Common Sandpiper

Common Sandpiper

Actitis hypoleucos
Common Sandpiper, Moss Taylor

Introduction

This small wader is most commonly encountered on upland rivers and lochs, and characteristically flicks its wings as it flies low over the water.

Brown above, with a well demarcated white breast, this handsome wader returns from its African wintering quarters in late April and pairs hold linear territories, defending them with noisy display flight. The species nests in vegetation by the water side, where, in common with most waders, it lays typically lays four eggs.

Numbers have declined steadily in recent years, for reasons that remain unclear, but may be linked to climate change increasing mortality in its wintering grounds.

  • Our Trends Explorer gives you the latest insight into how this species' population is changing.
Common Sandpiper, Moss Taylor

Key Stats

Status
Common
Common
Eggs
Eggs
4-4
BTO Records
BTO Records
300k records
Population and distribution stats for:
Population Change
Population Change
25% decrease 1995–2022
Distribution Change
Distribution_change
-15.3% contraction

Identification

Curated resources to aid in the identification of Common Sandpiper

Songs and Calls

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

Song:

Call:

Alarm call:

Movement

Information about Common Sandpiper 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 Common Sandpiper, 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 (5 May-6 Jun)
Typical (exceptional) number of broods
1

Egg measurements

Typical length x width
36x26 mm
Mass (% shell)
12.5g (5%)

Clutch Size

Typical number
4-4 eggs
Average ±1 standard deviation
3.85±0.45 eggs
Observed minimum and maximum
2-5 eggs

Incubation

Incubation by
Male + Female
Typical duration
22-21 days

Fledging

Type of chick
Precocial, downy
Typical duration
19-19 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
8 years with breeding typically at 2 years
Maximum age from a ringed bird
15 years, 1 month, 5 days (set in 2007)

Survival of adults

All adults
0.844±0.062
Females
0.67
Males
0.72

Survival of juveniles

All juveniles
0.57 (in first year)
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
112.3±3.4 mm
(107-118 mm, N=458)
All adults
112.2±3.3 mm
(107-117 mm, N=464)
Female
115.2±3 mm
(111-120 mm, N=41)
Male
110.8±3.1 mm
(106-115 mm, N=33)

Body weight

Average ±1 std deviation; range and sample size in brackets.
Juvenile
112.3±3.4 mm
(107-118 mm, N=458)
All adults
112.2±3.3 mm
(107-117 mm, N=464)
Female
115.2±3 mm
(111-120 mm, N=41)
Male
110.8±3.1 mm
(106-115 mm, N=33)
Visit our Trends Explorer for trend graphs and country statistics.

Ring Size

B+

Classification, names and codes

Taxonomy, names and species codes for Common Sandpiper

Classification and Codes

  • Order: Charadriiformes
  • Family: Scolopacidae
  • Scientific name: Actitis hypoleucos
  • Authority: Linnaeus, 1758
  • BTO 2-letter code: CS
  • BTO 5-letter code: COMSA
  • Euring code number: 5560

Alternate species names

  • Catalan: xivitona comuna
  • Czech: pisík obecný
  • Danish: Mudderklire
  • Dutch: Oeverloper
  • Estonian: vihitaja e. jõgitilder
  • Finnish: rantasipi
  • French: Chevalier guignette
  • Gaelic: Fìdhleir-bòrd-an-locha
  • German: Flussuferläufer
  • Hungarian: billegetocankó
  • Icelandic: Lindastelkur
  • Irish: Gobadán Coiteann
  • Italian: Piro piro piccolo
  • Latvian: upes tilbite
  • Lithuanian: paprastasis krantinis tilvikas
  • Norwegian: Strandsnipe
  • Polish: brodziec piskliwy
  • Portuguese: maçarico-das-rochas / maçarico-ribeirinho
  • Slovak: kalužiacik malý
  • Slovenian: mali martinec
  • Spanish: Andarríos chico
  • Swedish: drillsnäppa
  • Welsh: Pibydd Dorlan
  • English folkname(s): Sand Lark

Research

Interpretation and scientific publications about Common Sandpiper from BTO scientists.

Causes of Change and Solutions

Causes of change

The drivers of the decline of this species are unclear; however it is unlikely to be caused by changes in the wintering area and hence probably relates to problems occurring during either the breeding season or on migration, or both.

Further information on causes of change

Poorer breeding success and reduced survival of first-year birds over the winter in West Africa were both suggested as possible reasons for the failure of the Peak District population to recover after a hard-weather event in 1989 (Holland & Yalden 2002). The reasons for poor recruitment to the breeding population are hard to assess in the absence of firm information on where British birds spend the winter (Dougall et al. 2010). However recent tracking of ten adult birds from Scotland identified coastal Guinea-Bissau as the most important wintering area and concluded that it was unlikely that habitat change in this area had been sufficient to cause the observed decline. The tracked birds did experience some unfavourable weather during northward migration but further work would be needed to confirm whether this could have affected population levels (Summers et al. 2019).

UK clutch sizes appear to have shown a slight decline from the 1960s to the 1990s, which has since been almost reversed, although this is based on a small sample.

Information about conservation actions

In one study in the Peak District, disturbance from anglers restricted the area available to sandpipers at the study site and hence reduced the breeding population (Yalden 1992). Whilst it remains unclear whether similar disturbance has been widespread enough to have contributed to the population declines, actions to prevent disturbance at key sites would be prudent.

In the absence of any evidence identifying other specific recommendations, actions to conserve existing habitats and water quality should also be considered.

Publications (2)

Birds of Conservation Concern Wales 4: the population status of birds in Wales

Author: Johnstone, I.G., Hughes, J., Balmer, D.E., Brenchley, A., Facey, R.J., Lindley, P.J., Noble, D.G. & Taylor, R.C.

Published: 2022

The latest review of the conservation status of birds in Wales. The report assessed all 220 bird species which regularly occur in Wales. There are now 60 species of bird on the Red List, with 91 on the Amber List and just 69 - less than a third of the total number of species - on the Green List.

06.12.22

Reports Birds of Conservation Concern

View a summary report

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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