This code applies only in England, Wales, Scotland and Northern Ireland.
To ensure the long-term future of shooting, it is essential that the shooting of wildfowl is sustainable.
Within this context, sustainable shooting respects quarry species and seeks to conserve and improve the environment. It avoids excessive consumption, complies with the law, improves the health and well-being of participants, and provides food and economic benefits to the wider community.
This code relates to the quarry species listed below, particularly those where the available evidence demonstrates the need for action.
Gadwall
Goldeneye**
Mallard*
Scaup**1
Pintail**
Pochard**
Shoveler
Teal
Tufted duck
Wigeon
Canada goose
Greylag goose
Pink-footed goose
European white-fronted goose**2
Common snipe**
Golden plover
Jack Snipe1
Woodcock**
Coot**3
Moorhen**3
The ‘broad sustainability principles’ apply to all species, with the following variations.
a) * This code does not apply to reared and released mallard, and the shooting thereof.
b) ** Bespoke actions are required for these species; see species-specific recommendations.
c) 1 Northern Ireland only.
d) 2 England & Wales only.
e) 3 England, Wales, & Scotland only.
f) This code does not apply to the use of large bore historic firearms used to maintain historic, cultural and traditional aspects of wildfowling.
g) This code does not override any site-based requirements; all shooters need to abide by landowner, club, or consent restrictions.
It is important that those who shoot recognise that unsustainable shooting can affect population size, age composition, sex ratio, behaviour, and distribution of natural populations. Understanding the potential impacts of shooting is a prerequisite to managing quarry species in a sustainable manner.
i) Broad sustainability principles that can be applied to the shooting of all quarry species listed within this code and should be followed by all participants.
ii) Individual quarry species recommendations regarding the taking of species where the evidence review highlights potential conservation impacts. The ‘shooting restrictions’ recommendations must be followed but will vary subject to available data and will be updated periodically.
iii) Practical recommendations whereby shooters can contribute to the conservation of individual quarry species through behaviour changes, data collection and facilitating practical conservation.
a. Eat what you shoot. It is your responsibility to ensure all shot quarry is put to good use.
b. You must comply with any club or site-specific rules
or regulations, sector-specific codes and best practice guidance.
c. No more than six grey geese – to a maximum of five pinkfeet, four greylag, and two European white-fronts per person, per day – unless for conservation, health and safety, or crop protection measures (and supported by a licence agreement or management plan). At all times show restraint. Take what you need, not what you can.
a. Eat what you shoot. It is your responsibility to ensure all shot quarry is put to good use.
b. You must comply with any club or site-specific rules or regulations, sector-specific codes and best practice guidance.
c. No more than ten ducks per person, per day. At all times show restraint, Take what you need, not what you can.
Data will provide a more accurate assessment of local and national distribution and abundance. This will ultimately help ensure decisions are made on the best available science and evidence. Shooters can help by contributing towards the following initiatives:
a. Bird counts – these enable better understanding of species distribution and population sizes.
b. Bag data submission – this provides a better understanding of harvest and strengthens species population estimates.
c. Marking of birds – ring recovery and reporting enables better understanding of species movement and
survival rates.
d. Disease reporting – enables better understanding of threats to species and potential drivers of population trends.
Sustainable shooting is supported by practical conservation action that targets the habitats of quarry and non-quarry species alike. Shooters should, where possible, create management plans to highlight and capture conservation work and their approach to managing harvest. Below are several areas where shooters can take action to support species recovery or maintain species presence during the breeding and/or overwintering season:
a. Undertake targeted habitat creation, restoration and maintenance work.
b. Pest and predator control.
c. Nesting support (for example: fencing, duck nest tubes, provision of maintained islands).Â
d. Refuge provision, either for set periods of time (temporal), or over dedicated areas of land (spatial), dependent on site requirements.
It is important that shooting does not cause disturbance that impacts on waterbirds to an extent that there is a:Â
a. change in local distribution on a continuing basis; and/or
b. change in local abundance on a sustained basis; and/or
c. reduced ability of any significant group of birds to survive, breed, or rear their young.
Disturbance during periods of prolonged cold weather can have significant impacts; shooters must comply with the Joint Nature Conservation Committee (JNCC) and BASC ‘severe weather’ protocols.
The actions required for each species have been detailed below.Â
Aythya ferina
Recommendation: no take – targeted conservation effort required.
The UK hosts a very small number of breeding pochard; however, many over-winter in the UK.
The pochard population shows a ten-year wintering population decline in the UK of greater than 25 per cent between 2008-2018. This decline has been seen on a UK, European and global level and is predicted to continue; as such, the species has been listed as ‘vulnerable’ on the European International Union for Conservation of Nature (IUCN) Red List.
Action to prevent further continued population declines is required across the flyway (north-east to north-west Europe).
Within the UK, it is vital that we better understand the species distribution, abundance, and historic harvest of pochard in order to encourage the small breeding population to thrive. As a result, BASC has provided the following recommendations:
Research required
• Breeding and wintering surveys to better understand
local and national distribution and abundance.
• Historic bag returns and the submission of current bag data to better inform harvest estimates (data can be submitted to the Game & Wildlife Conservation Trust (GWCT) National Gamebag Census or BASC Green Shoots Bagged It).
Shooting restrictions
Voluntary moratorium, i.e. shooters should voluntarily refrain from shooting common pochard.
Habitat management
• Maintenance or restoration of freshwater floodplains to provide optimum feeding and roosting environments comprising of deep water (up to 2.5m).
• Maintenance or creation of abundant aquatic plant areas which provide roots, shoots, and seeds for food.
• Targeted predator control in areas where known breeding populations exist.
Anas acuta
Recommendation: take a maximum of two birds per day – targeted conservation effort required.
The northern pintail population shows a ten-year wintering population decline in the UK of greater than 25 per cent between 2008-2018.
This decline is reflected on the European continent within breeding populations in European Russia, Finland and Sweden, and is anticipated to continue. However, due to their large range and relatively high abundance, pintail are not yet considered ‘vulnerable’ to extinction at a global level but are listed as ‘vulnerable’ on the European IUCN Red List.
Population trends appear to be driven by pressures at breeding grounds and poor breeding success, as opposed to over-harvesting of adult birds.
Due to already low bag numbers in the UK and the limited impact of wintering adult mortality on population demographics, a full moratorium on the species will have limited effect. A moratorium could have a negative impact
by disincentivising conservation effort, so continued but controlled harvest is recommended.
The UK supports a very small number of breeding individuals; therefore, conservation focus should be on breeding populations abroad and over-wintering pintail populations in the UK. Pintail pair up during the winter and undertake the return migration as a pair, known as a ‘winter pair bond’.
Improved understanding of optimal wintering habitat requirements within and outside wetland reserves in the UK, particularly on neighbouring agricultural land, is vital. Based on the species trends and information, BASC has provided the following recommendations.Â
• International flyway-level collaboration with
relevant stakeholders.
• Wintering surveys to better understand local and national distribution and abundance.
• Submission of bag data to better inform harvest estimates (data can be submitted to the GWCT National Gamebag Census or BASC Green Shoots Bagged It).
• Shooters should support the BASC wing survey to enable better understanding of adult:juvenile and male:female harvest ratios.
• Two pintail per person, per day, bag limit recommended.
• Should target males where possible.
• No sale of shot pintail.
• Pintail prefer habitats with low vegetation and shallow water; they will also frequent large inland lakes, ponds, marshes, and coastal lagoons.
• In order to provide an abundant supply of high-energy and nutritional foods for pintail, wetland water depths should be less than 45cm but preferably less than 15cm for an abundant food source.
• Weed management can improve habitat for pintail when benefiting native plant species.
Bucephala clangula
Recommendation: delay shooting until October where resident breeding goldeneye are present.
Goldeneye show a ten-year wintering population decline in the UK of greater than 25 per cent.
Declines in the UK appear to be driven primarily by climate change and are a result of a redistribution of the species across the European flyway to more north-eastern edges of their range.
At a global level the population appears stable and therefore of ‘least concern’.
Enhancement of breeding habitat in the UK will have only a limited impact, as goldeneye are rare breeders.
Taking these trends into consideration, BASC has provided the following recommendations:
• Breeding and wintering surveys to better understand local and national distribution and abundance.
• Submission of bag data to better inform harvest estimates (data can be submitted to GWCT National Gamebag Census or BASC Green Shoots Bagged It).
• Shooters should support the BASC wing survey to enable better understanding of adult:juvenile and male:female harvest ratios.
• Increased ringing, ring resighting and ring recovery reporting required.
• Should delay shooting until October where resident breeding goldeneye are present.
• how restraint, even when resident birds are absent. Shoot what you need, not what you can.
• The installation of nest boxes has been shown to support goldeneye nesting and increase brood numbers where natural tree cavities are limited.
• Pest and predator control.
Aythya marila
Northern Ireland only
Recommendation: show restraint, targeted research and conservation effort required.
The UK does not host a breeding population of scaup, with only one or two pairs recorded each year; however, many overwinter in the UK.
The scaup population shows a ten-year wintering population decline in the UK of greater than 25 per cent between 2008-2018. This decline has been seen on a UK level but not replicated at a European or global level, where it is listed as of ‘least concern’.
The decline in the UK overwintering population correlates with changes in climate, food supply and other pressures. The eastern European population now winters closer to their breeding grounds, a phenomenon known as short-stopping.
With sufficient protected areas and effective habitat management, shooting restrictions are not necessary. However, it is vital that monitoring of abundance, productivity and bag data is enhanced to maximise the conservation benefits of future actions.
Based on the species trends and information available, BASC has provided the following recommendations:
• Wintering surveys to better understand local and national distribution and abundance.
• Submission of bag data is required to better inform harvest estimates (data can be submitted to GWCT National Gamebag Census or BASC Green Shoots Bagged It).
• Shooters should support the BASC wing survey to enable better understanding of adult:juvenile and male:female harvest ratios.
• Increased ringing, ring resighting, and ring recovery reporting required.
• Should show restraint.
• Site-based considerations required.
• Maintenance or restoration of large water habitats, either coastal or freshwater, to provide optimum feeding and roosting environments comprising of deep water (1m to 5m).
• Minimise impacts on the sea bed/lake bed to ensure availability of suitable foraging.
Anser albifrons
England and Wales only
Recommendation: take a maximum of two birds, per person, per day – targeted research required.
The European white-fronted goose population shows a moderate decline in the UK in the medium term and a significant decline of greater than 50 per cent in the long term.
However, this decline is not reflected on the European continent where the large population remains stable or increasing. This is reflected in the European IUCN listing of
‘least concern’.
The positive flyway status of the European sub-species of white-fronted goose is not shared with the Greenland white-fronted goose, which is now fully protected and cannot be harvested in the UK.
Greenland white-fronts come into Scotland, Northern Ireland, Northwest England and North Wales, while the European white-fronts tend to remain in England and are restricted to the East, South and Southwest. Due to this localised distribution, there is minimal potential for range overlap and the risk of lookalike shooting of the Greenland white-fronted goose is small.
With already-low bag numbers in the UK, and scientific evidence of the species short stopping because of climatic changes, a cessation of shooting will have limited benefit. Continued low harvest of this species and collection of bag data, ring recovery information and wing survey details will contribute to our wider understanding of the species demographics and movement.
Taking the above trend information, combined with the available science and evidence into consideration, BASC has provided the following recommendations:Â
• Wintering surveys to better understand local and national distribution and abundance.
• Submission of bag data is required to better inform harvest estimates (data can be submitted to GWCT National Gamebag Census or BASC Green Shoots Bagged It).
• Shooters should support the BASC wing survey to enable better understanding of adult:juvenile harvest ratios.
• Increased ringing, ring resighting and ring recovery reporting required.
• Two European white-fronts per person, per day, bag limit recommended.
• It is the responsibility of all who shoot to correctly identify your quarry. If in doubt, don’t shoot.
• Collaboration with agricultural managers in key feeding areas to ensure there is adequate feeding ground available.
Scolopax rusticola
Recommendation: delay shooting until late November where resident woodcock are present.
The UK hosts a breeding population of woodcock which remains resident all year round, as well as hosting a large migrant over-wintering population. The breeding population has shown substantial declines in its range and size over the last 20 plus years. The migrant wintering population has, in contrast, increased over the last 25 years; this is reflected in the European IUCN listing of ‘least concern’.
Changes in climate, predation and habitat availability in the UK are likely driving the decline in the resident UK population and a number of conservation recommendations have been made by the GWCT to reduce negative impacts on the declining UK breeding population. Taking these into consideration, BASC has provided the following recommendations.
• Breeding and wintering surveys to better understand local and national distribution and abundance.
• Submission of bag data to better inform harvest estimates (data can be submitted to the GWCT National Gamebag Census or BASC Green Shoots Bagged It).
• Hunters should support the BASC wing survey to enable better understanding of adult:juvenile and male:female harvest ratios.
• Should avoid shooting woodcock in areas where resident woodcock are present until the major fall of migrant woodcock in late November.
• Show restraint, even when resident birds are absent. Shoot what you need, not what you can.
• Shoot flightlines with caution.
• Curb shooting in severe weather.
• Targeted habitat creation and management for both breeding and wintering populations is required.
 o Create or widen woodland rides to provide breaks in the tree canopy. Ideally, rides should be at least 8m wide.
 o Mow rides and clearings to produce accessible grassy feeding and breeding display sites.
 o Create and reinstate clearings and young woodland using a little-but-often policy. Over time this creates a mosaic of woodland types and ages.
 o Periodically remove marginal vegetation along sections of ditch or pond edges where these features occur within or close to woodlands.
 o Create wet features that retain ground moisture into late summer.
• Pest and predator control.
• Refuge provision, either for set periods of time (temporal) or over dedicated areas of land (spatial), dependent on site requirements.
Gallinago gallinago
Recommendation: delay shooting until September where resident breeding common snipe are present.Â
The UK hosts a breeding population of common snipe which remains resident all year round, as well as hosting a large migrant overwintering population. The breeding population has experienced a marginal decline, while the wintering population has shown a more moderate decline. However, due to the large range and relatively high abundance, snipe are not yet considered ‘vulnerable’.
Changes in snipe populations in the UK and Europe are primarily attributed to agricultural changes. Although there is no evidence that shooting is driving this decline, the current snipe shooting season opening date of 12 August (England, Wales, and Scotland) crosses over with the species breeding period.
Management for other game birds, such as predator control, has been beneficial for snipe, and recovery of ringed birds by shooters has contributed to knowledge surrounding migration and movement of snipe. Therefore, continued bag reporting and participation in ringing studies are important roles for the shooting community.
Taking the above information into consideration, BASC has provided the following recommendations:
• Focused studies on snipe as opposed to lowland waders, as snipe are often missed in traditional survey techniques.
• Submission of bag data is required to better inform harvest estimates (data can be submitted to GWCT National Gamebag Census or BASC Green Shoots Bagged It).
• Shooters should support the BASC wing survey to enable better understanding of adult:juvenile ratios.
• Increased ringing, ring resighting, and ring recovery reporting required.
• Research into habitat factors that may be influencing snipe declines, such as food abundance.
• Greater understanding of recruitment is required to help disentangle habitat-mediated pressures from productivity issues.
• Should avoid shooting common snipe in areas where resident breeding snipe are present until 1 September
• Show restraint, even when resident birds are absent. Shoot what you need, not what you can
• Curb shooting in severe weather.
• Habitat management for both breeding and wintering populations is required:
 o Raise water levels to create wetter habitats.
 o Reduce grazing pressure around breeding sites.
 o Scrape creation and rush management.
• Pest and predator control.
• Refuge provision; minimise disturbance either for set periods of time (temporal), or over dedicated areas of land (spatial) dependent on site requirements.
Fulica atra
Recommendation: research required.
The UK breeding population shows a substantial ten-year decline of 24-44 per cent between 2010-2020.
This is mirrored in a wintering population decline of 24 per cent; as a result they are listed as ‘near threatened’ on the European IUCN Red List.
Although widespread, coots, like moorhens, remain relatively under-studied, particularly in relation to their movement and population demographics. Ringing studies show that coots do migrate within the UK as well as between the UK and central Europe/Russia.
The species receives very little shooting pressure in the UK and its popularity as a quarry species is decreasing across the flyway. Therefore, shooting is unlikely to be driving declines. Coots likely suffer from multiple pressures driven by habitat and climate change, but their flexible behaviour and ability to adapt may have diluted any obvious impacts. Shooting restrictions are unlikely to have any benefit. Instead, research investment to better understand the causes of ongoing declines is necessary, alongside habitat management and conservation interventions.
• Breeding and wintering surveys to better understand local and national distribution and abundance.
• Submission of bag data to better inform harvest estimates (data can be submitted to the GWCT National Gamebag Census or BASC Green Shoots Bagged It).
• Shooters should support the BASC wing survey to enable better understanding of adult:juvenile harvest ratios.
• Increased ringing and ring resighting effort to improve understanding of migratory movement.
• Should show restraint.
• Site-based considerations required.
• General wetland creation and management will benefit both breeding and wintering populations.
• A mosaic habitat of dense cover, open water and clearings is required to provide safe refuge and feeding areas.
• Ensure suitable breeding sites have ramp-like areas to enable chicks to leave the water easily.
• Pest and predator control.
• Refuge provision, either for set periods of time (temporal) or over dedicated areas of land (spatial), dependent on site requirements.
• Nesting support (for example: fencing, duck nest tubes, provision of maintained islands).
Gallinula chloropus
Recommendation: research required.
The UK breeding population of moorhen shows a substantial decline in breeding territories of 23 per cent.
The wintering population, which includes migrants from much of Europe and North Africa, shows a ten-year decline of 26 per cent between 2008-2018. This is primarily driven by declines in England, as the Scottish and Welsh populations have shown slight increases over this period (four and five per cent respectively). The decline in Europe has not yet pushed the species into an ‘at risk’ category and the moorhen is currently listed as ‘of least concern’ on the European IUCN Red List.
The decline of moorhens, like that of coots, is not well understood but, given the low bag size of the species, it is highly unlikely that shooting is the cause. Habitat loss and predation are suggested to be drivers, possibly impacting breeding success more than adult survival.
Therefore, shooting restrictions are unlikely to have any benefit. Instead, research investment to better understand the causes of ongoing declines is necessary, alongside habitat management and conservation interventions.
• Breeding and wintering surveys to better understand local and national distribution and abundance.
• Submission of bag data to better inform harvest estimates (data can be submitted to the GWCT National Gamebag Census or BASC Green Shoots Bagged It).
• Shooting should support the BASC wing survey to enable better understanding of adult:juvenile harvest ratios.
• Increased ringing and ring resighting effort to improve understanding of migratory movement.
• Should show restraint.
• Site-based considerations required.
• General wetland creation and management will benefit both breeding and wintering populations.
• A mosaic habitat of dense cover, open water and clearings is required to provide safe refuge and feeding areas.
• Ensure suitable breeding sites have ramp-like areas to enable chicks to leave the water easily.
• Pest and predator control.
• Refuge provision, either for set periods of time (temporal) or over dedicated areas of land (spatial), dependent on site.
• Nesting support (for example: fencing, duck nest tubes, provision of maintained islands).
Financial support could be provided to fund research and practical conservation measures in the UK and abroad through an application for grant funding to the BASC Wildlife Fund.
It is advisable to have adequate liability (third-party) insurance when shooting. Membership of BASC includes insurance for recreational sporting activities. Find out more and join BASC here.
• The Code of Good Shooting Practice
• BASC Wildfowling Code of Practice
• BASC Flight Ponds Code of Practice
• BASC Code of Practice for sporting agents and guides offering inland goose shooting in Scotland
• BASC Shotgun Safety Code of Practice
For further advice, please contact BASC’s wildfowl and wetlands team here.
Biosecurity refers to all the measures taken to minimise the risk of infectious diseases caused by viruses, bacteria or other microorganisms entering, emerging, establishing or spreading as a result of our actions.
BASC-affiliated wildfowling clubs manage sporting rights on approximately 700km of foreshore owned by The Crown Estate in England, Wales and Northern Ireland.
Fossil fuels are a finite resource, it is therefore essential to find renewable alternatives, with wind farms just one possible option.
