Figure 1: Total number of intense hurricanes, showing a
significant increase in category four and five storms over the period 1970-2004
(Webster et al, 2005).
The assessment of coral damage following hurricanes and
cyclones has been carried out for many years. Rogers et al (1991)
monitored coral reef off the south coast of St John, US Virgin Islands, at a
depth of 11-13m. Nine months after permanent transects were set up Hurricane Hugo struck, allowing the analysis of storm destruction. The category 5 hurricane caused patchy
damage to the reef, with large waves moving and damaging significant quantities
of coral and depositing sediment on the sea floor. Following the storm there
was a decrease in the percentage of living coral by 40%, 12 months later there
had been no significant increase in the amount of live coral. There was also a
decline in species diversity following the storm. The ability of a coral reef
to recover following storm damage is highly influenced by the extent of human
activities, with overfished ecosystems showing poor recovery compared with less
disturbed reefs. Similar results were found in a more recent study by Guillemot et al (2010), following Cyclone Erica in New Caledonia, South Pacific, 2003.
The cover of live coral decreased by 45% in the two year period following this
storm. After four years the coral reef displayed good signs of recovery, with a
return to pre-cyclone fish community. It is suggested that the moderate
anthropogenic pressure in this region was conducive to good resilience and recovery.
In order to predict how future changes in tropical storm
intensity are likely to affect coral reef ecosystems it is useful to assess long-term
variability as well as their role in ecosystem disturbances. Through topographical
surveys and geological dating of coral ridges and terraces (which are produced
by storms) it is possible to estimate historic storm surge and wave heights.
Nott and Hayne (2001) determine the intensity of tropical cyclones along the Great Barrier Reef over
the past 5,000 years using this method. Their results indicate a long history
of intense tropical cyclones in this region, with the majority leading to widespread
coral damage, including a weakening of the substrate which
enables severe damage to occur during less intense storms. This study suggests
that storm events are central to coral community structure and function,
including the life span of individual corals. Therefore, if the frequency and
intensity of these events is to change it may have significant negative
repercussions for coral reef ecosystems. The authors of this study consequently
believe that coral reef ‘vulnerability, exposure and risk is much higher than
previously estimated’ (Nott and Hayne, 2001 p.511).
Once again it appears that coral reefs are likely to be
negatively affected by climate change. Although there is strong evidence that
coral reefs are resilient to storm damage, and are able to recover in the
long-term, the ability of these ecosystems to do so is significantly reduced in
regions where human pressures are having damaging impacts. The need to
reinforce reef resilience through effective policies and management appears a
necessity if these fragile, yet globally important, habitats are to be
maintained.
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