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

Riparia riparia | UAE National Red List of Birds

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 occurs over open country and wetlands, including cultivations, parks or sewage treatment plants (Richardson 1990, Aspinall and Porter 2011). There is no information available about its feeding habits in the UAE; elsewhere it forages approximately 15 m above ground, feeding mainly on insects and spiders (Tucker and Heath 1994, Turner 2004). The species is migratory; it breeds between late April and August in Eurasia (Tucker and Heath 1994).
Taxon
Taxa
Riparia riparia | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Riparia riparia and R. diluta (del Hoyo and Collar 2016) were previously lumped as R. riparia following AERC TAC (2003), AOU (1998 and supplements), Cramp and Simmons;(1977-“1994), Dowsett and Forbes-Watson (1993), SACC (2005 and updates), Sibley and Monroe (1990, 1993), and Stotz et al. (1996).
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers are highest between August to May, when it is common over open land or waterbodies (Aspinall and Porter 2011, Pedersen et al. 2017). The species has been recorded in all months though (Pedersen et al. 2017).
Assessed status
Asessment status in full
Vulnerable
Assessment status abreviation
VU
Assessment status criteria
D1
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 has a relatively small non-breeding population within the UAE. On average, this would appear to even out at a level that would trigger Endangered under Criterion D, although accurately estimating the population size and trend of this species is hindered by its movement habits. A regional adjustment has been applied as it is deemed likely that a rescue effect from the wider breeding population could occur. Therefore, it is listed as Vulnerable under criterion D1.
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
Outside of the country, breeding sites are generally ephemeral and can often be lost through human activities (e.g. flood control, erosion control on rivers), and this could also be true for artificial sites where the species may occur within the UAE. Globally, the use of pesticides, causing declines in prey species, may impact the species (Tucker and Heath 1994), but this is not thought to be pertinent to the UAE. In Europe, it is often dependent on artificial breeding sites such as quarries (Turner 2004), however quarry work can adversely affect breeding, though workers often take measures to prevent this. In the past, droughts in wintering areas have caused severe large-scale population declines in western Europe (Tucker and Heath 1994, Turner 2004), and so this could be a further threat to the species within UAE.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Calandrella brachydactyla | UAE National Red List of Birds

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
During migration and winter, it is found in semi-desert plains (Jennings 2010, Aspinall and Porter 2011). During the breeding season, it favours lush vegetation, like cultivated and irrigated zones which experienced above average rainfall during the previous winter (Jennings 2010). During migration, it can form flocks of up to 5,000 individuals, which cross the country in April and August-November (Jennings 2010, Pedersen et al. 2017). It feeds on the ground and in low vegetation. There is no information available on its diet in the UAE, but elsewhere it feeds mainly on invertebrates, supplementing them with seeds and the green parts of plants (Jennings 2010). Little is known about its breeding biology in the UAE and Arabian Peninsula. The breeding period may last from March to June (Jennings 2010). Elsewhere, the nest is built by the female, of grasses, rootlets and similar vegetation, lined with softer material and placed in a shallow scrape on the ground, usually beside a shrub or grass tuft. It often has a small rampart of sticks or stones. Clutch size is about three eggs in Arabia (Jennings 2010).
Taxon
Taxa
Calandrella brachydactyla | (Leisler, 1814)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Calandrella brachydactyla and C. dukhunensis (del Hoyo and Collar 2016) were previously lumped into C. brachydactyla following AERC TAC (2003), Cramp et al. (1977-“1994), Dowsett and Forbes-Watson (1993), and Sibley and Monroe (1990, 1993).Closely related to C. cinerea, with which often previously merged, and to C. blanfordi, C. eremica and C. acutirostris; until recently considered conspecific with C. dukhunensis (see related note). Geographical variation slight and clinalà¢Ã¢â€šÂ¬becoming paler and greyer to E, more rufous and streaked above to Wà¢Ã¢â€šÂ¬but greatly complicated by strong influence of wear, considerable individual variation and lack of natural boundaries; described ranges of listed taxa somewhat arbitrary. We follow Donald and Alström (in prep) in treating Greater Short-toed Lark as monotypic, finding no support for the usually accepted subspecies woltersi, hungarica, hermonensis, rubiginosa, artemisiana and longipennis. Note that the breeding range does not extend so far east into Mongolia as previously thought, indeed it is unclear whether it occurs in Mongolia at all. The species is monotypic.
Taxon distribution as listed in assessment
The majority of occurrences of this species in the UAE are of migrating individuals on passage to and from the breeding sites. The abundance is highest in early April and in mid-August to November (Pedersen et al. 2017). It occasionally winters in the country, but numbers vary (Richardson 1990, Jennings 2010). It was thought to be likely that at least 5-20 pairs regularly breed in the country (Jennings 2010, Pedersen et al. 2017), but it is now believed that the species may no longer breed regularly in the UAE (R. Sheldon;in litt.;2019). Any remaining breeding population is still thought to be tiny, but there have been recent reports of individuals in suitable habitat in the breeding season.
Assessed status
Asessment status in full
Critically Endangered
Assessment status abreviation
CR
Assessment status criteria
D
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 has a small non-breeding population that would warrant a listing as Endangered under criterion D. However, the species is thought to have previously bred in the UAE, and the breeding status takes precedence here. Any remaining breeding population is still thought to be tiny, and there have been recent reports of individuals in suitable habitat in the breeding season. Therefore, the species is listed here as Critically Endangered under criterion D.
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
Within the UAE, predation by cats,;Felis catus,;has been noted to cause local declines on the Arabian Peninsula for Crested Lark (Symes;et al.;2015), and this is another possible threat to this species. Overgrazing outside of Protected Areas could also pose a threat. As a migratory species, individuals that over-winter in UAE but breed elsewhere may be subject to threats outside of the country too - although the scope and severity of impact on the UAE population is essentially unknown. From BirdLife International (2015), in Europe the main threats to the species are from agricultural intensification (leading to loss of fallows, increased number of irrigation schemes, increase in surface area covered by crops, etc.), afforestation of wastelands (de Juana;et al. 2012), and residential expansion (Tucker and Heath 1994).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Lanius excubitor | UAE National Red List of Birds

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 occurs in dry habitats with open wooded and thorn scrub areas (Jennings 2010, Aspinall and Porter 2011). Sparse and low vegetation is an important habitat characteristic for this species (Yosef and International Shrike Working Group 2016). It generally avoids narrow, enclosed areas such as wadis and hillsides, as well as cities (Jennings 2010). It prefers the same habitat type both during the breeding and the non-breeding season (Jennings 2010). It is closely associated with acacia scrub and only occurs where acacia is present (Jennings 2010). The species is a highly opportunistic feeder; it feeds principally on large insects and on small vertebrates such as rodents, particularly voles, but also small birds, lizards, amphibians and snakes (Lefranc and Worfolk 1997, Jennings 2010). Large items are broken down to transport and to swallow (Jennings 2010). Surplus food is stored on the thorns of acacia or other thorny plants, which are used as larders (Jennings 2010). The breeding period peaks in March to May, but breeding may start as early as November (Jennings 2010). The nest is an untidy structure with a loose foundation of twigs, grass, rootlets, string, lined with rootlets, feathers and hair. It is generally placed high above ground in a fork or on a lateral branch of a thorny bush or tree with thick foliage, preferably acacia (Jennings 2010). Clutches contain three to four, occasionally up to six eggs (Jennings 2010). In the UAE, up to three broods per season have been recorded (Jennings 2010).
Taxon
Taxa
Lanius excubitor | Linnaeus, 1758
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Lanius excubitor, L. borealis and L. meridionalis (del Hoyo and Collar 2016) were previously lumped as L. excubitor following AOU (1998 and supplements), Cramp and Simmons (1977-1994), Dowsett and Forbes-Watson (1993) and Sibley and Monroe (1990, 1993).
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are of breeding residents (L. e. aucheri), mainly in the northern and eastern part of the country (Jennings 2010, Pedersen et al. 2017). The UAE is also an important stop-over site for migrant individuals (L. e. pallidirostris) on passage from the breeding grounds in August-October (some of which over-winter), while a smaller number also visits the country on the way to the breeding grounds in March-April (Richardson 1990, Pedersen et al. 2017).
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 has a relatively large resident population in the UAE, which is thought to be increasing. Also in the wider Arabian Peninsula, the species is possibly increasing; thus, the potential for immigration from outside the UAE remains very high. Therefore, the species is listed as Least Concern at the national level.
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
Aspinall (1996) notes that increased pesticide use could have an impact on this species, although it is now thought that this will not be having an impact within the country.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Alauda arvensis | UAE National Red List of Birds

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 occurs in a variety of open habitats, including high and low grasslands, scrubland, cultivated fields, golf courses and large parks (Richardson 1990, Aspinall and Porter 2011). It avoids deserts (Richardson 1990). There is no information available about its diet in the UAE; elsewhere during winter, it is primarily herbivorous and feeds on seeds and other plant material (Donald and Garcia 2014). During winter, it forms flocks of more than 20 individuals (Richardson 1990). The species is migratory and breeds from late March to August and September throughout Eurasia.
Taxon
Taxa
Alauda arvensis | Linnaeus, 1758
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Alauda arvensis (AERC TAC [2003]; AOU [1998 and supplements]; Christidis and Boles [2008]; Cramp et al. [1977-1994]; Dowsett and Forbes-Watson [1993]; Sibley and Monroe [1990, 1993]; Turbott [1990]) and A. japonica (Sibley and Monroe [1990, 1993]) have been lumped into A. arvensis following del Hoyo and Collar (2016).
Taxon distribution as listed in assessment
The majority of occurrences of this species within the UAE are likely to be of wintering individuals (Pedersen et al. 2017). Numbers are highest in November to mid-March, when the species is fairly common in open areas near the coast (Richardson 1990, Pedersen et al. 2017). The species is rare in April and October (Pedersen et al. 2017). Individuals wintering in the UAE breed in north-eastern Europe and central Russia (Richardson 1990).
Assessed status
Asessment status in full
Endangered
Assessment status abreviation
EN
Assessment status criteria
D
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 has a very small non-breeding population. There was a suggestion that it was in decline in the late-1990s, but recent records instead suggest that the population is stable. The small population size does, however, mean it meets the threshold for listing as Endangered under criterion D.
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
Predation by cats,;Felis catus,;has been noted to cause local declines in Crested Larks on the Arabian Peninsula (Symes;et al.;2015), and it is plausible that this would be an potential threat to this species within the UAE. Overgrazing outside of Protected Areas could be be an additional threat within UAE.The main cause of global decline in this species is agricultural intensification. Recent research indicates the principal causes are changes in management of cereal-growing and grassland in its breeding range (leading to reduced nesting and foraging opportunities, and reduction of food resources [Donald and Garcia 2014]). In grasslands high fertiliser applications lead to vegetation that is too tall and dense for nesting. High hunting pressure in some countries poses an additional threat (Donald and Garcia 2014). However, it is uncertain to what extent these global threats impact the individuals that visit UAE, especially as records suggest the visiting population is stable (per R. Sheldon in litt. 2019).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
Off

Solanum virginianum | 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
Mahmoud et al. (2018) found the species in disturbed soil (without details). It may be tolerant of a range of conditions.
Taxon
Taxa
Solanum virginianum | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxonomic Notes
This species is a gene pool relative of Solanum melongena L. (CWR 2016).
Taxon distribution as listed in assessment
This species seems to be recently recorded for the UAE and appears to be scattered and widespread throughout the country. Sakkir et al. (2017) note that the species is known from offshore islands in Abu Dhabi Emirate, but without details. Mahmoud et al. (2018) recorded the species from eastern parts of the UAE, again without locality details. The native range of this species spans from north-east tropical Africa, through the Arabian Peninsula, to southern Iran and south-central China, Southeast Asia, and Japan (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
Solanum virginianum appears to have a widespread, although scattered, distribution throughout the UAE. In general, it prefers to grow in disturbed soils. As a result, it considered to be a relatively tolerant species and is not thought to face any major threats. Therefore, it is considered 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 do not appear to be any threats to this species, as it is able to tolerate disturbed areas.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Pseudotrapelus jensvindumi | 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 rocky areas, hills and mountains which range from well-vegetated wadis and slopes to barren, rocky hillsides (Gardner 2013). The species is found from sea level to 1,100 m asl.It is a diurnal species whose diet includes a wide range of invertebrates. The reproductive season is spring to summer, with females laying small clutches of three to five eggs.
Taxon
Taxa
Pseudotrapelus jensvindumi | Melnikov, Ananjeva & Papenfuss, 2013
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 is found from sea level to at least 1,100 m asl (Gardner 2013, Tamar et al. 2016, Burriel-Carranza et al. in press) in the Hajar Mountains with a disjunct record from the central valley of Jebel Hafeet.Globally, the species occurs throughout the Hajar Mountains from the Musandam Peninsula of Oman, United Arab Emirates, and south to Sharqiyah in Oman.
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
Pseudotrapelus jensvindumi within the United Arab Emirates is listed as Least Concern in view of its wide distribution, presumed large population and because it is unlikely to qualify for listing in a more threatened category. This taxon is not a non-breeding visitor, and it is assumed 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 not thought to be any widespread threats to this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Spratelloides delicatulus | 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 usually schools in inshore waters. It feeds mainly on crustaceans and has a maximum standard length of 7 cm (Whitehead 1985, Pillai et al. 1986). This species is short-lived (4-8 months) and spawns at 2-4 months of age (Milton et al. 1995).
Taxon
Taxa
Spratelloides delicatulus | (Bennett, 1832)
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. It is excluded from the Arabian Gulf. Globally, it is widespread in the Indo-West Pacific (Jones 1960, Whitehead 1985, Allen and Erdmann 2012). Its depth range is estimated to be 0-50 m.
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 the UAE, this inshore, pelagic species occurs only in the Sea of Oman. It is taken in fisheries at some level, but its population status is very poorly known; therefore, 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
The potential impacts from fishing are poorly understood.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Lavandula subnuda | 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
It is a perennial shrub species that grows on hillsides, ravines and summit cliffs (Jongbloed et al. 2003, Feulner et al. 2014, Mahmoud et al. 2018). It can grow up to 120 cm in height, has dissected leaves with round lobes and pale lavender-blue flowers which can be seen throughout the year (Jongbloed et al. 2003). This plant is often fed on by butterflies, including Chilades trochylus (Feulner 2014). It has also previously been recorded in the wild as heavily grazed when near by to goat herds (Feulner 2011).
Taxon
Taxa
Lavandula subnuda | Benth.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, it is known to be widespread across the Hajar Mountains and within the Ru'us al-Jibal (Jongbloed et al. 2003). It seems to grow between low to medium elevations and has been recorded up to 1250 m in the Ru'us al-Jibal (Feulner 2011). Globally, this species is native to the Gulf States and Oman (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 is assessed as Least Concern. Although grazing by goats may affect it, it appears to be generally widespread and common throughout the Ru'us al-Jibal and Hajar Mountains. In addition, it is known to occur in at least one protected area within its range.
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
Grazing by goats may threaten this species within some parts of its range (Feulner 2011).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Convolvulus ulicinus | 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
The species is primarily found on bedrock slopes (Feulner 2011). A perennial woody plant to 0.45 m in height (Jongbloed et al. 2003).
Taxon
Taxa
Convolvulus ulicinus | Boiss.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
In the UAE, this species is restricted to the Ru'us al-Jibal, where it is widespread but uncommon to rare at medium to high elevations, primarily from c.500 m asl (Feulner 2011). The global range of this species is through the eastern Arabian Peninsula (Oman to Qatar; Plants of the World online, 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
In the UAE, this species is restricted to the Ru'us al-Jibal, where it is widespread and characteristic of higher elevations, however it is rare, and the number of mature individuals may be below the threshold for a threatened category. Although it has a restricted distribution in the country, it may be resistant to grazing, and is considered 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
The plant is thought to be somewhat resistant to grazing pressure.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off

Cometes surattensis | 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 annual herb species is known to grow within fields in mountain environments (Mahmoud et al. 2018). It is also recorded from rocky slopes and wadis (Feulner 2016). Its basal leaves are spoon shaped, while the stem leaves are lance-shaped (Jongbloed et al. 2003). White flowers are visible between February and April and the fruit is a cylindrical capsule with small black seeds (Jongbloed et al. 2003).
Taxon
Taxa
Cometes surattensis | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Within the UAE, this species has been recorded from the Hajar Mountains, the Ru'us al-Jibal and Jebel Hafeet (Jongbloed et al. 2003). It is generally considered to occur at low elevations (Feulner 2011). Globally, the native range of this species spans from Sinai to India (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 is relatively widespread throughout the Hajar Mountain range in the UAE. In addition, it is considered to be locally common in its range and is known to occur in at least one protected area. It is therefore 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