Grey Plover

Grey Plover

Pluvialis squatarola
Grey Plover, Paul Hillion

Introduction

Primarily a winter visitor to our coastal estuaries, its British name reflects its drab plumage at this time of year.

In summer, though, the Grey plover is more strikingly coloured and elsewhere it is known as the Black-bellied or Silver Plover. This was probably the last regularly occurring British species to have its breeding areas identified – not surprising given they are in the northernmost reaches of Siberia.

As with many Arctic-breeding waders, while some birds come to Britain for the winter, others continue their journey to spend the winter in western Africa. Unlike most birds, Grey Plovers often replace their primary feathers in two stages, moulting some before migrating and the remainder when they've completed their journey.

Grey Plover, Paul Hillion

Key Stats

Status
Common
Common
Weight
Weight
243.4g
BTO Records
BTO Records
250k records
Population and distribution stats for:
Population Size
Population Size
No current data
Distribution Change
Distribution_change
No current data
Population Change
Population Change
31% decrease 1997 to 2022
Distribution Change
Distribution_change
3.1% expansion

Identification

Curated resources to aid in the identification of Grey Plover

ID Videos

This section features BTO training videos headlining this species, or featuring it as a potential confusion species.

Grey & Golden Plovers

Songs and Calls

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

Call:

Alarm call:

Flight call:

Movement

Information about Grey Plover 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 Grey Plover, 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
52x36 mm
Mass (% shell)
34.2g (5%)

Clutch Size

Typical number
4 eggs
Observed minimum and maximum
3-4 eggs

Incubation

Incubation by
Male + Female
Typical duration
26-27 days

Fledging

Type of chick
Precocial, downy
Typical duration
35-45 days

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
9 years with breeding typically at 2 years
Maximum age from a ringed bird
25 years, 1 month, 18 days (set in 2004)

Survival of adults

All adults
0.86

Survival of juveniles

All juveniles
0.63 (in first year)

Biometrics

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

Wing length

Average ±1 std deviation; range and sample size in brackets.
Juvenile
195.3±5.3 mm
(185-203 mm, N=115)
-
All adults
199.5±6 mm
(188-209 mm, N=253)

Body weight

Average ±1 std deviation; 5th and 95th percentiles and sample size in brackets.
Juvenile
235.3±35.5 g
(183-297 g, N=105)
-
All adults
243.4±27.7 g
(200-290 g, N=239)

Ring Size

D2

Classification, names and codes

Taxonomy, names and species codes for Grey Plover

Classification and Codes

  • Order: Charadriiformes
  • Family: Charadriidae
  • Scientific name: Pluvialis squatarola
  • Authority: Linnaeus, 1758
  • BTO 2-letter code: GV
  • BTO 5-letter code: GREPL
  • Euring code number: 4860

Alternate species names

  • Catalan: pigre gris
  • Czech: kulík bledý
  • Danish: Strandhjejle
  • Dutch: Zilverplevier
  • Estonian: plüü
  • Finnish: tundrakurmitsa
  • French: Pluvier argenté
  • Gaelic: Feadag-ghlas
  • German: Kiebitzregenpfeifer
  • Hungarian: ezüstlile
  • Icelandic: Grálóa
  • Irish: Feadóg Ghlas
  • Italian: Pivieressa
  • Latvian: juras kivite
  • Lithuanian: jurinis sejikas
  • Norwegian: Tundralo
  • Polish: siewnica
  • Portuguese: batuiruçu-de-axila-preta / tarambola-cinzenta
  • Slovak: kulík bledý
  • Slovenian: crna prosenka
  • Spanish: Chorlito gris
  • Swedish: kustpipare
  • Welsh: Cwtiad Llwyd
  • English folkname(s): Sea / Silver Plover

Research

Interpretation and scientific publications about Grey Plover from BTO scientists.

Causes of Change and Solutions

Causes of change

Many species of wader, including Grey Plover, have shown a flyway-level decrease in numbers in recent years [Kleefstra et al. 2022] . The drivers of these declines are unclear, but various pressures have been suggested as possible causes, including the effects of fishing, disturbance by tourism, agricultural use and encroachment by buildings, as well as climate change [van Roomen et al. 2022]. It has also been hypothesised that some wader species, including Grey Plover, have shifted to more northerly non-breeding grounds in response to a warming winter climate in Europe making it more feasible for individuals to winter further north in areas such as the Wadden Sea, Scandinavia or Iceland [Maclean et al. 2008, Schekkerman et al. 2021].

Publications (1)

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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