Aythya nyroca 

Scope: Global
Language: English

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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Anseriformes Anatidae

Scientific Name: Aythya nyroca
Species Authority: (Güldenstädt, 1770)
Regional Assessments:
Common Name(s):
English Ferruginous Duck, White-eyed Pochard, Ferruginous Pochard
French Fuligule nyroca
Spanish Porrón Pardo
Taxonomic Source(s): del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Lynx Edicions BirdLife International, Barcelona, Spain and Cambridge, UK.
Identification information: 38-42 cm. Dark chestnut coloured diving duck. Both sexes uniform chestnut, slightly darker on back with white belly and undertail; male with distinctive pale iris. Juvenile similar but belly and undertail grey-buff. In flight a broad white wingbar extends onto outer primaries. Similar spp. Easily distinguished from other Aythya ducks by white undertail when sitting and extensive wingbar in flight. Voice In spring female noisy in flight with err, err... call and male with a short chuk call. Hints Prefers shallower and more vegetated areas than other Aythya species and seldom sits out on open water. Outside of main range search flocks of other diving ducks.

Assessment Information [top]

Red List Category & Criteria: Near Threatened ver 3.1
Year Published: 2016
Date Assessed: 2016-10-01
Assessor(s): BirdLife International
Reviewer(s): Butchart, S. & Symes, A.
Contributor(s): Baral, H., Braunlich, A., Brouwer, J., Halder, R., Hatzofe, O., Heinicke, T., Hughes, B., Inskipp, C., Isfendiyaroglu, S., Jayadevan, P., Katzner, T., Khan, A., Liu Dongping, .., Mischenko, A., Parveen, A., Petkov, N., Sklyarenko, S., Subramanya, S., Tordoff, A.W., Xing Lianlian, .., Yasmeen, R. & Yerokhov, S.
Facilitator/Compiler(s): Benstead, P., Capper, D., Derhé, M., Harding, M., Malpas, L., O'Brien, A., Peet, N., Pilgrim, J., Ashpole, J
Given that this species's range may fluctuate considerably from year to year - particularly in Asia - owing to changing water levels, it is very hard to estimate the global population or trends. There have been rapid declines in Europe, but evidence of declines in the larger Asian populations is sparse, and sometimes contradictory, so it is currently listed as Near Threatened. Evidence of rapid declines in Asia would qualify the species for uplisting to Vulnerable.

Previously published Red List assessments:

Geographic Range [top]

Range Description:This species breeds principally in south-western Asia (east to China and south to Pakistan and India), central and eastern Europe, and north Africa (Callaghan 1999, Vinicombe 2000). The wintering range overlaps with the breeding range and extends to the Middle East, north-east and West Africa (mainly Mali and Nigeria [Vinicombe 2000]) and South-East Asia. Four main populations are recognised and migration occurs from early September to mid-October, whilst breeding grounds are re-occupied from mid-March to early May (Vinicombe 2000). The main part of the population occurs in Asia, where there is much suitable habitat and it remains common, although quantitative data are lacking. Given that this species's range may fluctuate considerably from year to year, owing to changing water levels, it is unclear how much one-off high counts from Asian countries represent just one mobile population (Petkov et al. 2003). The current global population is estimated to fall in the band of c.180,000-294,999 individuals. An estimate for North Africa and Asia of 10,000 individuals in 1991 (Perennou et al. 1994) appears too low. About 600 pairs breed in the El Kala National Park, Algeria (Vinicombe 2000), and there have been recent reports of breeding in Aswan, Egypt (Hoek et al. 2010). In Europe the breeding population is estimated at 17,400-30,100 pairs with the largest population in Romania (11,761-18,018 breeding pairs, concentrated in the Danube Delta) (O. Hatzofe in litt. 2005, BirdLife International 2015). Significant populations (between 1,000 and 5,000 pairs) are also found in Croatia and Azerbaijan, whilst smaller populations (c.500-1,000 pairs) are found in Russia, Hungary, Serbia and possibly Ukraine and Turkey (O. Hatzofe in litt. 2005, Dordevic et al. 2009, BirdLife International 2015). Populations in most European countries are showing signs of continuing large-scale declines. Sporadic breeding and/or wintering occurs in several western European countries. In Asia recent surveys have found high numbers, perhaps into the tens of thousands, in Inner Mongolia (Xing Lianlian pers. comm. 1998) (although the accuracy of these counts is unclear, and may refer to non-breeding birds from other areas), 6,000-7,000 breeding pairs in Kazakhstan (S. Yerokhov verbally per N. Petkov in litt. 2005) (although others have suggested it is uncommon [C. Inskipp in litt. 2005, A. A. Khan in litt. 2006]) and it is apparently common on the Tibetan Plateau, China (Scott 1993), and in winter in India, Bangladesh (70,000 birds counted at one group of four sites) (R. Halder in litt. 2002), Myanmar and Thailand. Other large winter counts have been made in Azerbaijan (9,000 birds), Turkmenistan (21,000 birds) (Carboneras 1992a) and Uzbekistan (7,000 birds [Kashkarov and Mukhina 1997], but recently less [S. Yerokhov verbally per N. Petkov in litt. 2005]). Small numbers occur on passage in Lebanon and Qatar and also in winter in Iraq, Israel, Jordan, Oman, Saudi Arabia, Syria, United Arab Emirates and Yemen

The species declined markedly in Europe where there have been declines of more than 20% in nine European countries (BirdLife International 2004, O. Hatzofe in litt. 2005, BirdLife International 2015). Following a large decline in Europe during 1970-1990 (Unpublished expert communications to S. Sklyarenko 2005), the species continued to decline during 1990-2000, when up to 45% of birds appear to have been lost (particularly in south-east Europe). The European population was believed to have declined overall by >30% (BirdLife International 2004, O. Hatzofe in litt. 2005). The most recent assessment of the European population size trend was assessed as Unknown (BirdLife International 2015). 

There is some evidence for declines in the number of birds in India (T. Katzner in litt. 2005, A. W. Tordoff in litt. 2005), Kazakhstan (Berezovikov and Samusev 1998, S. Subramanya in litt. 2006) (although other evidence suggests that this population is actually stable [S. Yerokhov verbally per N. Petkov in litt. 2005]), Kyrgyzstan (C. Inskipp in litt. 2005), Pakistan (N. Petkov in litt. 2005), Uzbekistan (Kashkarov and Mukhina 1997, S. Subramanya in litt. 2006) (but this population may have now stabilised [S. Yerokhov verbally per N. Petkov in litt. 2005]) and Vietnam (Tucker and Heath 1994), and to a minor degree in Nepal (C. Inskipp in litt. 2005) (but possibly stable there [H. S. Baral in litt. 2005]). Winter counts from Israel suggest that the population has been generally stable in recent years (T. Heinicke in litt. 2005). In Ukraine, numbers fell from an estimated 65,000 in the late 1960s (Vinicombe 2000) to an estimated 300-600 pairs, whilst declines have also been recorded in Moldova, Belarus, Croatia, Greece, Latvia, Lithuania, Montenegro, Poland, Russia, Slovakia and Turkey (Vinicombe 2000, BirdLife International 2015). The Albanian population declined from 100-300 pairs to 0-3 pairs (N. Petkov in litt. 2003) and is now estimated at 5-30 pairs (BirdLife International 2015). However, populations remain stable in a number of other countries and slight local increases may have occurred in parts of Russia and Ukraine since hunting has diminished due to the species's rarity (Vinicombe 2000). This species's range has fluctuated considerably over the last c.150 years, although the overall trend has been towards a declining population and distribution. It is currently listed as Least Concern in Europe as 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) (BirdLife International 2015). Evidence of declines in the larger Asian populations is sparse, and sometimes contradictory, and so there is insufficient evidence at present to warrant uplisting to Vulnerable globally.

Countries occurrence:
Afghanistan; Albania; Algeria; Armenia (Armenia); Austria; Azerbaijan; Bangladesh; Belarus; Belgium; Bhutan; Bosnia and Herzegovina; Bulgaria; Central African Republic; Chad; China; Croatia; Cyprus; Czech Republic; Egypt; Eritrea; Ethiopia; France; Gambia; Georgia; Germany; Greece; Hungary; India; Iran, Islamic Republic of; Iraq; Israel; Italy; Jordan; Kazakhstan; Kuwait; Kyrgyzstan; Latvia; Lebanon; Libya; Liechtenstein; Lithuania; Luxembourg; Macedonia, the former Yugoslav Republic of; Mali; Malta; Mauritania; Moldova; Mongolia; Montenegro; Morocco; Myanmar; Nepal; Netherlands; Niger; Nigeria; Oman; Pakistan; Palestinian Territory, Occupied; Poland; Portugal; Qatar; Romania; Russian Federation; Saudi Arabia; Senegal; Serbia (Serbia); Slovakia; Slovenia; South Sudan; Sudan; Switzerland; Syrian Arab Republic; Tajikistan; Thailand; Tunisia; Turkey; Turkmenistan; Ukraine; United Arab Emirates; Uzbekistan; Viet Nam; Western Sahara; Yemen
Bahrain; Benin; Bermuda; Burkina Faso; Cape Verde; Denmark; Finland; Ghana; Hong Kong; Ireland; Japan; Maldives; Norway; Seychelles; Sierra Leone; Spain; Sweden; Uganda; United Kingdom
Present - origin uncertain:
Cameroon; Togo
Additional data:
Continuing decline in area of occupancy (AOO):Yes
Extreme fluctuations in area of occupancy (AOO):NoEstimated extent of occurrence (EOO) - km2:25900000
Continuing decline in extent of occurrence (EOO):YesExtreme fluctuations in extent of occurrence (EOO):No
Number of Locations:11-100Continuing decline in number of locations:Unknown
Extreme fluctuations in the number of locations:No
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:The population is estimated to number 2,400-2,600 in North Africa; 52,200-90,500 in Europe (BirdLife International 2015); 25,000-100,000 in south-west Asia and north-east Africa (based on counts in the 1990s of 9,000 in Azerbaijan, 21,000 in Turkmenistan and 7,000 in Uzbekistan), and over 100,000 in the rest of Asia (based on tens of thousands breeding in Inner Mongolia (Xing Lianlian in litt. 1998), common occurrence on the Tibetan Plateau, and upwards of 90,000 being present on the hoars of north-east Bangladesh in January 2002). The global population is therefore estimated to fall in the band c.180,000-294,999 individuals.

Trend Justification:  This species's range has fluctuated considerably over the last c.150 years as it has modified its distribution. However, most figures suggest widespread declines (Wetlands International 2016). Owing to significant local declines it was classified as Vulnerable in Europe, however the most recent assessment of the European population listed the trend as unknown and the species's status as Least Concern (BirdLife International 2015). Evidence of declines in the larger Asian populations is sparse, and sometimes contradictory. The overall population is estimated to be declining at a moderate rate.
Current Population Trend:Decreasing
Additional data:
Continuing decline of mature individuals:Yes
Extreme fluctuations:NoPopulation severely fragmented:No
No. of subpopulations:2-100Continuing decline in subpopulations:Unknown
Extreme fluctuations in subpopulations:NoAll individuals in one subpopulation:No
No. of individuals in largest subpopulation:1-89

Habitat and Ecology [top]

Habitat and Ecology:Behaviour This species is chiefly migratory (del Hoyo et al. 1992, Scott and Rose 1996), although little is known about its migratory routes (Scott and Rose 1996) and some individuals in southern populations may remain on the breeding grounds all year (Kear 2005b). It breeds from April or May (del Hoyo et al. 1992) until late June (Madge and Burn 1988) in single pairs or loose groups (del Hoyo et al. 1992). Adults undertake a wing moulting period on the breeding grounds between July and August (Robinson and Hughes 2006) when large flocks of moulting individuals may gather (Robinson and Hughes 2006) (no moult migration is recorded however [Scott and Rose 1996]). Departure from the breeding grounds begins in mid- to late-August (N. Petkov in litt. 2008) and peaks in October (Kear 2005b), with the species arriving in wintering areas from late October (Scott and Rose 1996). The return migration to the breeding grounds begins in early March (Scott and Rose 1996). Large gatherings of up to 100 individuals may occur prior to migration at the end of the post-breeding moult (Madge and Burn 1988) (July to August Scott and Rose (1996]), and on migration the species often remains in small groups of 20-50 individuals (N. Petkov in litt. 2008). Outside of the breeding season the species may be observed solitarily, in pairs or small loose groups (Madge and Burn 1988) of 2-5 individuals (Snow and Perrins 1998), and larger gatherings of 1,000-2,000 individuals are also recorded from wintering grounds in Niger and Chad (Petkov et al. 2003). Habitat It shows a strong preference for fresh standing water (Snow and Perrins 1998, N. Petkov in litt. 2008) and is very rarely found on flowing streams or rivers (N. Petkov in litt. 2008). It requires shallow water 30-100 cm deep close to littoral vegetation for feeeding (del Hoyo et al. 1992, Kear 2005b) and generally avoids large open areas (Kear 2005b, Scott and Rose 1996). In Bulgaria there is evidence that the species shows a preference for well-vegetated, comparatively shallow wetlands with well-structured mosaic vegetation and a diversity of microhabitats. It is also found on shallow mudflats, possibly as a result of more accessible and abundant invertebrate food sources in this habitat (Petkov in prep.) Breeding Shallow eutrophic freshwater pools and marshes with dense abundant submergent, floating, emergent and shoreline vegetation (e.g. reedbeds) are the major breeding habitats (del Hoyo et al. 1992, Kear 2005b, N. Petkov in litt. 2008). Shallow banks with flooded vegetation and mudflats are particularly used for foraging during this season. The species shows a particular preference for breeding, moulting and staging on large river deltas (Kear (2005b, Scott and Rose 1996, Robinson and Hughes 2006) and extensively managed fish ponds in Eastern Europe (Petkov 2006, Robinson and Hughes 2006). It is also less-commonly known to utilise brackish waters of estuaries, coastal lagoons, reservoirs, salt-pans, sewage farms, canals and drainage ditches during this season (Snow and Perrins 1998, Robinson and Hughes 2006, N. Petkov in litt. 2008). Non-breeding Its habitat requirements outside of the breeding season are similar to those of the breeding season (Kear 2005b), although it may also frequent large lakes, open lagoons, coastal marshes with reedbeds (del Hoyo et al. 1992, Kear 2005b, Scott and Rose 1996) and shallow coastal bays, straits and estuaries (Robinson and Hughes 2006). Diet Although the species is omnivorous, plant material such as seeds, roots and vegetative parts of aquatic plants (del Hoyo et al. 1992) (Potamogeton spp., Ceratophyllum spp., Scirpus spp., Carex spp. and macroalgae Chara spp. [Kear 2005b]) dominates its diet. Animal matter taken includes worms, molluscs (del Hoyo et al. 1992) (snails [Kear 2005b]), crustaceans, adult and larval insects (del Hoyo et al. 1992) (beetles, chironomids (Kear 2005b), dragonflies, waterbugs, caddisflies, flies [Brown et al. 1982]), amphibians (del Hoyo et al. 1992) (frogs, tadpoles and spawn [Kear 2005b, Brown et al. 1982]) and small fish (del Hoyo et al. 1992) up to 3 cm long (Brown et al. 1982). Breeding site The nest is a low platform (Snow and Perrins 1998) of reeds and other vegetation (del Hoyo et al. 1992) placed on the ground or on an islet or hummock in thick vegetation close to water (Kear 2005b, Johnsgard 1978). Alternatively nests may be placed over water on floating mats of vegetation (Johnsgard 1978) or in dense reedbeds along the shoreline (Kear 2005b, Johnsgard 1978).

Systems:Terrestrial; Freshwater; Marine
Continuing decline in area, extent and/or quality of habitat:Yes
Generation Length (years):7.6
Movement patterns:Full Migrant
Congregatory:Congregatory (and dispersive)

Threats [top]

Major Threat(s): The species is threatened by the degradation and destruction of well-vegetated shallow pools and other wetland habitats (Vinicombe 2000, del Hoyo et al. 1992, Kear 2005b, Robinson and Hughes 2006) (e.g. changes to the vegetation community, disruption of water regimes, siltation, and increased water turbidity [Robinson and Hughes 2006]) as a result of excessive drainage and water abstraction (Vinicombe 2000, Grishanov 2006, Robinson and Hughes 2006), peat extraction (Grishanov 2006), eutrophication (from inadequate sewage treatment and nutrient run-off [Robinson and Hughes 2006]), oil pollution (Grishanov 2006), dam and barrage construction, the building of infrastructure on flood-plains (Vinicombe 2000, Robinson and Hughes 2006) and river canalisation (Kear 2005b). Changing land management practices such as reed cutting and burning during the breeding season (Petkov 2006), over-grazing (Robinson and Hughes 2006) decreased grazing and mowing of wet meadows (Grishanov 2006), and abandonment (causing succession to scrub) or intensification (causing reversion to open water) of extensively managed fishponds (Vinicombe 2000, Kear 2005b, Petkov 2006, Robinson and Hughes 2006) also threatens the species. The introduction of non-native species has caused further habitat degradation. For example the stocking of lakes with and accidental introduction of Grass Carp Ctenopharyngodon idella has resulted in reductions in macrophyte biomass and corresponding reductions in invertebrate biomass (Kear 2005b, Robinson and Hughes 2006), and in Bulgaria an introduced shrub (Desert False Indigo Amorpha fruticosa) is changing the ecological character of wetlands (Robinson and Hughes 2006). Introduced predators such as the Wels Catfish Silurus glanis (Kazakhstan) that predate ducklings, and the Muskrat Ondatra zibethicus (Aral Sea region) have also caused population declines (Robinson and Hughes 2006). Increased drought due to global climate change may pose a threat to the species in part of its range (Vinicombe 2000, Robinson and Hughes 2006). Disturbance by fishing boats and anglers alongside fringe vegetation could cause abandonment of the breeding sites or disrupt the timing of breeding (N. Petkov in litt. 2008). Hunting is another serious threat to the species (Vinicombe 2000, del Hoyo et al. 1992, Robinson and Hughes 2006). Large numbers are shot on passage in the autumn (e.g. through the Volga delta) and on the wintering grounds (e.g. Sudan) (Kear 2005b, Balmaki and Barati 2006). Illegal and accidental hunting also persists in most European countries. Other lower-level threats include lead poisoning (from ingestion of discarded lead shot), fires in areas of reed thickets, peat bogs and woods (Grishanov 2006) and entanglement and drowning in fishing nets (Robinson and Hughes 2006) and hybridisation with native species (e.g. Tufted Duck Aythya fuligula and Common Pochard Aythya ferina in Switzerland [Leuzinger 2010]).

Conservation Actions [top]

Conservation Actions: Conservation Actions Underway
The species is fully protected in Belarus, Bulgaria, Czech Republic, France, Germany, Hungary, Italy, Moldova, Netherlands, Russia, Slovakia, Slovenia, Spain and Switzerland, and is protected from hunting in Austria, Belgium, Greece, Poland, Turkey and Ukraine. It is listed on Annex I of the European Union Directive on the Conservation of Wild Birds, on Appendix III of the Bern Convention and on Appendices I and II of the Bonn Convention. The species has received little international conservation action, although a number of national initiatives have been developed recently, notably habitat management in Bulgaria and re-introduction schemes in Italy (Berezovikov and Samusev 1998). One of the highest priorities for this species is to establish systematic annual monitoring of Asian populations to more accurately assess trends. Such monitoring, if it provided evidence of continuing and significant declines across major Asian populations, could provide reason to uplist this species. An International Single Species Action Plan has been adopted by the Bern Convention, CMS and AEWA, which lays out a framework for conservation action throughout the specie's range (Robinson and Callaghan 2003). A restoration project for two key breeding sites on the Danube in Bulgaria is underway, funded by the World Bank (N. Petkov in litt. 2003).

Conservation Actions Proposed
Promote the full legal protection of the species and its habitat through national and international legislation, promote environmentally friendly management of fishponds in Eastern Europe, promote adequate protection and management of key sites, promote conservation in the wider environment for the benefit of the species and its habitat, prevent mortality and disturbance caused by hunting, monitor the remaining population (particularly in Asia)and develop census techniques, investigate productivity and mortality, investigate ecology and limiting factors, investigate the impact of C. idella on the species and its habitat; develop and implement education programmes for the conservation of the species and its habitats.

Citation: BirdLife International. 2016. Aythya nyroca. The IUCN Red List of Threatened Species 2016: e.T22680373A90031490. . Downloaded on 21 January 2017.
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