Title: Niche and neutrality debate in community ecology
1Niche and neutrality debate in community ecology
By Sandra P. Galeano
2Diversity maintenances in communities
- Explaining maintenance of species diversity
within - communities one of the most fundamental
- questions in ecology
- Patterns from mechanisms? mechanisms by
- patterns?
- Niche - neutrality debate
3Niche-neutrality debate some history
- The classical niche paradigm
- Grinnell (1917) Geophysical spatial unit
with the niche relationships of the California
thrashers - Gause (1934) Competitive exclusion
principle - From here, discussion relies almost exclusively
on competition - Hutchinson (1957) Niche hypervolume,
-
-
- Ecological niche sufficient and necessary to
explain coexistence!
4The competitive niche paradigm
- D. Tilman
- Resource based theory R (1982,1988)
- Life history trade-offs, essential for
coexistence - Arbitrary number of species could coexist based
on - fugitive species concept of Hutchinson!
- Hurtt Pacala (1995) Recruitment and dispersal
- limitation competitive exclusion infinitely
delayed - S. Hubbell (1990s)
- Not all species clearly niche differentiated.
Competitive exclusion or character displacement
not always evident Ecological equivalent
hypothesis and neutral theory
Is ecological niche sufficient to explain
coexistence?
5Neutral theorys in Biology
- Neutral theory in Biology did not start with
- Hubbells theory
2001
1960s
6Niche-neutrality debate some history
- The unified neutral theory of biodiversity and
biogeography (UNT) - S. Hubbell (2001)
Annual survival
after observing
Trade-off (gtsurvival shade sps-low growth in
sun) Species undistinguishable
Growth in gaps
Hubbell Foster 1992
7Hubbells neutral theory of biodiversity and
biogeography
- Distribution of species in an environment
stochastic processes operating at - regional scale
- local scale
Births
8Hubbells neutral theory assumptions
- The zero-sum ecological drift
- a) Community fixed number of individuals -
saturated - b) each death replaced by a birth at random by
any individual - Ecological equivalence Individuals of all
species are demographically similar (equivalent
probabilities of birth, - death, dispersal, speciation)very
criticized!!! - Null random and it is used as statistical test
of empirical data - Neutral Assumes functionally equivalence - uses
parameters
9Hubbells neutral theory
- What patterns result from the assumptions that
all species exhibit same demographic
stochasticity and only ecological drift,
dispersal, and speciation occur? - How similar are patterns predicted from UNT and
nature?
Abundance
Species sequence
matches almost all distributions of relative
abundance
Hubbell 1997
Magurran 1988
10Hubbells neutral theory
Hubbell 2006
- Prediction of UNT
- fits really well species
- abundance distribution of a
- tree community at Borneo
Hubbell 2001
- Prediction of UNT
- fits really well relative species abundance at
BCI, Panama
DESPITE RADICAL ASSUMPTIONS!
11Niche and neutrality debate
- Niche vs neutrality - the extreme perspective
-
- Is this way of thinking appropriate
productive? - What empirical data suggest?
vs
Each finch has its niche or niches are not
important at all
12Niche and neutrality debate in community ecology
study cases
- Species abundance distributions
- Assessing the fit of a neutral model to relative
- abundance patterns
- Identifying the mechanisms for relative abundance
- Spatial distribution (environment or dispersal?)
- Local scale
- Other studies
13Species abundance distributionAssessing the fit
of a neutral model
- A test of the unified neutral theory of
biodiversity - McGuill (2003a)
- Used data from BCI tree data set (same site than
Hubbell) - The log-normal and zero-sum model were fitted to
the data - Used maximum-likelihood
- methods and measured eight
- goodness of fit
14Species abundance distributionAssessing the fit
of a neutral model
- The lognormal beats the zero-sum on all goodness
of fit! - - However, success of lognormal does not mean
that community structure is random. Many other
models might explain it - - Low number of parameters and greater parsimony
McGuill 2003a
15Species abundance distributionAssessing the fit
of a neutral model
- Why did the results differed from Hubbell 2001?
- Fitting the data for a year or a cutoff in
minimum - tree size different than Hubells data?
- The study found some issues when fitting the
ZSM - ZSM predicts it will take thousands of years to
reach local - equilibrium (longer than time for environment
to be constant) - ZSM methods produce too many rare
- species so distribution must be stopped
- better prediction than log-normal
Sample size!
McGuill 2003a
16Assessing the fit of a neutral model
- Curve fitting is a weak test- McGuill (2003b)
- - More than one mechanism produce any given
distribution - There is not such a thing as a curve that fits
best - (depends on goodness of fit measure used)
- McGuill suggests better methods to test theories
(e.g. - constancy in parameters, correlations, temporal
and - spatial scale of exchangeability, etc)
- So fitting the curve seem to be
counterproductive as it - does not reveal the mechanisms!
17Niche and neutrality debate in community ecology
study cases
- Species abundance distributions
- Assessing the fit of a neutral model to relative
- abundance patterns
- Identifying the mechanisms for relative abundance
- Spatial distribution (environment or dispersal?)
- Local scale
- Other studies
18Species abundance distributionIdentifying the
mechanisms
- Non-neutral patterns of sps abundance in
grasslands - Harpole Tilman (2006)
- Three communities
- Minnesota (CDR oldfield) 60 years abandonment
- Minessota (CDR experiments) 5 years
experimentally assembled community (no regional
dispersal) - Kansas (KNZ) relict fragments
- Species traits to predict identity of
- dominant vs rare species (McGill 2003)
- N (nitrogen)
19Species abundance distributionAssessing the
mechanisms
- Distribution of species abundance consistent with
neutral - theory?
- - Data from CDR oldfields
- (percent cover data)
- Used an implementation of Volkovs solution to
fit ZSM (Volkov et al. 2003) - -Species abundance distribution was fit well by
both the ZSM and lognormal
Harpole Tilman 2006
20Species abundance distributionAssessing the
mechanisms
- Are species equivalent?
- - Three communities
- - R index inversely related
- to competitive ability for N
- - Correlations and likelihood
- of mean correlation by chance
- - Lower R species had greater
- abundance than higher R
Relative cover
Relative biomass
Harpole Tilman 2006
R
21Species abundance distributionAssessing the
mechanisms
- Are species equivalent?
- - Three communities
- - R index inversely related
- to competitive ability for N
- - Correlations and likelihood
- of mean correlation by chance
- - Lower R species had greater
- abundance than higher R
- - Mean correlation differs from
- 95 CI neutrality
Harpole Tilman 2006
22 Species abundance
distribution
Assessing the mechanisms
Species abundance change in a neutral manner with
environmental change?
- -Data from previous N addition
- experiment (CDR experiment)
- - Biomass
- - Correlations and likelihood
- of a relationship arising
- under neutral assumptions
- - Correlation was negative at low
- N lower R sps more abundant.
- At high N, correlation becomes
- Positive so higher R abundant
Harpole Tilman 2006
23Species abundance distributionIdentifying the
mechanisms
- Tests supported niche mechanisms as primary
drivers of grassland communities - Even for CDR oldfields (species abundance was
consistent with neutral theory) - Supports McGuill (2003), curve fitting might lead
to incorrect assumptions - But, greatest variation in R
- abundance correlation inCDR oldfields
- Dispersal still influence community,
- so conclusion?
Harpole Tilman 2006
24Niche and neutrality debate in community ecology
study cases
- Species abundance distributions
- Assessing the fit of a neutral model to relative
- abundance patterns
- Identifying the mechanisms for relative abundance
- Spatial distribution (environment or dispersal?)
- Local scale
- Other studies
25Spatial distribution environmental or dispersal?
- Neutrality, niches, and dispersal in a temperate
forest - understory Gilbert Lechowicz (2004)
- Gault Nature reserve, Montreal
- - Design decoupling distance and environment!
non-correlated for sites selection (GIS and
Mantel tests)
26Spatial distribution environmental or dispersal?
- Neutral theory predicts a decrease in community
similarity with distance (effects of dispersal
limitation) - Observed data does not follow neutral prediction
(environmental-distance effects decoupled)
Gilbert Lechowicz 2004
27Spatial distribution
environmental or dispersal?
- Measured soil moisture, soil nutrients, and other
22 physiographic variables - CCA analyses to identify species-specific niches
and dispersal patterns - Environmental explains plant distribution better
than dispersal (neutral), but dispersal partially
explains dispersal, so it is also important
Gilbert Lechowicz 2004
28Spatial distribution
environmental or dispersal?
- From CCA analyses determined relative importance
of variables explaining variations in species
distribution - High score on one axis species within group
differentiate ecologically along that axis
(distinct niches). -
- Shows evidence for niche structuring
Gilbert Lechowicz 2004
29Spatial distribution environmental or dispersal?
- Tests supported environment (niche mechanisms)
as - primary drivers for plant distribution, but
dispersal - (neutral mechanism) was also important
- Apparent neutral patterns of species
aggregation - previously detected in the reserve
- due to distance-environment correl.
- Niche differenciation occurred at
- both functional or phylogenetic level
Gilbert Lechowicz 2004
30Niche and neutrality debate
- Niche vs neutrality the extreme perspective
-
-
- Niche and neutral processes are not mutually
exclusive, therefore it is more important to ask
whether niche mechanisms are significantly more
important than an expectation from neutrality
vs
Each finch has its niche or niches are not
important at all
Gilbert Lechowicz 2004
31Niche and neutrality debate in community ecology
study cases
- Other studies
- Diversity patterns
- Beta diversity, species-area relationship,
local vs regional - Evolutionary characteristics
- Speciation rates, phylogenetic patterns
- It is a growing field, emerging as one of the
most often tested with field data and evaluated
with models (Clark 2008) - Sesile organism biased
- but more publications with
- animals from 2009!!