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NRLD - 330490 | Fulica atra

Assessment ID
330490
Taxon name
Fulica atra
Linnaeus, 1758
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Fulica atra
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
gruiformes
Family
rallidae
Genus
Fulica
Species
atra
Species authority
Linnaeus, 1758
Location and scope
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
Conservation Status
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.
Assessment details
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.
Further information
Endemism (according to assessment)
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
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
Habitat
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 and conservation measures listed
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