Projected climate change impacts on
upland heaths in Ireland
Climate Research July 2016 doi:
10.3354/cr01408
Ireland has a
high proportion of the northern Atlantic wet and alpine and boreal heaths of
high conservation value within Europe. These upland habitats of and their
associated oceanic species and vegetation are of high conservation value, but
are also considered vulnerable to climate change. For example, is anticipated that an amplification
of the elevation-dependant warming already detected will accelerate the rate of
change in mountain ecosystems, with the potential to exacerbate both the pace
and the amplitude of extinctions of vulnerable upland species uniquely adapted
to these habitats.
However,
projections from different climate models vary markedly and local processes for
upland regions are poorly captured, hence more localised modelling studies are
required to inform management decisions.
Various modelling approaches have been used to convert species
distributions into predictive maps, and bioclimatic envelope models (BEMs) are
widely used. However, confidence in the
predictive power of BEMs is compromised by conceptual, biotic and algorithm
flaws. Arising from this, the use of consensus methods is popular on the basis
that they decrease the predictive uncertainty of single-models to give a
probability distribution per pixel as opposed to a single value.
The use of
BEMs for habitats is novel, and only a limited number of studies have applied
these methods to landforms and habitats. In this work seven
bioclimatic envelope modelling techniques implemented in the BIOMOD modelling
framework were used to model Wet and Alpine and Boreal heath distributions in
Ireland. An ensemble prediction from all
the models was used to project changes based on a climate change scenario for
2031 to 2060 dynamically downscaled from the Hadley Centre HadCM3-Q16
global climate model. The climate change
projections for the individual models change markedly from the consistent
baseline predictions. Projected climate
space losses (gains) from the BIOMOD consensus model are -40.84% (limited
expansion) and -10.38% (full expansion) for Wet heath (Figure 1a); and -18.31%
(limited expansion) and +28.17% (full expansion) for Alpine and Boreal heath
(Figure 1b).
Fig. 1.
Mapped BIOMOD consensus model outputs for (a) wet heath and (b) alpine and
boreal heath habitats based on median probability ensemble forecasting method
values using the true skill statistic threshold. Red squares denote projected
losses of climate space for the A1B 2031−2060 scenario relative to the
baseline; blue squares denote stable climate space grids (areas of suitable
climate under a no dispersal—no habitat expansion—scenario); green squares
denote potential climate space gains relative to the baseline; blue and green
squares combined indicate areas of suitable climate under a full dispersal
(habitat expansion) scenario.
The projected
decline and fragmentation of the climate space associated with heath habitats
would
have significant
implications for the ecology of these complex upland ecosystems and their
associated species. Results indicate
that the distribution of wet heath habitats in Ireland is regionally sensitive
to climate change, most notably for lower-lying areas in the south and west of
the country. Increasing temperature and precipitation changes may reduce and
fragment the area that is suitable for heath development. Degrading heaths will also have an impact on
the wider structure and function of the uplands as the overall mosaic of
habitat types respond to climate change. For example, drier and warmer summers
may increase the frequency, size and severity of uncontrolled fires, and
drought effects may become more common later in the year. This may have severe
impacts in areas already subject to pressures such as overgrazing,
inappropriate burning, and loss of
vegetation cover combined with erosion of the peat or soil.
Some attempt has
been made to deal with uncertainty, at least in relation to differing results
between the model categories, by providing the results from the individual BEMs
implemented in the BIOMOD framework alongside the ensemble projection.
Certainly, there is substantial variation in the results between the individual
BEM types when the A1B scenario data are projected through the models. Although only the downscaled output from 1
GCM and scenario has been used to project climate space changes, the methods
lend themselves to using different GCM and RCM outputs from a range of
scenarios to better encapsulate uncertainty. Thus e.g., given the importance of
mean winter precipitation in all the BEM model families, if a wetter or dryer
model or scenario had been used from the ENSEMBLES RCMs, the results projected
via the BEMs could have varied further.
Such an expanded framework would allow the identification of adaptation
strategies that are robust (i.e. insensitive) to climate change uncertainties,
and would allow more confidence in identifying and targeting vulnerable areas
of heath habitat for priority conservation management measures. These sort of refinements would also help
inform best practice conservation management, whereby limited resources could
be directed to areas coincident with healthy and functional heath communities
and projected future climate suitability.
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