Ecology Letters,
Journal Year:
2013,
Volume and Issue:
16(10), P. 1294 - 1306
Published: Aug. 4, 2013
Abstract
Recent
functional
trait
studies
have
shown
that
differences
may
favour
certain
species
(environmental
filtering)
while
simultaneously
preventing
competitive
exclusion
(niche
partitioning).
However,
phenomenological
trait‐dispersion
analyses
do
not
identify
the
mechanisms
generate
niche
partitioning,
trait‐based
prediction
of
future
changes
in
biodiversity.
We
argue
such
predictions
require
linking
traits
with
recognised
coexistence
involving
spatial
or
temporal
environmental
heterogeneity,
resource
partitioning
and
natural
enemies.
first
demonstrate
limitations
approaches
using
simulations,
then
(1)
propose
tests
coexistence,
(2)
hypotheses
about
which
plant
are
likely
to
interact
particular
(3)
review
literature
for
evidence
these
hypotheses.
Theory
data
suggest
all
four
classes
could
act
on
variation,
but
some
will
be
stronger
more
widespread
than
others.
The
highest
priority
research
is
interactions
between
heterogeneity
variation
measure
variables
at
within‐community
scales
quantify
species'
responses
environment
absence
competition.
Evidence
similar
operate
many
ecosystems
would
simplify
biodiversity
forecasting
represent
a
rare
victory
generality
over
contingency
community
ecology.
Oikos,
Journal Year:
1999,
Volume and Issue:
86(3), P. 402 - 402
Published: Sept. 1, 1999
Ecologists
have
searched
for
general
principles,
or
assembly
rules,
which
determine
how
species
combine
to
form
communities.
Two
major
strands
of
research
highlight
the
interaction
rules
operating
at
different
levels
community
organisation.
and
within
uncertain
local
historical
contingencies.
Here,
we
review
aterature
on
context
three
principal
determinants:
dispersal
constraints,
environmental
constraints
internal
dynamics.
This
classification
separates
external
factors
(dispersal
constraints)
from
mternal
processes
(internal
dynamics).
We
assert
that
are
general,
deterministic
mechanistic,
operate
dynamies
imposed
by
environment
history
invasions.
Several
been
proposed
across
trophic
levels,
as
well
whole
systems.
The
act
through
resource
dynamics
spatial
select
subsets
can
coexist,
may
lead
patterns
increasing
biomass
non-random
distributions.
Environmental
restriet
establishment
mediate
interactions
among
successful
colonists;
a
change
in
either
exogenous
endogenous.
drive
change.
Even
systems
equilibrium,
influence
outcome
rules.
Dispersal
pool
potential
colonists
available
particular
time
place,
complex
amalgam
species-specific
traits,
storage
effects,
landscape
ecology,
history.
order
timing
invasions
interact
with
produce
priority
effects.
directionality
be
lost
if
rate
non-selective
extinctions
exceeds
selected
falling
apart,
disassembly,
breakdown
follow
trajectory.
Ecology Letters,
Journal Year:
2000,
Volume and Issue:
3(4), P. 362 - 377
Published: July 1, 2000
A
major
goal
of
community
ecology
is
to
link
biological
processes
at
lower
scales
with
patterns.
Microbial
communities
are
especially
powerful
model
systems
for
making
these
links.
In
this
article,
we
review
recent
studies
laboratory
bacteria
and
bacteriophage
(viruses
that
infect
bacteria).
We
focus
on
the
evolution
bacteriophage‐resistance
as
a
case
study
demonstrating
relationship
between
specific
genes,
individual
interactions,
population
dynamics,
structure,
evolutionary
change.
bacteriophage,
rapidly
evolve
resistance
infection.
Different
mutations
produce
distinct
phenotypes,
differing,
example,
in
whether
partial
or
complete,
magnitude
physiological
cost
associated
resistance,
mutation
can
be
countered
by
host‐range
bacteriophage.
These
differences
determine
mutant
invade,
effect
its
invasion
has
dynamics
sensitive
phage,
resulting
structure
community.
All
effects,
turn,
govern
community’s
response
environmental
change
subsequent
evolution.
Ecology Letters,
Journal Year:
2013,
Volume and Issue:
16(10), P. 1294 - 1306
Published: Aug. 4, 2013
Abstract
Recent
functional
trait
studies
have
shown
that
differences
may
favour
certain
species
(environmental
filtering)
while
simultaneously
preventing
competitive
exclusion
(niche
partitioning).
However,
phenomenological
trait‐dispersion
analyses
do
not
identify
the
mechanisms
generate
niche
partitioning,
trait‐based
prediction
of
future
changes
in
biodiversity.
We
argue
such
predictions
require
linking
traits
with
recognised
coexistence
involving
spatial
or
temporal
environmental
heterogeneity,
resource
partitioning
and
natural
enemies.
first
demonstrate
limitations
approaches
using
simulations,
then
(1)
propose
tests
coexistence,
(2)
hypotheses
about
which
plant
are
likely
to
interact
particular
(3)
review
literature
for
evidence
these
hypotheses.
Theory
data
suggest
all
four
classes
could
act
on
variation,
but
some
will
be
stronger
more
widespread
than
others.
The
highest
priority
research
is
interactions
between
heterogeneity
variation
measure
variables
at
within‐community
scales
quantify
species'
responses
environment
absence
competition.
Evidence
similar
operate
many
ecosystems
would
simplify
biodiversity
forecasting
represent
a
rare
victory
generality
over
contingency
community
ecology.