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Title: Physics in Ecology:


1
Physics in Ecology
  • The Utility of the Useless
  • Community and Conservation Ecology Group
  • Rampal S. Etienne

2
The Utility of the Useless
  • Some wisdom from Taoism (Zhuang-Zi) The useless
    tree

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  • Hear me out!

e
7
Darwins old Indian ruins
8
Darwins old Indian ruins
  • Throw up a handful of feathers, and all must
    fall to the ground according to definite laws
    but how simple is the problem where each shall
    fall compared to that of the action and reaction
    of the innumerable plants and animals which have
    determined, in the course of centuries, the
    proportional numbers and kinds of trees now
    growing on the old Indian ruins!

Darwin 1859. On the origin of species by means of
natural selection, or the preservation of
favoured races in the struggle for life. John
Murray
9
Physics and ecology
  • Can physics explain the diversity on the old
    Indian ruins as well as it can explain the
    falling of a handful of feathers?
  • A new philosophy
  • from detailed species/system specific
    (simulation) models to
  • first-order (analytical) approximations of more
    general systems

10
Mind the cultural differences
  • Vegetation was quantified using ocular cover
    estimates.
  • I just eyeballed the plant cover and might be off
    by an order of magnitude.
  • Sample points were subjectively placed using the
    relevé method.
  • Id already made my conclusions, and needed some
    data to support them.
  • The site was surveyed using random meander
    transects and prioritized based on habitat.
  • There was no way I was going to crawl through
    that poison oak looking for rare plants.

Mahony 2009. Ecology meets physics envy.
http//www.lablit.com/article/513
11
Phenomena to be explained
  • Species abundance distribution (SAD)
  • Species-area relationship
  • Species-time relationship
  • Diversity-productivity relationship
  • Diversity-hetereogeneity relationship
  • Diversity-habitat (loss) relationship
  • Phylogenetic diversity

12
Physics in ecology
  • Three fields mainly driven by physicists
  • I. Neutral theory of biodiversity
  • Alonso, Banavar, Chave, Cornell, Etienne,
    Haegeman, Maritan, McKane, ODwyer, Vanpeteghem,
    Volkov, Zillio
  • Bell, He, Hubbell, Jabot, Pueyo, Rosindell,
    Walker
  • II. Entropy maximization
  • Banavar, Dewar, Etienne, Haegeman, Harte,
    Maritan, Porte, Zillio
  • Loreau, Pueyo, Shipley
  • III. Metabolic ecology

13
I. The neutral theory of biodiversity
14
Ecology and chance
  • When we look at the plants and bushes clothing
    an entangled bank, we are tempted to attribute
    their proportional numbers and kinds to what we
    call chance. But how false a view is this!

Darwin 1859. On the origin of species by means of
natural selection, or the preservation of
favoured races in the struggle for life. John
Murray
15
Perspectives in community ecology
  • Classical view niche theory
  • Functional differences between species cause
    differences in resource and energy requirement
    which define its niche.
  • With sufficient variability in resources,
    multiple species can coexist.
  • New view neutral theory
  • Species are functionally equivalent.
  • Species coexist in a stochastic balance between
    speciation / immigration and extinction.
  • Motivation Paradox of the plankton

16
Neutral theory ecological nihilism1
Stephen P. Hubbell
1Schilthuizen 2006 Bionieuws
17
Ingredients of the neutral theory
  • Neutrality all individuals in an ecological
    community are functionally equivalent, regardless
    of species
  • Stochasticity
  • Two sources of diversity
  • Speciation
  • Immigration

18
Neutral theory is not really new
  • Grinnells (1922) accidentals (singletons)
  • Explained by dispersal
  • Gleasons (1926) individualistic concept
  • Independent species, chance, dispersal
  • MacArthurs (1957) broken stick
  • Often seen as niche model, but symmetric and
    stochastic
  • Can be derived within neutral framework!
  • MacArthur Wilson (1967) island biogeography
  • Stochasticity, dispersal, speciation, extinction
  • Caswell (1976) first dynamical neutral model
  • Borrowing concepts from population genetics
  • Lottery and voter models (Fagerström 1988,
    Bramson et al. 1996)

Etienne Alonso 2007. J. Stat. Phys. 128 485-510
19
Why then so popular now?
  • Because physicists got involved?
  • Quantitative / analytical predictions
  • Because it was popularized by an ecologist?
  • Hubbells motivation was the amazing biodiversity
    in tropical forests unexplained by classical
    niche theory

20
Theory vs. model
  • Theory the fundamental idea
  • Model an implementation of the idea

21
Ingredients of the main neutral model
  • Neutrality birth, death and immigration rates
    are equal for all individuals, regardless of
    species
  • Stochasticity purely demographic
  • Two scales mainland-island
  • Local (community) immigration
  • Regional (metacommunity) speciation by point
    mutation
  • Zero-sum individuals saturate all limiting
    resources (e.g. space) ? constant size

22
The world according to Hubbell
n
23
Neutral theorys predictions
  • Species-abundance distributions
  • Essential a species abundance caused by
    adaptation or chance?
  • Diversity patterns
  • With area, time, productivity, heterogeneity,
    habitat loss, .
  • Evolutionary characteristics
  • speciation rates, species longevity, phylogeny

24
Master equation approach (1)
  • Master equation for abundance of one species

Vallade Houchmandzadeh 2003. Phys. Rev. E 58
061902
25
Master equation approach (2)
  • Master equation for abundance vector S

Haegeman Etienne 2009. Bull. Math. Biol. In
press. Etienne Haegeman 2009. Subm.
26
Master equation approach (3)
  • Master equation for abundance vector N

Allouche Kadmon 2009. Ecol. Lett. In press
27
Genealogical approach
  • A local community
  • 7 individuals
  • 2 species (R and G)
  • 3 ancestors (1, 2 and 3)
  • Events
  • Death
  • Immigration
  • Coalescence

Etienne Olff 2004, Ecol. Lett. 7
170-175Etienne 2005. Ecol. Lett. 8
253-260Etienne 2007. Ecol. Lett. 10
608-618 Rosindell et al. 2008. Ecol. Inf. 3
259-271 Etienne 2009. J. Theor. Biol. 257
510-514 Etienne 2009. Ecology 90 847-852
28
Solution for SAD of a sample
29
Applications
30
Species abundance distribution
Volkov et al. 2003. Nature 438 658-661. Many
other papers
31
Species-area relationship
Rosindell Cornell 2007. Ecol. Lett.10 586-595
32
Effect of habitat heterogeneity
Kadmon Allouche 2007. Am Nat. 170 443-454
33
Effect of disturbance and productivity
Kadmon Benjamini 2006. Am Nat. 167 939-946
34
Effect of speciation on the SAD
  • Point mutation (blue)
  • Constant per individual (solid)
  • Constant per species (dashed)
  • Random fission (red)
  • Constant per individual (solid)
  • Constant per species (dashed)
  • Effect is weak when dispersal is limited

Etienne et al. 2007. Oikos 116 241-258 Haegeman
Etienne 2009. Bull. Math. Biol. In press.
Etienne Haegeman 2009. Subm.
35
Point mutation vs random fission (1)
  • Better fit of SADs

Etienne et al. 2007. Oikos 116 241-258 Etienne
Haegeman 2009. Subm.
36
Point mutation vs random fission (2)
  • But poorer prediction of
  • Speciation rate
  • Species longevity
  • Average species lifetime
  • Lifetime of highly abundant species
  • Can be resolved by protracted speciation
  • Speciation as a process rather than an
    instantaneous event

Ricklefs 2003. Oikos 100 185-192 Nee 2005.
Funct. Ecol. 19 173-176 Etienne Haegeman 2009.
Subm. Rosindell et al. 2009. Subm.
37
Robustness of the predicted SAD
  • Zero-sum assumption can be relaxed to
  • Independent species
  • Community-level density dependence
  • Neutrality can be relaxed to
  • Demographic trade-offs
  • Heterogeneous habitats

Etienne et al. 2007. J. Theor. Biol. 248 522-536
Etienne Haegeman 2008. J. Theor. Biol. 252
288-294. Allouche Kadmon 2009. J. Theor. Biol.
258 274-280. Allouche Kadmon 2009. Ecol. Lett.
In press.
38
The merits of neutral theory (1)
  • New philosophy of science in ecology
  • Parsimony Ockhams razor
  • Hypothesis testing against null model
  • Classical or Bayesian
  • To what extent do species differences matter?
  • First order approximation
  • Allows studying the effect of a particular
    mechanism without confounding / complicating
    differences between species
  • Difference between theory and model

39
The merits of neutral theory (2)
  • Information content in / confrontation to data
  • Sampling theory predictions are for samples
  • Connection between evolutionary and ecological
    factors
  • Effect of speciation mode on community structure
  • Matter of scale of perspective
  • Population ecologists treat individuals of same
    species as functionally equivalent in simplest
    model
  • Metapopulation ecologists treat populations of
    species as functionally equivalent in simplest
    model

40
The merits of neutral theory (3)
  • Emergent neutrality (Holt 2006)
  • Speciation (e.g. allopatric) consistent with
    functionally equivalent species
  • At large spatial scales, dispersal limitation may
    be overwhelmingly dominating
  • Convergent evolution because of similar
    constraints
  • Emerging guilds of functionally equivalent
    species (Scheffer Van Nes 2006, Bonsall et al.
    2004)

41
Dont throw out the baby with the bathwater!
42
II. Entropy maximization
43
Ecology and thermodynamics (1)
  • Ecological complexity poses challenges to
    con-ventional scientific ways of knowing. Ecology
    is not like thermodynamics, in which complexity
    can be simplified through statistical averaging
    of large numbers of identically behaving
    components

Taylor 2005. Unruly Complexity Ecology,
Interpretation, Engagement. University of Chicago
Press
44
Ecology and thermodynamics (2)
  • Aims to understand and predict the macroscopic
    behaviour of complex systems consisting of large
    numbers of interacting microscopic components.
  • Due to the large number of components
    (individual organisms), the same macroscopic
    behaviour can be realised in many different ways
    microscopically.
  • Ecological patterns are expressions of the
    community-level behaviour that can be realised in
    the greatest number of ways at the individual
    level.

Dewar Porte 2008. J. Theor. Biol. 251 389403
45
Ecology and thermodynamics (3)
  • Ecosystems have been characterized as
    medium-number systems for which both the
    approaches of mechanistic and statistical
    modelling are problematic there are too many
    components to describe each of the components
    explicitly, and there are not enough components
    to work with averaged properties.

Haegeman Loreau 2008. Oikos 117 1700-1710
citing ONeill et al. 1986. A hierarchical
concept of ecosystems. Princeton Univ. Press
  • Empirical studies should settle the question
    whether this method is useful.

Haegeman Loreau 2008. Oikos 117 1700-1710
46
Entropy maximization (1)
  • Aim predicting macroscopic behavior of complex
    systems consisting of large numbers of
    microscopic degrees of freedom, subject to given
    constraints
  • Constraints (C) are generally insufficient to
    determine the microstate i
  • Focus on the probability pi of microstate i
  • Macroscopic quantity Q is expectation value
  • Problem to be solved construct p that satisfies
    constraint but contains no other information

47
Entropy maximization (2)
  • Maximizing entropy H does exactly that
  • Only p that maximizes H encodes just information
    on C relative to prior information q

48
Example 1 vineyards
  • In 12 vineyards during 42 years, measurements of
  • relative abundance of 30 species
  • average trait value for 8 traits
  • Constraints

Shipley et al. 2006. Science 314 812814
49
Example 1 performance
Shipley et al. 2006. Science 314 812814
50
Example 1 problems (1)
  • Circularity
  • Averaged trait values were computed using species
    traits and relative abundances
  • Low-dimensionality
  • One-individual formulation shows only part of
    power of EM
  • Triviality
  • Constraints almost completely determine p

Haegeman Loreau 2008. Oikos 117
1700-1710 Haegeman Loreau 2009. Oikos. In press.
51
Example 1 problems (2)
Haegeman Loreau 2008. Oikos 117 1700-1710
52
Example 2 nitrogen-limited grasslands
  • S 26 species constrained by space (62
    individuals per m2) and resources (5.9 g nitrogen
    m-2 yr-1)
  • Solution

Dewar Porte 2008. J. Theor. Biol. 251 389-403
using data of Harpole Tilman 2006. Ecol. Lett.
9 1523.
53
Example 2 performance
54
Example 2 analogies
  • ß and µ are analogous to inverse temperature and
    chemical potential (of a physical system with
    constraints on average number of particles and
    energy)
  • Consequence Two interacting communities will
    eventually have equal ß and µ.

55
Example 3 general macro-ecology (1)
  • S0 species in area A0 with total number of
    individuals N0 and energy E0, probability density
    R(n,e), spatial abundance distribution PA(n)

Harte et al. 2008. Ecology 89 27002711
56
Example 3 performance (1)
  • Species-abundance distribution
  • Species-level spatial abundance distribution

Harte et al. 2008. Ecology 89 27002711
57
Example 3 performance (2)
  • Species-area curve
  • Endemics-area curve

Harte et al. 2008. Ecology 89 27002711
58
Example 3 discussion
  • No prior q needed 1/n behavior predicted, not
    assumed
  • Energy distribution is predicted, not assumed
  • With more constraints, EM entails non-realistic
    species-abundance distribution

Harte et al. 2008. Ecology 89 27002711
59
Example 4 spatial abundance distribution (1)
  • Different formulations
  • State of system is single-cell abundance
  • State of system is abundance vector for all cells
  • With abundance vectors several EM solutions are
    possible, differing in
  • Constraints
  • Hard total number of individuals is N
  • Soft average total number of individuals is N
  • Configurations
  • Labeled
  • Unlabeled

Haegeman Etienne. 2009. Subm.
60
Example 4 spatial abundance distribution (2)
multinomial, RP model
binomial
  • Joint distribution Marginal distribution

geometric
uniform
geometric
negative hypergeo-metric
SD model
negative binomial
Haegeman Etienne. 2009. Subm.
61
Example 4 spatial abundance distribution (3)
  • Joint distribution approach reveals that there is
    not one unique EM solution
  • Harte et als different models can all be seen as
    EM solutions
  • Unclear how Hartes model fits in
  • Mostly like unlabeled-hard/soft EM problem
  • But these are not scale-consistent
  • Choice of prior and system description important
    (and exchangeable)

62
A future for physics in ecology
  • Macro-ecological patterns may have simple,
    unifying physics-like explanations
  • Many ecological details inessential
  • Future work
  • Neutral theory
  • Space
  • Time
  • Phylogenetics
  • Entropy maximization
  • Prior
  • Constraints

63
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