United Arab Emirates (the)
Official name
United Arab Emirates
ISO alpha-2 code
AE
ISO alpha-3 code
ARE
ISO numeric-3 code
784
Continent
Asia
Assessment ID
330955
Taxon name
Lotus laricus
Uploaded by
National Red List Database
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330954
Taxon name
Dipcadi serotinum
Uploaded by
National Red List Database
Scientific name
Dipcadi serotinum
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
asparagales
Family
asparagaceae
Genus
Dipcadi
Species
serotinum
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
Although Dipcadi serotinum appears to have a fragmented distribution, it is relatively widespread along the Arabian Gulf Coast of the UAE. As such, it is likely that is exceeds the thresholds required for threatened categories under Criterion B. Therefore, it is assessed as Least Concern.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
In the UAE, this species occurs along the Arabian Gulf coast. Its range along the coast is considered to be fragmented. Globally, this species occurs from the Canary Islands, through Europe and northern Africa to the Arabian Peninsula and India (Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Incomplete
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
It is considered to be a salt-tolerant plant within the UAE (Karim and Dakheel 2006). It generally appears to be restricted to rocky outcrop habitats.
Threats listed in assessment
Dipcadi serotinum is affected by coastal development.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330953
Taxon name
Filago griffithii
Uploaded by
National Red List Database
Scientific name
Filago griffithii
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
asterales
Family
asteraceae
Genus
Filago
Species
griffithii
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Data Deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
The two records of this species in the UAE are currently unconfirmed and there is little available information for this species. As a result, it is assessed as Data Deficient.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the UAE, the species was listed for the UAE by Jongbloed et al. (2000). It is recorded from the Ru'us al-Jibal with two known records (Feulner 2011). Due to the lack of confirmed records, the species should be considered as 'uncertain' within the UAE (G.R. Feulner, in litt., MEW 2010). The species was recorded from the Musandam Mountains of northern Oman by Western (1991). The native range of this species encompasses the eastern Mediterranean and Central Asia (Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Not possible
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species grows as a small green, furry herb (Western 1991). In general, it is considered to look similar to other closely related species of the Filago genus (Feulner 2011).
Threats listed in assessment
Without detailed information on the distribution in the UAE, little can be said about threats.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330952
Taxon name
Crepis kotschyana
Uploaded by
National Red List Database
Scientific name
Crepis kotschyana
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
asterales
Family
asteraceae
Genus
Crepis
Species
kotschyana
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Data Deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
There is little information available on Crepis kotschyana and its status within the UAE. As a result, it is difficult to assign a category to this species. It is assessed as Data Deficient.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
In the UAE, it has been recorded from the Ru'us al-Jibal (MEW 2010). Western recorded the species from 10 km north of Masafi town (coll. R.A. Western, 1990, <a href=""http://data.rbge.org.uk/herb/E00086574"">RBGE Herbarium</a>, and also recorded by Karim). Globally, the native range of this species spans from the eastern Mediterranean through to central Asia and Pakistan (Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
It is found growing within silt in rocky environments (MEW 2010) and rocky slopes (Western, RBGE Herbarium). There is little other information available on this species.
Threats listed in assessment
There is no evidence of widespread threats.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330951
Taxon name
Corallocarpus epigaeus
Uploaded by
National Red List Database
Scientific name
Corallocarpus epigaeus
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
cucurbitales
Family
cucurbitaceae
Genus
Corallocarpus
Species
epigaeus
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Data Deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
It appears that this species is described from a single locality within the UAE, although this record may relate to a closely related species instead. Confirmation of the distribution and population status of this species is needed, in addition to its taxonomy. It is therefore assessed as Data Deficient.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the UAE, it is known from a single locality in Wadi Siji (Jongbloed et al. 2003, MEW 2010). However, it is unclear whether this record represents both this species and its relative, Corallocarpus schimperi, or if it relates only to C. schimperi. Globally, this species occurs from Senegal and Eritrea to Tanzania, the Arabian Peninsula and the Indian subcontinent (Board of Trustees, RBG Kew 2019). Plants of the World Online do not list the UAE as a native country of occurrence for this species (Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Little information is available relating specifically to Corallocarpus epigaeus. However, it may bear similarities to Corallocarpus schimperi: a perennial climbing herb which has heart-shaped leaves and yellow flowers (Jongbloed et al. 2003). C. schimperi grows within gravel on hillsides and in wadis (Jongbloed et al. 2003).
Threats listed in assessment
There is no information available.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330950
Taxon name
Cistanche phelypaea
Uploaded by
National Red List Database
Scientific name
Cistanche phelypaea
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
lamiales
Family
orobanchaceae
Genus
Cistanche
Species
phelypaea
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is relatively widespread in the UAE, occurring inland and within farm areas in addition to plantations. It is a parasite and is described as common within its range, in addition to being highly salt-tolerant and even considered as a weed in some areas. Although this plant is known to be grazed by gazelles, it is not known whether these factors pose a threat to the species. Therefore, this species is assessed as Least Concern.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the UAE, this species occurs in the Liwa area to the south of the country. It is also found in inland plantation sites. The distribution is uncertain due to confusion with Cistanche tubulosa. Globally, the native range of this species spans across the Mediterranean, Macaronesia and northern Africa to the Arabian Peninsula (Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Cistanche phelypaea is known to be a common parasite of shrub species, including Cornulaca monacantha and, occasionally, Zygophyllum qatarense (Brown et al. 2007, MEW 2010). The plant can reach up to 60 cm in height, has alternate scale-like leaves, in addition to dense spikes of yellow flowers which can be seen between December and March (Jongbloed et al. 2003, Karim and Dkaheel 2006, Norton et al. 2009). It is known to grow along roadsides, in plantations and farms, and is considered to be highly salt tolerant (Karim and Dakheel 2006, Norton et al 2009, MEW 2010). This species is also considered to be a weed and is known to be grazed by the sand gazelle, Gazella subgutturosa (Hornby 2003, Karim and Dakheel 2006).
Threats listed in assessment
This species may be grazed by livestock and wild animals, however, it is unknown whether this poses a major threat to the species.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330949
Taxon name
Chaenorhinum rubrifolium
Uploaded by
National Red List Database
Scientific name
Chaenorhinum rubrifolium
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
lamiales
Family
plantaginaceae
Genus
Chaenorhinum
Species
rubrifolium
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Data Deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is known from a small number of localities in the eastern UAE mountains and its primary global distribution is the Mediterranean region. However, S. Ghazanfar (pers. comm. 2019) considers it to be a rare native species. The distribution of the species is uncertain, and the identity of subspecies requires confirmation. As a result, the species is considered Data Deficient at present.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Within the UAE, this species has so far been recorded from Jebel Mleiha (Sharjah Emirate; reported by T. Carlisle via S.A. Ghazanfar pers. comm. 2019), Wadi Helo (El-Keblawy et al. 2016; record with photo, no specimen; S.A. Ghazanfar pers. comm. 2019), Jebel Mleiha (S.A. Ghazanfar pers. comm. 2019), in the western Ru'us al-Jibal (single locality above Wadi Sha'am; Feulner 2011), and in the Masafi area (G.R. Feulner, in litt, MEW 2010), including from Wadi Siji in the Wadi Wurayah National Park buffer zone (Feulner 2016). This species appears to have a Mediterranean distribution, but with no records from Libya, Egypt and the eastern Mediterranean, except Turkey, where it is considered introduced (Board of Trustees, RBG Kew 2019), although Marhold considers it native there. TavÅŸanoäŸlu et al. (2017) give the general distribution as Algeria, Morocco and Tunisia in North Africa, Spain (including the Baleares), France, Italy and Greece in Europe, and Turkey. However, there are mentions of this species from Saudi Arabia and from Iraq; the distribution is clearly not well understood, with the species having only just been reported from North Macedonia (Matevski et al. 2019).
Is there a map available in assessment?
Incomplete
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
Chaenorhinum rubrifolium is an annual herb species. In the Ru'us al-Jibal, the species was found in soil within stony scree (Feulner 2011). At Jebel Mleiha, the species was found amongst rocks in the gravel plain at the base of the mountain (T. Carlisle via S.A. Ghazanfar pers. comm. 2019). Where it was locally common near Masafi, it was found in wadi gravel (G.R. Feulner pers comm. 2019).
Threats listed in assessment
There is no information available.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330948
Taxon name
Centropodia fragilis
Uploaded by
National Red List Database
Scientific name
Centropodia fragilis
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
poales
Family
poaceae
Genus
Centropodia
Species
fragilis
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Data Deficient
Abbreviated status
DD
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is apparently known from few records in the UAE, including Sweihan (Al-Ain region), Bu Hasa to the west in Abu Dhabi Emirate, and from Abu Dhabi Island, which is presumably now lost due to development. This species can be confused with other species in the genus and is probably under-recorded, and perhaps has a much wider distribution in the deserts of western and central Abu Dhabi Emirate, given its occurrence in the eastern parts of Saudi Arabia (Mandaville 1990). Research is required to understand the distribution of this species in the UAE, as well as its population size and trend. At present, it is considered Data Deficient.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is apparently known from few records in the UAE. Jongbloed et al. (2003) reported it from Sweihan (Al Ain region) and from Bu Hasa to the west in Abu Dhabi Emirate (Brown and Sakkir 2004). Fisher (2007) recorded the species on Ras Al Akhdhar, on Abu Dhabi Island, which is now entirely developed. Globally, the species is found from the western Sahara to the Arabian Peninsula (Mandaville 1990, Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Incomplete
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
A perennial tussock-forming grass, the species is found primarily on high dunes (Jongbloed et al. 2003, MEW 2010), on deep sands, and even on mobile dunes (Mandaville 1990).Centropodia fragilis is hard to distinguish from C. forskalii, differentiated only by its taller appearance and longer inflorescence (Jongbloed et al. 2003).
Threats listed in assessment
Grazing by livestock may impact the species in parts of its range, and impacts from coastal development are likely to have been significant.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330947
Taxon name
Volutaria sinaica
Uploaded by
National Red List Database
Scientific name
Volutaria sinaica
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
asterales
Family
asteraceae
Genus
Volutaria
Species
sinaica
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
Although a wider distribution through the Hajar Mountains is given by Jongbloed et al. (2003), there is little information recorded for this species, aside from an observation of the plant at a single locality within the Olive Highlands where fewer than 50 individuals were seen. As a result, it qualifies as Critically Endangered. It is known from two other sites in Wilayat Mahdhah, part of Oman, at lower elevations within steep mountain wadis. The species was first recorded at the known UAE site in 2014, meaning it is possible that the species is the result of natural introduction (potentially through wind dispersal) from Oman. As such, the potential for future colonisation is considered to be high and a regional adjustment of one category is applied, making the final category Endangered.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
Jongbloed et al. (2003) show a narrow distribution through the Hajar Mountains in the UAE. This species has also been recorded within the Olive Highlands in the UAE (Feulner 2014), on the upper parts of Jebel Qitab summit plateau at c.1,000 m elevation. It also occurs in adjacent parts of Oman in the same mountain group, as well as at lower altitudes (Jongbloed et al. 2003). The species is found in fallow fields and in plantations (Jongbloed et al. 2003) and is a ruderal species (Feulner 2014), and its origin in the country perhaps requires confirmation. Globally, this species occurs across the Sahara and northern Africa from Morocco eastwards to the Arabian Peninsula (Board of Trustees, RBG Kew 2019). Plants of the World Online does not list the UAE as a native country for this species (Board of Trustees, RBG Kew 2019), however Ghazanfar (2015) includes the UAE, Oman, and northern and eastern Saudi Arabia in the regional distribution.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This annual herb has been recorded from ridge-tops and summit plateau within the mountainous habitat of the Olive Highlands (Feulner 2014) in stony areas. The species is found in fallow fields and in plantations (Jongbloed et al. 2003) and is a ruderal species (Feulner 2014). In Oman, the species occurs in the foothills and coastal plains, in sandy soil, in wadis, fallow fields, and roadsides (Ghazanfar 2015).
Threats listed in assessment
There are no known threats.
History
The species was first recorded for the UAE in 2014, however occurrence on a similar basis in 1996 is likely and is considered to have also been EN(D) at that time.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.
Assessment ID
330946
Taxon name
Viola cinerea
Uploaded by
National Red List Database
Scientific name
Viola cinerea
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
malpighiales
Family
violaceae
Genus
Viola
Species
cinerea
Specific locality or subnational name or regional name
United Arab Emirates (the)
Scope (of the Assessment)
National
Countries included within the scope of the assessment
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Not_assigned
Assessed as
Least Concern
Abbreviated status
LC
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species is widespread in the north-east of the UAE and qualifies as Least Concern.
Year assessed
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Criteria system used
IUCN
Reference for methods given
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.
Endemic to region
Not assigned
Taxon distribution as listed in assessment
This species is widespread in the Hajar Mountains and the Ru'us al-Jibal (Jongbloed et al. 2003). In the southern Hajar Mountains in the UAE, the species is found along ridges in the 'Olive Highlands' (Feulner 2014), in Wadi Wurayah National Park at all elevations (Feulner 2016), and at all elevations in wadis and on plateaus in the Ru'us al-Jibal (Feulner 2011). The global range of this species is through the Arabian Peninsula to Pakistan (Board of Trustees, RBG Kew 2019).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This annual herb is found on gravels, in wadis, plateaus, hillsides and mountain ridges at all elevations (Jongbloed et al. 2003; Feulner 2011, 2014, 2016).
Threats listed in assessment
There is no information available.
Publication
Allen, D.J., Westrip, J.R.S., Puttick, A., Harding, K.A., Hilton-Taylor, C. and Ali, H. 2021. UAE National Red List of Vascular Plants. Technical Report. Ministry of Climate Change and Environment, United Arab Emirates, Dubai.