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

Lutjanus malabaricus | 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 a variety of benthic habitats on the continental shelf, including coastal and offshore reefs, shoal grounds and areas of flat bottom with occasional epibenthos or vertical relief (Newman 2002). It is associated with sponge and gorgonian-dominated habitats in parts of Australia (Sainsbury 1987). Juveniles tend to inhabit shallow inshore waters and seagrass beds (McPherson et al. 1988). It forages at night primarily for fish and benthic crustaceans, cephalopods and other benthic invertebrates (Kailola et al. 1993). Its maximum total length is 100 cm (Allen 1985). This species is relatively slow-growing and long-lived; estimated natural mortality is 0.112, longevity is 48 years, maximum fork length is 80.2 cm, males reach maturity at about 24 cm and females at 25-30 cm (Newman 2002, Fry and Milton 2009, Fry et al. 2009). Age at first sexual maturity is not known, but Lutjanus argentimaculatus, which is a species of similar biology with a somewhat smaller maximum size, matures at 14 years of age. When applying an age at first reproduction of 14 years and longevity of 48 years, its estimated generation length is 31 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
Lutjanus malabaricus | (Bloch & Schneider, 1801)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Some reports of this species may have been based on misidentifications of Lutjanus timoriensis.
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widely distributed in the Indo-West Pacific (Allen 1985, Newman 2002, Kim et al. 2012). Its depth range is 12 to 140 m (Anderson and Allen 2001, R. Myers pers. comm. 2015).
Assessed status
Asessment status in full
Critically Endangered
Assessment status abreviation
CR
Assessment status criteria
A2bcd
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 species inhabits a variety of coastal habitats, and occurs throughout UAE waters. It is heavily exploited and highly-valued throughout the Arabian Gulf and the UAE. Catch has declined by about 90% since 1985, or over the past generation length. The status of population(s) outside the UAE is not well-understood, but declines have been documented in Kuwait and Bahrain. Based on catch data and fish market observations, this species is inferred to have declined by at least 50-90% over the past generation length (about 31 years). Three generation lengths is about 75 years, but quantified data are not available to calculate a decline over this period. Considering this species is particularly long-lived and late to maturity, it is intrinsically susceptible to declines from overexploitation. Assuming that the population was stable previous to 1985, we suspect a decline of at least 80% with an expected continuing decline due to fishing effort trends. It is listed as Critically Endangered A2bcd.
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 Arabian Gulf, including the UAE (Al-Husaini et al. 2015). The inshore habitats that this species utilizes are seriously degraded in the UAE and elsewhere 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:

Verified entry
Off

Lutjanus lutjanus | 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 offshore coral reefs and trawling grounds. It is frequently encountered in large schools with other Lutjanus species (Lieske and Myers 1994), and feeds on fishes and crustaceans (Sommer et al. 1996). Its maximum size is about 30 cm, but more commonly to 20 cm and maturity is reached at 12 cm (Anderson and Allen 2001). The age at maturity is 1.1 years and the reproductive lifespan is estimated at 4.5 years (Martinez-Andrade 2003). The estimated maximum age is at least 11 years (Anderson and Allen 2001). When applying an age at first reproduction of 1.5 years and longevity of 11 years, its estimated generation length is 6.25 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Taxon
Taxa
Lutjanus lutjanus | Bloch, 1790
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxonomic Notes
Lutjanuslutjanus has been previously reported as L. lineolatus (Randall 2005).
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Globally, it is widely distributed in the Indo-West Pacific (Anderson and Allen 2001). Its depth range is 1 to 96 m.
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 reef-associated species occurs throughout UAE waters. Fishing activity is not known to be causing declines in the UAE. 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. 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
Off

Pristipomoides filamentosus | 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 benthopelagic, reef-associated species occurs over rocky bottoms (Sommer et al. 1996). At night, it migrates vertically to the upper part of its habitat to feed on small fishes, shrimps, crabs, amphipods, ascidians and salps (Opic et al. 1994, Anderson and Allen 2001). Its maximum total length is 100 cm (Anderson 1986), but more commonly occurs to 50 cm standard length (Anderson and Allen 2001). Female fork length at first maturity ranges from 36 to 38 cm (Mees 1993).The maximum reported age is 44 years (Andrews et al. 2012).
Taxon
Taxa
Pristipomoides filamentosus | (Valenciennes, 1830)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
In UAE waters, this species occurs only in the Sea of Oman. A report of this species occurring in the Arabian Gulf from Blegvad (1944) is questionable (Carpenter et al. 1997b). Globally, it is widely distributed in the Indo-Pacific (Anderson and Allen 2001, Williams et al. 2006). Its depth range is 40 to 360 m (Anderson and Allen 2001).
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
In UAE waters, this relatively deep-living, reef-associated species occurs only in the Sea of Oman. It is exploited in the UAE and surrounding waters of the Sea of Oman. Anecdotal observations reported by fishermen indicate catch of this species declined by about 80% over the past decade. The generation length is not known due in part to the lack of data on age at first maturity. In addition, fishing effort trends are poorly understood. Based on the concern for its population status in the face of possible ongoing overexploitation, and general lack of data, it is listed as Data Deficient. It is recommended to conduct life history studies and improve fisheries management.
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. 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
Off

Digera muricata | 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 an annual amaranth that grows up to 45 cm (Jongbloed et al. 2003). It produces pink flowers between February and April and grows in fields and along roads (Jongbloed et al. 2003).
Taxon
Taxa
Digera muricata | Mart.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
In the UAE, this species was recorded once near Al Ain (Jongbloed et al. 2003). Globally this species occurs in East Africa, Madagascar, the Arabian Peninsula, India, Pakistan and South-East Asia (Board of Trustees, RBG Kew 2019).
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 grows within urban and artificial habitats, such as roadsides and fields. As a result, this may make it more tolerant to urban expansion and land use change. However, as it is currently considered to be rare and is only known from one locality, more information is needed to be able to confidently assess this species. Therefore, it is currently 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
There is no information available.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Naucrates ductor | 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 occurs in oceanic waters. It has a semi-obligate commensalism with large sharks, rays, other fishes, turtles, ships, and driftwood. Juveniles are often associated with seaweeds and jellyfishes. Larvae are epipelagic in ocean waters. Prey items include host's food scraps and small invertebrates. The only available data on maximum age (three years) is based on a few specimens kept in captivity (Reñones et al. 1999). Maximum size attained is 63 cm fork length, but common to 35 cm (Smith-Vaniz 2016).
Taxon
Taxa
Naucrates ductor | (Linnaeus, 1758)
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, it is circumglobally distributed in tropical and subtropical waters (Smith-Vaniz 1984, Smith-Vaniz 1986b, Bauchot 1987, Smith-Vaniz 2002). Its depth range is 0-150 m (Humann and Deloach 1993).
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 inshore and offshore, pelagic speciesoccurs throughout UAE waters. Fishing activity is not expected to be causing population declines 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 approaching a Near Threatened or threatened level in the UAE at this time. Sharks and rays are in decline in the region, and this may impact this species as it has a commensal relationship with these species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Sphyraena barracuda | 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 is found on shallow reefs and deep reefs to the shelf-edge (Feitoza et al. 2005). Juveniles school in shallow waters over sandy, weedy bottoms and in mangroves. Young barracuda will spend their first summer in shallow nursery areas and move offshore to deeper water in late fall. In the second summer, young enter mangrove habitat or deeper weed beds. In its third year, it enters coral reef habitat (de Sylva 1963). Larger adults (>65cm standard length) are usually solitary and found over reef areas and offshore waters. Large schools have been observed and are probably associated with spawning behavior. Its maximum length is 200 cm (Robins and Ray 1986). It feeds mainly on littoral schooling and coral reef fishes, cephalopods, and shrimps (de Sylva 1981, Cervigon 1993). It can reach at least 14 years of age. Males mature by year three, and females by year four. Off Abu Dhabi, the mean age and size at sexual maturity for males was 1.3 years and 56.2 cm and 2.6 years and 80.1 cm for females (Grandcourt et al. 2012). When applying an age at first reproduction of 2.5 years and longevity of 14 years, its estimated generation length is 8.25 years based on the following equation recommended by the IUCN Red List methods: Age at first reproduction + (Age at last reproduction -“ age at first reproduction)/2.
Taxon
Taxa
Sphyraena barracuda | (Edwards, 1771)
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, it is nearly circumglobally distributed in tropical to warm temperate waters, but does not occur in the eastern Pacific (Carpenter et al. 1997b, Russell 2002, Simon et al. 2013, Friedlander et al. 2014, Wirtz et al. 2014). It occurs mainly at the surface, but can be found to 100 m depth (Russell 2016).
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, coastal species occurs throughout UAE waters. Catch in Abu Dhabi has declined by 96% since 2011, and the cause of this decline is not known. Due to concerns for its population status, it is listed as Data Deficient in the UAE. Studies are needed to estimate life history parameters (age at sexual maturity and longevity) to calculate generation length. Improvements in fisheries management is also 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. 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
Off

Selar crumenophthalmus | 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 forms large inshore schools, usually in shallow waters (Smith-Vaniz 1984). It also occurs over shallow reefs or in turbid water. It can be associated with Whale Sharks (W. Smith-Vaniz pers. comm. 2013). Maximum size is to 27 cm standard length, but is common to ~24 cm fork length (Smith-Vaniz 2002). It feeds mostly at night on large planktonic animals; juveniles feed mostly on crustaceans (euphasiids, decapods) and adults are active predators of fish larvae and early juveniles (Roux and Conand 2000). In Hawaii, size at maturity is <20 cm standard length (Clarke and Privitera 1995). Its life cycle is rapid and short (Roos et al. 2007).
Taxon
Taxa
Selar crumenophthalmus | (Bloch, 1793)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs throughout UAE waters. Elsewhere, it is circumglobally distributed in tropical and subtropical waters (Simon et al. 2013, Wirtz et al. 2014). Its depth range is 1-170 m.
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 inshore and offshore, pelagic speciesis common in parts of UAE waters. Fishing activity is not expected to be causing population declines 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. 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
Off

Decapterus macarellus | 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 schools in open water, occasionally over outer reefs and frequently around islands. It feeds primarily on zooplankton (Cervigón et al. 1992, Smith-Vaniz 1995). The maximum size is 46 cm total length, and is common to about 25 cm fork length (Smith-Vaniz 2002, Jiménez and Béarez 2004). In Japan, the length at 50% maturity of females was estimated at 25.8 cm and age at maturity at two years old (Shiraishi et al. 2010). In Cape Verde, length at first maturity is 22 cm (Monteiro pers. comm. 2012).
Taxon
Taxa
Decapterus macarellus | (Cuvier, 1833)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Fishes
Assessed taxon level
Species
Taxon distribution as listed in assessment
In the UAE, this species occurs only in the Sea of Oman. It is excluded from the Arabian Gulf. Elsewhere, it is circumglobally distributed in tropical waters (Smith-Vaniz 1986, Smith-Vaniz 2002, Simon et al. 2013). The depth range is 1-400 m, but is more common from 0-200 m (Smith-Vaniz 1986, Mundy 2005).
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 speciesoccurs in UAE waters only in the Sea of Oman. Fishing activity is not expected to be causing population declines 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. 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
Off

Crenimugil seheli | 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 schools in shallow coastal waters, and is known to enter lagoons, estuaries, and freshwater rivers to feed. Mass shoaling takes place at sea during spawning. It consumes various algae, diatoms, foraminiferans, and detritus associated with sand and mud (Harrison and Senou 1999). The maximum total length is 60 cm (Lieske and Myers 1994). Spawning occurs from February to April in the southern Arabian Gulf, age and size at sexual maturity for males and females are 4.5 years and 38 cm and 4 years and 41.8 cm, respectively, and the maximum age is 9 years (Grandcourt et al. 2010). When applying an age at first reproduction of 4 years and longevity of 9 years, its estimated generation length is 6.5 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
Crenimugil seheli | (Forsskål, 1775)
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). This species is commonly referred to as Valamugil seheli in the literature. According to Eschmeyer's Catalog of Fishes, it is now valid as Crenimugil seheli.
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, and the stock in Abu Dhabi was considered fully exploited as of 2010. Since 2007, or over the past 11 years (approximately 1.5 generation lengths), catch declined by about 86%. Fishing effort trends are not well-understood. It is also exploited in areas neighboring the UAE. An updated stock assessment is expected to occur in 2020, and until then, the status of its population in the UAE is poorly understood; 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
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Juncus rigidus | 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?
Incomplete
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species is a perennial rush species with creeping rhizome, found in intertidal salt marshes, wadi streams and in permanent pools. It also sometimes grows on waste ground and in disturbed areas. The flowering period is from March to June (Jongbloed et al. 2003).
Taxon
Taxa
Juncus rigidus | Desf.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
The species has a mostly coastal distribution in the UAE (Jongbloed et al. 2003), with localised populations in salt marshes, streams in wadis and permanent pools (Karim and Dakheel 2006). It has been recorded from islands off Abu Dhabi northwards to Rams (Ra's al-Khaimah) e.g., at Khor Hulaylah (Llewellyn-Smith 2011). Feulner (2016) records the species from wet wadis of the Hajar Mountains but noted that it is largely absent from Shimayliyah and from the east side of the mountains in the UAE, including Wadi Wurayah National Park (Feulner 2011), although found north of the Masafi area and as far north as tributaries of Wadi Fa'y, on the southern edge of the Ru'us al-Jibal. G. Feulner (in litt. MEW 2010) that the two main areas where the species is found are Khor Hulaylah and the Abu Dhabi islands. According to participants of the National UAE Red List Workshop (15th-19th September 2019, Dubai), this species also occurs in Wadi Siji and Sharjah. J. rigidus and J. socotranus are easily confused, and confirmation of the identity of records of J. rigidus from the mountains is required. Globally, the species occurs throughout much of Africa, including Mediterranean countries, as well as scattered localities on the northern Mediterranean coast and islands, and east through the Arabian Peninsula and Asia Minor to Pakistan (Board of Trustees, RBG Kew 2019). There are also two records from Ras al-Khaimah within the RBGE Edinburgh collections.
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
The species has a mostly coastal distribution in the UAE, including islands, from Abu Dhabi to Ra's al-Khaimah. It is also found in the Hajar Mountains, although largely absent from the eastern side of the Hajar Mountains, with localised populations in salt marshes, streams in wadis and permanent pools. Although coastal populations, especially in Abu Dhabi, will have been impacted by intensive urban development, it is not thought that levels of decline will be such as to qualify for a threatened category, and the species occurs in more than ten locations. The species is assessed as Least Concern, however, monitoring of the larger coastal populations is required.
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
Subpopulations are inferred to be declining as a result of the transformation of coastal habitats.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off