Dairy farm creating a buzz

Authors: Gethin Davies (RSPB), Anna Hobbs (BBCT), Stuart Taylor (farmer, Argoed)

Dairying can be a challenging sector for farmers and wildlife. Small margins have driven increasing scale, efficiency and specialisation, which has tended to squeeze out people and space for nature. The number of dairy farmers in the UK has declined by two thirds since 1995.

Argoed Farm in North Wales showcases an alternative vision for dairying, one where nature and minimising environmental impacts are at the heart of the system.

Farming at Argoed

Argoed has been in the family of Stuart Taylor for more than 100 years. He farms it with the help of Robert and Owen Evans who have worked with him for over 20 years. As its current custodian, Stuart feels a strong responsibility to farm it well, and this extends to the farm’s natural environment, from its soil to the wildlife that share the fields overlooking the town of Mold in North Wales. This was a driver for converting to organic in 2000. The 68 hectare farm currently milks around 65 cows, selling milk through the Calon Wen organic dairy co-operative.

'Adopting a low input approach across the whole farm not only allows more space for nature to thrive – it’s also a more cost-effective way of farming.' Stuart Taylor

Stuart has kept faith with the traditional British Friesian cow. They average 6 to 7 lactations (around double the industry average), have excellent fertility and suit his focus on producing milk from grazed grass and conserved forage as he looks to minimise bought-in concentrate feed. The farm used to grow cereals in a rotation with grass but has moved to maintaining the whole farm as permanent grassland, with grass reseeding done by over-sowing into a minimally disturbed soil surface. He feels this brings more resilience to the system with the increasingly unpredictable weather making bare ground at reseeding a challenge.

Stuart has always tried to fit in wildlife conservation measures where he can, such as restoring hedgerows, digging ponds and putting up nest boxes. Recently, along with other Calon Wen farmers, he’s been working with the Bumblebee Conservation Trust and the RSPB on the Pasture for Pollinators project, which trialled simple grassland management changes to boost pollen and nectar resources for bumblebees and other pollinators.

'As a farmer it’s my responsibility to look after nature and the environment on the farm as best as I can whilst I’m here.'

This project showed Argoed to have a wealth of habitats on the farm, providing the foundations for a rich food web. Although the farm is visibly nature-friendly, we wanted a way to objectively illustrate why and how Stuart’s system delivers for wildlife.

Herb-rich grasslands underpin milk production on Argoed. Image (c) Anna Hobbs

How ‘Fair to Nature’?

We tallied all the various opportunities for nature on Argoed against the criteria of the Fair To Nature standard. This looks at the percentage of the farm delivering the Farm Wildlife key actions, accounting for both non-farmed habitats such as hedgerows and ponds as well as in-field nature-friendly cropping and grassland practices. This information also provides a means to benchmark a farm’s habitat delivery over time, and potentially, with other similar farms.

Established wildlife habitats

Well-established farmland habitats are often the most wildlife-rich. On Argoed, this included a network of dense hedgerows, some small areas of woodland and scrub, and around 3ha of species-rich grassland.

Stuart believes the area of species-rich grassland hasn’t been ploughed for at least 120 years, but did receive inputs of slurry and fertiliser into the 1980s. In the last few decades he has been managing it as a hay meadow and inputs have been restricted to composted farmyard manure. He has seen plant diversity increase and the area now includes abundant ribwort plantain, yarrow, vetch, trefoil and black knapweed, with the occasional orchid starting to appear. The hay is a valued feed for the farm’s youngstock.

The field boundaries are predominantly multi-species hedgerows with many hedgerow trees, both developing and mature. Stuart trims the hedges rotationally to increase flowering and fruiting, and into a dense A shape between restoration events to provide abundant shelter and wildlife habitat.

Dense rotationally trimmed hedgerows provide corridors for insects and other species. Image (c) Stuart Taylor

Although outside the farmed area, a small traditional orchard and farm garden provide early blossom and a wide diversity of flowering plants to help pollinators obtain a continuous source of food. Wet features on the farm include three ponds, two holding water for most of the year, the other seasonally.

Flower and seed-rich habitats within the farming system

As Argoed is organic, there is a need for leguminous plants to bring nitrogen into the farming system. Stuart has been increasingly sowing diverse legume and herb mixes into his grassland, and these provide an excellent source of pollen and nectar for insects if the grazing and mowing management allows them to flower. Such grassland can be included within ‘Fair to Nature’ with a conversion factor, since the wildlife benefits, although positive, are lower per hectare than semi-natural habitats or those created primarily for nature conservation.

Grazing practices allow plants to flower and seed. Image (c) Stuart Taylor

Around 42ha of grassland is periodically over-sown with a herbal mix containing a variety of grasses along with red, white and alsike clover, ribwort plantain and chicory. This grassland area is rotationally grazed or mown for silage, where three cuts are taken with a forage wagon. Having both white and red clovers in the sward caters for both short- and long-tongued bumblebees.

The ‘Pasture for Pollinators’ project trialled leaving unmown strips in the herbal leys to extend the flowering period. If such margins are not left, widescale silage cutting can mean the local landscape can go from ‘feast to famine’ for insects overnight.

Uncut herbal mix strip. Image (c) Anna Hobbs

Bumblebee Conservation Trust surveys identified all Big 7’ widespread bumblebee species to be present on the farm, along with a diversity of other pollinators. In addition to abundant flower-rich habitat, the farm also provides good nesting opportunities for bumblebees and other pollinators through tussocky grass, bare earth in sunny locations on tracksides and field edges, and some dry-stone walls.

Common carder bee. Image (c) Anna Hobbs

Beyond the 3ha of semi-natural grassland, there is another 9ha of long-term permanent grassland that isn’t over-seeded, some parts of which contain a high diversity of flowering plants, including yarrow, self-heal, lesser trefoil, sheep’s sorrel and finer grasses such as sweet vernal. Some of this land is grazed with youngstock and some is made into hay, weather permitting. This area was counted with the legume-rich grassland at a corrected value, rather than as semi-natural, but with ongoing appropriate management this can change in future.
A total of 7.8% of the farm is made up of a variety of well-established semi-natural habitats. The main area of productive but also wildlife-friendly grassland management contributed significantly, bringing the total for the farm to around 23%. Research has shown that if between 10% and 20% of farmland can be managed in a diversity of high-quality habitats, it will provide a major buffer to the negative effects caused by increasing agricultural productivity.

Nature-friendly Argoed

‘In the past, wildlife was a by-product of farming, but farmers now have to make a choice of how nature-friendly they want to be.’

Argoed highlights that despite the immense pressures in dairying, we still have wildlife-friendly systems to champion. We need future agricultural policy to better support farmland habitats and nature-friendly practices for the many public goods they provide and help farming deliver them at scale. But perhaps the most important way we can support nature-positive food producers like Stuart is to buy their produce, giving confidence for more farmers to do similar, and drive the creation of landscapes where farmland wildlife can thrive.

------------------------------------------------------------------------------------------------------------------------

Fair To Nature habitat requirements

All Fair to Nature farms manage at least 10% of their farmed area in a range of wildlife habitats based on the following specifications:

• Existing wildlife habitats – including native woodland planted on farmland since 1992, semi-natural grassland, heathland and other high nature value habitats – no minimum (contributes towards the 10%)

• Flower-rich habitats – minimum 4%

• Seed-rich habitats – minimum 2% (not obligatory on farms with less than 10% cropped land)

• Wildlife-rich field boundaries and margins – minimum 1%

• Wet features – one feature per 100ha, average size 25m2 (area contributes towards the 10%)

These specifications are based on the Farm Wildlife partnership’s key actions for farmland wildlife. Several habitats have a conversion factor since the wildlife benefits, although positive, are lower per hectare than semi-natural habitats or habitats created primarily for nature conservation.

New research: What limits bumblebee populations on farmland?

Authors: Dr Tom Timberlake and Prof Jane Memmott 

A new study by Tom Timberlake and colleagues at the University of Bristol shows how important late summer flowers and rural gardens can be for supporting bumblebees on UK farmland.

Does this offer an opportunity to devise more targeted agri-environment schemes for pollinators?

Pollen and nectar are the main source of food for bees, including the charismatic and agriculturally important bumblebee. It is no surprise then that declining flower densities – particularly on farmland – are considered one of the most important drivers of pollinator decline. Agri-environment schemes which incentivise the planting of wildflower strips and the expansion of semi-natural flowering habitats such as hedgerows and field margins are an important tool for reversing pollinator declines, but are they really the most efficient way of supporting pollinators?

Image 1: For bumblebees like this one (Bombus terrestris), it’s not just about how much food is available, it’s also when that food is available through the year. A dandelion flowering in early spring for example, would be more valuable to a bumblebee than an equivalent flower in mid-summer.
Image: T. Timberlake

Whilst agri-environment schemes have successfully increased the overall numbers of flowers on farmland, they tend to overlook the timing of when these flowers are available to pollinators. Different plants flower at different times and most of the plants in agri-environment schemes flower in late spring and early summer which often isn’t the period of greatest need for pollinators. Pollinators need a continuous supply of food throughout their flight season, and for species with long flight seasons such as bumblebees, this means from late February, right through until October. ‘Hunger gaps’ of even one week could limit the number of pollinators surviving through the year.

Hunger gaps

To support pollinators in the most effective and cost-efficient way, it makes sense to find out when these hunger gaps occur and then devise targeted management or planting schemes to plug these gaps. A previous study by our team did just this and showed that nectar supplies on farmland were most limited in early spring (March) and late summer.

To check what effect these ‘hunger gaps’ were having on bumblebee populations, we carried out a study on 12 farms around the west of England. We captured, recorded and released hundreds of bumblebees and then measured all sorts of features of the farms to find out which aspects of the farm were most important in determining bumblebee density.

To our surprise, the supply of nectar in late summer (September) was by far the most important factor driving bumblebee density on these farms – more so even than the amount of natural habitat. Late summer is a very important stage in the lifecycle of bumblebees – it is when new queens are produced and must pile on the pounds before their winter hibernation. A rich supply of flowers is therefore crucial, but with fewer and fewer hay meadows, cover crops and weedy areas to provide this late summer nectar on farmland, bumblebees are struggling.

Image 2: Low nectar supplies in late summer coincide with an important stage in the colony lifecycle, limiting colony density the following year. How might we change the shape of this curve to reduce the September bottleneck?

How to plug the gap

So what can we do to plug this late-summer hunger gap on farmland and support bumblebees? On our farms at least, ivy was the most important plant for providing nectar during this sparse time, so managing your hedgerows and woodland edges to promote this amazing plant is a good first step. Leaving some rough weedy corners for late flowering species like thistles, knapweed, scabious and dandelions can also contribute to plugging the gap.

We found that Environmental Stewardship Scheme pollen and nectar mixes were really effective at increasing overall nectar supplies but were far more effective when mown early, or in multiple phases, to extend flowering into the late summer.

Finally, if you want to give those hungry queen bumblebees a real treat in the run-up to autumn, a tasty cover crop of late-flowering red clover would do just the trick. A single hectare of this crop could provide around 1 kilogram of raw nectar sugar each day and completely close the late summer gap.

There was one final surprise in our results… Small patches of garden were having a significant influence on the density of bumblebees. Farms with more gardens had more bumblebee colonies.

Gardens have a far denser and more diverse supply of flowers than farmland and are often managed to keep things flowering throughout the whole year. These little floral oases seem to be throwing bumblebees a lifeline during periods when farmland offers very little.

Image 3: Species which flower in September such as dandelions, red clover, ivy and thistles (clockwise from top left) are likely to be disproportionately important to bumblebees and other pollinators. Including these and other late-flowering species in conservation schemes will help fill the late summer hunger gap.
Images: T. Timberlake & Wikimedia Commons

How much and when

The take home message is that it’s not just about how much food we provide for pollinators, it’s also about when that food is available through the year.

Providing more flowers in the early spring and late summer when bumblebees are at their hungriest is a great way to support these important creatures.

Image 4: Some examples of low quality (left) and high quality (right) farmland habitats for pollinators. The more diverse and flower-rich high quality habitats tend to provide a more consistent supply of nectar through the year, helping to fill those important hunger gaps.
Image: Nick Tew

This article is the summary of a University of Bristol-led research paper published by Thomas Timberlake, Jane Memmott, Ian Vaughan and Mathilde Baude in the Journal of Applied Ecology. The work was funded by the Natural Environment Research Council (NERC) with additional support from the NERC Biomolecular Analysis Facility.

Case Study: Managing Farmland for Grey Long-eared Bats

Author: Craig Dunton, Grey long-eared bat Project Officer, Bat Conservation Trust

Species: Grey Long-eared bat:

© Craig Dunton/www.bats.org.uk

 

Why is farmland important for this species?

With as few as 1000 individuals In the UK, the grey long-eared bat is one of our rarest mammals. Their distribution is restricted to the southern coast (Devon, Dorset, Somerset, Hampshire, Isle of Wight and Sussex) and there are only 9 known maternity colonies; meaning that this species is on the brink of extinction in this country. Currently, work is being carried out to conserve this species as part of 'Back from the Brink' – a Heritage Lottery funded conservation project aiming to save 20 species from extinction. https://naturebftb.co.uk/

Farmland is vitally important to all bat species. 70% of land in the UK is used for agriculture, so for very mobile species that utilise the whole landscape, farming practices can have significant impacts on bat populations. Some bat species are more resilient than others, but for those that have very low populations, are particularly sensitive to light and disturbance, and have very specific habitat requirements, there are significant threats to their survival.

Like all bats, the grey long-eared bat needs some key elements throughout its range in order to survive and thrive.

Roosts: Bats utilise a wide variety of structures to roost in, as their requirements change throughout the year. Roosts are needed for different activities – hibernation roosts, maternity roosts, night feeding roosts (for some bats) – these are all needed at different times of the year, and different bat species choose different structures for different activities.

Many bats hibernate underground, using caves, mines, cellars and tunnels that have a cool and constant temperature that bats need to hibernate. Many farms have these types of features, so it is important to be aware of their importance for bats. Some bats roost in a variety of different tree features; cracks, splits, woodpecker holes, loose bark – so it is important to retain trees that have ‘interesting’ features.

Grey long-eared bats are mostly associated with man-made roosts – usually the roof spaces of large, traditional, stone buildings with slate roofs. There are some records of them using caves and rock crevices, but no records of them using bat boxes in England.

Many buildings on farms can provide important roosts for grey long-eared bats, particularly large stone buildings with slate roofs and large, open roof voids. These can provide vital maternity roosts, temporary day and night roosts and opportunities for hibernation. As all bat species are protected, if you are planning to carry out any work that might impact bats or their roosts, the National Bat Helpline will point you in the right direction, please email enquiries@bats.org.uk

Foraging sites: As with roosts, different species of bats have different types of habitats that they favour for foraging. All UK bat species are insectivores, and depending on their size, flight habits and other physical adaptations, different species need different insect prey and therefore different habitats for foraging in. Greater horseshoe bats are large bats and so favour large prey, particularly around the maternity period. Cockchafers and dung beetles are their food of choice. Daubenton’s bats are often seen foraging over water, trawling insects from the surface of the water with their specially adapted, large hairy feet.

© Craig Dunton/www.bats.org.uk

Grey long-eared bats have a close association with unimproved lowland grassland and riparian (wet) habitats such as meadows and marshes.

Managing permanent pasture more extensively with very low or no inputs will benefit grey long-eared bat populations, offering more opportunities for invertebrates including the moths and craneflies that grey long-eared bats favour. Managing land to maintain or increase species diversity (more flowering plants) as well as structural diversity (a range in sward height), will give insects food and shelter resources. If possible, consider transitioning land back to hay meadow management as opposed to silage production, as this allows insects and plants to complete life cycles and thrive.

In terms of cultivated land, increase pollen and nectar plots and wildflower margins, and manage by cutting or grazing to maintain plant diversity. These areas alongside trees and tall hedgerows have proven benefits for some bat species. Minimise pesticide use and consider crops that contain lots of flowering plants such as herbal leys.  Within arable land, conservation headlands or low input cereals can be beneficial if management results in increased invertebrate numbers. These are all ways of increasing foraging opportunities on less productive areas of land for grey long-eared (and other) bats.

Farming organically has many advantages, including huge benefits to biodiversity, natural resource protection and reducing greenhouse gas emissions. Following organic principles should be considered if aiming to encourage bats and other biodiversity.

Connectivity: For so much of our wildlife, good habitat connectivity is critically important. Linear features in the landscape such as hedgerows, watercourses and ditches, enable different species to flow freely through the landscape, enabling opportunities for feeding, interacting and breeding. For bats, good connectivity is vital, as many bats use linear features to navigate through the landscape, using their echolocation to move from roosting sites to foraging sites. When these features are well managed, they can also provide foraging opportunities as well as providing obvious features to allow free movement. Extensive hedgerow management (2-3 year cutting cycle) allows hedgerow plants to flower and fruit, providing vital resources for insects. Buffer strips along streams and rivers not only provides increased opportunities for foraging, but can also protect watercourses from nutrient and pesticide run off, protecting aquatic flora and fauna.

For more information on land management for grey long-eared bats contact Craig Dunton (Grey long-eared bat project officer) on cdunton@bats.org.uk

 

 

 

Case Study: Adding Value to Chalk Grasslands: Creating Chalk Banks to benefit butterflies and other insects.

Author: Lynne Roberts . Farm: The RSPB’s Manor Farm, Newton Tony, Wiltshire

Aims and setting:

Manor Farm is a 296 ha working farm strategically placed between two of the largest tracts of semi-natural chalk grassland in the British Isles – Salisbury Plain and Porton Down. The RSPB purchased Manor farm in 2006 and have been reverting former arable land back to species-rich chalk grassland to create a landscape-scale stepping stone between these two areas.

Whilst this reversion has been very successful in establishing flower-rich grassland, even after several years the ex-arable fields still have unsuitable soil conditions for the plant species typical of very thin, nutrient-poor chalky soils. The fields are also rather flat as a result of historical cultivation, lacking the humps and hollows of natural grassland which help to create a variety of microclimates for a wider range of plants and insects.

For these reasons, in 2013 it was decided to create two large mostly south-facing banks to support viable populations of species characteristic of thin, chalky soils. Butterfly banks and scrapes can provide ideal conditions for butterflies, with sheltered sunny spots and bare ground for basking, alongside a mosaic of nectar-rich flowers for foraging adults and specific foodplants for growing caterpillars.

Funding for the creation of the banks was provided by the SITA Trust (now SUEZ) “Conservation of the small blue butterfly at RSPB Winterbourne Downs” project, and the Biffa Award “Saving a special place for Wiltshire’s endangered butterflies” project. Appropriate permissions for the work were also obtained.

Construction:

The site for the butterfly banks was flat terrain with a 20cm layer of flinty loam over chalk. Two large banks measuring 150m x 12m and 180m x 12m were constructed in two different fields. The loam topsoil was bulldozed into an S-shaped mound, oriented so that most of its length faced south. The mound was then covered with the chalk from the beneath the soil, leaving a wide 'scrape' area of bare chalk alongside.

The S-shape ensures that there are sides facing all possible directions, creating a variation in topography and diverse range of micro-climates. The idea is that this helps to increase the resilience of both plants and insects to the more extreme conditions predicted as a result of climate change. In the mornings, butterflies, bees and other warmth-loving insects can warm up on the east-facing side of the banks, which catches the early morning sun. During the main part of the day, they can use the warm, sunny, south-facing side. If it gets too hot on the south side, the insects can retreat to the north-facing side. As expected, during the middle part of the hottest July day on record in England in 2015, all the bee activity was on the banks’ north-facing slopes.

Construction begins

The first bank was initially seeded with a generic chalk grassland and wildflower mix as well as kidney vetch and horseshoe vetch, which are vital food plants for small blue, chalkhill blue and Adonis blue butterflies. On the second bank, only the kidney vetch and horseshoe vetch were introduced. The banks could have been left to regenerate naturally, but the butterfly foodplants were not growing in the vicinity and therefore seeding with specific species was preferred to ensure that the right plants established.

Development over time and ongoing management

The vetches were the first plants to establish and were flowering in the first summer after autumn sowing. Over the following two years other species, such as small scabious, ribwort plantain, harebell and quaking grass appeared, the coverage developing into a patchwork of abundant flowering species interspersed with bare areas - the ideal structure for butterfly habitat.

Vetches establish quickly on the bare chalk

The vegetation on the banks has become denser over time but has required little ongoing management as the tough conditions prevent many unwanted species from colonising. Sheep are our management tools, grazing from August onwards, when most flowering is over. This helps us to keep on top of any scrub encroachment and keeps the sward open, with some disturbance of the ground surface to create germination opportunities. Cattle would probably cause damage to the banks, so are avoided.

Where necessary, brush cutting is carried out in the summer and the arisings removed and taken to other areas of the farm which are species-poor and could benefit from wildflower sowing.

Brush cutting the coarser vegetation

Achievements:

Colonisation of the banks by breeding small blue butterflies was impressively quick - within the first three years, as the kidney vetch established readily. The abundance of suitable foodplants is particularly important for sustaining viable populations of butterflies, so the fact that small blues were seen on the banks in August, probably a second brood from eggs laid in June, was a good indication that suitable habitat for breeding had been achieved.

Small blue on its larval foodplant, kidney vetch

Other chalk grassland butterflies have also been recorded on the banks in the last few years: common blue, brown argus, marbled white, dark green fritillary and, excitingly, the marsh fritillary, a species in severe decline which has been attracted to Manor Farm by the abundance of scabious plants in the grassland. Good numbers of these species are now being seen on the farm as they are moving in from the neighbouring strongholds on Salisbury Plain and Porton Down. We have yet to record chalkhill blue, but the Adonis blue was a new record in 2018, so hopefully it will just be a matter of time before the chalkhills arrive.

The diversity of flora species continues to develop, with some of the less common chalk specialists such as devil’s-bit scabious, starting to appear on the banks.

In addition, we have shown that the fields containing the banks can still be used as grazing land, albeit in a carefully managed way.

Our experience and lessons learned:

Five years on we found that some plants had been harder to establish on the banks than others. The pioneer species kidney vetch and horseshoe vetch, two of our key butterfly food plants, established readily from seed and plug plants were not required. However, we didn’t have the same success with common rock rose, the food plant of the brown argus and cistus forester moth. This was easier to establish from plugs, although the sown seed may germinate eventually when conditions are favourable and the seed coat has weathered a little. Plugs are more expensive, so a pragmatic approach may be to try sowing seed first and then supplementing with a few plugs after a couple of years if the seed has not germinated. Germination rates of common rock rose can be improved by scratching the seed surface (scarifying) prior to sowing.

Where we sowed the generic mix, some of the taller plants have become dominant, greater knapweed particularly, shading out some of the foodplants, such as horseshoe vetch. We have therefore had to manage some of the less desirable species in order to help the key plants thrive.  This was not such issue on the second bank, where we had just sown the foodplants, with just the odd thistle to deal with.

We suspect that by creating the base of the banks from the flinty loam topsoil, the longer rooted chalk grassland species may be accessing nutrients from this base and gaining an advantage. Ideally, the bank would be created from pure chalk and the removed soil utilised elsewhere. A chalk-only bank would create the harsher alkaline conditions which favour the more extreme chalk specialists, including the kidney vetch and horseshoe vetch, and would slow the rate of encroachment by scrub species.

Although our butterfly banks are very large it is important to note that banks of any size can make a big difference to the survival of butterfly populations - even just moving soil around to create variation in the topography of reverted arable fields or pasture can help. Butterflies exist in small populations which are linked to create larger ‘metapopulations’, so even quite small areas of suitable habitat could provide a vital link in the chain.

All photos supplied by Patrick Cashman.   
For more information, contact: patrick.cashman@rspb.org.uk

Further examples of butterfly banks

Organisations such as Butterfly Conservation and Buglife have been constructing butterfly banks on several sites, both rural and urban, as a way of creating breeding habitat suitable for a number of different butterfly species. For further information see the following links:

Butterfly Conservation Fact Sheets

Case Study: Bare Ground for butterflies and moths

Case Study: Using hay strewing as a technique to create species-rich grassland

Author: Jennifer Palmer

Farm: High Burnham Farm, Epworth

Aims

High Burnham is a large (+300ha) arable farm.  As part of the RSPB’s Axholme and Idle Farmland Bird Initiative¹ (Lincolnshire), an opportunity was identified to revert an arable field corner to a species-rich meadow.  The 1.7ha field corner sits within the base of a large L-shaped arable field.  Because of the clay-based soil type, the field corner lay wet so was deemed unsuitable for arable cropping hence it was left out of production for four years.

The low-lying field corner lends itself to a pastoral management and is less than 200m from Rush Furlong Meadow SSSI.

This will be the only parcel on the holding managed as grassland.  It is anticipated that hay will be cut by a local contractor used by the Lincs Wildlife Trust and aftermath grazing will be carried out by a local grazier.

Management

Verbal advice and a written proposal were provided to the landowners on species-rich grassland establishment and management.  The RSPB’s Hay Meadow and Arable Reversion topic sheets were used to supplement this verbal and written advice.  The landowners understood the principles of grassland management through knowledge of a local grassland SSSI.

Hay strewing is a tried-and-tested method for enhancing the botanical diversity of species-poor grassland² and can also be used to create diverse grasslands on arable land³.  It entails taking freshly cut ‘green hay’ from a local donor site and, on the same day, strewing (spreading) it onto a suitable receptor site.  It is a cost-effective method and ensures that the received seeds are of local provenance.

Two donor sites were identified and Lincolnshire Wildlife Trust kindly donated and cut the hay from Sedge Hole Close, a damp meadow (MG4 National Vegetation Community) containing cowslip, great burnet, lesser knapweed, oxeye daisy and cuckooflower.  Natural England consent would have been required for using SSSI hay.

Loading a trailer with green hay at East Lound with Matt Cox Lincs Wildlife Trust

Technical advice was followed to ensure the receptor site’s soil was suitable, through testing phosphorus (P) levels.  The soil sample results showed a P Index of 1 (low) so was deemed acceptable.  The farmer prepared the site by spraying off weeds using herbicide and creating a create a fine, firm and level seedbed, avoiding looseness at depth.

The site has no historical significance.

Because the donor site is an NVC MG4 vegetation community, containing abundant great burnet, we followed advice from a floodplain grazing meadow conference (attended by Helen Norford of Yorkshire Wildlife Trust) to spread the hay at reasonable depth (up to 10cm).

Once strewn, in the first year the vegetation growth should be cut up to 4 times and then the grassland should be treated as a traditional hay meadow thereafter.

Because the donor site was smaller than the receptor site (0.9 and 1.7ha respectively) we found that we had a deficit of green hay for the receptor field and a ratio of 1:1 (as recommended by Dr Duncan Westbury) would have worked better.  Partners therefore plan to revisit, survey and repeat if necessary next year.

Black grass growth will also be re-sprayed off this year.

The cost of the green hay was free as it was donated by Lincolnshire Wildlife Trust.

There was a minimal fuel and labour cost incurred by the farmer transporting the two loads of green hay from the donor site to the receptor site.

Achievements

Breeding skylarks have been recorded in adjacent fields during RSPB bird surveys and breeding skylarks are also recorded at Rush Furlong SSSI so the parcels should attract skylarks.  The parcel also offers potential lapwing nesting habitat, providing the additional scrape excavation works are undertaken. There are records of yellowhammers in the hedges and reed buntings nesting in the adjacent OSR crop.

Sitting within the Humberhead Levels NCA, the project meets multiple NCA priorities – the creation of lowland meadow (biodiversity priority) and permanent grassland (landscape priority).

Advice for other farmers

Don’t be tempted to miss out the soil testing step! If phosphorous index is anything above low, species-rich grassland creation may not be viable for your site at this moment in time.

Ground preparation is really important and if strewing onto established grassland, really open up the sward so that lots of bare ground is showing.

Orchids may take several years before they appear so don’t be disheartened if nothing happens for the first few years.

Expect to have to consider repeating the method to ensure a diverse sward.

Additional information

¹ The Axholme and Idle Farmland Bird Initiative covered the river catchment area in the Idle Valley and Isle of Axholme, an area of Lincolnshire, South Yorkshire and Nottinghamshire recognised as being nationally important for its farmland bird assemblage.  The project area was one of the RSPB’s Farm Advice Focus Areas and ran from 2012 to 2018 combining farmland bird monitoring and farm conservation advice.
² Natural England Technical Information Note TIN063, Sward enhancement: diversifying grassland by spreading species-rich green hay.  Also through own experience on land owned by the Malvern Hills Trust, following advice from Dr Duncan Westbury of Worcester University.
³ Visit to arable reversion hay strewing site led by Professor Ian Trueman, 15-18 June 2012, FSC Shropshire Wildflower Weekend.
⁴ Natural England Technical Information Notes: TIN035, Soil sampling for habitat recreation and restoration and TIN036, Soil and agri-environment schemes: interpretation of soil analysis.

Case Study: Helping hedgehogs on farmland

Author: Nida Al-Fulaij, Grants Manager, People’s Trust for Endangered Species

Species: Hedgehog

Why is farmland important for this species?

Hedgehogs are found throughout the UK in all habitats. They have historically been associated with farmland for centuries. Hedgehogs are insectivores, foraging in fields and on grassland for worms, and along field margins and at the base of hedgerows for beetles, snails and other invertebrates. They are considered a generalist species, inhabiting most areas of our countryside, our villages and many areas of our towns too. However, as the dominant habitat in the UK, farmland is particularly important for hedgehogs.

Hedgehogs, like all animals, need to feed, hide from predators and find mates. A variety of habitats that provide foraging areas and secure nesting sites is ideal. Both arable and pasture land can support healthy hedgehog populations. Wide, species-rich hedgerows with buffers of grassy margins on either side provide safe ‘highways’ for hedgehogs to move around the landscape. Hedgerows with wide bases that are managed on rotation should have healthy invertebrate populations for hedgehogs to feed on. Old hedges with dense root systems and lots of deciduous leaves are ideal for them to use as nesting sites, both during the summer and in winter as hibernation spots.

The denser the network of hedges, the more securely hedgehogs can move around, and the higher the availability of prey species for them to feed on.

Recently ploughed fields can provide a bounty of earthworms and other prey; hedgehogs can be found in-field taking the opportunity to feed on invertebrates once crops have been harvested.

Recent studies show hedgehogs are found nearer to farm buildings. These areas could be providing safety from predators on farmland with less robust and fewer hedgerows, and larger fields.

Hedgehog (c) Ben Andrew (rspb-images.com)

Habitat management

Hedgerows:

Increasing hedgerow availability provides more nesting and foraging areas for hedgehogs. Ensure that hedgerows are species-rich, contain native trees and are as wide, high and dense as possible. Maintaining hedge bases at least 2m wide with minimal or no gaps provides secure safe nesting sites. Managing hedgerows on a 3 year rotation ensures that hedges remain diverse and robust.

Field margins:

Field margins provide buffer zones to protect hedgerow bases. 2m margins in arable fields and 3-6m margins in pasture ensures the hedges are protected from trampling and grazing, whilst the grassland provides extra invertebrate prey. Beetle banks also provide buffer zones and extra foraging areas.

Fields:

Smaller field sizes with a mixed crop provides greater variety, and therefore greater food security, for hedgehogs and other wildlife. Increasing hedges and field margins on farms with fewer, larger fields, provides habitat for hedgehogs. Reducing tillage or moving to no-till or conservation agriculture reduces soil compaction, increases soil invertebrates and improves and increases the depth and quality of the soil organic layer.

Pesticide & herbicide use:

Reducing pesticide and herbicide use means that more invertebrate prey, in particular earthworms, will be available on farmland for hedgehogs to feed on.

The above management measures recommended to provide a healthy landscape for hedgehogs are typically those associated with traditional farming practices. There should be no problems, though many of the measures may be more time-consuming than those associated with farming on a larger scale.

Hedgerow with grassy margin (c) Gethin Davies

Peoples Trust for Endangered Species (PTES) and British Hedgehog Preservation Society (BHPS) have created an advice note detailing management and stewardship options that will benefit not only hedgehogs but other wildlife too (see link below).

Benefits and costs

Creating and managing hedgerows sensitively has financial costs but there are stewardship options available; individual ones for the management regimes listed above are detailed in the attached advice note.

Managing a farm for a species such as a hedgehog involves looking at the farm as a whole. Unlike species that fly, such as butterflies, hedgehogs needs the entire landscape to be suitable in order to thrive. Consequently, many of the management techniques recommended to improve habitats for hedgehogs will also provide a healthier landscape. A denser proportion of hedges and associated smaller field sizes both help to reduce soil erosion. Reducing tillage improves soil organic matter and reduces soil compaction.

PTES guide - How to help rural hedgehogs

Case Study: Managing for wildlife in Caithness

Author: Katy Malone
Farm: Todholes Farm, Caithness

Todholes Farm is a 170ha lowland livestock farm in Caithness, where Ian Campbell raises prize winning beef cattle and sheep.

Ian Campbell took over the 170ha holding around 1990. Previously his father had managed the farm, having moved to Caithness in 1951. Since then, Ian has built up a herd of prize winning livestock, and won many rosettes for his Beef Shorthorn cattle as well as Lleyn and Texel sheep at a county level and further afield.

Aims:

Caithness holds nationally important populations of breeding waders such as lapwings, curlews, redshanks and snipe as well as twite, which have suffered from long-term declines in their breeding numbers across the UK. It is also a stronghold for the biodiversity action plan (BAP) priority species great yellow bumblebee which was previously widespread in the UK but is now one of our rarest native bumblebees. Populations of all these species have been maintained in Caithness thanks to high nature value farming systems. Todholes Farm is a typical example of these systems, which has been further enhanced through the tailoring of management for the benefit of key species.

The majority of the farm is grazed, with smaller areas of arable for livestock feed: spring barley for cattle feed, fodder rape for fattening lambs, and fodder turnips for wintering sheep.

Much of the farm is directly adjacent to the River Thurso, a Special Area of Conservation for Atlantic Salmon and a Site of Special Scientific Interest for a number of nationally rare or scarce plants.

Management:

Management advice was provided by the RSPB Scotland, specifically in relation to breeding waders and seed eating birds. Scottish Natural Heritage advised on management relating to designated sections of the site, and the Bumblebee Conservation Trust advised on the provision of pollen and nectar sources.

Of the options available for the non-designated parts of the farm, Ian opted for:

- Open Grazed Grassland for Wildlife (29ha)

- Management of Habitat mosaics (16ha)

- Management of Species Rich Grassland (4.5ha)

Open Grazed Grassland for Wildlife

Stock are excluded for six consecutive weeks between 15th March and 15th June, to restrict trampling of nests of waders such as lapwing and curlew. This could have had a high impact on the farm business, particularly in late spring, so the timing of the exclusions are calculated to allow two areas to be shut off while a third is opened up. This works well and has little detrimental impact on the economics of the business.

Management of Habitat Mosaics

This is an area of bog and heath with scattered rush and gorse bushes. Grazing is kept low between May to August to avoid trampling of wader nests and at the same time to avoid the vegetation becoming too rank.

Species Rich Grassland

Three areas of species rich grassland are managed on the farm. Wildflowers were relatively abundant right into early September, providing a much-needed late nectar source to bumblebees. In particular, the nationally rare great yellow bumblebee has been found on Todholes, and lapwings and curlews nest on the other areas of species rich grasslands.

There are some small areas of wetland within the habitat mosaics field, which were of concern to Ian in case they presented a problem with liver fluke. These areas were fenced off to address this. However, to prevent them from becoming rank, the wetlands still need to be grazed and cattle have access to them through the autumn/winter months. The cattle are dosed for fluke three times annually and Ian has not noticed any detrimental effect of fluke on his livestock as a result of grazing in these wetland areas.

Achievements:

It is still early days for the created species rich area and other taller more nutrient-loving species such as thistle currently dominate the field. Species that we hope will flourish here include vetches (e.g. tufted vetch and meadow vetchling), bird’s-foot trefoil and flag iris. Livestock are excluded between April and August but by the time the field is opened up again, the level of grazing is not sufficient to control the ‘weeds’. The grazing plan will be adjusted over time e.g. to increase grazing or allow for cutting so that a greater variety of plants can flourish. Some scarification and reseeding may also take place.