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NRLD - 330468 | Anas platyrhynchos

Assessment ID
330468
Taxon name
Anas platyrhynchos
Linnaeus, 1758
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Anas platyrhynchos
Linnaeus, 1758
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
anseriformes
Family
anatidae
Genus
Anas
Species
platyrhynchos
Species authority
Linnaeus, 1758
Taxonomic notes and synonyms listed
Anas platyrhynchos and A. fulvigula (incorporating diazi) (del Hoyo and Collar 2014) were previously treated as A. platyrhynchos (incorporating diazi) and A. fulvigula following Sibley and Monroe (1990, 1993).
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
Least Concern
Abbreviated status
LC
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
Expert opinion at the UAE assessment workshop is that it is possible to differentiate between resident (non-native) and visiting wild populations. The population size is estimated to be at least 1,000 mature individuals, and it is assessed as Least Concern.
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
This species is a common migrant and winter visitor, which occurs throughout the UAE between October and March (Richardson 1990, Pedersen et al. 2017). Large populations of several hundred individuals are regularly found at Dubai Creek (Dubai Emirate) and in Ayn al Fayda near Al Ain (Abu Dhabi Emirate) (Richardson 1990). A population of resident, breeding birds was introduced in the 1980s in Dubai and Abu Dhabi cities and on Sir Bani Yas Island (Richardson and Aspinall 1998, Jennings 2010), but this introduced population would not count towards its Red List assessment.
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
In the UAE, this species is most often found at estuaries, ponds, reservoirs, creeks, lagoons and water treatment plants (Richardson 1990, Aspinall and Porter 2011). It requires water less than 1 m deep for foraging (Snow and Perrins 1998). There is no information available about its diet in the UAE. In general, the species is omnivorous and opportunistic, feeding by dabbling in water and by grazing on the land (del Hoyo et al. 1992, Snow and Perrins 1998). Elsewhere, its diet consists of seeds and the vegetative parts of aquatic and terrestrial plants, as well as terrestrial and aquatic invertebrates such as insects, molluscs, crustaceans, worms and occasionally amphibians and fish (del Hoyo et al. 1992). The non-breeding population native to the UAE is migratory, leaving its breeding grounds in the western Palaeartic in September/October and returning in February/March (Richardson 1990). During migration and in winter, the species can be found in small to very large flocks numbering up to several hundred of individuals (Madge and Burn 1988, Richardson 1990, Richardson and Aspinall 1998, Snow and Perrins 1998). The species may also roost both nocturnally and diurnally in communal groups when not breeding (Brown et al. 1982).An introduced population breeds in early spring in various locations near human sites in Dubai and Abu Dhabi emirates (Richardson 1990, Richardson and Aspinall 1998, Jennings 2010), and chicks are present from late March on (Richardson 1990). While there is not much known about the breeding behaviour of the introduced population (Jennings 2010), usually the nest is a shallow depression or bowl of vegetation that can be situated in many different locations such as within vegetation on the ground, in natural tree cavities, under fallen dead wood, on tree stumps, under bushes and even in abandoned nests of other species (e.g. herons or crows) (Brown et al. 1982, Flint et al. 1984, del Hoyo et al. 1992, Snow and Perrins 1998). Nests are generally placed close to water (Kear 2005).
Threats and conservation measures listed
Threats listed in assessment
Within the UAE the main threats are likely to be from changes in wetland land-use, and potentially from oil pollution, but the severity of these on the population is uncertain - especially given the presence of a feral population here (which would not count to a Red List assessment).Outside of the UAE the species faces a range of threats, which could impact individuals that visit the country. The species is threatened by wetland habitat degradation and loss from pollution (e.g. petroleum [Grishanov 2006] and pesticides [Kwon et al. 2004]), wetland drainage, peat-extraction, changing wetland management practices (e.g. decreased grazing and mowing in meadows leading to scrub over-growth)and the burning and mowing of reedbeds (Grishanov 2006). The species is hunted over large areas (Kear 2005) and also suffers mortality as a result of lead shot ingestion (e.g. Mateo et al. 1999, Mondain-Monval et al. 2002). It is also susceptible to duck virus enteritis (DVE) (Friend 2006), avian influenza (Melville and Shortridge 2006) and avian botulism (Rocke 2006), so it may be threatened by future outbreaks of these diseases (although it may be able to withstand sporadic losses due to its high reproductive potential) (Rocke 2006).
History
The population in 1996 is thought to have also been moderately large (e.g., 1,000+ at Al Ain), with large visiting (= natural) populations. The species is considered to have been Least Concern in 1996.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates