The more avid blog followers amongst you will remember
towards the start of this blog, when we discussed phenology. We discussed it
with reference to our old friend the Pie Flycatcher (Ficedula hypoleuca), whom, according to studies by those such as
Both and Visser (2001) and Goodenough etal. (2010), is falling behind the peak of food abundance due to diurnally
triggered migration. Essentially, whilst the peak of prey species is creeping
ever forward at home in response to increasing temperatures, the Pied
Flycatcher is blissfully unaware and continuing to holiday in far flung
regions, essentially getting left behind. In this and the next few blogs, I
would like to take the opportunity to expand
upon this concept of phenology, exploring the important role it plays in
keeping ecosystems functional, and offer a few examples as to how climate
change, in a stunning turn of events, is throwing a spanner into the works.
I'm sure you remember our old friend the Ficedula hypoleuca |
I would like to begin by briefly recapping on the concept of
phenology, which was discussed so long ago and has been somewhat forgotten
under the incessant waves of blogs exploring range changes and invasive
species. Phenology, put simply, is the seasonal timing of certain events that
occur in an organism’s yearly cycle.
According to Gienapp et al.(2014) phenology has incredible importance for the fitness of a species, as for
most species there is a limited period wherein conditions are favourable for
critical lifecycle events. Activities such as reproduction, hibernation and
migration (as we have seen with the Ficedula
hypoleuca) are essential for survival and proliferation, and can be at the
mercy of how suitable a species phenology is to its surrounding ecosystem.
These ideal conditions can result from a variety of factors.
Often they can be set by weather conditions, whereby a certain temperature or
precipitation regime makes conditions favourable for specific activities. Other
times, they can be dictated by the phenology of other species; this is typical
in situations where predators are dependent on peak abundance of a certain prey
species to enable energy-intensive activities such as breeding and rearing
young (Gienapp et al 2014).
The essence of phenology |
Generally however, the forces that influence phenology are
climatic in nature. Due to year-to-year variation in the timing of certain
climatic conditions, phenological characteristics that are directly or
indirectly influenced consequently show a relative degree of plasticity – that
is, are relatively flexible. However, the ability of ecosystems to adapt to
short-term changes (those between years) is considerably greater than their
ability to adapt to long-term changes, a phenomenon largely due to differential
shifts across different trophic levels (Gienapp et al. 2014).
Species from different functional groups and trophic levels
within ecosystems (essentially, those that perform certain functions or exist
on different levels of the food chain) have experienced a varied magnitude of
response to climate change, which over the years has caused significant
advancements in phenology globally. These shifts, according to Gienapp et al. (2014), are typically more
pronounced at lower trophic levels. Gienappet al. explain this variation as resulting from species reacting to
differing environmental cues; for example, some species are sensitive to cues
in separate periods (some species may be sensitive to winter peaks in
temperature, whilst others to spring temperatures), whilst others are simply
more sensitive to conditions such as temperature, with more of its functions
influenced and hence will show greater plasticity. Some, like our unlucky
friend the Pied Flycatcher, aren’t sensitive to climatic triggers at all, and
instead rely on photoperiod (day length) triggers for phenology.
Phenology plays a critical role in all ecossytems - from the arctic to your back garden |
Across the globe, this is causing huge problems for
ecosystems. We are seeing increased instances of “decoupling” between
phenological relations, which can cause mass disruption for trophic
interactions through the altering of food-webs and can ultimately cause
destabilisation of ecosystems. Studies such as those by Edwards and Richardson(2004), that investigates the effect of phenological shifts on pelagic
ecosystems in the North Sea, and Visser and Holleman’s (2001) study on climatic
effects on winter moth (Operophtera
brumata) and Oak (Quercus robar)
bud burst synchrony are two examples I will be discussing in the coming blogs
that paint a very negative picture for the future of global ecosystems. We will
also be exploring the range of effects that phenological change can have on
inter-species interactions, such as what Stenseth et al. (2015) investigate in
their study on phenological effects on competitive relationships between Blue
Tits (Cyanistes caeruleus) and Great
Tits (Parus major).
Over the next couple of blogs, I hope that we can really
develop an appreciation for the extent of what is really a very intricate and
widespread problem. Phenological asynchrony, like range shifts and invasives, present huge barriers for ecosystems, and require an indepth and intricate understanding if we are to ever do anything to minimise the impacts of change on the life of our planet.
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