Ecology Letters,
Journal Year:
2008,
Volume and Issue:
11(11), P. 1147 - 1156
Published: Aug. 18, 2008
Abstract
Ecosystems
are
differentially
open
to
subsidies
of
energy,
material
and
organisms.
This
fundamental
ecosystem
attribute
has
long
been
recognized
but
the
influence
this
property
on
community
regulation
not
investigated.
We
propose
that
environmental
may
explain
variation
in
strength
trophic
cascades
among
ecosystems.
Simply
because
gravity,
we
should
predict
systems
with
convex
profiles
receive
low
amounts
whereas
concave
act
as
spatial
attractors,
high
subsidies.
The
subsidy
hypothesis
states
ecosystems
allochthonous
inputs
will
experience
strongest
cascades.
To
test
hypothesis,
derive
models
investigate
effect
location
magnitude
Predictions
from
our
support
highlight
need
consider
flows.
Science,
Journal Year:
2005,
Volume and Issue:
308(5728), P. 1621 - 1623
Published: June 9, 2005
Removal
of
top
predators
from
ecosystems
can
result
in
cascading
effects
through
the
trophic
levels
below,
completely
restructuring
food
web.
Cascades
have
been
observed
small-scale
or
simple
webs,
but
not
large,
complex,
open-ocean
ecosystems.
Using
data
spanning
many
decades
a
once
cod-dominated
northwest
Atlantic
ecosystem,
we
demonstrate
cascade
large
marine
ecosystem.
Several
cod
stocks
other
geographic
areas
also
collapsed
without
recovery,
suggesting
existence
cascades
these
systems.
Ecology Letters,
Journal Year:
2004,
Volume and Issue:
7(2), P. 153 - 163
Published: Feb. 1, 2004
Abstract
Trophic
cascades
are
textbook
examples
of
predator
indirect
effects
on
ecological
systems.
Yet
there
is
considerable
debate
about
their
nature,
strength
and
overall
importance.
This
stems
in
part
from
continued
uncertainty
the
ultimate
mechanisms
driving
cascading
effects.
We
present
a
synthesis
empirical
evidence
support
one
possible
mechanism:
foraging‐predation
risk
trade‐offs
undertaken
by
intermediary
species.
show
that
simple
trade‐off
behaviour
can
lead
to
both
positive
negative
predators
plant
resources
hence
explain
contingency
nature
among
Thus,
predicting
sign
effect
simply
requires
knowledge
habitat
resource
use
prey
with
regard
predators’
presence,
hunting
mode.
The
allows
us
postulate
hypothesis
for
new
conceptualization
trophic
which
be
viewed
as
an
between
intervening
In
this
context,
different
apply
rules
engagement
based
mode
use.
These
then
determine
whether
behavioural
persist
or
attenuate
at
level
food
chain.
Ecology Letters,
Journal Year:
2002,
Volume and Issue:
5(6), P. 785 - 791
Published: Nov. 1, 2002
Abstract
Although
trophic
cascades
(indirect
effects
of
predators
on
plants
via
herbivores)
occur
in
a
wide
variety
food
webs,
the
magnitudes
their
are
often
quite
variable.
We
compared
responses
herbivore
and
plant
communities
to
predator
manipulations
102
field
experiments
six
different
ecosystems:
lentic
(lake
pond),
marine,
stream
benthos,
marine
plankton,
terrestrial
(grasslands
agricultural
fields).
Predator
varied
considerably
among
systems
were
strongest
benthos
weakest
plankton
webs.
herbivores
generally
larger
more
variable
than
plants,
suggesting
that
become
attenuated
at
plant–herbivore
interface.
Top‐down
control
biomass
was
stronger
water
land;
however,
differences
five
aquatic
webs
as
great
those
between
wet
dry
systems.
Journal of Animal Ecology,
Journal Year:
2009,
Volume and Issue:
78(4), P. 699 - 714
Published: March 9, 2009
Summary
Top‐down
control
can
be
an
important
determinant
of
ecosystem
structure
and
function,
but
in
oceanic
ecosystems,
where
cascading
effects
predator
depletions,
recoveries,
invasions
could
significant,
such
had
rarely
been
demonstrated
until
recently.
Here
we
synthesize
the
evidence
for
top‐down
that
has
emerged
over
last
decade,
focusing
on
large,
high
trophic‐level
predators
inhabiting
continental
shelves,
seas,
open
ocean.
In
these
controlled
manipulations
are
largely
infeasible,
‘pseudo‐experimental’
analyses
predator–prey
interactions
treat
independent
populations
as
‘replicates’,
temporal
or
spatial
contrasts
climate
‘treatments’,
increasingly
employed
to
help
disentangle
from
environmental
variation
noise.
Substantial
reductions
marine
mammals,
sharks,
piscivorous
fishes
have
led
mesopredator
invertebrate
increases.
Conversely,
abundant
suppressed
prey
abundances.
Predation
also
inhibited
recovery
depleted
species,
sometimes
through
role
reversals.
Trophic
cascades
initiated
by
linking
neritic
food
webs,
seem
inconsistent
pelagic
realm
with
often
attenuating
at
plankton.
is
not
uniformly
strong
ocean,
appears
contingent
intensity
nature
perturbations
Predator
diversity
may
dampen
except
nonselective
fisheries
deplete
entire
functional
groups.
other
cases,
simultaneous
exploitation
inhibit
responses.
Explicit
consideration
anthropogenic
modifications
foodwebs
should
inform
predictions
about
trophic
control.
Synthesis
applications
.
Oceanic
socio‐economic,
conservation,
management
implications
mesopredators
invertebrates
assume
dominance,
overexploited
impaired.
Continued
research
aimed
integrating
across
levels
needed
understand
forecast
changing
abundances,
relative
strength
bottom‐up
control,
intensifying
stressors
change.
Oikos,
Journal Year:
2002,
Volume and Issue:
99(2), P. 201 - 219
Published: Nov. 1, 2002
Proposed
links
between
biodiversity
and
ecosystem
processes
have
generated
intense
interest
controversy
in
recent
years.
With
few
exceptions,
however,
empirical
studies
focused
on
grassland
plants
laboratory
aquatic
microbial
systems,
whereas
there
has
been
little
attention
to
how
changing
animal
diversity
may
influence
processes.
Meanwhile,
a
separate
research
tradition
demonstrated
strong
top‐down
forcing
many
but
considered
the
role
of
these
only
tangentially.
Integration
directions
is
necessary
for
more
complete
understanding
both
areas.
Several
considerations
suggest
that
multi‐level
food
webs
can
important
effects
be
qualitatively
different
than
those
mediated
by
plants.
First,
extinctions
tend
biased
trophic
level:
higher‐level
consumers
are
less
diverse,
abundant,
under
stronger
anthropogenic
pressure
average
wild
plants,
thus
face
greater
risk
extinction.
Second,
unlike
often
impacts
ecosystems
disproportionate
their
abundance.
Thus,
an
early
consequence
declining
will
skewed
structure,
potentially
reducing
influence.
Third,
where
predators
remain
at
lower
levels
change
effectiveness
predation
penetrance
cascades
trait
potential
compensation
among
species
within
level.
The
mostly
indirect
evidence
available
provides
some
support
this
prediction.
Yet
functional
rarely
tested
experimentally.
Evaluating
loss
function
requires
expanding
scope
current
experimental
webs.
A
central
challenge
doing
so,
evaluating
importance
specifically,
distribution
interaction
strengths
natural
communities
they
with
community
composition.
Although
topology
most
real
extremely
complex,
it
not
all
clear
much
complexity
translates
dynamic
linkages
aggregate
biomass
Finally,
need
detailed
data
patterns
from
(community
“disassembly”
rules).
Ecology,
Journal Year:
2005,
Volume and Issue:
86(2), P. 528 - 537
Published: Feb. 1, 2005
Trophic
cascades
have
been
documented
in
a
diversity
of
ecological
systems
and
can
be
important
determining
biomass
distribution
within
community.
To
date,
the
literature
on
trophic
has
focused
whether
which
occur.
Many
biological
(e.g.,
productivity
:
ratios)
methodological
experiment
size
or
duration)
factors
vary
with
ecosystem
data
were
collected,
but
type,
per
se,
does
not
provide
mechanistic
insights
into
controlling
cascade
strength.
Here,
we
tested
various
hypotheses
about
why
occur
what
determines
their
magnitude
using
from
114
studies
that
measured
indirect
effects
predators
plant
community
seven
aquatic
terrestrial
ecosystems.
Using
meta-analysis,
examined
relationship
between
effect
predator
manipulation
plants
18
quantified
these
studies.
We
found,
contrast
to
predictions,
high
system
low
species
do
consistently
generate
larger
cascades.
A
combination
herbivore
metabolic
taxonomy
(vertebrate
vs.
invertebrate)
explained
31%
variation
strength
among
all
Within
systems,
18%
was
similar
characteristics.
across
strongest
occurred
association
invertebrate
herbivores
endothermic
vertebrate
predators.
These
associations
may
result
true
differences
different
physiological
requirements
bias
organisms
studied
systems.
Thus,
although
described
by
characteristics
herbivores,
future
research
must
further
examine
Proceedings of the Royal Society B Biological Sciences,
Journal Year:
2005,
Volume and Issue:
273(1582), P. 1 - 9
Published: Nov. 29, 2005
Ecologists
have
greatly
advanced
our
understanding
of
the
processes
that
regulate
trophic
structure
and
dynamics
in
ecosystems.
However,
causes
systematic
variation
among
ecosystems
remain
controversial
poorly
elucidated.
Contrasts
between
aquatic
terrestrial
particular
inspired
much
speculation,
but
only
recent
empirical
quantification.
Here,
we
review
evidence
for
differences
energy
flow
biomass
partitioning
producers
herbivores,
detritus
decomposers,
higher
levels.
The
magnitudes
different
pathways
vary
considerably,
with
less
herbivory,
more
decomposers
detrital
accumulation
on
land.
Aquatic-terrestrial
are
consistent
across
global
range
primary
productivity,
indicating
structural
contrasts
two
systems
preserved
despite
large
input.
We
argue
variable
selective
forces
drive
plant
allocation
patterns
environments
propagate
upward
to
shape
food
webs.
small
size
lack
tissues
phytoplankton
mean
achieve
faster
growth
rates
nutritious
heterotrophs
than
their
counterparts.
Plankton
webs
also
strongly
size-structured,
while
position
correlated
most
(and
many
benthic)
habitats.
available
data
indicate
driven
primarily
by
rate,
nutritional
quality
autotrophs.
Differences
food-web
architecture
(food
chain
length,
prevalence
omnivory,
specialization
or
anti-predator
defences)
may
arise
as
a
consequence
character
producer
community.