Red Grouse

Red Grouse

Lagopus scotica
Red Grouse, Sarah Kelman

Introduction

Red Grouse inhabit heather moorland and are often flushed from cover before being seen; as they depart on whirring wings they may call 'go back go back'.

The Red Grouse was formely considered a subspecies of Willow Ptarmigan, but has recently been elevated to species status, making it the second species endemic to Britain and Ireland (Scottish Crossbill is endemic to Scotland). Individuals retain their reddish-brown plumage all year round and the males are territorial during winter, during which time they form pairs. Eggs are laid in a vegetation-lined scrape from April and the resulting chicks develop fast and are capable of flight at just two weeks of age.

Breeding Bird Survey data show the Red Grouse population to be cyclical, with numbers apparently influenced by parasite presence. Reliant on heather, Red Grouse habitat and associated fauna are intensively managed to maintain Red Grouse numbers for shooting from the "glorious" 12th August.

  • Our Trends Explorer gives you the latest insight into how this species' population is changing.
Red Grouse, Sarah Kelman

Key Stats

Status
Common
Common
Eggs
Eggs
6-9
BTO Records
BTO Records
78k records
Population and distribution stats for:
Population Change
Population Change
Stable 1995–2022
Distribution Change
Distribution_change
-25% contraction
Population Size
Population Size
No current data
Distribution Change
Distribution_change
11.4% expansion

Identification

Curated resources to aid in the identification of Red Grouse

ID Videos

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

Grouse

Songs and Calls

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

Song:

Call:

Movement

Information about Red Grouse 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

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.

Biology

Lifecycle and body size information for Red Grouse, 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
42x31 mm
Mass (% shell)
21.5g (7%)

Clutch Size

Typical number
9-6 eggs
Observed minimum and maximum
2-17 eggs

Incubation

Incubation by
Female
Typical duration
25-19 days

Fledging

Type of chick
Precocial, downy
Typical duration
13-12 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.

lifespan

Typical life expectancy of bird reaching breeding age
2 years with breeding typically at 1 year

Survival of adults

All adults
0.47

Survival of juveniles

All juveniles
0.34 (in first year)
Visit our Trends Explorer for trend graphs and country statistics.

Biometrics

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

Visit our Trends Explorer for trend graphs and country statistics.

Ring Size

F*

Classification, names and codes

Taxonomy, names and species codes for Red Grouse

Classification and Codes

  • Order: Galliformes
  • Family: Phasianidae
  • Scientific name: Lagopus scotica
  • Authority: Linnaeus, 1758
  • BTO 2-letter code: RG
  • BTO 5-letter code: REDGR
  • Euring code number: 3292

Alternate species names

  • Catalan: perdiu boreal
  • Czech: belokur rousný
  • Danish: Dalrype
  • Dutch: Moerassneeuwhoen
  • Estonian: rabapüü
  • Finnish: riekko
  • French: Lagopède des saules
  • Gaelic: Cearc-fhraoich
  • German: Moorschneehuhn
  • Hungarian: sarki hófajd
  • Icelandic: Dalrjúpa
  • Irish: Cearc Fhraoigh
  • Italian: Pernice bianca nordica
  • Latvian: (baltirbe), teteris
  • Lithuanian: paprastoji žvyre
  • Norwegian: Lirype
  • Polish: pardwa mszarna
  • Portuguese: lagopo-ruivo
  • Slovak: snehula kapcavá
  • Slovenian: barjanski jereb
  • Spanish: Lagópodo común
  • Swedish: dalripa
  • Welsh: Grugiar Goch
  • English folkname(s): Grouse, Heather Cock

Research

Interpretation and scientific publications about Red Grouse from BTO scientists.

Causes of Change and Solutions

Causes of change

Longer-term trends in Red Grouse abundance are overlain by cycles, with periods that vary regionally, linked to the dynamics of infection by a nematode parasite and to interrelated variations in the aggressiveness of males in autumn.

Further information on causes of change

Given its economic significance, long-term population trends of Red Grouse are likely to be closely associated with changes in management practices (see below). Shooting bags have revealed long-term declines, apparently driven by a combination of a loss of heather moorland, increased predation from corvids and foxes, and an increasing incidence of viral disease (Hudson 1992, Newton 2004). However, these trends appear to be overlain by cycles, with periods that vary regionally, linked to the dynamics of infection by a nematode parasite Trichostrongylus tenuis (Dobson & Hudson 1992, Gibbons et al. 1993) and to interrelated variations in the aggressiveness of males in autumn (Martinez-Padilla et al. 2014). Recent increases in the Red Grouse population have been attributed to the use of higher strengths of medicated grit (Thompson et al. 2016).

Strip burning of heather is undertaken to increase suitable habitat for Red Grouse. Although the short-term effect is to reduce the abundance of birds using the recently burnt areas (Douglas et al. 2017), densities subsequently increase most in areas where heather recovery is greatest (Ludwig et al. 2018c). Analysis of game bag data since 1890 linked population changes to changes in keeper density and afforestation (Robertson et al. 2017). However the wider environmental impacts of moorland management for grouse are contested (Thompson et al. 2016, Sotherton et al. 2017). Whilst long-term declines are most likely linked to habitat changes (Thirgood et al. 2000), raptor predation may subsequently have limited population growth at some sites (Thirgood et al. 2000, Roos et al. 2018). In a study looking at four upland areas in the UK, higher Red Grouse abundance was correlated positively with higher predator control (Buchanan et al. 2017), and abundance and breeding success was higher at a Scottish site in years when predators were controlled (Ludwig et al. 2017). Other studies have concluded that mortality associated with raptors are important factors in survival but could not exclude scavenging so may have over-estimated true predation (Ludwig et al. 2018b, Francksen et al. 2019).

Hen Harriers in particular can reduce grouse shooting bags, limit grouse populations and cause economic losses to moor owners, which has led to instances of illegal persecution (Thompson et al. 2009, 2016, Murgatroyd et al. 2019; see also Conservation Actions section, below).

Laying dates in the Scottish Highlands advanced by about ten days between 1992 and 2011, and were inversely correlated with pre-laying temperatures, but no overall effect of climate change on chick survival could be identified (Fletcher et al. 2013).

At Langholm Moor, Red Grouse productivity was lower, suggesting higher chick predation, in years with high vole abundance; the reasons for this were unclear but were believed to be more consistent with the hypothesis that 'apparent competition' was occurring between voles and grouse, rather than the 'alternative prey' hypothesis, i.e. that incidental grouse chick predation is higher when increased vole numbers attract more predators (Ludwig et al. 2020b).

Information about conservation actions

This species is Amber-listed in the UK due to its European status; however, the fluctuating BBS trend does not raise any alerts and so does not give cause for concern. The species benefits from intensive management of moorland, to increase numbers available to be shot, and therefore no specific additional conservation actions are currently required.

Some observers have questioned the legitimacy of grouse shooting if it is only viable when birds of prey are routinely killed (Thompson et al. 2009), whilst others contend that grouse shooting protects the conservation of heather moorland and hence populations of some declining birds such as waders that depend upon it (Sotherton et al. 2009). The relative importance of predation and habitat management on numbers of Red Grouse, and on the wider environment including other moorland birds, in particular Hen Harrier, is the source of much debate with strongly opposing views (Redpath & Thirgood 2008, Thompson et al. 2016, Sotherton et al. 2017, Hodgson et al. 2018, 2019, St John et al. 2018). This has consequences for wider moorland management and the bird populations that live there (Redpath & Thirgood 2009, Thompson et al. 2016). The final report of the Langholm Moor Demonstration project concluded that whilst some targets had been met, the project was unable to achieve compatibility for management between raptor and Red Grouse interests and grouse numbers remained insufficient to make driven shooting viable (LMDP Partners 2019).

Publications (1)

Nesting dates of Moorland Birds in the English, Welsh and Scottish Uplands

Author: Wilson, M.W., Fletcher, K., Ludwig, S.C. & Leech, D.I.

Published: 2022

Rotational burning of vegetation is a common form of land management in UK upland habitats, and is restricted to the colder half of the year, with the time period during which burning may be carried out in upland areas varying between countries. In England and Scotland, this period runs from the 1st October to 15th April, but in the latter jurisdiction, permission can be granted to extend the burning season to 30th April. In Wales, this period runs from 1st October to 31st March.This report sets out timing of breeding information for upland birds in England, Scotland and Wales, to assess whether rotational burning poses a threat to populations of these species, and the extent to which any such threat varies in space and time.

17.02.22

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More Evidence

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