LC
Assessment ID
330024
Taxon name
Phyla nodiflora
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
330021
Taxon name
Pulicaria arabica
Uploaded by
National Red List Database
Scientific name
Pulicaria arabica
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
asterales
Family
asteraceae
Genus
Pulicaria
Species
arabica
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 thought to be rare within the UAE, but locally common within its distribution in the Hajar Mountains. It is also cultivated in a botanic garden. 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
Within the Hajar Mountains in the UAE, it is considered to be widespread (Jongbloed et al. 2003). Globally, this species occurs from the south and eastern Mediterranean, through to the Arabian Peninsula and on to Afghanistan (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 small shrub inhabits environments in or near to water, such as irrigation channels and wetlands (Jongbloed et al. 2003, Mahmoud et al. 2018). It is an annual species and can grow up to 30 cm in height, producing green hairy stems with narrow lance-shaped leaves, in addition to yellow button-like flower-heads which are present between February and April (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
330020
Taxon name
Cressa cretica
Uploaded by
National Red List Database
Scientific name
Cressa cretica
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
solanales
Family
convolvulaceae
Genus
Cressa
Species
cretica
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
The species is widespread in the UAE and, although subpopulations are likely to have been impacted by coastal development, the species is considered 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, Jongbloed et al. (2003) reported a small number of isolated localities in coastal or near-coastal areas of the Ajman, Dubai and Abu Dhabi emirates. More recent records suggest a more frequent and widespread distribution, and Karim and Dhakeel (2006) give the distribution as Abu Dhabi (e.g., Sila, Tarif), Dubai, Fujairah, and Umm al-Qaiwain. In Ra's al-Khaimah, Feulner (2011) reported the species from, or adjacent to, salt marshes north of Rams and Llewellyn-Smith (2011) recorded the species at the Khor Hulaylah coastal wetland complex. Sakkir and Brown (2014) found the species at Jebel Hafeet, but comment that the species has been introduced to the area through human disturbance and benefits from irrigated agriculture. Globally, this species occurs throughout the Mediterranean, east through western and central Asia, to India and south to northern and central Africa, as well as South America, Australia and parts of Southeast Asia. There is no information on whether some of these populations may be non-native. In the Arabian Peninsula, this species occurs throughout coastal areas in the region, and locally inland in Oman.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This salt-tolerant perennial species is found in sand, plantations and gardens, in addition to around sabkhas or salt marshes (Jongbloed et al. 2003, Karim and Dhakeel 2006). It grows as a weed in cultivated areas (Karim and Dhakeel 2006). G. Brown (pers. comm. 2019) considers the main habitat to be saline soils (margins of sabkha), but also gardens.
Threats listed in assessment
Impacts from coastal development are likely to have been significant for this 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
329999
Taxon name
Cyperus rotundus
Uploaded by
National Red List Database
Scientific name
Cyperus rotundus
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
liliopsida
Order
poales
Family
cyperaceae
Genus
Cyperus
Species
rotundus
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 common along the Arabian Gulf coast of the UAE. Although populations will have been impacted by habitat loss and degradation, 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
This species is common along the Arabian Gulf coast of the UAE, from west of Abu Dhabi city to Ras Al-Khaimah (Jongbloed et al. 2003). The species has been recorded from Wadi Wurayah, however the origin of the species here is uncertain, and is likely to be the result of accidental introduction (Feulner 2016). Al Mehairbi et al. (2019) show a very much broader distribution for this species, across almost the entire UAE; it is thought that, if correct, this broader distribution may be the result of introduction. Globally, the species is considered to be native to the Mediterranean and throughout most of sub-Saharan Africa, east through the Middle East and Indian sub-continent to China and to Southeast Asia, south to Australia (The Board of Trustees of the Royal Botanic Gardens, Kew 2019). It occurs as a non-native in parts of Europe, the Pacific island states and through South and Central America, north to parts of the United States (The Board of Trustees of the Royal Botanic Gardens, Kew 2019). Within the Arabian Peninsula, this species is described as widespread and weedy in Saudi Arabia (Chaudhary 2001, Norton et al. 2009), common in Bahrain, Qatar (Norton et al. 2009), Oman (Ghazanfar 1992) and the United Arab Emirates (Western 1989, Jongbloed et al. 2003, Norton et al. 2009) and widespread in Yemen (Wood 1977).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
It occurs in sand along the Gulf coast, and also in gardens and cultivated areas associated with fresh or slightly brackish water (Jongbloed et al. 2003).
Threats listed in assessment
The coastal habitat of this species is impacted in the UAE by urban, industrial and touristic 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
329901
Taxon name
Polycarpaea spicata
Uploaded by
National Red List Database
Scientific name
Polycarpaea spicata
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
caryophyllales
Family
caryophyllaceae
Genus
Polycarpaea
Species
spicata
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 appears to be fairly widespread within the UAE, although it is scattered. As a result of its distribution both inland and on offshore islands, the extent of occurrence (EOO) is likely to exceed the threshold for threatened categories. It is suggested that it may well be more common than it appears due to under-collection. As a result, 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
Within the UAE, it is considered to be widespread although scattered (Brown et al. 2007). It can be found on coastal sands and plains, including Taweela and Al Jazeera al-Hamra (Brown et al. 2007). It has also been recorded from offshore islands of Abu Dhabi (Sakkir et al. 2017). Globally, this species occurs from north-east 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 an annual herb species that can grow up to 15 cm in height (Jongbloed et al. 2003, Brown et al. 2007). This plant has fine stems, basal rosette leaves and spoon-shaped stem leaves (Jongbloed et al. 2003). Flower spikes that resemble a tuft of grass can be seen between February and April (Jongbloed et al. 2003). It generally grows within stable sand and silt substrates that can be found in between rocks 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
330682
Taxon name
Curruca nana
Uploaded by
National Red List Database
Scientific name
Curruca nana
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
sylviidae
Genus
Curruca
Species
nana
Taxonomic notes and synonyms listed
Previously placed in Sylvia;(del Hoyo and Collar 2016) but moved to current genus following Cai et al. (2019). Until recently considered conspecific with C. deserti;(AERC TAC 2003, Cramp and Simmons 1977-1994, Dowsett and Forbes-Watson 1993 and Sibley and Monroe 1990, 1993) (see related note/s). Proposed subspecies theresae (from Sind, in Pakistan) falls within range of individual variation of nominate. Monotypic.
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
The very small non-breeding population size of this species in the UAE means that the species could warrant listing as Near Threatened under Criterion D1. However, with conditions not deemed to be deteriorating significantly, and there being a good likelihood for a rescue effect for this population, a regional adjustment has been made. The species is, therefore, instead listed 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
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. Numbers are highest between September and early April, when the species is common in arid zones throughout the country (Aspinall and Porter 2011, Pedersen et al. 2017). Individuals wintering in or passing through the UAE breed in southern central Asia.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species inhabits a variety of arid, sparsely vegetated habitats, including desert, semi-desert, gravel plains, scrubland, hillsides with low scattered bushes, scrubby saltflats and coastal dunes (Richardson 1990, Aspinall and Porter 2011). It avoids wooded areas (Aspinall and Porter 2011). The diet is thought to consist mostly of small insects (e.g. grasshoppers, moths), seeds and berries. The species is migratory. The breeding season starts in late April.
Threats listed in assessment
In the breeding range, the species is affected by habitat loss driven by overgrazing and agricultural intensification (Hagemeijer and Blair 1997). Continuing drought along with overgrazing can result in habitat loss (Aymà and Gargallo 2016). Overgrazing outside of Protected Areas may also be an issue for this species within the UAE too.
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates
Assessment ID
330679
Taxon name
Passer domesticus
Uploaded by
National Red List Database
Scientific name
Passer domesticus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
passeridae
Genus
Passer
Species
domesticus
Taxonomic notes and synonyms listed
Passer domesticus and P. italiae (del Hoyo and Collar 2016) were previously lumped as P. domesticus following AERC TAC (2003); AOU (1998 and supplements); Christidis and Boles (2008); Cramp et al. (1977-1994); Dowsett and Forbes-Watson (1993); SACC (2005 and updates); Sibley and Monroe (1990, 1993); Stotz et al. (1996); Turbott (1990).
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 thought to have an extremely large resident population size within the UAE, which is suspected to be increasing as it colonises new areas. Therefore, it is assessed here 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 an abundant resident; its range expanded rapidly since the 1980s and now spans the entire country (Jennings 2010, Pedersen et al. 2017). The earliest records of the species in the UAE are from the 1940s. In Abu Dhabi City, the species was not found until the 1970s, but was already regarded as common by 1980 (Jennings 2010). During the 1980s, it spread through Liwa (Abu Dhabi) and colonised several islands, including Das Island in the 1990s (Jennings 2010). The rapid expansion of the range and population are likely a consequence of the spread of irrigation, cultivation and urban developments in the country (Jennings 2010). Subspecies indicus occurs throughout the year in the UAE, but it is possible that several other subspecies from western and central Asia visit the country (Jennings 2010, Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
This species is often associated with man, living around buildings from isolated farms to villages and urban centres, though it also colonizes isolated areas far away from human population. It has been expanding its range in Arabia by using human developments like villages, farms, plantations or even petrol stops as dispersal corridors (Jennings 2010). The availability of water is crucial for the species (Jennings 2010). The diet is mainly vegetable material, particularly seeds of grasses and green shoots, cultivated cereals and low herbs, but also fruits, such as dates and berries, and wide range of household scraps (Summers-Smith et al. 2015). It also feeds on invertebrates, such as moths, caterpillars and ants (Jennings 2010). It forages mainly on the ground or in low vegetation. It shows a wide variety of foraging techniques, from hovering flights to pick items from leaves, to running and hopping or aerial pursuits in search for insect prey (Jennings 2010). It nests colonially, sometimes together with other species (e.g. Spanish Sparrow Passer hispaniolensis, although P. hispaniolensis is now possibly extinct as a breeding species within the UAE). Nests are constructed mainly of plant stems, lined with feathers or other soft material. They can be placed almost anywhere, e.g. in a hole in a building, in a cliff or in a tree (Jennings 2010, Summers-Smith et al. 2015). While breeding has been observed year-round, the main period lasts from May to June (Jennings 2010).
Threats listed in assessment
Declines in western Europe have been attributed to a decrease in availability of suitable invertebrate food necessary for rearing young as well as possible reduced fitness of those young that fledge successfully (Summers-Smith et al. 2015). This may be as a result of changes in agricultural practices such as the increased use of pesticides and herbicides and the autumn sowing of cereals, which have lead to decreases in food for this species (Hagemeijer and Blair 1997), although this is not thought to be a threat operating within the UAE. Indeed, Aspinall (1996) did not highlight any particular threats to the species within the country.
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates
Assessment ID
330676
Taxon name
Lanius excubitor
Uploaded by
National Red List Database
Scientific name
Lanius excubitor
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
laniidae
Genus
Lanius
Species
excubitor
Taxonomic notes and synonyms listed
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).
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 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.
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
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).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
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).
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.
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates
Assessment ID
330650
Taxon name
Gallinula chloropus
Uploaded by
National Red List Database
Scientific name
Gallinula chloropus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
gruiformes
Family
rallidae
Genus
Gallinula
Species
chloropus
Taxonomic notes and synonyms listed
Gallinula chloropus and G. galeata (del Hoyo and Collar 2014) were previously lumped as G. chloropus following Sibley and Monroe (1990, 1993).
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 has a large and increasing breeding population in the UAE and 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
A breeding population recently colonised the country; the first successful breeding attempts were confirmed in April 1989 in Sharjah Emirate near Kalba and Sharjah City. Breeding has further been confirmed in Hatta Wadi and Al Marmoom Conservation Reserve (S. Alam (Dubai Municipality) pers. comm. 2019). The species has since been breeding regularly, but it is localised (Pedersen et al. 2017). The species also visits the UAE as a wintering species and migrant individuals occur on passage to and from the breeding grounds (Pedersen;et al. 2017). It is common at wetlands throughout the country, from the mountains at the border to Oman;to permanent water sites along the east and west coasts, as well as artificial lakes (Jennings 2010, Pedersen;et al. 2017, S. Alam in litt. 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 species inhabits all kinds of permanent wetland sites (Jennings 2010). It particularly prefers freshwater marshy pools and lakes with abundant vegetation cover along the borders, floating and emergent vegetation, dense reeds and wet bushy areas near watercourses offering abundant hiding places (Richardson 1990, Jennings 2010, Aspinall and Porter 2011, R. Khan pers. comm.). Occasionally, it occurs in eutrophic water near dump sites, in saline habitats or mangroves. Recently, populations became established in artificial waterbodies (S. Alam (Dubai Municipality) pers. comm. 2019, R. Khan (Dubai Safari, Dubai Municipality) pers. comm. 2019). When foraging, it may venture into open water or dry habitats, such as crop fields and gardens near wetlands (Jennings 2010). There is no information available about its diet in the UAE; elsewhere it is omnivorous and opportunistic, its diet consisting of earthworms, crustaceans, molluscs, insects, spiders, small fish, tadpoles and occasionally birds eggs, as well as plant matter such as filamentous algae, moss and the vegetative parts of reeds and aquatic plants, as well as berries and fruits (del Hoyo et al. 1996). While the species forms small flocks during the non-breeding season, it becomes territorial and aggressive with the onset of the breeding season in early spring. The breeding season is very long; eggs have been recorded from January in the UAE until August on the Saudi Arabian coast of the Arabian Gulf, the majority of chicks have been observed between April and July (Jennings 2010). The nest is a bulky cup constructed from twigs and waterside vegetation, which is placed on floating or partially submerged objects on water, in reed beds or adjacent to water (del Hoyo et al. 1996, Jennings 2010). Clutches contain around eight, seldom up to 13 eggs (Jennings 2010). Part of the population in the UAE is migratory; individuals breed from eastern Europe to central Asia and move south towards the UAE or from September to December and return again from March to May (del Hoyo et al. 1996, Jennings 2010).
Threats listed in assessment
In UAE the main threat to the species is development and infilling of wetland habitats (Aspinall 1996).The species is susceptible to avian influenza (Melville and Shortridge 2006, Gaidet et al. 2007) and avian botulism (Rocke 2006) and may be threatened by future outbreaks of these diseases.
History
Aspinall (1996) listed 20-200 mature individuals, qualifying as CR, adjusted by one category to EN. There were very much fewer areas of suitable habitat at that time.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates
Assessment ID
330613
Taxon name
Emberiza striolata
Uploaded by
National Red List Database
Scientific name
Emberiza striolata
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
emberizidae
Genus
Emberiza
Species
striolata
Taxonomic notes and synonyms listed
Emberiza striolata and E. sahari (del Hoyo and Collar 2016) were previously lumped as E. striolata following Cramp and Simmons;(1977-1994); Dowsett and Forbes-Watson (1993); Sibley and Monroe (1990, 1993).
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
The species has a resident population size within UAE of 10,000-50,000 mature individuals. There is insufficient information to suggest a population trend, and so in the absence of any firm information to suggest a decline, the species is not deemed to approach the threshold for Vulnerable. Therefore, it is listed here 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 a fairly common breeding resident in the UAE (Pedersen et al. 2017). It mainly occurs in the mountains, but disperses to adjacent plains in winter (Jennings 2010, Pedersen et al. 2017), and is a vagrant in western Abu Dhabi (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
The species occupies dry rocky hillsides with little vegetation or wadis (Jennings 2010, Aspinall and Porter 2011). It is often found in close proximity to water, particularly during hot days (Jennings 2010). It feeds in small groups, taking seeds on the ground or from small plants (Jennings 2010). A peculiarity of this species is its feeding technique of jumping up to grab seed heads of herbs and grass and feed while standing on them to hold them down (Fry and Eriksen 1994, Jennings 2010). The breeding season starts in January or February, with juveniles fledging in April and May (Jennings 2010). The clutch consists of two to four eggs (Jennings 2010). Nests are small cups of twigs, roots and grass and are placed in holes in cliffs and precipices (Jennings 2010, Aspinall and Porter 2011).
Threats listed in assessment
Within the UAE, there are no known significant threats to this species (Aspinall 1996), although montane development potentially could have an impact.
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates