Annual Review of Ecology Evolution and Systematics,
Journal Year:
2004,
Volume and Issue:
35(1), P. 557 - 581
Published: Nov. 2, 2004
▪
Abstract
We
review
the
evidence
of
regime
shifts
in
terrestrial
and
aquatic
environments
relation
to
resilience
complex
adaptive
ecosystems
functional
roles
biological
diversity
this
context.
The
reveals
that
likelihood
may
increase
when
humans
reduce
by
such
actions
as
removing
response
diversity,
whole
groups
species,
or
trophic
levels;
impacting
on
via
emissions
waste
pollutants
climate
change;
altering
magnitude,
frequency,
duration
disturbance
regimes.
combined
often
synergistic
effects
those
pressures
can
make
more
vulnerable
changes
previously
could
be
absorbed.
As
a
consequence,
suddenly
shift
from
desired
less
states
their
capacity
generate
ecosystem
services.
Active
management
governance
will
required
sustain
transform
degraded
into
fundamentally
new
desirable
configurations.
Annual Review of Ecology Evolution and Systematics,
Journal Year:
2014,
Volume and Issue:
45(1), P. 471 - 493
Published: Oct. 8, 2014
Species
diversity
is
a
major
determinant
of
ecosystem
productivity,
stability,
invasibility,
and
nutrient
dynamics.
Hundreds
studies
spanning
terrestrial,
aquatic,
marine
ecosystems
show
that
high-diversity
mixtures
are
approximately
twice
as
productive
monocultures
the
same
species
this
difference
increases
through
time.
These
impacts
higher
have
multiple
causes,
including
interspecific
complementarity,
greater
use
limiting
resources,
decreased
herbivory
disease,
nutrient-cycling
feedbacks
increase
stores
supply
rates
over
long
term.
experimentally
observed
effects
consistent
with
predictions
based
on
variety
theories
share
common
feature:
All
trade-off-based
mechanisms
allow
long-term
coexistence
many
different
competing
species.
Diversity
loss
has
an
effect
great
as,
or
than,
herbivory,
fire,
drought,
nitrogen
addition,
elevated
CO
2
,
other
drivers
environmental
change.
The
preservation,
conservation,
restoration
biodiversity
should
be
high
global
priority.
Ecology,
Journal Year:
2007,
Volume and Issue:
88(1), P. 42 - 48
Published: Jan. 1, 2007
Stable
isotope
ratios
(typically
of
carbon
and
nitrogen)
provide
one
representation
an
organism's
trophic
niche
are
widely
used
to
examine
aspects
food
web
structure.
Yet
stable
isotopes
have
not
been
applied
quantitatively
characterize
community-wide
structure
(i.e.,
at
the
level
entire
web).
We
propose
quantitative
metrics
that
can
be
this
end,
drawing
on
similar
approaches
from
ecomorphology
research.
For
example,
convex
hull
area
occupied
by
species
in
δ13C–δ15N
space
is
a
total
extent
diversity
within
web,
whereas
mean
nearest
neighbor
distance
among
all
pairs
measure
packing
space.
To
facilitate
discussion
opportunities
limitations
metrics,
we
empirical
conceptual
examples
drawn
Bahamian
tidal
creek
webs.
These
illustrate
how
methodology
quantify
redundancy
webs,
as
well
link
individual
characteristics
which
they
embedded.
Building
extensive
applications
ecologists,
may
new
perspective
structure,
function,
dynamics.
Science,
Journal Year:
2007,
Volume and Issue:
315(5820), P. 1846 - 1850
Published: March 30, 2007
Impacts
of
chronic
overfishing
are
evident
in
population
depletions
worldwide,
yet
indirect
ecosystem
effects
induced
by
predator
removal
from
oceanic
food
webs
remain
unpredictable.
As
abundances
all
11
great
sharks
that
consume
other
elasmobranchs
(rays,
skates,
and
small
sharks)
fell
over
the
past
35
years,
12
14
these
prey
species
increased
coastal
northwest
Atlantic
ecosystems.
Effects
this
community
restructuring
have
cascaded
downward
cownose
ray,
whose
enhanced
predation
on
its
bay
scallop
was
sufficient
to
terminate
a
century-long
fishery.
Analogous
top-down
may
be
predictable
consequence
eliminating
entire
functional
groups
predators.
American Journal of Botany,
Journal Year:
2011,
Volume and Issue:
98(3), P. 572 - 592
Published: March 1, 2011
Over
the
past
several
decades,
a
rapidly
expanding
field
of
research
known
as
biodiversity
and
ecosystem
functioning
has
begun
to
quantify
how
world's
biological
diversity
can,
an
independent
variable,
control
ecological
processes
that
are
both
essential
for,
fundamental
to,
ecosystems.
Research
in
this
area
often
been
justified
on
grounds
(1)
loss
ranks
among
most
pronounced
changes
global
environment
(2)
reductions
diversity,
corresponding
species
composition,
could
alter
important
services
ecosystems
provide
humanity
(e.g.,
food
production,
pest/disease
control,
water
purification).
Here
we
review
over
two
decades
experiments
have
examined
richness
primary
producers
influences
suite
controlled
by
plants
algae
terrestrial,
marine,
freshwater
Using
formal
meta-analyses,
assess
balance
evidence
for
eight
questions
hypotheses
about
functional
role
producer
These
include
efficiency
resource
use
biomass
production
ecosystems,
transfer
recycling
other
trophic
groups
web,
number
spatial
/temporal
scales
at
which
effects
apparent.
After
summarizing
stating
our
own
confidence
conclusions,
outline
new
must
now
be
addressed
if
is
going
evolve
into
predictive
science
can
help
conserve
manage
Ecology Letters,
Journal Year:
2007,
Volume and Issue:
10(6), P. 522 - 538
Published: April 23, 2007
Understanding
how
biodiversity
affects
functioning
of
ecosystems
requires
integrating
diversity
within
trophic
levels
(horizontal
diversity)
and
across
(vertical
diversity,
including
food
chain
length
omnivory).
We
review
theoretical
experimental
progress
toward
this
goal.
Generally,
experiments
show
that
biomass
resource
use
increase
similarly
with
horizontal
either
producers
or
consumers.
Among
prey,
higher
often
increases
resistance
to
predation,
due
increased
probability
inedible
species
reduced
efficiency
specialist
predators
confronted
diverse
prey.
predators,
changing
can
cascade
affect
plant
biomass,
but
the
strength
sign
effect
depend
on
degree
omnivory
prey
behaviour.
Horizontal
vertical
also
interact:
adding
a
level
qualitatively
change
effects
at
adjacent
levels.
Multitrophic
interactions
produce
richer
variety
diversity-functioning
relationships
than
monotonic
changes
predicted
for
single
This
complexity
depends
consumer
dietary
generalism,
trade-offs
between
competitive
ability
intraguild
predation
openness
migration.
Although
complementarity
selection
occur
in
both
animals
plants,
few
studies
have
conclusively
documented
mechanisms
mediating
effects.
complex
will
benefit
from
theory
simulations
network-based
approaches.
Ecology,
Journal Year:
2008,
Volume and Issue:
89(6), P. 1510 - 1520
Published: May 30, 2008
The
composition
of
communities
is
strongly
altered
by
anthropogenic
manipulations
biogeochemical
cycles,
abiotic
conditions,
and
trophic
structure
in
all
major
ecosystems.
Whereas
the
effects
species
loss
on
ecosystem
processes
have
received
broad
attention,
consequences
dominance
for
emergent
properties
ecosystems
are
poorly
investigated.
Here
we
propose
a
framework
guiding
our
understanding
how
affects
interactions
within
communities,
ecosystems,
dynamics
regional
scales.
Dominance
(or
complementary
term,
evenness)
reflects
distribution
traits
community,
which
turn
strength
sign
both
intraspecifc
interspecific
interactions.
Consequently,
also
mediates
effect
such
coexistence.
We
review
evidence
fact
that
directly
functions
as
process
rates
via
identity
(the
dominant
trait)
evenness
frequency
traits),
indirectly
alters
relationship
between
richness.
influences
temporal
spatial
variability
aggregate
community
compositional
stability
(invasibility).
Finally,
coexistence
altering
metacommunity
dynamics.
Local
leads
to
high
beta
diversity,
rare
can
persist
because
source-sink
dynamics,
but
anthropogenically
induced
environmental
changes
result
low
reducing
Given
rapid
alterations
many
strong
implications
these
changes,
should
be
considered
explicitly
analysis
biodiversity.
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.
Global Ecology and Biogeography,
Journal Year:
2014,
Volume and Issue:
23(7), P. 726 - 743
Published: March 6, 2014
Abstract
Aim
To
reassess
the
capacity
of
mangroves
for
ecosystem
services
in
light
recent
data.
Location
Global
mangrove
ecosystems.
Methods
We
review
four
long‐standing
roles
mangroves:
(1)
carbon
dynamics
–
export
or
sink;
(2)
nursery
role;
(3)
shoreline
protection;
(4)
land‐building
capacity.
The
origins
pertinent
hypotheses,
current
understanding
and
gaps
our
knowledge
are
highlighted
with
reference
to
biogeographic,
geographic
socio‐economic
influences.
Results
role
as
C
sinks
needs
be
evaluated
a
wide
range
biogeographic
regions
forest
conditions.
Mangrove
assimilation
may
under‐estimated
because
flawed
methodology
scanty
data
on
key
components
dynamics.
Peri‐urban
manipulated
provide
local
offsets
emission.
function
is
not
ubiquitous
but
varies
spatio‐temporal
accessibility.
Connectivity
complementarity
adjacent
habitats
enhance
their
through
trophic
relay
ontogenetic
migrations.
effectiveness
coastal
protection
depends
factors
at
landscape/geomorphic
community
scales
local/species
scales.
Shifts
species
due
climate
change,
degradation
loss
habitat
connectivity
reduce
protective
mangroves.
Early
views
land
builders
(especially
lateral
expansion)
were
questionable.
Evidence
now
indicates
that
mangroves,
once
established,
directly
influence
vertical
development
by
enhancing
sedimentation
and/or
direct
organic
contributions
soil
volume
(peat
formation)
some
settings.
Main
conclusions
Knowledge
thresholds,
scaling
variability
geographic,
settings
will
improve
management
services.
Many
drivers
respond
global
trends
change
changes
such
urbanization.
While
have
traditionally
been
managed
subsistence,
future
governance
models
must
involve
partnerships
between
custodians
offsite
beneficiaries