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Climate change impacts and vulnerability in Europe 2016

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<strong>Climate</strong> <strong>change</strong> <strong>impacts</strong> on environmental systems<br />

4.4 Terrestrial ecosystems, soil <strong>and</strong> forests<br />

Key messages<br />

• Observed climate <strong>change</strong> has had many <strong>impacts</strong> on terrestrial ecosystems, such as <strong>change</strong>s <strong>in</strong> soil conditions, advances <strong>in</strong><br />

phenological stages, altitud<strong>in</strong>al <strong>and</strong> latitud<strong>in</strong>al migration of plant <strong>and</strong> animal species (generally northwards <strong>and</strong> upwards),<br />

<strong>and</strong> <strong>change</strong>s <strong>in</strong> species <strong>in</strong>teractions <strong>and</strong> species composition <strong>in</strong> communities, <strong>in</strong>clud<strong>in</strong>g local ext<strong>in</strong>ctions.<br />

• The relative importance of climate <strong>change</strong> as a major driver of biodiversity <strong>and</strong> ecosystem <strong>change</strong> is projected to <strong>in</strong>crease<br />

further <strong>in</strong> the future. In addition to climate <strong>change</strong>, human efforts to mitigate <strong>and</strong> adapt to climate <strong>change</strong> can both<br />

positively <strong>and</strong> negatively affect biodiversity <strong>and</strong> other ecosystem services.<br />

• In <strong>Europe</strong>, 14 % of habitats <strong>and</strong> 13 % of species of <strong>in</strong>terest have been assessed to already be under pressure because of<br />

climate <strong>change</strong>. The number of habitats threatened by climate <strong>change</strong> is projected to more than double <strong>in</strong> the near future.<br />

Many species <strong>in</strong> the Natura 2000 network are projected to lose suitable climate niches.<br />

• Modelled <strong>and</strong> projected <strong>change</strong>s <strong>in</strong> soil moisture, such as significant decreases <strong>in</strong> the Mediterranean region <strong>and</strong> <strong>in</strong>creases <strong>in</strong><br />

parts of northern <strong>Europe</strong>, are hav<strong>in</strong>g a direct effect on terrestrial ecosystems.<br />

• Forest ecosystems <strong>and</strong> their services are affected by range shifts of tree species towards higher altitudes <strong>and</strong> latitudes, by<br />

<strong>in</strong>creases <strong>in</strong> forest fire risk, <strong>in</strong> particular <strong>in</strong> southern <strong>Europe</strong>, <strong>and</strong> by an <strong>in</strong>creased <strong>in</strong>cidence of forest <strong>in</strong>sect pests. Coldadapted<br />

coniferous tree species are projected to lose large fractions of their ranges to broadleaf species. In general, forest<br />

growth is projected to decrease <strong>in</strong> southern <strong>Europe</strong> to <strong>in</strong>crease <strong>in</strong> northern <strong>Europe</strong>, but with substantial regional variation.<br />

• <strong>Climate</strong> <strong>change</strong> is likely to exacerbate the problem of <strong>in</strong>vasive species <strong>in</strong> <strong>Europe</strong>.<br />

4.4.1 Overview<br />

<strong>Climate</strong> <strong>change</strong> is already affect<strong>in</strong>g terrestrial<br />

ecosystems <strong>and</strong> biodiversity <strong>and</strong> is projected to<br />

become an even more important driver of biodiversity<br />

<strong>and</strong> ecosystem <strong>change</strong> <strong>in</strong> the future (Kovats et al.,<br />

2014; Urban, 2015). <strong>Climate</strong> <strong>change</strong> will have a<br />

broad range of positive <strong>and</strong> negative <strong>impacts</strong> on<br />

biodiversity at genetic, species (e.g. plant <strong>and</strong> animal<br />

species) <strong>and</strong> ecosystem levels, <strong>in</strong>clud<strong>in</strong>g shifts <strong>in</strong> the<br />

distribution of species <strong>and</strong> ecosystems, <strong>change</strong>s <strong>in</strong><br />

species abundance, <strong>change</strong>s <strong>in</strong> species phenology<br />

(i.e. tim<strong>in</strong>g of annual events) <strong>and</strong> an <strong>in</strong>creased risk of<br />

ext<strong>in</strong>ctions for some species. Soil organic carbon is<br />

potentially affected by climate <strong>change</strong>, <strong>and</strong> <strong>change</strong>s <strong>in</strong><br />

soil organic carbon <strong>in</strong> turn have an impact on climate<br />

<strong>change</strong>. Soil erosion by water <strong>and</strong> w<strong>in</strong>d is already<br />

affect<strong>in</strong>g soils across <strong>Europe</strong>, thereby jeopardis<strong>in</strong>g<br />

many of the services that soils provide (see also<br />

Box 4.6). Changes <strong>in</strong> temperature, precipitation, <strong>and</strong><br />

atmospheric CO 2 concentration will have <strong>impacts</strong> on<br />

the physical <strong>and</strong> chemical properties of the habitat<br />

(e.g. through <strong>change</strong>s <strong>in</strong> soil moisture), on <strong>in</strong>dividual<br />

species, <strong>and</strong> on ecological <strong>in</strong>teractions between<br />

species (e.g. competition, symbiosis or food webs)<br />

(see Figure 4.15). Furthermore, climate <strong>change</strong><br />

usually acts not <strong>in</strong> isolation but together with other<br />

stressors, such as human l<strong>and</strong> use <strong>and</strong> management.<br />

Human efforts to mitigate (e.g. biofuel production,<br />

hydropower) <strong>and</strong> adapt (e.g. l<strong>and</strong>-use <strong>change</strong>s<br />

or coastal defences) to climate <strong>change</strong> could also<br />

exacerbate the direct <strong>impacts</strong> (Paterson et al., 2008;<br />

Turner et al., 2010). <strong>Climate</strong> <strong>change</strong> will also affect the<br />

ability of ecosystems to deliver ecosystem services to<br />

humans (see Section 4.5 for further <strong>in</strong>formation).<br />

The pr<strong>in</strong>cipal response mechanisms of species to<br />

climate <strong>change</strong> depend on their adaptive capacity <strong>and</strong><br />

<strong>in</strong>clude phenological <strong>and</strong>/or physiological adaptation,<br />

altered migration <strong>and</strong> colonisation from locations<br />

<strong>and</strong> habitats. All these mechanisms are likely to face<br />

constra<strong>in</strong>ts <strong>in</strong> terms of tim<strong>in</strong>g <strong>and</strong>/or effectiveness.<br />

For example, migration may be constra<strong>in</strong>ed by the<br />

speed of dispersal mechanisms <strong>and</strong> by migration<br />

barriers, <strong>in</strong>clud<strong>in</strong>g habitat fragmentation <strong>in</strong>duced by<br />

human activities. If all these response mechanisms<br />

fail, the species may gradually disappear from its<br />

current range <strong>and</strong> eventually become ext<strong>in</strong>ct.<br />

In its AR5, the IPCC highlights the importance<br />

of species <strong>in</strong>teractions <strong>and</strong> states that '[…]<br />

climate‐related <strong>change</strong>s <strong>in</strong> abundance <strong>and</strong> local<br />

ext<strong>in</strong>ctions appear to be more strongly related to<br />

species <strong>in</strong>teractions than to physiological tolerance<br />

limits (low confidence)] […]' (Settele et al., 2014).<br />

Chang<strong>in</strong>g climatic conditions can lead to a mismatch<br />

between species' life-cycle events <strong>and</strong> food sources<br />

(Schweiger et al., 2012) or to decoupled predator‐prey<br />

<strong>Climate</strong> <strong>change</strong>, <strong>impacts</strong> <strong>and</strong> <strong>vulnerability</strong> <strong>in</strong> <strong>Europe</strong> <strong>2016</strong> | An <strong>in</strong>dicator-based report<br />

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