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Climatic differentiation of the invasive alien plant Senecio inaequidens (Asteraceae) during invasion

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(1)

Laboratory of Ecology

Gembloux Agricultural University, Belgium

Arnaud Monty Grégory Mahy

Climatic differentiation of the alien plant Senecio

inaequidens (Asteraceae) during invasion

When evolutionary phenomena make predictions uncertain…

(2)
(3)

IPCC 2002 Technical report

Projected impacts of changes

in mean climate and extreme

climatic events on terrestrial

and marine ecosystems:

 « Changes in phenology are expected to occur in

many species »

 « The general impact of climate change is that the

habitats of many species will move poleward or

(4)
(5)

Modeling a specie’s range modification due to global warming

(6)
(7)

Modeling a specie’s range modification due to global warming

These impacts are forecasted with the global assumption that species remain constant in their climatic optimal

requirements.

Species ‘follow’ their abiotic niche… Global warming

(8)
(9)

But:

Species are not static entities: they can

potentially develop adaptations in response to a changing environment !

Evolutionary theory might be ‘troublesome’ when trying to forecast global warming impacts !

(10)
(11)
(12)

In the present study, we address the following questions:

 Can plant populations develop adaptative differentiations in relation to climate (e.g. temperature) ?

 Is the timescale of this potential differentiation compatible with that of global warming?

Plant invasions are an opportunity to study these questions at a large biogeographical scale

(13)

Material &

Methods

(14)

Trying to answer these questions is made possible by the study of Senecio inaequidens invasion…

Senecio inaequidens DC. (Asteraceae):

• Perrenial herbaceous shrub from South Africa and Lesotho • Numerous yellow capitulae; mostly self-incompatible; tetraploid • Long flowering period (6 months)

(15)

Invasion History :

• The species was introduced to Europe as a wool alien in several locations linked to wool industries:

 Verviers (Belgium) : 1892  Bremen (Germany) : 1896  Mazamet (France) : 1936  Verona (Italy) : >1940

Trying to answer these questions is made possible by the study of Senecio inaequidens invasion…

(16)

Invasion History :

• During several decades, it was only found in the vicinity of wool processing areas

Trying to answer these questions is made possible by the study of Senecio inaequidens invasion…

1900- 1950 ~1900

(17)

Invasion History :

From 1950-1970, it started to spread throughout Europe, it climatic contrasted zones…

 During ~ 50 years, Senecio encountered increasing and

decreasing temperatures during invasion, while colonizing different altitudinal zones !

Trying to answer these questions is made possible by the study of Senecio inaequidens invasion…

1900- 1950

(18)
(19)

Global warming

Senecio invasion

- Temperature gradient +

(20)

Global warming

Senecio invasion

- Temperature gradient +

(21)

Global warming

Senecio invasion

- Temperature gradient +

(22)

Global warming

Senecio invasion

Migration

- Temperature gradient +

(23)

Global warming

Senecio invasion

Adaptation ?

- Temperature gradient +

(24)

Global warming

Senecio invasion

Adaptation ?

- Temperature gradient +

(25)

Global warming

Senecio invasion

Adaptation ?

- Temperature gradient +

(26)

Global warming

Senecio invasion

Adaptation ?

- Temperature gradient +

(27)

Global warming Senecio invasion Adaptation ? Adaptation ? - Temperature gradient + - Temperature gradient +

(28)

Topography:

0 – 1700 m

Seeds collection and population characterization along altitudinal gradients

French transect:

•5 altitudinal-climatic zones x 2 populations x 10 individuals • Temperature and summer drought gradient

• Mean annual T° : 16.1 to 6.3 °C

• Downward invasions: + 3.4°C • Upward invasions : - 6.4°C

(29)

Seeds collection and population characterization along altitudinal gradients

Belgian transect:

• 4 altitudinal-climatic zones x 2 populations x 10 individuals

• Temperature and rainfall gradient

• Mean annual T° 9.6 to 5.7 °C

Topography:

(30)

Seed collection and elimination of intra-maternal effects Parent individual (random) Capitulae collected Sorting of achenes 10 biggest achenes without anomaly MEASUREMENTS: • Plant height • Plant volume

• Plant above-ground biomass

In situ population characterization

10 biggest individuals

(31)

Sowing and measurements

Sown in one pot

10 biggest achenes without anomaly

1 plant was kept

One plant per parent

individual

Germination study (n = 2400)

Phenology and growth study (n = 240)

(32)

Sowing and measurements

Sown in one pot

10 biggest achenes without anomaly

1 plant was kept

One plant per parent

individual

• Germination delay • Flowering delay (since germination) • Height at first flowering

• Final height

• Final above-ground biomass • Reproductive allocation

(33)
(34)

For each transect separetely:

Comparisons of transect zones  ANOVAs

Linear correlation  Population trait means vs Altitude

(35)
(36)

Topography:

0 – 1700 m

(37)

In situ population characterization

• Plant height

• Plant volume

(38)

In situ population characterization

• Plant height

• Plant volume

• Above-ground biomass

Significant differences between transect zones

(39)

In situ population characterization

• Plant height

• Plant volume

(40)

In situ population characterization

• Plant height

• Plant volume

• Above-ground biomass

In the field, plants from lower elevations grow larger

(41)

Common garden • Germination delay

• Flowering delay (since germination) • Height at first flowering

• Final height

• Final above-ground biomass • Reproductive allocation

(42)

Common garden • Germination delay

• Flowering delay (since germination) • Height at first flowering

• Final height

• Final above-ground biomass • Reproductive allocation

Significant differences between transect zones

(43)

Common garden • Germination delay

• Flowering delay (since germination) • Height at first flowering

• Final height

• Final above-ground biomass • Reproductive allocation

(44)

Common garden • Germination delay

• Flowering delay (since germination) • Height at first flowering

• Final height

• Final above-ground biomass • Reproductive allocation

Significant decrease with altitude, (especially along downward invasion)

(45)

Common garden • Germination delay

• Flowering delay (since germination) • Height at first flowering

• Final height

• Final above-ground biomass • Reproductive allocation

Significant increase with altitude, along downward invasion only

(46)

Common garden • Germination delay

• Flowering delay (since germination) • Height at first flowering

• Final height

• Final above-ground biomass • Reproductive allocation

Significant increase with altitude, along downward invasion only

In the common garden, plants from lower

elevations tend to germinate earlier, grow larger and

(47)

Belgian transect

Topography:

0 – 500 m

Same altitudinal pattern for growth traits in the common garden… whereas less marked !

(48)
(49)

 This study reports a species differentiation in relation to a

spatial climatic variation… what about a temporal climatic

variation (global warming)?

 Plants from lower elevations tend to germinate earlier, to bloom at a greater age and to allocate more ressources to growth (Changes in germination, phenology and growth allocation!)

 Differentiation was steeper while the species encountered an

increase in temperature (downward invasion)

 The differentiation is most likely adaptative for: - Typical clinal variation

- Same pattern along both independent gradients

 Adaptative differentiations took place in a timescale of less

(50)

 Other studies reported adaptative differentiation in relation to climate for invasive species

(Tamarix sp.; Solidago spp.; Impatiens

(51)

 Other studies reported adaptative differentiation in relation to climate for invasive species

(Tamarix sp.; Solidago spp.; Impatiens

glandulifera)

 In this point of view, global

warming can force evolution of species

But are all species able to adapt ?

If not, global warming would favour

some species (e.g. invasive species) through diversification while

disadvantaging others!

(52)

Take-home messages:

 Species are not static entities: increasing research

suggests that adaptations (e.g. in relation to a changing climate) can appear faster than previously thought.

This makes species distribution models even more uncertain: need to quantify the differentiation to include it in models…

 Global warming can force the irreversible differentiation of species. In the case of alien invasive species, a great

adaptation potential is likely to induce a positive reaction to global warming…

(53)

Thank You

Laboratory of Ecology

Gembloux Agricultural University, Belgium

This research was supported by the project FRFC 2.4605.06 from the FONDS NATIONAL DE LA RECHERCHE SCIENTIFIQUE.

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