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

Halodule uninervis | UAE National Red List of Vascular Plants

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
This is a sublittoral seagrass found from the mid-intertidal to a depth of 20 m. It is the least habitat-specific species of the seagrasses that occur in the UAE, being found in inter-tidal and sub-tidal zones, shallow sandy bays, in mangrove flats of fine mud and sand, in sheltered habitats with high levels of organic matter sediments, and in shallow open coast (EAD 2008). It is very fast growing, colonizes rapidly, and can flower prolifically, and some locations have very large seed banks. It can form dense meadows at some sites, whilst patchy and intermixed with other seagrass species (Short et al. 2010). In the Arabian Gulf, it tolerates extreme conditions with salinity varying from 38-70 ppt and temperatures of 10-“39'°C (inshore) and 19-33'°C (offshore; Short et al. 2010). Halodule uninervis is one of favoured foods of the Dugong and often heavily grazed (H.S. Das pers. comm. 2019).
Taxon
Taxa
Halodule uninervis | (Forssk.) Boiss.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Halodule pinifolia is sometimes confused with this species.
Taxon distribution as listed in assessment
This is the most common species of seagrass in the UAE. In the Arabian Gulf, there are large areas of this species in inshore areas and around most, if not all, islands in Abu Dhabi Emirate, from the Abu Dhabi Islands to Ra's Hanjurah, with a total area of c.55 km<sup>2</sup> estimated and representing c. 60% of seagrass bed content (EAD 2017); seagrass was found to be much more abundant in eastern Abu Dhabi, with the highest densities occurring north of Abu Dhabi Island around Al Samaliyah Island (EAD 2008). There is estimated to be around 4,000 km<sup>2</sup> of this species within Abu Dhabi Emirate (H.S. Das pers. comm. 2019). The species also occurs in Dubai Emirate, with records of extensive seagrass beds containing this species in the Jebel Ali area, particularly between Ras Hasyan and Ras Ghantoot, with their distribution primarily linked to areas of unconsolidated, deep sand (CBD 2016), and offshore from Jumeirah Beach. The species occurs eastwards to at least Umm Al Quwain. This species has a wide Indo-Pacific distribution. In the Pacific, it is found in southern Japan, Taiwan, the Philippines, Malaysia, Indonesia, throughout the Gulf of Thailand and along the coast of Vietnam and southern China. It occurs throughout insular Southeast Asia, northeast to the Northern Mariana Islands, Micronesia, and southeast to the Fiji Islands, as well as across northern Australia and the Great Barrier Reef. In the Indian Ocean, it is found from Geographe Bay in Western Australia extending across the Timor Sea, the south coast of Indonesia, and to the Andaman Sea and extending around the Bay of Bengal and around India to the Malabar Coast. It ranges from the Persian Gulf to the Red Sea, south to the east coast of South Africa to Madagascar and the islands of the western Indian Ocean.
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
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 is the most common species of seagrass in the UAE, where it occurs along the Arabian Gulf coast. Large areas of this species are found in inshore areas and around most, if not all, islands in Abu Dhabi Emirate, from the Abu Dhabi Islands to Ra's Hanjurah, extending eastwards to at least Umm Al Quwain. This species is susceptible to coastal development and water quality decline but can recover quickly if disturbance ceases and conditions improve. It is assessed as Least Concern.
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 particularly susceptible to coastal development but can recover quickly if disturbance ceases and conditions improve. It can also be affected by siltation and sedimentation (Short et al. 2010, Erftemeijer and Shuail 2012). In the UAE, the species is impacted by coastal dredging and land reclamation and development, fish trawling activities, oil spills and oil pollution, oil extraction developments, coastal water eutrophication and salinisation (from water desalination plants), siltation, and other forms of pollution (Erftemeijer and Shuail 2012). Given its shallow water habitat, this species may also be threatened by climate change and the associated increase in storm activity, water temperature, and/or sea-level rise (Short et al. 2010).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Halophila stipulacea | UAE National Red List of Vascular Plants

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
This perennial herb is a seagrass species (Norton et al. 2009, Phillips et al. 2002). It can grow at depths between 2-8 m (H.S. Das pers. comm. 2019).
Taxon
Taxa
Halophila stipulacea | (Forssk.) Asch.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species is known to occur along the Arabian Gulf coast (Phillips et al. 2002). The maximum AOO of this species is estimated to be under 2,000 km<sup>2</sup>, incorporating the area of this species found in Abu Dhabi and Ras al-Khaimah (H.S. Das pers. comm. 2019). Due to the occurrence of multiple seagrass meadows along the UAE coastline, there are estimated to be greater than ten threat-based locations. The native range of this species encompasses Egypt to India and the West Indian Ocean (Board of Trustees, RBG Kew 2019).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
B2ab(iii)
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 seagrass species occurs along the Arabian Gulf coastline of the UAE, in Abu Dhabi, Dubai and Ras al-Khaimah. The estimated AOO is under 2,000 km<sup>2</sup> and there are considered to be more than ten threat-based locations. Halophila stipulacea is currently undergoing a decline in the extent and quality of its habitat due to multiple threats including oil-related activities, pollution, dredging, coastal development and fishing culture. Therefore, this species is assessed as Near Threatened.
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 particularly susceptible to coastal development but can recover quickly if disturbance ceases and conditions improve. It can also be affected by siltation and sedimentation (Short et al. 2010, Erftemeijer and Shuail 2012). In the UAE, the species is impacted by coastal dredging and land reclamation and development, fish trawling activities, oil spills and oil pollution, oil extraction developments, coastal water eutrophication and salinisation (from water desalination plants), siltation, and other forms of pollution (Erftemeijer and Shuail 2012). Given its shallow water habitat, this species may also be threatened by climate change and the associated increase in storm activity, water temperature, and/or sea-level rise (Short et al. 2010).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
Coastal development within the UAE has been increasing in frequency and intensity since 1996, reducing the extent and quality of available habitat for this species.
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Indotyphlops braminus | 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
This fossorial species is a human commensal and found in and around human habitation, also in gardens, loose soil, refuse heaps, decaying logs and trees, gutters and drainage ditches, and under leaf litter, heaps of stones and piled up bricks, flower pots.
Taxon
Taxa
Indotyphlops braminus | (Daudin, 1803)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Reptiles
Assessed taxon level
Species
Taxonomic Notes
The species has also been recently placed in the typhlopid genera Typhlops and Typhlina (see Wallach 2009 for a complete synonymy). Following Wallach (2009), Typhlops khoratensis is considered a junior synonym of Indotyphlops braminus. Typhlops fletcheri has widely been treated as a junior synonym of Indotyphlops braminus, but examination of the holotype suggests that it is likely to represent a distinct species (A. Wynn pers. comm. to P. Uetz, in Uetz 2019). It is treated as valid (as I. fletcheri) without comment by Hedges et al. (2014), but as it has not been formally resurrected this account follows Pyron and Wallach (2014) in retaining it within I. braminus pending further taxonomic research.
Taxon distribution as listed in assessment
Within the United Arab Emirates, this species has been recorded from urban areas of Dubai (Gardner 2013, Burriel-Carranza et al. in press) and Abu Dhabi, where it is considered to be introduced. It occurs from sea level to 100 m asl. This species is native to tropical Asia (possibly Sri Lanka or southern India), but is invasive in many parts of the world and is now known from approximately 84 countries worldwide (Lever 2003, Wallach 2009). This cosmopolitan distribution includes Old World tropical and subtropical regions, with encroachment into the northern Hemisphere of the New World and adjacent temperate areas (Wallach 1999, 2009). It is found at a wide range of elevations.
Assessed status
Asessment status in full
Not Applicable
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
Within the United Arab Emirates, this species has only been recorded from Dubai and Abu Dhabi cities, where it is restricted to urban gardens. The species is considered Not Applicable for the UAE national Red List as a non-native introduction.
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 threats to this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Pomadasys argenteus | 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 inshore waters in open bays and estuaries (McKay 1984, 2001). It can also occur near reefs and occasionally mangroves. It spawns from mid May to early October and females spawn about six times in one season (Almatar et al. 2004). The maximum total length is 70 cm (Kuiter and Tonozuka 2001).
Taxon
Taxa
Pomadasys argenteus | (Forsskål, 1775)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Pomadasys argenteus was originally described as Sciaena argentea by Forsskål (1775) from Jeddah, Saudi Arabia, Red Sea.
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widespread in the Indo-West Pacific (Talwar and Jhingran 1991, al Sakaff and Esseen 1999, Bijukumar and Sushama 2000, Almatar et al. 2004, Rahman and Akhter 2009, B. Russell and Y. Iwatsuki pers. comm. 2013).
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 demersal, inshore species occurs throughout UAE waters. Catch declines have been recorded in both Abu Dhabi and on the eastern coast, but the cause of this decline is poorly understood. The status of population(s) outside the UAE are not well-understood, though declines have been reported from Kuwait. Based on the uncertainty regarding the population trend of this exploited species, it is listed as Data Deficient in UAE waters. Improvements in fisheries monitoring are needed.
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 potential major threat to this species. Corals in the UAE and Arabian Gulf have severely declined due to the increasing frequency of mass bleaching events caused by rising water temperatures, which is a consequence of climate change, as well as pervasive coastal development (Riegl et al. 2018, Burt et al. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Aegilops kotschyi | UAE National Red List of Vascular Plants

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
This species is a crop wild relative of wheat, Triticum aestivum (Kameswara Rao 2013). It is recorded as growing on rocky slopes of the Ru'us al-Jibal (Feulner 2011).
Taxon
Taxa
Aegilops kotschyi | Boiss.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Based on the interpretation of the bread wheat gene pool of van Slageren (1994), Aegilops kotschyi Boiss. is a secondary wild relative of Bread Wheat, Triticum aestivum L. subsp. aestivum, Durum Wheat, T. turgidum subsp. durum (Desf.) Husn., and a number of other cultivated wheats - including Emmer Wheat, T. turgidum subsp. dicoccon (Schrank) Thell., Einkorn Wheat, T. monococcum L. subsp. monococcum, Spelt, T. aestivum subsp. spelta (L.) Thell., and Sanduri Wheat, T. timopheevii (Zhuk.) Zhuk. subsp. timopheevii.
Taxon distribution as listed in assessment
Within the UAE, this species has been recently recorded from the Ru'us al-Jibal (Feulner 2011). It is thought to generally grow at high elevations within this area, between 1,200 and 1,350 m (Feulner 2011). Globally, this species' native range spans from Tunisia to Afghanistan (Board of Trustees, RBG Kew 2019).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
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 species occurs at high elevations within the Ru'us al-Jibal. Although it is not as common as other species in the north of this area, this may be due to being overlooked and as a result of occurring at particularly high altitudes. It is, however, described as locally common within the south of the region. As such, it is assessed as Least Concern.
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 is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Avena barbata | UAE National Red List of Vascular Plants

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
Avena barbata is a tall and thin grass (Jongbloed et al. 2003) known to occur in one site in the Ru'us al-Jibal in the UAE. Globally, Avena barbata has been reported to be very successful in undisturbed sites, preferring shallow stony hillsides, open parkland, pastures and cultivated land. It does not favour shrubby or forested sites (Duarte et al. 2011). In the UAE, it was found in silt amongst rock, on bedrock on ridge, c. 0.2 km above cultivation (Feulner 2011, G.R. Feulner pers. comm. 2019). This species is a crop wild relative of the oat crop, Avena sativa (Kameswara Rao 2013).
Taxon
Taxa
Avena barbata | Pott ex Link
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
Avena barbata Link is a secondary wild relative of oats, Avena sativa L. and A. byzantina K. Koch. (A. Katsiotis pers. comm. 2010). Five subspecies are native to Europe: A. barbata Link subsp. barbata, A. barbata subsp. castellana Romero Zarco, A. barbata subsp. hirtula (Lag.) Tab. Morais, A. barbata subsp. lusitanica (Tab. Morais) Romero Zarco and A. barbata subsp. wiestii (Steud.) Mansf.<span style=""background-color: yellow;""> (Valdés and Scholz; with contributions from Raab-Straube and Parolly 2009).<span style=""background-color: yellow;""><span style=""background-color: yellow;""><span style=""background-color: yellow;"">Romero Zarco (pers. comm. 2015) considers Avena saxatilis to be valid as a subspecies of Avena barbata (as Avena barbata subsp. castellana Romero Zarco), a situation that Euro+Med (2015, citing Valdés and Scholz 2009) agree with. Similarly, Loskutov and Rines (2011) consider A. saxatilis to be a form of Avena barbata. However, The Plant List (2015) considers Avena saxatilis to be a valid taxon).
Taxon distribution as listed in assessment
Avena barbata occurs in the Ru'us al-Jibal mountains in the north of the UAE (Jongbloed et al. 2003, Feulner 2011). Within this area, it has been recorded from one confirmed locality in the UAE at 900 m elevation, above bedrock on a ridge. A second record at 1,500 m elevation (Feulner 2011) may not be within the UAE. The origin and distribution of the species in the UAE requires confirmation; it may be native or be present here as a result of natural introduction, or may have been introduced alongside agriculture. Globally, this species occurs in northern, middle, east, south-east and south-west Europe, temperate Asia, Macaronesia, northern Africa and the Indian Subcontinent, and is naturalized in the Azores, Australia and the Americas (Duarte et al. 2011, Board of Trustees, RBG Kew 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 species is known from one site within the Ru'us al-Jibal. The species occurs at high elevations and are relatively undisturbed sites, which this plant appears to prefer. In addition, it is generally described as rare and detailed distribution data is lacking for this species. It would benefit from further research into its tolerance of threats, including disturbance, in addition to confirming its overall distribution in the UAE to be able to accurately assess it. For now, it is assessed as Data Deficient and further research is needed for this species.
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 is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Auxis rochei | 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 is a pelagic, oceanodromous species that forms schools. It is an offshore predator feeding on whatever abundant resource is available with a preference for planktonic crustaceans, small cephalopods, and fish larvae (Mostarda et al. 2007). Its maximum fork length is 50 cm. Longevity is 5 years and maturity occurs around 2 years of age or about 35 cm fork length for both males and females, but this can vary by region (Muthiah 1985, Yesaki and Arce 1994, Niiya 2001a, b, Collette 2010). When applying an age at first reproduction of 5 years and longevity of 2 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
Auxis rochei | (Risso, 1810)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Before 1960, many researchers thought that there was only one world-wide species in the genus Auxis, which was recorded as Auxis thazard (Collette and Aaland, 1996).The species contains two subspecies; A. rochei rochei (Risso, 1810) worldwide except for the eastern tropical Pacific where it is replaced by A. r. eudorax Collette and Aadland, 1996.
Taxon distribution as listed in assessment
In UAE waters, this species does not occur in the Arabian Gulf (B. Collette pers. comm. 2013), but may occur on the Sea of Oman coast, though records are not yet confirmed. Elsewhere, it is cosmopolitan in warm waters (Collette and Aadland 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 pelagic, open ocean species is not yet confirmed to occur in the UAE, but may occur on the Sea of Oman coast. If it does range into UAE waters (Sea of Oman only), its presence there is apparently marginal. There has been some confusion with Auxis thazard in some nearby areas where exploitation occurs (e.g., Iran), and this confusion may contribute to the lack of confirmed records in the UAE. 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 to this species in the UAE and neighboring area are poorly understood.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Thunnus tonggol | 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 pelagic species primarily occurs on the continental shelf, but can also occur in the open-ocean, and avoids very turbid waters and areas with reduced salinity such as estuaries. It may form schools of varying size. It feeds on a variety of fishes, cephalopods, and crustaceans, particularly stomatopod larvae and prawns. This species probably spawns more than once a year and is reported to be confined to coastal waters (Nishikawa and Ueyanagi 1991). Maximum fork length (FL) is 145 cm. Very few life history studies have been conducted, but in the Indian Ocean, longevity is about 20 years, males and females reach maturity at about 40 cm fork length and age at first maturity is not known (IOTC 2018). In Australia, longevity is estimated to be about 10 years (Wilson 1981), and age at first maturity in Thailand is estimated to be 2 years (Boonragsa 1987). It may live as long as 18 years in the central Indo-Pacific (Griffiths et al. 2009). Natural mortality in a study conducted across Iranian waters was 0.49 year<sup>-1</sup> (Darvishi et al. 2018).
Taxon
Taxa
Thunnus tonggol | (Bleeker, 1851)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, itis 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 pelagic species occurs throughout UAE waters, but may be less common there due to its preference for deeper waters such as areas off Iran. It is targeted by commercial fisheries that operate throughout the Indian Ocean, including the Gulf and Sea of Oman, and the Indian Ocean is considered a single stock by the Indian Ocean Tuna Commission (IOTC). According to the 2018 IOTC stock assessment, this species is overfished with overfishing occurring due to unsustainable fishing pressure. A recent assessment conducted off Iran also reported it as overfished. Catch has been declining since 2012, or over the past five years, but effort data are largely unavailable. In addition, the lack of life history studies prevents an estimation of generation length at this time. Conservation measures are likely insufficient to reduce fishing effort. Due to the lack of population and life history data, and acknowledging the ongoing major threat from overfishing across the Indian Ocean and in Iran, this species is listed as Data Deficient in the UAE. It is recommended to improve fisheries monitoring and determine generation length, specifically age at first maturity.
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 major threat to this species in the UAE in part due to its overfished status across the Indian Ocean stock, in which the Arabian Gulf and Sea of Oman are included (IOTC 2018).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Auxis thazard | 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 is a pelagic, oceanodromous species that is also epipelagic in neritic and oceanic waters (Collette 1995). Adults are coastal or near-coastal, while juveniles are more widely spread throughout the ocean. It feeds on small fish, squids, planktonic crustaceans (megalops), and stomatopod larvae. Its maximum fork length is 62 cm. Longevity is approximately 4 years (Muthiah 1985, Yesaki and Arce 1994, Collette 2010). In the southern Indian Ocean, spawning extends from August to April, north of the equator from January to April at sea surface temperatures of 24'°C or higher (Klawe 1963, Collette 2010).
Taxon
Taxa
Auxis thazard | (Lacepède, 1800)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Prior to 1960, many authors have used the name Auxis thazard as including Auxis rochei in the belief that there was only a single worldwide species of Auxis.
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Elsewhere, it is cosmopolitan in warm waters (Collette and Aadland 1996, Robertson and Allen 2015).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
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, open ocean and coastal species occurs throughout UAE waters. Fishing activity is not known to be causing declines in the UAE or in surrounding areas at this time. There are no known major threats; therefore, it is listed as Least Concern in the UAE.
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
Fishing activity is not known to be driving declines in the UAE at this time.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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Euthynnus affinis | 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 pelagic and oceanodromous species occurs in open waters, but always remains close to the shoreline. It is found to 50 m depth. The young may enter bays and harbours. It forms multi-species schools by size with other scombrid species, comprised of 100 to over 5,000 individuals. It is a highly opportunistic predator that feeds indiscriminately on small fishes, especially clupeoids and atherinids (Griffiths et al. 2009). Its maximum fork length is 100 cm. This species spawns extensively, both geographically and temporally, throughout its range (Schaefer 2001). Size at first maturity off Pakistan was 37.7 cm and longevity was about 9 years (Ahmed et al. 2015). A study conducted in Taiwan reported the age at first maturity to be 2 years (Chiou et al. 2004). Longevity has been estimated at 6 years (Landau 1965). When applying an age at first reproduction of 2 years and longevity of 6 years, its estimated generation length is 4 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
Euthynnus affinis | (Cantor, 1849)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, itis widely distributed in the tropical and sub-tropical Indo-West Pacific (Williams 1963, Collette 1984, Randall 1995, Rohit et al. 2012).
Assessed status
Asessment status in full
Least Concern
Assessment status abreviation
LC
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, open ocean and coastal species occurs throughout UAE waters. It is taken in fisheries in UAE, but is likely frequently confused with Auxis thazard. Its status in Iranian waters may impact the population that occurs in UAE waters, but this is not currently expected to be driving declines approaching a Near Threatened or threatened level at this time. There are no known major threats; therefore, it is listed as Least Concern in the UAE. It is recommended to improve species-specific fisheries data collection.
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
Overexploitation is a potential major threat in the Arabian Gulf, but declines are not expected to be approaching a threatened or Near Threatened level at this time.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

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