United Arab Emirates

Official name
United Arab Emirates
ISO alpha-2 code
AE
ISO alpha-3 code
ARE
ISO numeric-3 code
784
Continent
Asia

Neophocaena phocaenoides | UAE National Red List of Mammals: Marine and Terrestrial

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
The shallow channels between sandbanks and mangrove-lined islands, typical of western UAE waters, are apparently a favoured habitat. It has been seen close to shore off Dubai. Throughout its range, the Indo-Pacific Finless Porpoise favours shallow inshore waters, including mangrove areas, lagoons and estuaries (Pilleri and Gihr 1974, Reeves et al. 1997, Aspinall and Baldwin 1999, Preen 2004, Jefferson and Hung 2004) and this makes it particularly vulnerable to bycatch and anthropogenic impacts (Collins et al. 2005).
Taxon
Taxa
Neophocaena phocaenoides | (G. Cuvier, 1829)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Mammals
Assessed taxon level
Species
Taxonomic Notes
The recognition of two externally distinct morphological forms of Finless Porpoises as separate biological species, the Indo-Pacific Finless Porpoise (Neophocaena phocaenoides) and the Narrow-ridged Finless Porpoise (N. asiaeorientalis), was accepted only recently when it was demonstrated that the two forms are reproductively isolated (and likely have been separated since the last glacial maximum) even though they occur sympatrically in a fairly large area of eastern Asia (Wang et al. 2008, Jefferson and Wang 2011). [Much of the literature published before ca 2010 refers to all Finless Porpoises (both species) as N. phocaenoides.] Differences in the external morphology of the dorsal aspect of the two species are distinguishable even amongst free-ranging animals (as opposed to only specimens in-hand) (Wang et al. 2010). Intermediates between the two main forms have never been reported even though several hundreds to thousands of carcasses have been examined. The two species also clearly differ in craniometry (Amano et al. 1992, Jefferson 2002). There is evidence to suggest subpopulation structure within Indo-Pacific Finless Porpoises in some areas (Jefferson 2002, Yang et al. 2008, Chen et al. 2010, Xu et al. 2010, Li et al. 2011, Ju et al. 2012, L. Li et al. 2013, S. Li et al. 2013, Jia et al. 2014, Lin et al. 2014) and this may apply throughout much of the species' distribution.
Taxon distribution as listed in assessment
All UAE records, apart from several from Dubai, are from the waters off western Abu Dhabi, with concentrations in the Marawah Island and Sila'a areas (Aspinall and Baldwin 1999). Collins et al. (2005) considered there to be a more or less contiguous distribution along the western and southern margins of the Arabian Gulf. Globally, the species occurs in a narrow strip of shallow (usually (<) 50 m deep) coastal marine waters, as well as some river mouths and estuaries, around the northern rim of the Indian and western Pacific Oceans eastwards to Indonesia and north to central Chinese waters (Wang and Reeves 2017).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
A2bc; C2a(i); D
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
Preen (2004) reported a 71% decline in small species of dolphins in the Arabian Gulf from 1986 to 1999, which included this species. There is no information available on decline rates in the individual species, so based on the assumption that they all declined equally it appears reasonable to infer a population reduction of &gt;50% for Neophocaena phocaenoides over the past three generations (45 years). The species, therefore, qualifies for assessment as Endangered (EN) under criterion A2bc. The reduction was due to a combination of pressures including declining habitat quality because of increasing coastal development, bycatch, collision with boats and declines in fish stocks. The decline is continuing but it is not possible to say if it is at the same rate. The species also qualifies for listing as EN under criterion C2a(i) and under criterion D as the population size is less than 250 mature individuals. The species might qualify for listing as Critically Endangered under criterion C2a(ii) if it is determined that the UAE animals are a single subpopulation. There is no rescue effect, as the species does not move that far; the species tends to be very localised in its occurrence.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
The main threats to cetaceans in UAE waters include: incidental mortality in trawl and drift nets, depletion of prey populations (due in part to commercial overfishing); ship and boat strikes, offshore oil and gas exploration; noise from shipping, submarine sonar and oil and gas rigs. A UAE Fisheries Resource Assessment Survey in 2002 found that fish stocks in the Gulf had declined by 60%. Inshore and shallow-water species are further threatened by entanglement in abandoned fishing gear; coastal development including port and harbour construction, dredging, land reclamation, residential and tourist development; pollution (oil and hydrocarbons) and damage to feeding grounds in seagrass beds and reefs. During surveys by EAD, a large number of dolphins were observed with scars that were attributed to propeller cuts, indicating that vessel strike is a major threat to dolphin populations in Abu Dhabi waters (EAD 2015). A lack of information on most species (e.g. population size and trend, the location of critical areas, and feeding ecology) hinders the development of appropriate conservation actions.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
Hornby (1996) assessed the species as Critically Endangered. It is not clear what criteria would have been used in 1996, but likely to have been assessed under criteria different than those currently applied by IUCN, and we consider Endangered to be the appropriate backcasted category in 1996 (under criteria A2bc; C2a(i); D), as it appears that Hornby was not aware of the declines in the species between 1986 and 1999 as reported by Preen (2004).
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Seriola dumerili | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This epibenthic and pelagic species occurs over reefs or at deep offshore holes or drop-offs, usually in small or moderate-sized schools, but may be solitary (Smith-Vaniz 2002). It is also found over rocky outcrops and wrecks (Harris et al. 2007). Juveniles associate with Sargassum or flotsam in oceanic and offshore neritic waters (Bortone et al. 1977). Prey items include fish, invertebrates and sometimes live, dead, and artificial bait. Its maximum size is 188 cm total length, but common to about 70-110 cm fork length (Smith-Vaniz 2002). The fork length at 50% maturity is 64.6 cm for males and 73.3 cm for females. Several studies have estimated the maximum age using methods of varying accuracy, and in general, this fish is considered difficult to age (SEDAR9 2011). Estimates of maximum longevity range from 10-17 years, but an age of 15 years was used for this assessment as described in SEDAR33 (2014). This species is assumed to be fully mature by age two (SEDAR33 2014). The Hoenig maximum age natural mortality estimator recommended by the SEDAR33 (2014) is 0.28 year<sup>-1</sup>; however, it is unlikely that this parameter remains constant across all sizes and ages.The generation length was estimated to be 6 years using the equation 1/natural mortality + age of first reproduction. Using the equation age of first reproduction + [z * (length of the reproductive period)] where z = 0.5, generation length was estimated at 7 years. Therefore, the median of 6.5 years is applied.
Taxon
Taxa
Seriola dumerili | (Risso, 1810)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
This species is commonly misidentified as Seriola rivoliana and S. carpenteri, making market data unreliable (W. Smith-Vaniz pers. comm. 2013).
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Elsewhere, it is circumglobally distributed except for the eastern Pacific (Smith-Vaniz 1984, Smith-Vaniz 2002).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This pelagic species occurs throughout UAE waters. It is a minor component of handline and trap fisheries off Abu Dhabi, but is considered valuable and highly desirable by commercial and recreational fishers. Catch in Abu Dhabi declined by about 80-90% over the past two generation lengths (about 12 years), but there is uncertainty associated with the effort trends, and catch in the recreational fishery are not recorded. Anecdotal observations of its presence in fish markets indicate it has declined on the eastern coast of the UAE. The status of population(s) outside the UAE is not well-understood, though it is also taken by fisheries elsewhere. Based on the uncertainty regarding the population trend of this exploited species, it is listed as Data Deficient in UAE waters until updated data become available. Improvements in fisheries monitoring are needed.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Exploitation is a potential major threat to this species in the UAE. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Trapelus flavimaculatus | UAE National Red List of Herpetofauna: Amphibians & Terrestrial Reptiles, Sea Snakes & Marine Turtles

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
The species is found in open areas, where it basks in the branches of small Acacia and Prosopis trees, and on the ground in sandy areas. In the United Arab Emirates, this species occurs on stable sand and gravelly surfaces, usually with bushes and shrubs, on which it is found sunning itself (Arnold 1980, Gardner 2013). The species is also found in urban and rural gardens. In disturbed areas, heaps of stones and earth may be used for sunning (Arnold 1980). The breeding season is spring and summer. The females lay four to six eggs.
Taxon
Taxa
Trapelus flavimaculatus | Rüppell, 1835
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxon distribution as listed in assessment
In the United Arab Emirates, this species has been recorded from the Sila area through the coastal deserts of Abu Dhabi to Ras Al Khaimah, and further inland around Sweihan and Al Ain (Gardner 2013, Burriel-Carranza et al. in press). The species has also been recorded along the east coast of the United Arab Emirates but is absent from the Hajar Mountains. The species is found from sea level to 400 m asl.This species is present in Saudi Arabia, Oman, Yemen, United Arab Emirates, Qatar, Bahrain and Kuwait.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
About the assessment
Assessment year
2018
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
Trapelus flavimaculatus is listed as Least Concern in view of its wide distribution within the UAE, presumed large population, and because it is unlikely to be declining fast enough to qualify for listing in a more threatened category. This taxon is not a non-breeding visitor, and it is presumed that any immigration from populations outside the UAE is not significant, and therefore there is no adjustment to the Category according to the IUCN regional and national Guidelines (IUCN 2012).
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
There are no widespread threats to this species, but there will be localised impacts from development, to which its habitat is particularly susceptible.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Moolgarda cunnesius | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species inhabits inshore marine, brackish and freshwater areas, including coral reefs, mangroves and estuaries (Khatoon et al. 2014, Kamrani et al. 2016, Jawad et al. 2018). Its maximum length is 14 cm (Carpenter et al. 1997b).
Taxon
Taxa
Moolgarda cunnesius | (Valenciennes, 1836)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
The taxonomy of species in the Mugilidae family is complex and under revision (Durand and Borsa 2015). According to Eschmeyer's Catalog of Fishes, this species is now considered valid as Moolgarda cunnesius.
Taxon distribution as listed in assessment
This species occurs throughout UAE waters (Carpenter et al. 1997b, Jawad et al. 2018). Elsewhere, it is widespread in the Indo-Pacific. Its depth range is 0-3 metres, but has been recorded to 42 m (Jawad et al. 2018).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This inshore species occurs throughout UAE waters. It is exploited throughout the UAE, but species-specific catch data are not collected. It comprises a smaller proportion of the mullet catch than Crenimugil seheli, but catch in that fishery declined by about 80% over the past 11 years. Fishing effort trends are not well-understood. It is also exploited in areas neighbouring the UAE. In addition, the difficulty in distinguishing the mullet species taxonomically and easy confusion with other mullet species in the catch prevents an understanding of their status. Based on the uncertainty in the status of its population in the UAE, and concerns for possible over-exploitation, it is listed as Data Deficient. Improvements in fisheries monitoring are needed.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Overfishing is a potential major threat to this species in the UAE and surrounding areas. In addition, estuaries and nearshore habitats have been seriously degraded in the Arabian Gulf region. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Ellochelon vaigiensis | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species is found in coastal waters in lagoons, marshes, mangroves, estuaries and brackish waters of rivers, as well as reef flats. It spawns at sea and its maximum length is 63 cm (Harrison and Senou 1999, Coad 2017).
Taxon
Taxa
Ellochelon vaigiensis | (Quoy & Gaimard, 1825)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
The taxonomy of species in the Mugilidae family is complex and under revision (Durand and Borsa 2015).
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widely distributed in the Indo-West Pacific (Harrison and Senou 1999).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This inshore species occurs throughout UAE waters. It is exploited throughout the UAE, but species-specific catch data are not collected. It comprises a smaller proportion of the mullet catch than Crenimugil seheli, but catch in that fishery declined by about 80% over the past 11 years. Fishing effort trends are not well-understood. It is also exploited in areas neighboring the UAE. In addition, the difficulty in distinguishing the mullet species taxonomically and easy confusion with other mullet species in the catch prevents an understanding of their status. Based on the uncertainty in the status of its population in the UAE, and concerns for possible overexploitation, it is listed as Data Deficient. Improvements in fisheries monitoring are needed.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Overfishing is a potential major threat to this species in the UAE and surrounding areas. In addition, estuaries and nearshore habitats have been seriously degraded in the Arabian Gulf region. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Planiliza subviridis | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species inhabits coastal waters in lagoons, marshes, estuaries and lower courses of rivers and spawns at sea (Thomson and Luther 1984). It consumes detritus and benthic algae (Carpenter et al. 1997b). The maximum standard length is 40 cm (Harrison and Senou 1999).
Taxon
Taxa
Planiliza subviridis | (Valenciennes, 1836)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
The taxonomy of species in the Mugilidae family is complex and under revision (Durand and Borsa 2015). The family comprises of seven lineages which radiated early on, and many of its genera are paraphyletic or polyphyletic (Durand et al. 2012).This species has many synonyms, with over 280 specific names having been assigned to mullets of the Mugilidae family (Thomson 1997). There is a long history of confusion between the populations assigned these names (Ogilby 1908), and many of these have now been recognised as synonyms in the past 120 years (Thomson 1997).
Taxon distribution as listed in assessment
This species may occur throughout UAE waters, but records are not yet confirmed. Globally, it is widely distributed in the Indo-West Pacific.
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This inshore and estuarine species is not yet confirmed from UAE waters, but may occur there. Confusion with other mullet species contributes to this uncertainty. It is likely impacted by habitat loss from coastal development and cessation of rivers in the Arabian Gulf region. It is taken in fisheries, but it not thought to be as heavily exploited as Liza klunzingeri. It is listed as Data Deficient.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
This species is likely impacted by habitat loss from cessation of rivers and coastal development in the Arabian Gulf. It is not thought to be as heavily exploited as Liza klunzingeri, so it is not suspected that overfishing is a major threat in the UAE at this time.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Planiliza persica | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species inhabits shallow coastal waters (Carpenter et al. 1997b). It feeds on detritus, algae, and small benthic invertebrates. The maximum total length is 30 cm (Randall 1995, Senou et al. 1996).
Taxon
Taxa
Planiliza persica | (Senou, Randall & Okiyama, 1995)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
The taxonomy of species in the Mugilidae family is complex and under revision (Durand and Borsa 2015).
Taxon distribution as listed in assessment
In UAE waters, this species is only known from juvenile records taken off Dubai (N. Cordero Deatras pers. comm. 2019). On the global-level, it is only known from records taken off Bahrain and Qatar in the Arabian Gulf (Randall 1995, Senou et al. 1996).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This coastal species is only known from juvenile specimens collected in Dubai Creek in the UAE on the Arabian Gulf coast. It is taken in fisheries and the only confirmed specimens on a global-level were collected from Qatar and Bahrain in the 1970s and 1980s. It is listed as Data Deficient.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Threats are unknown. Overfishing may be a potential threat.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Planiliza klunzingeri | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species inhabits inshore waters and ascends rivers for feeding (M. Almukhtar pers. comm. 2014). It consumes detritus, algae, and small benthic invertebrates (Carpenter et al. 1997). It spawns from December to May in the Arabian Gulf, with a peak in December and the mean length at 50% sexual maturity is 15.4 cm (Elahi et al. 2012). The maximum length is 20 cm (Carpenter et al. 1997), age at first reproduction is about 2 years (Hakimelahi et al. 2010) and maximum age is about 5 years (M. Al-Husaini pers. comm. 2014). When applying an age at first reproduction of 2 years and longevity of 5 years, its estimated generation length is 3.5 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Taxon
Taxa
Planiliza klunzingeri | (Day, 1888)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
The taxonomy of species in the Mugilidae family is complex and under revision (Durand and Borsa 2015).
Taxon distribution as listed in assessment
In UAE waters, this species occurs on the Sea of Oman coast, but its presence on the Arabian Gulf coast is not yet confirmed, in part due to confusion with other mullet species. Globally, it is restricted to the northern Indian Ocean where it occurs from the Arabian Gulf to India (Randall 1995).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This inshore and estuarine species is not yet confirmed to occur in UAE Arabian Gulf waters, but has been detected in mullet fisheries catch on the Sea of Oman coast. It rarely occurs in the catch, and its population status there is very poorly understood. In addition, the difficulty in distinguishing the mullet species taxonomically and easy confusion with other mullet species in the catch prevents an understanding of their status. It is a commercially important species elsewhere in the Arabian Gulf, and overfishing is considered to have contributed to declines. In addition, habitat loss due to cessation of rivers and coastal development in the Gulf has also caused declines. The status of population(s) outside the UAE is not well-understood, but declines have been recorded in Kuwait, Iran and Bahrain. Little is known on its distribution and population status in UAE waters; therefore, it is listed as Data Deficient. Improvements in fisheries monitoring are needed.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Major threats to this species in the Arabian Gulf include overfishing and habitat loss due to cessation of rivers and coastal development (E. Abdulqader, F. Kaymaram, J. Bishop, K. Al-Khalaf, M. Al-Husaini, M. Almukhtar, Q. Alghawzi, S. Alam, and S. Hartmann pers. comm. 2014).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Planiliza carinata | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species inhabits coastal marine waters, and can enter rivers, and unlike Liza klunzingeri, it is rarely found in El Hammar Marsh in Iraq.
Taxon
Taxa
Planiliza carinata | (Valenciennes, 1836)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
The taxonomy of species in the Mugilidae family is complex and under revision (Durand and Borsa 2015).
Taxon distribution as listed in assessment
This species is not yet confirmed from UAE waters, but may occur there. Globally, it is widely distributed in the Indo-West Pacific (Masuda et al. 1984).
Assessed status
Asessment status in full
Data deficient
Assessment status abreviation
DD
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This inshore and estuarine species is not yet confirmed to occur in UAE waters, but may occur there. It is easily confused with Planiliza klunzingeri, and would be taken at some level in mixed mullet landings along with this species. It is listed as Data Deficient.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
This species is likely experiencing the same threats as Liza klunzingeri, which declined by about 40-50% over the past 10 years due to exploitation and habitat loss caused by cessation of rivers and coastal development, but few data exist as it has been historically confused with this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Rhinoptera jayakari | UAE National Red List of Marine Species: Reef-building corals, cartilaginous fishes and select bony fishes

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
Yes
Habitat
Habitat details as listed in assessment
This species is benthopelagic over the continental shelf, often close inshore, usually forming very large aggregations (Last et al. 2016). It reaches at least 90 cm disc width (DW) (Last et al. 2016). Litter size is 1 pup per litter (R. W. Jabado unpubl. data), but it is unknown if reproductive periodicity is annual or biennial. Generation length is estimated to be ~10 years based on the larger (110 cm DW) R. bonasus (Fisher et al. 2013).
Taxon
Taxa
Rhinoptera jayakari | Boulenger, 1895
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
The Oman Cownose Ray occurs throughout UAE waters. Globally, it has a wide range throughout the Indo-West Pacific (Bogorodsky et al. 2014, Spaet and Berumen 2015, Last et al. 2016).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
A2d
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
The Oman Cownose Ray occurs throughout UAE coastal waters, and may be common there. Due to confusion with the Javanese Cownose Ray (Rhinoptera javanica), population data can be uncertain, but it is suspected this species is the more common 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 30 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.
Criteria system
Criteria system specifics
IUCN v3.1
Criteria system used
IUCN
Criteria Citation
IUCN. 2012. IUCN Red List Categories and Criteria: Version 3.1, Second edition. IUCN, Gland, Switzerland and Cambridge, UK. iv + 32pp pp. And IUCN. 2012. Guidelines for Application of IUCN Red List Criteria at Regional and National Levels: Version 4.0. Gland, Switzerland and Cambridge, UK: IUCN. iii + 41pp.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
This species has been impacted by fisheries in the UAE and across its broader range. Marine habitats in the Arabian Gulf region have experienced high levels of disturbance and are quickly deteriorating due to major impacts from development activities (Sheppard et al. 2010).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off