Lakes - Cherished yet forgotten?

Raising awareness and opportunities for restoration

Key messages

Lakes, both naturally formed and human-made, are important priority habitats. They provide vital benefits for wildlife and people, along with a wide range of ecosystem services, and often have great cultural significance in our landscapes.

Despite this importance, and protection within legislation, lakes are mostly in a very degraded condition and have generally not featured prominently within catchment or river basin plans.

However, there are positive and achievable actions at different scales that can be taken, to both raise their profile within catchment planning, and improve the condition of lakes and their catchments.

The aim of this StoryMap is to summarise the situation and provide ideas and links to further information, to help start or support restoration of some of our most cherished yet threatened freshwater habitats.

Tatton Mere (c) Natural England

Why lakes are important

Lakes, both naturally formed and human-made, are important priority habitats within many catchments. They provide vital benefits for both wildlife and people, along with a wide range of ecosystem services, and often have great cultural significance in our landscapes and lives.

There are many thousands of lakes and other standing waters in England. Generally, if a standing water body is > 2 hectares it’s considered a lake. (If <2 hectares it's considered a pond. For more information on these priority habitats see the  Freshwater Habitats Trust ). There are almost 3000 lakes above 2ha. All lakes in England are covered by the priority habitat definitions, although there's  ongoing work  to identify the priorities within these.

Under the WFD, all lakes above 50 hectares, those designated as European sites above 5 hectares, and some other SSSI lakes are recognised as WFD ‘waterbodies’ – and so are of particular importance in River Basin and associated catchment plans. 161 lakes are designated as SSSI’s, ‘Ramsar’ wetland or European sites. ‘European sites’ comprise those designated as Special Areas of Conservation (for habitats) or Special Protection Areas (for birds) designated part of the EU’s Natura 2000 network. For River Basin plans the same considerations are applied to environmental water objectives for Ramsar sites as to WFD EU ‘protected areas’. These designations and recognition under the WFD provide the legal basis for their conservation.  

Key  25-year environment plan  goals and associated indicators include lakes. Lakes have an important role to play, providing habitat and refuges for a diversity of wildlife, as part of the Nature Recovery Network.

There is a wide diversity in  lake types    and the wildlife they support across the country. Action in catchments often benefits the range of freshwater and wetland habitats that occur within them, including ponds, lakes, streams, rivers and wetlands. 

Delivery at catchment scale can take account of these synergies, and secure opportunities to achieve biodiversity benefits across the full range of habitats.

However, there are also some actions that may be required specifically on a lake to improve its functioning and condition, but these can still have wider benefits for rivers and wetlands. For example, restoring shoreline and riparian land can lead to wetland creation; removing barriers can also be good for fish in rivers, and improving water quality is beneficial across a catchment. As part of a  Nature Recovery Network , lakes provide ‘stepping’ stones in the landscape and resilience to the freshwater habitat resource, even when they are not directly hydrologically connected.

However, despite their importance for wildlife and people, and protection by legislation, many lakes are in a degraded condition and have generally not featured prominently within catchment or river basin plans - although there are excellent examples of restoration work around the country, some of which are represented in our case study section.

In part, this is due to the challenges in restoring what in some cases are some of the most threatened or modified aquatic habitats in England. However, there are positive and achievable actions at different scales, that can be taken to improve the condition of lakes and their catchments. Continue reading to find out more about the pressures on lakes and what can be done to address them.

Why are lakes (generally) in poor condition?

The degraded condition of lakes in England is widespread, both within and outside designated sites.

Some lake habitat types, particularly those predominantly found in the lowlands, are faring worse than others, with hardly any examples (<1% by area) in good condition.

Photo: Colemere SSSI & Ramsar site, Shropshire, showing evidence of nutrient enrichment (c) Natural England

Only 14 % of lake waterbodies assessed under the  WFD  are recorded as having ‘good’ ecological status or potential.

(Note 24% of WFD lake water bodies are also lake habitat SSSIs).

Photo: Highly modified lake shoreline at Ellesmere Mere (c) Marek Isalski on Flickr

Only 25 % of SSSI units with lake habitat are recorded in ‘favourable’ condition.

(53% ‘unfavourable’ - no change or declining condition, 22% are ‘unfavourable-recovering’).

Photo: Hydrological modification to Crummock Water, Cumbria (c) Jonny on Flickr

Some of the key pressures that lead to many lakes, large and small, being in a degraded condition include:

Lakes stocked with Carp can result in increased turbidity and nutrients, often with few/dislodged submerged plants. Photo: (c) NE

    • Diffuse and point source pollution (including those from  septic tanks );
    • Physical modifications and abstraction;
    • Invasive non-native species; and
    • Inappropriate fish stocking.

The legacy of some issues e.g. pollution accumulated in lake sediments, can lead to long recovery times, but any action that improves water quality will improve lake habitat. So there is value in undertaking such measures, at whatever scale is available.

All these impacts are recorded as SSSI ‘reasons for adverse condition’ and WFD water body ‘reasons for not achieving good’, leading to many designated sites and waterbodies being recorded as being in ‘unfavourable’ condition or less than ‘good’. Poor water quality resulting from diffuse pollution is the most frequent issue.

WFD Status

Lake waterbodies are sampled by the Environment Agency for a number of different elements to determine ecological and chemical quality. The status classes range from 'High' to 'Bad' for overall and ecological status as per the legend below and Pass(green)/Fail(red) for chemical status.

In 2019, only 14% of lakes were classified as being in Good Ecological Status/Potential making no significant change since the last classification in 2016.

WFD Lake waterbody classification: Lake ecological status or potential (% / no). Courtesy EA 2020 – based on 589 lake waterbodies.

Use the buttons below to see the 2022 WFD ecological, overall and chemical status of lakes in England.

Click on a lake on the map to retrieve a link to the Environment Agency's Catchment Data Explorer where you can find out more information including details of failing elements and reasons for not achieving good status.

Reasons for WFD waterbodies not achieving ‘good’ – recorded significant water management issue (SWMI) elements for WFD lakes. 

SSSI Condition Assessment

Natural England assess the condition of SSSI's which for lakes are classified into the following condition categories from 'Favourable' to 'Unfavourable Declining' as shown on the map to the right.

Click on a lake on the map to access a link to Natural England's Designated Sites View where you can find the latest condition assessment for each lake or lake SSSI unit together with any identified reasons for adverse condition if applicable.

Currently only 25% (83) lakes are assessed as being in Favourable condition.

Condition of SSSI units with Lake habitat features (No. and %), Source: Natural England.

Condition of the five lake habitat types in England (Summarised from data supporting Article 17 reporting, courtesy Ruth Hall, 2019)

Top 5 Adverse Condition Reasons (ACR) on standing water SSSIs not in ‘Favourable’ condition.

Nutrient Sensitive Areas - Eutrophic Lakes

Nutrient sensitive areas are those areas designated as sensitive under the Urban Waste Water Treatment Directive (UWWTD). The UWWTD describes eutrophication as:

‘the enrichment of water by nutrients, especially compounds of nitrogen and/or phosphorous, causing an accelerated growth of algae and higher forms of plant life to produce an undesirable disturbance to the balance of organisms present in the water and to the quality of the water concerned’.

The map to the right highlights those lakes in blue that have been designated as a Sensitive Area.

In particular, a large proportion of ‘Ramsar’ and European designated lakes are failing to meet their conservation objectives.

Failure is often due to poor water quality, with phosphorus a more widespread issue than nitrogen - but both are a problem

Boldermere SSSI has invasive species issues, and filamentous algae indicating elevated nutrients. Photo: (c) Natural England

Naturally nutrient poor sites with upland catchments are those which are most likely to have escaped the pressure of eutrophication that is pervasive in lowland England. However, even these sites with cleaner water are still subject to other pressures e.g. invasive species (although these are often under-recorded).

Climate change impacts are cross cutting and so not currently well captured by the data above, but recent review work considers:

the climate change sensitivity of standing open water habitats, including lakes and ponds, to be ‘High’.

The Climate Change Adaptation Manual by Natural England and RSPB is a resource to support practical and pragmatic decision-making, by bringing together recent science, experience and case studies, and is intended to be an accessible entry point to a range of available resources and tools. 

There has been action to tackle point source and diffuse pollution (e.g. through water company investment, and activities through agri-environment schemes and catchment sensitive farming advice) as well as targeted habitat restoration activity on some lakes.

However, it’s recognised that there has been a lack of progress in improving the condition of lakes and their catchments.

(see specific reference to lakes in the Environment Agency’s RBMP3 ‘Challenges & Choices’ consultation ‘Biodiversity Challenge’ information). With continued and sometimes increasing pressures, condition is generally being held at a standstill, rather than improving. 

BUT the battle to restore these precious habitats is not lost. The following sections describe actions that can be taken for all lakes, some examples of successes, and sources of advice.

What can be done?

There are several approaches that Catchment Partnerships and their members can take to influence and directly improve the condition of lakes:

From a planning and strategic perspective these include:

  • Raising general awareness of lakes - their importance and condition, their association with other freshwater habitats in a catchment, and opportunities for improvement.
  • Including lakes and possible restoration activity in catchment plans.
  • Including key actions for lakes in catchment pages of RBMP3, as part of the program of measures.

And in terms of ‘direct action’ on the ground, examples include:

  • Action to improve water quality will improve lake habitat, so there is value in undertaking any measures, at whatever scale, that can contribute to this. 
  • Advice to landowners, managers and farmers around best practice soil and nutrient management within the lake catchment (e.g. through  CSF ).
  • Where opportunities allow, maintaining and restoring a natural hydrological regime, including water-level fluctuations and inflows and outflows.
  • Restoring natural marginal and riparian vegetation can benefit biodiversity and potentially improve water quality.
  • Restoring more natural mixed fish communities, especially where the fish assemblage is contributing to habitat degradation or preventing restoration of a clear water state. Doing so can help restore clear water and enable submerged plants and biodiversity to recover.
  • Sediment removal may be an option in some circumstances but usually addressing excess nutrient and sediment inputs first, is a priority. Tangible improvements to condition can still be achieved with other measures, before considering de-silting, such as those above.

Guidance and a fuller description of actions to restore natural lake function can be found within the CaBA Biodiversity Pack - Lake Guidance. It is recognised that restoring natural ecosystem function may not be appropriate or desirable in all locations. It’s about the art of the possible, working in locations most conducive to restoration, although every step toward achieving natural function on any lake, will bring about positive changes for plants and wildlife.

The  CaBA website  also provides more information on a range of resources and tools that can help support CaBA partnerships to deliver these actions. For example:

Examples of different approaches to lake conservation and restoration

The following are short case studies describing a range of ideas and approaches that can be used to address some of the issues affecting lakes. We hope to build a library of case studies to capture examples and experience of lake and lake catchment restoration. If you have any to contribute, please see contacts at the end of this StoryMap.

Explore the case study media: Click the arrow buttons to the right of each image to scroll through the images and videos that support each case study. Click on the info (i) button in the top left corner of each image to see its caption. Zoom out of the map and click the number buttons to jump to other case studies.

1

Elterwater, Cumbria

Elterwater SSSI is situated in the Lake District and consists of three distinct interconnected basins. It supports a diverse habitat including open water, fen, marshy grassland and woodland. Elterwater had historically received discharge from the local water treatment plant (1974 to 1999), inflows had been altered (probably in the 1940’s) and septic tanks also contributed nutrients. Whilst the major inputs have now ceased, reduced flow through the system meant that the nutrients were not leaving Elterwater, with water levels undynamic, resulting in degradation of the special in-lake and shoreline plant communities. 

A project has been undertaken by the South Cumbria Becks to Bay Catchment Partnership to restore the hydrology, through piping water and re-naturalising some of the inflows. This should start to flush Elterwater, helping rid the lake of the nutrients that have accumulated over time. It may also help prevent the lake from becoming oxygen deficient which can lead to an increased release of nutrients from the sediment. A key septic tank issue has now been dealt with.

A Water Environment Grant project is looking at re-naturalising the remaining diverted inflows; as well as managing invasive non-native littoral vegetation to allow recolonisation by native plants, and with the aim of reducing overall nutrient loading and cycling in the lake. Monitoring is ongoing to see whether this is enough to improve the water quality and biology. Other improvements to lake fringe habitats include restoring reedbeds and reed swamps, that will further benefit habitat diversity, and the lakes flora and fauna such as nesting birds and juvenile fish.

2

Hatchmere, Cheshire

Hatchmere SSSI in Cheshire, is an internationally important ‘Ramsar’ site and SSSI, part of the wider ‘Meres and Mosses’ wetland landscape. It is designated for its varied lake and wetland plant communities, birds and insects including the rare hairy dragonfly and variable damselfly. It has been under the ownership of Cheshire Wildlife Trust since the late 90s. 

Much like other meres in Cheshire the lake suffers from poor water quality, with no single large contributor of nutrients into the lake, rather several smaller sources within the catchment. The hydrology of the lake has also been significantly altered. There is also a population of introduced carp, which can result in regular disturbance of the lake bed, increasing turbidity and releasing nutrients into the water column. Historically there have also been significant numbers of people swimming in the lake.

A range of approaches are being tried to address these issues, including: blocking surrounding ditches with woody debris dams to trap sediment, and re-naturalising modified inflows to restore the hydrology of the surrounding wetland habitats; treatment to try and reduce phosphorous release; limits on wild swimming, and selective fish exclusions to some areas of the lake to see if water quality will improve and enable aquatic plants to grow; and work with surrounding landowners to adopt catchment sensitive practices. The Trust has just released a pair of Eurasian beaver into an enclosed area to create new wetland habitat that will help filter water into the Hatchmere main inflow and create greater habitat diversity. 

3

Cockshoot Broad

Many of the shallow lakes (broads) of the Broads National Park have undergone restoration using a range of approaches, at different scales, and levels of ambition, by a range of partners including the Broads Authority (BA), Norfolk Wildlife Trust (NWT), Environment Agency(EA), Natural England (NE), and UEA.

Cockshoot Broad was one of the first sites at which restoration techniques were trialled. It is a SSSI 5ha shallow lake surrounded by carr woodland and fen in the river Bure catchment, is a National Nature Reserve, SSSI and part of the Broads SAC and SPA and Ramsar international sites, and managed by NWT.

Cockshoot Broad was severely affected over a long period by a build-up of silt, resulting in algae-rich, very shallow turbid water, unsuitable for native flora and fauna.

In 1981, the Broad was isolated with a dam, cutting it off from the river Bure catchment to lower the input of unacceptably high phosphorous level from the river water. At the same time, accumulated silt within the broad was also removed to a depth of 0.75 m. 

The broad’s fish populations have been monitored and electrofished each year since 1989 (with fish removal until 2012) to reduce the population of certain fish species that feed on zooplankton (like ‘water fleas’)  that normally keep algae concentrations low in the water column.

Also in 1982, 2002 and 2011 and other times, overhanging trees were removed from a strip around much of the broad’s perimeter in order to restore the littoral margin (but retaining some tree areas important for bat roots, birds and invertebrates). Once removed, light levels increased and riparian plants began to recover, including a wide diversity of open fen and emergent plants, followed by reed and lesser reedmace in the open water. This proved to be a simple and effective method for improving biodiversity of the littoral zone.

Submerged macrophyte re-introduction was trialled in 2000-03 by UEA using coir pallets with plugs of rooted macrophyte species introduced to areas around the lake. The introduced plants failed to colonise due to smothering with filamentous algae.

Since the dredging and ‘biomanipulation’, water depth is sufficient for macrophytes over the majority of the area. Phosphorus levels and algal populations have reduced in the river and broad, and the lake has returned toward a macrophyte dominated system, particularly by the rare holly-leaved naiad. Monitoring of macrophytes (by BA) and water quality (EA) continues, along with ensuring nutrient sources from within the catchment are minimised.

Saline incursion from rising sea level and climate change are threats to the freshwater dependant species of the Broads, including those in Cockshoot in the longer term.

Useful Links and Further Information

The  CaBA Biodiversity Pack’   includes advice and habitat guides to support catchment partnerships and others in their delivery of freshwater and wetland biodiversity projects. There is a  specific guide for lakes .

Information on Priority freshwater lake and river habitats, and  maps  can be found at the FBAs  https://priorityhabitats.org/  where  lake restoration priorities , and  lakes with high natural function  can be recorded on the  priority habitats web portal .  

The  Aquatic restoration partnership  a comprehensive introductory peer-reviewed guide to aquatic restoration, including different lake types.

 The Freshwater Habitat Trust  website provides a wealth of information around freshwater habitats including ponds and lakes.

 Restoring England’s Special Lakes  – Natural England & Environment Agency Guidance on the Restoration of Lake SSSIs and Natura 2000 Network Sites.

 A review of lake restoration practices and their performance in the Broads National Park 1980-2013  – describes various case studies and issues around restoration of shallow lakes.

Maps and data on all UK lakes can be found at the UKCEH  UK Lakes Portal  – which provides location and ecological data (Note WBID codes are not the same as the WFD waterbody ID).

The  Catchment Data Explorer  for information on WFD Lake Water bodies.

 Designated Site View  for SSSI, European and Ramsar site information. 

Contacts

 Glen Cooper , Natural England Lake Restoration Programme Manager

Environment Agency Catchment Co-ordinators  Listed Here 

 Ruth Hall , Natural England, Standing Waters Senior Specialist.

 Jo-Anne Pitt     Senior Environment Agency Specialist, Research, Analysis & Evaluation: Air, Land and Water Research Team.

 Andrea Kelly  Senior Ecologist, the Broads Authority.

 Josh Jones , CaBA & The Rivers Trust Data & Evidence Team

Credits and References

This StoryMap has been developed in partnership by Natural England and the CaBA Technical Support team with funding from the  EU Natural Course LifeIP Project .

Content

Glen Cooper, Natural England

Tatton Mere (c) Natural England

Lakes stocked with Carp can result in increased turbidity and nutrients, often with few/dislodged submerged plants. Photo: (c) NE

Boldermere SSSI has invasive species issues, and filamentous algae indicating elevated nutrients. Photo: (c) Natural England

WFD Lake waterbody classification: Lake ecological status or potential (% / no). Courtesy EA 2020 – based on 589 lake waterbodies.

Reasons for WFD waterbodies not achieving ‘good’ – recorded significant water management issue (SWMI) elements for WFD lakes. 

Condition of SSSI units with Lake habitat features (No. and %), Source: Natural England.

Condition of the five lake habitat types in England (Summarised from data supporting Article 17 reporting, courtesy Ruth Hall, 2019)

Top 5 Adverse Condition Reasons (ACR) on standing water SSSIs not in ‘Favourable’ condition.