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 />
4.4.3 Phenology of plant <strong>and</strong> animal species<br />
Key messages<br />
• The tim<strong>in</strong>g of seasonal events has <strong>change</strong>d across <strong>Europe</strong>. A general trend towards earlier spr<strong>in</strong>g phenological stages<br />
(spr<strong>in</strong>g advancement) has been shown <strong>in</strong> many plant <strong>and</strong> animal species, ma<strong>in</strong>ly due to <strong>change</strong>s <strong>in</strong> climate conditions.<br />
• As a consequence of climate-<strong>in</strong>duced <strong>change</strong>s <strong>in</strong> plant phenology, the pollen season starts on average 10 days earlier<br />
than it did <strong>and</strong> is longer than it was <strong>in</strong> the 1960s.<br />
• The life cycles of many animal groups have advanced <strong>in</strong> recent decades, with events occurr<strong>in</strong>g earlier <strong>in</strong> the year, <strong>in</strong>clud<strong>in</strong>g<br />
frogs spawn<strong>in</strong>g, birds nest<strong>in</strong>g <strong>and</strong> the arrival of migrant birds <strong>and</strong> butterflies. This advancement is attributed primarily to<br />
a warm<strong>in</strong>g climate.<br />
• The breed<strong>in</strong>g season of many thermophilic <strong>in</strong>sects (such as butterflies, dragonflies <strong>and</strong> bark beetles) has been<br />
lengthen<strong>in</strong>g, allow<strong>in</strong>g, <strong>in</strong> pr<strong>in</strong>ciple, more generations to be produced per year.<br />
• The observed trends are expected to cont<strong>in</strong>ue <strong>in</strong>to the future. However, simple extrapolations of current phenological<br />
trends may be mislead<strong>in</strong>g because the observed relationship between temperature <strong>and</strong> phenological events may <strong>change</strong><br />
<strong>in</strong> the future.<br />
Relevance<br />
Phenology is the tim<strong>in</strong>g of seasonal events such<br />
as budburst, flower<strong>in</strong>g, dormancy, migration <strong>and</strong><br />
hibernation. Some phenological responses are<br />
triggered by mean temperature, while others are more<br />
responsive to day length or weather (Menzel et al.,<br />
2006, 2011; Urhausen et al., 2011). Altitude <strong>and</strong> the<br />
amount of urbanisation have an effect on temperature<br />
<strong>and</strong>, consequently, on phenology (Jochner et al., 2012).<br />
Generally, so-called 'spr<strong>in</strong>g advancement' is seen <strong>in</strong><br />
hundreds of plant <strong>and</strong> animal species <strong>in</strong> many world<br />
regions (Peñuelas et al., 2013). Changes <strong>in</strong> phenology<br />
affect the grow<strong>in</strong>g season <strong>and</strong>, thus, ecosystem<br />
function<strong>in</strong>g <strong>and</strong> productivity. Changes <strong>in</strong> phenology are<br />
hav<strong>in</strong>g an impact on farm<strong>in</strong>g (see Section 5.3), forestry,<br />
garden<strong>in</strong>g <strong>and</strong> wildlife. Changes <strong>in</strong> flower<strong>in</strong>g have<br />
implications for the tim<strong>in</strong>g <strong>and</strong> <strong>in</strong>tensity of the pollen<br />
season <strong>and</strong> related health effects.<br />
<strong>Climate</strong> warm<strong>in</strong>g affects the life cycles of all animal<br />
species. Populations at the northern range marg<strong>in</strong>s of<br />
a species' distribution may benefit from this <strong>change</strong>,<br />
whereas populations at the southern marg<strong>in</strong>s may<br />
encounter <strong>in</strong>creas<strong>in</strong>g pressure on their life cycles.<br />
Mild w<strong>in</strong>ters <strong>and</strong> the earlier onset of spr<strong>in</strong>g allow for<br />
an earlier onset of reproduction <strong>and</strong>, <strong>in</strong> some species,<br />
the development of extra generations dur<strong>in</strong>g the year.<br />
However, under unfavourable autumn conditions, the<br />
attempted additional generation can result <strong>in</strong> high<br />
mortality. This developmental trap has been suggested<br />
as the cause for the dramatic decl<strong>in</strong>e of the wall brown,<br />
a butterfly with non-overlapp<strong>in</strong>g, discrete generations,<br />
<strong>in</strong> <strong>Europe</strong> (Van Dyck et al., 2015). In the case of a<br />
phenological decoupl<strong>in</strong>g of species <strong>in</strong>teractions <strong>in</strong> an<br />
ecosystem (e.g. reduced pressure from parasitoids<br />
<strong>and</strong> predators), certa<strong>in</strong> populations may reach very<br />
high abundances that atta<strong>in</strong> or exceed damage<br />
thresholds <strong>in</strong> managed ecosystems (Baier et al., 2007).<br />
Desynchronisation of phenological events, such as<br />
shortened hibernation times, may deteriorate body<br />
condition, <strong>and</strong> <strong>in</strong>teractions between herbivores <strong>and</strong><br />
host plants could be lost (Visser <strong>and</strong> Holleman, 2001),<br />
<strong>and</strong> may also negatively affect ecosystem services such<br />
as poll<strong>in</strong>ation (Hegl<strong>and</strong> et al., 2009; Schweiger et al.,<br />
2010). There is robust evidence that generalist species<br />
with a high adaptive capacity are favoured, whereas<br />
specialist species will be affected mostly negatively<br />
(Schweiger et al., 2008, 2012; Roberts et al., 2011).<br />
Past trends<br />
A variety of studies show that there has been a general<br />
trend for plant, fungi <strong>and</strong> animal species to advance<br />
their spr<strong>in</strong>gtime phenology over the past 20–50 years<br />
(Cook et al., 2012). An analysis of 315 species of fungi<br />
<strong>in</strong> Engl<strong>and</strong> showed that, on average, they <strong>in</strong>creased<br />
their fruit<strong>in</strong>g season from 33 to 75 days between 1950<br />
<strong>and</strong> 2005 (Gange et al., 2007). Furthermore, climate<br />
warm<strong>in</strong>g <strong>and</strong> <strong>change</strong>s <strong>in</strong> the temporal allocation of<br />
nutrients to roots seem to have caused significant<br />
numbers of plant species to beg<strong>in</strong> fruit<strong>in</strong>g <strong>in</strong> spr<strong>in</strong>g<br />
as well as autumn. A study on 53 plant species <strong>in</strong> the<br />
United K<strong>in</strong>gdom found that they have advanced leaf<strong>in</strong>g,<br />
flower<strong>in</strong>g <strong>and</strong> fruit<strong>in</strong>g on average by 5.8 days between<br />
1976 <strong>and</strong> 2005 (Thackeray et al., 2010). Similarly,<br />
29 perennial plant species <strong>in</strong> Spa<strong>in</strong> have advanced leaf<br />
unfold<strong>in</strong>g on average by 4.8 days, with first flower<strong>in</strong>g<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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