Purple Sandpiper
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.
Key Stats
Identification
Songs and Calls
Call:
Status and Trends
Conservation Status
Population Change
The UK plays host to wintering Purple Sandpipers from the eastern Canadian, Scandinavian and Svalbard breeding populations. It is also a very scarce breeding species, with one or two confirmed breeding records reported annually. This species is found on rocky shores in small numbers around UK coastlines, with internationally important numbers at a few sites in Scotland and north-east England, . The number of birds wintering here peaked in the mid 1980s, after which the species declined, although numbers have remained stable in recent years.
Distribution
Purple Sandpipers prefer northern, exposed, shallow rocky shores in winter. High concentrations occur along the coasts of the northern North Sea, Northern Isles and Outer Hebrides and around exposed headlands in Ireland. Elsewhere, occupied areas around Wales and southeastern and southern England hold very few birds. Purple Sandpiper is among the UK's rarest breeding species, with occasional breeding in the Scottish Highlands.
Occupied 10-km squares in UK
2007/08–10/11
or view it on Bird Atlas Mapstore.
2008–11
or view it on Bird Atlas Mapstore.
European Distribution Map
Distribution Change
Change in occupied 10-km squares in the UK
from 1981–84 to 2007–11
or view it on Bird Atlas Mapstore.
from 1968–72 to 2008–11
or view it on Bird Atlas Mapstore.
Seasonality
Purple Sandpipers are winter visitors; returning birds can arrive from June onwards.
Weekly pattern of occurrence
The graph shows when the species is present in the UK, with taller bars indicating a higher likelihood of encountering the species in appropriate regions and habitats.
Movement
Britain & Ireland movement
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)
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
Productivity and Nesting
Nesting timing
Egg measurements
Clutch Size
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
Survival of adults
Biometrics
Wing length and body weights are from live birds (source).
Wing length
Body weight
Ring Size
Classification, names and codes
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
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
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
Aggressive behaviour and correlates of dominance in Purple Sandpipers Calidris maritima at a communal winter roost
Author: Burton, N.H.K. & Evans, P.R.
Published: 2001
01.01.01
Papers
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