In the forthcoming Winter 2021 issue of Conservation Land Management (CLM) magazine Jenny Price and Lyndsay Wayman-Rook describe how the Old Chalk New Downs project in Kent has been trialling biodegradable cardboard tree guards as an alternative to plastic. Here you can read a summary of the article.
The main purpose of a tree guard is to protect newly planted trees from browsing, but they also provide other benefits; they create a more favourable microclimate that helps to promote the growth of young trees and protect the plants from wind, competing vegetation, herbicides and water loss. Wooden and wire tree guards have been in use since the 1820s, but it wasn’t until the 1980s that plastic versions were first used. As a cheaper material compared to alternatives, plastic is now widely used for guards in planting schemes.
It has been predicted that between 1980 and 2020 over 200 million plastic tree guards were used, and with the UK government’s ambitious target to increase woodland cover by 19% by 2050, the rate of tree planting is sure to increase, as will the number of tree guards used. It is recommended that plastic tree guards are removed 2–3 years after their installation, but they are often left behind to degrade in the landscape, which can be both damaging to the wider environment (although the impacts of this are not yet fully understood) and to the tree itself. It is possible to recycle plastic polymer guards, but not if they have already started to break down or are contaminated.
The Old Chalk New Downs project, hosted by Kent County Council and funded by the National Lottery Heritage Fund, has been exploring alternative options to plastic tree guards. It first compared the costs of different materials, including plastic, cardboard and biodegradable plastic, and looked at the pros and cons for each guard type. For instance, one of the advantages of a cardboard guard is that it does not need to be removed after installation, but it may deteriorate a lot faster than other guard types, especially in particularly wet areas.
It was decided that cardboard guards would be used for this particular project, owing to their no-plastic design and availability. Between autumn 2019 and spring 2021, more than 9,000 trees with cardboard guards were planted across seven hedgerows at three different sites. How these fared was closely monitored, and the success rate of planting was high. One key aspect of this project was to gather feedback from landowners and contractors involved in sourcing and using the cardboard guards, and overall the comments were positive.
In the full article Jenny Price and Lyndsay Wayman-Rook discuss how the cost of tree guards made from plastic, biodegradable plastic and cardboard compare, and provide an in-depth overview of how cardboard guards performed when used for hedge planting, both in this project and in examples from elsewhere. They also include a summary of the feedback received from landowners and contractors, and clearly describe the advantages and disadvantages of different tree guard options.
Other articles featured in the Winter 2021 issue include:
RSPB Nigg Bay: Scotland’s first coastal realignment
Helping to make and document conservation decisions: the Evidence-to-Decision tool
The Stage Zero approach – lessons from North America on restoring river, wetland and floodplain habitats
Viewpoint: Plant fewer, better: good tree and shrub establishment
In this and every issue you can expect to see Briefing, keeping you up to date with the latest training courses, events and publications, and On the ground which provides helpful tips or updates on products relevant to land management. Other features that regularly appear in CLM include Viewpoint, a similar length to our main articles, but here authors can voice their own views on various conservation issues, and Review, which can include letters from readers or updates from our authors.
CLM is published four times a year in March, June, September and December, and is available by subscription only, delivered straight to your door. Subscriptions start from £22 per year. Previous back issues are also available to purchase individually (subject to availability). Current subscribers can expect to receive their copy of the Winter 2021 issue in the next couple of weeks.
If you are involved in a conservation project and think your experiences could be useful to other practitioners, we would love to hear from you. If you are interested in writing for CLM feel free to contact us – we will be happy to discuss your ideas with you.
Woodland is the next habitat in our NHBS Introduction to Habitats series. Broadly, these habitats are land that is covered with trees, but the term woodland encompasses a diverse group of habitats that can be rich in wildlife. They are a key habitat for many invertebrates, plants, birds, mammals and other species groups. Woodlands are also incredibly useful habitats, for instance by providing flood protection by holding back water in the soil, sequestering carbon dioxide and reducing local temperatures. They also help reduce soil erosion and regulate weather patterns, such as local rainfall and temperature. Woodland may also be beneficial to our health, as it’s thought that spending time in forests decreases blood pressure, reduces stress levels and boosts your immune system. However, studies are still ongoing into the validity of these effects.
The types of woodland habitat include, but are not limited to, ancient, broadleaved, coniferous, mixed and wet woodland, as well as temperate rainforest, Caledonian forest, wood pastures and urban woodland. Each can have defining criteria such as plant types, soil moisture levels, humidity levels and age. There are also semi-natural and plantation woodlands, which are classified based on the percentage of planted trees. There are several indicator species used to determine the type of woodland habitats, such as the violet click beetle (Limoniscus violaceus), which rely exclusively on ancient decaying beech and ash trees. Several of these habitats are UK Biodiversity Action Plan (BAP) Priority Habitats, which are a range of threatened semi-natural habitats that require conservation action.
What species can you find here?
Flora
While trees often define woodland, this is not the only type of flora in these habitats. Woodland habitats host 60% of all known vascular plant species. Wildflowers, grasses, sedges, ferns, mosses, fungi and lichen all occur in woodland habitats, although the species found varies depending on the abiotic and biotic conditions within the habitat.
Oak Tree (Quercus spp.)
Did you know that there are actually over 500 species of oak tree in the world? The dominant oak tree in the UK is the English oak (Quercus robur). The sessile oak (Quercus petraea) is the UK’s other native oak species, but there are many more non-native species here, such as the Turkey oak (Quercus cerris) and holm oak (Quercus ilex). Oak trees can be keystone species in many ecosystems, with one study finding that a single oak tree can host more than 2,300 organisms (data supplied by Natural Environment Research Council). Some of those don’t occur on any other tree species. Oak trees can also live to around 1,000 years old!
Wood Anemone (Anemone nemorosa)
The wood anemone is an ancient woodland indicator species as they are slow-growing and take a long time to fully establish. Therefore, large patches show that the habitat has been relatively undisturbed for a long time.
They are a spring species, often appearing with bluebells, another ancient woodland indicator. This species has a star-shaped white flower, that can have a pink tinge. It has distinctive yellow anthers in the middle.
Herb-Robert (Geranium robertianum)
A type of crane’s-bill, herb-robert is a low-growing plant with pink flowers and a reddish stem. It is widespread across the UK and prefers shaded habitats, such as woodland. This plant has many traditional uses, such as treating headaches, stomach aches and nosebleeds. It is an important nectar source and food plant for many invertebrates, such as bees and the barred carpet moth (Martania taeniata).
Fungi
Woodland, particularly habitats with a high amount of deadwood and leaf litter, can be key habitats for a wide variety of fungi species. These species break down dead organic matter and facilitate the recycling of carbon and nutrients back into the soil. They are also food for many species, including a number of invertebrate species, and are used as nesting material, for both birds and invertebrates.
Candlesnuff Fungus (Xylaria hypoxylon)
Also known as stag’s horn fungus and candlestick fungus, this species grows up to 6cm tall, with a black base, grey body and white tip that is often branched, resembling deer antlers. It is a common species within the UK and grows in groups on dead wood. It prefers broadleaf trees, often growing through moss.
Bird’s Nest Fungus (Crucibulum leave)
This woodland fungus is so named as it resembles a bird’s nest filled with a number of ‘eggs’. These eggs are actually periodoles, structures that contain the spores. A yellowish membrane initially covers the cup, before eventually rupturing to reveal the periodoles once they’ve developed. The energy of raindrops disperses them, allowing the fungus to spread.
Woodland ecosystems are often rich in fauna and can host 80% of all known amphibians, 75% of all birds and 68% of all mammal species.
Willow Tit (Poecile montanus)
This species lives mostly in wet woodlands, feeding mainly on insects but also berries and seeds. Unusually for tit species, the willow tit digs into decaying wood to make nest holes. This is why older woodlands are so important for this species, as there is a higher abundance of decaying wood and trees. The willow tit is so similar to the marsh tit (Poecile palustris) that it wasn’t recognised as a separate species until 1897.
Small Pearl-Bordered Fritillary (Boloria selene)
Woodlands are home to thousands of invertebrate species in the UK. The small pearl-bordered fritillary is widespread across Scotland and Wales but is more limited in England. Like many other invertebrate species, they have suffered severe declines in numbers. Its bright orange and black markings make it a striking butterfly, quite easily seen against the green and brown woodland background.
European Badger (Meles meles)
This unmistakable creature is one of the most well known of Britain’s wildlife, with its iconic black-and-white striped face, grey body and black stomach. Did you know that a large amount of their diet is earthworms? They also prey upon hedgehogs, small mammals, other invertebrates, toads and frogs, and also eat fruit, such as plums and elderberries. This species is fully protected by the law but is still threatened by culls in certain areas, due to its association with bovine tuberculosis.
Eurasian Red Squirrel (Sciurus vulgaris)
Another iconic British species that use woodland habitats is the red squirrel! This native species is far rarer than its non-native cousin, the grey squirrel (Sciurus carolinensis), due to being out-competed for food and habitat. Also, grey squirrels transmit a virus called squirrelpox, which has little effect on them but frequently kills red squirrels. Because of this, red squirrels are being pushed out of their normal habitat range. They now only occur in parts of Scotland, northern England and isolated areas such as Anglesey.
Scottish Wildcat (Felis silvestris silvestris)
This elusive species, also known as the ‘tiger of the Highlands’, may be functionally extinct in the wild, as the population is too small to be viable. Threats from persecution, habitat loss, interbreeding with feral and domestic cats, road collisions and disease mean that this species will not recover without serious conservation action. There are now captive breeding programmes in place and a record number of kittens were born in captivity in 2020, with plans for the first cats to be released back to the wild from 2022 onwards.
Threats
Britain is one of the least-wooded countries in Europe, with only 13% of our land covered in woods compared to Europe’s average of 44%. The main threat to woodland habitat is deforestation, often for development or agriculture. Population growth leads to an increased need for housing and infrastructure, particularly in urban areas, often at the expense of woodland. Natural woodland regeneration is not always possible, especially for ancient woodland, which takes hundreds of years to develop. Additionally, high deer populations, particularly in Scotland, are curbing much of the growth of young plants. This is a serious threat to woodland such as Caledonian forests and it is sometimes necessary to fence off areas to allow for new growth. For more information on deforestation, as well as the potential impacts of the COP26 summit, check out our blog: Climate Challenges: 4. Deforestation.
Reduced management also threatens woodland habitats. Traditional practices, such as coppicing, which involves cutting a tree to ground level to stimulate more growth, are now less common. This led to changes in woodland structures, reducing the diversity of growth, the amount of light that can enter the canopy and reducing habitat opportunities for animals. The lack of regularly felled trees or unwanted branches that used to rot down within the woodland reduces the availability of key habitats for invertebrates and small mammals.
Invasive and non-native species can also impact woodland habitats. For instance, new plantations of tree crops, which have replaced areas of native trees, are usually less suitable for native woodland species. Diseases and pests are also causing issues for UK woodland. For example, ash dieback is predicted to kill around 90% of ash trees in the UK, and Dutch elm disease has killed millions of elm trees over the last 40 years.
Further threats also include pollution, climate change and forest fires. For more information about this threat, check out our blog: Climate Challenges: 2. Forest Fires. With the combined pressures from many of these threats and without current and future conservation efforts and protection, the future could see the loss of these habitats as we know them.
Areas of significance in the UK
Galloway Forest, Scotland – UK’s largest forest
Kielder Forest, Northumberland – England’s largest forest
Grizedale, Cumbria
Forest of Dean, Gloucestershire
Savernake Forest, Wiltshire
Abbots Wood, Sussex
Banagher Glen, County Derry, Northern Ireland
Coed y Brenin, Snowdonia, Wales
Temperate rainforests examples: Taynish National Nature Reserve and the Caledonian Forest, Scotland. Ancient woodland example: Wistman’s Wood, Devon. Wet woodland example: Amberley Wild Brooks, West Sussex
Useful resources and further reading
Miyazaki, Y., et al. 2017. Shinrin-Yoku (Forest Bathing) and Nature Therapy: A State-of-the-Art Review. International Journal of Environmental Research and Public Health, 14(8): 1-48
The Bat Conservation Trust’s annual National Bat Conference, held online via Zoom from 29th–31st October, covered many aspects of bat conservation through a wide variety of activities and talks, including monitoring, surveying and development. We are extremely pleased to have sponsored this event and we were lucky enough to have been able to attend many of these sessions, including talks by Professor Tigga Kingston from Texas Tech University on the human dimensions of bat conservation, and Thomas Foxley, University of the West of England, who spoke about the role of landscape features in spatial activity patterns of greater horseshoe bats. We also attended a few of the amazing workshops that took place, such as Shirley Thompson’s gardening for bats.
Bat Conservation Trust update
Bat Conservation Trust also shared an update on their current and future work. Bats make up more than a quarter of all mammal species in the UK, but sadly, these species face many threats. Habitat loss and fragmentation, decreasing food resources, chemical use, disturbance to roosts and threats from cats have all led to a dramatic decline in bat populations over the last century. Diseases, wind farms, flypaper, artificial lighting and the presence and construction of roads also negatively impact.
Currently, Bat Conservation Trust supports a number of local bat groups, working with volunteers, scientists, industry and government on a range of projects. They focus on discovering more about bats, taking action to protect them, inspiring people to care about bats and strengthening their work by improving relevant skills and knowledge. Their programmes include a National Bat Monitoring Programme, education and engagement, the National Bat Helpline, Landscapes for Bats, and science and research.
During this update, Bat Conservation Trust spoke of the many ways they will be increasing their efforts to help bat populations, for example by increasing the spread of their monitoring programs and organising a petition regarding key amendments to the Environment Bill, including legally binding targets for wildlife recovery. Through new acoustic and monitoring approaches, they also aim to improve their evidence base and Bat Conservation Trust are also working towards improving their engagement with policymakers, the public and the media. Their Bat in Churches project has also been expanded to include training on bat care basics, surveying a church, the best architectural practices for bats and cleaning workshops.
One key scheme they are developing is the Bat Roost Tree Tag Scheme where recognisable tags are placed on trees that contain bat roosts. The aim of this is to make sure all trees that have been surveyed and found to contain bat roosts are easily identifiable. When woodland managers and workers see a tag on a tree, they will know to seek advice before proceeding with work. This will also give a significantly increased level of protection for ancient trees, which are vitally important for a large number of species.
Future events and how to get involved
The National Bat Conference was a very interesting and educational event, and it was wonderful to see such a wide range of knowledge and skillsets being shared through the many talks, activities and workshops throughout the weekend. If you missed out this time or would like to attend further events, the Bat Conservation Trust has a number of future events planned, including Spring into Action, Midlands Bat Conference and the East of England Bat Conference. More information about these and other events can be found on the Bat Conservation Trust website.
There are a number of ways you can help to support Bat Conservation Trust, such as by becoming a member or donating. You can also contact your local bat group, fundraise for bats or volunteer for their various projects. However you choose to get involved, you can make a real difference to the future of bats in the UK.
The Lancashire Peatland Initiative, run by the Lancashire Wildlife Trust, has delivered habitat restoration across over 200 hectares of degraded lowland raised bog. These habitats are peatland ecosystems that develop primarily in areas less than 150m above sea level, particularly in cool, humid regions. These deep bodies of peat can be raised several metres higher than the surrounding land and are much wetter, usually covered in typical bog vegetation, such as cotton grass, sphagnum moss and heather.
This pioneering initiative has spanned the past three decades, with active restoration activities on numerous sites, including Little Woolden Moss, Winmarleigh Moss SSSI and Astley Moss SSSI SAC. The Trust’s tireless efforts, in collaboration with Natural England and other partners, has ultimately halted the decline of these nationally significant sites and species, resulting in an expansion of active raised bog habitats.
The Lancashire Peatland Initiative won the NHBS sponsored Best Practice Award for Large Scale Nature Conservation at the 2021 CIEEM Awards. Project Manager Sarah Johnson has kindly taken the time to answer a few questions for us.
Could you tell us about the Lancashire Peatland Initiative and how it started?
The Lancashire Peatland Initiative was born out of a desire to bring together and co-ordinate all of the peatland restoration work happening in Lancashire, Manchester and North Merseyside, raising awareness of the importance of these amazing habitats, and ensuring their protection in the future.
In 2019 we were delighted to be awarded funding from the Esmeé Fairbairn Foundation to create and support the Lancashire Peatland Initiative. This allowed us to fund Project Officers, Assistant Project Officers, communications support, and myself as Lancashire Peatland Initiative Project Manager, to work across all of the Wildlife Trust for Lancashire, Manchester and North Merseyside’s peatland nature reserves in the area. We also co-ordinate the Lancashire Peat Partnership and the Northern Lowland Peatland Coalition, and work closely with the Great North Bog Coalition and the Great Manchester Wetlands Partnership, bringing together partners and other organisations who are involved in our peatlands.
This allows the Lancashire Peatland Initiative to work on our own peatland restoration projects, but also support those of our partners and develop new projects across areas of commonality and innovation.
How did these habitats become so degraded and what are the main threats they are currently facing?
Our peatlands face threats from all directions. Historically peatlands have been seen as wastelands that needed to be tamed by humans before they could be exploited, either for conversion to agricultural land or for the extraction of the peat. Deep ditches were dug to drain the water from the peat, destroying these fragile ecosystems.
Unfortunately, many of these same threats are still faced by our peatlands today. Drainage and conversion to agriculture, overgrazing, rotational burning and extraction of peat for use in the horticultural industry has left only 13% of England’s peatlands in a near-natural state.
Public opinion is often integral in the success of large restoration projects such as this; how have you found local reception of peatland restoration? Are people generally supportive?
Peatlands are not always at the top of people’s agendas, so we are working hard to get the message out there about the importance of our peatlands, not only to provide a habitat for lots of amazing plants and animals but also in our fight against climate change, as natural flood mitigators, water filters and protection against wildfires.
However, we have found that once people know about these fantastic ecosystems they really support our work to restore and care for them. Of course, there are some issues still to fully answer, such as the need to protect both peat and our food supplies, so much of which is grown or grazed on drained peatland. But we have found that as the plight of our peatlands enters more people’s consciousnesses, they are more willing to work with us to find solutions.
The sale of peat compost to gardeners is to be banned from 2024; how do you think this will affect peatland degradation and restoration? Are there any other policies you think are needed to protect these habitats?
A ban on domestic sales of peat compost is a fantastic step towards protecting our peatlands. But so much more still needs to be done. Large amounts of peat are still being used in commercial horticulture, growing the plants that are for sale in your local garden centre, and this is an issue that is yet to be addressed. Another really damaging practice is the growing of lawn turf on drained peatlands, one of the highest carbon dioxide emitting uses of peat that not many people are aware of.
However, we do need to be careful that we are not simply exporting the issue elsewhere to areas of lower regulation. For example, Ireland recently announced an end to its peat extraction, but just a few months later there were reports of millions of tonnes of peat being imported into the country from one of the Baltic states.
We also really need policy support for the movement towards more environmentally sensitive management of land on peat-based soils. For example, the adoption of paludiculture or higher water table agriculture (wet farming) and land management could have a huge impact on CO2e emissions from our peatlands, but until these practices can be shown to be financially viable how can we expect landowners to take up these changes? This is an area where public subsidies and financial incentives could make a real difference.
There also needs to be an immediate end to all peatland burning, as the current legislation is riddled with loopholes.
Species reintroductions began in 2018; how are the species chosen for reintroduction? What are the criteria for determining whether an area has recovered enough to support these reintroduced species?
Species reintroductions are one of my favourite parts of my job! Currently, we are focusing on reintroducing species lost from Greater Manchester, and so a working group from the Great Manchester Wetlands Partnership comes together to appraise which species would be suitable for reintroduction. However, this can only happen after years of habitat restoration to create the right conditions for these returned species to thrive.
A recent success story was the reintroduction of the large heath butterfly. Locally known as the Manchester argus, the destruction of its peatland habitat drove it into local extinction almost 150 years ago. However, by following strict IUCN guidelines and working closely with Natural England and Chester Zoo, we were able to reintroduce the species to Astley Moss in the summer of 2020. Since then we have had the privilege of seeing the first native population flying on the moss this summer.
With the current COP26 summit, what are your hopes for the future of the Lancashire Peatland Initiative and the restoration of these habitats?
We have really high hopes for the future of our peatlands. It seems clear to anyone in the know that we need to be prioritising the recovery of these habitats as they can provide us with quick, massive wins in terms of carbon reductions. For example, at our pioneering carbon farm we have already seen a 90% reduction in CO2e emissions from the site, compared to an adjacent area of drained peatland that has been converted to agricultural pasture. This has been achieved in just over a year by simply re-wetting the land, and give us another year or two to fully re-vegetate the site and we expect it to become a functioning carbon sink.
What we are really hoping to see out of COP26 is a commitment to ambitious peatland restoration targets, that are backed up by both the policy and the funding to actually achieve this. In the words of Greta, we need action now – not more ‘blah, blah, blah’!
You can find out more about the Lancashire Peatland Initiative from the Lancashire Wildlife Trust website and by following them on Facebook and Twitter.
The next habitat in our NHBS Introduction to Habitats series is farmland. Farmland encompasses a wide variety of different habitats, many of which can be rich in wildlife. Farmland itself is not defined under the UK Biodiversity Action Plan as a habitat, but it contains four habitat types that are identified: arable and horticulture, boundary and linear features, improved grassland and standing open water. These habitats are important for many plant species, as well as a variety of birds, mammals, amphibians and reptiles.
Farming has been a part of the UK landscape for thousands of years and methods are constantly changing as consumer tastes shift and new technological innovations emerge. With an estimated three-quarters of the UK being farmland, it is unsurprising that these habitats are used by so many species. It is also not surprising just how important environmentally friendly farming practices are.
The need to utilise as much of the land as possible to increase productivity has led to a rapid decline of boundary and linear features, such as stone walls and hedgerows. These features constitute a significant ecological part of the farmland habitat, providing variety, food and shelter for wildlife, as well as helping to reduce run-off, flooding and soil erosion. Hedgerows and tree lines can also play an important role in carbon sequestration in agricultural landscapes.
What species can you find here?
Flora
Beyond crop species, farmland can be home to a large number of flora species that can all play key roles in the ecosystem. These plants support the large variety of fauna species found on farmland. The abundance and diversity of plant species depends on the type of habitat and the level of ‘improvement’. Improved grasslands are areas that have been re-seeded and treated with chemicals, such as fertilisers, herbicides and pesticides, and typically species diversity is much lower compared to unimproved or semi-improved grasslands.
Blackthorn (Prunus spinosa)
A common hedgerow species, blackthorn flowers in early spring and produces fruits in autumn and winter, providing an important food source for many species, including invertebrates and birds. It is visually similar to several other species, such as wild plum and wild cherry, but can be distinguished by its fruit size, leaf shape and the time of year that the flowers bloom.
Common Hawthorn (Crataegus monogyna)
Hawthorn is another common hedgerow species, providing food and shelter for species such as yellowhammers (Emberiza citrinella) and the hawthorn moth (Scythropiacrataegella). The red berries, called haws, develop during autumn and winter, and are an important source of food during the colder months for many farmland species. Did you know that hawthorn was originally associated with May Day? It was used before the development of the Maypole, with its leaves and flowers used in garlands.
White Clover (Trifolium repens)
This plant is often used as a companion plant for crops, providing additional ground cover to reduce soil erosion. White clover also fixes nitrogen within the soil, allowing for better crop growth. Clover suppresses the growth of unwanted or damaging plants too, and also acts as a trap for pests to draw them away from valuable crop plants. This practice helps to improve farmland for wildlife as it prevents it from becoming a monoculture, adding more variety in food and shelter resources. The use of cover crops within agriculture has reduced, however, and white clover is much less abundant on farmland than it once was.
Creeping Thistle (Cirsium arvense)
The creeping thistle is an important source of food for many farmland birds, such as goldfinches and linnets, but it’s often considered a ‘weed’ and is normally quite heavily managed on agricultural land. Its flower heads consist of lilac-pink florets on a cylinder of spiny leaf-like structures called bracts. During the late summer, it releases fluffy, wind-borne seeds en masse.
Fauna
Many iconic UK species use farmland and the fauna present changes depending on the time of year. Farmland can seem to come alive during spring and summer, although there is still much to see during the colder months.
Grey Partridge (Perdix perdix)
This species is an iconic part of farmland wildlife, with its orange face, dark black semi-circle patch on its abdomen and stripy grey and orange-brown feathers. The grey partridge relies on the seeds, leaves and certain invertebrate species that it finds in open farmland and has a preference for areas with hedges. It is a ground-nesting bird, laying the most number of eggs per clutch of any bird (the record is 25).
Grey partridge numbers have declined by more than 80% in the UK since the 1980s. This has mostly been attributed to a loss of seed sources, habitat loss and predation, for example by cats and foxes. Luckily there are several conservation efforts in place to help this species.
Yellowhammer (Emberiza citrinella)
These brightly coloured birds prefer open countryside with bushes and hedgerows, and so they are often found in farmland habitats. Yellowhammers feed on invertebrates and seeds, relying on farmland seeds during the winter as snow cover can make it difficult to find food elsewhere.
Heart and Dart Moth (Agrotis exclamationis)
Farmland habitats are home to a great many invertebrate species, with a large variety of butterflies and moths. The heart and dart is an easily identifiable moth due to its distinctive markings. It has a blackish v-shaped collar, with a dark dart mark and two circular marks on its wings. The wing colour can vary from lightish grey to a much darker brown. They feed on a variety of plants such as brambles (Rubus spp.), maize (Zea spp.) and lettuce (Lactuca spp.).
Brown Hare (Lepus europaeus)
While not a true native to the UK, as they were thought to have been introduced during Roman times, this species is now considered naturalised. It prefers a mixture of grassland, arable fields and hedgerows, grazing on vegetation and the bark of young, woody plants. Rabbits (Oryctolagus cuniculus) can also be seen on farmland, although they can be distinguished quite easily as hares are much larger, with longer limbs and longer, black-tipped ears.
Intensification of agricultural practices has led to a reduction in habitat areas that are seen as unproductive, such as hedgerows, rough grassland and open water areas. It has been reported that 60% of farmland species are now in decline. As well as agricultural intensification, other factors behind this decline include changes in farming practices; the use of harmful chemicals, such as insecticides; overgrazing by livestock; destruction of habitats and soil erosion.
Habitat changes caused by development, afforestation or conservation efforts that prioritise alternative habitat types can also pose a threat to farmland. As can changes in management, or a lack thereof; the abandonment of farmland can lead to encroachment by scrubs and trees. While scrubland can be an important habitat for many wildlife species, it is not necessarily suitable for all farmland species, such as ground-nesting birds that prefer open habitats. This could lead to a change in community structure and may even lead to localised extinction of vulnerable species that rely on farmland and cannot survive in other habitats. Changes in land use through development can also impact in a similar way. Furthermore, if the land was originally woodland or wetland, for example, there may be a push to restore it to its previous habitat type, which may not be suitable for the species previously inhabiting the farmland area.
Farmland habitats also face climate change-related challenges. Changes in precipitation, increased extreme weather and increased temperatures can lead to soil degradation, reduced plant growth and changes in the availability of food, shelter and fresh water for wildlife. These factors can also impact crop production, and where this results in reduced yields, this increases the need for agricultural intensification to meet demands, further impacting the farmland ecosystem.
Hopes for the future
A change in the way farmers receive subsidies may signal a shift away from a rather bleak picture for these habitats. Previously, farmers were paid grants based on how much land they owned and farmed. This encouraged them to use as much of their land for productivity as possible. Now, however, farmers will be paid for more sustainable practices instead. Under the Sustainable Farming Incentive, grants will be rewarded for restoration of non-crop habitats, the provision of resources for farmland species year-round and reducing the use of harmful pesticides.
The Autumn issue of Conservation Land Management (CLM) covers a variety of themes relevant to those involved in managing land for conservation, from the creation of bare ground habitats to incorporating climate objectives into the management of wildlife sites. Here, Assistant Editor Catherine Mitson provides a summary of the articles featured in this latest issue.
Ingleborough National Nature Reserve (NNR) covers a huge expanse of limestone grassland and pavement, acidic grassland, blanket bog and heath in the south-western Yorkshire Dales. Previously, the land had been grazed by sheep, numbers of which had doubled from the late 1960s to the 1980s while the number of cattle halved. The negative impact of sheep grazing was evident, especially in heavily-grazed areas where grasses dominated, and the only plants remaining in significant numbers were hardy species such as thyme, clovers and daisies. But an opportunity arose to reduce sheep numbers and to promote cattle grazing, and in this article Andrew Hinde, Peter Welsh and Bill Grayson describe the success of the reintroduction of cattle grazing to Ingleborough and outline the NNR’s conservation objectives going forward.
The next article brings us to Havergate Island in the Alde–Ore Estuary SSSI in Suffolk. Since 1997, spoonbills have been trying to colonise the estuary but breeding attempts failed, mainly due to the presence of and predation by foxes. But over on Havergate Island, a more secluded site with little human disturbance, spoonbill numbers were increasing. To encourage breeding on Havergate, RSPB set up elevated nesting platforms and, owing to the presence of foxes and other predators on the island, installed predator-exclusion fences. Vivienne Booth, Aaron Howe and Adam Rowland describe how the predator-exclusion fences were designed and installed, leading to the return of breeding spoonbills to Suffolk.
Christopher du Feu and Michael Gillman take us to Treswell Wood in north-east Nottinghamshire. In 2014 Nottinghamshire Wildlife Trust purchased an area of the wood that had previously been cleared for agriculture, known as the assart. Instead of planting trees, it was decided to let nature take its course and leave the assart to return to woodland naturally. Monitoring of woodland regeneration began in 2016, but in 2017 ash dieback struck the assart. In this article the authors report the results of this ongoing monitoring, and demonstrate the remarkable effect that ash dieback has had on natural regeneration.
With COP 26 fast approaching, many of us have noticed increasing news coverage of the climate and biodiversity emergencies. But on nature conservation sites, can climate objectives and biodiversity-related priorities co-exist? Heathlands, for example, are managed by techniques such as burning, a contradictory approach from a climate perspective. John Bacon addresses this dilemma, and takes a look at some initiatives in Shropshire to demonstrate how climate objectives are being incorporated into habitat management, with biodiversity still being the top priority.
The final article encourages us to appreciate the importance of bare ground habitats. Many species of spiders, ground beetles, wasps, bees and reptiles (to name a few) depend on the warm microclimate that bare ground provides for hunting, basking and nesting. Using examples from south Staffordshire, Katie Lloyd describes the process of bare ground creation, including the design, type and size of scrapes; how to maintain and manage newly-created bare patches; mitigation and other considerations to be aware of before undertaking such a project; and the benefits that this overlooked habitat provides.
In this and every issue you can expect to see Briefing, keeping you up to date with the latest training courses, events and publications, and On the ground which provides helpful tips or updates on products relevant to land management.
Other features that regularly appear in CLM include Viewpoint, a similar length to our main articles, but here authors can voice their own views on various conservation issues, and Review, which can include letters from readers or updates from our authors.
CLM is published four times a year in March, June, September and December, and is available by subscription only, delivered straight to your door. Subscriptions start from £22 per year. Previous back issues are also available to purchase individually (subject to availability).
If you are involved in a conservation project and think your experiences could be useful to other practitioners, we would love to hear from you. If you are interested in writing for CLM feel free to contact us – we will be happy to discuss your ideas with you.
In just a few weeks, the UK will host the UN’s 26th Climate Change Conference, COP 26, in Glasgow. In an editorial in the October issue of British Wildlife, David Stroud, former Senior Ornithologist at JNCC and co-author of International Treaties in Nature Conservation: A UK Perspective, describes the build-up to the conference and what we can expect from the event itself. The editorial is shared in full below.
Psychologists tell us that humanity evolved to focus on immediate threats – the sabre-toothed tiger lurking in a cave – rather than to ‘over the horizon’ challenges that will affect us only at some distant time in the future. That, at least, is the suggested justification for humanity’s failure to address seriously the problem of anthropogenic climate change over the last half-century, despite increasingly definitive evidence of the existential threat it poses. The frequency of extreme weather events in recent years, however, no longer allows lack of immediacy to be used as an excuse: from flooding and wildfire to sea-level rise, the consequences of climate change are apparent here and now and they are part of the lived experience of people across the world.
The effects of global heating are not restricted to weather catastrophes. As naturalists, we are ever-more familiar with changes to our flora and fauna, as documented elsewhere in this issue (pages 13–20) and previously in British Wildlife. This presents significant challenges to national conservation policies, which have traditionally relied on essentially static networks of protected areas and protected species lists. Despite the announcement of various welcome (but limited) projects, UK governments are yet to promote or implement climate-change adaptation at the scale required to make a meaningful impact.
In August, the Sixth Assessment of the Intergovernmental Panel on Climate Change (IPCC) provided the starkest of stark warnings yet (IPCC 2021). This report was described by the UN Secretary-General as nothing less than ‘a code red for humanity’ (UN 2021). He noted that the internationally agreed threshold of 1.5°C above pre-industrial levels of global heating is ‘perilously close… The only way to prevent exceeding this threshold… is by urgently stepping up our efforts, and pursuing the most ambitious path. We must act decisively now…’ With the 26th Conference of Parties (COP 26) of the UN Framework Convention on Climate Change (UNFCCC) soon to be held in Glasgow, the international community has an immediate opportunity to act on this latest science, and to use it as a solution. But will the response be adequate?
The nearly 30-year history of UNFCCC COPs is chequered and has been (rightly) dominated by issues of international development. Essentially, when the UNFCCC was negotiated, developing countries highlighted the need for developed nations – those with the largest economies and the greatest greenhouse-gas emissions – to take primary responsibility for the global issue they had (albeit unwittingly) created by more than two centuries of carbon-driven industrialisation. For this reason, the UNFCCC’s 1997 Kyoto Protocol (of COP 3) was framed on the basis of ‘common but differentiated responsibilities’, placing the primary obligation to address the problem on developed countries (it also, importantly, recognised the contributions to climate change of greenhouse gases other than CO2).
The UNFCCC’s 2015 Paris Agreement (COP 21) made the progressive step of moving away from Kyoto’s top-down assignation of national targets, and instead established a bottom-up approach to delivering objectives through ‘Nationally Determined Contributions’ or NDCs. In essence this allows each country to put on the table what it pledges to do, hoping that this is collectively adequate. Importantly, the NDC approach was agreed by, and thus brought on board, the developing countries – still recognising ‘common but differentiated responsibilities’ while acknowledging that low- and especially middle-income countries also have individual contributions to make to the global solution.
The human development needs of the poorest countries, however, are yet to be met, as recognised by the UN’s Sustainable Development Goals (SDGs). Thus, for affluent nations such as the UK there are actually two requirements for an effective Paris Agreement: not only to offer an adequate NDC, but also to contribute to the ‘financial mechanisms’ that allow developing countries to skip dirty, greenhouse-gas-emitting industry and move directly to green economies. ‘Resource mobilisation’ from the developed world will therefore be a central focus of COP 26.
Media commentators have been calling recently for binding quotas to be agreed in Glasgow. While theoretically desirable, this will not happen and it misunderstands the complexities of the global political process. Should there be a World Government at some point, such a prescriptive approach might be achievable – but for now it lives in fantasyland (along with alternative economic systems). The reality is, regrettably, much messier and is here for the foreseeable future.
At COP 26, the UK has a unique responsibility to ensure a successful outcome. Not only does it have to contribute an NDC of significant ambition as one of the world’s largest economies, but as conference chair the UK has a crucial cheerleader role, with an onus to encourage all other countries to deliver ambitiously, too. Decisions at the COP will, as is the norm for such meetings, be taken by consensus, which leaves a real risk of lowest common denominator decision-making because all countries effectively hold a veto. The role of the UK diplomatic services here is critical to build momentum, impetus and pressure (as was that of France ahead of 2015’s COP 21). They also have a vital job in gaining prior intelligence from other countries and working to fix problems and issues ahead of time through face-to-face dialogue in other capitals. As at all intergovernmental COPs, most of the content of decisions is developed well beforehand, while the conference itself is used to finesse the details and formally sign off the final texts. With (we hope) all 197 Contracting Parties attending and just a few days available together in Glasgow, there is no time to do otherwise.
Parties will already have prepared their broad national negotiating positions over the course of the last year, not least because for a meeting of such significance these will typically need to be agreed by the head of government. Many parties work together, giving them greater collective influence. National positions further evolve within regional and other negotiating blocks, including the 27 member states of the EU; the G77 (a coalition of 134 developing countries) and China; the African Group; and the multiple Small Island Developing States which, faced by pressing existential impacts from rising sea levels, have become an increasingly influential political force in climate negotiations.
Yet ultimately, while civil servants can prepare much of the ground, at the COP the tough, final negotiations and trade-offs will be undertaken by heads of government and their ministers. In this, simple peer pressure is important: no national politician likes to be presented as internationally unambitious. And personal relationships, as in any negotiation, are key to success.
Public pressure can also play an essential role by creating a political climate in which it is easier to commit to difficult things when they are presented as ‘the desire of the people’. The last few years of school strikes and other radical actions have demonstrated great public concern, rendering it increasingly difficult, for European leaders at least, not to engage. Hence, the environmental community has an important lobbying role, reminding politicians of what is expected from them, not just ahead of the COP but crucially after it as well, and holding governments globally to account. Commitments are easy to make, but also easy to forget (especially when they involve tough policy changes), and an important agenda item at COP 26 will be the first global stocktake on progress in implementing the measures agreed in Paris.
Beyond governments, contributing to the necessary profound societal change involves all of us. The latest form of climate-change denial is to accept the reality but to make no consequential alterations to one’s lifestyle: ‘business (and life) as usual’. Yet everyone will need to make changes – not least to rediscover the much-anticipated (but so far elusive) ‘new normal’ that was predicted to emerge from the Covid-19 pandemic. This will include switching urgently to more sustainable modes of transport, insulating our homes, changing diet and, critically, reducing consumption and having simpler lifestyles: buy less and live more. In promoting such behavioural changes, the environmental community has an important leadership role within society. Gandhi stressed the need to ‘be the change you want to see in the world’. Exactly.
Subscriptions to British Wildlife start from £35 – for more information or to subscribe, visit the website. Individual back issues are available to purchase through the NHBS website.
Across the world, there have been significant declines in butterfly and moth populations. Since 1976, 76% of UK butterfly species have seen a decrease in abundance or distribution, with the abundance of larger moths declining by 33% since 1968. This trend is echoed across UK biodiversity, with 41% of all UK species declining since the 1970s. Butterflies and moths are clear indicators of the broader health of the environment; their decline is a stark warning about our natural world.
The UK has 59 butterfly species, 57 of which are resident. There are around 2,500 species of moths in the UK, split into two groups: larger macro-moths and smaller micro-moths. Almost 70 species of butterfly and moth have become extinct in the last 100 years. A variety of threats have contributed to these extinctions and the general decline of other species, including the destruction of habitats and major land-use changes, such as the intensification of agriculture. Climate change, chemical pollution and artificial light at night have also all be identified as threats to UK populations.
Butterflies and moths have an intrinsic value in their own right, but they are also an important component in many ecosystems. They provide environmental services, including pollination and pest control and are prey for many other species, such as birds, bats and other insectivores. Butterflies and moths are also important ‘model’ organisms, used for centuries to investigate different areas of biological research and are key to understanding many diverse fields, such as pest control, mimicry, genetics and population dynamics.
The Big Butterfly Count 2021
Butterfly Conservation, a UK nonprofit environmental charity, is determined to reverse this decline. Their vision is a world where butterflies and moths thrive and can be enjoyed by everyone, everywhere. To help with the assessment of the health of our environment, Butterfly Conservation runs an annual nationwide citizen science survey, the Big Butterfly Count. Launched in 2010, it is the world’s biggest survey of butterflies.
Big Butterfly Count 2021 ran between 16th July and 8th August (read our blog to see how our NHBS staff got on this year). The results of this count showed that the overall number of butterflies recorded per count is at its lowest since the event began. Over 150,000 counts were registered this year, more than ever before, but the results showed that the populations of some of our most-loved species, such as the peacock butterfly (Aglais io), are suffering. Luckily, it’s not all bad news, as some species, such as the marbled white (Melanargia galathea), appear to be bouncing back from last year’s low numbers. But the significant, long-term decline of many butterfly and moth species in Britain is alarming.
Butterfly Conservation’s new strategy
In their new 2021-2026 strategy, launched in October 2021, Butterfly Conservation outlines a bold, ambitious road map to bringing abundance back to nature. After 16 months of reviewing their position in butterfly and moth conservation, they have defined three new strategic goals:
Reduce the number of threatened species of butterflies and moths by half,
Improve the condition of 100 of the most important landscapes for butterflies and moths,
Transform 100,000 wild spaces in the UK, not just for butterflies and moths, but also for people.
To help them deliver their strategic goals, Butterfly Conservation have five initiatives. The first initiative is focused on recovery, through refocusing their science program to increase the understanding of why species are declining and how to recover their populations. They will also establish a new Threatened Species program, which will target conservation action for 65 species at serious risk. Butterfly Conservation will also expand their monitoring program to follow species recovery and gather data on a country-wide level. By 2026, they hope to have increased their species recovery actions by 65%.
The second initiative aims to inspire and enable more people to enjoy the natural world by improving access to learning, particularly for younger audiences. The third initiative is focused on uniting for wildlife, and the fourth is to tackle the threats species face, such as artificial light at night. They’ll achieve these goals by collaborating with a network of supporters and increasing their investment in research by 80% to establish five habitat quality indicators to better understand the impact of conservation work or policy changes. The final initiative focuses on managing land sustainably, by creating a land management advisory hub and delivering and demonstrating best practice land management for butterflies and months across landscapes.
Butterfly Conservation believes that the next five years are key and, through their bold new steps to conserve butterflies and moths, they can help to restore biodiversity, mitigate the climate crisis and start to rebuild the relationship between us and the natural world.
The next habitat we will be exploring in our Introduction to Habitats series is urban and suburban habitats. These are extremely diverse, from parks, gardens, cemeteries and bare ground to highrises, bridges, landfills and houses. Due to this wide diversity, urban habitats are often extremely fragmented, with small, isolated patches surrounded by unsuitable areas. These patches are also often highly disturbed, by light, people, pets, cars and other anthropogenic activities. Some species also have to deal with reduced availability of food, due to the limited plant life, and fewer nesting and breeding spaces. Much of the surfaces in the urban environment have been altered, covered in concrete, roofing tiles, and tarmac. This changes the amount of rainwater that can infiltrate the soils underneath, as well as how much heat from the sun is absorbed. The temperatures can be higher in urban areas, particularly when there is little to no tree coverage to provide shade.
To survive in an urban environment, species must be adaptable. Many studies have found key behavioural and physical differences between urban and rural dwellers of the same species. For example, birds have been found to sing higher, longer and louder in cities than in the countryside. Generalist species are more likely to be able to exploit these habitats as they can occupy wider ecological niches. Specialist species can have more restricted diets or need more specific conditions to develop or reproduce, making them less able to adapt to changing environments. Those able to transition from natural to man-made habitats, however, may actually see large fitness benefits, due to fewer predators and, for some species, abundant food supplies.
Gardens and public green spaces can often be a refuge for many urban species, providing food, shelter and protection from other disturbances. But overly manicured gardens and parks do not provide the resources necessary for many species to survive. Wildflowers, hedges, shrubs, trees and other native vegetation are needed to boost insect numbers, along with limiting the use of harmful herbicides and pesticides. Many other species rely on insects for food, and so increasing insect populations benefits other species throughout the food web.
What species can you find here?
Flora:
Cow Parsley (Anthriscus sylvestris)
This species is a member of the carrot family and is commonly found on verges, hedgerows and less intensively-managed green spaces, with a preference for shaded habitats. It is a fast-growing plant, that appears in the summer before dying back, and its white flowers are clustered together in an umbrella-like shape. They are a great food resource for many invertebrate species, as well as for rabbits. There are several similar-looking plants, including the poisonous hemlock (Conium maculatum), although hemlock has distinctive purple blotches on its stem.
Three-cornered Garlic (Allium triquetrum)
This is an invasive species, often found along verges, roadside banks, hedgerows and on waste ground. It can form dense colonies and are spread naturally by ants. Its white flowers have a green stripe on each petal and a garlic/oniony smell. They are edible, tasting similarly to spring onion or chives.
Common Chickweed (Stellaria media)
This plant has multiple common names, including chickenwort, maruns, craches and winterweed. They form large mats and are found in many gardens and fields. It has one line of fine hairs on its stem, with oval leaves and small white flowers. Chickweed was used in folk medicine as a remedy for pulmonary disease and several itchy skin conditions. It is even prescribed today by modern herbalists for many other conditions, although not all these uses are supported by scientific evidence.
English Ivy (Hedera helix)
This is a climbing plant that can often be found on walls, buildings, trees and other man-made and natural structures. It is an evergreen species that can also grow as groundcover when there are no vertical surfaces. The flowers are a greenish-yellow colour and the fruits, which ripen in late winter, can vary in colour from purple-black to orangy-yellow. They are an important food source for many insects and birds, particularly in autumn and winter, and their foliage is also browsed by deer.
Fauna:
Feral Pigeon (Columba livia domestica)
There are several species of pigeon in our urban areas. Feral pigeons, also known as city or street pigeons, are descended from the domestic pigeon, a subspecies derived from the rock dove (Columba livia). They have substituted their natural habitats of sea cliffs with ledges on buildings and other man-made structures. They have a wide variety of colours and patterns compared to the rock dove, but urban pigeons tend to have a darker plumage compared to individuals in rural areas.
Red Fox (Vulpes vulpes)
An iconic urban species, the red fox is one of our largest land predators. Usually living in groups or pairs, they feed mainly on small mammals and birds, but also amphibians and fruit. In urban areas, they are very successful scavengers, helped occasionally by people who leave food out for them. They are more common in less dense suburban areas but have been found right in city centres. It is thought that the movement between urban and rural fox populations is quite fluid.
European Hedgehog (Erinaceus europaeus)
Another iconic British species, the hedgehog has seen severe population declines, though true population estimates are difficult, due to the lack of data and their elusive nature. In the 1950s, population estimates put the number of hedgehogs in the UK at 36.5 million (although this is not thought to be accurate), which is now thought to have dropped to 1.55 million by 1995. It is believed that populations are still declining, but there are still no reliable methods for estimating the true numbers. They face several threats, including habitat loss, chemical use in gardens, cars and a drop in invertebrate populations.
Peregrine Falcon (Falco peregrinus)
This bird of prey is not only the fastest bird in the world, but also the fastest member of the animal kingdom, clocking up a dive speed of over 320km/h. Their populations suffered after decades of persecution and pesticide use, but their numbers have begun to recover. They nest in tall buildings, bridges and pylons, and prey mainly on pigeons but also collared doves, blackbirds and starlings.
Garden Snail (Cornu aspersum)
A wide variety of invertebrates can be found in urban and suburban habitats, particularly gardens and parks. The garden snail is a common visitor to our lawns, plants and vegetable patches. They’re often considered a pest due to the damage they cause to leaves and fruits but they play a vital role in the health of our soils. They help decompose plant matter, allowing for the cycling of nutrients back into the soil. Snails are also an important food and calcium source for many animals, such as birds.
Urban and suburban environments are also home to many garden bird species, as well as bats, butterflies, moths and spiders. For more information on these, check out some of our guides to UK species identification.
Threats
Urban and suburban areas are becoming more and more densely inhabited as more of the UK’s population moved into towns and cities. This increases the levels of disturbance, from more cars on the road, more noise, light, waste, pets and people. Higher disturbances decrease the ability of species to survive, as they are less likely to feed, develop and reproduce successfully. It can also increase the likelihood of direct mortality.
With a rising human population is an increasing need for more housing and infrastructure. Consequently, this reduces the amount of undeveloped and semi-natural areas; fewer green spaces and the over maintenance of gardens and parks are serious threats to biodiversity in urban habitats.
Public opinion can also threaten urban wildlife. Many species that have managed to colonise the urban environment are considered pests and there are often calls to eradicate them. Fox culls are a controversial suggestion, with many people wanting a way to control the populations and reduce the damage they cause, while others are concerned with animal rights. Additionally, there are suggestions that culls are ineffective, as removed foxes are often replaced by another individual, with no change made to urban population numbers.
What can you do to help?
There are several simple steps you can take to help improve urban biodiversity. You could plant more native plants, reduce the chemicals you use and decrease how often you mow your lawn. Placing bird feeders, nests, and other shelters are also ways that can help wildlife. On a bigger scale, you can urge your local council and government to help too. They could increase the areas of green space and tree cover, and manage roadside verges with nature in mind. Another important step is to decrease light and noise pollution. With some simple steps, we can help to increase the suitability of urban habitats for many wildlife species.
In our new NHBS Introduction to Habitats series, we will be exploring the various habitats found in the UK. In this article, we will take a look at the first habitat of the series, heathland and moorland. Featuring prominently in famous novels such as Wuthering Heights by Emily Brontë and The Return of the Native by Thomas Hardy, heathland is a unique habitat. Originally manmade, it is a product of agricultural grazing and tree clearing practices originating thousands of years ago. Unlike the heathland in countries such as Australia and South Africa, European heathland is relatively low in flora species variety. It is characterised by heather species (Family Ericaceae), but also other plant species such as gorse (Ulex spp.) and bracken (Pteridium spp.).
As this habitat is manmade, it requires management to be maintained. This usually involves a variety of methods such as using grazing animals, removing older species and trees, and controlling the encroachment of scrub. They can even be managed by controlled burning. If neglected, the heathland would be overtaken by successive species and become woodland.
There are several different types of heathland, depending on physical factors such as soil drainage, terrain, and altitude. These types include lowland, chalk, and wooded heath. Lowland heath can be further divided into wet, dry, and humid heath, and upland heath is more commonly known as moorland. The types of species found can vary between these habitats.
What species can you find here?
Flora:
While there may not be a large variety of flora, the species present all play important roles within the habitat. There are also some iconic species within the heathland.
Bell Heather (Erica cinerea)
Between June and September, bell heather blooms across the heathland, creating a blanket of purple. This species is an important nectar source for many invertebrate species, such as the buff-tailed bumblebee (Bombus terrestris) and the silver-studded blue butterfly (Plebejus argus).
It is similar to another heather species, cross-leaved heath, but the flowers of the bell heather are smaller and occur around the stem, rather than clustered on one side.
Common Gorse (Ulex europaeus)
Flowering from January to June, this bright yellow plant provides an early source of food for many invertebrates. As a large evergreen shrub, it also provides shelter for many species, including Dartford warblers (Curruca undata) and linnets (Linaria cannabina).
Common gorse is also very similar to two other gorse species, western (Ulex gallii) and dwarf (Ulex minor). The easiest way to identify the species is by the time of year that they flower and their height, as common gorse grows much taller and can reach up to 2.5 metres.
Common Bracken (Pteridium aquilinum)
The UK’s most common fern species, it grows in dense groups on heathland and moorland. A bright green during spring and summer months, this species dies back in winter, creating a sea of brown fronds. Bracken is poisonous to grazing livestock, therefore it needs to be cut back to maintain heathland habitats. If left to grow, it can dominate the habitat and out-compete other plant species, such as bell heather, for nutrients, light, and water.
Heath Bedstraw (Galium saxatile)
Heath bedstraw is a mat-forming herb found in heathland habitats. It is a fairly common species, found widespread across most of the UK. The white petalled flowers bloom between June and August. This species is a key food source for Britain’s only true alpine butterfly species: the small mountain ringlet (Erebia epiphron).
Key identifying features of heath bedstraw are its square, hairless stem and its white, four-petal flowers that give off a sickly, unpleasant smell.
Fauna:
Heathland supports a large variety of species, particularly invertebrates, but also birds, mammals and reptiles. Several rare species present here are hardly found in any other habitat.
Silver-Studded Blue Butterfly (Plebejus argus)
This species is found mainly in heathland, chalk grassland, and sand dune habitats, and is almost entirely restricted to southern England. It is a rare species, with the adults appearing between July to September.
This species is sexually dimorphic, meaning the males and females look different. The males (pictured) are blue with a darker border, while the females are brown with red spots along their border. Both have the pale fringe to their wings.
Golden-Ringed Dragonfly (Cordulegaster boltonii)
This species, found in heathland, freshwater, and wetland habitats, is easy to identify, due to its distinctive yellow and black markings. Their larvae are aquatic, and so rely on streams or standing water within the heathland to breed. While voracious predators in their own right, they are also an important food source, along with other dragonfly species, for many nesting birds such as the hobby (Falco subbuteo).
Dartford Warbler (Silvia undata)
The Dartford warbler suffered a population crash in the 1960s but has since begun recovering. It is a ground-nesting bird, living on lowland heath and relies on gorse for a protective covering. Within the UK, this species is also mostly restricted to southern England. However, there are populations of this species within western Europe, particularly within the Iberian peninsula.
Stoat (Mustela erminea)
The stoat, also known as the short-tailed weasel or Eurasian ermine, is a small member of the mustelid family, related to otters (Lutra lutra) and the very visually similar weasel (Mustela nivalis). While stoats are slightly larger, the key to discerning this species from the weasel is the tail – stoats have a longer tail with a black tip.
Lack of management is one of the main threats that heathland faces. This habitat needs variety, for example, dry heath, wetter areas such as bogs and ponds, patches of older vegetation, and areas of bare, sandy ground. This all improves the biodiversity of the area and helps to strengthen the ecosystem. Without management, these areas could all be taken over by scrub and tree cover.
Clearing for urban development, ploughing, and quarrying also threaten this habitat, and are some of the main causes of heathland loss over the last few decades. Further threats include the expansion and planting of forests, overgrazing, and uncontrolled fire.
More than 80% of heathland in the UK has been lost during the past 150 years, but widespread conservation efforts hope to reverse this. The UK Biodiversity Action Plan, for example, aims to restore 58,000 hectares of heathland, with further plans to recreate 6,000 hectares.
Areas of significance:
Upland heathland or moorland:
– Exmoor, Dartmoor, and Bodmin Moor
– Pennines
– Brecon Beacons
– Other areas such as Yorkshire, Northumberland, Greater Manchester, and the Peak District.
Lowland heathland
– The New Forest
– Ashdown Forest
– South Purbeck Heaths
– Other areas such as Cornwall, Devon, Surrey, and Pembrokeshire