This large, lanky wader is most often picked up in wetlands on autumn passage by its distinctive three-note call.
Reports to BirdTrack peak from mid-July to late-September, as individuals migrate south to their wintering grounds in the west of Africa. At this time of year, Greenshank can be found in both coastal and freshwater wetlands, but in the breeding season this is very much a bird of remote moorland, with breeding records confined to the Highlands and islands of Scotland.
Much is known about Greenshank breeding behaviour thanks to a classic study by Desmond Nethersole-Thompson, which was carried out in the “Flow Country” of northern Scotland. Territories usually include a large rock or dead tree as song-post.
Select a topic for more facts and statistics about the Greenshank
Ruff, with their variable size and plumage, often present identification issues. However, by learning how to recognise Ruff in their various guises through this video, you’ll be able to pick them out with confidence, and have a great reference point for identifying other similar-looking waders.
Listen to example recordings of the main vocalisations of Greenshank, provided by xeno-canto contributors.
Other
Call
Song
Develop your bird ID skills with our training courses
Our interactive online courses are a great way to develop your bird identification skills, whether you're new to the hobby or a competent birder looking to hone your abilities.
Greenshank breeds in the far north and west of Scotland where it is difficult to survey. The only national survey was made over 20 years ago and came up with a population estimate of 1,080 breeding pairs (Hancock et al. 1997). Hence the status and long-term trend is unclear. The breeding range in the 2008–11 Breeding Atlas was similar to that in 1968–72 with a very slight increase of 2% in the number of occupied squares (Balmer et al. 2013).
Breeding Greenshanks are largely restricted to the bogs and moors of the northwest Highlands and Hebridean islands, with the highest densities in Sutherland, Wester Ross, Lewis, Harris and North Uist. Most wintering bird are associated with large estuary complexes throughout the coasts of Britain & Ireland. Densities are highest in the west, especially in Ireland and parts of western Scotland.
Britain and Ireland Breeding Distribution 2008-2011. More from the Atlas Mapstore.
Britain and Ireland Winter Distribution 2008-2011. More from the Atlas Mapstore.
There have been minor breeding-range expansions, mostly on Shetland, Lewis, North Uist and in West Inverness. Losses are most evident in the eastern fringes of the range, particularly in Badenoch and Strathspey.
Britain and Ireland Breeding Distribution Change 1968–72 to 2008–11. More from the Atlas Mapstore.
Britain and Ireland Winter Distribution Change 1981–84 to 2007–11 More from the Atlas Mapstore.
Change in occupied 10-km squares in the UK
% change in range in breeding season (1968–72 to 2008–11)
Greenshanks are recorded throughout the year, though most likely during autumn passage.
Weekly occurrence patterns (shaded cells) and reporting rates (vertical bars) based on BirdTrack data. Reporting rates give the likelihood of encountering the species each week.
Movement
Information about movement and migration based on online bird portals (e.g. BirdTrack), Ringing schemes and tracking studies.
An overview of year-round movements for the whole of Europe can be seen on the EuroBirdPortal viewer.
The current trend is uncertain and hence drivers of change are also unclear. Some local declines may be linked to habitat degradation and afforestation (Hancock et al. 1997). However, Watson & Francis (2012) suggested a number of possible causes to explain local losses in Deeside including acidic deposition, overgrazing and trampling, disturbance, predation and reforestation. Further research is needed therefore to confirm whether or not any of these possible causes contribute towards population trends.
Protected sites are assigned based on population statistics for vulnerable and endangered species. This new study using WeBS data shows that changes in population size can affect local abundance, and thus influence whether or not key targets are met for site protection.
GRESH 
Share this page