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Climate change, impacts and vulnerability in Europe ... - MemoFin.fr

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<strong>Climate</strong> <strong>impacts</strong> on environmental systemsBox 3.2Alien plant species <strong>and</strong> climate <strong>change</strong> — new ranges?Horticulture <strong>and</strong> ornamental plant trade are by far the most important pathways of plant <strong>in</strong>troductions to <strong>Europe</strong>(Hanspach et al., 2008; Hulme et al., 2008; Hulme, 2011). However, climate <strong>change</strong> mitigation <strong>and</strong> adaptationmeasures may also contribute to the <strong>in</strong>troduction of new species, for example through <strong>in</strong>creas<strong>in</strong>g use ofdry‐adapted species <strong>in</strong> forestry, <strong>and</strong> cultivation of energy plants (IUCN, 2009). Furthermore, climate <strong>change</strong> itselfmay <strong>in</strong>crease the establishment <strong>and</strong> reproduction rates <strong>and</strong> the niche breadth of alien plant species (Walther et al.,2009; Kle<strong>in</strong>bauer et al., 2010).An <strong>in</strong>creas<strong>in</strong>g number of warm-adapted alien plant species has recently become established <strong>in</strong> central <strong>Europe</strong>,such as palms, cacti <strong>and</strong> evergreen tree species (Berger et al., 2007; Walther et al., 2007; Essl <strong>and</strong> Kobler, 2009).One example is the W<strong>in</strong>dmill Palm (Trachycarpus fortunei), which was <strong>in</strong>troduced more than a century ago,but established <strong>in</strong> the wild only recently after average w<strong>in</strong>ter temperature <strong>in</strong>creased <strong>and</strong> severity of cold spellsdecreased (Berger et al., 2007). Alien plant species have also <strong>in</strong>creased their range by mov<strong>in</strong>g uphill (Pauchardet al., 2009).Most alien plant species orig<strong>in</strong>ate <strong>fr</strong>om warmer regions <strong>and</strong> will therefore benefit <strong>fr</strong>om projected climate <strong>change</strong> <strong>in</strong><strong>Europe</strong> (Walther et al., 2009; Schweiger et al., 2010; Hulme, 2012). For example, Map 3.14 shows the potentialfuture distribution of 30 major <strong>in</strong>vasive alien plant species for Austria <strong>and</strong> Germany as projected under differentclimate <strong>change</strong> scenarios (Kle<strong>in</strong>bauer et al., 2010).Map 3.14Actual <strong>and</strong> potential future alien plant <strong>in</strong>vasion hotspots (2081–2090) undertwo emissions scenariosCurrent 10°B2 10°A210°50°50°50°50°50°50°0 500 km 0 500 km 0 500 km10°10°10°Actual <strong>and</strong> potential future alien plant <strong>in</strong>vasion hotspots (2081–2090) under two emission scenariosNumber of species (out of 30)0 1–5 6–10 11–15 16–20 21–25 > 26 Outside coverageNote:Potential future alien plant <strong>in</strong>vasion hotspots <strong>in</strong> Austria <strong>and</strong> Germany under climate <strong>change</strong>, based on 30 <strong>in</strong>vasive alienvascular plant species <strong>and</strong> the SRES A2 <strong>and</strong> B2 emissions scenarios. Colours mark number of <strong>in</strong>vasive alien speciessuitable <strong>in</strong> an area.Source: Kle<strong>in</strong>bauer et al., 2010.<strong>Climate</strong> <strong>change</strong>, <strong>impacts</strong> <strong>and</strong> <strong>vulnerability</strong> <strong>in</strong> <strong>Europe</strong> 2012137

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