grouper fisheries throughout the Arabian Gulf and off Oman. It is considered overexploited in the UAE, Oman and the Gulf. In addition, degradation of coral reefs and estuaries is pervasive throughout the Gulf, and is also impacting this species. According to fish market observations, catch data and biomass estimates from scientific surveys, this species has undergone an inferred decline of at least 20-45% and possibly more, since about 1998, or over the past two generation lengths. Conservation measures, including protected areas and fishing regulations (minimum catch length and some fishing license control in Abu Dhabi), have prevented the rate of decline from exceeding 50% at this time; however, fishing effort exceeds sustainability, causing overexploitation to continue. Fishing effort is expected to remain the same or increase in the future time period over the next generation length. Population(s) in areas neighboring the UAE are also in serious decline and it is unlikely that fishing effort is decreasing at a significant level elsewhere. Therefore, this species is listed as Vulnerable A2bcd+4bcd.
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 (Heemstra and Randall 1993). Its depth range is 0 to 100 metres.
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 coral reefs typically along continental coastlines and large islands (Carpenter et al. 1997a, Grandcourt et al. 2005). Juveniles often occur in estuaries over sand, mud and gravel substrate and amongst mangroves (Kailola et al. 1993, Randall et al. 1997). It primarily consumes fishes, shrimps, crabs and other benthic crustaceans (Grandcourt et al. 2005). Its maximum total length is 172 cm and is a diandric protogynous hermaphrodite (Grandcourt et al. 2009). Juvenile sexual differentiation in this species can be significantly influenced by social factors (Liu and Mitcheson 2011). In the Arabian Gulf, it has been aged to at least 22 years (Mathews and Samuel 1991, Grandcourt 2006, M. Abdullah pers. comm. 2010). Females reach first maturity at 4 years and 34 cm total length. Males reach maturity at 67.5 cm and 7.5 years and transition occurs at 50 to 75 cm at 4 to 8 years of age (M. Abdullah pers. comm. 2010). McIlwain et al. (2015) reported a size and age at 50% maturity for females of 58 cm total length and 4 years. Based on a longevity of 22 years, age of first maturity of 4 years, and applying the mean generational turnover formula in Depczynski and Bellwood (2006), one generation length is estimated to be 12.5 years. It forms seasonal spawning aggregations in the Arabian Gulf from March to June (Heemstra and Randall 1993, Grandcourt et al. 2009).
Threats and conservation measures listed
Threats listed in assessment
Overfishing is a major threat to this species in the Arabian Gulf (Grandcourt et al. 2005). Degradation of estuaries (juvenile habitat) due to coastal development and pollution may also impact this species. The effects of reduced discharge of the Shatt Al-Arab River caused by damming of the Tigris and Euphrates Rivers has greatly impacted the estuarine habitats in the northern Gulf (Al-Husaini et al. 2015), and caused reduced recruitment in this species (Ben-Hasan et al. 2018). Chlorinated-hydrocarbons (sourced from pollution) have been detected in this species in sampling conducted in the UAE, and this is considered to be an additional stressor to the health of adults of this species (De Mora 2005). 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
329899
Taxon name
Stegostoma tigrinum
Forster, 1781
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Stegostoma tigrinum
Forster, 1781
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
orectolobiformes
Family
stegostomidae
Genus
Stegostoma
Species
tigrinum
Species authority
Forster, 1781
Taxonomic notes and synonyms listed
The nomenclatural history of the species is somewhat complicated. The name Stegostoma fasciatum (Hermann, 1783) has been the standard name used, however Dahl et al. (2019) concluded that the original name Stegostoma tigrinum Forster, 1781 is the correct senior synonym.
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Zebra Shark occurs throughout UAE coastal waters usually near coral and rocky reef habitat, and is relatively common there. It is susceptible to capture in a range of inshore fisheries, but is rare in landings in the UAE due to its relatively low value. This species is not targeted or valued in markets of the UAE, trawling has been banned there since 1980 and it remains commonly sighted by divers. It has strong site fidelity and can form aggregations, which can facilitate the rapid removal of individuals in fisheries operations. In the Arabian Sea, it is landed in India and Pakistan, but less commonly elsewhere. 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 at least 30% over the past three generation lengths, or about 50 years. It is listed as Vulnerable 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 Zebra Shark occurs throughout UAE waters (Field 2005). Globally, it is found in inshore waters of the continental and insular shelves of the Indo-West Pacific (Compagno 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
The Zebra Shark occurs in tropical and subtropical, shallow inshore and offshore waters, often found on and around coral and rocky reefs and on sandy plateaus near reefs, at depths down to at least 62 m. It is often observed resting on the bottom as well as swimming near the surface as both juveniles and adults. The species undergoes seasonal movement patterns, forms aggregations and demonstrates strong site fidelity to particular reefs (Dudgeon et al. 2013), which may make them more susceptible to targeted fishing.The Zebra Shark is an oviparous species. Size at birth ranges between 20 and 36 cm total length (TL). Reproductive periodicity in the wild is unknown. Captive aquaria animals have demonstrated annual egg laying periods of up to 3 months with 40-“80 eggs laid per year (Robinson et al. 2011) with up to 25% of eggs resulting in hatchlings (L. Squire Jnr pers. comm. 22/07/2014). Age of maturity of captive female sharks is approximately 6-8 years of age based on the commencement of egg laying (Thomas pers. comm. 18/02/2015, Robinson pers. comm. 11/01/2015) and 7 years of age for males (Watson pers. comm. 18/02/2015). Adults reach a maximum size of 246 cm TL with no sexual dimorphism evident (Dudgeon et al. 2008) and live over 28 years in aquaria (Thomas pers. comm. 17/02/2015). Generation length estimates based on 6 years first age at maturity and 28 years maximum longevity for female sharks is 17 years.
Threats and conservation measures listed
Threats listed in assessment
In the UAE, sharks have been impacted by targeted commercial fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). Sharks continue to be impacted by artisanal and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018). This species 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). 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
329898
Taxon name
Hemipristis elongata
(Klunzinger, 1871)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Hemipristis elongata
(Klunzinger, 1871)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
hemigaleidae
Genus
Hemipristis
Species
elongata
Species authority
(Klunzinger, 1871)
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Snaggletooth Shark occurs throughout UAE coastal waters and is uncommon there and in surrounding areas. It is taken in a variety of fisheries in the Arabian Sea region. While there is limited information available on this species in the region, its large size, relative rarity, and the presence of intensive fisheries mean that, like many large carcharhinids (that are morphologically and ecologically similar to hemigaleids) in the region, it will have undergone significant declines. 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 30-50% over the past three generation lengths, or about 27 years. It is listed as Vulnerable 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 Snaggletooth Shark occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific.
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 Snaggletooth Shark occurs on the continental shelf from inshore waters to 130 m depth (Compagno 1998). This species attains 281 cm total length (TL), with males maturing at approximately at 122-131 cm TL (Jabado et al. 2016). This viviparous species has a seasonal reproductive cycle, producing 2 to 11 (mean = 6) young per litter. Size at birth is up to 38 cm TL (Henderson et al. 2004). Smart et al. (2013) provided age and growth data for specimens caught off the east coast of Queensland (Australia). Growth appears to be quite rapid, with maturity reached in 2-“3 years. Maximum observed age was 15 years. Generation length is estimated to be 9 years based on age data from Smart et al. (2013).
Threats and conservation measures listed
Threats listed in assessment
In the UAE, sharks have been impacted by targeted commercial fisheries until 2014 when a ban on export of sharks was imposed (Ministry of Climate Change and Environment). Sharks continue to be impacted by artisanal and bycatch fisheries (Annual Fisheries Statistical Report for Abu Dhabi Emirate 2001-2018), though catch data are not species-specific. 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
329893
Taxon name
Rhina ancylostoma
Bloch & Schneider, 1801
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Rhina ancylostoma
Bloch & Schneider, 1801
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
rhinopristiformes
Family
rhinidae
Genus
Rhina
Species
ancylostoma
Species authority
Bloch & Schneider, 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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Bowmouth Guitarfish occurs throughout UAE inshore waters. This species is not targeted in the UAE and trawling has been banned there since 1980; however, it is frequently taken as bycatch in coastal net fisheries. It is taken in variable quantities in gill net and trawl fisheries elsewhere in the Arabian Gulf, and coastal habitat degradation is a significant threat, particularly in the Gulf. It is under extremely intense and increasing demersal fishing pressure in much of the Arabian Sea region. It exhibits 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 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 30-50% over the past three generation lengths, or about 39 years. It is listed as Vulnerable 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 Bowmouth Guitarfish occurs throughout UAE waters (Tourenq et al. 2008). Globally, it is widespread in the Indo-West Pacific (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 Bowmouth Guitarfish has an intertidal and coastal distribution. It generally occurs close inshore and around coral reefs to about 90 m (Fricke et al. 2011). It occurs on or close to the seabed, mainly over sandy or muddy substrates. Very little is known about the life history characteristics of this species. However, it is a large species growing to at least 294 cm total length (TL) and is lecithotrophic viviparous (Compagno and Last 1999, Jabado 2018). Males mature between 150 and 175 cm TL, and one pregnant female was recorded with 9 mid-term embryos ranging between 27-31 cm TL (Last and Stevens 2009). A single new born individual of 53 cm TL has been recorded from Bahrain (Randall 1995). Further research on the biology and life history of this species is needed.Maximum age for Rhynchobatus spp. in Australia is 5 years (males) and 12 years (females), but these data were not from the largest individuals (White et al. 2014) and are not reliable for the estimation of generation length for rhinids. This is therefore estimated from the maximum age (19 years) and age at maturity (7 years) taken from the growth curve provided by White et al. (2014) for the Giant Guitarfish (Glaucostegus typus), which gives an estimated generation length of 13 years.
Threats and conservation measures listed
Threats listed in assessment
This species is impacted by fishing activities in the UAE, where it is targeted for local consumption and taken as bycatch (Jabado 2018). This species may also be 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-family: Georgia; font-size: 12pt;""> 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
329887
Taxon name
Echinorhinus brucus
(Bonnaterre, 1788)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Echinorhinus brucus
(Bonnaterre, 1788)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
squaliformes
Family
echinorhinidae
Genus
Echinorhinus
Species
brucus
Species authority
(Bonnaterre, 1788)
Taxonomic notes and synonyms listed
Genetics studies have led some researchers to suspect that there may be an undescribed species of Echinorhinus off Oman and elsewhere in the Arabian Sea region (Henderson 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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2d
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
In UAE waters, the Bramble Shark, a large deepsea species, occurs only in the Sea of Oman. There are no fisheries that take this species in UAE waters due to the lack of deepsea fisheries. It is exploited off southwest India and historically in the Maldives. Its limited biological productivity infers an overall susceptibility to rapid population decline. 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, it is suspected to have declined by at least 30% over the past three generation lengths, or about 90 years. It is listed as Vulnerable 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 Bramble Shark occurs in UAE waters on the Sea of Oman coast. It is excluded from the Arabian Gulf (Javadzadeh et al. 2010, Jabado et al. 2014). Globally, it is widespread but patchy in the Indo-Pacific and Atlantic Oceans (al Sakaff and Esseen 1999, Henderson et al. 2007, Javadzadeh et al. 2010, Ebert et al. 2013, K.V. Akhilesh pers. obs.).
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 Bramble Shark is a deepsea species that occurs primarily on continental and insular slopes at depths of 200-900 m, although it has been found as shallow as 18 m (usually in colder water) and as deep as 1,214 m (Kabasakal 2005, Ebert and Stehmann 2013). Examination of landings from Kochi Fisheries Harbour, Kerala, India, recorded a maximum size of 318 cm total length (TL); female maturity (L<sub>50</sub>) at 189 cm TL; male maturity at 187 cm TL; size at birth 42-46 cm TL (Akhilesh et al. 2013). Reproduction is viviparous with litter sizes of 10-36 pups (Akhilesh et al. 2013). Age data are not available for the species, but generation length is estimated as 30 years following Ferretti and Buscher (2015, 2016).
Threats and conservation measures listed
Threats listed in assessment
Information pertaining to threats specific to the UAE are unavailable. In the Arabian Seas region, the major threat to the Bramble Shark is the rapid expansion of deepsea fisheries off western India, including a targeted gulper shark (Centrophorus spp.) fishery, and a deepsea shrimp trawl fishery which takes the species as bycatch. As marine fish stocks from nearshore waters off India are heavily exploited, it is likely that fisheries will continue to expand into deeper water.
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
329879
Taxon name
Carcharhinus amblyrhynchoides
(Whitley, 1934)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Carcharhinus amblyrhynchoides
(Whitley, 1934)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
carcharhiniformes
Family
carcharhinidae
Genus
Carcharhinus
Species
amblyrhynchoides
Species authority
(Whitley, 1934)
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Graceful Shark occurs throughout UAE inshore waters. It is often confused with the Blacktip Shark (Carcharhinus limbatus) and possibly the Spinner Shark (C. brevipinna), which introduces uncertainty when interpreting catch data. Little specific data are available for this species in the UAE. 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 in gill net, line and purse seine 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. This species faces intense fishing pressures throughout the Arabian Sea. Based on recorded levels of exploitation and decline in habitat quality, it is suspected to have declined by at least 30% over the past three generation lengths, or about 39 years. It is listed as Vulnerable 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 Graceful Shark occurs throughout UAE waters. Globally, it is widespread but patchy in the Indo-West Pacific (Last and Stevens 2009). This species is often confused with the Common Blacktip Shark (Carcharhinus limbatus) and possibly the Spinner Shark (C. brevipinna), which causes its distribution to be somewhat uncertain.
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 Graceful Shark is an inshore species that occurs on continental and insular shelves to a depth of 75 m (Ebert et al. 2013). It attains a maximum size of 243 cm total length (TL) (Jabado et al. 2015). Males mature about 140-177 cm TL and females at 167- 204 cm TL (Ebert et al. 2013, Jabado et al. 2015). Size at birth is probably 50-60 cm TL (Ebert et al. 2013). There are no age data available for this species, so generation length is inferred from the closely related Blacktip Shark (C. limbatus) from Indonesia at 13 years (Smart et al. 2015).
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 region have experienced high levels of disturbance and are quickly deteriorating due to major impacts from development activities (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
329876
Taxon name
Urogymnus asperrimus
(Bloch & Schneider,1801)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Urogymnus asperrimus
(Bloch & Schneider,1801)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Fishes
Kingdom
Animalia
Phylum
chordata
Class
chondrichthyes
Order
myliobatiformes
Family
dasyatidae
Genus
Urogymnus
Species
asperrimus
Species authority
(Bloch & Schneider,1801)
Taxonomic notes and synonyms listed
Formerly, U. asperrimus was the only species within Urogymmus. Last et al. (2016) added five more species to the genus.
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
A2cd
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
The Porcupine Ray occurs throughout UAE inshore waters, but is rarely observed. It is highly susceptible to a variety of fishing methods, and its life history characteristics cause it to be particularly susceptible to population decline in areas where fishing pressure is high. Significant declines of rays have been documented in parts of the Arabian Sea region (e.g., India), and the loss of coastal habitats across the region is also a concern. 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 at least 30% over the past three generation lengths, or about 64 years. It is listed as Vulnerable 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 Porcupine Whipray occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific.
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 occurrence of this species appears to be patchy with localized hotspots (Chin 2014). Juveniles appear to be site-attached, and highly resident to small areas of shallow coastal mud and mangrove habitats (Cerutti-Pereyra et al. 2014). It has been recorded from coral reefs, sandy reef lagoons, beaches, mud flats and mangroves, at depths of ~1 m to at least 30 m (O'Shea 2013, Cerutti-Pereyra et al. 2014, Chin 2014).The Porcupine Ray reaches a maximum size of at least 115 cm disc width (DW) with females mature by ~100 cm DW and males at ~90 cm DW (Last and Stevens 2009). Little else is known of the biology of this species. Attempts to collect size-at-age data from vertebral counts have proved difficult due to the fragile nature of vertebra (O'Shea 2013). Using data from the Brown Stingray (Dasyatis lata), a related species from the Pacific as a proxy, generation length for the Porcupine Ray is inferred to be 21.5 years (Dale and Holland 2012).
Threats and conservation measures listed
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. Its small litter size and schooling behaviour in inshore areas causes it to be susceptible to rapid population declines when experiencing intense fishing activity. 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.