Part 3: Food-Web Robustnessrockmore/CSSS2006/Dunne2006-3.pdfS = 28, 4 sub-webs Remove 2 Grasses, 2...
Transcript of Part 3: Food-Web Robustnessrockmore/CSSS2006/Dunne2006-3.pdfS = 28, 4 sub-webs Remove 2 Grasses, 2...
Part 3: Food-Web Robustness
In short, there is no comfortable theorem assuring thatincreasing diversity and complexity beget enhancedcommunity stability; rather, as a mathematical generalitythe opposite is true. The task, therefore, is to elucidatethe devious strategies which make for stability in enduringnatural systems.
Bob May (1973) Stability and Complexity in Model Ecosystems
Why might ecological network structure matter?
“Devious Strategies” for EcosystemStability, Robustness, Persistence
Robustness of small world, scale free networks
Albert, R., Jeong, H., and Barabási, A.-L. 2000. Error and attack tolerance of complex networks. Nature 406:378-382.
fraction of nodes removed
S = 6209, L = 12,2000, C = 0.003, scale free
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pat
h le
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(pro
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r slo
wne
ss o
f rou
ting)
Internet Routers
error - random nodes removed
attack - highdegree nodesremoved
• Small-world, scale-free networks: -are tolerant of errors (random node losses) -are vulnerable to attacks (removal of hubs)
• Demonstrated for -WWW -Internet routers -yeast protein network -metabolic networks
• What about networks that lack small-world, scale-free topology? (like food webs!)
An ecological perspective
What is the potential for biodiversity loss to triggercascading extinctions in food webs? Loss of prey items can lead to secondary extinctions
Other dynamics can mitigate or exacerbate trophic effects Species richness/ecosystem function
Average effects of species loss vs. loss of particular types of species
Does complexity confer robustness to perturbation? Dynamical Stability of Communities – MacArthur, May, and beyond Structural Stability of Communities – a complementary approach
Remove 4 Grasses 15 Secondary Extinctions
S = 61, C = 0.03
UK Endophytic Grassland Web
S = 42, C = 0.04
UK Endophytic Grassland Web
Remove 4 Insects 10 Secondary Extinctions
S = 28, 4 sub-webs
Remove 2 Grasses, 2 Insects 19 Secondary Extinctions
UK Endophytic Grassland Web
S = 5, 2 food chains
Total: 12 Primary Removals 44 Secondary Extinctions
UK Endophytic Grassland Web
Systematically remove taxa from food webs
4 criteria for species removal sequences (based on degree centrality)1) Most-connected species2) Most-connected species, but protect basal taxa3) Random species4) Least-connected species
If a taxon loses all prey items, it goes extinct
Quantify secondary extinctions
“Robustness” = proportion of species removed that results in 50% total species loss (primary removals + 2° extinctions)
Simulated species loss & secondary extinctions
Species Deletion Sequences:
Most connected ; Most connected, no basal deletions ; R andom ; Least connected
Species Deletion Sequences:
Most connected ; Most connected, no basal deletions ; R andom ; Least connected
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St. Marks Estuary
Dark dashed line: 100% total species loss line
Red dashed line: 50% total species loss line
Robustness: Proportion ofprimary species loss toreach ≥ 50% total speciesloss for a particular foodweb and type of loss
species removed / S
2° extinctions in empirical food webs
Species Deletion Sequences:
Most connected ; Most connected, no basal deletions ; R andom ; Least connected
Species Deletion Sequences:
Most connected ; Most connected, no basal deletions ; R andom ; Least connected
Coachella
(S=29, C=0.31)0.8
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Coachella
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Coachella
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Coachella
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St. Marks
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St. Marks
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El Verde
(S=155, C=0.06)0.8
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El Verde
(S=155, C=0.06)0.8
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El Verde
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Grassland
(S=61, C=0.03)0.8
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Grassland
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Grassland
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Increasing connectance of food web
What types of food webs tend to be robust?
Robustness: Proportion of primary removals that results in ≥ 50% total species loss
Structural robustness increases with connectance
Loss of most-connected taxa
y = 0.15Ln(x) + 0.63; R2 = 0.74
Random extinctions
y = 0.06Ln(x) + 0.55; R2 = 0.56
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Shelf
Benguela
Reef
Robustness of 19 food webs
connectance (L/S2)
robu
stne
ss
• Different types of biodiversity loss lead to different levels of potential 2° extinctions in food webs.
Loss of highly connected species (high 2° extinctions, threshold effects) Loss of random species (lower 2° extinctions) Loss of minimally connected species (usually few 2° extinctions) Protecting basal species generally mitigates 2° extinctions
• Food web structure (empirical and model) displays increasing robustness to species loss with increasing connectance. Higher C (and less skewed degree distributions) results in:
Lower sensitivity to species loss Delayed thresholds of increased sensitivity Differences among different types of species loss
• Structural robustness doesn’t vary with S or omnivory in empirical webs; in model webs structural robustness increases slowly with S.
Robustness Summary