NT

Bubulcus ibis | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species inhabits inland freshwater areas, like marshes, bogs, ditches, wet or irrigated grassland, occasionally creeks, but only rarely coastal areas and saltwater habitats (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). Particularly the resident population is well adapted to humans and can be considered commensal; when feeding, it often visits human sites, including crop fields, livestock enclosures, rubbish dumps and gardens (Jennings 2010). Its diet consists primarily of insects and small reptiles (Jennings 2010). The species is a diurnal feeder (del Hoyo et al. 1992). It breeds colonially; in Dubai, the colony is shared with breeding Sacred Ibis Threskiornis aethiopicus (del Hoyo et al. 1992, Jennings 2010). The timing of the breeding season in eastern Arabia is not known; in general, the species may breed throughout the year with different regional peaks depending on food availability (del Hoyo et al. 1992, Kushlan and Hancock 2005). The nesting effort of the species is related to rainfall patterns, leading to an annual variation in productivity (Kushlan and Hancock 2005). The nest is constructed of sticks and positioned in a bush or tree, preferably acacia, tamarisk or ghaf (Jennings 2010). In Arabia, clutches contain two to three, seldom up to five eggs (Jennings 2010). Outside of the breeding season the species remains gregarious (Brown et al. 1982, del Hoyo et al. 1992).
Taxon
Taxa
Bubulcus ibis | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
The resident population is increasing in the UAE; it has been breeding regularly at a site near Dubai City since 2001 and has bred near Al Ain (Abu Dhabi Emirate) in 2013 and 2015 (Pedersen et al. 2017). The resident population is supplemented by wintering birds between December and late April, as well as by migrant individuals stopping-over in April/May and in October/November on passage to and from the breeding grounds (Richardson 1990, Pedersen et al. 2017). During these periods, the species is common at wetlands throughout the country (Richardson 1990, Pedersen et al. 2017).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
The population size of the breeding population qualifies as Endangered under Criterion D. However, because there is a high likelihood of rescue effect, the species has received a regional adjustment of two categories down to Near Threatened (D1). The non-breeding population qualifies as Least Concern.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
The most relevant threats to this species within UAE are potentially from wetland land-use changes, and possibly oil pollution at coastal sites, although the severity of these threats is essentially unknown. Individuals that visit UAE may also be impacted upon by other threats. In its wider breeding range outside of the UAE, the species is threatened by wetland degradation and destruction, for reasons such as lake drainage for irrigation and hydroelectric power production (Balian;et al.;2002), and in some parts of its range it is susceptible to pesticide poisoning (organophosphates and carbamates) (Kwon;et al.;2004). Large colonies nesting in urban areas are perceived as a public nuisance and may be persecuted (e.g. by disturbance to prevent colony establishment, removal or direct killing) (Kushlan and Hancock 2005).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The species was first confirmed as breeding in Dubai in 1998, and so it would not have been assessed in 1996. However there was a non-breeding population, for which we can look to see if there was a genuine change. In 1996, the non-breeding population size was fewer than 200 mature individuals, which qualifies as Endangered. The category is adjusted to Vulnerable based on a regional adjustment of one step. Now it is considered Least Concern. Its increase is likely linked to increases in the availability of suitable artificial habitats.
Verified entry
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Ardea alba | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species occurs at large, shallow inland wetlands rich with fish (Richardson 1990, del Hoyo et al. 1992, Aspinall and Porter 2011). It frequents mainly rivers and creeks, marshes and lakes (Richardson 1990).;Outside of the breeding season, the species may feed solitarily or in small loose groups, although flocks of hundreds or more individuals may form where food is abundant (Brown et al. 1982, Marchant and Higgins 1990, del Hoyo et al. 1992). The species is a diurnal feeder, but is most active at dawn and dusk (del Hoyo et al. 1992, Kushlan and Hancock 2005). The species is migratory. Individuals wintering in or migrating through the UAE may breed in southern-central Asia. The timing of the breeding season varies geographically, but concentrates around spring and summer. The species typically breeds in colonies of tens, hundreds or even a thousand pairs, sometimes with other species (del Hoyo et al. 1992, Kushlan and Hancock 2005).
Taxon
Taxa
Ardea alba | Linnaeus, 1758
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Ardea alba;(del Hoyo and Collar 2014);was previously placed in the genus Casmerodius as C. albus. Casmerodius albus (Sibley and Monroe 1990, 1993) was previously retained as a cross-regional species contra Christidis and Boles (2008) who moved;C. albus into the genus Ardea and split it into two cross-regional species A. alba and A. modesta (note gender agreement of specific name for alba).
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). Numbers are highest between August and April, when the species is common at large wetlands throughout the country (Richardson 1990, Pedersen et al. 2017). Some non-breeding individuals stay in the country over summer (Richardson 1990, Pedersen et al. 2017).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has a small non-breeding population in the UAE, which qualifies it for listing as Endangered. The population has increased within the country since 1996 but the trend is now thought to be stable.Conditions outside of the UAE are considered unlikely to deteriorate, so there is a potentially very high rescue effect from individuals outside of the country. Therefore, the species is downlisted by two categories to Near Threatened at the national level.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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 threatened by a range of threats that operate outside of the country. Globally, the species is threatened by wetland habitat degradation and loss (Marchant and Higgins 1990, del Hoyo et al. 1992) for example through drainage, grazing, clearing, burning, increased salinity, groundwater extraction and invasion by exotic plants (Marchant and Higgins 1990). The species previously suffered from intense persecution for the plume trade (this is no longer a threat) (del Hoyo et al. 1992). Climate change is a potential future threat.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
In 1996, the species was less common, however with a population size that still exceeds 50 mature individuals, found in natural lagoons rather than in anthropogenic habitats. The species qualified as Endangered, downlisted by two categories to Near Threatened based on the significant global rescue effect.
Verified entry
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Phalacrocorax carbo | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species occurs along the coast, where it frequents sandbanks, lagoons and coastal breakwaters (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). It is occasionally found at large inland lakes like dams, reservoirs and fish farms (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). It feeds predominantly on fish, which it are caught by diving pursuits (del Hoyo et al. 1992, Jennings 2010). Birds wintering in the UAE may breed in Turkey, the southern Caspian region or southern Pakistan (Jennings 2010).
Taxon
Taxa
Phalacrocorax carbo | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
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). Numbers are highest between November and March, when the species is common in coastal zones and occasionally at inland wetlands (Richardson 1990, Pedersen et al. 2017). A small number of individuals remain in the country over summer (Pedersen et al. 2017).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has a small non-breeding population in the UAE, which might qualify it for listing as Vulnerable. However, the population is stable, indicating that the conditions within the UAE are not deteriorating. Moreover, the species is increasing globally, so there is a potentially high rescue effect from individuals outside of the country. Therefore, the species's status has undergone a regional adjustment down one category and is classified as Near Threatened at the national level.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
Due to the species's foraging behaviour (shallow diving) and habit of hunting within purse-seine and gill-nets, the species is particularly susceptible to bycatch. Although these unintentional effects of fishing activities are not currently found to be driving colony declines, they could present problems on both local and global scales if populations were to decline (Bregnballe and Frederiksen 2006). The species is also susceptible to oil spills across its range.Outside of the UAE the species also faces a range of other threats, which could impact individuals that visit the country. The species is often persecuted by the aquaculture industry and may be shot, drowned or poisoned in attempts to control numbers (Carss 1994) or for hunting;(Bzoma;et al. 2011). It may also suffer from disturbance from coastal wind farms (wind turbines) (Bradbury;et al. 2014), and is susceptible to avian influenza (Melville and Shortridge 2006) and Newcastle disease (Kuiken 1999), so may be threatened by future outbreaks of these viruses (Kuiken 1999, Melville and Shortridge 2006).;Recreational activities taking place at sea may also cause displacement from critical habitat. The species is hunted for recreation and is sold at commercial food markets in some countries e.g. Iran (Balmaki and Barati 2006).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
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Thalasseus bergii | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species occurs on the open sea up to 50 km off the coast, and only comes to offshore islands or to the mainland for resting on sandy beaches (Jennings 2010, Aspinall and Porter 2011). It forages in small groups by plunge-diving or surface-dipping (Jennings 2010). There is no information available about its diet in the UAE; elsewhere, it feeds predominantly on small pelagic fish, but it will opportunistically take cephalopods, crustaceans, insects and hatchling turtles (Urban et al. 1986, del Hoyo et al. 1996, Higgins and Davies 1996). The species also preys on chicks of White-cheeked Tern Sterna repressa and Lesser Crested Tern Thalasseus bengalensis (Jennings 2010). The species breeds in spring to early summer; in the UAE, eggs have been recorded between May and June (Jennings 2010). It breeds on offshore islands in large dense colonies of up to 1,000 pairs, often associated with Lesser Crested Tern Thalasseus bengalensis and other tern species (Jennings 2010). The colonies are located on open, sandy areas (Jennings 2010). On Qarnayn;Island, the nesting habitat is in the soft sandy areas on the northwestern part of the island. A single egg is laid on the bare sand; only during incubation and nestling stage, a shallow scrape develops (Jennings 2010). Juveniles leave the nests a few days after hatching and form crèches along the shoreline (Jennings 2010). After the breeding season, individuals breeding off the UAE coast migrate south as far as the coast of Kenya, while birds from the northern Arabian Gulf may winter in the UAE (Jennings 2010).
Taxon
Taxa
Thalasseus bergii | (Lichtenstein, 1823)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Thalasseus bergii (del Hoyo and Collar 2014) was previously placed in the genus Sterna.
Taxon distribution as listed in assessment
The majority of occurrences of this species is likely to be of migrant individuals on passage to and from the breeding grounds and of wintering birds along the coast of the UAE (Pedersen et al. 2017). Additionally, the species is a rare breeding visitor on Qarnayn;Island, with breeding on Sir Abu Nair to be confirmed. It breeds between March and November (Jennings 2010, Pedersen et al. 2017).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D2
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
Assessment rationale/justification
This species has a moderate breeding population in the UAE of 2,700-3,000 mature individuals. The species is known to currently nest on only one island (Qarnayn Island), with evidence of breeding on Sir Abu Nair to be confirmed. On Qarnayn Island, the impact of introduced predators is significant. However, the species is stable within the country and in the wider Arabian Peninsula and there is no evidence of continuing decline in population, AOO or quality or extent of habitat in the UAE. The species is assessed as Vulnerable (D2). However, the potential for immigration from outside the UAE remains very high. Therefore, the species is listed as Near Threatened at the national level.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
On Qarnayn;Island, threats include predation by rats and cats. Aspinall (1996) identifies the key threats to this species as egg collecting, invasive mammals, development, disturbance and pollution (e.g. from oil, and other chemicals). The severity of these threats, however, is uncertain.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is thought that the species previously nested on two islands with restricted EOO and AOO and qualifying as two locations. At the time it would not have been deemed that threats could have driven the species Regionally Extinct or Critically Endangered in a short period of time and so the species is thus backcast as Near Threatened in 1996, downlisted with a regional adjustment to Least Concern as a result of the substantial potential for immigration from outside the UAE. With the species now restricted to just one location, threats are now deemed to be able to drive the species Regionally Extinct or to Critically Endangered within a short period of time; hence its current listing as Near Threatened (regionally adjusted down from Vulnerable).
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Charadrius leschenaultii | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
Habitat details as listed in assessment
This species is mainly coastal (Jennings 2010, Aspinall and Porter 2011). It inhabits sandy and rocky beaches, low sand dunes, salt and mud flats, as well as saline creeks on sheltered coasts (Richardson 1990, Jennings 2010). Occasionally, it can be found on wetlands inland, such as irrigated grasslands and marshes (Richardson 1990). Its diet in the UAE is not known; elsewhere in Arabia, the species feeds on crabs and other crustaceans, marine worms, molluscs and terrestrial invertebrates like ants, beetles and ticks (Jennings 2010). The species is migratory, and is likely to migrate without stopping on a broad front between breeding and non-breeding areas (del Hoyo et al. 1996). Individuals wintering in the UAE breed from the eastern Caspian region to eastern Kazakhstan (Jennings 2010). Migratory flocks form after the end of breeding between mid-June and early-August, and arrive in the wintering grounds between mid-July and November (adults and immature birds arriving before juveniles) (del Hoyo et al. 1996). The species is typically gregarious, feeding in flocks of 2-50 individuals, and sometimes congregating in groups of up to 1,000 individuals when roosting (Urban et al. 1986, del Hoyo et al. 1996). It often associates with other plovers like Lesser Sandplover Charadrius mongolus (Jennings 2010).
Taxon
Taxa
Charadrius leschenaultii | Lesson, 1826
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxon distribution as listed in assessment
This species is very common during winter and during passage to and from the breeding grounds, when it occurs mostly along the coast (Aspinall and Porter 2011, Pedersen et al. 2017). Main wintering sites include Khor Kalba (Sharjah Emirate) and Khor Al Beidah (Umm al-Quwain Emirate) (Richardson 1990). The highest numbers are recorded in April and in September/October (Richardson 1990). Some individuals remain in the UAE during summer (Pedersen et al. 2017).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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 still considered as Least Concern although declines have been observed, however a rescue effect is still considered likely. The population is stable within the country, and the assessment category is revised from Vulnerable by one category to Near Threatened.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.The species also faces a range of threats globally, that could have an impact on individuals that visit the country. In some parts of its breeding range this species is threatened by the destruction of wetlands and bordering fallow steppe through drainage and water extraction for irrigation (Turkey) (del Hoyo et al. 1996, Snow and Perrins 1998). Favoured migration staging posts, such as the Çukurova delta in southern Turkey are under increasing pressure from hunting, tourism and industrial activities, and are often polluted along the coast with oil (Tucker and Heath 1994).;The species is also susceptible to disturbance from tourists (e.g. National Parks and Wildlife Service 1999, Wearne and Underhill 2005).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
While the species was not observed prior to 1988, and still observed in small numbers at individual sites in 1996, it is thought that the overall population size would still have qualified the species as Vulnerable in 1996, downlisted by one step to Near Threatened.
Verified entry
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Charadrius dubius | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
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).
Taxon
Taxa
Charadrius dubius | Scopoli, 1786
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
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).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
Threats listed in assessment
The main potential threat to this species within UAE is the infilling of its wetland habitat (Aspinall 1996).
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
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.
Verified entry
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Charadrius hiaticula | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
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).
Taxon
Taxa
Charadrius hiaticula | Linnaeus, 1758
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
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).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
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.
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Calidris pugnax | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
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).
Taxon
Taxa
Calidris pugnax | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
Taxonomic Notes
Calidris pugnax (del Hoyo and Collar 2014) was previously placed in the genus Philomachus.
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).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
The population is thought likely to have been the same or similar in 1996, and it is assessed as NT.
Verified entry
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Calidris alba | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
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).
Taxon
Taxa
Calidris alba | (Pallas, 1764)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
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).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
History
It is assessed that in 1996, the national Red List status of this species would have been the same as in this assessment.
Verified entry
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Arenaria interpres | UAE National Red List of Birds

Location
Scope (Assessment)
National
Countries in Assessment
United Arab Emirates
Country ISO code(s)
ARE
Does the assessment cover a marine EEZ area(s)?
Off
Is there a map available in assessment?
Yes
Ecological system type
Terrestrial system
No
Freshwater system
No
Marine system
No
Habitat
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).
Taxon
Taxa
Arenaria interpres | (Linnaeus, 1758)
Taxonomic Group
Vertebrates
Taxonomic Group Level 2
Birds
Assessed taxon level
Species
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).
Assessed status
Asessment status in full
Near Threatened
Assessment status abreviation
NT
Assessment status criteria
D1
About the assessment
Assessment year
2019
Assessors/contributors/reviewers listed
UAE National Red List Workshop
Affliation of assessor(s)/contributors/reviewers listed on assessment
Government
IGO
Assessor affiliation specific
Government|IGO
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.
Criteria system
Criteria system specifics
IUCN v3.1 + Regional Guidelines v4.0
Criteria system used
IUCN
Criteria Citation
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.
Endemism
Endemic to region
Not_assigned
Endemism Notes
Is an endemic?: Not_assigned
Conservation
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.
Conservation Measures

Conservation measures:
Conservation measures notes:
Required conservation measures:

Further information
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.
Verified entry
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