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Community resistance to
biological invasions : role of
diversity and network structure
Patrice DAVID, François MASSOL
CNRS
COREIDS
Biological invasions
Rabbits
(Orycolagus cuniculus)
Water lilies
(Eicchornia crassipes)
Nile perchs
Lates niloticus
Zebra mussels
(Dreissena polymorpha)
- A worldwide revolution
in ecosystems and a major
component of global
change
- Concerns all kinds of
organisms and habitats
- Large impacts on
biodiversity but largely
unpredictable
biodiversity.europa.eu
Networks of species interactions
• Impacts of invasions
depend on interactions
with resident species
• Interactions are organized
in networks (eg food
webs)
• What properties of
networks make them
sensitive to invasion ?
The COREIDS group
• A group of scientists working
on invasions and/or
networks in France, Canada,
New Zealand
• Field biologists,
experimental biologists,
statisticians, theoreticians
• Synthesis, Meta-analysis,
modelling
Four types of local impacts of
invaders on food webs
I
R
1. Top-down
Invasive
predator
Resident
prey
Euglandina rosea
(predatory « wolf » snail)
Endemic
Partula spp
(tree snails)
- Direct predation is responsible for most
species extinctions following invasions
(Moorea
island)
Four types of local impacts of
invaders on food webs
I
R1
2. Exploitative
competition
R2
Invasive
species
Resident
prey
Resident
competitor
Endemic
Ceratitis catoirii
C. Capitata
Introd 1939
Locally
cultivated
fruit
(La Réunion
island)
Four types of local impacts of
invaders on food webs
I
R1
2. Exploitative
competition
R2
Invasive
species
Resident
prey
Resident
competitor
Endemic
Ceratitis catoirii C. Capitata
Introd 1939
Locally
cultivated
fruit
C. rosa
Introd 1955
(La Réunion
island)
Four types of local impacts of
invaders on food webs
I
R1
2. Exploitative
competition
R2
Invasive
species
Resident
prey
Resident
competitor Endemic
Ceratitis catoirii
C. Capitata
Introd 1939
Locally
cultivated
fruit
C. rosa
Introd 1955
Bactrocera zonata
Introd 1991
- Invasive competitors often arrive in successive series
- Resident species are reduced or displaced more often than they go extinct
(La Réunion
island)
Four types of local impacts of
invaders on food webs
I
3. Bottom-up
Invasive
prey
Resident
predator
- Resident predators may limit populations of invasive species (biotic resistance)
- Invasive species usually have positive effects on their predators
R
Invasive Gobies (Neogobius
melanostomus)
Endemic water snake (Nerodia
sipedon insularum)
(Lake Erie)
Four types of local impacts of
invaders on food webs
I
3. Bottom-up
Resident
predator
- Invasive species usually have positive effects on their predators
- … but these benefits are sometimes outweighed by competition with
more profitable resident prey
- This situation is common with invasive plants eg Caulerpa taxifolia, Rubus
alceifolius >> herbivore diversity decreases
R
R2
Resident
competitor
Horned Lizard
Phrynosoma coronatum
Invasive
prey
Argentine ant
Linepithema humile
Native ant
Crematogaster californica
(California)
Four types of local impacts of
invaders on food webs
I
4. Apparent
competition
Resident
predator R
R2
Resident
prey
Invasive
prey
Golden eagle
Aquila chrysaetos
Island fox
Urocyon littoralis
Feral pig
Sus scrofa
- Invasive species may benefit local generalist predators and
indirectly affect local species
(California
channel
islands)
The filter hypothesis• ASYMMETRY : Invaders tend to
have more impact (often strong) on
natives than natives have on
invaders; they are fiercer
predators, better defended prey,
and stronger competitors
The filter hypothesis• ASYMMETRY : Invaders tend to
have more impact (often strong) on
natives than natives have on
invaders; they are fiercer
predators, better defended prey,
and stronger competitors
• LACK OF COEVOLUTION :
Invaders and residents are
evolutionary naive to each other :
their interactions may often be
extreme
• Major outcomes
Predation
efficiency
coevolved
Not coevolved
Frequency
Example of predator introduction
The filter hypothesis• ASYMMETRY : Invaders tend to
have more impact (often strong) on
natives than natives have on
invaders; they are fiercer
predators, better defended prey,
and stronger competitors
• LACK OF COEVOLUTION :
Invaders and residents are
evolutionary naive to each other :
their interactions may often be
extreme
• FILTER : Only species that happen
to be tolerant to resident species
successfully invade
• Major outcomes
Predation
efficiency
coevolved
Not coevolved
Mean
natives
Invasion
fails
Invasion succeeds
Mean
invaders
Frequency
Example of predator introduction
Propagation of effects in the recipient
network : attenuation or amplification ?
I
Theoretical predictions
• Theoretical models : construction of model food webs by
addition of species and evolution of trophic traits (eg body
size)
• Introduce virtual invaders, measure probability of success
and impact
• Diversity >> filling of niche space >> less invasions and
smaller impacts
• Connectance : no clear effect
Empirical data : Three cases of far-reaching
impact of species introduction
1) Trophic
cascades in lakes
Favoured by the relatively
low diversity and high
efficiency of primary
consumption of
phytoplankton
(unlike in many plant-based
terrestrial ecosystems)
http://www.lmvp.org
Empirical data : Three cases of far-reaching
impact of species introduction
2) Disequilibrium
- Recent human modification :
eutrophication, elimination of top
predators, replacement of native
forest by agriculture or secondary
habitat >> low diversity, lots of
unexploited resource
- Evolutionary immaturity : remote
islands lacking particular groups >>
idem
http://www.lmvp.org
Guam island
Tree snake
Boiga irregularis
Empirical data : Three cases of far-reaching
impact of species introduction
3) Ecosystem
engineering
- Large modification of habitat:
sessile filter-feeders : water
clarification, creation of habitats
- Attracts many new species, limits
many others, deeply reorganizes
energy and matter fluxes in lake
ecosystem (pelagic >> benthic)
http://ian.umces.edu
Zebra mussel
Great Lakes
Detritivore Predator
Omnivore Producer
Detritivore Omnivore Producer
Herbivore Predator
Aquatic Terrestrial
Increases
Effect on
diversity
Decreases
Meta-analysis
Lessons for ecosystem conservation
• Fight against causes of invasions rather than invasions
themselves : pollution, perturbation, predator removal
• Islands are hypersensitive due to past isolation : prevent
introductions, especially of generalist predators
• Eradication is usually costly and ineffective; resident
communities often change ecologically and evolutionarily
after invasions, there is often no way back. Look for
mitigation rather than eradication.
Next issue of
Advances in Ecological Research
Networks of Invasions
#56
2017
Thanks for your attention

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Community resistance to biological invasions : role of diversity and network structure.

  • 1. Community resistance to biological invasions : role of diversity and network structure Patrice DAVID, François MASSOL CNRS COREIDS
  • 2. Biological invasions Rabbits (Orycolagus cuniculus) Water lilies (Eicchornia crassipes) Nile perchs Lates niloticus Zebra mussels (Dreissena polymorpha) - A worldwide revolution in ecosystems and a major component of global change - Concerns all kinds of organisms and habitats - Large impacts on biodiversity but largely unpredictable biodiversity.europa.eu
  • 3. Networks of species interactions • Impacts of invasions depend on interactions with resident species • Interactions are organized in networks (eg food webs) • What properties of networks make them sensitive to invasion ?
  • 4. The COREIDS group • A group of scientists working on invasions and/or networks in France, Canada, New Zealand • Field biologists, experimental biologists, statisticians, theoreticians • Synthesis, Meta-analysis, modelling
  • 5. Four types of local impacts of invaders on food webs I R 1. Top-down Invasive predator Resident prey Euglandina rosea (predatory « wolf » snail) Endemic Partula spp (tree snails) - Direct predation is responsible for most species extinctions following invasions (Moorea island)
  • 6. Four types of local impacts of invaders on food webs I R1 2. Exploitative competition R2 Invasive species Resident prey Resident competitor Endemic Ceratitis catoirii C. Capitata Introd 1939 Locally cultivated fruit (La Réunion island)
  • 7. Four types of local impacts of invaders on food webs I R1 2. Exploitative competition R2 Invasive species Resident prey Resident competitor Endemic Ceratitis catoirii C. Capitata Introd 1939 Locally cultivated fruit C. rosa Introd 1955 (La Réunion island)
  • 8. Four types of local impacts of invaders on food webs I R1 2. Exploitative competition R2 Invasive species Resident prey Resident competitor Endemic Ceratitis catoirii C. Capitata Introd 1939 Locally cultivated fruit C. rosa Introd 1955 Bactrocera zonata Introd 1991 - Invasive competitors often arrive in successive series - Resident species are reduced or displaced more often than they go extinct (La Réunion island)
  • 9. Four types of local impacts of invaders on food webs I 3. Bottom-up Invasive prey Resident predator - Resident predators may limit populations of invasive species (biotic resistance) - Invasive species usually have positive effects on their predators R Invasive Gobies (Neogobius melanostomus) Endemic water snake (Nerodia sipedon insularum) (Lake Erie)
  • 10. Four types of local impacts of invaders on food webs I 3. Bottom-up Resident predator - Invasive species usually have positive effects on their predators - … but these benefits are sometimes outweighed by competition with more profitable resident prey - This situation is common with invasive plants eg Caulerpa taxifolia, Rubus alceifolius >> herbivore diversity decreases R R2 Resident competitor Horned Lizard Phrynosoma coronatum Invasive prey Argentine ant Linepithema humile Native ant Crematogaster californica (California)
  • 11. Four types of local impacts of invaders on food webs I 4. Apparent competition Resident predator R R2 Resident prey Invasive prey Golden eagle Aquila chrysaetos Island fox Urocyon littoralis Feral pig Sus scrofa - Invasive species may benefit local generalist predators and indirectly affect local species (California channel islands)
  • 12. The filter hypothesis• ASYMMETRY : Invaders tend to have more impact (often strong) on natives than natives have on invaders; they are fiercer predators, better defended prey, and stronger competitors
  • 13. The filter hypothesis• ASYMMETRY : Invaders tend to have more impact (often strong) on natives than natives have on invaders; they are fiercer predators, better defended prey, and stronger competitors • LACK OF COEVOLUTION : Invaders and residents are evolutionary naive to each other : their interactions may often be extreme • Major outcomes Predation efficiency coevolved Not coevolved Frequency Example of predator introduction
  • 14. The filter hypothesis• ASYMMETRY : Invaders tend to have more impact (often strong) on natives than natives have on invaders; they are fiercer predators, better defended prey, and stronger competitors • LACK OF COEVOLUTION : Invaders and residents are evolutionary naive to each other : their interactions may often be extreme • FILTER : Only species that happen to be tolerant to resident species successfully invade • Major outcomes Predation efficiency coevolved Not coevolved Mean natives Invasion fails Invasion succeeds Mean invaders Frequency Example of predator introduction
  • 15. Propagation of effects in the recipient network : attenuation or amplification ? I
  • 16. Theoretical predictions • Theoretical models : construction of model food webs by addition of species and evolution of trophic traits (eg body size) • Introduce virtual invaders, measure probability of success and impact • Diversity >> filling of niche space >> less invasions and smaller impacts • Connectance : no clear effect
  • 17. Empirical data : Three cases of far-reaching impact of species introduction 1) Trophic cascades in lakes Favoured by the relatively low diversity and high efficiency of primary consumption of phytoplankton (unlike in many plant-based terrestrial ecosystems) http://www.lmvp.org
  • 18. Empirical data : Three cases of far-reaching impact of species introduction 2) Disequilibrium - Recent human modification : eutrophication, elimination of top predators, replacement of native forest by agriculture or secondary habitat >> low diversity, lots of unexploited resource - Evolutionary immaturity : remote islands lacking particular groups >> idem http://www.lmvp.org Guam island Tree snake Boiga irregularis
  • 19. Empirical data : Three cases of far-reaching impact of species introduction 3) Ecosystem engineering - Large modification of habitat: sessile filter-feeders : water clarification, creation of habitats - Attracts many new species, limits many others, deeply reorganizes energy and matter fluxes in lake ecosystem (pelagic >> benthic) http://ian.umces.edu Zebra mussel Great Lakes
  • 20. Detritivore Predator Omnivore Producer Detritivore Omnivore Producer Herbivore Predator Aquatic Terrestrial Increases Effect on diversity Decreases Meta-analysis
  • 21. Lessons for ecosystem conservation • Fight against causes of invasions rather than invasions themselves : pollution, perturbation, predator removal • Islands are hypersensitive due to past isolation : prevent introductions, especially of generalist predators • Eradication is usually costly and ineffective; resident communities often change ecologically and evolutionarily after invasions, there is often no way back. Look for mitigation rather than eradication.
  • 22. Next issue of Advances in Ecological Research Networks of Invasions #56 2017 Thanks for your attention