Biological Destruction on the Great Barrier Reef
Abstract
This thesis is an experimentally based study of the processes of
biological destruction on dead coral substrates on the Great
Barrier Reef. By placing recently killed coral samples in reef
environments it has been possible to compare the impact of
bioerosion processes on hard coral skeletons between different
environments and reefs. The experiments have shown that once a
dead coral substrate becomes available it is subjected to
recruitment by a diverse assemblage of endolithic borers that
excavate the interior of the substrate, while its surface is
eroded by the grazers that are adapted to scraping carbonate
substrates to remove epilithic and endolithic algal growth.
Experiments on Lizard Island reef have identified grazing as the
major destruction agent on coral substrates over the initial 4
years of exposure. Major differences between environments in the
amount of grazing are controlled by the distribution of the
highly mobile herbivorous fish community that is dominated by
scarids and acanthurids. Subtidal reef slopes and lagoon
environments of water depths less than 20 m are subjected to
higher rates of grazing erosion than shallow reef flat
environments. These differences in grazing are a result of tidal
cycles limiting the access of grazing fish to reef flats to high
tides only. The variability of grazing activity by bioeroding
fish is highly complex due to ecological and behavioral factors.
However, over time periods important to the geological
development of reef environments, these factors would be less
important than the major physical features of the reef that
determine scarids and
acanthurids populations between environments.
The Lizard Island experiments indicate that extensive borer
populations require at least 4 years to develop and that
consecutive 2-year sampling periods show significant differences
in the successful recruitment of borers. Early cryptofauna to
colonise dead coral substrates are small fabriciniid polychaetes.
These small polychaetes are followed by larger cirratulids,
spionids, eunicids and sabellines. Sipunculans, bivalve molluscs
and sponges only become important in the experiments after 4
years. This importance of time to the extent of borer excavation
in experimental substrates suggests that reef surfaces will be
extensively bored if they survive the destructive effects of
grazing. Recruitment differences within and between environments
and season will influence the structure of the borer community.
However, the long-term erosional impact of endolithic borers on
reef framework will be closely linked to the rate of surface
destruction by grazers.
The geological impact of the relationship between grazing and
boring is further revealed in experiments in the southern Great
Barrier Reef. These experiments were designed to assess the
differences in grazer and borer communities for 2 years on reefs
that represent adolescent, mature and senile stages of evolution
at sea level. These reefs were Llewellyn, One Tree, and Wreck.
Experimental samples placed in reef slope, flat, and lagoon
environments show that destruction caused by grazing fish is
reduced as lagoon environments are restricted by sedimentary
infill that expands reef flat conditions. In addition, grazing
by gastropods becomes increasingly important in these reef flat
conditions. However, the rates of erosion by these grazing
molluscs in senile environments on the protected surfaces of
substrates are considerably less than the rates of destruction
caused by fish in subtidal adolescent reef environments. With
reduced destruction, accretion by encrusters is important on
substrates. This accretion further protects surfaces, preserving
the volume of the substrate and allowing the establishment of
borer communities. Through the turnover of these borers and the
addition of encrustation, substrates may be preserved, but they
are likely to be converted from original coral to substrates
composed of bored encrustation. Extrapolating the patterns of
the accretion - erosion balance on experiments to the long term
impact on reef surfaces predicts that framework in senile reef
environments will be subjected to many cycles of boring and
encrustation, producing a highly altered reef rock. Dead coral
framework in adolescent environments is subjected to rapid
destruction by grazers such that borer communities may remain in
early successional stages. The conversion of framework to
sediment through this destruction is an important contribution to
the infilling of the lagoons and to the way that growth
frameworks are ultimately incorporated into the foundation of the
reef.
In addition to these experiments in subtidal environments, an
experiment was designed to measure rates of surface destruction
on windward intertidal reef crest surfaces at One Tree Reef.
Using an instrument that measures differences in the elevation of
reef surfaces through time it was possible to establish that
rates of destruction increase toward the reef margin and that the
highest rates recorded approach the rates of construction that
have been estimated by others for the environment. Biological
processes, including grazing, are interpreted to be responsible
for this destruction since longer exposure to subtidal conditions
increases erosion and the activity of grazers and borers. The
intertidal pavement that is submerged for longer periods during
tidal cycles recorded rates of erosion more than twice those
recorded on the supertidal cemented rubble platform. The rates
indicate the magnitude of accretion that has been necessary to
maintain this environment in intertidal conditions.
Overall, the study provides a different view of short-term
biological processes that effect the long-term geological
development of reefs. The changing relationship of grazing,
boring and accretion on frameworks as a reef evolves provides a
geological record that is a potential measure of the physical and
ecological change that has occurred in the past, and is occurring
on reefs today.
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