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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 />

Box 4.3<br />

Examples of observed <strong>change</strong>s <strong>in</strong> species phenology <strong>in</strong> <strong>Europe</strong>'s seas<br />

The tim<strong>in</strong>g of spawn<strong>in</strong>g of sole <strong>in</strong> the Irish Sea <strong>and</strong> parts of the Greater North Sea has shifted to earlier <strong>in</strong> the year, at a rate<br />

of 1.5 weeks per decade s<strong>in</strong>ce 1970, <strong>in</strong> response to <strong>in</strong>creas<strong>in</strong>g sea surface temperature (MCCIP, 2013).<br />

Long-term <strong>change</strong>s <strong>in</strong> the phytoplankton communities <strong>in</strong> the northern Baltic Sea <strong>and</strong> the Gulf of F<strong>in</strong>l<strong>and</strong> have occurred over<br />

the past 30 years. This can be seen <strong>in</strong> a decl<strong>in</strong>e <strong>in</strong> the spr<strong>in</strong>g bloom but an <strong>in</strong>crease <strong>in</strong> the phytoplankton biomass dur<strong>in</strong>g<br />

summer <strong>in</strong> this period. These <strong>change</strong>s appear to reflect both climate-<strong>in</strong>duced <strong>change</strong>s <strong>and</strong> the eutrophication process.<br />

A <strong>change</strong> <strong>in</strong> the annual tim<strong>in</strong>g of peak seasonal abundance of decapoda larvae from 1958 to 2009 <strong>in</strong> the central North Sea<br />

has been observed. S<strong>in</strong>ce the 1990s, the seasonal development of decapoda larvae has occurred four to six weeks earlier<br />

than the long-term average. This trend towards an earlier seasonal appearance of decapoda larvae dur<strong>in</strong>g the 1990s was<br />

correlated with sea surface temperature rise. These phenological shifts are a response at the species level, <strong>and</strong> not simply<br />

different seasonal tim<strong>in</strong>gs by different species (L<strong>in</strong>dley <strong>and</strong> Kirby, 2010).<br />

copepod species has <strong>change</strong>d considerably over time<br />

(Figure 4.5). While C. helgol<strong>and</strong>icus is becom<strong>in</strong>g more<br />

abundant <strong>in</strong> the North Sea, the overall Calanus biomass<br />

has decl<strong>in</strong>ed by 70 % s<strong>in</strong>ce the 1960s (Edwards et al.,<br />

<strong>2016</strong>). Such rapid shifts <strong>in</strong> distribution range can<br />

reorganise mar<strong>in</strong>e species communities <strong>and</strong> have an<br />

impact on human communities that depend on them.<br />

For example, it has been shown that occurrences<br />

of <strong>Europe</strong>an sprat are positively correlated with C.<br />

f<strong>in</strong>marchicus, while species such as Atlantic horse<br />

mackerel are positively correlated with C. helgol<strong>and</strong>icus<br />

(Montero-Serra et al., 2015).<br />

Figure 4.5<br />

2010<br />

2005<br />

2000<br />

Ratio of Calanus species <strong>in</strong> the Greater<br />

North Sea<br />

Calanus helgol<strong>and</strong>icus/Calanus f<strong>in</strong>marchicus ratio<br />

0.9<br />

0.8<br />

0.7<br />

0.6<br />

0.5<br />

Benthic <strong>in</strong>vertebrates are also shift<strong>in</strong>g their<br />

distribution range as temperatures <strong>change</strong> <strong>in</strong> the<br />

Greater North Sea, but their response lags beh<strong>in</strong>d<br />

the temperature <strong>in</strong>crease. Unless the <strong>in</strong>dividual<br />

species are able to withst<strong>and</strong> a <strong>change</strong> <strong>in</strong> thermal<br />

regime, this mismatch could lead to a drop <strong>in</strong> benthic<br />

diversity (Hidd<strong>in</strong>k et al., 2015). Such reorganisation<br />

will have an impact upon human communities <strong>and</strong><br />

challenge traditional approaches to management of,<br />

for example fisheries, which have to consider species<br />

responses to temperature when plann<strong>in</strong>g future fish<strong>in</strong>g<br />

opportunities (Rutterford et al., 2015).<br />

1995<br />

1990<br />

1985<br />

1980<br />

1975<br />

1970<br />

0.4<br />

0.3<br />

0.2<br />

0.1<br />

Very fast rates of northwards movement were<br />

observed <strong>in</strong> the coastal waters of southern Norway<br />

from 1997 <strong>and</strong> 2010. About 1 600 benthic mar<strong>in</strong>e<br />

species were found, <strong>and</strong> of these 565 species had<br />

exp<strong>and</strong>ed their distribution northwards along the<br />

coast, at rates of 500–800 km per decade (Brattegard,<br />

2011). Phytoplankton <strong>and</strong> highly mobile pelagic species<br />

are the fastest migrat<strong>in</strong>g organisms; their migration<br />

rate can be an order of magnitude faster than those of<br />

terrestrial species (Poloczanska et al., 2013).<br />

Note:<br />

Source:<br />

1965<br />

1960<br />

2 4 6 8 10<br />

Month<br />

Temporal <strong>and</strong> seasonal distribution of the ratio of Calanus<br />

species from 1958 to 2014.<br />

Edwards et al., <strong>2016</strong>. © <strong>2016</strong> Sir Alister Hardy Foundation<br />

for Ocean Science (SAHFOS). Reproduced with permission.<br />

116 <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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