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Climate Change is considered to be one of the most serious environmental issues of this century. The United Nations Inter-government Panel on Climate Change (IPCC) has identified the build-up of atmospheric greenhouse gases (GHGs) such as carbon dioxide, methane and nitrous oxide as threatening global climate stability. By 2100 the global climate is expected to warm by between 1.8 and 6.4oC (IPCC, 2007). The impacts of climate change on natural ecosystems, biodiversity, human health and water resources are already being observed and are projected to become more pronounced (Anonymous, 2007).
Peatlands as carbon sinks
In their natural state peatlands act as long-term sinks for atmospheric
carbon dioxide. A persistently high water table is necessary
for this function. Peatlands are the most important long-term
carbon store in the terrestrial biosphere. They sequester and
store atmospheric carbon for thousands of years (Charman et al,
2008). The peatlands in the northern hemisphere alone store approximately
450 billion tonnes of carbon (Gorham, 1991).
Undisturbed peatlands accumulate carbon from the air at a rate of up to 0.7 tonnes per hectare per year (Pearce, 1994). The Wildlife Trusts in the UK have estimated that a 2m deep peatland stores 8,000 tonnes of carbon per hectare (Paul, 2008). Blanket bogs and fens in general are likely to hold lower carbon stores than deep, intact raised bogs. In Ireland peatlands are estimated to store 1085 Mega tonnes (Mt) of carbon, this corresponds to 53% of all soil carbon stored in the island of Ireland on just 16% of the land area (Tomlinson, 2005). The delicate balance between production and decay easily causes peatlands to become carbon sources following interference. A drop in water table due to drainage, peat removal, burning and other human influences leads to significant releases in some greenhouse gases but conversely a decrease in others (e.g. methane). Between 1990 and 2000 up to 23 Mt of soil carbon has been lost, mainly due to industrial peat extraction (Tomlinson, 2005). It is vital to maintain a pristine water table on peatland habitats to prevent the large scale release of these gases.
In Ireland the long-term carbon storage function of 47% of our original peatland area has been severely diminished through domestic and mechanical peat extraction. Wilson (2008) estimates that small-scale mechanisation, currently operated by turbary rights owners, could release around 2.3 tonnes of carbon per hectare from the degraded areas of peatland. This corresponds to an annual emission of 1.25 Mt carbon from peatlands in the Republic of Ireland. At such levels, it will be increasingly difficult for Ireland to reach its Kyoto targets. Because of the large emissions from degraded peatlands, rewetting and restoring them is one of the most cost-effective ways of avoiding anthropogenic greenhouse gas emissions (Charman et al, 2008).
Carbon dynamics in intact
peatlands
In a natural peatland system, the movement of greenhouse gases
(e.g. methane and carbon dioxide) between the peatland and the
air is complex. Although peatlands accumulate carbon over the
long term, they both fix and emit carbon dioxide and release
considerable amounts of methane, a by-product of anaerobic decomposition.
Drainage of a peatland upsets the accumulation process and leads
to a vast increase in the amount of carbon dioxide released to
the atmosphere from the peatland, a by-product of aerobic decomposition.
The diagrams prepared by Wilson (2008) inset below illustrate
these concepts.
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Climate change and peatland
biodiversity loss
The Millennium Ecosystem Assessment 2005 predicted that by the
end of the 21st Century, climate change would be the major cause
of biodiversity loss. The predicted increase in temperature and
the changes in rainfall patterns, coupled with centuries of habitat
loss, are likely to have a major impact on peatland ecosystems.
As peatland formation in Ireland is strongly linked to climate, any changes in the climate is going to have an adverse effect on our peatland types. A research team in Trinity College Dublin led by Mike Jones have quantified the likely impact of climate change on the three major peatland types in Ireland. Jones et al (2006) predict that within the next 50 years, climate change will cause a loss of between 30 and 40% of all peatland types.
The 1990's have been the warmest decade in the Irish instrumental record (Sweeney et al, 2006). As well as temperature changes rainfall patterns will also change, with prolonged periods of dry weather more likely to occur in the future. Analysis of the Irish meteorological monitoring network has shown that already the south and east of the country are experiencing drier summers, while the north and west are experiencing wetter winters (Sweeney et al, 2006). As a result changes are anticipated in the distribution of peatlands, with south easterly sites most at risk initially. However this may be counter-balanced by better conditions for peat accumulation further north, thanks to increased rainfall in winter.
The impact of climate change
on peatland species
The MONARCH (Modelling Natural Resource Responses to Climate
Change) programme 2001 is a long-term programme developed to
assess the impact of predicted climate change on wildlife in
Britain and Ireland (Harrison et al, 2001) (Walmsley et al, 2007).
It points to where climate is likely to become favourable or
unfavourable for species, thereby influencing their future distribution.
MONARCH predicts a loss in suitable climate space in Ireland for the Skylark (Alauda arvensis) and a gain in suitable climate space for the Marsh Fritillary butterfly (Euphydryas aurinia). The dominant vegetation of most bogs is Sphagnum moss, of which there are many species. MONARCH investigated the likely future extent of Sphagnum papillosum. Its climate space is likely to remain and possibly enlarge across Ireland. A similar response is seen for other bog species such as Bog Myrtle (Myrica gale) and White-beaked sedge (Rhynchospora alba). But more northern species will probably lose a significant part of their distribution, such as Cloudberry (Rubus chamaemorus), which may find conditions too warm and could disappear entirely from Ireland.
As most peatland species are extreme habitat specialists they
may be unable to adapt to the rapidly changing climatic conditions
that are predicted. Further research is needed on the environmental
requirements of each individual species so as to determine which
species are likely to be most at risk. Unfortunately, at present,
relatively little is known about the vulnerability of most of
our bogland plant and animal species to enable a more accurate
assessment. A survey of 850 native plant species carried out
by Dr. Peter Wyse Jackson of the National Botanic Gardens of
Ireland showed that 171 (20%) of Ireland's flora appears to be
particularly vulnerable to
climate change up to 2050. 34 of these vulnerable species occur
on peatlands including Fen Violet (Viola persicifolia),
Bog Orchid (Hammarbya paludosa), Cloudberry (Rubus
chamaemorus) and Marsh Saxifrage (Saxifraga hirculus).
In conclusion, the current management of Irish peatland resources
is generally not
sustainable and is having major negative impacts on climate and
biodiversity. Strict protection of intact peatlands is critical
for the conservation of biodiversity and to maintain their carbon
storage and sequestration capacity and associated ecosystem functions.
Rehabilitation and integrated management of peatlands can generate multiple benefits including maintaining biodiversity and mitigating climate change, as well as decreasing poverty and combating land degradation. Concerted action for the protection and wise use of peatlands should therefore be a national priority linking work at national, regional and local levels (Charman et al, 2008).
| Actions Needed to Halt Climate Change on Peatlands | Priority |
On-going Short (0-3 years) Medium (3-5 years) Long (5-10 years) |
| Lobby for a reduction in the use of peat fossil fuels, so as to reduce carbon emissions from this source. | High | Medium |
| Carbon emissions from domestic peat extraction must be accounted in Ireland's carbon emissions to Kyoto. | High | Short |
| Initiate research programmes on the environmental requirements of peatland species and habitats. | Medium | Medium |
| Lobby government to develop a conservation, restoration and wise use plan for all peatlands, so as to provide measures to adapt to climate change. This is essential for Ireland's long-term climate change mitigation and adaptation. | High | Long |
| Campaign for an expansion of renewable green energy production and decrease peat production for energy and domestic fuel. However, no wind farm developments should take place on intact peat soils. | High | Long |
| Create connectivity between peatland habitats and the wider countryside to allow for species migration in response to climate change. | Medium | Medium |
| Introduce measures to cease all turf cutting on protected sites. | High | Short |
| Phase out the production of milled peat for electricity generation and horticulture. No new peat production sites should be initiated. | High | Medium |
| Restore water table levels on protected peatland sites affected by drainage as a priority. | High | Long |
| Restore peatland habitats on cutaway bogs and highlight the benefits of this in combating climate change and biodiversity loss. | High | Long |
| Educate land owners on the methodologies needed to restore peatlands to peat accumulating, carbon storing ecosystems. | High | Long |
| Inform the public of the role peatlands play in carbon storage and climate regulation. | Medium | On-going |
| Restore afforested peat soils to peat accumulating systems. | High | Long |
| Restore peat accumulating vegetation to degraded peatland types through active reintroduction of Sphagnum moss. | High | Long |
| Document, protect and restore peatlands which are of importance as carbon stores. | High | Long |
Source Citation
Malone, S. and O'Connell, C. (2009) Ireland's Peatland Conservation
Action Plan 2020 - halting the loss of peatland biodiversity.
Irish Peatland Conservation Council, Kildare.
Expanding on the content
of the IPCC Action Plan 2020
Please follow the links below to further information
from the IPCC Action Plan 2020.
Peatlands 2020 IPCC Conservation Action Plan Summary
Extent and Utilisation of Irish Peatlands
Designation of Peatlands of Conservation Importance
Halting the Loss of Biodiversity
Peatland Site List of Conservation Importance in Ireland
Over-Exploitation of Peatlands for Peat
Nutrient Pollution of Peatlands
Invasive Species and Peatlands
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