The health of coral reefs in many parts of the world is declining
due to a variety of direct, local human pressures (such as
overfishing, land-based activities affecting water quality; see
Wilkinson 2004). Coral reefs are now subject to an additional
global-scale threat to their long-term wellbeing due to the enhanced
Greenhouse effect. The two most important consequences of the enhanced
Greenhouse effect for coral reefs are warming of the oceans and
changes in ocean chemistry.
Rising sea temperatures increase the frequency of mass coral
bleaching events. Corals live only 1-2oC below their upper
thermal limit and sustained periods of water temperatures above this
threshold stresses the coral and the symbiotic algae (the essential
partner for reef-building corals) are expelled. The host coral may
die, partially die or recover though coral growth and reproduction can
be affected in surviving corals. 16% of the world’s reefs were
seriously damaged during the 1998 bleaching event – probably the
warmest year experienced by modern corals. Although some affected
reefs have recovered it is clear that healthy (more resilient) coral
reefs recover better than reefs degraded by other human pressures. The
Great Barrier Reef (GBR) is probably the best managed and protected
reef (because of GBRMPAs Representative Areas Program, zoning and
permitting systems, the July 2004 declaration of 30% No-Take Areas and
the Reef Water Quality Protection Plan) in the world yet major
bleaching occurred in 1998 and 2002 as a consequence of the relatively
modest warming of GBR waters (<0.5oC) since the end of the
19th century. Current projections suggest that average
tropical ocean temperatures could warm 1-3oC by the end of
this century. There is general scientific consensus that global
warming and consequent coral bleaching are a significant threat to the
maintenance of coral reef communities as they presently exist and that
healthy coral reefs (more ecologically intact and less exploited) will
be more resilient than those degraded by other human pressures. There
is some evidence emerging that corals may be able to alter their
symbiotic algae to more thermally tolerant partners though this may be
at the expense of growth rates. This change may, however, only occur
in a few species and not be sufficiently rapid to keep pace with
temperature rises. Current research at AIMS focuses on these possible
adaptive changes in corals and their effects on coral growth.
Increasing atmospheric carbon dioxide (CO2, the
principal greenhouse gas) is changing the chemistry of the
oceans. About 30% of the CO2 released into the atmosphere
by human activities since the Industrial Revolution has been absorbed
by the oceans. This changes the chemistry of the oceans, which become
more acidic (lower pH) and these change the concentrations of
carbonate and bicarbonate ions. Many marine organisms (corals,
calcareous algae, shells, benthic and planktonic organisms such as
foramanifera and coccolithophores) use calcium and carbonate ions from
seawater to secrete calcium carbonate skeletons. Changing the ocean
chemistry essentially shifts the geochemical equation by which these
organisms "calcify". The implication of continued change in ocean
chemistry due to rising CO2 is that these organisms will
not calcify as well as they did in pre-industrial times and thus
produce weaker skeletons and grow more slowly. For coral reefs weaker
structures would reduce their resilience to the natural forces of
erosion and slower growth will set back the rate of recovery after
bleaching and other disturbances. Also, changing ocean chemistry will
alter the deep ocean depths at which dissolution of calcium carbonate
skeletons of different mineralogies occurs. Modelling and experimental
(eg Biosphere 2 mesocosm) studies have demonstrated that increased CO2
reduces coral calcification rates. A recent media report, based on
respected coral reef researcher Jonathan Erez’s work in Israel,
provides the first observational evidence from the field that lower pH
is associated with reduced coral growth. Calcification rate also
depends on water temperature and AIMS provided evidence (Lough &
Barnes 2000) that several long-lived massive Porites on the GBR had
increased their calcification rate towards the end of the 20th
century (up to ~1980 when cores were collected) which matched the
observed rise in GBR water temperatures (AIMS is currently examining
more recent coral growth rates from short coral cores). This finding
generated some controversy, as it did not match the model or
experimental findings. The conclusion from this work was that, at
least initially, some corals might respond more to rising water
temperatures than to changes in ocean chemistry. More recently
scientists from UNSW, CSIRO and AIMS (McNeil et al., 2004) published
model results suggesting that the warming effect on coral
calcification (in one coral species) outweighs the change in ocean
chemistry and that coral calcification will increase with global
warming. These controversial findings are currently being debated in
the scientific literature. These studies focused on the most heat
resistant type of coral and did not consider the overall effects on
reef calcification rates of the widespread death of the majority of
corals that are less heat resistant. How much ocean warming reefs can
withstand will, however, be limited by when temperature thresholds for
coral bleaching are regularly exceeded. The general scientific
consensus is that changes in ocean chemistry due to rising CO2
has serious implications for coral reefs and other calcifying marine
organisms of the open ocean and could well alter the makeup of marine
ecosystems and weaken coral reef structures. There is clearly much
more we need to learn about the effects of rising CO2 and
marine calcification and the importance of this problem and its
impacts on marine ecosystems is recognized by a planned international
Workshop on the Impacts of Increasing Atmospheric CO2 on
Coral Reefs and Other Marine Calcifiers, 18-20 April 2005, St
Petersburg, Florida sponsored by NSF/NOAA/USGS (Lough from AIMS will
be attending).
Coral reefs of the world are under threat from both local and
global-scale stresses. The enhanced Greenhouse effect (through
bleaching and ocean chemistry changes) is likely to alter the
community structure of reefs, including the world’s best-managed reefs
of Australia. There is a clear scientific consensus (eg Wilkinson
2004) that reducing and reversing local human pressures on coral reefs
has to be accompanied by reduction in greenhouse gas emissions if
coral reefs are to survive.
Erez, J (2005) As reported by BBC
http://news.bbc.co.uk/2/hi/science/nature/4226917.stm
McNeil BI, RJ Matear & DJ Barnes (2004) Coral reef
calcification and climate change: the effect of ocean warming. Geophys
Res Lett 31, L22309
Lough, JM & DJ Barnes (2000). Environmental controls on
growth of the massive coral Porites. J Exp Mar Biol Ecol 245: 225-243.
Wilkinson, C (2004). Status of Coral Reefs of the World:
2004. GCRMN, ICRI, AIMS