|Scientific Name:||Netta rufina (Pallas, 1773)|
|Taxonomic Source(s):||Cramp, S. and Simmons, K.E.L. (eds). 1977-1994. Handbook of the birds of Europe, the Middle East and Africa. The birds of the western Palearctic. Oxford University Press, Oxford.|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Reviewer(s):||Butchart, S. & Symes, A.|
|Facilitator/Compiler(s):||Ashpole, J, Butchart, S., Ekstrom, J., 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 is not known, but the population is not believed to be decreasing sufficiently rapidly to approach the thresholds under the population trend criterion (>30% decline over ten years or three generations). The population size is very 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:|
Native:Afghanistan; Albania; Algeria; Armenia; Austria; Azerbaijan; Bangladesh; Belarus; Belgium; Bhutan; Bosnia and Herzegovina; Bulgaria; China; Croatia; Cyprus; Czech Republic; Denmark; Egypt; Estonia; France; Georgia; Germany; Greece; Hungary; India; Iran, Islamic Republic of; Iraq; Israel; Italy; Jordan; Kazakhstan; Kyrgyzstan; Latvia; Macedonia, the former Yugoslav Republic of; Moldova; Mongolia; Montenegro; Morocco; Myanmar; Nepal; Netherlands; Pakistan; Poland; Portugal; Romania; Russian Federation (Central Asian Russia, Eastern Asian Russia, European Russia); Serbia; Slovakia; Slovenia; Spain (Canary Is. - Vagrant); Switzerland; Syrian Arab Republic; Tajikistan; Turkey; Turkmenistan; Ukraine; Uzbekistan
Vagrant:Bahrain; Finland; Ireland; Japan; Lebanon; Libya; Malta; Norway; Oman; Qatar; Saudi Arabia; Sri Lanka; Sweden; Thailand; Tunisia; United Arab Emirates
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||The global population is estimated at 420,000-600,000 individuals (Wetlands International 2015). The European population is estimated at 27,500-43,000 pairs, which equates to 55,100-86,000 mature individuals (BirdLife International 2015).|
Trend Justification: The overall population trend is uncertain, as some populations are increasing or have unknown trends (Wetlands International 2015). The population trend in Europe is unknown (BirdLife International 2015).
|Current Population Trend:||Unknown|
|Habitat and Ecology:||Behaviour The species is fully migratory (Snow and Perrins 1998) or locally dispersive (e.g. in Europe) (del Hoyo et al. 1992) and breeds from mid-April to early-June (Madge and Burn 1988) in single pairs or loose groups (del Hoyo et al. 1992). Males and non-breeders moult and become flightless for four weeks between June and August (females moulting one month later) (Scott and Rose 1996) prior to which they may make extensive moult migrations which take them considerable distances from the breeding waters (Madge and Burn 1988). Once this post-breeding moult is complete the species departs for its winter quarters, arriving there from October onwards (Madge and Burn 1988). The species is highly gregarious for most of the year (Snow and Perrins 1998) and although it is more commonly found in small groups (Madge and Burn 1988) it often forms large concentrations (Madge and Burn 1988, Scott and Rose 1996) of several hundred individuals (Scott and Rose 1996) in moulting and wintering areas (Madge and Burn 1988). It feeds diurnally, being most active during the early morning and evening (Kear2005b). Habitat The species inhabits inland deep fresh or brackish (del Hoyo et al. 1992) reed-fringed lakes, rivers, or saline and alkaline lagoons (Kear2005b) in open country (del Hoyo et al. 1992), also occurring (less often) on estuaries, river deltas and other sheltered coastal habitats (del Hoyo et al. 1992) on passage (Madge and Burn 1988) or during the winter (Scott and Rose 1996). Diet The diet of this species consists predominantly of the roots, seeds and vegetative parts of aquatic plants (Johnsgard 1978, del Hoyo et al. 1992) (e.g. Chara spp. (del Hoyo et al. 1992), Hippurus spp., hornworts Ceratophyllum spp., pondweeds Potamogeton spp., milfoil Myriophyllum spp. (Johnsgard 1978) and especially stonewort Nitellopsis obtusa (Ruiters et al. 1994)), although it will occasionally also take aquatic invertebrates (del Hoyo et al. 1992) (e.g. molluscs) (Johnsgard 1978), amphibians and small fish (del Hoyo et al. 1992). Breeding site The nest is constructed of roots, twigs and leaves near water (del Hoyo et al. 1992, Kear2005b) on the ground in dense vegetation or on floating mats of vegetation amidst reedbeds (Johnsgard 1978). Although the species usually breeds well-dispersed, neighbouring pairs may sometimes nest as close as 30 m apart (Snow and Perrins 1998, Kear2005b). Management information A study in the Czech Republic found that fish ponds with a fish stock density of less than 400 kg ha1, water transparency of more than 50 cm, mixed fish stocks (e.g. tench and pike or perch) rather than monospecific stocks (e.g. of carp or other herbivorous fish species), and systems that include ponds with fish fry are more likely to have high abundances of aquatic vegetation and are therefore more successful in supporting breeding pairs of this species (Musil 2006).|
|Continuing decline in area, extent and/or quality of habitat:||Unknown|
|Generation Length (years):||7|
|Movement patterns:||Full Migrant|
|Congregatory:||Congregatory (and dispersive)|
|Major Threat(s):||The two main threats to this species are habitat degradation (Defos du Rau 2002) (e.g. through land-use changes) (Kear2005b) and hunting (Kear2005b) (e.g. the species is hunted in France, Portugal and Spain without any official hunting bag monitoring (Defos du Rau 2002)). The species also suffers poisoning from lead shot ingestion (Spain) (Mateo et al. 1998)and is occasionally drowned in freshwater fishing nets with mesh sizes greater than 5 cm (China) (Quan et al. 2002). Deterioration in the water quality of wetlands can reduce the abundance of stonewort Nitellopsis obtusa (which is an important part of the species's diet) (Ruiters et al. 1994), and it is susceptible to avian influenza so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Utilisation The species is hunted recreationally and for commercial purposes in Iran (Balmaki and Barati 2006).|
Conservation Actions Underway
CMS Appendix II. EU Birds Directive Annex II. The species is listed in the Red Book of endangered species in seven countries in the European Union (Defos du Rau 2002).
Conservation Actions Proposed
The following information refers to the species's European range only: Long-term monitoring should be continued and extended to cover all potential wintering sites and formal programs for monitoring hunting bags should be introduced. Research is needed on the species's population dynamics and habitat selection to help inform conservation measures, hunting regulation and the restoration of habitat (Defos du Rau 2002). The protection of key wetland sites is also needed (Tucker and Heath 1994).
|Citation:||BirdLife International. 2016. Netta rufina. The IUCN Red List of Threatened Species 2016: e.T22680348A86012189.Downloaded on 20 July 2018.|
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