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The Birds of Irish Bog
Introduction
Since the last glaciation peat bogs of various kinds developed
to cover a large proportion of NW Europe; that original extent
now considerably reduced by the activities of man. The bog plants,
whose remains have resulted in these accumulations of organic
matter, show a high degree of specialisation and adaptation to
grow and prosper in this inhospitable environment that is characterised
by extremes of acidity, low nutrient status, wetness and exposure.
In contrast there is not a single bird species confined to bogs
in the Western Palaearctic. Instead a number of bird species
have developed strong affinities with this habitat mostly utilising
it as a breeding habitat, with the majority ground nesting. Bogland
avian communities are thus typically poor in species but have
abundant individuals of one or two dominant passerines such as
Meadow pipit Anthus pratensis and Skylark Alauda arvensis,
both of which are ground-dwelling omnivores. Numbers of species
and their abundance are associated with bog size, habitat patchiness
and structure, and the proportion of open water (for example
see Bolscher 1995, Fuller 1982).
The birds of Irish bogs have not been subjected to national surveys
despite the significant area of raised bog and blanket bog in
the countryside. The Countryside Bird Survey, launched in 1998,
comes closest to meeting that requirement on a sample basis but
analysis of the data is only commencing now. So our knowledge
and understanding arises from a series of wider ecological surveys
starting with investigations focussed on Red grouse Lagopus
lagopus scoticus on blanket bog at Glenamoy, Co Mayo in the
1960s and 1970s (Watson and O'Hare 1979). The studies of MacLochlainn
(1984) at Glenveagh National Park in Co Donegal and Haworth (1987)
in Connemara, Co Galway followed. A synthesis of the information
available at the time on the birds of raised bogs is included
in Cross (1990).
Subsequently two PhD studies on the impacts of drainage and
woodland on the breeding birds of raised bogs were carried out
by Thomas Pohler and Birgit Huvendick at Clara, Raheenmore and
All Saint's bogs in the Irish midlands. These, the work of Feehan
and O'Donovan (1996) and various observations by colleagues and
myself over the years constitute the basis of this account.
Bogs at first glance may be seen as bleak, boring and uniform
environments. But this is not the case. They show considerable
natural variation, both within and between bogs, in surface topography,
extent and seasonality of open water and the composition and
structure of the vegetation. Man, principally through cutting
and drainage activities, has introduced further variation. In
so far as the available information allows this account will
seek to recognise this variation and link the breeding and wintering
birds to it. In particular it will seek to identify the bird
communities of open intact bog, those of the natural features
that occur on or are associated with bogs, e.g. flushes, soaks,
lakes, rivers, trees and areas of woodland, and those of anthropogenically
related change. The bog's role in the life cycle of these species
will also be covered.
The Birds of Open Bog
Traditionally the Red Grouse has been considered the most
characteristic bird of our bogs. Undoubtedly this arises from
its original popularity as a game bird with evidence present
on many of our remaining bogs today, systems of shallow parallel
drains and lines of shooting butts, of the efforts of landowners
to manage these areas for grouse and grouse shooting. It is unique
amongst the suite of birds found on bogs in that it can, without
recourse, complete its entire life cycle there. There the presence
and abundance of heather Calluna vulgaris as food, cover
and nesting habitat determines its presence and abundance. Heather
may appear to be everywhere but it is particular in its requirements.
It only becomes luxuriant and dominant where drier and better-drained
conditions exist. Grouse are still present on some raised bogs
and widely distributed on blanket bogs where densities are naturally
low, probably less than one bird per 40 ha. It never attains
the densities recorded on heaths where the shallower peats and
sloping ground provide drier conditions for the growth of heather.
It is likely that the over-grazing of the blanket bogs has reduced
this density estimate further. Continuing reduction in size,
isolation and fragmentation of bogs further threaten to reduce
the distribution of the species and its abundance.
As you traverse the open bog in spring these days there is therefore
a decreasing likelihood of hearing a Grouse call but the air
will be filled with the songs of the recently arrived Meadow
pipits and Skylarks as they compete for breeding territories.
Meadow pipits are nearly always more numerous than Skylarks and
often by up to a factor of two to one or even three to one in
some blanket bog areas, greatly outnumbering any other species.
They nest on the ground, laying three to six eggs per clutch
and raising two and, depending on altitude, possibly up to four
broods in the case of the Skylark. They congregate in separate
flocks usually from late July onwards and have largely departed
the bogs before the onset of winter.
These two species are the principal prey of the Merlin Falco
columbarius and the bogs, together with the uplands generally,
are its main hunting and breeding grounds. Presence of Merlin
is most easily established by looking for their plucking posts
within the bog, on hummocks or boulders or at the edge on prominent
turf banks or fence posts. Viewed traditionally as a ground nester,
recent survey work (D Norriss pers comm.) shows the Irish population
is now primarily tree nesting, with most nests located on the
wooded perimeters of the raised bogs and the conifer plantations
established on blanket bogs. Here it occupies the old nests of
the Grey or Hooded crow Corvus corone cornix. The last
record of ground nesting on raised bogs was c. 20 years ago in
Co Westmeath where a pair bred successfully in two consecutive
years on a small heather covered islet in a complex of pools
(J Moore, pers comm.). Some heather clad lake islands or those
with stunted woodlands in the western blanket bogs are still
used as nesting sites. Although adult Merlin remain within their
breeding territories on raised bogs year round, the young disperse.
Consequently the species cannot be regarded exclusively as a
year round resident of the bogs.
Snipe Gallinago gallinago, Curlew Numenius arquata
and Golden plover Pluvialis apricaria all nest on the
bogs, the latter species confined to the western blanket bogs
between Cos Galway and Donegal. Nest sites are always close to
wet areas such as Sphagnum lawns, flushes and pool systems
that are essential feeding areas for their insectivorous chicks.
At this time the adults largely feed on adjacent pastures and
wetlands, their favoured habitat in winter. Snipe will use undisturbed
bogs as daytime roosts in winter when numbers are swelled by
the influx of Icelandic migrants.
Golden plover is one of the few breeding species that show specific
adaptations to breeding on bogs. Amongst waders they lay the
largest egg and have the longest incubation period for their
size. This is seen as a means of importing nutrients and reducing
the chick's dependence on the bog before fledging.
While it is possible to see almost any bird flying over the bogs,
certain species use it more purposefully. Hovering Kestrels Falco
tinnunculus and quartering Hooded crows and Ravens Corvus
corax are seeking food. Small mammals and birds together
with large invertebrates are the quest of the Kestrel and carrion,
principally sheep, probably sustains large populations of the
latter two species on blanket bogs where isolated trees and nearby
cliffs provide suitable nesting sites.
The Greenland White-fronted goose Anser albifrons flavirostris
or 'bog' goose is a winter visitor with a traditional and
specialised association with bogs (see box). Another arctic species
which may be flushed during winter as it feeds amongst the vegetation
is the rare Snow bunting Plectrophenax nivalis. (This
next section can be placed in a box if required)
[The distribution of the Greenland White-fronted Goose in Ireland,
and in Scotland and Wales, coincides with the climatic template
that engenders the formation of oceanic blanket bog. These bogs,
together with the midland raised bogs are bounded by the four-degree
January isotherm and hence rarely freeze. They constituted the
species' traditional habitat before the influence of man began
to change things. The species feeds by probing for the nutritionally
rich underground storage organs of Cotton grass Eriophorum
angustifolium and White-beaked sedge Rhyncospora alba.
Extraction of the plants is easiest where the bog substrate
is softest and these areas are characterised by pools and hummocks
and quake underfoot. Wet areas such as these make up a relatively
small proportion of the total bog area, vary considerably in
size and are not distributed evenly. Strong evidence of high
site fidelity, a well developed social structure involving extended
family relationships and small flock size all suggest that the
species is highly adapted to exploit this unevenly dispersed
and perhaps, rotationally used, food resource. Bog feeding still
pertains in Iceland and Greenland, the staging area on spring
and autumn migration and breeding area respectively.
For many goose species worldwide traditional habitats on the
wintering grounds have been progressively lost to programmes
of reclamation, drainage and afforestation. Like these other
species the Greenland White-front has been able to adapt and
take advantage of agricultural grasslands and other crops. So
with the gradual disappearance of the bogs, particularly the
raised bogs, that link with the bogs is in the process of being
broken. In the early years of the Greenland White-front Survey
(1982-85) 11 flocks out of 34 continued to use bogs in the midlands
and in Cos Kerry, Galway, Mayo, Sligo and Donegal. 0nly eight
flocks, mostly on blanket bog, do so presently, and on a much
more reduced basis, despite the population in Ireland increasing
from c. 9-10,000 then to c. 13-14000 now (Fox et
al 1994).]
The Birds of Natural Bog Features
Areas of local nutrient enrichment occur in nearly all bogs
as flushes, or where these are more extensive, as soaks which
can be additionally characterised by small lakes with floating
mats of vegetation. Streams and swallow holes may also occur.
More plant species are present and the vegetation is generally
more luxuriant. For birds the most significant change is the
increase in structural complexity of the vegetation, particularly
the vertical component, which increases cover and foraging and
nesting opportunities. The plants that most notably effect this
change are Molinia caerulea, Myrica gale, Juncus effusus and
Rubus fructicosus. Scattered trees, mostly Betula pubescens
and Pinus sylvestris, may also be present. Small woodlands
develop in certain raised bogs, where the canopy is dominated
by Betula pubescens, and the under story by Salix species.
Breeding Stonechat Saxicola torquata and Reed Bunting
Emberiza schoeniclus are the first species to exploit
this situation where nesting cover, perches and better feeding
opportunities are now available. They are followed closely by
Wren Troglodytes troglodytes. While this latter species
is more typically associated with woodland that has a well-developed
field and shrub layers, it is the field layer that is the primary
requirement and this is what is provided in these locations.
Once trees begin to dominate, the usual compliment of breeding
woodland birds arrive represented by Robin Erithacus rubecula,
Chaffinch Fringilla coelebs, and Willow Warbler Phylloscopus
trochilus.
Mallard Anas platyrhynchos, Teal Anas crecca and
Moorhen Gallinula chloropus are associated with bog lakes
which with their islands and marshy fringes provide suitable
nesting and feeding habitat. The seclusion and safety of islands
attract a number of colonial breeders. The Grey Heron Ardea
cinerea, where islands are covered in scrub woodland, and
Cormorant Phalocrocorax phalocrocorax, Black-headed Gull
Larus ridibundus and Common Gull Larus canus at
certain locations in the western blanket bogs.
Where rivers flow through the blanket bogs Dipper Cinclus
cinclus, Grey Wagtail Motacilla cinerea and Common
Sandpiper Actitis hypoleucos are most noticeable during
the breeding season.
The Wheatear Oenanthe oenanthe requires drier parts of
the bog, e.g. where rock or mineral soil protrudes through the
blanket bogs or along bog fringes. Holes, necessary as nest sites
are only located in these areas.
In these drier areas, particularly if they are sheltered as well,
Calluna vulgaris may reach its full growing potential
with all the features of miniature woodland. These include many
of the woodland birds already mentioned, namely Wren, Robin and
the Dunnock Prunella modularis. Other notable observations
have been a colony of nesting Twite Carduelis flavirostris
in metre high heather near Belderg, Co Mayo and wintering Woodcock
Scolopax rusticola using it as daytime roosting cover.
Influence of Man
For centuries, and particularly so over the past 50-60 years,
man has modified these bogs through direct drainage and indirectly
from the impacts of arterial drainage on the local water table
of raised bogs. This, together with peat cutting on the margins,
the provision of servicing roads and afforestation, has all lead
to a drying out of the bogs which favours the growth of Calluna
vulgaris and Molinia caerulea and the appearance of
bird species more associated with woodland and hedgerows as outlined
above.
The cutaway areas are now extensive and form a veritable complex
of habitats including open water, abandoned banks, rough grassland,
scrub, broadleaf woodlands and coniferous plantations. These
now constitute potentially the richest habitat for birds in the
country with upwards of 40 breeding species being confirmed from
various studies. This 'habitat', and its birds, is deserving
of more conservation consideration and study in its own right.
Future Opportunities and Prospects
Open bog in Ireland is poor in breeding bird species and almost
devoid of bird-life in winter. Only Meadow pipit and Skylark
are fairly ubiquitous. Natural features and many of man's activities
influence the structure and composition of the vegetation positively
for birds by increasing cover and providing a combination of
additional nesting and foraging opportunities. Certain hedgerow,
woodland and wetland species invade and boost breeding species
diversity locally. However all species recorded on the bogs occur
at higher densities in other habitats which is not surprising
given the recent evolutionary history of these bogs.
Comparative work on open raised bogs in NW Europe confirm this
pattern of low species numbers and diversity but with their continental
location adding a few more species, e.g. Lapwing Vanellus
vanellus, Wood sandpiper Tringa glareola and Whinchat
Saxicola rubetra. In contrast Stroud et al (1987)
showed for the blanket bogs of Caithness and Sutherland in Scotland
a much greater diversity and density of breeding birds. This
assemblage includes both Red and Black-throated Divers Gavia
stellata and Gavia arctica, Dunlin Calidris alpina,
Greenshank Tringa nebularia and a number of other
rarer waders, Wigeon Anas penelope, Pintail Anas
acuta and Arctic skua Stercorarius parasiticus,
species more associated with the Boreal sub-arctic. Latitudinal
position and climate will probably ensure that many of these
species will not breed on Irish bogs.
The continuing loss of the 'total extent' of our bogs and the
accompanying diversity of forms that characterise these bogs,
fragmentation, increasing hydrological stress and over-grazing
makes the future look bleak for the habitat itself and consequently
the birds of bogs.
References
Bolscher, B. (1995) Niche requirements of raised bog birds.
Matching habitat attributes resulting from bog restoration.(to
be provided).
Cross, J. R. (1990b) The Raised Bogs of Ireland: their ecology,
status and conservation. Government Stationary Office, Dublin,
pp 87.
Feehan, J. and O'Donovan, G. (1996) The Bogs of Ireland:
An Introduction to the Natural, Cultural and Industrial Heritage
of Irish Peatlands. Walsh Printers, Roscrea, Ireland, pp
518.
Fox, A.D. et al (1994) Greenland White-fronted Geese in
Ireland and Britain 1982/83 1993/94: the first twelve years
of international conservation monitoring. GWGS Research Report
No. 8, pp 54.
Fuller, R. (1982) Bird Habitats in Britain. Poyser Calton,
pp 320.
Haworth, P.F. (1987) Survey of West Galway. Unpublished
Report to the WWF (Project 26/86), pp 42.
MacLochlainn, C. (1984) Breeding and wintering bird communities
of Glenveagh National Park, Co. Donegal. Irish Birds 2,
pp 482-500.
Stroud, D.A. et al (1987) Birds, Bogs and Forestry:
The Peatlands of Caithness and Sutherland. Nature Conservancy
Council, pp 121.
Watson, A and O'Hare, P.J. (1979) Bird and mammal numbers on
untreated and experimentally treated Irish bog. OIKOS 33,
pp 97-105.
Copyright Dr John Wilson 2002
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Copyright © Irish Peatland Conservation Council
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