Purple Sandpiper

Purple Sandpiper

Calidris maritima
Purple Sandpiper, Liz Cutting

Introduction

This hardy wader is found on exposed rocky shores in winter; only its breeding plumage is purple-tinged.

Never common as a breeding bird, with only a handful of pairs recorded in northern Scotland, the Purple Sandpiper is now a less than annual breeder. A plump, stocky wader with distinctive yellow legs it is distributed around almost all coasts in winter, only being scarce in southern and eastern England.

Ringing records show that Purple Sandpipers are remarkably faithful to wintering sites, with individuals returning to the exact same stretch of coast year after year.

Purple Sandpiper, Liz Cutting

Key Stats

Status
Scarce
Scarce
Weight
Weight
70.8g
BTO Records
BTO Records
99k records
Population and distribution stats for:

Identification

Curated resources to aid in the identification of Purple Sandpiper

Songs and Calls

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

Call:

Movement

Information about Purple 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 Purple Sandpiper, 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
38x26 mm
Mass (% shell)
13.3g (5%)

Clutch Size

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

Incubation

Incubation by
Male (occ. Female)
Typical duration
21-22 days

Fledging

Type of chick
Precocial, downy
Typical duration
15-28 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
6 years with breeding typically at 2 years
Maximum age from a ringed bird
15 years, 2 months, 27 days (set in 1997)

Survival of adults

All adults
0.795±0.028

Biometrics

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

Wing length

Average ±1 std deviation; range and sample size in brackets.
Juvenile
130.4±3.9 mm
(123-136 mm, N=115)
-
All adults
131.8±4.1 mm
(125-138 mm, N=1533)

Body weight

Average ±1 std deviation; 5th and 95th percentiles and sample size in brackets.
Juvenile
67.6±7.6 g
(55-80 g, N=114)
-
All adults
70.8±9 g
(57-86 g, N=1524)

Ring Size

B+ or C2

Classification, names and codes

Taxonomy, names and species codes for Purple Sandpiper

Classification and Codes

  • Order: Charadriiformes
  • Family: Scolopacidae
  • Scientific name: Calidris maritima
  • Authority: Brünnich, 1764
  • BTO 2-letter code: PS
  • BTO 5-letter code: PURSA
  • Euring code number: 5100

Alternate species names

  • Catalan: territ fosc
  • Czech: jespák morský
  • Danish: Sortgrå Ryle
  • Dutch: Paarse Strandloper
  • Estonian: merirüdi e. meririsla
  • Finnish: merisirri
  • French: Bécasseau violet
  • Gaelic: Luatharan-rìoghail
  • German: Meerstrandläufer
  • Hungarian: tengeri partfutó
  • Icelandic: Sendlingur
  • Irish: Gobadán Cosbhuí
  • Italian: Piovanello violetto
  • Latvian: juras šnibitis
  • Lithuanian: jurinis begikas
  • Norwegian: Fjæreplytt
  • Polish: biegus morski
  • Portuguese: pilrito-escuro
  • Slovak: pobrežník morský
  • Slovenian: morski prodnik
  • Spanish: Correlimos oscuro
  • Swedish: skärsnäppa
  • Welsh: Pibydd Du
  • English folkname(s): Grollick

Research

Interpretation and scientific publications about Purple Sandpiper from BTO scientists.

Causes of Change and Solutions

Causes of change

A study on the declining Purple Sandpiper population wintering in the Moray Firth in Scotland [Summers et al. 2012] concluded that this decline may be due to poor recruitment into the breeding population (possibly as a result of a decline in productivity in Norway and Canada), but may also be a response to changes in local sewage treatment systems on the Moray affecting food availability or a general reduction in the number of Purple Sandpipers wintering in Scotland. The number of Purple Sandpipers wintering in the UK may also be impacted by climate change, in particular, increasing temperatures [Rehfisch et al. 2004].

Publications (3)

The status of our bird populations: the fifth Birds of Conservation Concern in the United Kingdom, Channel Islands and Isle of Man and second IUCN Red List assessment of extinction risk for Great Britain

Author: Stanbury, A.J., Eaton, M.A., Aebischer, N.J., Balmer, D., Brown, A.F., Douse, A., Lindley, P., McCulloch, N., Noble, D.G. & Win, I.

Published: 2021

Commonly referred to as the UK Red List for birds, this is the fifth review of the status of birds in the UK, Channel Islands and Isle of Man, published in December 2021 as Birds of Conservation Concern 5 (BOCC5). This updates the last assessment in 2015. Using standardised criteria, experts from a range of bird NGOs, including BTO, assessed 245 species with breeding, passage or wintering populations in the UK and assigned each to the Red, Amber or Green Lists of conservation concern. The same group of experts undertook a parallel exercise to assess the extinction risk of all bird species for Great Britain (the geographical area at which all other taxa are assessed) using the criteria and protocols established globally by the International Union for the Conservation of Nature (IUCN). This resulted in the assessment of 235 regularly occurring species (breeding or wintering or both), the total number assessed differing slightly from BOCC5 due to different rules on the inclusion of scarce breeders and colonisation patterns. The results of this second IUCN assessment (IUCN2) are provided in the same paper as BOCC5. Increasingly at risk This update shows that the UK’s bird species are increasingly at risk, with the Red List growing from 67 to 70. Eleven species were Red-listed for the first time, six due to worsening declines in breeding populations (Greenfinch, Swift, House Martin, Ptarmigan, Purple Sandpiper and Montagu’s Harrier), four due to worsening declines in non-breeding wintering populations (Bewick’s Swan, Goldeneye, Smew and Dunlin) and one (Leach’s Storm-petrel) because it is assessed according to IUCN criteria as Globally Vulnerable, and due to evidence of severe declines since 2000 based on new surveys on St Kilda, which holds more than 90% of the UK’s populations. The evidence for the changes in the other species come from the UK’s key monitoring schemes such as BTO/JNCC/RSPB Breeding Bird Survey (BBS) for terrestrial birds, the BTO/RSPB/JNCC Wetland Bird Survey (WeBS) for wintering populations and the Rare Breeding Bird Panel (RBBP) for scarce breeding species such as Purple Sandpiper. The IUCN assessment resulted in 108 (46%) of regularly occurring species being assessed as threatened with extinction in Great Britain, meaning that their population status was classed as Critically Endangered, Endangered, or Vulnerable, as opposed to Near Threatened or of Least Concern. Of those 108 species, 21 were considered Critically Endangered, 41 Endangered and 46 Vulnerable. There is considerable overlap between the lists but unlike the Red List in BOCC5, IUCN2 highlights the vulnerability of some stable but small and hence vulnerable populations as well as declines in species over much shorter recent time periods, as seen for Chaffinch and Swallow.

01.12.21

Reports Birds of Conservation Concern

Download file

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

Birdfacts is based on data collected by volunteers participating in surveys that are organised and funded by BTO, RSPB, Esmée Fairbairn Foundation, JNCC and other partners.

Citing BirdFacts

If you wish to cite particular content in this page (e.g. a specific value) it is best to use the original sources as linked in the page. For a more general citation of the whole page please use: BTO (20XX) BirdFacts Species: profiles of birds occurring in the United Kingdom. BTO, Thetford (www.bto.org/birdfacts, accessed on xx/xx/xxxx).

Find a Species

Search by common or scientific name