Shelduck

Shelduck

Tadorna tadorna
Shelduck, John Harding

Introduction

Between the size of most ducks and the larger geese, the Shelduck is easy to identify with its white, black and chestnut plumage and bright red bill.

In winter, Shelduck favour muddy estuaries and coastal marshes. Wetland Bird Survey data reveal the importance of north-west England for this species, with about ten thousand birds wintering on both the Dee and Mersey Estuaries. There has been a noticeable extension of range during the last 50 years.

The breeding range in Britain has also been extending inland over this period, with valley farmlands, pig fields and reservoirs are the habitats where Shelduck are most often encountered. This is a burrow-nesting species, so sandy soils and Rabbit warrens assist the birds in finding suitable nest sites.

  • Our Trends Explorer gives you the latest insight into how this species' population is changing.
Shelduck, John Harding

Key Stats

Status
Common
Common
Weight
Weight
1250g
Eggs
Eggs
8-10
BTO Records
BTO Records
880k records
Population and distribution stats for:
Population Change
Population Change
Stable 1995 to 2023
Population Size
Population Size
7,850 pairs
Distribution Change
Distribution_change
38.8% expansion
Population Change
Population Change
25% decrease 1997 to 2022
Distribution Change
Distribution_change
17.2% expansion

Identification

Curated resources to aid in the identification of Shelduck

Songs and Calls

Listen to example recordings of the main vocalisations of Shelduck, provided by xeno-canto contributors.

Call:

Flight call:

Movement

Information about Shelduck movements and migration based on online bird portals (e.g. BirdTrack), Ringing schemes and tracking studies.

Britain & Ireland movement

View a summary of recoveries in the Online Ringing Report

Foreign locations of birds ringed or recovered in Britain & Ireland

Dots show the foreign destinations of birds ringed in Britain & Ireland, and the origins of birds ringed overseas that were subsequently recaptured, resighted or found dead in Britain & Ireland. Dot colours indicate the time of year that the species was present at the location.

  • Winter (Nov-Feb)
  • Spring (Mar-Apr)
  • Summer (May-Jul)
  • Autumn (Aug-Oct)
Foreign locations of birds ringed or recovered in Britain & Ireland

European movements

EuroBirdPortal uses birdwatcher's records, such as those logged in BirdTrack to map the flows of birds as they arrive and depart Europe. See maps for this species here.

The Eurasian-African Migration Atlas shows movements of individual birds ringed or recovered in Europe. See maps for this species here.

Biology

Lifecycle and body size information for Shelduck, including statistics on nesting, eggs and lifespan based on BTO ringing and nest recording data.

Productivity and Nesting

Nesting timing

Typical (exceptional) number of broods
1

Egg measurements

Typical length x width
66x47 mm
Mass (% shell)
78g (9%)

Clutch Size

Typical number
8-10 eggs
Observed minimum and maximum
3-12 eggs

Incubation

Incubation by
Female
Typical duration
29-31 days

Fledging

Type of chick
Precocial, downy
Typical duration
45-50 days
Visit our Trends Explorer for trend graphs and country statistics.

Survival and Longevity

Survival is shown as the proportion of birds surviving from one year to the next and is derived from bird ringing data. It can also be used to estimate how long birds typically live.

View number ringed each year in the Online Ringing Report.

Lifespan

Typical life expectancy of bird reaching breeding age
10 years with breeding typically at 2 years
Maximum age from a ringed bird
19 years, 7 months, 27 days (set in 2013)

Survival of adults

All adults
0.886
Females
0.88
Males
0.909

Survival of juveniles

All juveniles
0.166 (to age 2)
Visit our Trends Explorer for trend graphs and country statistics.

Biometrics

Wing length and body weights are from live birds (source).

Wing length

Average ±1 std deviation; range and sample size in brackets.
Juvenile
296.5±21.4 mm
(256-324 mm, N=94)
All adults
328.5±16.5 mm
(298-348 mm, N=731)
Female
311.9±14 mm
(291-338 mm, N=193)
Male
335.2±12 mm
(316-350 mm, N=526)

Body weight

Average ±1 std deviation; 5th and 95th percentiles and sample size in brackets.
Juvenile
1045.9±245.4 g
(730-1500 g, N=83)
All adults
1250±190 g
(900-1550 g, N=602)
Female
1080±170 g
(850-1400 g, N=153)
Male
1310±150 g
(1050-1560 g, N=437)
Visit our Trends Explorer for trend graphs and country statistics.

Ring Size

G*

Classification, names and codes

Taxonomy, names and species codes for Shelduck

Classification and Codes

  • Order: Anseriformes
  • Family: Anatidae
  • Scientific name: Tadorna tadorna
  • Authority: Linnaeus, 1758
  • BTO 2-letter code: SU
  • BTO 5-letter code: SHELD
  • Euring code number: 1730

Alternate species names

  • Catalan: ànec blanc
  • Czech: husice lišcí
  • Danish: Gravand
  • Dutch: Bergeend
  • Estonian: ristpart
  • Finnish: ristisorsa
  • French: Tadorne de Belon
  • Gaelic: Cràdh-ghèadh
  • German: Brandgans
  • Hungarian: bütykös ásólúd
  • Icelandic: Brandönd
  • Irish: Seil-lacha
  • Italian: Volpoca
  • Latvian: Samsalas dižpile
  • Lithuanian: paprastoji urvine antis
  • Norwegian: Gravand
  • Polish: ohar
  • Portuguese: tadorna
  • Slovak: kazarka pestrá
  • Slovenian: duplinska kozarka
  • Spanish: Tarro blanco
  • Swedish: gravand
  • Welsh: Hwyaden yr Eithin

Research

Interpretation and scientific publications about Shelduck from BTO scientists.

Causes of Change and Solutions

Causes of change

There is little good evidence available regarding the drivers of the breeding population change in this species in the UK.

Further information on causes of change

No further information is available.

Information about conservation actions

The recent trend for Shelduck is uncertain and hence it is unclear whether direct conservation action is currently required for this species in the UK. There is little specific research evidence relating to breeding requirements for the species, but it is likely that actions to maintain and improve availability and habitat quality in wetland habitats will benefit Shelduck. The species nests in underground holes or similar cavities (e.g. rabbit burrows) and the provision of artificial nest sites may help support nesting (BirdLife International)

Publications (4)

Consequences of population change for local abundance and site occupancy of wintering waterbirds

Author: Méndez, V., Gill, J.A., Alves, J.A., Burton, N.H.K. & Davies, R.G.

Published: 2017

Protected sites for birds are typically designated based on the site’s importance for the species that use it. For example, sites may be selected as Special Protection Areas (under the European Union Directive on the Conservation of Wild Birds) if they support more than 1% of a given national or international population of a species or an assemblage of over 20,000 waterbirds or seabirds. However, through the impacts of changing climates, habitat loss and invasive species, the way species use sites may change. As populations increase, abundance at existing sites may go up or new sites may be colonized. Similarly, as populations decrease, abundance at occupied sites may go down, or some sites may be abandoned. Determining how bird populations are spread across protected sites, and how changes in populations may affect this, is essential to making sure that they remain protected in the future. These findings come from a new study by Verónica Méndez and colleagues from the University of East Anglia working with BTO. Using Wetland Bird Survey (WeBS) data the study looked at changes in the population sizes and distributions of 19 waterbird species across Britain during a period of 26 years and their effect on local abundance and site occupancy. Some of these species saw steady increases in population size (up to 1,600%, Avocet), whereas other saw mild declines (-26%, Purple Sandpiper and Shelduck). The results showed that changes in total population size were predominantly reflected in changes in local abundance, rather than through the addition or loss of sites. This is possibly because waterbirds tend to be long-lived birds, with high site fidelity and new suitable sites may not always be available. Thus colonisation of new sites may typically occur when their existing sites approach their maximum capacity. As changes in populations are largely manifested by changes in local abundance – and as sites are often designated for many species – the numbers of sites qualifying for site designation are unlikely to be affected. Understanding the dynamic between population change and change in local abundance will be key to ensuring the efficiency of protected area management and ensuring that populations are adequately protected. Data from the Wetland Bird Survey and its predecessor schemes, which are celebrating 70 years of continuous monitoring of waterbirds this year, have been integral to both the designation of protected sites and monitoring of their condition. Continuation of this monitoring through future generations will ensure that the impacts to waterbird populations of future environmental changes may be understood.

20.09.17

Papers

More Evidence

More evidence from Conservation Evidence.com

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