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________________________________________________________________________
Declining
coral
growth on
the Great
Barrier
Reef
Recent
work by
scientists
at the
Australian
Institute
of Marine
Science
(AIMS) has
identified
a
wide-spread
and rapid
decline in
the growth
rate of
massive
Porites
coral
colonies
on the
Great
Barrier
Reef. A
systematic
analysis
of
potential
causes
suggests
that a
combination
of rising
sea
surface
temperature
and
ocean
acidification,
due to
increased
carbon
dioxide
(CO2)
in the
atmosphere,
is likely
to be the
cause of
this
dramatically
slowed
growth.
With coral
growth
being an
important
determinant
of the
health of
reef
ecosystems,
there is
great
concern
that this
trend will
have
significant
consequences
for the
Great
Barrier
Reef, and
perhaps
for reefs
worldwide.
A
scientific
paper
entitled
"Declining
coral
calcification
on the
Great
Barrier
Reef" by
Glenn
De’ath,
Janice
Lough and
Katharina
Fabricius,
published
in the
prestigious
international
scientific
journal
Science
on 2
January
2009,
gained
widespread
attention
and has
been the
subject of
public
debate.
Presented
below is
an outline
of the
study and
its
findings
together
with a
brief
discussion
of the
implications.
Outline
and
findings:
- The
study is
based on
the
analysis
of
skeletal
records
of 328
colonies
of
massive
Porites
coral
colonies
from 69
reefs
throughout
the
Great
Barrier
Reef (GBR).
-
Coral
calcification
is shown
to have
declined
by 14.2%
since
1990.
Long-term
records
show
that
this
severe
and
sudden
decline
in coral
growth
is
unprecedented
in at
least
the last
400
years
and that
1990 may
have
been a
"tipping
point"
for
coral
calcification
rates on
the GBR.
- By a
systematic
process
of
excluding
all
potential
alternative
explanations,
and by
comparisons
with
similar
results
of
published
laboratory
experiments,
the
authors
suggest
that
increasing
sea
surface
temperature
and
ocean
acidification
are the
two most
likely
factors
to have
affected
Porites
calcification
at a GBR-wide
scale.
Discussion
of the
results:
- The
study
considered
a range
of
factors
known to
determine
coral
growth
and
calcification
including
competition
for
space,
water
quality,
salinity,
diseases,
irradiance,
currents,
large-scale
and
long-term
oceanographic
oscillations,
temperature
stress,
sea
surface
temperature
and
ocean
acidification.
All but
the last
two,
both
attributable
to
rising
atmospheric
CO2,
were
excluded
as being
likely
causes
of the
observed
decline.
- The
observations
made
during
the
study
were
based on
the
analysis
of data
recovered
from
coral
cores
gathered
in the
field –
they
were not
based on
computer-generated
models.
-
Coral
calcification
rates
are
known to
increase
linearly
with
long-term
rises in
sea
water
temperature
(Lough,
2008a)
but
respond
non-linearly
when
short-term
sea
water
temperatures
are
above or
below
optimal
levels
(Lough
and
Barnes,
2000,
De’ath
et al,
2009).
-
While
the
sharp
decline
occurred
toward
the end
of a
long-term
period
of
increasing
sea
water
temperatures
-
average
temperatures
having
increased
0.120C
per
decade
since
1950
(Lough,
2008a) –
it
coincides
with a
period
characterised
by
repeated
thermal
stress
events
(1990-2005).
- The
study
took
into
account
variations
in
calcification
responses
of
corals:
-
along
the
north-south
gradient
in
long-term
average
sea
water
temperatures;
- to
the
warming
over
the
20th
century;
and,
- in
years
that
were
unusually
cold
or
warm
(high
and
low
temperature
anomalies).
-
Previous
studies
have
shown
that the
combination
of ocean
acidification
and
rising
sea
water
temperatures
reduces
the
carbonate
saturation
state of
seawater,
slowing
hard
coral
growth
rates.
- The
widespread
nature
of the
observed
decline
–
affecting
reefs
from
inshore
to
offshore
and
north to
south
along
the GBR
– argues
against
localised
agents
such as
water
quality
being
the main
factor
causing
the
decline.
Although
water
quality
and
land-based
runoff
are not
the
causes
of
declining
calcification,
research
has
shown
that
high
levels
of
nutrients
and
sediments
lead to
high
macroalgal
cover,
low
coral
biodiversity
and low
rates of
coral
recruitment
on
inshore
reefs,
slowing
rates of
coral
recovery
after
disturbances,
and
increasing
frequency
of
outbreaks
of
crown-of-thorns
starfish
(Brodie
et al.,
2005,
Fabricius
et al.,
2005,
De’ath
and
Fabricius
2008).
The
future
-
Coral
reefs,
including
the
Great
Barrier
Reef,
are
facing
unprecedented
pressure
worldwide
due to
climate
change,
changes
in water
quality
from
terrestrial
runoff
and
over-exploitation
of reef
resources
such as
seafood
(Lough
2008b).
-
Substantial
reductions
in
global
CO2
emissions,
together
with
effective
water
quality
management
to
reduce
macroalgal
competition
and
facilitate
coral
recovery
(Wooldridge
et al.,
2005)
are
required
to
ensure
the
long-term
biodiversity
and,
perhaps
survival,
of coral
reefs.
- The
GBR is
one of
the
healthiest
and is
the best
managed
reef
system
in the
world,
as
recently
confirmed
in
Status
of Coral
Reefs of
the
World
2008
(Wilkinson,
2008).
The
Great
Barrier
Reef
Marine
Park
Authority,
informed
by the
very
best and
latest
marine
science,
manages
the reef
superbly.
However,
there
are
fundamental
processes
underway,
driven
by
increased
concentrations
of CO2
in the
atmosphere,
to which
no reef
can be
immune.
-
While
AIMS
congratulates
the
Australian
Government
on the
recently
announced
Carbon
Pollution
Reduction
Scheme (CPRS),
ongoing
efforts
by State
and
Commonwealth
Authorities
to
reduce
local
and
regional
pressures
must be
maintained
to
maximise
the
resilience
of the
GBR.
- It
must be
noted
that the
CPRS
target
of a
unilateral
5% cut
in CO2
emissions
(with
the
possibility
of a 15%
cut by
2020
contingent
upon
international
agreements)
is well
short of
what
science
says is
needed
to
achieve
the
stated
objective
of
stabilising
long-term
atmospheric
CO2
concentration
at
450 ppm.
Indeed,
the
science
suggests
that
reductions
of less
than 25%
will
mean the
goal of
450 ppm
is
unachievable
and,
even at
450 ppm,
there
will be
continuing
impacts
on the
growth
and
health
of the
Great
Barrier
Reef (Hoegh-Guldberg
et al
2007).
- As
Australia’s
tropical
marine
research
agency,
a
significant
challenge
for AIMS
into the
future
is the
task of
filling
current
knowledge
gaps
about
how
coral
reefs,
including
the GBR,
are
responding
to
climate
change.
This
knowledge
will
underpin
Australia’s
policy
and
management
decision
making,
helping
to
ensure
the
ongoing
health
of our
reefs
and
providing
a basis
for
developing
mitigation
options
if they
are
needed
in the
future.
References
Brodie
J,
Fabricius
K,
De’ath G
& Okaji
K, 2005.
Are
increased
nutrient
inputs
responsible
for more
outbreaks
of
crown-of-thorns
starfish?
An
appraisal
of the
evidence.
Marine
Pollution
Bulletin
51:
266–278.
De’ath
G,
Fabricius
KE,
2008.
Water
quality
of the
Great
Barrier
Reef:
distributions,
effects
on reef
biota
and
trigger
values
for the
protection
of
ecosystem
health.
Great
Barrier
Reef
Marine
Park
Authority,
Townsville,
Qld.:
104 pp.
De’ath
G, Lough
JM &
Fabricius
KE,
2009.
Declining
Coral
Calcification
on the
Great
Barrier
Reef
Science
323:
116-119.
(see:
http://www.sciencemag.org/
).
Fabricius
KE,
De’ath
G,
McCook
L, Turak
E &
Williams
DMc,
2005.
Changes
in
algal,
coral
and fish
assemblages
along
water
quality
gradients
on the
inshore
Great
Barrier
Reef.
Marine
Pollution
Bulletin
51:
384–398.
Hoegh-Guldberg
O, Mumby
PJ,
Hooten
AJ, et
al.
2007.
Coral
reefs
under
rapid
climate
change
and
ocean
acidification.
Science
318:
1737-1742.
Lough
JM,
2008a.
Shifting
climate
zones
for
Australia’s
tropical
marine
ecosystems.
Geophysical
Research
Letters
35,
L14708,
doi:
10.1029/2008GL034634.
Lough
JM,
2008b. A
changing
climate
for
coral
reefs.
Journal
of
Environmental
Monitoring
10:
21-29.
Lough
JM, &
Barnes
DJ,
2000.
Environmental
controls
on
growth
of the
massive
coral
Porites.
Journal
of
Experimental
Marine
Biology
and
Ecology,
245:
225-243.
Wilkinson,
C.,
(2008).
Status
of coral
reefs of
the
world:
2008.
Global
Coral
Reef
Monitoring
Network
and Reef
and
Rainforest
Research
Centre,
Townsville,
Australia,
296 p.
Wooldridge
SA, Done
TJ,
Berkelmans
RWC,
Jones R
&
Marshall
PA,
2005.
Precursors
for
resilience
in coral
communities
in a
warming
climate:
a belief
network
approach.
Marine
Ecology
Progress
Series
295:
157-169.
Scientific
Consensus
Statement
on Water
Quality
in the
GBR.pdf
(see
-http://www.reefplan.qld.gov.au/library/pdf/publications/Scientific%20Consensus%20Statement%20on%20Water%20Quality%20in%20the%20GBR.pdf).
Notes
Coral
calcification,
a
measure
of coral
growth,
is a
term
used to
describe
the rate
at which
reef-building
corals
lay down
their
calcium
carbonate
skeleton
and is a
product
of
colony
extension
(dimensional
growth)
and
density.
Hard
corals
extract
the raw
materials
for
their
calcium
carbonate
skeletons
from the
surrounding
water
column.
The
availability
of these
raw
materials
is
determined
by the
“carbonate
saturation
state”
of that
water.
For further information, please contact:
Dr Glenn
De'ath;
g.death@aims.gov.au
Dr Janice Lough;
j.lough@aims.gov.au
Dr
Katharina
Fabricius;
k.fabricius@aims.gov.au
January
15, 2009
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