Blackbird

Blackbird

Turdus merula
Blackbird, Edmund Fellowes

Introduction

The Blackbird is one of our most common and familiar birds. It is particularly numerous in gardens, but can be found almost everywhere in Britain & Ireland, apart from the highest ground.

This species forages on the ground, and is most often seen turning over leaf litter, probing the soil for food, or visiting flat feeders like bird tables. Adult male birds are black with a contrasting yellow bill and eyering, whilst females are browner and streakier. The Blackbird's fluting, melodic song, often performed from a high perch, is a particular feature of summer evenings.

Breeding numbers have increased in the UK since the mid-1990s, following a decline during the 1970s and 1980s. The UK also hosts many additional birds from northern Europe in the winter.

  • Our Trends Explorer gives you the latest insight into how this species' population is changing.
Blackbird, Edmund Fellowes

Key Stats

Status
Common
Common
Weight
Weight
101.8g
Eggs
Eggs
3-4
BTO Records
BTO Records
12m records
Population and distribution stats for:
Population Change
Population Change
19% decrease 1967–2022
Distribution Change
Distribution_change
-0.6% contraction

Identification

Curated resources to aid in the identification of Blackbird

ID Videos

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

#BirdSongBasics: Robin and Blackbird

#BirdSongBasics: Blackbird and Song Thrush

Nightingale and Other Night Singers

Ring Ouzel and Blackbird

Songs and Calls

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

Song:

Call:

Alarm call:

Flight call:

Movement

Information about Blackbird 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 Blackbird, 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
22 Apr (22 Mar-14 Jun)
Typical (exceptional) number of broods
2-3(5)

Egg measurements

Typical length x width
29x21 mm
Mass (% shell)
7.2g (6%)

Clutch Size

Typical number
4-3 eggs
Average ±1 standard deviation
3.86±0.75 eggs
Observed minimum and maximum
2-7 eggs

Incubation

Incubation by
Female
Typical duration
14-12 days
Observed average ±1 standard deviation
12.97±1.34 days
Observed minimum and maximum
10.5-15.5 days

Fledging

Type of chick
Altricial, downy
Typical duration
16-13.5 days
Observed average ±1 standard deviation
14.64±1.54 days
Minimum and maximum
12-17 days
N=3892, Source
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
3 years with breeding typically at 1 year
Maximum age from a ringed bird
15 years, 2 months, 5 days (set in 2000)

Survival of adults

All adults
0.65±0.003
Females
0.655±0.007
Males
0.67±0.006

Survival of juveniles

All juveniles
0.564±0.005 (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
129.8±3.9 mm
(124-136 mm, N=53822)
All adults
130.8±4.4 mm
(124-138 mm, N=81803)
Female
128.6±3.8 mm
(123-134 mm, N=39130)
Male
132.9±3.9 mm
(126-139 mm, N=42493)

Body weight

Average ±1 std deviation; range and sample size in brackets.
Juvenile
129.8±3.9 mm
(124-136 mm, N=53822)
All adults
130.8±4.4 mm
(124-138 mm, N=81803)
Female
128.6±3.8 mm
(123-134 mm, N=39130)
Male
132.9±3.9 mm
(126-139 mm, N=42493)
Visit our Trends Explorer for trend graphs and country statistics.

Ring Size

C

Classification, names and codes

Taxonomy, names and species codes for Blackbird

Classification and Codes

  • Order: Passeriformes
  • Family: Turdidae
  • Scientific name: Turdus merula
  • Authority: Linnaeus, 1758
  • BTO 2-letter code: B.
  • BTO 5-letter code: BLABI
  • Euring code number: 11870

Alternate species names

  • Catalan: merla
  • Czech: kos cerný
  • Danish: Solsort
  • Dutch: Merel
  • Estonian: musträstas
  • Finnish: mustarastas
  • French: Merle noir
  • Gaelic: Lòn-dubh
  • German: Amsel
  • Hungarian: fekete rigó
  • Icelandic: Svartþröstur
  • Irish: Lon Dubh
  • Italian: Merlo
  • Latvian: melnais mežastrazds
  • Lithuanian: juodasis strazdas
  • Norwegian: Svarttrost
  • Polish: kos
  • Portuguese: melro
  • Slovak: drozd cierny
  • Slovenian: kos
  • Spanish: Mirlo común
  • Swedish: koltrast
  • Welsh: Mwyalchen

Research

Interpretation and scientific publications about Blackbird from BTO scientists.

Causes of Change and Solutions

Causes of change

The causes of change are uncertain although it is likely that reduced survival drove the initial declines. Agricultural intensification may have contributed to the decline in farmland, but other factors probably operated in woodland and urban habitats.

Further information on causes of change

CBC results show that the decline began in the mid 1970s. It is likely that reduced survival drove the decline (Siriwardena et al. 1998a), although there has been little overall change in survival as recorded by CES since 1983. Adult survival in an intensive colour-ringing study was lowest in the spring during the early breeding season and highest during the autumn (Robinson et al. 2010a); the survival rates found by this study were similar to those found by an earlier study in the 1970s (Batten 1978). However, the 2010 study covered a small geographical area and the survival rates from this area may not be representative of the whole of the UK. Subsequent demographic analysis of national data indicates that annual population changes actually correlate best with adult survival, although population processes appear to differ between eastern and western Britain (Robinson et al. 2012). Fledgling numbers per breeding attempt increased during the population decline and are now decreasing again, suggesting that productivity is density-dependent. Agricultural intensification is likely to have contributed to the population decline (Fuller et al. 1995) but, since numbers fell in woodland as well as farmland, additional factors probably operated. Analysis of nest record data suggests that different factors may affect nest survival in urban and countryside habitats, and that nest productivity is higher in intermediate (urban rural) habitats (Miller et al. 2017).

Information about conservation actions

The causes of the decline from the 1970s to the mid-1990s are uncertain and hence it is also unclear which conservation actions will be most likely to help reverse the declines. Blackbird numbers did increase from the late 1990s until around 2010, suggesting that the earlier issues may no longer be occurring, but these increases have stalled and numbers remain substantially lower than in the late 1960s.

Decreases in farmland may relate to agricultural intensification, where conservation actions to support other species may also benefit Blackbird, particularly those that could aid survival as this is suspected to be the main cause of the decline. These could include providing supplementary food over winter, managing hedgerows or woodland habitat for wildlife, and providing additional habitat, e.g. wild bird seed or cover mixtures, set-aside or grass buffer strips/margins. As Blackbird is a partial migrant, local conservation actions to support birds in winter will not necessarily benefit local populations, and changes over a large scale may hence be required in order for conservation actions to have a significant effect on British (and European) populations. During the breeding season, soil moisture can affect breeding success (Miller et al. 2017), and therefore policies that encourage damper soil may benefit Blackbirds, e.g. reduced drainage.

Much of the population of this species lives in woodland and urban areas, where declines have also occurred. Similar conservation actions to try to improve habitats in these areas would be prudent, but further research is needed before specific targeted actions for Blackbird can be proposed.

Publications (3)

Breeding periods of hedgerow-nesting birds in England

Author: Hanmer, H.J. & Leech, D.I.

Published: Spring 2024

Hedgerows form an important semi-natural habitat for birds and other wildlife in English farmland landscapes, in addition to providing other benefits to farming. Hedgerows are currently maintained through annual or multi-annual cutting cycles, the timing of which could have consequences for hedgerow-breeding birds.The aim of this report is to assess the impacts on nesting birds should the duration of the management period be changed, by quantifying the length of the current breeding season for 15 species of songbird likely to nest in farmland hedges. These species are Blackbird, Blackcap, Bullfinch, Chaffinch, Dunnock, Garden Warbler, Goldfinch, Greenfinch, Linnet, Long-tailed Tit, Robin, Song Thrush, Whitethroat, Wren and Yellowhammer.

05.03.24

Reports Research reports

Download PDF

Combining host and vector data informs emergence and potential impact of an Usutu virus outbreak in UK wild birds

Author: Lawson, B., Robinson, R.A., Briscoe, A., Cunningham, A.A., Fooks, A.R., Heaver, J.P., Hernández-Triana, L.M., John, S.K., Johnson, N., Johnston, C., Lean, F.Z.X., Macgregor, S.K., Masters, N., McCracken, F., McElhinney, L.M., Medlock, J.M., Pearce-Kelly, P., Seilern-Moy, K., Spiro, S., Vaux, A.G.C. & Folly, A.J.

Published: 2022

The identification of the Usutu virus in Greater London in the summer of 2020 raises questions about the extent of the incursion and its impacts on wild bird populations.

18.06.22

Papers

View this paper online

More Evidence

More evidence from Conservation Evidence.com

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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.
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