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

Anas platyrhynchos | 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
In the UAE, this species is most often found at estuaries, ponds, reservoirs, creeks, lagoons and water treatment plants (Richardson 1990, Aspinall and Porter 2011). It requires water less than 1 m deep for foraging (Snow and Perrins 1998). There is no information available about its diet in the UAE. In general, the species is omnivorous and opportunistic, feeding by dabbling in water and by grazing on the land (del Hoyo et al. 1992, Snow and Perrins 1998). Elsewhere, its diet consists of seeds and the vegetative parts of aquatic and terrestrial plants, as well as terrestrial and aquatic invertebrates such as insects, molluscs, crustaceans, worms and occasionally amphibians and fish (del Hoyo et al. 1992). The non-breeding population native to the UAE is migratory, leaving its breeding grounds in the western Palaeartic in September/October and returning in February/March (Richardson 1990). During migration and in winter, the species can be found in small to very large flocks numbering up to several hundred of individuals (Madge and Burn 1988, Richardson 1990, Richardson and Aspinall 1998, Snow and Perrins 1998). The species may also roost both nocturnally and diurnally in communal groups when not breeding (Brown et al. 1982).An introduced population breeds in early spring in various locations near human sites in Dubai and Abu Dhabi emirates (Richardson 1990, Richardson and Aspinall 1998, Jennings 2010), and chicks are present from late March on (Richardson 1990). While there is not much known about the breeding behaviour of the introduced population (Jennings 2010), usually the nest is a shallow depression or bowl of vegetation that can be situated in many different locations such as within vegetation on the ground, in natural tree cavities, under fallen dead wood, on tree stumps, under bushes and even in abandoned nests of other species (e.g. herons or crows) (Brown et al. 1982, Flint et al. 1984, del Hoyo et al. 1992, Snow and Perrins 1998). Nests are generally placed close to water (Kear 2005).
Taxon
Taxa
Anas platyrhynchos | Linnaeus, 1758
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Anas platyrhynchos and A. fulvigula (incorporating diazi) (del Hoyo and Collar 2014) were previously treated as A. platyrhynchos (incorporating diazi) and A. fulvigula following Sibley and Monroe (1990, 1993).
Taxon distribution as listed in assessment
This species is a common migrant and winter visitor, which occurs throughout the UAE between October and March (Richardson 1990, Pedersen et al. 2017). Large populations of several hundred individuals are regularly found at Dubai Creek (Dubai Emirate) and in Ayn al Fayda near Al Ain (Abu Dhabi Emirate) (Richardson 1990). A population of resident, breeding birds was introduced in the 1980s in Dubai and Abu Dhabi cities and on Sir Bani Yas Island (Richardson and Aspinall 1998, Jennings 2010), but this introduced population would not count towards its Red List assessment.
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
Expert opinion at the UAE assessment workshop is that it is possible to differentiate between resident (non-native) and visiting wild populations. The population size is estimated to be at least 1,000 mature individuals, and 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
Within the UAE the main threats are likely to be from changes in wetland land-use, and potentially from oil pollution, but the severity of these on the population is uncertain - especially given the presence of a feral population here (which would not count to a Red List assessment).Outside of the UAE the species faces a range of threats, which could impact individuals that visit the country. The species is threatened by wetland habitat degradation and loss from pollution (e.g. petroleum [Grishanov 2006] and pesticides [Kwon et al. 2004]), wetland drainage, peat-extraction, changing wetland management practices (e.g. decreased grazing and mowing in meadows leading to scrub over-growth)and the burning and mowing of reedbeds (Grishanov 2006). The species is hunted over large areas (Kear 2005) and also suffers mortality as a result of lead shot ingestion (e.g. Mateo et al. 1999, Mondain-Monval et al. 2002). It is also susceptible to duck virus enteritis (DVE) (Friend 2006), avian influenza (Melville and Shortridge 2006) and avian botulism (Rocke 2006), so it may be threatened by future outbreaks of these diseases (although it may be able to withstand sporadic losses due to its high reproductive potential) (Rocke 2006).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The population in 1996 is thought to have also been moderately large (e.g., 1,000+ at Al Ain), with large visiting (= natural) populations. The species is considered to have been Least Concern in 1996.
Verified entry
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Tadorna tadorna | 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 prefers sandy or muddy coasts, where its is found in brackish or freshwater lakes and marshes, as well as along tidal creeks (Richardson 1990, Aspinall and Porter 2011). It also occurs near water treatment plants or ponds further inland (Richardson 1990). There is no information available about its diet in the UAE. Elsewhere, it feeds predominantly on salt-water molluscs as well as other aquatic invertebrates (e.g. insects, crustaceans and worms), small fish, fish spawn and plant material (e.g. algae, seeds and agricultural grain) (del Hoyo et al. 1992, Kear 2005). Individuals occurring in the UAE are migratory and breed mainly in southern central Asia. Especially during the non-breeding season, the species is gregarious and occurs in small groups (Richardson 1990, Kear 2005).
Taxon
Taxa
Tadorna tadorna | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is a localised winter visitor, occurring in small numbers in coastal zones of the UAE (Richardson 1990, Pedersen et al. 2017). It winters in the country between October and mid-April, with peak occurrences in January to early March. The highest number recorded in the UAE were 150 individuals in December 2008 at Al Wathba Wetland Reserve near Abu Dhabi City (Pedersen et al. 2017). Occasional passage migrants occur in the UAE mainly in April/May (Richardson 1990). Individuals recorded during summer months likely refer to escaped or released birds (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 small non-breeding population in the UAE, which qualifies it for listing as Endangered. The population is increasing, rather than decreasing, within the UAE, and conditions outside of the UAE are considered unlikely to deteriorate, hence there is a potentially very high rescue effect from individuals outside of the region. Therefore, it is tentatively adjusted by one category to Vulnerable under criterion D1, as it is currently dependent on a small number of key sites.
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
While some of the following threats are taken from BirdLife International (2015) or are not taking place within the UAE, they are potentially impacting the population that overwinters in UAE while they are outside of the country. In parts of Europe, the species is threatened by habitat loss as a result of tidal barrage schemes (Kear 2005, Burton 2006), but changes in coastal land-use are also taking place in UAE which may be impacting the species. It also;is susceptible to avian influenza so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Hunting within its range outside of the UAE could also pose a threat (e.g Iran; Balmaki and Barati 2006). Additionally, oil pollution is a potential threat to wetland ecosystems in UAE.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
In 1996 the species may have warranted listing as Critically Endangered based on small numbers, but it would have been adjusted by one category to Endangered, given the global LC assessment. This change is likely as a result of increases in artificial water sources.
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Alectoris chukar | 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 on arid and semi-arid rocky slopes and hillsides with low vegetation cover and occasional stunted trees and bushes (Watson 1962, Papaevangelou 1980, Jennings 2010, Aspinall and Porter 2011). It is found mainly between 500 and 1,500 m, but ranges down to 200 m during foraging trips, when it also occurs on agricultural land (Pantelis 1980, Papaevangelou 1980, Serez 1992, Khan et al. 2009, Aspinall and Porter 2011). There is little known about the diet of the species in the UAE, but individuals in Musandam (Oman) have been observed feeding on berries (Jennings 2010). Elsewhere in the Middle East, the species also takes seeds of grasses and weeds, leaves and insects (Jennings 2010). Availability of water influences population density, even though birds will move up to 10 km to access water (Watson 1962), and likely limits a range expansion in eastern Arabia (Jennings 2010). There is no information available on the breeding behaviour of the species in the UAE. In Musandam (Oman), nests were made of twigs and placed in shallow depressions on gravelly ground, hidden under bushes at the edge of cultivated or grassy fields (Jennings 2010). These nests contained eggs in February and March, while juveniles were recorded in June (Jennings 2010). It is unclear if there is competition for feeding sources and nesting sites with Sand Partridge Ammoperdix heyi (Jennings 2010).
Taxon
Taxa
Alectoris chukar | (Gray, 1830)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is native to the northern Hajar Mountains (Fujairah and Ras al-Khaimah emirates) north of Dibba and Masafi, where it is an uncommon resident (Pedersen et al. 2017). It was first recorded in the UAE in Fujairah in April 1987 (Pedersen et al. 2017). Birds outside of the Hajar Mountains are of feral origin and likely not self-sustaining: In 2012, 500 birds were released near Al Ain on Jebel Hafeet (Abu Dhabi Emirate); further releases took place on Jebel Buhays and Qarn Nizwa (Sharjah Emirate) as well as on several islands in the Arabian Gulf (Das, Sir Bani Yas, Marawa, Abu al-Abyad) (Jennings 2010, Pedersen et al. 2017).
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
Due to a presence of a large number of released birds both the population size and trend are uncertain, although it is suspected that the naturally wild population of this species in UAE is fewer than 250 mature individuals. It is therefore listed here 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
Released birds pose a threat to this species through genetic contamination from non-native populations;(Panayides et al. 2011).
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
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Ammoperdix heyi | 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 arid environments on desolate rocky and stony hillsides, in wadis and cliffs (Jennings 2010, Aspinall and Porter 2011). It requires some vegetation cover and is thus rarely found in sandy places (Jennings 2010). While it is able to persist without water for long periods, it readily visits water sources when available, where flocks of up to 70 individuals may congregate (Jennings 2010). During the hottest time of the day, it hides in shady places under rocks and vegetation, and is only active around sunrise and sunset (Jennings 2010). The species is intolerant of any disturbance and very shy; thus it generally avoids proximity to humans and only occasionally visits open, cultivated landscapes for foraging (Jennings 2010). It feeds mainly on insects, but may also take leaves, fruits and even human food scraps (Jennings 2010). There is not much known about its breeding biology. In spring, males occupy and aggressively defend territories, and pairs are forming (Jennings 2010). It is assumed that nests are hidden in rock crevices, and clutches contain up to 15 eggs (Jennings 2010). While in central Arabia, adults with chicks have mostly been observed from March to July, records of small chicks from Oman in August suggest that also the population in the UAE might breed fairly late (Jennings 2010). It is likely that males and females raise separate broods (Jennings 2010).
Taxon
Taxa
Ammoperdix heyi | (Temminck, 1825)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is a fairly common and widespread resident of the mountains of northern and north-eastern UAE (Jennings 2010, Pedersen et al. 2017). It has been introduced to Das and Sir Bani Yas islands (Jennings 2010).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
C2a(ii)
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 resident population size, which is likely to be all within one subpopulation and is suspected to be in decline at an unknown rate. It is therefore listed here as Near Threatened under Criterion C2a(ii).
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
Recreation within the species's occupied range could have an impact, reducing local numbers and potentially leading to individuals altering their behavioural patterns (Aspinall 1996), but in UAE the degree of impact on the species as a whole is thought to be negligible due to how inaccessible its habitat is (Aspinall 1996, Khan;et al.;2009). However, its habitat is becoming more accessible, with development leading to habitat loss and fragmentation. A potential threat to the species, which should not be allowed to occur in the future, is the introduction of See-see Partridge, Ammoperdix griseogularis, into the native range of Sand Partridge, due to the risk of hybridisation (Aspinall 1996), while introduction of Arabian Partridge and Chukar within Sand Partridge's range may be leading to increased competition over resources, and the risk of introduced diseases.
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
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Seriphidium sieberi | 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 can be found growing in rock and gravel plains, in addition to rocky areas at high altitude (Ghazanfar and Fisher 1998, MEW 2010). In general, it favours dry steppe habitats (Ghasemkhani et al. 2008). Its growth form is a dwarf shrub (Ghazanfar and Fisher 1998).
Taxon
Taxa
Seriphidium sieberi | (Besser) K.Bremer & Humphries ex Y.R.Ling
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species occurs within the Ru'us al-Jibal and persists at high elevations within this area (MEW 2010). Globally, the native range of this species spans from the eastern Mediterranean, through to the Arabian Peninsula and western 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 is generally considered to be common within its range, appearing to be a dominant species within its preferred habitat. It is also able to persist at high altitudes. This species 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
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Periploca aphylla | 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 shrub or small tree species can grow up to 4 m (Western 1992, Fawzi and Ksiksi 2012). It produces white and purple flowers between January and April and grows on hillsides and Wadi banks (Jongbloed et al. 2003).When damaged, this species produces a milky white sap (latex) characteristic of the Asclepiadaceae family (Jongbloed et al. 2003). The species is utilised as the food plant for the Desert White Butterfly (Pontia glauconome; Jongbloed et al. 2003).
Taxon
Taxa
Periploca aphylla | Decne.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Periploca aphylla occurs in the Hajar mountains and the Ru'us al Jibal mountains in the UAE (Jongbloed et al. 2003); it is considered to be widespread within montane areas (Western 1992, Jongbloed et al. 2003). This species occurs at a range of altitudes, from around 400-500 m to high elevations (Feulner 2011). Globally, this species occurs in West Africa, the Middle East, Central Asia and India (Board of Trustees, RBG Kew 2018).
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 common and widespread within rocky habitats, such as the Hajar Mountains, at medium to high elevations. It is also reported from at least one protected area within its range. Although grazing may pose a threat to this species, the impact of this on Periploca aphylla is not yet known. 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 plant is reportedly browsed by native grazers within the UAE, such as gazelle and ibex (Ghazanfar and Fisher 1998) in addition to other species such as goats (Stuart and Stuart 1998, Shahid 2017).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Pergularia tomentosa | 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 perennial twining herb, typically free standing, that grows up to 2 m in height (Western 1992). It produces small red-brown flowers between February - April and September - October (Jongbloed et al. 2003, Karim and Dakheel 2006). It grows in sand and gravel plains, in addition to disturbed areas (Jongbloed et al. 2003, Feulner 2011, 2016), and is classed as a xerophyte (Jongbloed et al. 2003, Böer and Saenger 2006). This species is utilised as a food plant by Danaus chrysippus caterpillars (Jongbloed et al. 2003).
Taxon
Taxa
Pergularia tomentosa | L.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
Pergularia tomentosa occurs in the northern emirates, within the north-east of Abu Dhabi Emirate and rarely in the Ru'us al-Jibal (Jongbloed et al. 2003, Feulner 2011) as well as the Wadi Wurayah National Park (Feulner 2016). Where it occurs in montane areas, it is restricted to low altitudes (Jongbloed et al. 2003). Globally, this species occurs from the Sahara in northern Africa 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 was previously assessed as Least Concern, and it is known to occur in at least one protected area. Although it may be badly grazed, it is unknown to what extent this currently impacts the population. Pergularia tomentosa can also persist in disturbed areas which may increase its resistance to development and land use change. Therefore, 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 believed to be badly overgrazed by goats (Western 1991).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Cyperus aucheri | 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
All specimens held by RBGE were collected from roadside verges.
Taxon
Taxa
Cyperus aucheri | Jaub. & Spach
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
The distribution of this species in the UAE has previously been debated due to misidentification for other members of the genus, including Cyperus conglomeratus. The only determinations found are those by L. MacKinnon at RBG Edinburgh Herbarium, representing five specimens from three localities; - <a href=""https://data.rbge.org.uk/search/herbarium/?specimen_num=679006&cfg=zoom.cfg&filename=E00647618.zip"">Sharjah</a>, Dubai road (two specimens; E102; at side of road), 139 m on inland red sand dunes beside the road.- <a href=""https://data.rbge.org.uk/search/herbarium/?specimen_num=678987&cfg=zoom.cfg&filename=E00647633.zip"">Abu Dhabi Emirate</a>; Tarif (two specimens; by side of road, E45), 33 m, inland area of coastal white sand dunes close to edge of sabkha area.- <a href=""https://data.rbge.org.uk/search/herbarium/?specimen_num=678892&cfg=zoom.cfg&filename=E00647666.zip"">Abu Dhabi Emirate</a>, south of Madinat Zayed (one specimen, by side of road, E45), disturbed roadside verge, inland red sand dunes. However, it appears that this species is relatively widespread, occurring across the majority of inland UAE. This species has a wide global distribution from the Sahara, through the Arabian Peninsula, to Pakistan (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 inland UAE. As a result, the EOO of this species will far exceed the thresholds for threatened categories under Criterion B. 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
It is currently unclear which threats may be affecting this species.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
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Carthamus oxyacantha | 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?
Not possible
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
The species appears to be restricted to rural gardens and plantations in the UAE (MEW 2010), in addition to wadi environments.
Taxon
Taxa
Carthamus oxyacantha | M.Bieb.
Taxonomic Group
Plants
Taxonomic Group Level 2
Flowering Plants
Assessed taxon level
Species
Taxon distribution as listed in assessment
The distribution and origin of this species in the UAE is uncertain. <a href=""http://data.rbge.org.uk/herb/E00262941"">RBGE Herbarium</a> holds one specimen from Al Khazna on the Abu Dhabi - Al Ain road (from cultivated garden; coll. R.A. Western, 1984). MEW (2010) considered the species ""not common"", restricted as a weed to plantations, without distribution data. Jongbloed et al. (2003) cite presence in Al Ain and Ghail. A wild individual has also been recorded from Masafi. The global range of this species is from the Caucasus to Central Asia and the western Himalayas, and south to Saudi Arabia in the Arabian Peninsula (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
The distribution and origin of this species in the UAE is uncertain. The native range of the species seems to be centred on Central Asia south to India and Pakistan (Ahmad et al. 2007), and in the UAE the species is restricted to plantations and rural gardens. With several traditional uses, it is possible that the species is present in the UAE as a result of cultivation. The species is assessed 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
Without detailed information on the distribution in the UAE, little can be said about threats.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Verified entry
Off