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NRLD - 330558 | Nycticorax nycticorax

Assessment ID
330558
Taxon name
Nycticorax nycticorax
(Linnaeus, 1758)
Uploaded by
National Red List Database
Taxonomic information
Scientific name
Nycticorax nycticorax
(Linnaeus, 1758)
Assessed taxon level
Species
Higher level taxonomic groupings
Vertebrates
Birds
Kingdom
Animalia
Phylum
chordata
Class
aves
Order
pelecaniformes
Family
ardeidae
Genus
Nycticorax
Species
nycticorax
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
Endangered
Abbreviated status
EN
Qualifying criteria (if given)
D
Criteria system used
IUCN

(see Assessment details)

Assessment rationale/justification
This species has a tiny breeding and non-breeding population, both of which are thought to be increasing within the UAE. The breeding population size is low enough that it would trigger listing as Critically Endangered under Criterion D, while the non-breeding population size would trigger a listing as Endangered. Based on the regional criteria, however, the breeding population warrants a regional adjustment due to the likelihood of a rescue effect. The non-breeding population is precautionarily not thought to warrant such a change. The breeding status takes precedence and so the species is listed as Endangered under Criterion D.
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 (Pedersen et al. 2017). Numbers are highest in autumn, when it is fairly common at freshwater sites throughout the country (Richardson 1990, Pedersen et al. 2017). Some individuals stay in the country over summer (Pedersen et al. 2017). Breeding has been recorded near Dubai City in 1992, 2013 and 2015, but it has been suggested that the species breeds annually (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 inland wetlands including rivers, freshwater and brackish lakes, densely vegetated marshes, reservoirs, irrigation ponds and sewage treatment plants (Richardson 1990, Jennings 2010, Aspinall and Porter 2011). During migration, it may also be found in wadis (Richardson 1990). Its diet in the UAE is not well known; elsewhere it is an opportunistic feeder taking fish, frogs, tadpoles, turtles, snakes, lizards, insects, spiders, crustaceans, molluscs, leeches, small rodents, bats and the eggs and chicks of other bird species (del Hoyo et al. 1992, Kushlan and Hancock 2005). The species is largely crepuscular and nocturnal, but may feed diurnally, especially during the breeding season (del Hoyo et al. 1992). It breeds during mid to late summer; nesting sites may be used in consecutive years (Jennings 2010). There is not much known about its breeding biology in the UAE or in Arabia. Usually, the nest is platform constructed of sticks and vegetation placed 2-50 m above water or on dry ground near water in trees, bushes, reedbeds, on cliff ledges and on the ground in protected sites (del Hoyo et al. 1992, Snow and Perrins 1998, Kushlan and Hancock 2005). The species nests close together in single- and mixed-species colonies (del Hoyo et al. 1992).
Threats and conservation measures listed
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. The species is threatened by wetland drainage and destruction (del Hoyo et al. 1992, Kushlan and Hancock 2005) and by droughts in wintering areas (Hafner and Kushlan 2002). It is highly susceptible to pesticides (del Hoyo et al. 1992, Kwon et al. 2004, Kushlan and Hancock 2005) such as organophosphates, carbamates (Kwon et al. 2004) and DDE (a breakdown product of DDT), which negatively affect hatching success (Kushlan and Hancock 2005). There are also cases of genetic damage to chicks as a result of petroleum contamination (Custer 2000). The species is susceptible to avian influenza (Melville and Shortridge 2006) and Newcastle disease so may be threatened by future outbreaks (Kuiken et al. 2006). It is also persecuted (anti-predation killing) at aquaculture facilities due to its depredation on fish stocks (Kushlan and Hancock 2005), and has suffered declines due to the exploitation of chicks from nesting colonies in the past (del Hoyo et al. 1992).
History
The species first bred in the UAE in 1992. The species would have qualified as CR (D) under its breeding population, but without rescue effect since it was just becoming established. Its successful colonisation of the country is likely related to increases in suitable artificial habitats.
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