Assessment ID
330507
Taxon name
Calidris alpina
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
330506
Taxon name
Calidris temminckii
Uploaded by
National Red List Database
Scientific name
Calidris temminckii
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Calidris
Species
temminckii
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 has a restricted non-breeding population in the UAE, which qualifies it for listing as Endangered. Based on the stable global population, the species's status has undergone a regional adjustment downl by one category. Therefore, the species is considered Vulnerable 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 or of winter visitors (Pedersen et al. 2017). The species occurs in wetlands throughout the country, particularly along the coast. While numbers peak during autumn passage from August to December, the species has been recorded in the UAE in all months except June (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
Outside of the breeding season, this species inhabits inland freshwater wetlands such as pools and sewage farms, as well as marshes and mudflats along the coast (Richardson 1990, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere in inland habitats is feeds primarily of insects and their larvae as well as the occasional plant matter, while along the coasts it takes annelids, crustaceans and small molluscs (Johnsgard 1981, del Hoyo et al. 1996). The species is migratory and breeds in the tundra of northern Eurasia (del Hoyo et al. 1996). Individuals wintering in the UAE leave the breeding grounds in July to early August and migrate southward on broad front (del Hoyo et al. 1996, Snow and Perrins 1998). Part of the population moves further south to winter in sub-Sahara Africa.
Threats listed in assessment
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. Outside of the UAE, it is also threatened in its breeding range by shrinkage and deterioration of suitable habitats (due to eutrophication and the overgrazing of shore meadows), and by increased human recreational disturbance due to the building up of breeding sites (trampling and disturbance often lead to increased hatchling predation and abandonment of nests) (Ronka 1996). The species is also susceptible to avian influenza and may therefore be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Climate change could have an impact on this species in the future.
History
Assessed as VU (D) for 1996 based on similar population size and rescue effect.
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
330505
Taxon name
Calidris minuta
Uploaded by
National Red List Database
Scientific name
Calidris minuta
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Calidris
Species
minuta
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 non-breeding population in the UAE, which is assumed to be stable at high numbers. 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 likely to be of winter visitors and migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers peak between August and May, but non-breeding individuals may remain in the country 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
During the non-breeding season, this species inhabits coastal mudflats, estuaries, enclosed lagoons, tidal creeks and saltpans, but it also occurs at inland freshwater wetlands such as open pools in marshes and sandbanks along rivers (Urban et al. 1986, del Hoyo et al. 1996, Richardson and Aspinall 1998, Aspinall and Porter 2011).There is no information available about its diet in the UAE; elsewhere the diet consists chiefly of invertebrates like ants, Hymenoptera, Diptera, beetles, waterbugs, annelids, small molluscs, crustaceans and freshwater mites, but also of plant material (del Hoyo et al. 1996, Snow and Perrins 1998). The species is a long-distance migrant (del Hoyo et al. 1996). It breeds between late June and early July in the tundra of the Russian high Arctic (del Hoyo et al. 1996). Autumn movements to wintering grounds occur between July and November; the return migration occurring mid-May to early-June (del Hoyo et al. 1996). A typical migratory flock consists of 20-30 individuals (del Hoyo et al. 1996). Part of the population occurring in the UAE remains in the country over winter, while another part pauses in the country before continuing further south to wintering grounds in Africa (Richardson 1990). Many immatures also remain in the wintering grounds all year round (Richardson 1990, del Hoyo et al. 1996, Pedersen et al. 2017). The species is gregarious outside of the breeding season; and occurs in small groups in its winter range, often aggregating into larger flocks to roost at high tide or at night (Urban et al. 1986, Snow and Perrins 1998, Hockey et al. 2005).
Threats listed in assessment
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. This species is also susceptible to avian malaria (Mendes et al. 2005) and avian botulism (Blaker 1967, van Heerden 1974), so may be threatened by future outbreaks of these diseases. Climate change may have an impact on this species in the future.
History
The species would have qualified as Least Concern in 1996,;with c. 1,000-3,000 mature individuals in 1996 (EBRC data).
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
330503
Taxon name
Calidris tenuirostris
Uploaded by
National Red List Database
Scientific name
Calidris tenuirostris
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Calidris
Species
tenuirostris
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 very small non-breeding population in the UAE, which qualifies it for listing as Critically Endangered. On a global scale, the species is listed as Endangered due to a rapid decline. Therefore, breeding populations outside of the country may not have a large rescue effect, and the species is retained as Critically Endangered 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 or migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). The species is common on passage and fairly common during winter, occurring mostly in Umm al-Quwain Emirate at Khor Al Beidah, on Merawah Island and in Sharjah Emirate at Khor Kalba (Richardson 1990, Richardson and Aspinall 1998). Numbers peak between August and April, but single individuals are also recorded during summer (Richardson and Aspinall 1998, Pedersen et al. 2017). The species was first recorded in the UAE in 1986 and has been occurring regularly in the country since 1990 (Richardson and Aspinall 1998).
Is there a map available in assessment?
Yes
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat details as listed in assessment
During winter, the species inhabits sheltered coastal habitats such as inlets, bays, harbours, estuaries and lagoons with large intertidal mud and sandflats, oceanic sandy beaches with nearby mudflats, sandy spits and islets, muddy shorelines with mangroves and occasionally exposed reefs or rock platforms (del Hoyo et al. 1996, Higgins and Davies 1996, Aspinall and Porter 2011). On passage, the species stages in estuaries and on intertidal mudflats (Tomkovich 1997, Moores 2006). There is no information available about its diet in the UAE; elsewhere during winter and on passage, it takes bivalves up to 36 mm long from intertidal mudflats, as well as gastropods, crustaceans, annelid worms and echinoderms (del Hoyo et al. 1996, Higgins and Davies 1996). It forages in small groups (Johnsgard 1981). It roosts in refuges, such as shallow water in sheltered sites, on coastal dunes or on saltflats amongst mangroves during high tides (Higgins and Davies 1996, Rogers et al. 2006). This species is a long-distance migrant and largely travels along the coast with few stopovers, but utilises different routes in autumn and in spring (del Hoyo;et al.;1996, Higgins and Davies 1996). Individuals wintering in the UAE breed between May and July in north-east Siberia. The species leaves the breeding grounds in July and arrives on the wintering grounds between August and October (del Hoyo;et al.;1996). The return migration to the breeding grounds takes place from March to April,;although juvenile non-breeders often remain in the wintering range for the breeding season (Hayman;et al.;1986, del Hoyo;et al. 1996, Pedersen et al. 2017).
Threats listed in assessment
Within the UAE the main threats to this species are likely to due coastal land-use changes and potentially oil pollution, but the severity of these threats to this species is uncertain. Globally, the population is declining very rapidly, predominantly due to development of the East Asian-Australasian Flyway (especially in the Yellow Sea), but the degree of impact this has on the population that visits the UAE is unknown. The species is also potentially threatened by climate change because it has a geographically bounded distribution: its global distribution is restricted to within c. 10<sup>o</sup> latitude from the polar edge of continent, within which 20-50% of current vegetation type is projected to disappear under doubling of CO<sub>2</sub> levels (BirdLife International unpublished data).
History
It is thought likely that the population in 1996 exceeded 250 individuals but still fewer than 1,000, and the species is assessed as Vulnerable (D1) in 1996. Even though considered Least Concern in 1996, recent information has shown that in fact the global population was already declining rapidly at that time, and so no regional adjustment has been made to the 1996 assessment for this species.
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
330501
Taxon name
Actitis hypoleucos
Uploaded by
National Red List Database
Scientific name
Actitis hypoleucos
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Actitis
Species
hypoleucos
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 has a very small non-breeding population in the UAE, which qualifies it for listing as Endangered. On a global scale, the species is in decline and breeding populations outside of the country may not have a large rescue effect. Therefore, the species is precautionarily retained as Endangered 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 of migrant individuals on passage to and from the breeding grounds (Pedersen et al. 2017). Numbers are highest between late July and early May, when the species may be found on any freshwater wetland in the country, but individuals are recorded through the summer months as well (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 on the edges of freshwater wetlands, mostly at ponds, water treatment plants and in irrigated grassland (Richardson 1990, Aspinall and Porter 2011). It is rarely found in saline habitats like mudflats and only sometimes on shorelines and rocky coasts (Richardson 1990). There is no information available about its diet in the UAE; elsewhere it consists of adult and larval insects, spiders, molluscs, snails, crustaceans, annelids, and occasionally frogs, toads, tadpoles and small fish, as well as plant material (Urban et al. 1986, del Hoyo et al. 1996). It forages solitarily during the day (Richardson 1990, del Hoyo et al. 1996), but may aggregate at night into roosts of over 100 individuals (Johnsgard 1981, del Hoyo et al. 1996). The species is migratory (del Hoyo et al. 1996). It breeds between May and June on freshwater margins throughout Eurasia (del Hoyo et al. 1996, Snow and Perrins 1998). Immature individuals may also remain in the winter range throughout the summer breeding season (Snow and Perrins 1998, Pedersen et al. 2017).
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.
History
The population is thought to have been similar in 1996; significant impacts from development had not yet commenced, whilst wetland creation had also not started in a large way.
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
330500
Taxon name
Xenus cinereus
Uploaded by
National Red List Database
Scientific name
Xenus cinereus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Xenus
Species
cinereus
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 has a restricted but stable non-breeding population in the UAE, which qualifies it for listing as Endangered, however this assessment is downlisted by one category to Vulnerable given the large and Least Concern global population.
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 (Pedersen et al. 2017). The species is fairly common to common along the coast of the UAE, on passage also further inland (Pedersen et al. 2017). While it is recorded in all months, numbers peak between late July and October (Richardson 1990, Pedersen et al. 2017). Preferred wintering sites include Khor Al Beidah (Umm al-Quwain), Khor Al Jazeera (Ras al-Khaimah), Khor Kalba (Sharjah) and the lagoons around Abu Dhabi City (Richardson 1990).
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 is found along the coast, especially in mudflats, tidal pools and creek edges, mangroves and salt marshes (Richardson 1990, Aspinall and Porter 2011). During migration, the species may stop-over at inland freshwater wetlands, such as muddy lakes or river edges (Urban et al. 1986, del Hoyo et al. 1996).There is no information available about its diet in the UAE; elsewhere in the non-breeding season and on migration, the diet is varied and consists of insects, small molluscs, crustaceans (including crabs), spiders and annelid worms (del Hoyo et al. 1996). It forages both diurnally and nocturnally, but its nocturnal activities may be restricted to moonlit nights (Rohweder and Baverstock 1996). The species is migratory (del Hoyo et al. 1996). Individuals occurring in the UAE breed between May and June in boreal forest and tundra of north-western Asia; they migrate south overland through the Caspian region and the Middle East (del Hoyo et al. 1996). Many one-year-old and other non-breeding birds remain in the wintering grounds throughout the northern summer (Urban et al. 1986, del Hoyo et al. 1996, Pedersen et al. 2017).
Threats listed in assessment
Within its European range, the breeding success of this species is not well known, but there are indications that an overall increase of common gulls, crows and mammalian predators has led to increased nest predation (BirdLife International 2015). Anthropogenic habitats in the wood processing industry are subject to unpredictable changes that can drive small-ranged populations to extinction within a short period of time (BirdLife International 2015). However, 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. Climate change may have an impact on this species in the future.
History
In 1996 the population is thought to have been lower, but still qualifying as Endangered, and downlisted to VU.
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
330498
Taxon name
Tringa totanus
Uploaded by
National Red List Database
Scientific name
Tringa totanus
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Tringa
Species
totanus
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 moderate non-breeding population within UAE and record counts have shown the population to be increasing rapidly. The population size exceeds the threshold for Vulnerable under the relevant Criterion D, and so 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
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 July and April, when the species is very common particularly along the coast (Richardson 1990, Pedersen et al. 2017). The species breeds from northern Europe to north-eastern China; while a part of the population winters in the UAE, other individuals migrate further south to non-breeding grounds in East and Central 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 favours coastal zones, including rocky, muddy and sandy beaches, as well as mudflats (Richardson 1990, del Hoyo et al. 1996, Aspinall and Porter 2011). In smaller numbers, it can also be found at inland wetlands like sewage treatment plants, ponds, marshes and standing water (Richardson 1990, del Hoyo et al. 1996, Aspinall and Porter 2011). There is no information available about its diet in the UAE; elsewhere during the non-breeding season, the species takes insects, spiders and annelid worms, as well as molluscs, crustaceans and occasionally small fish and tadpoles (del Hoyo et al. 1996). Outside of the breeding season the species forages singly, in small groups or occasionally in larger flocks of up to c.1,000 individuals, especially at roosting sites or when feeding on fish (Hayman et al. 1986, del Hoyo et al. 1996, Snow and Perrins 1998). The species is migratory. It breeds between March and August solitarily or in loose colonies in swampy areas of north-central Eurasia (Hayman et al. 1986, Richardson 1990, del Hoyo et al. 1996). It leaves the breeding grounds from June to October, and returns from the wintering grounds between February and April (Hayman et al. 1986). Some non-breeding individuals may remain in the non-breeding grounds over summer (Pedersen et al. 2017).
Threats listed in assessment
The species is susceptible to avian influenza so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). 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
The population size is not known for 1996 but is presumed to exceed 1,000 mature individuals, and hence it is assessed as Least Concern for that year.
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