Dendrocygna viduata 

Scope: Global
Language: English

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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Anseriformes Anatidae

Scientific Name: Dendrocygna viduata (Linnaeus, 1766)
Common Name(s):
English White-faced Whistling-duck, White-faced Duck, White-faced Whistling Duck, White-faced Whistling-Duck
French Dendrocygne veuf
Taxonomic Source(s): SACC. 2005 and updates. A classification of the bird species of South America. Available at: #

Assessment Information [top]

Red List Category & Criteria: Least Concern ver 3.1
Year Published: 2016
Date Assessed: 2016-10-01
Assessor(s): BirdLife International
Reviewer(s): Butchart, S. & Symes, A.
Facilitator/Compiler(s): Ekstrom, J., Butchart, S., Malpas, L.
This species has an extremely large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (Extent of Occurrence <20,000 km2 combined with a declining or fluctuating range size, habitat extent/quality, or population size and a small number of locations or severe fragmentation). The population trend appears to be increasing, and hence the species does not approach the thresholds for Vulnerable under the population trend criterion (>30% decline over ten years or three generations). The population size is extremely large, and hence does not approach the thresholds for Vulnerable under the population size criterion (<10,000 mature individuals with a continuing decline estimated to be >10% in ten years or three generations, or with a specified population structure). For these reasons the species is evaluated as Least Concern.
Previously published Red List assessments:

Geographic Range [top]

Countries occurrence:
Angola; Antigua and Barbuda; Argentina; Aruba; Barbados; Benin; Bolivia, Plurinational States of; Botswana; Brazil; Burkina Faso; Burundi; Cameroon; Central African Republic; Chad; Colombia; Comoros; Congo; Congo, The Democratic Republic of the; Côte d'Ivoire; Cuba; Dominica; Dominican Republic; Equatorial Guinea; Eritrea; Ethiopia; French Guiana; Gabon; Gambia; Ghana; Guadeloupe; Guinea; Guinea-Bissau; Guyana; Haiti; Kenya; Lesotho; Liberia; Madagascar; Malawi; Mali; Martinique; Mauritania; Mauritius; Mayotte; Montserrat; Mozambique; Namibia; Nicaragua; Niger; Nigeria; Paraguay; Peru; Réunion; Rwanda; Saint Kitts and Nevis; Saint Lucia; Saint Vincent and the Grenadines; Senegal; Sierra Leone; Somalia; South Africa; South Sudan; Sudan; Suriname; Swaziland; Tanzania, United Republic of; Togo; Trinidad and Tobago; Uganda; Uruguay; Venezuela, Bolivarian Republic of; Zambia; Zimbabwe
Possibly extinct:
Costa Rica
Regionally extinct:
Puerto Rico
Chile; Panama; Seychelles; Spain
Additional data:
Continuing decline in area of occupancy (AOO):Unknown
Extreme fluctuations in area of occupancy (AOO):NoEstimated extent of occurrence (EOO) - km2:75400000
Continuing decline in extent of occurrence (EOO):UnknownExtreme fluctuations in extent of occurrence (EOO):No
Continuing decline in number of locations:Unknown
Extreme fluctuations in the number of locations:No
Upper elevation limit (metres):1000
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:The population is estimated to number 1,700,000-2,800,000 individuals.

Trend Justification:  The overall population trend is increasing, although some populations are decreasing (Wetlands International 2006).
Current Population Trend:Increasing
Additional data:
Continuing decline of mature individuals:Unknown
Extreme fluctuations:NoPopulation severely fragmented:No
Continuing decline in subpopulations:Unknown
Extreme fluctuations in subpopulations:NoAll individuals in one subpopulation:No

Habitat and Ecology [top]

Habitat and Ecology:Behaviour This species is subject to upredictable local nomadic movements (Johnsgard 1978) (usually of less than 500 km) in relation to variations in water and food availability (Madge and Burn 1988). Breeding commences at the start of the local rainy season (del Hoyo et al. 1992) with the species nesting individually (Langrand 1990, Hockey et al. 2005) or in loose colonies or small groups (del Hoyo et al. 1992). Adults undergo a post-breeding flightless moult period lasting for 18-25 days during which they are particularly vulnerable and seek the cover of densely vegetated wetlands (Kear 2005a). When not breeding the species is gregarious and may forage in flocks of up to several thousands of individuals (Kear 2005a). The species mainly forages at night (del Hoyo et al. 1992) (although it may also feed diurnally during the winter) (Madge and Burn 1988). Habitat The species inhabits a wide variety of freshwater wetlands (del Hoyo et al. 1992) including lakes, swamps (Kear 2005a), marshes, large rivers, river deltas, flood-plains (Madge and Burn 1988), reservoirs (Madge and Burn 1988, Kear 2005a), sewage farms (Africa) (Johnsgard 1978) and estuaries (Kear 2005a), and is commonly encountered feeding in rice fields (Kear 2005a). It shows a preference for wetlands in open country (del Hoyo et al. 1992) (although it is likely to inhabit fresh or brackish waters in more forested areas in South America) (Johnsgard 1978) with mud or sandbars for roosting and rich shoreline (Johnsgard 1978), emergent and surface vegetation (Brown et al. 1982). Adults require densely vegetated permanent wetlands for cover during their flightless post-breeding moult period (Hockey et al. 2005, Kear 2005a), although breeding birds prefer more ephemeral wetlands (Hockey et al. 2005). Diet Its diet consists of grasses (e.g. Echinochloa spp.), aquatic seeds e.g. of water-lilies Nyphaea and Nymphoides spp., rice (del Hoyo et al. 1992), pondweeds (e.g. Potamogeton spp.) (Hockey et al. 2005) and tubers (especially in the dry season) (Kear 2005a), as well as aquatic invertebrates such as molluscs, crustaceans and insects (del Hoyo et al. 1992), the consumption of which is highest during the rains (Kear 2005a). Breeding site The nest is a depression (Johnsgard 1978) or low construction of vegetation (Kear 2005a) placed over or at varying distances from water, usually in stands of dense vegetation (e.g. long grass, sedge or rice) (Kear 2005a) on dry ground or in reedbeds (Johnsgard 1978, del Hoyo et al. 1992), occasionally also in open crevices in trees (South America) (Madge and Burn 1988, Kear 2005a). The species may nest in solitary pairs (Langrand 1990, Hockey et al. 2005) with nests placed more then 75 m apart (Africa) (Brown et al. 1982, Hockey et al. 2005), although it may also nest in loose colonies or small groups (del Hoyo et al. 1992).
Systems:Terrestrial; Freshwater
Continuing decline in area, extent and/or quality of habitat:Unknown
Generation Length (years):5.3
Movement patterns:Full Migrant
Congregatory:Congregatory (and dispersive)

Threats [top]

Major Threat(s): The species is susceptible to avian botulism (van Heerden 1974) and avian influenza (Gaidet et al. 2007) so may be threatened by future outbreaks of these diseases. Utilisation The species is hunted for local consumption and trade in Malawi (Bhima 2006) and is hunted in Botswana (Herremans 1998). It is also hunted and traded at traditional medicine markets in Nigeria (Nikolaus 2001).

Citation: BirdLife International. 2016. Dendrocygna viduata. The IUCN Red List of Threatened Species 2016: e.T22679763A92829021. . Downloaded on 20 May 2018.
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