NT
Assessment ID
330519
Taxon name
Charadrius leschenaultii
Uploaded by
National Red List Database
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
330517
Taxon name
Charadrius dubius
Uploaded by
National Red List Database
Scientific name
Charadrius dubius
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
charadriidae
Genus
Charadrius
Species
dubius
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
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a small breeding and a very small non-breeding population. Both the breeding population and the non-breeding populations are assumed to be increasing within the UAE. The breeding population size is low enough, though, that it triggers listing as Vulnerable under Criterion D1. Based on the regional criteria, however, the breeding population warrants a regional adjustment of one category to Near Threatened due to the likelihood of a rescue effect.The non-breeding population is under a greater risk of extinction, qualifying as Endangered, but undergoing an adjustment down to Vulnerable based on global status (LC). However, the national status is based on its breeding population, which takes precedence. Therefore, overall the species is listed as Near Threatened.
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 breeds along the southwestern and west coast of the UAE, as well as in the mountains in the northern and north-eastern part of the country (Jennings 2010, Pedersen et al. 2017). The breeding population is temporarily supplemented by migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Some individuals stay in the country during the non-breeding season (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
During the breeding season, this species inhabits preferably freshwater sites like gravelly river islands, sandy shores of lakes, brackish and freshwater ponds as well as sewage treatment plants, and is also found at pools in remote deserts and along streams in the mountains (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). The preferred habitat of individuals overwintering in the UAE is not well known; but it may frequent more coastal areas like mudflats (Aspinall and Porter 2011). Migrants mainly occur in small flocks between February and April on their journey to the breeding grounds and between September and October on passage to the wintering grounds; they tend to stay further inland at temporary desert rain pools, while avoiding mudflats along the coast (Richardson 1990, Jennings 2010). Its diet consists mainly of terrestrial and aquatic invertebrates, which it takes from the water surface or wet ground, often near fish drying places or livestock enclosures (Jennings 2010). The breeding season lasts from March to July (Jennings 2010). The species is territorial and nests in open areas with patches of sand or shingle near streams and lagoons of freshwater, brackish water or irrigated lands (Jennings 2010). The nest consists of a shallow, unlined depression in gravel or bare ground, in which three to four eggs are laid (Jennings 2010).
Threats listed in assessment
The main potential threat to this species within UAE is the infilling of its wetland habitat (Aspinall 1996).
History
The breeding population is thought to have been 150-300 mature individuals in 1996, qualifying as Endangered, but adjusted down to Vulnerable based on rescue effect. The population has increased since then and it is now listed as Near Threatened.
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
330516
Taxon name
Charadrius hiaticula
Uploaded by
National Red List Database
Scientific name
Charadrius hiaticula
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
charadriidae
Genus
Charadrius
Species
hiaticula
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
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a very small non-breeding population in the UAE, which qualifies it for listing as Vulnerable. On a global scale, the species is in slight decline however still Least Concern. Therefore, the species is downlisted by one category to Near Threatened (D1) 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 in the UAE are likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). The species is very common between mid-August and October along the coast (Richardson 1990, Pedersen et al. 2017). Some individuals stay in the country over summer, though they do not breed (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 along coastal creeks, in tidal mudflats and along sandy, muddy and stony shores (Richardson 1990, Aspinall and Porter 2011). During migration, is also found further inland in marshes and larger water bodies (Richardson 1990). There is no information available about its diet in the UAE; elsewhere, the diet consists of small crustaceans, molluscs, polycheate worms, isopods, amphipods, insects (e.g. ants, beetles, flies and fly larvae) and millipedes (del Hoyo et al. 1996). The species is gregarious and often roosts communally in flocks of several hundred individuals close to its feeding areas (Hayman et al. 1986, Urban et al. 1986, del Hoyo et al. 1996). The species is migratory. Individuals wintering in the UAE or further south breed between April and June in solitary pairs or loose colonies along the Arctic coast and in the tundra of northern Eurasia (del Hoyo et al. 1996).
Threats listed in assessment
The most relevant threats within UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown.Individuals of this species that visit UAE are also potentially threatened by a range of threats that operate outside of the country. Migratory stop-over habitats for this species may be threatened by petroleum pollution, wetland drainage for irrigation, land abandonment and changing land management practices leading to scrub overgrowth (Grishanov et al. 2006). The species is also susceptible to avian botulism, so may be impacted on by future outbreaks of the disease (Blaker 1967). Climate change is a potential future threat.
History
The population size in 1996 is thought to have been more or less the same as at present, with anthropogenic wetland habitats replacing those lost to development on the coast, so the species is also assessed as NT for 1996.
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
330510
Taxon name
Calidris pugnax
Uploaded by
National Red List Database
Scientific name
Calidris pugnax
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Calidris
Species
pugnax
Taxonomic notes and synonyms listed
Calidris pugnax (del Hoyo and Collar 2014) was previously placed in the genus Philomachus.
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
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a restricted non-breeding population in the UAE, which qualifies it for listing as Vulnerable. However the population is stable within the country and globally. Therefore, the species's status has been regional adjusted down to Near Threatened 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 likely to be of migrant individuals on passage to and from the breeding grounds, which are common to very common at wetlands throughout the country (Pedersen et al. 2017). Numbers peak between July and December, and between February and April (Richardson 1990). Moreover, the species is a fairly common winter visitor, while single individuals have also been recorded during summer (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 freshwater wetlands like creeks, pond edges, wet grassland and sewage treatment plants, but also in saline habitats like coastal lagoons and mudflats (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere on passage and during winter, it takes insects, small crustaceans, spiders, molluscs, annelid worms, frogs, small fish and plant material (del Hoyo et al. 1996). The species is migratory. It breeds from May to August in northern Eurasia, particularly in tundra habitats from the coast to the Arctic treeline (Johnsgard et al. 1981, Hayman et al. 1986, del Hoyo et al. 1996). The species leaves the breeding grounds between late-June and August and returns from the wintering grounds from March to mid-May (del Hoyo et al. 1996). The species migrates in large flocks of hundreds or thousands of individuals and forms huge dense groups on its wintering grounds (Hayman et al. 1986, del Hoyo et al. 1996).
Threats listed in assessment
Across its global range the species is threatened by petroleum pollution, wetland and flood-plain drainage (for irrigation and water management), peat-extraction, and land abandonment and changing land management practices that lead to scrub and reed overgrowth (del Hoyo et al. 1996, Grishanov 2006). The species may also suffer future population declines and range contractions as a result of global climate change (Zöckler 2002), and is susceptible to avian influenza (Melville and Shortridge 2006, Gaidet et al. 2007), avian botulism (Blaker 1967, van Heerden 1974, Hubalek et al. 2005) and avian malaria (Mendes et al. 2005), so may be threatened by future outbreaks of these diseases. The most relevant threats within the UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown.
History
The population is thought likely to have been the same or similar in 1996, and it is assessed as NT.
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
330504
Taxon name
Calidris alba
Uploaded by
National Red List Database
Scientific name
Calidris alba
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Calidris
Species
alba
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
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a restricted non-breeding population in the UAE, which qualifies it for listing as Vulnerable (D1). The population is stable within the country. The global population is stable, therefore, the species's status has undergone a regional adjustment down by one category to Near Threatened 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 likely to be of migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers peak between April and May and in September. While the species is scarcer in winter, it has been recorded during the entire year (Pedersen et al. 2017). The species occurs mainly along the coastline, but during passage it may also occur at wetlands further inland (Richardson 1990, Aspinall and Porter 2011), and it is also found on near-shore and some offshore islands. Recorded from 50+ sites across the UAE (EAD unpublished data).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
During the non-breeding season, this species inhabits sandy beaches and mudflats along the coast (Richardson 1990, Aspinall and Porter 2011). During migration, it is also found further inland along shallow muddy creeks and pools (Richardson 1990). There is no information available about its diet in the UAE; elsewhere during winter, its diet consists of small molluscs, crustaceans, polychaete worms and adult, larval and pupal insects, as well as occasionally fish and carrion (del Hoyo et al. 1996). It forages in small flocks (Richardson 1990, del Hoyo et al. 1996). The species is a long-distance migrant (del Hoyo et al. 1996). It breeds between June and July in the high Arctic on barren, stony tundra (Johnsgard 1981, del Hoyo et al. 1996). During migration, it travels in small flocks mainly via offshore and coastal routes to the wintering grounds along the coastlines of all southern continents (Johnsgard 1981, Richardson 1990, del Hoyo et al. 1996).
Threats listed in assessment
The species is sensitive to disturbance on beaches (del Hoyo et al. 1996) (e.g. from recreational activities and free-running dogs; Thomas et al. 2003), and is susceptible to avian influenza so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Changes in coastal land-use and the possibility of oil pollution could affect this species in UAE, but the severity of these threats towards this species is unknown. Climate change is likely to have an effect on this species in the future.
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
330502
Taxon name
Arenaria interpres
Uploaded by
National Red List Database
Scientific name
Arenaria interpres
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Arenaria
Species
interpres
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
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a restricted non-breeding population in the UAE, which qualifies it for listing as Vulnerable. On a global scale, the species is in slight decline, however it is still considered Least Concern. The population is stable within the UAE; natural wetland habitats within the UAE are likely to be deteriorating due to land conversion, however new anthropogenic habitats have been created. Therefore, the species is downlisted by one category to Near Threatened.
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 (Pedersen et al. 2017). Numbers peak in the UAE between August and October and between March and May, when the species is common throughout the country (Richardson 1990, Pedersen et al. 2017). The species is fairly common during winter, mainly along the coast (Pedersen et al. 2017). A small number of non-breeding individuals remains over summer in the UAE (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 winters along the coast, where it frequents sandy or rocky beaches, mudflats or tidal creeks (Richardson 1990, Aspinall and Porter 2011). Only during migration, it is found on lakes or sewage treatment plants further inland (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere outside the breeding season, it mainly feeds on insects, crustaceans, molluscs, annelids, echinoderms, small fish, carrion and birds eggs (del Hoyo et al. 1996). The species is fully migratory (del Hoyo et al. 1996). Birds wintering in the UAE breed from May to August in solitary pairs along the coast or on islands in the high Arctic (Hayman et al. 1986, del Hoyo et al. 1996, Snow and Perrins 1998). Part of the population may migrate further south to winter along the coast of eastern and southern Africa. Someone-year-old birds remain in the wintering range during the summer. The species migrates in large flocks and is gregarious and sociable when feeding or roosting in winter, often foraging in large flocks in tidal areas (del Hoyo et al. 1996, Snow and Perrins 1998).
Threats listed in assessment
The most relevant threats within the UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown. It is also susceptible to avian influenza so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Climate change is also a future potential threat.
History
Considered Vulnerable (D1) in 1996 revised down by one category to Near Threatened as a result of potential rescue effect from the global population.
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
330499
Taxon name
Tringa nebularia
Uploaded by
National Red List Database
Scientific name
Tringa nebularia
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Tringa
Species
nebularia
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
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a small and stable non-breeding population in the UAE, which qualifies it for listing as Vulnerable. On a global scale, the species is stable, so breeding populations outside of the country may have a large rescue effect. Therefore, the species's status is adjusted down by one step to Near Threatened 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 in the UAE are likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers are highest between August and April, when the species is very common along the coast and at wetlands throughout the country (Aspinall and Porter 2011, Pedersen et al. 2017). The species breeds in the northern temperate zone of Eurasia; while a part of the population winters in the UAE, other individuals migrate further south to non-breeding grounds in Indo-China and sub-Sahara Africa (Richardson 1990). Single non-breeding individuals remain in the UAE over summer (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 inhabits a variety of freshwater, marine and artificial wetlands, including coastal shores and mudflats, inland wetlands and pond edges, as well as water treatment plants and sewage outlets (Richardson 1990, el Hoyo et al. 1996, Aspinall and Porter 2011). During migration, the species occurs on inland flooded meadows, dried-up lakes, sandbars and marshes (del Hoyo et al. 1996). There is no information available about its diet in the UAE; elsewhere it is chiefly carnivorous, its diet consisting of insects and their larvae, crustaceans, annelids, molluscs, amphibians, small fish and occasionally rodents (del Hoyo et al. 1996, Hockey et al. 2005). It feeds singly, both diurnally and nocturnally (Richardson 1990, del Hoyo et al. 1996). The species is migratory. It breeds between late April and June in dispersed pairs in swampy boreal forests throughout Eurasia (Johnsgard 1981, del Hoyo et al. 1996, Snow and Perrins 1998). On passage, it can occur singly or in small flocks, although congregations of 100 or more may very rarely occur at high tide or at roosting sites (Urban et al. 1986, Richardson 1990, Snow and Perrins 1998). Some non-breeding birds may remain in the wintering grounds throughout the summer (del Hoyo et al. 1996, Snow and Perrins 1998, Pedersen et al. 2017).
Threats listed in assessment
Within Europe the species has suffered in some areas from habitat degradation caused by off-road vehicles or dry conditions causing vegetation to become rank (Hagemeijer and Blair 1997), but it is unsure whether these threats affect individuals of this species that visit UAE. The most relevant threats within UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown.
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
330496
Taxon name
Numenius phaeopus
Uploaded by
National Red List Database
Scientific name
Numenius phaeopus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Numenius
Species
phaeopus
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
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a restricted non-breeding population in the UAE, which qualifies it for listing as Vulnerable. The population is increasing within the country, and the species is assessed as Least Concern globally, although some declines are recorded. Therefore, the species's status is tentatively adjusted down to Near Threatened (D1) 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 likely to be of migrant individuals on passage to and from the breeding grounds. The species is very common particularly between August and September (Pedersen et al. 2017). It is less common in winter, when it is found mainly close to the coast (Richardson 1990, Pedersen et al. 2017). A few non-breeding individuals remain in the country over summer (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 along the coastline, where it frequents estuaries, sandy or rocky beaches, mangrove swamps, tidal ponds and creeks, mudflats or coral reefs (Richardson 1990, del Hoyo et al. 1996, Richardson and Aspinall 1998, Aspinall and Porter 2011). Especially during migration, it is also found further inland at freshwater sites like pools, sewage treatment plants or damp grassland (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE or Arabia; elsewhere, when inland on migration, its diet consists of adult and larval insects, spiders, earthworms, molluscs and plant material (Johnsgard 1981, del Hoyo et al. 1996). On the coast during the winter, the species takes crustaceans, molluscs, large polychaete worms and occasionally fish, reptiles or young birds (del Hoyo et al. 1996). The species is migratory (del Hoyo et al. 1996, Snow and Perrins 1998). It breeds from May to August in the tundra of the Eurasian Arctic (Hayman et al. 1986, del Hoyo et al. 1996).
Threats listed in assessment
The most relevant threats within UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown. The species is susceptible to avian influenza, so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006), and climate change is a potential future threat.
History
The species is also thought to qualify as Vulnerable (D1) in 1996, downlisted to NT.
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
330493
Taxon name
Gallinago gallinago
Uploaded by
National Red List Database
Scientific name
Gallinago gallinago
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Gallinago
Species
gallinago
Taxonomic notes and synonyms listed
Gallinago gallinago and G. delicata (del Hoyo and Collar 2014) were previously lumped as G. gallinago 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
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a restricted non-breeding population in the UAE, which qualifies it for listing as Vulnerable. However, the population is increasing within the country, therefore, the species's has undergone a regional adjustment down to Near Threatened (D1) 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
This species is common in the UAE between late August and April, when wintering birds and migrant individuals on passage to and from the breeding grounds occur at wetlands throughout the country (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 inhabits freshwater wetlands, including wet or flooded grasslands, marshes, pond edges, ditches and water treatment plants overgrown with vegetation (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere the diet includes insects, earthworms, small crustaceans, small gastropods and spiders, but also plant fibres and seeds in smaller quantities. The species forages in small groups by vertical and rhythmic probing in substrate, often without removing the bill from the soil. The species is migratory and breeds between April and June throughout Eurasia.
Threats listed in assessment
The most relevant threats within the UAE are changes in land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown. Individuals that visit the UAE will also be impacted by a range of threats that occur outside of the country:Declines noted in breeding populations of Europe are probably chiefly due to habitat changes, especially drainage (BirdLife International 2015). Low water levels shorten the period of food availability in pastures, due to the lower penetrability of soil, and thereby strongly influence the length of the breeding season (BirdLife International 2015). Changes in habitat structure and food abundance, which already negatively affect this (and many other) species might also lead to increased predation risks for nestlings (BirdLife International 2015). Estimated 1,500,000 birds are hunted annually in Europe (Van Gils;et al. 2015).
History
Populations would have been smaller in 1996, qualifying as Endangered, adjusted down to VU after rescue effect from the large global population. These increases are likely due to increased availability of artifical water sources.
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
330490
Taxon name
Fulica atra
Uploaded by
National Red List Database
Scientific name
Fulica atra
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
gruiformes
Family
rallidae
Genus
Fulica
Species
atra
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
Near Threatened
Abbreviated status
NT
Qualifying criteria (if given)
D1
Criteria system used
IUCN
(see Assessment details)
Assessment rationale/justification
This species has a restricted resident population in the UAE, and even though it is supplemented in the non-breeding season, it qualifies the species for listing as Endangered in both the breeding and non-breeding seasons. However, the resident/breeding population is increasing, and the potential for immigration from outside the UAE remains very high. The species is stable/increasing within the Arabian Peninsula. Therefore, the species has been reduced by two categories and is thus listed as Near Threatened 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 likely to be of wintering birds and migrant individuals on passage to and from the breeding grounds in central Eurasia. Numbers are highest between mid-October and mid-March, when the species is locally common at large wetlands throughout the country. A resident population has recently become established; since 2002 the species has been regularly breeding at the Warsan Lake near Dubai City (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 inhabits large, open freshwater bodies like lakes, reservoirs, large ponds with grassy margins, or water treatment plants (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). It is seldom found on densely vegetated wetlands (Jennings 2010). In winter, it occasionally occupies saltwater habitats like sheltered coastal harbours (Richardson 1990, Jennings 2010). During migration, it may also occur on islands and even in arid desert (Jennings 2010). There is no information available about its diet in the UAE; elsewhere it is omnivorous, although its diet consists primarily of vegetable matter such as algae, the vegetative pasts of aquatic and terrestrial plants, the seeds of waterweeds, sedges, water-lilies, grasses and cereal crops, clubmoss Selaginella and aquatic fungi (del Hoyo et al. 1996, Taylor and van Perlo 1998). Animal matter in its diet includes molluscs, adult and larval insects, worms, leeches, shrimps, spiders, small fish, fish eggs, frogs, birds and bird eggs, and small mammals (Urban et al. 1986, del Hoyo et al. 1996, Taylor and van Perlo 1998). It may feed in flocks on land, especially when winds cause high waves on water (del Hoyo et al. 1996). The species is diurnally active and roosts at sunset solitarily or in flocks (Taylor and van Perlo 1998). The breeding season in Arabia lasts from May to June and clutches may contain around six eggs (Jennings 2010). There is nothing known about its nests in Arabia; elsewhere it is a platform of vegetation that may be resting on the bottom of shallow water, floating or on a foundation of trampled plant matter in emergent vegetation (del Hoyo et al. 1996).
Threats listed in assessment
Across its range, the species suffers from threats that could impact individuals that pass through or overwinter in UAE. These threats include oil and petroleum pollution (del Hoyo et al. 1996, Grishanov 2006), habitat degradation and loss due to agricultural drainage schemes (Taylor and van Perlo 1998), wetland drainage, changing wetland management practices and the burning and mowing of reeds (Grishanov 2006). The species is often drowned in freshwater fishing nets with mesh sizes greater than 5 cm (Quan et al. 2002). It is also susceptible to avian influenza, so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Hunting may also impact this species (del Hoyo et al. 1996, e.g. in Iran; Balmaki and Barati 2006). Of these threats, some such as changing land-use and oil pollution may also have impacts on the species within the UAE, particularly at the coast.
History
Breeding was not conformed in the UAE until 2002, and it is considered NA for the 1996 UAE Red List. The assessment here is, therefore, based on the non-breeding population. The species has increased since 1996, but it is tentatively suspected that the minimum population size would still have been >50 mature individuals in 1996, which would have still qualified it as Endangered then, and with regional adjustments taken into account the Red List status it would have received in 1996 would have been the same as here.
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