Would
you give us some background on your education and early research?
I grew up in Sydney, Australia. From my earliest years, I had a
fascination for nature and science in general. After a youth spent
preoccupied with nature (from butterflies to reptiles), I completed
an Honours degree at the University of Sydney, focusing in my last
year on a series of invertebrates that housed symbiotic
dinoflagellates. And so began my interest in plant-animal symbioses.
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“Our work has identified climate warming as the number-one threat to coral reefs.”
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After obtaining a scholarship, I did my Ph.D. with Professor
Leonard Muscatine at the University of California at Los Angeles on
the population dynamics of symbiotic dinoflagellates in sea anemones
and corals. This led me to examine (with Professor Muscatine)
samples from a curious event in the Caribbean. Little did I know
that this phenomenon (coral bleaching) was to preoccupy me over much
of my research career. I eventually returned home to take a
lectureship at the University of Sydney (1991), moving to the
University of Queensland in 2000 to take up the Foundation Chair in
Marine Studies.
What
do you consider the main focus of your research?
I have spent the last 10 years focused on the impacts/changes
that occur in coral reef communities as rapid changes to the
environment occur. This work has sought to explain the linkages and
drivers between changes at the physiological level and how they
manifest themselves at successfully higher levels. I obtain
particular pleasure when I can marry phenomena at these different
levels of complexity. For example, some years ago, my research group
(as well as colleagues elsewhere) deciphered the fundamental
problems that corals and their dinoflagellate symbionts face as they
become heat-stressed. The mechanism uncovered a key role for light
in exacerbating the damage caused by heat. This insight suddenly
explained why ecological studies were picking up the observation
that corals were damaged during mass bleaching events on their upper
sides or in areas of high light levels. These types of linkages
between physiology and ecology (in this case) are powerful, as they
allow you to reinforce one’s understandings from several different
directions or disciplines.
In recent times, I have become increasingly interested in the
complex behaviors of reef systems. For example, understanding the
thermal threshold of corals to bleaching allowed us some predictive
power when we wedded these to climate projections. From these data,
we have been able to project trends (some of which we are already
seeing) into the future. However, we have also been aware that these
projections, although powerful, do not give credence to the
important role that local variability (spatial and temporal) plays
and will play in climate change. This has led me to initiate a large
study on the southern Great Barrier Reef in which we are studying
phenomena from dinoflagellates to sea birds, from storms to
large-scale shifts in the East Australian Current. It is a massive
project that involves NOAA and NASA, several universities, and a set
of islands called the Capricorn-Bunker group. Ambitious though this
may sound, I believe that these studies are critical if we are to
understand the many challenges that we are likely to face as carbon
dioxide concentrations continue to rise.
A
great deal of your papers focus on coral reef studies. What impact is
global warming having on the world's coral reefs?
Coral reefs appear to be unusually sensitive to changes in ocean
temperature and acidity. Unfortunately, the corals that Len
Muscatine and I examined in the early 1980s were telling a highly
significant story that few of us recognized at the time. Coral
bleaching has been on the rise ever since—becoming more and more
intense as the climate has warmed. Coral bleaching is a general
response to stress—it happens when corals face conditions that are
too warm or cold, or when there are toxins in the water such as
herbicides or cyanide (used to catch aquarium fish in many
developing nations). It represents a state in which the symbiosis
(critical to the ability of corals to build coral reefs) between
corals and their brown symbionts breaks down. The net effect is that
the dinoflagellates depart, leaving the transparent coral tissue and
gleaming white skeleton behind.
Our work has identified climate warming as the number-one threat
to coral reefs. One has only to consider the impact of the global
cycle of bleaching in 1997-1998, in which unusually warm weather
worldwide plus some strange regional current patterns caused at
least 16% of the world’s coral reefs to die. I think one needs to
stop and consider that number. It might seem small until you
consider that this is 16% of 400,000 km2, or over 25,000
km2 of coral reef! Sometimes this may be hard to imagine
given the fact that we don’t visit or walk through coral reefs
every day. But just imagine if we woke up one morning to discover
that 16% of the world’s forests had died overnight.
Mass bleaching events such as these (which have continued since
1998) cause many of us to spend nights tossing and turning. Much of
our research efforts consequently are focused on gaining better
perspectives of how coral populations (and the hundreds of thousands
of other dependent species) will fare when we warm the planet by a
minimum of 2 degrees. These questions get us into areas such as the
socio-economic ramifications of changes of this magnitude. For
example, what happens to the estimated 100 million people that are
dependent on coral reefs for food and other resources?
I believe that the writing is on the wall for coral reefs under
climate change. Studies from the best laboratories project that
coral reefs as we know them may largely disappear under rapid
climate change. Two facts stand out. At 375 ppm carbon dioxide, we
are at the highest levels in at least 1 million years (if not 20
million years). Secondly, the rates of change are almost two orders
of magnitude faster than the faster rates of change seen in the last
million years (outside short-lived spikes in the climate record such
as the Younger Dryas event).
The latter is the key to understanding the problems faced by
organisms under rapid human-driven climate change. When the earth
warmed as it came out of the last ice age, global temperature
changed by approximately 5-7 degrees over a period of about 10,000
years. This was so rapid that dramatic changes occurred to the
distribution of almost every group of marine or terrestrial species.
Many species went extinct. The issue we are now facing is that
conditions are changing at approximately 50 to 100 times as fast.
Some paleontologists have confused the debate by saying that the
current rates of change are nothing unusual and that the earth
experienced change as rapid as that seen during the rare events like
the Younger Dryas. Again, two facts stand out. Firstly, these events
never took the earth above 300 ppm carbon dioxide and secondly, they
were short-lived (in geological time) and returned to values similar
to those prior to the event. These characteristics are fundamentally
different to those involving the sustained increase of carbon
dioxide to levels potentially as high as 600 ppm.
How
resilient are coral reef ecosystems?
Under normal circumstances, complex ecosystems like coral reefs
are fairly resilient to disturbances that might push them away from
equilibrium. Occasional storms and coastal flooding are examples of
circumstances in which corals may be removed in great numbers from
reef structures. Under natural conditions, coral populations and the
myriad of other species have rebounded, usually over a couple of
decades. This is due to the fact that components of healthy reefs
such as grazing fish and invertebrates, and conditions such as low
nutrient and sediment concentrations, keep fouling organisms like
seaweeds at bay so that corals can recruit into the ecosystem. Over
time, coral populations increase and reefs are restored following
calamity.
Coral reefs are also ecologically complex—perhaps over a
million species shelter within coral reefs. One of the consequences
of this complexity is that ecological roles (e.g., grazing) may be
performed by several groups of organisms on a coral reef with the
next effect of adding insurance against the impact of losing one or
another through natural perturbations. That is, if the numbers of
one grazing species fall, another is there to step forward and
fulfill the ecological function.
In more recent times, coral reefs have been beset with a
multitude of impacts that have weakened their resilience.
Overexploitation of fish has removed a significant component of the
grazers from reef communities, leaving invertebrate grazers to hold
the line. At the same time, water quality along most coastlines that
have coral reefs has deteriorated, tipping the balance further in
favor of non-coral organisms. And so on. The net effect of each of
these changes is that we have significantly and drastically reduced
the resilience of coral reefs such that recovery is taking longer
and more and more reefs are not returning to their former high coral
cover.
The resilience of coral reefs has a major role to play in the
dynamics of coral reefs in a warmer, more acidic global ocean. One
of the projections we are almost 100% certain of is that mass
bleaching events will become increasingly frequent and severe, with
mortality events such as the one in 1998 becoming much more
commonplace. Recovery processes and hence factors that promote
resilience consequently assume greater importance. This is why
increasing rather than decreasing our efforts to reduce the stresses
on coral reefs is crucial if we are to allow coral reefs any hope of
being present in these much more disturbed worlds. These issues are
a major focus of the recently formed Australian Research Council
Centre for Excellence in Coral Reef Studies, which has provided a
powerful network of research groups and laboratories focused on
working out how we might boost the resilience of coral reefs under
the challenging changes in the environment that they face.
What
can be done to protect coral reefs? Have any such programs been
implemented, and if so, has progress been observed?
There are two basic strategies that must be put into place
immediately if we are to have any reef ecosystem that resembles the
coral-dominated reefs of today. Firstly, we must limit the rise in
carbon dioxide to 500 ppm at the most. We know that anything higher
than a 2-degree warming will lead to unsustainable rates of coral
bleaching and mortality. Even then, we will be left with about 20%
of the coral reefs we have today. We also know that the associated
decrease in carbonate ions at 500 ppm carbon dioxide will also lead
to corals being unable to form skeletons.
Secondly, we must increase our efforts to reduce the other
stresses on coral reefs. If we continue to take away the
"gardeners" (grazing fish and invertebrates) and the
"pest-control officers" (mainly predatory fish) and
persist in increasing the amount of sediments and nutrients that run
off coastal areas into the waters surrounding coral reefs, their
ability to bounce back will continue to erode. If this happens at
the same time as the frequency and intensity of climate-related
impacts like bleaching and mortality increase, we may see coral
reefs like the Great Barrier Reef disappear into the annals of
history.
That said, we are optimistic that emissions will be wrestled
under control and that there is a lot we can do to increase
resilience to allow coral reefs the best chances under this
deepening crisis. This will involve a major global effort. The Coral
Reef Targeted Research Project funded by the World Bank, Global
Environment Facility and the University of Queensland is an example
of the scale of the networks needed to begin to deal with this
issue. With over 100 institutions and research laboratories
worldwide, this project is bringing many minds to bear on the
problems. I am hopeful that we will reverse the current
deterioration of these wonderful and important ecosystems.
Please
tell us a little about your current projects, if you are free to do
so.
I have a number of interesting directions and projects right now.
The first is that we have been successful in producing the first EST
(expressed sequence tag) libraries for Symbiodinium, the
dinoflagellate that forms the all-important symbiosis with corals.
We now have 1,360 different genes, whereas there were 13 known when
we started. This is leading to a lot of activity in my laboratory
aimed at finding and understanding how corals deal with stresses as
broad as bacterial infection, thermal stress, and carbon limitation.
It is fascinating to see the array of different genetic elements—this
project has opened up our understanding of probably the most
important organism on coral reefs. Out of this we are hoping to find
genes that may explain why some corals are more tolerant to thermal
stress.
The second direction we are putting effort into is understanding
which elements of the carbonate balance on a coral reef are
vulnerable to the problem of ocean acidification. In this regard, we
are expanding previous excellent work on corals to organisms such as
the developing stages of echinoderms and crustaceans, as well as
asking questions about how bioerosion changes when you shift the
concentration of carbonate ions. The latter could have major
implications for existing reef structures as the rate of bioerosion
(removal of carbonate by excavating organisms) is sensitive to
seawater acidity.
The third major project going on in the laboratory is one focused
on the spatial and temporal variability of climate impacts on coral
reefs. This project involves people looking at a range of organisms
from Symbiodinium to sea birds, and involves projects
investigating the connectivity of reef systems, how one translates
physiological vulnerability to the risk of mortality, and satellite
projects with NOAA and NASA. This is a truly exciting and
challenging project that will allow us to understand local and
regional patterns. We are also interested in relating these sorts of
changes to ecosystems to social and economic impacts. Coral reefs
are very important worldwide in terms of supporting human societies
through food and industries such as fisheries and tourism; many of
these societies live in developing regions of the world. There is a
direct linkage from ecosystem health to poverty. We are trying to
understand how fundamental changes in the health of reef systems
will affect these societies.
Professor Ove Hoegh-Guldberg, Ph.D.
Centre for Marine Studies
University of Queensland
Brisbane, Queensland, Australia
| Professor Ove Hoegh-Guldberg's
most-cited paper with 429 cites to date: |
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Walther GR, et
al., "Ecological responses to recent climate change," Nature 416(6879): 389-95, 28 March 2002. |
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Source:
Essential Science Indicators |
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