Oystercatcher

Oystercatcher

Haematopus ostralegus
Oystercatcher, Liz Cutting

Introduction

The Oystercatcher is a striking and familiar wader, its pied plumage contrasting with the bright orange bill and pinkish legs.

The species breeds widely, both around the coast and inland, particularly in northern Britain, whilst during winter large flocks congregate on our estuaries. In Ireland the breeding population remains predominantly coastal. Britain & Ireland support a significant proportion of the global population of this species.

Ringing studies highlight that there is little interchange between the Atlantic subpopulation – which includes those breeding in Iceland, the Faeroes, Britain and Ireland – and the continental subpopulation, which is made up of birds from Scandinavia and the Low Countries.

  • Our Trends Explorer gives you the latest insight into how this species' population is changing.
Oystercatcher, Liz Cutting

Key Stats

Status
Common
Common
Weight
Weight
546.2g
Eggs
Eggs
2-3
BTO Records
BTO Records
1.3m records
Population and distribution stats for:
Population Change
Population Change
21% decrease 1995–2022
Distribution Change
Distribution_change
27.7% expansion
Population Change
Population Change
21% decrease 1996/97–2021/22
Distribution Change
Distribution_change
37.6% expansion

Identification

Curated resources to aid in the identification of Oystercatcher

Songs and Calls

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

Song:

Call:

Alarm call:

Flight call:

Movement

Information about Oystercatcher 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 Oystercatcher, including statistics on nesting, eggs and lifespan based on BTO ringing and nest recording data.

Productivity and Nesting

Nesting timing

Average (range) fo first clutch laying dates
19 May (15 Apr-9 Jun)
Typical (exceptional) number of broods
1

Egg measurements

Typical length x width
56x40 mm
Mass (% shell)
46.5g (7%)

Clutch Size

Typical number
3-2 eggs
Average ±1 standard deviation
2.7±0.69 eggs
Observed minimum and maximum
1-5 eggs

Incubation

Incubation by
Male + Female
Typical duration
27-24 days

Fledging

Type of chick
Precocial, downy
Typical duration
37-34 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
12 years with breeding typically at 4 years
Maximum age from a ringed bird
41 years, 1 month, 5 days (set in 2017)

Survival of adults

All adults
0.88

Survival of juveniles

All juveniles
0.39 (to age 5)
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
258.2±7 mm
(247-269 mm, N=1494)
All adults
263.4±7.5 mm
(251-275 mm, N=8270)
Female
264.3±7.8 mm
(251-278 mm, N=177)
Male
263.4±6.4 mm
(253-274 mm, N=146)

Body weight

Average ±1 std deviation; range and sample size in brackets.
Juvenile
258.2±7 mm
(247-269 mm, N=1494)
All adults
263.4±7.5 mm
(251-275 mm, N=8270)
Female
264.3±7.8 mm
(251-278 mm, N=177)
Male
263.4±6.4 mm
(253-274 mm, N=146)
Visit our Trends Explorer for trend graphs and country statistics.

Ring Size

F

Classification, names and codes

Taxonomy, names and species codes for Oystercatcher

Classification and Codes

  • Order: Charadriiformes
  • Family: Haematopodidae
  • Scientific name: Haematopus ostralegus
  • Authority: Linnaeus, 1758
  • BTO 2-letter code: OC
  • BTO 5-letter code: OYSTE
  • Euring code number: 4500

Alternate species names

  • Catalan: garsa de mar
  • Czech: ústricník velký
  • Danish: Strandskade
  • Dutch: Scholekster
  • Estonian: merisk
  • Finnish: meriharakka
  • French: Huîtrier pie
  • Gaelic: Gille-Brìghde
  • German: Austernfischer
  • Hungarian: csigaforgató
  • Icelandic: Tjaldur
  • Irish: Roilleach
  • Italian: Beccaccia di mare
  • Latvian: juras žagata
  • Lithuanian: eurazine juršarke
  • Norwegian: Tjeld
  • Polish: ostrygojad (zwyczajny)
  • Portuguese: ostraceiro
  • Slovak: lastúrniciar strakatý
  • Slovenian: školjkarica
  • Spanish: Ostrero euroasiático
  • Swedish: strandskata
  • Welsh: Pioden Fôr
  • English folkname(s): Sea Pie

Research

Interpretation and scientific publications about Oystercatcher from BTO scientists.

Causes of Change and Solutions

Causes of change

The main causes of the recent decline are unclear.

Further information on causes of change

The increase in nest failure rates during the 27-day egg stage (25 days for incubation and 2 days for laying) probably results from the spread of the species into less favourable habitats, where nest losses through predation or trampling may be more likely. A 95% decline over 1990-2015 at a study area in Perthshire, Scotland, was attributed to land use and crop type changes (Bell & Calladine 2017). The trend towards earlier laying may be linked to recent climate change (Crick & Sparks 1999).

Information about conservation actions

The causes of the recent decline are unclear and hence conservation requirements are also uncertain. Oystercatchers breed in wetland habitat both along the coast and inland, and therefore actions to improve breeding habitat for other waders may also improve breeding success for Oystercatchers. These could include maintaining and restoring saltmarsh and other wetland habitats, less intensive management of grasslands (including reduced drainage to raise water) and delaying mowing of grasslands in which waders are breeding.

Declines in the Netherlands have been attributed to over-exploitation by shell-fisheries in the Wadden Sea and hence reduced survival during winter (van de Pol et al. 2014). Exploitation of shellfish has also affected some sites in the UK (e.g. Norris et al. 1998; Atkinson et al. 2003), although it is unclear if the UK population declines have been caused by it. However, the majority of the UK breeding population winters around the UK coast, with many estuaries holding protected status as they support nationally and internationally important numbers of Oystercatchers and other wetland species during winter. Appropriate management of shellfish numbers at key wintering sites is therefore likely to be important for this species, along with other policies to ensure these sites continue to be protected and habitat quality maintained or improved (e.g. Goss-Custard et al. (2019).

Publications (11)

Decline in the numbers of Eurasian Oystercatchers Haematopus ostralegus on the Exe estuary Special Protection Area

Author: Goss-Custard, J.D., Austin, G.E., Frost, T.M., Sitters, H.P. & Stillman, R.A.

Published: 2024

The Exe Estuary in Devon is a nationally important site for Oystercatchers wintering in the UK. However, the proportion of this species found in south-west England and wintering on the Exe declined from 60% in the late 1980s to 35% by the late 2010s. This study uses 45 years of data collected by volunteers taking part in the Wetland Bird Survey (WeBS) to investigate why.

07.11.24

Papers

View on journal website

How effective has the management of Cockle and Mussel fisheries on The Wash estuary been in ensuring that there is sufficient food for birds?

Author: Kirkland, M., Atkinson, P.W., Clark J.A. & Robinson, R.A.

Published: 2024

The Wash is England’s largest Special Protection Area, with Oystercatchers being a designated feature. During the winter, Oystercatchers rely heavily on Cockles and Blue Mussels for their food requirements, creating the potential for conflict with the human fisheries for these species.

10.07.24

Reports Research reports

Download PDF

Changes in breeding wader populations of the Uist machair and adjacent habitats between 1983 and 2022

Author: Calladine, J., Fuller, R., Hodkinson, D., Franks, S. & Boyle, J.

Published: 2023

Periodic surveys of machair and associated habitats on the west coast of North Uist, Benbecula and South Uist have documented marked changes in the composition of an important breeding wader assemblage. Within the study area of there was a 25% decline in the total number of breeding waders recorded between 1983 and 2022.

15.06.23

Papers

Modelling important areas for breeding waders as a tool to target conservation and minimise conflicts with land use change

Author: Calladine, J., Border, J., O’Connell, P. & Wilson, M.

Published: 2022

The future of Britain’s breeding wader populations depends on land use policy and local management decisions, both of which require robust evidence and appropriate tools if they are to support the conservation of these priority species. One of the biggest challenges has been the geographical scale at which national data on wader abundance and distribution are available. These data are coarse in their resolution, making them poorly suited to directing conservation initiatives or informing land management decisions at a local scale. But can a statistical approach produce high-resolution maps of predicted wader abundance that are sufficiently accurate to be used for decision-making?

27.09.22

Papers

View this paper online

Sensitivity mapping for breeding waders in Britain: towards producing zonal maps to guide wader conservation, forest expansion and other land-use changes. Report with specific data for Northumberland and north-east Cumbria

Author: O’Connell, P., Wilson, M., Wetherhill, A. & Calladine, J.

Published: 2021

Breeding waders in Britain are high profile species of conservation concern because of their declining populations and the international significance of some of their populations. Forest expansion is one of the most important, ongoing and large-scale changes in land use that can provide conservation and wider environmental benefits, but also adversely affect populations of breeding waders. We describe models to be used towards the development of tools to guide, inform and minimise conflict between wader conservation and forest expansion.Extensive data on breeding wader occurrence is typically available at spatial scales that are too coarse to best inform waderconservation and forestry stakeholders. Using statistical models (random forest regression trees) we model the predicted relative abundances of 10 species of breeding wader across Britain at 1-km square resolution. Bird data are taken from Bird Atlas 2007–11, which was a joint project between BTO, BirdWatch Ireland and the Scottish Ornithologists’ Club, and modelled with a range of environmental data sets.

09.12.21

Reports Research reports

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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.

20.09.17

Papers

The decline of a population of farmland breeding waders: a twenty-five-year case study

Author: M.V. Bell, Calladine, J.

Published: 2017

The breeding populations of many different wader species are in decline across the globe, and the UK is no exception. These declines have been linked to increased predator numbers, changes in agricultural practices, and in the management of the wider landscape. There is an urgent need for information on how such changes in land management, particularly within farmland, may affect breeding waders. This information can then be used to inform future land management decisions.

12.04.17

Papers Bird Study

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