Please note, this National Red List website contains a subset of data whilst we transition to national focal point driven data uploads. We thank you for your patience with this and welcome national contributors to get in touch to update their national dataset. Terms of Use including citation guidance are found here.

The previous dataset is available via: https://archive.nationalredlist.org/. This site is no longer updated but can help with most enquiries whilst we focus on redevelopment.

NRLD - 330510 | Calidris pugnax

Assessment ID
330510
Taxon name
Calidris pugnax
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Calidris pugnax
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
charadriiformes
Family
scolopacidae
Genus
Calidris
Species
pugnax
Species authority
(Linnaeus, 1758)
Taxonomic notes and synonyms listed
Calidris pugnax (del Hoyo and Collar 2014) was previously placed in the genus Philomachus.
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 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.
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 migrant individuals on passage to and from the breeding grounds, which are common to very common at wetlands throughout the country (Pedersen et al. 2017). Numbers peak between July and December, and between February and April (Richardson 1990). Moreover, the species is a fairly common winter visitor, while single individuals have also been recorded during summer (Pedersen et al. 2017).
Is there a map available in assessment?
Yes
Habitat and systems
Ecological system type
Terrestrial
Not_assigned
Freshwater
Not_assigned
Marine
Not_assigned
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).
Threats and conservation measures listed
Threats listed in assessment
Across its global range the species is threatened by petroleum pollution, wetland and flood-plain drainage (for irrigation and water management), peat-extraction, and land abandonment and changing land management practices that lead to scrub and reed overgrowth (del Hoyo et al. 1996, Grishanov 2006). The species may also suffer future population declines and range contractions as a result of global climate change (Zöckler 2002), and is susceptible to avian influenza (Melville and Shortridge 2006, Gaidet et al. 2007), avian botulism (Blaker 1967, van Heerden 1974, Hubalek et al. 2005) and avian malaria (Mendes et al. 2005), so may be threatened by future outbreaks of these diseases. The most relevant threats within the UAE are changes in coastal land-use and the possibility of oil pollution, but the severity of these threats towards this species is unknown.
History
The population is thought likely to have been the same or similar in 1996, and it is assessed as NT.
Publication
Burfield, I.J., Westrip, J., Sheldon, R.D., Hermes, C., Wheatley, H., Smith, D., Harding, K.A. Allen, D.J. and Alshamsi, O. 2021. UAE National Red List of Birds. Ministry of Climate Change and Environment, Dubai, United Arab Emirates