speciesaccounts_svalbardbarnaclegooseSvalbard Barnacle Goose

Branta leucopsis

The Svalbard population of Barnacle Goose breeds on the Svalbard archipelago, mainly in Spitsbergen, and winters predominately at the Solway Firth, which is on the border of Dumfries & Galloway, Scotland and Cumbria, England.

The wintering range of this population is small and the birds tend to remain within 5 km of their roost sites on the mudflats of the Solway coast, ranging along the firth to sites no more than 50 km apart.

  • Conservation Status

    Global status (IUCN Red List of Threatened Species) Least Concern
    African-Eurasian Waterbird Agreement (AEWA) A3a
    European status (European Red List of Birds) Least Concern (Europe and EU27)
    The Birds Directive (European Commission) Annex I
    UK status (Birds of Conservation Concern) Amber
    UK quarry species (Wildlife & Countryside Act 1981) not huntable, but licensed control occurs in Scotland

    Population Status

    Flyway population size (CSR 8; Wetlands International 2021) 40,000 individuals
    UK estimate (APEP 4) 43,500 individuals
    GB estimate (Frost et al. 2019) 43,000 individuals
    Irish estimate (Burke et al. 2018) 21 individuals
    UK trend (Frost et al. 2021) 25-year trend (1993/94-2018/19) = 164% increase
    10-year trend (2008/09-2018/19) = 32% increase

    Summary statistics

    Table 1. Annual estimates of the population size, percentage of young (%) and mean brood size (young per successful pair) for the Svalbard Barnacle Goose recorded at the Solway Firth, 2003/04-2020/21.

    Season Estimate of population size Percentage of young (%) Mean brood size
    2020/21 39,700 13.1 2.20
    2019/20 36,000 5.2 1.6
    2018/19 40,400 6.3 1.74
    2017/18 42,600 4.8 1.8
    2016/17 41,700 16.0 1.9
    2015/16 41,000 7.8 1.9
    2014/15 37,300 5.0 1.68
    2013/14 38,100 7.0 1.98
    2012/13 31,000 5.5 1.6
    2011/12 33,900 13.9 2.1
    2010/11 35,900 10.8 2.5
    2009/10 32,800 5.1 1.8
    2008/09 29,900 8.7 2.0
    2007/08 29,000 12.8 2.4
    2006/07 25,000 14.6 2.2
    2005/06 23,900 7.9 2.5
    2004/05 26,900 2.1 1.5
    2003/04 27,000 4.0 2.0
    Reference

    Frost, T., G.E. Austin, R.D. Hearn, S. McAvoy, A. Robinson, D.A. Stroud, I. Woodward & S.R. Wotton. 2019. Population estimates of wintering waterbirds in Great Britain. British Birds 112: 130-145.

    Frost, T.M., N.A. Calbrade, G.A. Birtles, C. Hall, A.E. Robinson, S.R. Wotton, D.E. Balmer & G.E. Austin. 2021. Waterbirds in the UK 2019/20: The Wetland Bird Survey. BTO, RSPB and JNCC, in association with WWT. British Trust for Ornithology, Thetford.

    Wetlands International. 2021. Waterbird population estimates. Retrieved from http://wpe.wetlands.org/ September 2021.

    Data access

    Svalbard Barnacle Goose data for the Solway Firth presented in Table 1 (Estimate of population size/Percentage of young/Mean brood size) are licensed under the Open Government Licence 3.0 except where otherwise stated.

    When you use information from this report under the Open Government Licence you must include the following attribution:

    Contains Goose & Swan Monitoring Programme (GSMP) data from “WWT. 2021. Goose & Swan Monitoring Programme: survey results for Svalbard Barnacle Goose Branta lecopsis. WWT/JNCC/NatureScot, Slimbridge” retrieved from https://monitoring.wwt.org.uk/our-work/goose-swan-monitoring-programme/species-accounts/bewicks-swan/ © copyright and database right 2021. The GSMP is organised by the Wildfowl & Wetlands Trust (WWT) in partnership with the Joint Nature Conservation Committee (JNCC) and NatureScot with fieldwork conducted by volunteers.

  • The Svalbard population of Barnacle Goose breeds in the Svalbard archipelago, mostly in western Spitsbergen, the largest of the islands. Migration begins in late August and early September, and many stage on Bear Island, Norway, for up to three weeks before continuing their migration southwards. Some, however, are known to migrate direct to the wintering grounds of the Solway Firth, on the border between Scotland and England. Return passage begins in mid- April, and during this migration most birds stop over at Helgeland and Vesterålen, off the west coast of mainland Norway, for two to three weeks, before reaching Svalbard by the end of May (Griffin 2008).

    flyway map barnacle_svalbard

    Flyway of the Svalbard Barnacle Goose

    The wintering range of this population is small and the birds tend to remain within 5 km of their roost sites on the mudflats of the Solway coast, ranging along the firth to sites no more than 50 km apart. Winter habitat use is confined to saltmarsh and improved pastures on the Solway. Feeding occurs preferentially on Trifolium repens in autumn on saltmarsh habitats, supplemented by grasses and herbs, and on Lolium perenne on pasture. In autumn, the geese may also forage in stubble fields for spilt grain. Four principal areas on the Solway are used, namely farmland around Caerlaverock and Southerness on the Scottish side of the Solway and Rockcliffe Marsh and Newton Marsh on the English side (Owen & Black 1999, Griffin & Mackley 2004). However, other areas are, to an increasing extent, also being used including areas along the River Nith towards Dumfies, and areas further west around Colvend, Auchencairn, Rascarrel and Wigtown later in the winter. Also to a lesser extent, sites further east around Redkirk and Gretna are also being utilised.

    With increasing numbers of birds in the population, conflicts have arisen as a result of damage to agricultural crops by grazing geese. Consequently, in 1993, Scottish Natural Heritage established a goose management scheme to help alleviate such problems.

    References

    Griffin, L.R. 2008. Identifying the pre-breeding areas of the Svalbard Barnacle Goose Branta leucopsis between mainland Norway and Svalbard: an application of GPS satellite-tracking techniques. Vogelwelt 128: 226-232.

    Griffin, L.R. & E.R. Mackley. 2004. WWT Svalbard Barnacle Goose Project Report 2003-2004. WWT Report, Slimbridge.

    Owen, M. & J.M. Black. 1999. Barnacle Goose Branta leucopsis: Svalbard. In: Madsen, J., G. Cracknell & A.D. Fox (eds.). 1999. Goose populations of the Western Palearctic. A review of status and distribution. Wetlands International Publication no. 48, Wetlands International, Wageningen, The Netherlands/National Environmental Research Institute, Ronde, Denmark.

  • Annual counts and age assessments

    Coordinated counts of Svalbard Barnacle Geese are undertaken at least once a month from September through to May, with weekly counts carried out during the arrival and departure periods.  Age assessments are also made, during which counters record the proportion of first winter geese present within flocks as well as brood sizes (i.e. the size of family groups) to determine the breeding success of the population. Surveys of Svalbard Barnacle Geese are organised by WWT as part of a long-term research programme on this population.

    Results from these surveys can be found on the ‘Latest results’ page.

    Find out more about age assessments

  • Results for 2020/21 [added September 2021]

    Abundance

    The adopted total for the Svalbard Barnacle Goose population wintering on the Solway Firth (where the majority of this population winters) in 2020/21 was 39,700 geese (the mean of the maximum count of 42,303 and two other counts within 10% of this, rounded up to the nearest 100). This represents an increase of 3,700 birds (10.3%) on last winter’s adopted total of 36,000 geese, almost balancing the loss of 4,000 birds seen that winter (Figure 1).

    Figure 1. Annual census-derived estimates (for the Solway Firth only) of the Svalbard Barnacle Goose population size, 1958/59–2020/21.

    The first arrival of Barnacle Geese thought to be genuine migrants from Svalbard was a flock of 28 birds recorded at WWT Caerlaverock on 16 September 2020, a date that is joint earliest on record, with 140 by 20 September (albeit including a Snow x Barnacle Goose hybrid which could indicate a feral Loch Leven origin for a percentage of these birds) and 2,000 by 27 September. Then there was a gradual build up in numbers to 6,590 on 8 October, with 5,000 being typical for the reserve area from then until 9,086 recorded on 20 October. For the first time in the last 15 years, no peak count above 10,000 was recorded for the reserve area and total counts remained noticeably low, with 4,362 on 27 April and 40 on 2 May 2021 being the final birds recorded during the spring departure period.

    The census count on 7 October 2020 recorded 29,900 geese on the Solway and another 800 at Budle Bay, Northumberland, suggesting an early rapid mass exit from Svalbard. By 14 October numbers were already close to the maximum recorded for the winter at 38,100 on the Solway and 2,250 at Budle Bay and by 28 October 2020, the maximum count for the season across the two main sites of the Solway (42,303) and Budle Bay (1,400) was recorded, with six leucistic Barnacle Geese also being noted (the maximum number of leucistic geese recorded in winter 2020/21).

    Covid-19 restrictions and advice did not affect as many counts in winter 2020/21 as it did in the latter months of winter 2019/20 (see WWT 2020) with only the December count and February count being affected to a small degree by some counters abstaining. The November count was cancelled due to poor weather and from December onwards one count section at Boreland of Colvend, rarely used by the geese except in harsh winter conditions, was avoided out of respect for the landowner’s wishes.

    Significant numbers of birds again staged/wintered on the east coast at Budle Bay, Northumberland with an estimated 2,250 there on 14 October 2020 dropping to a more sustained 1,400 to 2,200 for the rest of the winter until at least the last week of February 2021. By the count of 24 March 2021, and on subsequent counts in April and May, no Barnacle Geese were recorded. This pattern of reduced numbers by March is similar to what has been recorded in previous years though it is still not clear if all of these birds are at that time moving southwest to the Solway or to other locations in the UK or elsewhere. An effort to ring or tag a cohort of birds at Budle Bay in late winter would help elucidate what happens to these birds and the extent to which they are short-stopping Svalbard birds.

    It is known from past years that ringed birds from small feral flocks at Loch Leven (Perth & Kinross) and the Highland Wildlife Park (HWP, Kincraig, Inverness-shire) can be present throughout the winter on the Solway and that birds over-summering in Cumbria can also be present. Further to this evidence of UK feral/naturalised birds wintering on the Solway Firth, in December 2020 a cohort of 11 geese were tagged with Global Positioning System (GPS) collars on the WWT Caerlaverock reserve, being part of a flock of 450 birds in the field at the time of the catch. These tagged birds stayed close together on the reserve fields and those of neighbouring farms throughout mid-winter and migrated north together to Loch Leven in the last week of February, breeding on St Serf’s Island in April/May 2021. The tagged birds were observed at various points during the winter on the fields of the reserve and tended to be in a flock of 4-500 birds. No blue leg-ringed birds from HWP were seen alongside the tagged birds in such flocks so it could be that there are now over 500 feral/naturalised birds wintering on the Solway and perhaps as many as 1,000 if breeding populations in the Lake District and elsewhere also winter wholly or in part on the Solway.

    Due to count variation, with possible inaccuracies and the chance of double-counting, an adopted count total for the Solway population is derived by averaging those counts within 10% of the maximum recorded during the winter. In 2020/21, eight full census counts were completed from October–April (May counts are affected by spring migration and not included in the adopted count estimation process) and the counts of 38,090 on 14 October 2020, 42,303 on 28 October 2020 and 38,535 on 28 April 2021 fulfilled this criterion (albeit the late April count could have been affected by some earlier departing geese) and were thus averaged to produce an adopted Solway population total of 39,700 Svalbard Barnacle Geese (rounded up to the nearest 100; c.f. 36,000 in 2019/20). Therefore, in terms of either the peak count or adopted count there has been an increase in the population total on the Solway in 2020/21. This increase on the Solway does not take account of birds at Budle Bay and does not account for the UK resident birds referred to above known to be wintering on the Solway.

    Breeding success

    The breeding success of Svalbard Barnacle Geese sampled on the Solway Firth from October 2020 to December 2020 ranged from 2.7% to 28.7% (c.f. 0.7% to 14.6% in 2019/20) with a mean of 13.1% young derived from 19 flocks and 14,296 geese sampled (c.f. 5.2%; n = 14 flocks; 10,111 geese sampled in 2019/20) (Figure 2). Across the same area, the total number of broods sampled was 250, with a mean family size of 2.2 young, ranging from 1–5 young (c.f. 1.6 young; n = 121 broods; range 1–4 young in 2019/20).

    Figure 2. The mean percentage of young (blue columns) and mean brood size (red circles) of Svalbard Barnacle Geese, 1958/59–2020/21.

    Discussion

    The adopted count of 39,700 represents a recovery of the total population size wintering on the Solway, the gain in numbers being similar to the loss reported in winter 2019/20. This increase is likely to be a response to the above average breeding season, the percentage young being the second highest in the last decade and well above the current ten-year mean of 8.3%. Thus the previous stable population trajectory over the longer term remains.

    It is becoming increasingly apparent from marking and tracking work that a considerable percentage of the birds wintering on the Solway, perhaps around 2.5% or more, are naturalised/feral birds mostly resident and breeding within the UK, with c. 3,000 recorded as UK naturalised by the Wetland Bird Survey (WeBS) up to 2019/20 (Frost et al. 2021). It has already been established that many of those from two breeding sites at HWP and Loch Leven, the only sites with substantial marking/tracking programs, do winter on the Solway. Therefore it could be the case that many of these naturalised/feral birds at sites in the north of England and Scotland may well be using the Solway in winter and thus mixing with, and remaining indistinguishable from, the Svalbard flyway birds and thus contributing to the population counts recorded and the percentage juvenile and brood size estimates.

    As the naturalised population has mainly had an exponentially positive growth rate over the last five years up to 2019/20, while the Solway population trajectory has been mainly stable, these naturalised birds will presumably be making an increasing contribution to the population metrics that the Goose & Swan Monitoring Programme (GSMP) monitors. This means that any future population counts or assessments of juvenile productivity should more fully try and take account of this element within the Svalbard flyway population especially if using such monitoring data for modelling for any adaptive management plans. Efforts to ring or tag birds across other feral populations of the UK would help elucidate the true number of UK “resident” birds (albeit some HWP birds have turned up in Iceland and in Norway) wintering on the Solway.

    Another issue of relevance to the understanding of the true numbers of birds wintering on the Solway that are of Svalbard origin is the degree to which feral/naturalised birds move away from the Solway and the timing of such movements in relation to any counter movements from short-stopping sites such as Budle Bay, Northumberland. GPS tracking of a group of Loch Leven breeding Barnacle Geese revealed that they departed the Solway in late February at a time when possibly the Solway numbers were being topped up by up to 2,000 birds from the Budle Bay area, many of which seem likely to be genuine Svalbard birds based on ring sightings. However we have very limited knowledge of these site switches by relatively large groups of birds and how that affects the stability of the population counts that the GSMP is able to achieve and so again marking/tracking of a proportion of the birds at Budle Bay would be recommended.

    The peak count for the flyway population across the Solway and Budle Bay sites on 28 October 2020 was 43,700 (albeit this will include an unknown number of naturalised UK birds). Any backward calculation of historical flyway totals would have to take account of WeBS counts for Budle Bay, and possibly other east coast sites, to be comparable with the population total given here, and might need to consider the timing of movements and size of UK naturalised populations too.

    Acknowledgements

    Many thanks to the Solway census team and to the counter at Budle Bay for sending us their observations.

    References

    Frost, T.M., N.A. Calbrade, G.A. Birtles, C. Hall, A.E. Robinson, S.R. Wotton, D.E. Balmer & G.E. Austin. 2021. Waterbirds in the UK 2019/20: The Wetland Bird Survey. BTO/RSPB/JNCC, Thetford.

    WWT. 2020. Goose & Swan Monitoring Programme: survey results 2019/20 Svalbard Barnacle Goose Branta leucopsis. WWT/JNCC/NatureScot, Slimbridge.

  • Previous annual results will be archived here.

    2019/20 Results

    2018/19 Results

    2017/18 Results

    2016/17 Results

    2015/16 Results

    2014/15 Results

    2013/14 Results

    2012/13 Results

    2011/12 Results

    2010/11 Results

    2009/10 Results

    2008/09 Results

    2007/08 Results

    2006/07 Results

    2005/06 Results

  • Relevant publications

    Svalbard Barnacle Goose distribution around the Solway Firth: Flock counts from the Solway Goose Management Scheme area – reports can be found on the Reports and newsletter page

    Other relevant material

    BirdLife International Species factsheet

    British Trust for Ornithology: BirdFacts

    Review of Goose Management Policy in Scotland 2010

    Norwegian Polar Institute species information for Svalbard

    SNH Solway Barnacle Goose Management Scheme