Spring rehearsal

 

This weekend brought me the first real rehearsal for the course I will assist in at the end of this month.

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A clear sign of spring: the daffodil (Narcissus)

As we did last year, we will take the students of biology of our university to the beautiful Hallerbos, a forest known for its bedazzling spring flora. There, we will introduce them to the ecology of forest types.

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A wonderful little patch of spring forest on a calcareous slope: wild garlic (Allium ursinum) as far as the eye could see

With the first warm spring days upon us, and a visit to the valley of the Lesse in Wallonia, this weekend brought me already a lot of these forest types ànd their accompanying spring flowers.

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In Belgium at its northern range edge: the stinking hellebore (Helleborus foetidus). 

Aim of the course is to give students a crash course in plant species, an overview of the variation in forest types and an idea about how abiotic conditions and species composition interact with each other, even on a very small scale. And – of course – let them admire the pure beauty of nature.

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Micro-environment for the fern Common polypody (Polypodium vulgare) on a mossy tree

Totally ready for the best teaching opportunity of the year!

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One of my new favourites of the season: the February daphne (Daphne mezereum)

 

 

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Just cause I like him

Just look at him, with its curly branches and fluffy catkins!

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I love the corkscrew hazel, one of the most beautiful views in early spring.

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There is not much I have to tell about him, though, just that he cheers up those days before temperatures finally start rising, and helps us overcoming the last weeks of darkness.

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Now we finally changed back to summer time, and all of a sudden the evenings became much longer. The corkscrew hazel got replaced by plenty of other pretty flowers and in the meantime, my science is going well: oh I feel like spring!

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Paper output

Our new paper on moving plants featured on the EOS-blog, the blog of the Belgian popular science journal!

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Nice read for the Dutch-speaking readers of this blog. For all others: this was the English version.

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Plant traffic along mountain roads

Roads help us to get from point A to point B. They are extremely useful structures for doing exactly that, which is why mankind has spend considerable amounts of energy to create a network of them that spans the whole globe, with tentacles reaching to the furthest desert and highest mountain region.

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Gravel road through Torres del Paine National Park in the Chilean Andes

But it is not only us humans who love these roads. Several species can use them to travel far and wide. Yes, even plants are not too proud to hitchhike a ride to discover new horizons. A new paper from the Mountain Invasion Research Network (MIREN, www.mountaininvasions.org) in Ecography shows that mountain roads all over the world indeed host busy plant traffic. With the help of thorough plant surveys along roads in eight mountain regions, they show how the elevational ranges of a wide variety of plant species change along these roads.

In short: the elevation range at which these species occur, differs significantly between roadsides and adjacent vegetation. Some species grow at higher elevations in the roadsides than in the surroundings, while others reside at lower elevations. In general, most of them have distributions spanning larger elevational ranges in the roadsides than next to them.

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Examples of different elevational niches in roadsides (red) and the adjacent vegetation (black) for Pinguicula vulgaris in Norway (left), and Tragopogon dubius in Montana (right).

That non-native species would use the mountain roads to expand their ranges towards higher elevations in the mountains does not come as a surprise anymore. These species have the reputation of being fast at following humans wherever they go. Expanding their ever-growing ranges into high mountain areas is just as predicted. This new study however expands on this by showing how several native species mimick this behaviour of upward movement and occur at higher elevations in mountains along roads than they do in the natural vegetation. Even more surprisingly, a group of high elevation species expands its range in the opposite direction, towards lower elevations.

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Average differences in elevation optimum for non-native (left) and native (right) species. Most non-native species are introduced in the lowlands, but their roadside distribution is more than 600 meters higher in elevation than their achieved distribution in the natural vegetation. Native species with a lowland origin follow the same pattern, highland species on the contrary have on average elevation optima of more than 200 meters lower in the roadsides than in the adjacent vegetation.

Roads thus play a much more significant role as drivers of range changes than always assumed, and for a wider range of species. They can provide important facilitation for climate-induced upward range shifts, for both native and non-native plant species, and they could serve as corridors to allow the exchange of alpine species between adjacent mountain sites.

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Mountain roads can span steep environmental gradients and as such facilitate transportation of species from one system to the other.

We have to keep in mind though that roadside systems in mountains, as everywhere, will be highly sensitive to short-term instability. It is however clear now that for various groups of plant species, these roadsides can serve as a way to go from one place to another, invade new areas and connect distant populations.

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Global invaders like white clover (Trifolium repens) make use of roadsides to invade mountain ranges.

From a species perspective, that might be a good thing. These processes will however also facilitate the reshuffling of the original species composition, and as always there will be winners and losers. The large set of non-native species shows the danger in this: roadsides might play an important role in the global homogenisation of the vegetation, with the same few species being successful in human-influenced ecosystems all over the world. From an ecosystem perspective, that is definitely a bad thing.

Reference

Lembrechts JJ et al. (2016). Mountain roads shift native and non-native plant species ranges. Ecography, doi: [10.1111/ecog.02200].

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Forest variation

Small-scale variation. It is a super important part of my research. I mostly look at it from a human perspective: how humans can disturb an ecosystem and change the whole hidden set of abiotic and biotic factors that drive these systems with it.

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Arum maculatum (arum lily), a species of the dry beech forest floor

Yet, microvariation is of course not limited to human influences, it is omnipresent in many ecosystem and an important driver of the large diversity we observe in many places.

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Golden saxifrage (Chrysosplenium), typical for wet forests

One of my favourite examples of natural microvariation is given by forests accompanying creeks. This forest type never counts for a large percentage of the forest area, yet it means an important lot for the biodiversity.

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As conditions can change dramatically over the course of tens of centimeters, so does the vegetation, with the most rare species survival only on these few small spots throughout the forests of the region.

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Forest anemone

We found a beautiful patch of this forest type in the Condroz in the Walloon region, last week. Even more interesting, it was accompanied by some human disturbance: old stone walls and remnants that provided the totally opposite conditions and were a walhalla for rock species.

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Maidenhair spleenwort, a typical rock fern

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On how leaves decompose

Climate poses a stronger control on litter decomposition than the species or the origin of the litter. That is the main conclusion of our recent paper in Biogeosciences (on which I collaborated primarily as a statistician).
Leaf of Norway maple - National Park Hoge Kempen
Getting to know the details about the decomposition of organic matter is a key part in our growing understanding of climate change, as it is a fundamental part of the cycle driving the movement of elements like carbon and nitrogen throughout the ecosystem. The latter is in its turn strong interwoven with the causes and effects of climate change.
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Experimental litter in bags in beech forest in Denmark  (These and the next pictures: MPE)
We now proved with data from a large European gradient that the rates at which this plant litter decomposes strongly depends on the climate. Temperature, precipitation and water content of the soil, all of them influenced how much of the litter remained, and which elements to find in the remaining parts.
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Pine forest in southern Estonia

 This clear correlation is interesting, as it allows us to predict the decomposition with a few parameters that are easy to obtain. Within our diverse set of sites throughout Europe, warmer and wetter climate makes the breakdown go faster. We could then start speculating if this decomposition would also accelerate when the climate gets warmer.
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Litter bags distributed on the forest floor

This nice correlation with the climate of course does not replace the role of all kinds of other factors that drive decomposition on a small scale (like mycorrhiza and soil organisms, for example), yet the broad correlations found along the European gradient prove that fast large-scale predictions are definitely possible.

Reference

Portillo-Estrada et al. (2016). Climatic controls on leaf litter decomposition across European forests and grasslands revealed by reciprocal litter transplantation experiments. Biogeosciences.

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