Sanderling

Sanderling

Calidris alba
Sanderling, Edmund Fellowes

Introduction

The caricature of a Sanderling is a small, white mouse-like wader chasing the tideline back and forth on a sandy beach.

These birds are winter visitors to Britain & Ireland, distributed widely around the coast and preferring long sandy beaches and sandbars.

Sanderlings are seen less frequently at inland sites than other coastal waders. It was previously thought that all our winter visitors originated from breeders in Siberia, but ringing studies have shown that we also host individuals from the Greenland population on passage, some of which stay for the winter.

Sanderling, Edmund Fellowes

Key Stats

Status
Common
Common
Weight
Weight
57.7g
BTO Records
BTO Records
180k records
Population and distribution stats for:
Population Size
Population Size
No current data
Distribution Change
Distribution_change
No current data
Population Change
Population Change
55% increase 1997 to 2022
Distribution Change
Distribution_change
31.5% expansion

Identification

Curated resources to aid in the identification of Sanderling

ID Videos

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

Sanderling & Curlew Sandpiper

Songs and Calls

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

Flight call:

Movement

Information about Sanderling 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 Sanderling, 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
36x25 mm
Mass (% shell)
11.2g (5%)

Clutch Size

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

Incubation

Incubation by
Female (occ. Male)?
Typical duration
24-27 days

Fledging

Type of chick
Precocial, downy
Typical duration
16-18 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
7 years with breeding typically at 2 years
Maximum age from a ringed bird
17 years, 7 months, 3 days (set in 1988)

Survival of adults

All adults
0.83

Biometrics

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

Wing length

Average ±1 std deviation; range and sample size in brackets.
Juvenile
126.2±3.1 mm
(121-132 mm, N=138)
-
All adults
126.7±3.6 mm
(121-133 mm, N=1392)

Body weight

Average ±1 std deviation; 5th and 95th percentiles and sample size in brackets.
Juvenile
55.5±9 g
(42.6-71 g, N=134)
-
All adults
57.7±8.3 g
(46-73 g, N=1473)

Ring Size

B2

Classification, names and codes

Taxonomy, names and species codes for Sanderling

Classification and Codes

  • Order: Charadriiformes
  • Family: Scolopacidae
  • Scientific name: Calidris alba
  • Authority: Pallas, 1764
  • BTO 2-letter code: SS
  • BTO 5-letter code: SANDE
  • Euring code number: 4970

Alternate species names

  • Catalan: territ de tres dits
  • Czech: jespák písecný
  • Danish: Sandløber
  • Dutch: Drieteenstrandloper
  • Estonian: leeterüdi e. leeterisla
  • Finnish: pulmussirri
  • French: Bécasseau sanderling
  • Gaelic: Luatharan-glas
  • German: Sanderling
  • Hungarian: fenyérfutó
  • Icelandic: Sanderla
  • Irish: Luathrán
  • Italian: Piovanello tridattilo
  • Latvian: gaišais šnibitis
  • Lithuanian: paprastasis smiltinukas
  • Norwegian: Sandløper
  • Polish: piaskowiec
  • Portuguese: maçarico-branco / pilrito-das-praias
  • Slovak: pobrežník belavý
  • Slovenian: pešcenec
  • Spanish: Correlimos tridáctilo
  • Swedish: sandlöpare
  • Welsh: Pibydd y Tywod
  • English folkname(s): Towillee, Curwillet

Research

Interpretation and scientific publications about Sanderling from BTO scientists.

Causes of Change and Solutions

Causes of change

Despite Sanderlings being common across the flyway, the exact reasons for both the long-term increase and the more recent stabilisation are unknown [van Roomen et al. 2022]. Previous studies have identified threats to Sanderling populations including density-dependent factors [Ntiamoa-Baidu et al. 2014], habitat destruction, climate change [Reneerkens et al. 2016, Schmidt et al. 2019, Reneerkens 2020], human disturbance [Burger & Gochfeld 1991], pollution [Bianchini & Morrissey 2018] and hunting, but it is unclear to what extent these factors have affected Sanderling population growth. A more recent study by Reneerkens [2022] identified that the growth of the Sanderling flyway-population is currently limited by annual variation in clutch survival and adult survival in West Africa.

Publications (2)

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

Partners

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