Choosing an option in REPS 3
Catherine Keena, Teagasc Environment Specialist
Farmers joining REPS 3 have choices to make. The new scheme involves higher payments and two additional undertakings. Two options must be chosen. These cannot be changed during the course of the plan. There are two categories of options. At least one must be chosen from Category 1. Both can come from Category 1 with none from Category 2. One option in Category 1 can be doubled and count as the two options. Some options are not relevant for some enterprises or farm types. Identify options which may be possible.
Category 1 (7 Options)
Three options are relevant only to tillage farms. 9A: Green Cover Establishment (14 ha), 9B: Environmental Management of Set Aside and 9C: Increased Arable Margins (14 ha). 5C: Additional Stonewall Maintenance is possible where there are sufficient stone walls. 5A: Hedgerow Rejuvenation: Coppicing / Laying suits ‘Escaped hedgerows', which have grown up and lost their dense base, but not yet become mature top-heavy trees. 5B: New hedgerow establishment and 4A: Creation of a new habitat are possible on most farms.
Category 2 (11 Options)
Two tillage options 9A: Green Cover Establishment and 9C: Increased Arable Margins are available as Category 2 based on a smaller area (7 ha). There are two options if there is an archaeological site on the farm - 7A: Increase in Archaeological and Historical Buffer Margins and 7B: Management of Publicly Accessible Archaeological Sites. There are two options where watercourses are present - 3A: Increased watercourse margin and 3B: Exclude all bovine access to watercourses. Grassland options include 2A: Traditional Hay Meadows, 2B: Species Rich Grassland or 4C:Nature Corridors - Increased Grassland Field Margins. General options include 8A: Landscaping around the farmyard and 4B: Broad-leaved Tree Planting.
Consider carefully before making choices.
Field Margins
(Nature Corridors or Field Margins 4C)
(Increased Arable Margins 9C)
Field margins are the most widespread wildlife habitat. They are used by wildlife for food, shelter, breeding and corridors of movement. Examples of broad-leaved plants are wild carrot, common sorrel and cow parsley. Traditional grasses in field margins such as cocksfoot, Yorkshire fog, crested dog’s tail and sweet vernal are rarely found in intensively farmed land.
Field margins are often not documented as wildlife habitats by botanists. For example they are not listed in our main reference book for habitats ‘A Guide to Habitats in
Ireland’, published by the Heritage Council. Their value may not be in rare flora. However their structure and diversity of flora support a wide range of invertebrates, including beetles and butterflies. Some such as lacewing and hoverfly larvae control aphids. These are critical in the food chain, as are small mammals such as bank voles and mice.
Ground-nesting birds such as pheasant and meadow pipit use field margins. Their use by birds such as barn owl and linnet to feed highlight their connectivity value for many species
Awareness
Awareness of the existence and importance of field margins is the key issue for REPS advisers. Farmers are more likely to manage correctly if they understand. Because management involves a change in practice rather than new activity, it is easy to overlook. The inclusion of extended field margins as an option will help increase awareness.
Cutting
Under Option 9C in tillage, rregular annual cutting of the rough grass field margin is not permitted (except in the first year when it must be mown at least three times in the first year to promote tillering of the grass and aid establishment). However, occasional cutting later in the year when plants have seeded is good. Leave some uncut as safe havens for wildlife. If never mowed or grazed, field margins become invaded by scrub.
Establishment
The concept of reseeding arable field margins is welcome. It further highlights the aim, can help address complaints of problem arable weeds such as scutch grass and cleavers. The source of seed is an issue.
Conservation field margins established by sowing any cereal at fifty per cent of the recommended sowing rate are not fertilised or sprayed. These provide a different habitat with annual arable weeds and associated invertebrates.
Wildflower seeds
Design by Nature, Monavea Cross, Crettyard, Co. Carlow 056 42525 is a producer and supplier of wildflower seeds. wildflow@indigo.ie
Environmental management of setaside 9B
Setaside provides a great opportunity for wildlife conservation in a relatively straightforward way. A lot has been learned about its value and potential to help species of conservation concern. These include farmland birds which have declined over the past 25 years, such as yellowhammer, skylark and linnet. With little effort, setaside can put food and suitable nesting conditions for these birds back into the farming system.
No single type of setaside provides perfect farmland bird habitat, as most species have slightly different requirements. A mixture of rotational and permanent set-aside is beneficial. Areas rich in insects provide food for chicks. Vegetation containing seeds and grains provide food for winter birds. Another important requirement is undisturbed nest sites.
Strips of setaside along woodland or hedgerows benefit yellowhammer and reed bunting. Large blocks of setaside in open areas benefit skylark and lapwing.
Rotational
Rotational set-aside is used by skylarks, which like to nest undisturbed on open land. They are attracted to grassy cover and favour sparse, patchy swards. Lapwings nest where swards are short. Rotational setaside has abundant insect life, attracted to annual flowering weeds. Annual weeds such as fat hen are excellent for birds. Fat hen also known as white goosefoot was gathered and fed to domestic fowl in earlier times. Natural regeneration of rotational setaside provides seed food over winter. These are used by seed eating birds such as linnets and yellowhammers.
Permanent
Permanent setaside with semi-permanent grass cover provides a sward varied in height and structure with tussocks, patches of fine grasses and plenty of flowers. Annual weeds disappear as the sward closes over. This is full of insects and small mammals, providing rich feeding for owls and kestrels. Reed buntings nest on the ground in set-aside. Yellowhammers also do, close to hedgerows. Chicks of both are fed on insects.
Management issues
Up to twenty-five per cent of the setaside area may be left unmown. In non-rotational setaside, rotate unmown areas as necessary to prevent scrub encroachment. Centre out mowing allows young fledglings to escape into the margins. The main benefit is the diverse flora and associated invertebrates because no sprays or fertilisers are used.
Green Cover Establishment 9A
Cereal stubbles, which contain annual broad-leaved plants, provide food for seed-eating birds such as yellowhammers and linnets. Spraying or ploughing in autumn for spring-sown cereals is equally detrimental. Flocks of wintering skylarks, finches and buntings, as well as game birds use stubbles. Skylarks nest in spring cereals. Winter crops are too dense.
Brassicae cover crops, established without ploughing, unsprayed and unfertilised under this option will benefit wildlife. It will also utilise residual nutrients in the soil following the harvesting of a cereal or oilseed crop.
Creation of a new habitat 4A
Creating a habitat can allow nature take its course. Topping is allowed, but toppings must not be removed. If it is not topped, what will happen?
Woodland is the climax vegetation that would prevail over most of Ireland under natural conditions. Natural succession is the process by which grassland is overgrown with scrub and finally by forest trees, which grow up through the scrub, overtop it and largely suppress it. Developing over time, it generates mixed age stands of local, native species, with an irregular structure. Stunted or misshapen trees are just as valuable to wildlife and add character. Dead wood, as fallen or standing trees are important habitats.
At all stages of transition it suits various flora and fauna. Linnets benefit at the grass to small bush stage. As bushes develop it suits thrushes, warblers, whinchats, stonechats, dunnocks and yellowhammers. One quarter of Irish breeding birds use woodland as their primary habitat choice.
Scrub is pioneer woody growth spanning the transition period from open ground to woodland cover. It is made up of shrubs, interspersed as time goes by with the young trees which will form the ultimate woodland.
The word scrub has unfortunate connotations. It is often found on poor, inaccessible land, which has been unprofitable to cultivate. However, whatever the reason for its presence, it is a valuable habitat and a landscape feature. So while there is no desire for wholesale scrub encroachment on abandoned farmland, areas of scrub woodland within the farmed landscape are very important for wildlife.
When planning the location of scrub woodland, take account of the presence of other habitats. Connecting habitats provides corridors of movement for wildlife. Species which will naturally colonise depend on location and also the availability of seed sources. Adjoining habitats including mature hedgerows assist colonisation. Natural regeneration maintains natural genetic variety. It favours natural distribution of species with soil type.
Scrub woodland should not replace habitats which are of high ecological value, such as species rich semi-natural grassland. In the right place, with time and nature taking its course, a scrub woodland habitat can improve biodiversity or wildlife on a farm.
Consider a pond in the new habitat from Teagasc Environmentalists Updating with John Feehan in 2004
Choose your site carefully. Use common sense. Don’t put it directly under lots of trees, though a few trees are valuable such as alder or native willows. Some leaves are useful because they contribute organic matter to the bottom and promote microscopic life which in turn feeds insects and other larger animals. Don’t put it where pesticide residues can affect it.
How deep?
Water lilies need water deeper than approximately 0.5 m. They will live in shallower water but won’t do well. At least 0.7 m depth is recommended. Fish need water that is deeper than approximately 20 cms, though shallower is excellent for their small fry. Deep water is excellent for fish in very cold weather, but if too deep you can’t see what’s in the pond. Tadpoles and small insects like shallow water. The best solution is to have both: a pond which is about 0.3m deep over a wide area, with a sloping shallow at one end, and a deeper pool somewhere for lilies, into which fish can retreat in colder weather.
A tunnel of ridge tiles from a roof can provide shelter for fish if threatened by fish-eating birds such as herons or kingfishers. However, it’s nice to such birds too! It can be useful to screen off a small loop or bay in the side of the pond with small-mesh wire under the water; this will provide a retreat for smaller fish etc. when threatened by larger fish.
To get water plants to grow really well it is a good idea to partition off a sizeable area with bricks cemented only here and there to allow the passage of water, and fill this with leaf mould. Top the partition with natural stones rising above the water for appearance. If you stop it short of the surface birds tend to stand on the edge and can do a lot of damage to the plants. Keep the earth on the plant side just at surface level so birds don’t mess things up too much. Plant with a wide variety of native emergent plants that you can usually source locally. Marsh marigolds will grow very well, as can bog-bean though it has invasive rhizomes. Yellow flag and bulrushes can be planted in the pond itself away from the walled-off plant section. Water plantain grows well out in the open water, growing up from the bottom. Be careful not to let duckweed take over. And be careful of plants such as Canadian pondweed, which can take over the whole pond.
Small native or naturalised fish are best. Take your time about stocking with fish. Never put fish in at once: they may be killed by the effect of the fresh cement, but this will soon pass. Don’t feed the fish. The rest of the livestock will look after themselves! Water beetles and water boatmen will fly in by night and dragonflies, damselflies, caddis flies, alderflies and lots of others during the day.
If your pond does not have its own water supply, you need to keep it filled from a rainwater supply, and you may need to siphon off the water from the pond at intervals. Most water plants prefer an acid soil, so water with a lot of lime is not good as a rule.
Hedgerows
(Escaped hedgerows for Rejuvenation 5A)
(New hedgerows 5B)
Hedgerows vary with pronounced regional differences. Underlying factors such as geology, soil type and climate create variation. Farming systems also have an influence. No single method of management is appropriate for all. Method of management will depend on the objectives. Evaluate each hedgerow before deciding on management. Consider the long-term effect of current management. What will the hedgerow look like in twenty years?
On a farm a management plan should be done for all hedgerows. Decide on objectives for sections of hedgerows. Management may be planned for future years. Having a plan with objectives will prevent inappropriate management being carried out in the meantime. Plans can and should change in time depending on circumstances and experience gained from other management.
Assess Hedgerows
On site assessment of all hedgerows is required prior to drawing up a farm hedgerow management plan. Consider the following:
- Type of hedgerows
- Previous management history.
- Condition
- Age
- Species richness - whether composed of only one or two shrub species or of several;
- Species rareness
- Presence and frequency of trees;
- Location - their location relative to other habitats
- Location within designated areas such as Natural Heritage Areas, Special Areas of Conservation or Special Protection Areas.
- Archaeological or historical value – Townland boundaries
- Contribution to visual value of the surrounding landscape
- Contribution to amenity value of the surrounding landscape
- Contribution to cultural value of the surrounding landscape
- Adjacent features
- Adjacent land use
- Responsiveness to specific management
- Objectives for the future function of the hedgerow.
Decide on management aims
The extent and state of repair of hedgerows on the farm must be established and used to draw up an appropriate conservation and maintenance programme. Actions required should be clearly identified to maintain and conserve these farm habitats and features. These actions should be considered against the landscape character of the area and how they will contribute to the environmental and amenity value of the farm and surrounding countryside. Management may be limited by cost, practicality and personal interest. Where the extent of planned hedgerow management is limited, priorities should be established. Those of greatest ecological value and those most prominent in the landscape should be selected for maintenance.
Where major wildlife habitats exist on farms consideration should be given to allowing hedgerows that adjoin and link these areas to grow naturally. In general increasing the variety of hedgerows in terms of height, width, shape and species mix will promote diversity in flora and fauna. The most valuable species for wildlife include oak, birch, mountain ash, whitethorn, alder, willow, ash, holly, crab and Scots pine.
Hedgerows give the Irish landscape its distinctive character and field pattern and provide an important wildlife habitat especially for woodland flora and fauna. Mature flowering hedgerows, predominately of whitethorn, provide a strong visual impact in the countryside during May and June each year. A balance of young and mature whitethorn is required for continuity of this impact. An appropriate conservation and maintenance programme promotes the flowering, fruiting, vigour and wildlife potential of hedgerows.
A variety is best. The quest for neatness should not take precedence over ecological and landscape considerations.
Mature relict hedgerows
Mature hedgerowsshould be allowed to grow freely and naturally. Maintenance in these situations should be confined to control of invasive species to prevent field encroachment. Where there are no mature hedgerows on a farm, selected sections should be allowed to develop and blossom freely.
In these instances maintenance should be confined to the light trimming of the sides to curtail outward spread. If necessary, remove overhanging lower branches interfering with normal machinery operations. Side trimming, where required, should be carried out using a two or three year cycle.
Over-managed hedgerows
Inappropriate or untimely maintenance often results in the weakening and ultimate demise of hedgerows. Where they have been cut too often and too low, allow to grow unchecked to regain height and vigour. The extent of recovery will indicate what further action is required.
Trees
If it is decided to allow sapling trees to develop these should be selected singly or in groups at irregular intervals and allocated sufficient space to grow. Where mechanical trimming is required those saplings identified for retention should have the vegetation around them cleared manually and clearly marked to alert the machine operator.
Smooth wood species such as ash and sycamore when topped respond by throwing up many vertical shoots with little lateral growth. Hedgerows consisting a high proportion of these species, which have previously not been managed, should only be side trimmed where necessary. Remove unwanted saplings.
Gappy hedgerows
Gaps may be closed by inplanting. Plant blackthorn quicks, or other suitable shade tolerant species such as holly in prepared ground. Once established, whitethorn can be cut back 75 mm to promote growth. Keep weed free and protect from stock until established.
New hedgerows 5B
New stockproof hedgerows are valuable additions to farms, wildlife and the countryside. Wouldn’t it be nice to think our generation will leave a lasting positive impression on the landscape?
Guidelines on planting hedgerows
Native species adapted to Irish conditions benefit wildlife more. Locally grown plants, tolerant of local conditions, are likely to thrive. Plants grown from locally collected seed conserves local provenance (origin). Could this be encouraged in each county?
Choice of species will depend on objectives. A high proportion of thorny species are required for a stockproof hedgerow. A variety of species provides a varied food supply for wildlife throughout the year. Include another hedgerow species or climber approximately every metre. Include trees, singly or in groups, at irregular intervals, provided they will be allowed to grow up and are NOT topped when the hedgerow is routinely trimmed.
Plant from late October to March. Autumn is best in free-draining soil, spring in heavy soil. Avoid waterlogged soil and very wet or frosty weather.
Site preparation is critical. Cultivation before planting is essential for optimum growth. Mounding is advisable on wet site. Dig in well rotted Farm Yard Manure.
Two to three year old plants are most suitable. Fibrous healthy roots and thick lower stems are more important than height. Roots must be kept moist before and during planting to avoid drying out and dying. Plant at the same level as previously planted and firm in.
Whitethorn may be cut back to 75mm to promote basal growth. If plastic is used to control weeds, pruning is done at planting to facilitate this. Weed control is critical to prevent smothering and to allow lower branches develop, giving a dense base. This can be done manually, chemically or with mulches of wood chippings, paper, etc.
Exclude livestock using temporary fencing. Consider livestock reach and future access for machine trimming, when positioning the fence. Rabbit-proof fencing may be needed if these are a problem locally.
Replace dead plants. For the first few years after planting, it may be beneficial to cut whitethorn back to 75mm above previous level of cut, gradually shaping into a triangular shape.
Some sources of native species:
- Coillte Nurseries, Ballintemple, Ardattin, Co Carlow 0599155621 www.coilltenurseries.ie
- Future Forests, Kealkill, Bantry, Co. Cork 027 66176 www.futureforests.net
Escaped hedgerows for Rejuvenation 5A
Hedgerows with little basal growth if left alone will grow into mature relict hedgerows. It may be more appropriate to rejuvenate the hedgerow by laying or coppicing distinct sections over the period of the plan. Careful consideration should be given when prescribing the lowering of the height of a hedgerow. Topping of hedgerows consisting of mature previously unmanaged whitethorn/blackthorn may also result in undesirable growth characteristics such as bushy top-heavy growth (the “toilet brush” effect).
There is a new Hedgelaying Society of Ireland Hedge Laying Association of Ireland (HLAI). Contact: The Secretary, Moyvore, Mullingar, Co. Westmeath. (087) 2794045
Email: hlai@eircom.net
Hedgerow Management and Mechanical Hedgecutting Courses
In response to increasing interest in this issue and changes in REPS 3, Networks for Nature, Teagasc and the Professional Agricultural Contractors Association developed a voluntary hedgecutting training programme. This programme leads to FETAC qualifications.
Courses are offered at four agricultural colleges: Gurteen in Tipperary (067 21282) ; Ballyhaise in Cavan (049 4338108); Pallaskenry in Limerick (061 393100); and Kildalton in Kilkenny (051 643105).
These two-day courses for hedgecutting contractors and farmers will help to understand the environmental, legal and safety requirements of hedgerow management and mechanical hedgecutting. The course costis €200 per participant. Having practised the skills this can lead to a FETAC Certificate demonstrating proficiency in the use of mechanical hedgecutters. The cost of the Proficiency Test is €250. It is carried out at the contractor’s own machine at his own location.
Teagasc Leaflets: Countryside Management Series
- The Value of Hedgerows
- Routine Trimming of Hedgerows
- Hedgerow Rejuvenation
- New Farm Hedgerows
New Hedgerow Book
Irish Hedgerows: Networks for Nature was produced by Networks for Nature. This is a forum of government departments, semi-state agencies, farming organisations, environmental concerns, academia and business interests. It will be launched by Professor David Bellamy at a national conference on Wednesday 17th November 2004 in the Radisson SAS Hotel, Athlone. www.networksfornature.com
Stone Walls 5C
Maintenance Guidelines
Replace fallen stones regularly, as gaps attract livestock, causing further damage.
Follow good local traditional practice. Carry out repairs using materials and styles similar to the original structure. Don’t fill the centre of dry stone walls with concrete. Cement introduces rigidity into flexible structures, so cracking can occur. It is also impermeable, so can only dry out through exposed stone. Appropriate repairs to mortared walls involves the use of lime. Consult the National Monuments Section of the Department of the Environment about walls surrounding graveyards or other archaeological sites.
A good reference book is ‘Irish Stone Walls’ by Patrick McAfee.
Tree Planting
(Broad-leaved Tree Planting 4B)
(Landscaping around the Farmyard 8A)
Many trees will be planted in REPS 3. These may be around or adjacent to farmyards, in field corners, along boundaries or out in fields. So what species are likely to be planted? To appreciate something, one must know it. A survey in the Castlerea district of County Roscommon examined awareness of tree species. There was a high awareness rate for trees such as ash, oak, hawthorn, sycamore, beech, and horse chestnut. Others such as birch, holly, willow and alder had low rates of awareness. Although present, no farmer listed crab apple, rowan or elm on their farm.
A question was asked to establish each farmer's favourite tree or shrub. Beech was clearly the most popular. Oak, ash, hawthorn, sycamore and horse chestnut, which were all very familiar, were favoured. Oak was chosen by half the 250 people who responded at the Teagasc Environment stand at the National Ploughing Event. Ash was second at 27 per cent.
Plant native
Native species are used by more wildlife. Three common species which are not native are beech, sycamore and horse chestnut. They were introduced here in Roman times. While they have become naturalised, farmers will notice they are not generally found growing naturally out the land.
Consider tree height
Tree heights vary. Oak, ash and scots pine grow to over thirty metres. Hazel, holly, hawthorn, spindle, rowan and crab apple remain below fifteen. Alder, aspen, birch and wild cherry are in between.
Get to know what species are growing naturally in your area. These are preferable. Take note of less common species.
Trees remain long after those who plant then (Maireann an crann, ach ní mhaireann an lámh a chur é). Choose carefully.
“Our Trees” is a guide to growing Ireland 's native trees. It is free from the Tree Council of Ireland, The Park, Cabinteely, Dublin 18 (€2 for P&P) 01 2849211.
Watercourse protection
(Increased watercourse margin 3A)
(Exclude all bovine access to watercourses 3B
Watercourse margins
Fencing watercourse margins allows vegetation to grow. This provides a filter preventing nutrients entering watercourses. Vegetation also stabilises banks. It prevents soil erosion and the build-up of silt in rivers. Field margins are used by intensive dairy farmers in New Zealand to protect watercourses.
Two options offer further protection to watercourses. To participate in these options, a farm must have watercourses that require fencing. The farm must be planned to include bovines. Option 3A is to increase watercourse margin s from 1.5 to 2.5 metres. The application of pesticides and chemical fertilisers within this margin is prohibited. Option 3B excludes all bovine access to all watercourses on the farm. A minimum of two piped drinking troughs per farm must be provided in fields adjoining the watercourse(s) in question.
Archaeological Features
In grassland the monument itself and an area of 20 metres around it must not be interfered with through activities such as ground disturbance, excavation, construction of buildings or tree planting. REPS 3 clarifies that this includes ploughing for reseeding. Monuments in tillage fields must be surrounded by an unploughed margin of 5 metres.
No materials of any type should be removed from or dumped on such sites. Avoid damaging monuments through the use of heavy machinery nearby. Continuous movement or overwintering of animals on earthwork features is not permitted. REPS 3 confirms that grazing is good, provided no damage occurs. It prevents scrub encroachment. If protection is required, temporary fencing can be used. Grazing can be reintroduced as appropriate.
Two options relate to archaeological and historical features. One option is to increase the protection margin around archaeological and historical sites. Farmers choosing Option 7A must maintain a minimum buffer margin of 30 metres in grassland and 7.5 metres in tillage land.
Option 7B allows public access to a site on a farm, which is detailed in the Record of Monuments and Places. Management includes maintaining the site litter free and maintaining public access points to the site. The Minister shall not be liable for any public liability claims relating to the lands the subject of this option
Booklet:
Good Farming Practice and Archaeology by Department of the Environment, Heritage and Local Government. Available in Teagasc Offices
Using LINNET crops in the Grey Partridge Area in Offaly
The grey partridge has been in serious decline since the 1950’s and practically gone since 1960. Since 1995, native grey partridge have been removed from the huntable species list; game farmed birds can still be hunted under license. In autumn 2002, there was less than fifty wild partridge remaining in Ireland, which is not considered to be a viable population. The Boora area of west Offaly remains the only breeding location of wild partridges in Ireland.
They have found refuge in cutaway bogs – adding an interesting aspect to the debate on future land use of 80,000 hectares of cutaway bogland arising within the next thirty years. This is typified in Lough Boora Parklands in County Offaly, location of the Irish Grey Partridge Conservation Project.
Irish Grey Partridge Conservation Project
Since 1992, research by Zoologist, Dr Brendan Kavanagh of the Royal College of Surgeons in Ireland has been conducted on the grey partridge in Boora. This work is currently funded by the National Parks and Wildlife Service. In 1996, in conjunction with Bórd na Móna, a conservation programme was instigated.
While predation on healthy populations in suitable habitat is normal, predators can cause significant declines when a species is a vulnerable level. The project aims to reduce predation levels.
Since 1997 both average and maximum covey size has declined. Small brood sizes are a sign of genetic depression. Given the low number of grey partridge in the population, there is a disproportionate contribution by one or two individuals to subsequent populations. This has been occurring for generations. If not addressed, this would accelerate the decline of the species. The decision to import wild grey partridge from France to augment the native Irish birds was taken in view of the loss of genetic diversity.
Creation of habitats
After hatching, partridge chicks feed on insects to grow and feather-up quickly. Without this protein-rich diet, they become stunted and die. They need areas where broods can safely forage in early summer. A crop with a canopy protects chicks from birds of prey.
Adult grey partridges feed mainly on seeds. They like setaside, winter stubbles, harvested rootcrops and weedy areas. Modern combine harvesters leave little spilt grain. Early cultivation for winter crops buries spilt grain and weed seeds. Partridges need cover for shelter and protection from predators.
In Boora, crops are sown to provide a habitat in which birds can safely forage. Nesting cover, chick-rearing cover and winter food crops are sown in 0.25 hectare strips, fifteen metres wide. Strips maximise the length of edge. Crops are sown on a three-year rotation. Linseed provides food, as do germinating weeds such as redshank and chickweed in unsprayed crops. Linseed; which is a relatively cheap seed, triticale; which is more expensive and stubble turnips are ideal for partridges. Mixes including kale, forage rape and jonty provide cover particularly in winter. Fodder radish provides rapid cover in winter. It can be broadcast into stubbles after harvest in autumn. It has the added advantage of providing green cover over winter. Game crop with quinoa and kale, which is designed for pheasants, is too high and dense for partridge.
With increasing day-length from Christmas partridges start to pair. They look for nest sites on free-draining soil on a slope preferably facing south with shelter from prevailing weather. Nests are a shallow scrape in the ground concealed in dead vegetation such as rank tussocky grass, herbaceous perennials, game cover and nettle beds. In Boora, nesting banks are 1.5 metres high to prevent flooding of nests. They are sown with non-commercial grasses including cocksfoot, canary grass, timothy and bent.
An area of farmland surrounding Boora is potential location for the expansion of grey partridge populations. LINNET plots on farms in this ‘Grey Partridge Area’ could help their survival.
Website www.greypartridge.ie
Supplementary Measures
Supplementary Measures offer a chance to increase payments. They are optional. There are six available. A farmer can receive payment on two, one from each group of three. Options must be undertaken from the start of a new five year REPS plan.
Group 1 Supplementary Measures
Payments on these three replace basic REPS payments on areas involved. However they do not reduce the number of hectares paid at the high rate of €200 (unless farms less than twenty hectares). Creation of these new habitats will not reduce the Single Farm Payment.
LINNET
Farmers can receive an extra €1300 annually where 2.5 hectares of land is setaside to grow crops as wild bird cover. No harvesting or grazing is allowed.
Traditional Irish Orchards
An annual payment of €150 per new orchard established. The minimum size is 500 m 2.
Riparian Zones
A payment of over €1800 annually is available where 2.5 hectares is set aside from farming along salmonid rivers. This is more attractive now with land set-aside for five years only, renewable for twenty years.
Group 2 Supplementary Measures
These are top up payments additional to basic REPS payments.
Corncrake
This is only available to farmers in the Shannon Callows where corncrakes have been known to breed in recent years. A payment of €100 per hectare will be available annually on lands identified as corncrake habitat areas. This is a top up on the €242 Measure A payment on these SPA lands.
Conservation of Animal Genetic Resources
In addition to Kerry, Irish Maol (Moiled) and Irish Draught; Dexter cattle, Connemara ponies and Galway sheep are now eligible. Annual payments of €200 per qualifying Livestock Unit are now available which is a change from the REPS 2 payment system.
Organic Farming
Payment for full organic status remains at €91 per hectare, but is now payable up to 55 hectares.
Don't forget these Supplementary Measures to increase payments further, with increased benefits to biodiversity.



