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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 society<br />

climate projection model anticipates a 3.8 % overall<br />

habitat expansion for Ixodes ric<strong>in</strong>us <strong>in</strong> <strong>Europe</strong> by<br />

2040–2060, with expansion <strong>in</strong>to higher altitudes <strong>and</strong><br />

latitudes (notably Sc<strong>and</strong><strong>in</strong>avia <strong>and</strong> the Baltic countries)<br />

<strong>and</strong> a contraction <strong>in</strong> some areas <strong>in</strong>clud<strong>in</strong>g the Alps,<br />

the Pyrenees, the <strong>in</strong>terior of Italy <strong>and</strong> north-western<br />

Pol<strong>and</strong> (Boeckmann <strong>and</strong> Joyner, 2014). This aligns<br />

with other models of climate <strong>change</strong> that anticipate<br />

Ixodes ric<strong>in</strong>us range expansions under climate <strong>change</strong><br />

scenarios (Estrada-Peña, Ayllón, et al., 2012; Porretta<br />

et al., 2013), but it has been acknowledged that<br />

many uncerta<strong>in</strong>ties exist <strong>in</strong> these models <strong>and</strong> that<br />

extrapolat<strong>in</strong>g the projected habitat range of ticks to<br />

generate projections of the <strong>in</strong>cidence of tick-borne<br />

disease leads to additional uncerta<strong>in</strong>ties.<br />

Nonetheless, the <strong>in</strong>cidence of TBE may shift to higher<br />

altitudes <strong>and</strong> latitudes along with the distribution of<br />

Ixodes ric<strong>in</strong>us, potentially <strong>in</strong>creas<strong>in</strong>g the risk <strong>in</strong> some<br />

parts of northern <strong>and</strong> central <strong>Europe</strong>, unless targeted<br />

vacc<strong>in</strong>ation programmes <strong>and</strong> TBE surveillance are<br />

<strong>in</strong>troduced. Similarly, TBE risk is generally expected<br />

to decrease <strong>in</strong> southern <strong>Europe</strong>. Warmer w<strong>in</strong>ters<br />

may facilitate the expansion of Lyme disease to<br />

higher latitudes <strong>and</strong> altitudes, particularly <strong>in</strong> northern<br />

<strong>Europe</strong>, but it would decrease <strong>in</strong> the parts of <strong>Europe</strong><br />

that are projected to experience <strong>in</strong>creased droughts<br />

(Semenza <strong>and</strong> Menne, 2009).<br />

Projections: mosquito-borne diseases<br />

Various studies have found that warm seasonal <strong>and</strong><br />

annual temperature <strong>and</strong> sufficient ra<strong>in</strong>fall provide<br />

favourable climatic conditions for Aedes albopictus<br />

<strong>in</strong> <strong>Europe</strong> (Roiz et al., 2011). The climatic suitability<br />

for Aedes albopictus is projected to <strong>in</strong>crease where<br />

climate models project warmer <strong>and</strong> wetter climates,<br />

such as south-eastern United K<strong>in</strong>gdom (Medlock<br />

<strong>and</strong> Leach, 2015), the Balkans <strong>and</strong> central <strong>Europe</strong>,<br />

while suitability generally decreases where climate<br />

becomes drier, such as <strong>in</strong> some regions of Spa<strong>in</strong> <strong>and</strong><br />

Portugal (Cam<strong>in</strong>ade et al., 2012). This corresponds<br />

with a modell<strong>in</strong>g study that demonstrated a general<br />

decl<strong>in</strong>e <strong>in</strong> habitat suitability <strong>in</strong> southern <strong>Europe</strong> <strong>and</strong><br />

the Mediterranean area, <strong>and</strong> an <strong>in</strong>crease <strong>in</strong> habitat<br />

suitability <strong>in</strong> northern <strong>and</strong> eastern <strong>Europe</strong>an countries<br />

(Proestos et al., 2015).<br />

The risk of chikungunya may <strong>in</strong>crease <strong>in</strong> <strong>Europe</strong>,<br />

particularly <strong>in</strong> those regions where the seasonal<br />

activity of Aedes albopictus aligns with the seasonality<br />

of endemic chikungunya <strong>in</strong>fections abroad, thereby<br />

potentially <strong>in</strong>creas<strong>in</strong>g the risk of importation via<br />

travellers (Charrel et al., 2008). Models of chikungunya<br />

transmission <strong>in</strong> <strong>Europe</strong> under climate <strong>change</strong><br />

scenarios have identified France, northern Italy <strong>and</strong><br />

the Pannonian Bas<strong>in</strong> (east-central <strong>Europe</strong>) as the<br />

areas at highest risk, with <strong>in</strong>creases <strong>in</strong> the level of risk<br />

<strong>in</strong> much of western <strong>Europe</strong>, <strong>in</strong>clud<strong>in</strong>g the Benelux<br />

countries <strong>and</strong> Germany. In contrast, Mediterranean<br />

regions demonstrated a decreased risk, although<br />

the models suggested that they will mostly rema<strong>in</strong><br />

climatically suitable for chikungunya transmission<br />

(Map 5.6) (Fischer et al., 2013).<br />

A climate-related <strong>in</strong>crease <strong>in</strong> the density or active<br />

season of Aedes albopictus could lead to a small<br />

<strong>in</strong>crease <strong>in</strong> the risk of dengue <strong>in</strong> <strong>Europe</strong>. The risk could<br />

also <strong>in</strong>crease if the temperature <strong>in</strong>crease facilitated<br />

the re-establishment of Aedes aegypti, the primary<br />

dengue vector. Further modell<strong>in</strong>g studies are required<br />

to assess whether climate <strong>change</strong> would <strong>in</strong>crease or<br />

decrease the climatic suitability for Aedes aegypti <strong>in</strong><br />

cont<strong>in</strong>ental <strong>Europe</strong>.<br />

Some malaria models suggest that there will be<br />

<strong>in</strong>creased suitability for malaria transmission <strong>in</strong><br />

cont<strong>in</strong>ental <strong>Europe</strong> under future climate <strong>change</strong>,<br />

but projected malaria <strong>impacts</strong> are highly sensitive to<br />

model design (Cam<strong>in</strong>ade et al., 2014). Nevertheless,<br />

socio-economic development, l<strong>and</strong>-use <strong>and</strong> public<br />

health control measures would most likely be<br />

sufficient to mitigate the risk of malaria at the fr<strong>in</strong>ges<br />

of its distribution, despite the likelihood of sporadic<br />

<strong>in</strong>troductions of the parasite through global travel<br />

(Semenza et al., 2014).<br />

<strong>Climate</strong> <strong>change</strong> has previously not been expected<br />

to have a significant impact on WNV transmission<br />

<strong>in</strong> <strong>Europe</strong> (Gale et al., 2009; Gould <strong>and</strong> Higgs,<br />

2009). However, climate <strong>change</strong> could <strong>in</strong>fluence the<br />

transmission of the virus by affect<strong>in</strong>g the geographical<br />

distribution of vectors <strong>and</strong> pathogens, by chang<strong>in</strong>g the<br />

migratory patterns of bird populations <strong>and</strong> through<br />

<strong>change</strong>s <strong>in</strong> the life cycle of bird-associated pathogens.<br />

Temperature <strong>in</strong>creases could also play a role. The<br />

WNV risk <strong>in</strong> <strong>Europe</strong> has been projected <strong>in</strong>to 2025<br />

<strong>and</strong> 2050, with July temperature projections under a<br />

medium emissions scenario (SRES A1B), keep<strong>in</strong>g other<br />

variables constant (e.g. state of vegetation, water<br />

bodies <strong>and</strong> bird migratory routes) (Semenza et al.,<br />

<strong>2016</strong>). The results reveal a progressive expansion of<br />

areas with an elevated probability for WNV <strong>in</strong>fections,<br />

particularly at the edges of the transmission areas<br />

(Map 5.7). Projections for 2025 show an <strong>in</strong>creased<br />

probability of WNV <strong>in</strong>fection <strong>in</strong> eastern Croatia,<br />

north‐eastern Greece <strong>and</strong> north-western Turkey;<br />

high‐risk areas will have exp<strong>and</strong>ed even more by 2050.<br />

216 <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

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