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Population trends for breeding birds in the UK, to 2024

This page hosts the Official Statistic ‘Population trends for breeding birds in the UK’, published on 15 May 2025.

Official Statistic description

  • This publication presents trends for breeding bird populations in the UK and for each UK country, showing change in population between 1994 and 2024. The statistics are based on data gathered through the BTO/JNCC/RSPB Breeding Bird Survey (BBS), which is a long-term citizen science monitoring scheme involving annual sampling at around 4,000 sites across the UK.
  • Trends reporting changes for 119 species in the UK between 1995 and 2023 are published using data collected from the duration of the survey (1994–2024). These trends also include data from 31 squares in the Channel Islands and Isle of Man. Trends from 1995–2023 are reported for 116 species in England, 77 species in Scotland, 60 species in Wales, and 39 species in Northern Ireland
  • UK and country-level trends are also reported for more recent shorter time periods (1-year, 5-year, and 10-year).
  • The survey methods and analytical methods are described in the Methods section below.
  • The Breeding Bird Survey annual report also includes the results presented here, methods, and papers published during 2024/25 that use BBS data.

The Breeding Bird Survey is a partnership jointly funded by the British Trust for Ornithology (BTO), the Royal Society for the Protection of Birds (RSPB), and the Joint Nature Conservation Committee (JNCC). The BBS is indebted to the thousands of volunteer data recorders who take part.

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Scope of Statistics

  • The statistic presents trends for the UK and for England, Scotland, Wales, and Northern Ireland. UK trends include data collected by BBS from the Channel Islands and the Isle of Man.

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Results

Trend tables showing the 1-year, 5-year, 10-year, and 28-year BBS species trends for the UK and for each UK country are available for download.

For related information that sits outside of the BBS official statistic, including trend tables for the English regions, the Waterways Breeding Bird Survey (WBBS), and mammal data collected through BBS, please visit the BTO website.

Summary of results

Table 1: Summary of species trends over the whole BBS period, ten years, and one year for each region.

Country

Total number of species

28-year trend

(1995–2023)

10-year trend

(2013–2023)

1-year trend

(2023–2024)

 

 

Significant declines

Significant increases

Significant declines

Significant increases

Significant declines

Significant increases

UK

119

43

36

52

24

21

15

England

116

41

35

53

26

20

16

Scotland

77

14

22

14

13

8

5

Wales

60

15

17

14

13

4

3

Northern Ireland

39

1

16

11

8

7

7

 

  • Across the UK, 36 species have statistically significant long-term (1995–2023) increases and 43 species have significant long-term declines. Note that:
    • Some species that are in decline are too rare to be robustly monitored by the BBS and so will not be included in these figures.
    • Population increases include the expansion of recent colonists and non-native species.
  • Of the 26 Birds of Conservation Concern (BoCC) Red-listed species with long-term trends, 1 had a statistically significant increase and 22 had significant declines.
  • Of the 31 BoCC Amber-listed species with long-term trends, 10 had statistically significant increases and 13 had significant declines.
  • As in previous years, the largest long-term increase is for Little Egret (2,726%) but note this may contain a high proportion of birds away from breeding sites. The next largest increases are for Red Kite (2,464%) and Ring-necked parakeet (2,406%). The former continues to expand its population and range following reintroductions in the late 1980s–1990s.
  • The largest long-term declines continue to be for Turtle Dove (-98%), Willow Tit (-90%) and Wood Warbler (-81%).
  • 24 species have statistically significant increases over the past 10 years and 52 species have statistically significant declines.
  • 23 species have statistically significant increases over the past 5 years and 42 species have statistically significant declines.
  • 15 species have statistically significant increases over the past year and 21 species have statistically significant declines. Note that populations generally fluctuate from year to year, although shorter-term results can be important if these build on longer-term trends.
  • Results in England are similar to the UK. 35 species have statistically significant long-term increases and 41 species have long-term declines. Similar to previous years, the largest long-term increases are for Red Kite (24,725%), Ring-Necked Parakeet (2,397%), and Little Egret (2,479%). The largest long-term declines are Turtle Dove (-98%), Willow Tit (-91%), Little Owl (-78%), and Spotted Flycatcher (-71%).
  • Two species have had trends in England published for the first time in this year’s BBS results: Golden Plover and Marsh Harrier. This is due to a change in analytical methods for Golden Plover and the success of conservation efforts for Marsh Harrier, boosting numbers enough to produce robust trends. The new analytical methods for Golden Plover are detailed in the BBS report.
  • The report also highlights the different trends of many woodland species in different countries of the UK. Many are in decline in England (e.g. Bullfinch have declined by 33% in England) but are increasing by 46% or more in Scotland (1995–2023). Other species such as Tree Pipit and Willow Warbler are in a similar position.
  • 22 species have statistically significant long-term increases and 14 species have significant long-term declines. The greatest long-term increases are for Chiffchaff (1,219%), Blackcap (714%) and Jay (472%). The greatest long-term declines are Greenfinch (-70%), Whinchat (-64%), and Swift (-63%).
  • Of note is a 67% increase in Scottish Cuckoo populations since 1994, countering the significant declines seen across much of the Cuckoo’s range in the UK. Conversely, the Curlew is in severe decline with a 15% decline in the last ten years, and a 60% decline since the survey began in 1994.
  • 17 species have statistically significant long-term increases and 15 species have significant long-term declines. The greatest long-term increases are for Canada Goose (675%), Red Kite (545%) and Stonechat (391%). The greatest long-term declines are Greenfinch (-76%), Curlew (-76%), Swift (-76%) and Yellowhammer (-75%).
  • Notably, Great Spotted Woodpecker populations have increased by 20% in the past decade, contributing to a long-term increase of 240% since BBS began. Similarly, Welsh House Sparrow populations, generally in decline across the UK, have almost doubled in the last 30 years. Curlew populations, declining across the UK, are hardest hit in Wales, with a 76% decrease.
  • 16 species have statistically significant long-term increases, and 1 species has a significant long-term decline. Note that these figures are likely to omit some species in decline in Northern Ireland but currently with insufficient BBS sample sizes in the country to be robustly monitored.
  • The greatest long-term increases are for Blackcap (2,021%), Buzzard (1,082%) and Goldfinch (533%). The statistically significant long-term decline is for Greenfinch (-82%).
  • Of particular interest are increases in populations of Blackbirds (40%), Song Thrush (68%) and Skylark (42%) over the last ten years. This is contrasted by other regions, with Blackbird populations falling by 10% in England over the same period.

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Interpretation notes

Drivers of change

  • Many of the historical declines in bird populations have been caused by land management changes resulting in habitat loss, a lack of suitable nesting habitat, and reduced food sources (particularly during the breeding period in spring, and over winter).
  • Agri-environment options – particularly those that enhance food resources over winter – may have important positive effects on some farmland species. However, farmland bird declines are still widespread and attributable to historic changes in farming practices over the 20th century, as described in the most recent update to the UK farmland bird indicator.
  • Colonisation into already available habitat is also a key reason for large increases in some species, such as Red Kite, which is recolonising after historic persecution, and the non-native Ring-necked Parakeet.
  • Disease continues to play a role in the declines of some species (e.g. Greenfinch and Chaffinch, through Trichomonosis), and potentially others (e.g. Blackbird and Usutu virus). BBS, along with other monitoring schemes, will also be important for understanding impacts of High Pathogenicity Avian Influenza (HPAI).
  • The results also highlight diverging trends of some bird species in northern versus southern Britain, with population trends of six species of woodland and scrub increasing in Scotland but declining in England. The effects of climate change have already been implicated for one of these (Willow Warbler), and understanding changes for other species will be an important challenge.

Population changes to UK species are not solely due to conditions on the breeding grounds. The 2024 BBS report highlights recent research on two long-distance migrants – Cuckoo and Nightingale – which demonstrates the importance of non-breeding locations and migration routes in influencing population change.

Confidence in results and caveats

  • The survey and analytical approaches follow standardised peer-reviewed methods to ensure results are comparable between survey sites and over time. All data undergo a combination of automated and manual validation and verification. See Massimino et al. (2025) for full details.
  • Some species that are in decline are too rare to be robustly monitored by the BBS.
  • Work has been carried out to assess the reliability of BBS trends, to ensure that reported trends are based on reliable data and sufficient sample sizes. This work has resulted in the following exclusions and caveats:
    • We do not report population trends for six species of gull (Black-headed, Mediterranean, Common, Great Black-backed, Herring and Lesser Black-backed), as a large proportion of the records are of non-breeding, wintering or migratory individuals
    • Trends for rare breeding species with substantial wintering populations (e.g. Fieldfare) are excluded
    • Trends for Common Tern, Cormorant, Grey Heron and Little Egret are reported with the caveat that counts may contain a high proportion of birds away from breeding sites
    • Trends for Barn Owl and Tawny Owl are reported with the caveat that the BBS monitors nocturnal species poorly
    • Counts for six wader species (Oystercatcher, Lapwing, Golden Plover, Curlew, Snipe and Redshank) are corrected to exclude counts from non-breeding flocks. Spatial filters (based on Bird Atlas distributions) are also applied to observations of Golden Plover to exclude birds outside of suitable breeding areas.
  • Data collection was much reduced during 2001 due to the foot-and-mouth disease outbreak and during 2020 due to Covid restrictions on fieldwork (Gillings et al. 2022), and the data collected had spatial and temporal biases. To avoid biasing subsequent results, 2001 and 2020 data are not used in the analyses. For more details, please see BBS report for 2020 (pp. 10–11).

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Methods

  • 2,779 volunteers took part in the Breeding Bird Survey in 2024, covering 3,967 1-km square sites across the UK.
  • Each 1-km square is visited twice by a volunteer between April and June, and all birds encountered while walking two 1-km line transects are recorded.
  • For the UK, a population trend is produced for species recorded on at least 40 survey squares on average over the trend period. For countries of the UK, trends are produced when the species is recorded on at least 30 squares on average over the trend period. Species that no longer fulfil these criteria, but that have done previously, continue to be published.
  • Population changes are estimated using a log-linear model with Poisson error terms. Counts are modelled as a function of year and site effects, weighted to account for differences in sampling densities across the UK, with standard errors estimated by bootstrapping.
  • The trend is statistically significant where the 95% confidence limits of the change do not overlap with zero.
  • The long-term trends cover the lifetime of BBS (1994 to 2024). 10-year, 5-year, and 1-year trends cover the most recent periods. Trends have been smoothed, and the end years truncated because at the two ends of the series the smoothed population index is very sensitive to fluctuations of the unsmoothed index. As such, although data from 1994 and 2024 are used to create the smoothed index values, the long-term trend period is presented from 1995 to 2023.
  • Methods are described in full in Massimino et al. (2025) and supporting references. Also see the BBS Report p.16 for an overview.

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Involvement and contacts

  • The statistic was produced by the Breeding Bird Survey partnership, with BTO having primary responsibility.
  • Quality assurance was undertaken by BTO, RSPB, and JNCC and by ornithologists in each of the Country Nature Conservation Bodies.
  • The data are published as a JNCC Official Statistic. If you have any queries, please contact us.

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Relation to other National and Official Statistics

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References

Gillings, S., Balmer, D.E., Harris, S.J., Massimino, D., Pearce-Higgins, J.W. 2022. Impacts of COVID-19 restrictions on capacity to monitor bird populations: a case study using the UK Breeding Bird Survey. Bird Study, 68, 220-232. DOI: https://doi.org/10.1080/00063657.2021.2019187

Harris, S.J., Massimino, D., Balmer, D.E., Eaton, M.A., Noble, D.G., Pearce-Higgins, J.W., Woodcock, P. & Gillings, S. (2021). The Breeding Bird Survey 2020. BTO Research Report 736. British Trust for Ornithology, Thetford.

Massimino, D. et al. (2025) ‘The Breeding Bird Survey of the United Kingdom’, Global Ecology and Biogeography, 34(1), p. e13943. Available at: https://doi.org/10.1111/geb.13943.

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