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Conservation Council Phortaigh na hÉireann FOR BOGS & WILDLIFE Growing wiser wildlife gardening series Bog factsheets Bogs formation, ecology, distribution and conservation issues Current Issues Specific Campaign Actions Bog watch - a guide to how you can help the Save the Bogs Campaign |
Crex Crex - The CorncrakeCallows The campaign to protect the callows has been closely linked to the protection of one particular species - the Corncrake. Study of the dramatic decline of this species, its near extinction, and its more recent recovery and even re-introduction to new or formerly abandoned areas makes an excellent example of how man can and has influenced his environment. Study of the conservation measures applied to corncrakes together with more environmentally conscious farming activities show how these can work together to improve the survival opportunities for a rare and threatened species. A Study of the Callows will help us understand how mechanisation and changes in agricultural and economic practices, have had a major impact on other Irish habitats, including raised bogs, uplands and hedgerows. What a Crecker!
Corncrake Life Cycle Once a nest has been built mating occurs and the females start
to lay their first brood in late May. The first clutch contains
about 12 eggs with later clutches containing 10 eggs or less.
The nest is a grass lined scrape or a swirl of grass on the
ground located in areas of tall vegetation, usually in hay or
silage fields. This ensures continuous cover to the birds and
a good food supply for the chicks. The incubation period lasts
about 16-18 days with peak hatching dates in mid-June. The females
care for their black chicks for the first 12 days. The chicks
can run very quickly and find food for themselves. After approximately
five weeks the chicks fledge. There is virtually no delay between
the completion of rearing of the first brood and the commencement
of egg laying of the second clutch. Furthermore there is only
an interval of about 40 days between the hatching dates of the
two broods. Peak hatching dates for the second brood are in
late July. In general males appear to take no part in rearing
young, and move around during the season in the hope of attracting
more females (Stowe and Hudson 1991). Calling males are usually
heard most often in the middle of the night. By day they move
quite widely, feeding on, among other things slugs, weevils and
seeds. In August the birds moult so that they have new feathers
for migration. From the beginning of September both adults and
young take flight from Ireland, back for another winter in south-eastern
Africa. Breeding Habitat Traditional corncrake breeding grounds are tall grass meadows (callows) or other tall grasses but some nest in silage fields, rough pasture and less frequently in marshes, peat bogs, gardens, cereal and rootcrops (Mayes and Stowe 1989). However in some areas hay-meadows have been replaced by sheep pasture, in which the grass is too short for corncrakes, and in other areas abandonment of hay making has led to the spread of rushes (Juncus species) which are tall plants but are too closely spaced to be used by the corncrake. Unmowed vegetation along ditches, mosaics of small meadows mowed at different times, and strips of meadows left unmown are also important in providing refuges for corncrakes during and after mowing of the hay meadows. Corncrakes nest on the ground close to the centre of the meadow and the tall vegetation provides cover and protection from predators whilst feeding and breeding. The soils of these meadows are overflowing with insects, bugs and worms providing a feast on which the corncrakes can feed themselves and their young. The wetter and softer the soil the easier it is for the adult corncrake to dig deep into the soil to reach their food. Callows A number of habitats can be found on the callows which support a diverse range of vegetation. Nearest to the river the grasslands are rich from silt deposits and waterlogged for most, if not all of the year. As the distance from the river increases the grasslands become drier during the summer months. The vegetation is adapted to these wet conditions and, typically includes water forget-me-not (Myosotis scorpioides), marsh marigold (Caltha palustris), yellow loosestrife (Lysimachia vulgaris), ragged robin (Lychnis flos-cuculi) and grasses including meadow fescue (Festuca pratensis), rough and smooth meadow grass (Poa trivialis and Poa pratensis) and tufted hair grass (Deschampsia cespitosa). Drier soils are found further away from the river. These occur on a higher level on old river soil deposits. This habitat is home to a number of grasses including the cock's foot (Dactylis glomerata), false oat grass (Arrhenatherum elatius), timothy (Phleum pratense) and crested dog's tail (Cynosurus cristatus); as well as adder's tongue fern (Ophioglossum vulgatum), the common spotted orchid (Dactylorhiza maculata) and the green twayblade (Listera ovata). Callows are particularly important for birds. The saturated
soils in the spring make ideal feeding conditions for waders.
The wet ground conditions delay the cutting of the grass, and
provides time and space for ground nesting birds such as the
corncrake to complete their breeding cycles. In October the
river floods the fields forming a shallow elongated lake. This
creates an important wintering ground to many birds such as the
whooper swan, greenland white-fronted geese, golden plover, lapwing
and curlew. Corncrake Distribution Corncrakes that breed in western Europe travel south into Africa via Egypt. In 1990 it was estimated that there was a western European population of between 5,000-7,500 calling males, with several thousand in eastern Europe (Hudson et al 1990). In 1993 there were 7,000 calling males in Poland and 489 in the UK. In 1991-1992 there were 1,100-1,200 calling males in France. Distribution numbers in the former Soviet Union are unclear however it is known that distribution and numbers have declined in the Baltic states whereas the corncrake is still quite widespread and common further east.
Corncrake Population Decline in Ireland One Irish survey completed by BirdWatch Ireland in 1978 which coincided with a similar survey conducted in Britain in 1978-79 concluded that the geographical range of the corncrake had declined noticeably during the 1970's. Gaps that had existed in the south and east had joined up, leaving the distribution of the corncrake largely restricted to Ulster and Connacht. Munster and Leinster only contained a few small pockets of distribution. The 1978 survey revealed that the population had declined to about 1,000-1,200 pairs concentrated west of the river Shannon. Joint surveys in 1988 carried out by BirdWatch Ireland and RSPB in Ireland (Mayes and Stowe 1989) and the RSPB in Britain (Hudson et al 1990) found that although there were areas where the bird could be found in strength, further declines were definitely apparent. The survey revealed that the total count of calling birds for all of Ireland was 903-930, with 781-797 in the Republic and 122-143 in Northern Ireland. From the map below it can be seen that in 1988 there were only five areas in which corncrakes were relatively common. Only 310-320 calling birds were identified along the northern coastline of Donegal but with smaller numbers overall along the Foyle and Swilly catchments. The Moy river catchment in Mayo and west Sligo recorded fairly good numbers as did the western seaboard, including the Mullet Peninsula, and the islands of Inishturk and Inishbofin. The Shannon Callows between Athlone and Portumna recorded 125 birds, with virtually all of them calling from the large hay meadows on the Callows. In Northern Ireland the corncrake population was centred around Lough Erne. The 1988 survey showed a decline of 30% from the previous survey in 1978. Even in 1988 it was clear from the findings that the distribution of corncrakes had changed, with very few birds in counties Galway and Clare, for example, and fewer in the eastern part of Northern Ireland. As expected most birds were recorded in meadows. The New Atlas of Breeding Birds in Britain and Ireland 1988-1991 showed a further reduction of 70% in the range of the corncrake since the 1968-72 survey (Gibbons et al 1993). The 1993 BirdWatch Ireland/RSPB Corncrake Census recorded 174 singing male corncrakes in Ireland, a decline of over 80% since the previous survey in 1988. The remaining population was found to be concentrated in four main areas: the Moy valley in Co. Mayo, the Shannon callows in the midlands, North Donegal and the Erne catchment in Fermanagh. 129 calling males were recorded in 1994, a decrease of 25% on the previous years numbers. This decrease was due mainly to the flooding that occurred in June 1993 on the Shannon Callows. In 1995 the Corncrake population in Ireland increased for the first time since recording began. Numbers rose by almost 35% to 174 calling males, with the greatest increase in Donegal, particularly on the islands of Inishbofin and Tory. This increase continued in 1996, when 184 calling males were recorded. Declines in Corncrake numbers have been reported from most parts of the world. It is the only Irish bird species listed as "rare" on a world-wide scale in the International Union for the Conservation of Nature's Red List of Threatened Animals. Corncrakes and Farming Traditional farming practices pre-1940's The introduction of the scythe, which is thought to have been brought to Ireland by the Normans, created a new farming practice commonly known as hay-making. Traditional hay-making was the physical cutting of tall grasses with a scythe to produce winter fodder. This practice although it would have disturbed the corncrake to a certain extent did not pose any significant threat to its life or that of its young. The movement of the farmer through the field, scythe in hand, alerted the corncrake to his presence and the possible dangers that this could entail thus giving the bird plenty of time to escape and giving the farmer the opportunity to avoid killing the bird, its eggs or chicks. This kind of farming practice allowed the farmer and the corncrake to exist side by side without interference or disturbance. From the middle of the 20th century cattle numbers rose steadily creating a growing demand for hay to be made for winter fodder. This caused problems for the corncrake as meadows changed to hay-making factories. The replacement of the hand-scything of hay by mowing with horse drawn machines has been the most important factor initiating the decline in corncrakes prior to 1940 (Norris 1947). Modern Farming Practices In 1992 the collapse of financial subsidies for beef cattle farming led farmers to switch to sheep farming. Farmers managed the land differently. Hay meadows filled with tall grasses were replaced by short pasture land. More recently with the BSE ("mad cow" disease) scares that have hit farmers the length and breath of the country there has been a notable decrease in beef cow production. No cattle means no hay, no hay means no corncrake causing the potential extinction of an already rare, but once very common bird. The switch from hay-making to silage making also had an important influence on the survival of the corncrake and this change in practice is a direct result of increased mechanisation. Wet summers in 1985 and 1986 resulted in some serious hay loss and therefore saw many western dairy farmers change over to silage making on a permanent basis. Silage production involves more than one crop per year with the first crop being taken before the meadow plants can flower. Corncrakes need vegetation taller than 20 cm, that is not too dense or matted for nesting and moving about in. A shortage of tall vegetation also occurs in late summer after mowing. However along the shores of Lough Erne and in the Shannon Callows farming intensity is generally low with minimum use of fertilisers. This results in late maturing of hay crops and harvesting is later compared with surrounding land giving the corncrake a chance to raise their young to a stage of flight. In general mowing takes place from mid June onwards. As a result second nests and both first and second broods are at risk of being destroyed. Many adults and chicks are killed during mowing when machines work from the periphery of the field inwards. Reluctant to run out into the open and across the part of the field that has been mowed the birds become trapped in the middle of the field and have little chance of escape. Other secondary reasons for the decline of the corncrake, include the introduction of herbicide/chemical fertilisers which encourage the vigorous growth of agricultural grasses, while chemicals poison the soil and its inhabitants and therefore the only source of food available to the corncrake.
Incentives for Farmers There is also a grant for mowing from the centre of the field outward, which gives young corncrakes a chance to run towards the edges, to safety, under cover of the remaining grass. This is an unconventional more time consuming way of farming, nevertheless, many farmers on the Shannon Callows demonstrated their concern in 1992 by attempting this corncrake friendly practice. There is often a shortage of cover available for corncrakes when they arrive in Ireland in Spring. Nettles and Iris patches provide suitable early cover and BirdWatch Ireland has been working with farmers encouraging them to increase the area of such cover. Cover may also be limited at the end of the season, after most of the hay has been cut. This is a particular problem in the Shannon Callows and some farmers in this area are offered a further grant payment to delay mowing further, until 1 September, in order to provide cover for corncrakes through the month of August. In the future consideration will be given to expanding and refining Corncrake Conservation Schemes in the Republic and Northern Ireland, increasing state compensation payments to farmers, including more corncrake breeding areas within Environmentally Sensitive Areas and Special Protection Areas and defining management prescriptions for the conservation of corncrakes under the Rural Environment Protection Scheme. The RSPB is also promoting a 'hay premium scheme' through the Common Agricultural Policy, to pay farmers to grow hay, not silage, with a later harvesting date, reducing risks to corncrakes (Williams et al 1997). Ultimately if these schemes are successfully run they could help to prevent one of our best loved birds from becoming extinct. But even if farmers are making silage, they can take steps to ensure that corncrakes are given a good chance to breed in safety. Leaving areas of rough vegetation on the farm uncut during spring and summer will also help. A new corncrake census has confirmed that the project is being
successful in protecting the corncrake in the areas covered by
the grant scheme. It is doubtful if they would succeed however,
without the goodwill of farmers and the advice and encouragement
of the corncrake field workers. Factors contributing to the increase
include an 80% uptake of grants in the Callows as opposed to
60% in the north-western areas and the fact that a substantial
area of the mid- Shannon flood plains is not suitable for the
level of agricultural intensification that has taken place elsewhere.
Can the Corncrakes be Saved? The Corncrake is the only Irish breeding bird that is threatened with global extinction. Following decades of decline, the trend is changing and increases in corncrake numbers were recorded in 1995 and 1996. A series of conservation measures have been put in place in an effort to halt the decline in the numbers of birds and to increase the numbers if possible. These measures must be kept up to ensure that the positive trend seen in recent years is maintained. The link between land use and the birds is direct and simple. Corncrakes need hay fields. Silage will not do. Radio-tracking studies showed that corncrakes need vegetation taller than about 20 cm to survive, if it is taller than this they can find it difficult to walk through. Populations tended to decline in regions where tall marsh vegetation and hay meadows decreased and short pasture grazed by sheep increased. There can also be a shortage of tall vegetation in late summer after mowing. This problem is most common in the Shannon Callows in Ireland where mowing and grazing remove most of the available cover. In such areas patches of unmowed vegetation along ditches and small meadows left unmown are important in providing refuges for corncrakes during and after mowing. Where the average mowing date was in early July the number of chicks raised was half of that where the mowing date was in mid August. Corncrake populations were relatively stable in most areas where the average mowing date was in August, but they were declining where mowing was earlier. Observations of chicks during mowing showed that many were killed when mowing machines worked from the periphery of the field inwards. Chicks are reluctant to run along the part of the field that has been mowed and become trapped in the section remaining to be mowed. Moving from the centre of the meadow outward allows chicks to run into vegetation outside the meadow without leaving the cover of tall vegetation. Starting cutting along one side of the field only, reversing or turning round to cut the next strip, again herds any birds present towards the field edge and away from danger. Mowing from the centre of the meadow outward reduces mortality of chicks per mowing episode from about 40% to about 10%. This is probably an under-estimate of the effect of the change in mowing method because chicks are more likely to escape from the meadow during Corncrake friendly mowing without being recorded. It is estimated that the productivity of Corncrakes would be increased by about 20% by switching from outside-inwards to Corncrake friendly mowing if the average mowing date is in early July and by 10% if it is in August. Radio-tracking of pairs revealed that all nests were within 160 m of the calling place of the male and brood-rearing areas were within 200-300m. Hence conservation actions during mowing would be effective if applied near to calling places of males. In Scotland and Ireland Corncrakes only persist in areas where stands of vegetation tall enough to provide cover in spring and late summer occur adjacent to hay meadows, and where the mean date of mowing is in late July or August. Areas with ample tall vegetation, but where mowing is early and those where mowing is late but there is little cover are not suitable for corncrakes. Conservation measures to increase the area of suitable vegetation and change the timing and method of mowing must be introduced together if they are to be effective. The public in areas where the Corncrake still breeds are enthusiastic in assisting in it's survival. The local media are always interested to hear how the season is progressing and local people report Corncrakes they hear to Birdwatch Ireland field workers. This support is vital to the continued success of the project and allows anyone with an interest to support the campaign. Corncrakes are protected by the Wildlife Act (1976) which
means that it is illegal to disturb them in any way. Further Reading Batten, L. A., Bibby, C. J., Clement, P., Elliott, G. D. and
Porter, R. F. (1990) Red Data Birds in Britain. T. and A. D.
Poyser, London. Further Information BirdWatch Ireland - IWC, Ruttledge House, 8 Longford Place, Monkstown, Co. Dublin. Tel. 01 2804322, e-mail: by clicking here Visit their web site by clicking here - http://www.birdwatchireland.ie/ Dr Catherine O'Connell |