Assessment ID
330018
Taxon name
Ophioglossum polyphyllum
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
330000
Taxon name
Pupalia lappacea
Uploaded by
National Red List Database
Scientific name
Pupalia lappacea
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
caryophyllales
Family
amaranthaceae
Genus
Pupalia
Species
lappacea
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
This species is considered to be very rare: it is known from few records and has a restricted distribution. The number of mature individuals is estimated to not exceed 200-300. In addition, it doesn't appear to occur in any protected areas and is not cultivated in any way. It is also unclear whether this species is currently threatened. The species is assessed as Endangered on the basis of the restricted number of mature individuals. There not known to be any adjacent populations in Oman, and no rescue effect is inferred; the seed is burred and presumed to be transported by larger animals.
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 is found in Wadi Naqab and in the Ru'us al-Jibal Mountains in the UAE (Jongbloed et al. 2003, Feulner 2011). Karim and Fawzi (2007) recorded it from Wadi Sha'am. The extent of occurrence (EOO) of this species is estimated at less than 294 km<sup>2</sup>. This species is widespread in the tropics of the Old World. It occurs in tropical Africa from Egypt to South Africa and Madagascar (APD 2019), through the Arabian Peninsula (Yemen, Oman, the UAE) to Pakistan, India and Sri Lanka, and Southeast Asia (Board of Trustees, RBG Kew 2018). It is introduced in Australia.
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 an annual or perennial amaranth that grows up to 150 cm (Jongbloed et al. 2003). It grows in silt among rocks and produces round leaves in addition to flowers from February to April (Jongbloed et al. 2003). It is typically found in shaded, sheltered and relatively mesic conditions. The species appears to be long lived as known individuals have survived in the same locality for over a decade (G.R. Feulner, in litt, MEW 2010).
Threats listed in assessment
The species appears to be grazed, however, it is not clear to what extent this poses a threat to the species.
History
The situation in 1996 is thought to be similar to the current situation, including a relatively small population size.
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
329914
Taxon name
Olea europaea
Uploaded by
National Red List Database
Scientific name
Olea europaea
Assessed taxon level
Species
Higher level taxonomic groupings
Plants
Flowering Plants
Kingdom
Plantae
Phylum
tracheophyta
Class
magnoliopsida
Order
lamiales
Family
oleaceae
Genus
Olea
Species
europaea
Taxonomic notes and synonyms listed
Olea taxonomy is far from being clearly understood. Some molecular studies (Balboni et al. 2006, Besnard et al. 2009, Besnard et al. 2013) strongly suggest that there have been successive episodes of cross-breeding among wild, feral and cultivated forms of Olea europaea, throughout the Mediterranean region for several centuries. As the cultivated forms were brought from the eastern to the western Mediterranean, they also crossbred with spontaneous Olea subspecies and then became feral. As centuries passed, this process resulted in the gradual dilution of oriental haplotypes into the western haplotypes. However, it is considered that some of the conclusions presented in the above molecular studies are not robust, since they may lack some taxonomic accuracy regarding the sampled taxa (with different taxa sampled as the same taxon) (J. Capelo pers. comm. 2016) and therefore molecular studies are not yet conclusive in terms of the taxonomy of this species; we follow the classical taxonomic treatment from Green (2002). Four subspecies and one variety of Olea europaea L. are considered native to Europe (WCSP 2016):<ul><li>O. europaea subsp. cerasiformis G.Kunkel & Sunding</li><li>O. europaea subsp. europaea</li><li>O. europaea subsp. guanchica P.Vargas, J.Hess, Muñoz Garm. & Kadereit</li><li>O. europaea var. sylvestris Brot.</li></ul>These taxa are related to cultivated Olive.
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species was first recorded for the UAE in 1997 and is now known to be largely restricted to the 'Olive Highlands' area of the Hajar Mountains in eastern UAE, with additional records from northern slopes of Jebel Jabsah and north of Wadi Ham on the outskirts of Fujairah city. The extent of occurrence (EOO) is less than 200 km<sup>2</sup>. The area of occupancy (AOO) has not been measured as detailed locality records are not available, but it is likely to be less than 200 km<sup>2</sup>. The impact of current and potential threats are not known, however grazing by livestock and feral animals may account for the poor regeneration that was observed in the early 2000's. The species is assessed as Vulnerable (VU D1) because there are thought to be c. 500 mature individuals. No rescue effect is applied as, although the species occurs in Oman, no young trees have been seen. Conservation action and research is required for this species in order to protect significant subpopulations, and to understand the impacts of hybridisation and climate change in the mountains.
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 species is found at higher elevations along connected high elevation ridges in the 'Olive Mountains' of the UAE. This species was first recorded for the UAE in 1997 at sites including the summit of Jebel Qitab (at c. 1,000 m asl), and above Wadi al-Iyeli; at each of these localities approximately two dozen specimens were present in adjacent ravines, and observations suggested that limited numbers were present in the intervening area (Feulner 1997). In general, it is restricted to the highest ridges of the Hajar Mountains southwest of Fujairah above 600 m (G.R. Feulner, in litt, MEW 2010, Feulner 2014). Records from the ""Olive Highlands"" area include the higher ridges above Wadi Mayy, Wadi Hayl and Wadi Saham, on north-facing cliffs of Jebel Al-Iyeli and on the northern slopes and ravines of Jebel Sfai (Feulner 2014). Individual small specimens have been found at wadi level in Wadi Hayl (M.A.R. Khan pers. comm. in Feulner 2014). The only other records are of two small trees (<1.5 metres tall) on the northern slopes of Jebel Jabsah, and north of Wadi Ham on the outskirts of Fujairah city (Feulner 2014). The species is absent from Wadi Wurayah National Park (Feulner 2016) and from the Ru's al-Jibal (Feulner 2011). The EOO is less than 200 km<sup>2</sup>. The AOO has not been measured as detailed locality records are not available, but it is likely to also be 200 km<sup>2</sup>. It is considered to be native to the UAE. The species has been very widely cultivated so it is difficult to determine its full native range, but currently it is considered native to parts of Africa, Europe and western Asia.
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
A tree that grows to at least 3-4 m in height in the UAE (G.R. Feulner pers. comm. 2019). The species is generally found along ridge tops, summit cliffs, and north and east-facing slopes and ravines of the Hajar Mountains above 800 m as well as, occasionally, in ravine beds in wadi bottoms at Wadi Hayl and Wadi Mayy (Feulner 2014).
Threats listed in assessment
The species is at the northern extent of its range in these mountains. Individuals in wadi beds and the lower parts of ravines are vulnerable to grazing, development (housing, roads etc), and other threats. Grazing by livestock and feral animals might be the cause of the poor regeneration observed by G.R. Feulner (in litt, MEW 2010). There has been localised loss of individuals as a result of development (radio mast construction). In parts of the Olive Highlands, introduced (e.g., from Spain and Italy) olive plantations have been developed. Hybridisation between wild olives and planted olive trees is highly likely by pollinators and wind pollination.
History
Same population size, although the individual trees were in better condition as a a result of higher rainfall.
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.
NRL Publication ID
2002
Published
2021
Uploaded by
National Red List Database
Locality (as published)
United Arab Emirates (the)
Scope of the publication
National
Countries included within the publication
United Arab Emirates (the)
Country ISO code(s)
ARE
Does the publication cover a marine EEZ area(s)?
Not_assigned
Taxonomic groups included
Flowering Plants
Ferns and Allies
Gymnosperms
Multi-taxa
Full taxonomic coverage?
No
Assessments extracted and within NRLD?
Yes
Data Stewardship Groups responsible
IUCN, Ministry of Climate Change and the Environment of the United Arab Emirates (MOCCAE)
Publication format
Electronic format
Database
Hard copy
Reference and Website
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.
Language
English
Assessments within the NRLD
Species or Taxon | Taxonomic Group | Year Assessed | Countries | Criteria system | Status | More info |
---|---|---|---|---|---|---|
No results. |
Assessment ID
330683
Taxon name
Alaudala rufescens
Uploaded by
National Red List Database
Scientific name
Alaudala rufescens
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
alaudidae
Genus
Alaudala
Species
rufescens
Taxonomic notes and synonyms listed
Calandrella rufescens (AERC TAC [2003]; Cramp et al. [1977-1994]; Dowsett & Forbes-Watson [1993]; Sibley & Monroe [1990, 1993]) and C. cheleensis (Sibley & Monroe [1990, 1993]) have been lumped into Alaudala rufescens following del Hoyo and Collar (2016).
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
Critically Endangered
Abbreviated status
CR
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a small non-breeding population that would warrant a listing as Endangered under criterion D. However, the species is thought to have previously bred in the UAE, and the breeding status takes precedence here. The species is suspected to no longer be a breeding species in the country, but lack of sufficient survey work to confirm its disappearance from the whole country means that it is tentatively treated here as being still extant. Any remaining breeding population is still thought to be tiny. Therefore, the species is listed here as Critically Endangered under criterion D.
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 migrant individuals on passage to and from the breeding grounds in September-November and March-April (Richardson 1990, Pedersen et al. 2017). It is also a common wintering bird in the country (Pedersen et al. 2017). Since 1993, there was a small resident population of about 20 pairs in the UAE, which bred on Taweela Island/Ras Ghanada (Abu Dhabi) and Siniyah Island (Umm al-Quwain), as well as along the coast from Umm al-Quwain to Ras al-Khaimah emirates (Richardson and Aspinall 1998, Jennings 2010, Pedersen et al. 2017). However, it is now believed that the species no longer breeds regularly in the UAE, if it still breeds at all (R. Sheldon;in litt.;2019). There hasn't been sufficient surveying work, though, to confirm its disappearance from the country as a breeding species, and it is quite possible that there could be individuals breeding in unsurveyed areas. Therefore, for this process it is tentatively treated as being still extant.
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 on open plains of sand or gravel, covered with a dense layer of grasses and herbs (Jennings 2010). It is often found on cultivated areas, near rain pools and on saltflats (Jennings 2010, Aspinall and Porter 2011). It avoids areas with dense vegetation of bushes and trees, and is rare in rocky deserts and on hillsides (Jennings 2010). It is often found in association with other larks, especially the Greater Short-toed Lark Calandrella brachydactyla (Jennings 2010). In winter, the species can form flocks of up to several thousand individuals (Jennings 2010). There is no information available on its diet in the UAE. Elsewhere, the diet varies seasonally between invertebrates and seeds. In the spring it feeds mostly on invertebrates and in winter mostly seeds with a mix of the two consumed in summer. Fruits and bulbs are also taken. The breeding season lasts from February to August. The nest is a small scrape on the ground beside a small shrub or tuft, or in the open and lined with vegetation. Normally four to five eggs are laid.
Threats listed in assessment
Development around Ras Ghanada could encroach on breeding sites, but this was thought to be likely to only have a negligible impact on the population, and Aspinall (1996) believed that unless there is to be any significant change in land-use in the near future it is unlikely that the species will face any severe threats. Given that the species has now potentially gone extinct within the UAE as a breeding species either Aspinall (1996) underestimated the impact of development on this species or there are further unidentified threats that have driven the species's potential disappearance as a breeding bird in UAE. Predation by cats,;Felis catus,;has been noted to cause local declines on the Arabian Peninsula for Crested Lark (Symes;et al.;2015), and this is another possible threat to this species.
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment, as while there was still confirmed breeding in 1996, the population size would still likely have met the thresholds for listed as Critically Endangered.
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
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 (AymĂ 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
330681
Taxon name
Anthus similis
Uploaded by
National Red List Database
Scientific name
Anthus similis
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Anthus
Species
similis
Taxonomic notes and synonyms listed
Anthus similis and A. nyassae (del Hoyo and Collar 2016) were previously lumped as A. similis following AERC TAC (2003); Cramp and Simmons (1977-1994); Dowsett and Forbes-Watson (1993). Anthus longicaudatus is no longer recognized as a species, following del Hoyo and Collar (2016); available material in museums is an amalgam of specimens of A. vaalensis and A. similis.
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
Vulnerable
Abbreviated status
VU
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species's breeding population within the UAE is small enough to trigger a listing as Endangered under Criterion D. However, the species is likely a recipient of immigration from outside of the country which would provide a rescue effect. Therefore, the category has undergone a regional adjustment, and the species is listed here as Vulnerable under Criterion D1.
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 uncommon to fairly common resident in the northern highlands as well as in the eastern part of the UAE. Occasionally, individuals stop in the country during migration or for wintering (Pedersen et al. 2017). The occurrence of wintering individuals in the lowland plains along the coast might be of local altitudinal migrants within the country (Jennings 2010).
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 rocky hills, slopes and terraced fields in the highlands (Jennings 2010, Aspinall and Porter 2011). It favours areas with bushes, sparse trees and a dense vegetation cover on the ground (Jennings 2010). Its diet includes invertebrates (grasshoppers and other insects), which it takes from the ground, sometimes even by running and chasing (Jennings 2010). Within the UAE, it breeds above c. 500 m, ranging to he highest elevations (Jennings 2010). During winter, highland birds migrate to lower elevations (Jennings 2010). In general, the breeding season of this species varies across regions and the onset of breeding in the UAE remains largely unknown. It has been suggested that the species is double-brooded, with a first clutch produced at lower altitudes with juveniles hatching between October and April, and a second clutch produced subsequently after moving to higher altitudes from late March/April on (Jennings 2010). The nest is usually loosely constructed of grass and placed in a natural hollow on a hillside, concealed by a boulder or bush (Jennings 2010). There is the possibility that locally nests might be parasitised by the Common Cuckoo (Cuculus canorus), which is assumed to breed in Musandam (Oman) and maybe ranging into northern UAE (Jennings 2010).
Threats listed in assessment
Development in montane areas may potentially pose a threat, as may coastal development in its wintering range. Overgrazing outside of Protected Areas potentially could also 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
Assessment ID
330680
Taxon name
Anthus richardi
Uploaded by
National Red List Database
Scientific name
Anthus richardi
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
passeriformes
Family
motacillidae
Genus
Anthus
Species
richardi
Taxonomic notes and synonyms listed
Anthus richardi and A. cinnamomeus (del Hoyo and Collar (2016) were previously lumped as A. richardi following AERC TAC (2003); Dowsett and Forbes-Watson (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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
Retained in this Red List assessment due to its regional listing as Vulnerable as a breeding bird in the Arabian Peninsula, this species has a very small non-breeding population within the UAE. It is listed here as Endangered under Criterion D, having been adjusted down by one category because it has a relatively small population size in UAE compared to the regional and global population. Further research is required to identify whether the species may be being impacted by factors such as habitat loss.
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 or migrant individuals on passage to and from the breeding grounds. Numbers are highest between mid-September and mid-April, occasionally to early May, when the species is fairly common to common throughout the country (Pedersen et al. 2017). Individuals wintering in or migrating through the UAE breed in central-eastern 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 grassland, irrigated grassland, marshes, scrubland and cultivations (Richardson 1990, Richardson and Aspinall 1998, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere it is insectivorous and feeds mainly on beetles and grasshoppers (Tyler 2019). The species is a long-distance migrant and breeds between April and July in grasslands of Siberia and Kazakhstan (Tyler 2019).
Threats listed in assessment
Symes et al. (2015) does note that its habitat could be declining (with no first level threat described) in the wider Arabian Peninsula, although pesticide use is potentially a key threat in its wider range. Within the UAE itself, overgrazing in areas outside of Protected Areas could potentially be an issue for this species too.
History
It is considered 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