Global
average temperature has increased by 0.6oC ±0.2oC since
1860 with accelerated warming apparent in the latter decades of the 20th
century. A further increase of 1.5-6.0oC from 1990 to 2100 is
projected, depending on how emissions of greenhouse gases increase over the
period.
The
last century was the warmest of the last millennium in the Northern Hemisphere,
with the 1990s being the warmest decade and 1998 being the warmest year.
Warming has been most pronounced at night than during the day.
Reductions
in the extent of snow cover of 10% have occurred in the past 40 years with a
widespread retreat also of mountain glaciers outside the polar regions. Sea-ice thickness in the Arctic
has declined by about 40% during late summer/early autumn, though no comparable
reduction has taken place in winter. These
trends are considered likely to continue. In the Antarctic, no similar trends have been
observed.
One
of the most serious impacts on global sea level could occur from a catastrophic
failure of grounded ice in West Antarctica. This is, however, considered unlikely over the
coming century.
Global
sea level has risen by 0.1-0.2m over the past century, an order of magnitude
larger than the average rate over the past three millennia. A rise of approximately 0.5m is considered
likely during the period 1990-2100.
Precipitation
has increased over the landmasses of the temperate regions by 0.5-1.0% per
decade. Frequencies of more intense rainfall events appear to be increasing
also in the Northern Hemisphere. In contrast, decreases in rainfall over the
tropics have been observed, though this trend has weakened in recent years. More frequent warm phase El Niño events are
occurring in the Pacific
Basin. Precipitation increases are projected,
particularly for winter, for northern middle and high latitudes and for Antarctica.
No
significant trends in the tropical cyclone climatology have been detected.
As
a mid latitude country, these global trends have implications for the future
course of Irish climate, and with it for a range of impacts which it is
judicious to anticipate. This report from
Maynooth University
presents an assessment of the magnitude and likely impacts of climate change in
Ireland
over the course of the present century. It approaches this by firstly establishing
scenarios for Irish climate based on global climate model projections for the
middle and last quarter of the present century. Secondly these projections are then used to
assess probable impacts in key sectors such as agriculture, forestry, water
resources, the coastal and marine environments and on biodiversity.
The
purpose of the report is to firstly identify where vulnerability to climate
change exists in Ireland,
and what adjustments are likely in the operation of environmental systems in
response to such changes. In many
sectors, such as in agriculture, some new opportunities are likely to arise for
optimising climatic resources. In other
instances e.g water resource management, long term planning strategies will be
necessary to avoid adverse impacts. Long
lead in times for adjustment characterise many sectors e.g. forestry and it is
important to provide as much advance warning of likely changes as possible to
enable adaptation to commence early. By
anticipating change it is possible for a country such as Ireland to
position itself better to minimise the adverse impacts and maximise the
positive aspects which global climate changes may present.
Current mean January figures are
predicted to increase by 1.5oC mid century with a further increase
of 0.5oC-1.0o C by 2075. By 2055, the extreme south and south west
coasts may have a mean January temperature of 7.5-8.0oC. By then, winters in Northern
Ireland and in the north Midlands
will be similar to those presently experienced along the south coast.
Since
temperature is a primary meteorological parameter, secondary parameters such as
frost frequency and growing season length and efficiency can be expected to
undergo considerable changes over this time interval.
July
temperatures will increase by 2.5oC by 2055 and a further increase
of 1.0oC by 2075 can be expected. Maximum July temperatures in the order of 22.5oC
will prevail generally with areas in the central Midlands
experiencing maximum July temperatures of 24.5oC.
Overall
increases in precipitation are predicted for the winter months of December-
February. On average these amount to 11%. The greatest increases are suggested
for the north west
where increases of approximately 20% are suggested by mid century. Little change is suggested as occurring on the
east coast and in the eastern part of the Central Plain.
Marked
decreases in rainfall during the summer and early autumn months across eastern
and central Ireland
are predicted. Nationally, these are of
the order of 25% with decreases of over 40% in some parts of the south-east.
Agriculture
The
scenarios produced were used as input to crop simulation models for a range of
present and potential future crops. The
simulation results show that the expected climate changes will have a major
impact on Irish agriculture which, though significant, cannot be regarded as
potentially catastrophic.
For
livestock production, the expectation of more frequent summer droughts will
require significant supplementation of grazed grass.
Maize
silage is increasingly likely to replace grass silage, potentially increasing
grazing land areas. At the same time, increased production of grain maize is
expected. Barley is another potentially
important source of energy for supplemental feeding of livestock. The expected increases in cereal grain
production may be expected to reduce the cost of feed barley. However, the extra costs associated with
irrigation may offset this if it proves necessary thereby bringing the economic
viability into question, especially if barley is in competition with maize as a
forage crop.
Soy-bean
is an important supplemental source of livestock protein and is currently
imported. Soybean has the potential to replace maize as the marginal crop in
Irish agriculture.
Although
warmer temperatures would be expected to result in shorter winter housing times
for livestock, a trend towards wetter winters may result in problems of
poaching and soil damage which may
negate this. The balance of grazing
season length against winter rainfall will dictate the stored feed requirement,
and the actual climate will dictate the choice of forage crop grown. Opportunities to spread slurry or dirty water
in winter will be substantially reduced and increased slurry storage
requirements are likely to be needed. Drought
stress will become increasingly important.
Irrigation
will become important for all crops in the eastern half of the country. This
will have a major impact on the economics, machinery requirement and labour demand
in both tillage and livestock systems. Irrigation in dairying in the drought-prone
southeast is currently justified economically only if water is available
without charge and without the construction of farm reservoirs. With the projected scenarios, a much greater
area of agricultural land will be affected by drought loss, and the quantities
of water involved to compensate by irrigation will be large. Given that agriculture may have to compete for
scarce summer water extraction with other users, the consequent economic
effects may make crops with good potential uneconomical.
For
potato, drought stress will be the most important limiting factor determining
its viability and it is likely that
potatoes will cease to be a commercially viable crop over much of Ireland.
Spring
barley yield increases of approximately 25% are likely by 2055 with harvesting
time earlier than today. Maize grain
yields are expected to increase dramatically,
in western areas by more than 150% on today’s national average value. Later harvest dates may pose an increased risk
factor.
Soybean
will remain a marginal crop with the projected changes in climate. Although temperature conditions become more favourable,
precipitation changes mean that any gains could be negated by drier summers.
Irish
agricultural land use distributions will alter in response to climate change. A sharpening of east-west contrasts is likely
to occur with livestock production dominating more to the west, and arable
production dominating east of the Shannon. Planning for irrigation is needed,
particularly in the east, to ensure that water costs are acceptable and summer
surface and ground water resources are not overused.
Using the climate scenarios as input to a hydrological
model a number of likely impacts were suggested:
A
widespread reduction in annual runoff is likely that will be most marked in the
east and south-east of the country. Winter
runoff is predicted to increase in most of Ireland.
All
areas will experience a major decrease in summer runoff, particularly in the
east of the country. These reductions are likely to average approximately 30%
over large parts of eastern Ireland
by mid century.
The
magnitude and frequency of individual flood events will probably increase in
the western half of the country.
Seasonal
flooding may occur over a larger area and persist for longer periods of time.
Areas such as the Shannon basin will be
vulnerable to these changes. Turloughs
in western Ireland
will also be particularly vulnerable to these changes.
During
the summer months, long term deficits in soil moisture, aquifers, lakes and
reservoirs are likely to develop. It is
likely that the frequency and duration of low flows will also increase
substantially in many areas.
Since
evaporative losses are also likely to increase during summer months, the water
resource changes projected will have a significant effect on reservoir yields. Water supply infrastructure is expected to
come under growing pressure particularly in the Greater Dublin Area and the
strategic implications of this are profound for a number of areas, particularly
spatial settlement strategy.
The
projected changes in water availability pose potential problems for the
dilution of water-borne effluent. With a
greater frequency of low flow conditions, additional precautions will be
required to ensure that concentrations of water pollutants do not give rise to
acute effects. It is recommended that
minimum flow constraints are determined more conservatively, particularly where
new urban or agricultural discharges are envisioned. Greater incorporation of groundwater
protection considerations is also recommended as aquifers assume increasing
importance as sources of water supply as competition for reduced surface
resources intensifies.
Forests cover 9% of the land area of Ireland, a
figure which is planned to double by 2030. In planning for the future, foresters must
select species that will perform optimally over a full rotation of 40-50 years.
The time span that this report addresses
is therefore highly relevant in influencing decisions being taken today in the
forestry area.
Increased
CO2 concentrations and warmer temperatures are expected to benefit
Irish forest growth. Decreased summer
rainfall, however, would negate this, as would any increase in storm frequency.
Secondary effects of climate change on
forest productivity are also expected to be considerable. Increased nutrient mineralisation in warmer
temperatures is likely, though so also are changes in pest and disease
incidence.
Among the more significant of the latter are:
Green
spruce aphid (winter warmth may encourage large population increases)
Pine
Weevil (favoured by warmer temperatures)
Great
Spruce Bark Beetle (currently a major problem in continental Europe)
European
Pine Saw Fly (outbreaks occur on a series of three consecutive dry summers)
Fomes
(optimum temperature for the growth of this fungus is 22.5oC)
Phytopera
Disease of Alder (recently identified in Ireland, may thrive in warmer,
drier summers)
Honey
Fungus (grows optimally at temperatures 20-25oC; drought conditions
renders trees more liable to infection).
Increased
fire damage and increased deer and
squirrel populations may also constitute negative indirect impacts of climate
change on forestry. The interaction of
different effects on forest growth is difficult to model, and different species
will respond differently to changed climatic conditions. However, there is no reason to believe that
Sitka Spruce will not continue to be viable as the mainstay of commercial
forestry in Ireland.
Despite this, there is a need to assess
different provenances and species in long term research trials. Particular attention should be given to
alternative provenances for Douglas Fir and Western Red Cedar. It is also recommended that the national
tree-breeding programme should be re-assessed in the light of current knowledge
on potential climate change with a view to the selection of traits that will
accommodate and capitalise on these changes. The potential for the production and
transplanting of containerised nursery stock should also be reassessed. Finally, it is urged that climate change
scenarios should be included in the Forest Inventory and Planning System
currently operated by the Forest Service in the Department of Marine and
Natural Resources.
Changes in climate zonation were identified as having a
range of impacts for natural ecosystems and biodiversity in Ireland, with
considerable gaps in knowledge and data requiring further research to enable
definitive conclusions in key areas.
The
projected increases in temperature, combined with a longer growing season, were
found to have the potential to cause distributional and behavioural changes on
Irish species. These are summarised
below.
Climate
changes are also likely to result in significant alterations to habitat
conditions, though movement of habitats in Ireland will be restricted by
non-climatic considerations. Salt
marshes and sand dune habitats are vulnerable to sea-level and climate changes
and may experience significant changes in species composition. Montane heaths are suggested as being
particularly sensitive to climate change since many montane species are at the
lower altitude/southern latitude edge of their distribution, with limited
migration potential and an increase in temperature combined with summer drying
may prove detrimental for this habitat in Ireland. Similarly, peatlands are expected to suffer
considerably from summer drying. An increase in decomposition, a reduction in peat
formation, more erosion, changes in species composition, loss of carbon storage
and an increase in acid runoff may occur in this already fragile resource.
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Distributional
Changes
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Decline
(and in some cases extinction) of Arctic and Boreal relicts, cold hardy
species, water-dependent species, wetland and oceanic species.
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Extension
of Boreo-temperate species and other species that favour increased
temperatures e.g. deep-rooted calcareous forbs, butterflies, insect predators
and pests.
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Increases
in migrant species – mainly insects and vagrant birds.
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Changes
in distribution of introduced or invasive species.
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Behavioural
Changes
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Changes
in the phenological processes of plants (bud burst, germination and leaf
emergence).
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Changes
in plant decomposition and productivity.
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Alterations
in competitive interactions between plants.
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Increased
numbers of generations of many insects which may lead to population growth.
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Greater
winter survival rates of invertebrates.
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Changes
in phenological processes of insects e.g. early appearance of butterflies.
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Earlier
breeding of amphibians.
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Possible
changes in the competitive relationships between frogs and newts.
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Changes
in timing of migration, hatching, development and spawning of freshwater fish
with negative and positive implications for specific species.
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Increased
competition between species for niche space e.g. Salvelinus alpinus
(Arctic Char) and other species.
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Changes
in bird migrational patterns.
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Earlier
breeding of birds and larger and more numerous clutch sizes.
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Greater
numbers of overwintering birds, with reduced mortality but greater
competition between species.
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Changes
in the life cycle of bats.
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Greater
winter survival rates of bats.
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Reduction
in birth weight of Cervus elaphus (Red Deer).
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The existence of many marine species in the seas around Ireland is
temperature controlled. However it is difficult to extrapolate predictions for
land temperature increase to determine likely changes in sea temperatures,
particularly for sub surface temperature changes which may be controlled by
larger oceanographic circulation patterns. Thus, although species which are sensitive to
climate change may be identified quite easily, the extent to which actual
changes will happen is difficult to predict. Many of the impacts are likely to be indirect,
where the reduction of one species allows for an increase in another through
reduced competition. A notable impact
exists with respect to salmon farming, however, where an increase in sea
temperature may have serious consequences. Salmon are near the southern range
of their distribution and any increases in temperature could harm the
commercial viability of farms and render them subject to increased algal bloom,
pest and disease problems.
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Factors
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Certainty of potential impacts
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Increase in temperature
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Biogeography
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Range
shift for species on limit of distribution
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Likely
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Restriction
of Northern species range
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Likely
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Extension
of Southern species range
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Likely
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Loss
and gain of species at local level due to alteration
in
habitat suitability
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Likely
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Increase
in exotic species
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Very
likely
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Fisheries
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Reduction
in spawning capabilities for some species
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Possible
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Loss
or reduction of 'colder water' species
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Likely
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Gain
or increase in 'warmer water' species
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Likely
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Aquaculture
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Shift
in habitat suitability leading to the loss of ‘cold water’ species and
increase in production of ’warm water’ species
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Possible
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Increase
in harmful infections
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Likely
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Increase
in exotic species
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Very
likely
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Increase
in algal blooms
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Likely
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Loss
of production in salmon due to reduction in maturation time
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Likely
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Reduction
in availability in local smoult
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Likely
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Increase
culture possibilities for other species
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Very
likely
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Increased precipitation
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Biogeography
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Range
shift for species on limit of distribution
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Less
likely
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Restriction
of Northern species
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Less
likely
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Extension
of Southern species
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Less
likely
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Loss
and gain of species at local level due to alteration in habitat suitability
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Likely
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Fisheries
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Reduction
in spawning capabilities in coastal areas
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Less
likely
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Aquaculture
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Development
of husbandry techniques and technologies
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Likely
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Sea level rise
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Biogeography
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Extension
of habitats inshore
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Likely
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Loss
of intertidal habitats in low-lying areas (coastal lagoons and estuaries)
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Likely
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Fisheries
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Reduction
in suitable spawning grounds
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Less
likely
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Aquaculture
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Reduction
in available intertidal sites
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Less
likely
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Increased storm events
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Biogeography
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Local
change in intertidal species from wave sheltered species to wave exposed
species
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Less
likely
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Fisheries
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Loss
of fishing days
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Likely
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Aquaculture
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Reduction
of suitable intertidal and coastal sites
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Likely
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Requirement
to develop offshore sites
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Likely
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The coast is a dynamic environment which is constantly
responding to processes operative on a range of time scales. The single most important control on these
processes is sea level which has varied considerably over the past 20,000
years. Global sea level is projected to
rise by approximately 0.5 metres by the end of the century, predominantly due
to warming and expansion of the ocean water body. In Ireland this figure will be modified by
local land level changes, though a higher platform for wave attack will
inevitably mean greater erosion of ‘soft’ coastlines, formed of glacial drift
or unconsolidated materials. As a general approximation, about 1 metre land
retreat can be anticipated on sandy coastlines in Ireland for every centimetre rise
in sea level.
Inundation
risk must also take into account storm surge events and high tide frequencies. A value of 2.6m for extreme water level
presently occurs with a return frequency of 12 years on the west coast and 100
years on the east coast. These return
periods of extreme water level are likely to reduce considerably as sea levels
rise. Combining these extreme water
levels with a sea-level rise of 0.49m places approximately 300km2 of
land in Ireland
at risk of inundation.
The
loss of agricultural land cannot economically be defended against, and should
not be contemplated. Where infrastructure is at risk of inundation, cost
beneficial solutions may exist. This is particularly the case in the cities of Dublin, Cork, Limerick and Galway, and for assets such as railway lines, airports,
power stations etc. ‘Hard’ engineering
solutions should be viewed as a last resort outside of these categories,
however, as the evidence suggests this type of engineering can have dramatic effects further along the coastline. Recommendations for coastal management
policies to cope with sea-level rise would include the following:
no
building or development within at least 100 metres of ‘soft’ coastline
no
further reclamation of estuary land
no
removal of sand dunes, beach sand or gravel. Measures to protect and
rehabilitate dune systems should be implemented.
all
coastal defence measures to be assessed for environmental impact
where
possible the landward migration of coastal features such as dunes and marshes
should be facilitated
Conclusions
Climate
changes over the next half century can be anticipated and their regional
dimensions can be projected using statistical downscaling techniques. While considerable uncertainty remains,
especially with respect to precipitation changes, forward planning is now
required to accommodate climate change in Ireland.
In
key areas such as agriculture, water resources, coasts, marine and the natural
environment, climate change impacts are likely to be considerable and
significant adjustment of present management practices will be required to
ensure a sustainable future.