Bassenthwaite lake by Stewart Smith.CT

Bassenthwaite National Nature Reserve

Bassenthwaite National Nature Reserve


Management Plan

Bassenthwaite Lake National Nature Reserve (NNR) Management Plan will guide how we intend to manage the NNR for the next five years with resources available. As landowner and land manager, the Lake District National Park Authority is required to maintain an up-to-date management plan for Bassenthwaite Nature Reserve to:

  • manage priority wildlife and habitats identified by Natural England, UK/EU law
  • address issues identified by landowners, lake users, permit users, stakeholders.
  • offer lakeside recreation at Peel Wyke, Beck Wythop, Woodend
  • focus on outcomes: how and where we can make a difference over five years

Bassenthwaite Management Plan (PDF) can be emailed to you on request.

Please send your request to cath.johnson@lakedistrict.gov.uk

Our vision and how we will achieve It

The Vision sets out how we would like the NNR to function in 50 years time and helps guide our decision making to improve and look after Bassenthwaite Lake.

Bassenthwaite Lake in 2074

  • Naturally, functioning lake system, supporting a wealth of wildlife and habitats.
  • Water quality improved, the lake will continue to support diverse assemblages of native and notable species of fish, plants, invertebrates, mammals and birds.
  • Supporting a resilient well-functioning natural, transition of habitats from open water to riparian vegetation and wet woodland along the majority of shoreline. Areas of unvegetated shore will be absent or restricted to localised areas. Away from lakeshore, fen meadows, flood plain fen and woodland will support a healthy undisturbed wealth of native flora and fauna.
  • Invasive, introduced species, particularly, New Zealand pygmy weed, Himalayan balsam, Japanese knotweed and mink, will be either absent, or present at very low controlled levels, such that they present no competitive or predatory threat to the native species present in and around the lake. No new invasive non-native species will have been introduced.
  • The lake will be managed as a place where responsible visiting is encouraged. People will come to enjoy quiet recreation and the wealth of wildlife present, both on the water and shore and a place.
  • Communities will be motivated and inspired to support the management of the lake through volunteer and educational opportunities and stimulate a strong sense of pride and ownership of the local environment and its distinctive character.

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About Bassenthwaite

Bassenthwaite Lake lies in the north-west of the Lake District National Park in the valley of the river Derwent some three kilometres north-west of Keswick.

Map: Bassenthwaite lake within the Lake District National Park

Bassenthwaite Lake within the lake district national park map

© Lake District National Park Authority 2024 Crown Copyright and database right 2024. Ordnance Survey AC0000807483. You are not permitted to copy, sub-licence, distribute or sell any of this data to third parties

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Land Ownership

nature reserve - bassenthwaiteImage: Bassenthwaite lakeshore (Pete Barron)

The lake bed and shorelines at Ouse Bridge, Woodend and Beck Wythop and the shore and meadow at Broadness Meadow are owned freehold by the Lake District National Park Authority. In addition to this the National Park Authority (NPA) has leasehold agreements on the Peel Wyke jetty and car park.

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The interactive map below shows the management areas within the National Nature Reserve and access on and around Bassenthwaite Lake. Zoom in to a location using the scroll wheel or navigation buttons. Use the tick boxes to show access types and management areas.

Factors affecting the NNR

Bassenthwaite Lake NNR is an important site for people and wildlife. There are many internal and external factors that create both positive and negative effects on the management of the site. The table below summarises the issues affecting the NNR.

National Conservation Status

Bassenthwaite Lake supports internationally and nationally important populations of aquatic plants including floating water plantain, six-stamened waterwort and autumn water-starwort.

The lake also hosts nationally and internationally important populations of fish such as, Atlantic salmon, brook lamprey and vendace. Vendace are only found naturally in two lakes in the UK, Derwent Water and Bassenthwaite Lake and the Bassenthwaite population is very small.

Unlike many lakes in the Lake District Bassenthwaite has extensive sections of natural lakeshore vegetation and these support nationally important assemblages of invertebrates, plants and birds including thread rush, water sedge, great crested grebe, little ringed plover, osprey, kingfisher, reed bunting, reed warbler and grasshopper warbler.

The lake is designated as the River Derwent and Bassenthwaite Lake Special Area of Conservation and Bassenthwaite Lake Site of Special Scientific Interest.

Recreation and Access

sailing on bassenthwaite

In terms of recreational use Bassenthwaite Lake is the least developed and quietest of the larger lakes in the National Park.

There is no public right of navigation on the lake and all lake users require a permit. Bassenthwaite Sailing Club has a lease allowing it to use the lake, with the exception of two no boating zones and Calvert Trust, Scarness Outdoor Centre, Scarness Bay Park and Armathwaite Hall who can launch small numbers of boats at their own slipways.

  • The only slipway for use by permit holders is at Peel Wyke. Woodend Lakeshore is also used for launching by windsurfers, canoes, kayaks and paddleboarders.
  • Public access to lakeshore is mainly from car parks and laybys along the western shore at Ouse Bridge, Peel Wyke, Beck Wythop, Blackstock Point and Woodend.
  • Access along eastern shore is limited to a lakeside public footpath, Scarness to Broadness Farm and a public footpath down to lakeshore at Lakeside Wood.
  • Fishing is a significant recreational activity on the lake, particularly for salmon at Ouse Bridge and pike and roach at Beck Wythop. All fishing requires a permit.

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Site strengths

Bassenthwaite

Size

  • Bassenthwaite Lake is officially the only lake by name, the others are meres or waters.
  • 4th largest lake in the English Lake District
  • Bassenthwaite lake is likely a key component of natural recovery network due to size and integrity.
  • Bassenthwaite's hydrosere vegetation is the most intact and extensive of major Cumbrian lakes.
  • The wintering population of wildfowl is the second largest in the Lake District.
  • The stands of Phalaris arundinacea tall herb fen on Rough and Green Mires are one of the largest expanses of this vegetation type in the National Park

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Bassenthwaite lake by Stewart Smith.CT

Biodiversity

  • Rich aquatic macrophyte flora, including 3 nationally scarce species.
  • Diverse range of plant communities (open water, woodland, swamp and fen, marshy grassland, and mesotrophic grassland).
  • One of only two vendace populations in England.
  • 74 species of breeding bird recorded.
  • Diverse invertebrate assemblage.

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Bassenthwaite lake

Intrinsic appeal

Bassenthwaite has immense intrinsic appeal as it is one of the main landscape features of the north-western Lake District.

  • Aesthetic appeal lies in relatively undisturbed nature of lake and lakeshore habitats and its setting between Skiddaw to the east, Wythop Woods and low Wythop fells to the west with views of Borrowdale and Derwent Fells to the south.
  • More natural appearance and feel than many of the other large lakes in the National Park due to the low-level recreational activity on and around it.

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Bassenthwaite lake by Stewart Smith.CT

Water quality

  • Low retention time and high volume of through-flow acting as a buffer, reducing effect of eutrophication on plankton.

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Wintering Populations of Wildfowl

  • British Trust for Ornithology’s (BTO) Wetland Bird (WeBS) counts conducted monthly providing population, abundance and distribution data trends.
  • The network of sites protected for importance to wintering water birds depends on WeBS counts -  ducks, geese, swans, waders, rails, divers, grebes, cormorants, herons, gulls, terns.
  • Counts are conducted by a local ornithologist for BTO. Volunteers support management of the site, from engaging visitors and lake users, to monitoring activity, invasive non-native species and keeping access clear of vegetation.
  • Volunteers and staff use INNS Mapper to record and follow up on invasive non-native species, downloaded onto NPA GIS as a monitoring tool.

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Site weaknesses

Eutrophication

  • High phosphate load in lakebed sediments.
  • Although Bassenthwaite has a low retention time, its shallowness and susceptibility to wind mixing means it is sensitive to slight changes in nutrient loading and sediment inputs.
  • The lack of deep water means bottom sediments and nutrients are not lost from the system but can be recirculated by wind-induced mixing.
  • The loss of nutrients and sediments from the system is largely down to flushing out of the lake.  This may mean Bassenthwaite is actually very sensitive to slight changes in nutrient loading and slow to respond to reductions in nutrient loading.

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Himalayan Balsam

Invasive non-native species

  • There's been speculation on introduction of roach, dace and ruffe into Bassenthwaite through live baiting contributing to reduced vendace population. Roach and vendace are zooplanktivores, roach may out-compete vendace for its main food source, however roach occupy a different niche to vendace, so competition may not be great.
  • Roach populations are declining, threat may be waning. Ruffe are known to prey on schelly Coregonus lavaretus eggs - it is possible it will feed on vendace eggs reducing reproductive success of vendace. Both introduced species favour eutrophic waters, vendace favours oligotrophic or mesotrophic conditions. Dace numbers are high, first recorded in 1996, not thought to pose a threat to vendace.
  • Sedimentation is considered the primary cause of extinction of vendace. Eggs laid by fish in early winter months become smothered by sediment before they hatch the following spring. The majority of sediment affecting vendace spawning grounds is inorganic, from the catchment.
  • New Zealand pygmy weed Crassula helmsii is established, a highly invasive non-native aquatic weed which could seriously threaten aquatic flora and may be impacting wintering wildfowl numbers, in decline since 2014/15.
  • Himalayan balsam Impatiens glandulifera and Japanese knotweed Fallopia japonica are present throughout the NNR, generally in small stands.
  • American mink (Neovison vison) escapees and deliberate releases have resulted in mink becoming well established across the UK. An invasive non-native species that eat fish, birds and are largely responsible for Britain’s rapidly declining water vole population. There are occasional sightings around the lake. We support targeted control of American mink to protect native wildlife.

There is the potential for the spread of other invasive non-native species not currently present through increased use of the lake and both a lack of awareness of the need for biosecurity and compliance with biosecurity measures, particularly amongst new lake users. We need to ensure better habitat resilience to the effects of extreme climatic events resulting from climate change, such as high winds, floods and droughts to prevent the occurrence of new pathways to non-native invasive species and their negative impact on native biodiversity.

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External Opportunities

England Catchment Sensitive Farming Delivery Initiative

Bassenthwaite Lake is one of the catchments included in the England Catchment Sensitive Farming Delivery Initiative to reduce the pollution of surface-water bodies caused by farming operations. It is a joint Department for Environment, Food and Rural Affairs (Defra), the Environment Agency and Natural England initiative. The objectives of the initiative are largely delivered through Countryside Stewardship.

Development of the Environmental Land Management (ELM)

  • The Government’s 25 Year Environment Plan sets out how the government propose to improve the environment, within a generation. As part of its delivery new Environmental Land Management Schemes have been created intended to support the rural economy through payment of farmers, and other land managers, for the delivery of more focused sustainable environmental land management. Defra is currently rolling out schemes i.e. Landscape Recovery, which are aimed at promoting the following outcomes:
  • Creating, restoring, and maintaining wildlife-rich habitats
  • Improving water quality
  • Increasing resilience to flooding and drought
  • Increasing woodland and tree cover
  • Reducing carbon emissions, storing carbon and increasing resilience to climate change

Future schemes include Countryside Stewardship Plus Sustainable Farming Incentive & Landscape Recovery.

Cumbria Local Nature Recovery Strategy

Cumbria Local Nature Recovery Strategies (LNRS) is still in development but will become the driving strategy for nature recovery in Cumbria. As such, this plan will play an important role in implementing the Cumbria LNRS.

Landscape Scale Recovery

ELMs and delivery of the LNRS also presents an opportunity to look towards adjacent land to work in partnership with other landowners to deliver a landscape scale project to create a bigger, better and more joined-up habitats with the aim of protecting wildlife and helping to tackle climate change by creating resilience, restoring freshwater habitats, and improving water quality. It will provide people with greater opportunity to visit, bringing nature closer to people with consequent spin offs that will benefit the local economy.

Mine Water Treatment Schemes

The Environment Agency monitors water bodies for heavy metals as part of the Water and Abandoned Metal Mines (WAMM) Programme, working with the Coal Authority and Defra to deliver remediation schemes where they are needed.

An existing treatment scheme has been operational at Force Crag Mine since 2014, improving the water quality up to 10 km downstream in Coledale Beck. Feasibility work is planned for 2024/25 to determine what more can be done to improve the performance of this scheme and to address other diffuse sources in the area.

A new treatment scheme is proposed for Threlkeld Mine, aiming to be implemented by 2028 subject to funding, planning and other permissions. This scheme would significantly improve water quality in Gategill Beck and up to 25km downstream.

Other opportunities include further investigations to identify diffuse pollution sources in Newlands Beck and work to investigate the behaviour of metals in Bassenthwaite Lake.

Lakes Surveillance Network (LNS)

The Environment Agency’s Lakes Surveillance Network (LSN) is a national scale surveillance monitoring network being delivered by the Natural Capital and Ecosystem Assessment programme. The LSN is designed to provide data and evidence on the national condition and trend in condition in the lake resource for England. A representative sample of all of England’s lakes larger than 2 hectares will be monitored; Bassenthwaite is scheduled to be monitored in 2028. Monitoring elements will include water chemistry, phytoplankton, macrophytes, fish and physical habitat. Physical habitat and fish community analysis will utilise innovative monitoring techniques including eDNA analysis, satellite imagery, aerial photography, and Lidar. This data has the potential to be linked to other data sets (both modelling and monitoring data) providing a more detailed picture of water quality in the catchment.

Diffuse Water Pollution Plan

The River Derwent, Tributaries and Bassenthwaite Lake Diffuse Water Pollution Plan will assess current and modelled water quality under different scenarios to inform an Options Appraisal (OA) for tackling diffuse pollution. The plan and OA will be jointly agreed between NE and the EA and will require both organisations to agree to work collaboratively to progress actions in the plan. The sign off deadline for the plan is March 2025, after which date work to progress agreed actions will begin”

Research Needs

The plan presents an opportunity to work with partners to identify future research needs required to support delivery of the plan. For example, the ongoing research by Natural England, Environment Agency and Glasgow University into the viability of vendace populations. A recent report by Natural England (2021) advocates for a habitat-led approach to restore populations in both Derwentwater and Bassenthwaite Lake (Definition of Favourable Conservation Status for Vendace - RP2958 (naturalengland.org.uk)).

The identification and development of a research programme with a list of priority projects/questions to be addressed in order to build a more robust environmental evidence base to inform future management decisions will be key to the continued management of the NNR.

Wastewater Treatment

United Utilities is planning to invest in improving the removal of phosphorous from a number of its wastewater treatment works in the catchment (subject to OFWAT approval). In addition, the Bassenthwaite catchment is identified for nutrient neutrality which requires the additional nutrient load arising from any new development to be mitigated. These projects and initiatives could contribute to delivery of water quality objectives outlined in the plan.

Nutrient Neutrality

At present, certain types of development which discharges waste and/or surface water into parts of the SAC which are exceeding targets for Total Phosphorus must demonstrate that they are nutrient neutral[1].

This means that at planning application stage developers must show that there are mitigation measures available upstream to prevent additional phosphorus entering the watercourse which would further add to current exceedance. Planning permission can only be granted by LDNPA officers where there is certainty that there will be no net increase in nutrients.

Opportunities for multiple benefits delivered through mitigation measures, including: the creation of new wetlands, woodland or grasslands, providing additional benefit for nature recovery and offering potential new income streams for landowners.

West Cumbria Catchment Partnership

Opportunity to work in collaboration with the WCCP. Led by West Cumbria Rivers Trust the partnership.

works closely with local communities and land managers to prioritise, plan and deliver actions; share information and expertise; ensure coordination of project delivery and funding sources and champion nature-based solutions that provide multiple benefits.

Invasive Non-Native Species (INNS)

Working with the National Trust, Environment Agency, West Cumbria Rivers Trust and Natural England will be crucial to achieving effective coordination of actions to address INNS in the Derwent Catchment. The Derwent Invasives Partnership and an interactive INNS map is available: Derwent Invasives Map.

River Corridor Group

Opportunities to work more closely with the RCG. The project is long-term and ongoing, with the key objectives of improving riparian habitat through stock-exclusion and riparian planting, tree management, improving in-river habitat for fish species through the introduction of large woody debris, providing spawning gravels, creating wildlife corridors through assisted natural recovery projects, and contributing to natural flood management processes.

Research Needs

The plan presents an opportunity to work with partners to identify future research needs required to support delivery of the plan. For example, the ongoing research by Natural England, Environment Agency and Glasgow University into the viability of vendace populations. A recent report by Natural England (2021) advocates for a habitat-led approach to restore populations in both Derwentwater and Bassenthwaite Lake: RP2958 Edition 1 Definition of Favourable Conservation Status for Vendace.pdf. A comprehensive review of research needs would be a valuable addition to the management plan.

National Highways Cycle Trail

  • National Highways have an aspiration to upgrade the permitted path along the west side of the lake to a cycle trail which will also improve access to people with limited mobility and help manage visitors; discouraging them from entering more sensitive areas.
  • The Cycle Trail will take cyclists, walkers and mobility scooters from Dubwath to Powter How along the shores of Bassenthwaite Lake. The NPA has created the potential for access along Power How woods to the car park. It has huge potential for reducing carbon, by creating a safe alternative to the A66 for commuting purposes, and by creating a low carbon alternative for visitors to use instead of driving. The ultimate aim is for it to connect with the Keswick to Threlkeld and Derwentwater Trails in Keswick, creating a network for longer journeys and strengthening Keswick’s role as a sustainable transport hub.
  • There will be considerable scope within both the NPA and National Highways ownership boundaries for enhancement of the ecological value of the site as the development of the cycleway should encompass Biodiversity Net Gain principals and the objectives of the management plan.

The proposed trail has the potential to bring large health and wellbeing benefits by creating a more accessible path not only for cyclists but also for people with limited mobility and people with pushchairs.

External Challenges

Funding

Over the last ten years LDNP budgetary constraints has resulted in significant changes in staffing and other resources. As a result, NPA resources available for site management have reduced, leading to less of a physical presence on site.

Eutrophication

  • Eutrophication of the lake waters from sewage outfalls and agricultural run-off causes anoxia in the hypolimnion in late summer which is detrimental to vendace and the ecology of the lake as a whole. Eutrophication has also resulted in the accumulation of dead algae and other dead plant material on vendace spawning grounds which has detrimental effects on vendace reproductive success, though further investigation has revealed that the major component of this silt is inorganic and consequently not the product of nutrient enrichment.
  • Although the main external source of nutrients has been dealt with by adding a phosphate stripper to the Keswick wastewater treatment works in 1995, there are still nutrients stored in lake sediments. Further, not all the phosphate is removed by the stripper, even under normal circumstances, as the efficiency of the process is reduced due to dilution due to high precipitation levels. During periods of heavy rain, the success of phosphate removal declines further, as the capacity of the works is exceeded, and the tertiary treatment is bypassed.
  • The re-suspension of these phosphate-rich sediments by wave action in the shallow waters of Bassenthwaite Lake is thought to be the main reason why there has been a far less dramatic improvement in the aquatic ecology of this lake following the introduction of phosphate stripping than has been seen in deeper lakes, like Lake Windermere. Sediment removal is considered to be impractical as a remedial action for Bassenthwaite Lake, due to its size.

Sedimentation

  • Sedimentation is considered to be the primary cause of the extinction of vendace. Eggs laid by the fish in the early winter months become smothered by sediment before they have had chance to hatch the following spring. The majority of the sediment affecting vendace spawning grounds is inorganic and is derived from the catchment. Several issues to do with catchment management have affected the sediment load entering the lake, including, soil erosion, land drainage and riverbank maintenance works, forestry and road building.

Abandoned Metal Mines

Abandoned metal mines pollute about 36km of rivers in the Derwent catchment. These polluted watercourses all enter Bassenthwaite Lake, including Coledale Beck, Newlands Beck, Comb Beck and Gategill Beck.

Non-native invasive species

  • The presence of New Zealand pygmy weed Crassula helmsii in Derwent Water and elsewhere outside the NNR renders attempts at eradication ineffective due to high likelihood of reintroduction.
  • Himalayan balsam Impatiens glandulifera and Japanese knotweed Fallopia japonica are present on site and upstream on the River Derwent, leading to potential for invasion of lakeshore habitats by these species.

National Highways Cycle Trail

  • Any future plans to upgrade the current permitted path to a cycle trail has the potential to increase disturbance along the western shore. Although the permitted route is currently fenced off from the lakeshore sensitive areas will need to be screened and managed to minimise disturbance of wildlife through tree planting and further soft engineering to discourage users from accessing sensitive areas along the lake shore.

Climate change

  • Climate change brings a number of challenges for the NNR, including warming of the lake water which may make it less viable for vendace; increased frequency and magnitude of storms which can result in pollution of the lake by floodwaters, lakeshore erosion, disturbance of sediments and damage to the visitor infrastructure such as paths and hides.
  • Extreme climatic events resulting from climate change, such as high winds, floods and droughts can transport and open new pathways to non- native invasive species into to new areas and decrease the resistance of natural habitats to invasions. Become, negatively impacting on native biodiversity.

Other

  • Pollution from chemical spillage following road accidents on the A66(T) is an ongoing threat to the lakes water quality however measures have been taken by the EA and the County Council Highways Department to contain any such incidents including the drawing up of an emergency plan.
  • Since the lifting of visitor restrictions post Covid-19 pandemic in 2020

visitor numbers and activity have increased and are likely to remain high as predictions indicate that numbers visiting the Lake District will increase and trends in water sports such as wild swimming and paddleboarding will be sustained.

  • Visitor numbers will need to be closely monitored and if necessary, a Visitor Management Action Plan be assigned to support the maintenance of the “quiet recreation” visitor experience and wildlife and habitats.

Management of these activities and clearing of litter following them is likely to become a major feature of visitor management in the future.

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Objectives and targets

The table below provides a summary of the objectives, targets and actions for each site feature. The objectives are designed to address the internal and external issues identified and focus our available resources on over the next five years.

Objectives

Targets

Objective 1: Subject to natural change, to maintain the aquatic habitats of the lake, with particular reference to the internationally important aquatic plant and animal communities and species.

  • Good water quality consistent with a mesotrophic lake with natural hydrological process, sediment loads
  • A natural shoreline and substrate
  • Natural aquatic macrophyte, fish and otter populations and communities

Objective 2: Subject to natural change, to maintain the natural stony lakeshore vegetation and transitional habitats from open water, fen and woodland.

  • No reduction in extent of lakeshore vegetation , no loss of component vegetation types/species
  • Invasive species should be absent or no more than rare if present

Objective 3: Subject to natural change, to maintain wet meadow and flood-plain fen vegetation.

  • No reduction in extent of wet meadow vegetation, no loss of component vegetation types/species
  • Managed encroachment of scrub.
  • Invasive species should be absent or no more than rare if present.

Objective 4: Subject to natural change, to maintain breeding and wintering bird populations.

  • No loss of extent and mix of habitat types around the lake.
  • No significant declines in numbers of breeding pairs and number of wintering birds or numbers of bird species present.

Objective 5: To keep comprehensive records of plant and animal populations in the lake and surrounding environment.

  • All land based and lakeshore areas of the NNR to be surveyed.

Objective 6: To maintain and enhance the quality of the landscape around the lake.

  • No reduction in extent of lakeshore vegetation and no loss of component vegetation types and species.
  • No year-on-year accumulation of lakeshore litter

Objective 7: To maintain public access to specified areas of the lake and lakeshore and provide interpretive material, where compatible with nature conservation objectives and erosion control.

  • No significant increase in public access in terms of both visitor numbers and range of activities on and off the water.

Objective 8: To fulfil all legal and other obligations arising from Parliamentary Acts and conveyances.

  • 100% compliance.

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Bassenthwaite - white flowers

How to find out more

Thank you for your interest in the management of Bassenthwaite Lake National Nature Reserve. For more information on Bassenthwaite Lake, including how to purchase a permit please visit:


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