Coral
bleaching is defined as the loss of algal symbionts and/or their
pigments in response to environmental stress conditions. Tropical
symbiotic corals, cnidarians, and mollusks exhibit signs of
bleaching. Environmental stresses include decreased salinity,
sedimentation, darkness, exposure at low tide, fluctuations in
temperature, and solar radiation. One stress, or a comination of
several stress factor, can result in a sudden reduction in the density
of algae in corals. Corals turn white because of the loss of
pigments from the algae (Fitt, Brown, Warner, Dunne, August 2001, p.
57-65.)
Image
12: Bleached coral
Image
13: Bleached coral
Bleaching
is a new phenomenon that was identified in the 1970s. The
increase in freqeuncy of coral bleaching incidences worldwide is
attributed
primarily to increases in sea temperature and levels of solar
radiation. Photosynthetic
symbionts of coral become vulnerable to light damage at higher sea
temperatures. The increase in sea temperature results in the
expulsion
of zooxanthellae from the host, leaving only the white tissue of the
coral.
The
increase in sea temperatures worldwide has been correlated to increased
concentrations of carbon dioxide and greenhouse gases in the
atmosphere. A 0.07 to 0.5 degree Celsisus increase in sea
temperature has been reported per decade. By 2100, scientists
expect sea temperature to increase by 1 degree to 2 degrees Celsius per
decade. Currently, coral bleaching occurs ever three or four
years, however, bleaching is expected to occur annually over the next
thirty to fifty years.
Image 14: Map
of 1997-1998 Bleaching Event
Scientists
Coles and Jokiel were the first to correlate coral bleaching
with elevated sea temperatures. Their research also demonstrated
seasonal differences in thermal tolerance of corals and the importance
of length of exposure time to upper lethal temperature limits (Fitt, Brown, Warner, Dunne, August 2001, p. 53).
There are three different types of coral bleaching:
physiological, algal-stress, and animal stress,
Physiological constraints
affect the size of population of symbionts living in coral host
cells. Coral tissue can only hold a certain number of symbiotic
dinoflagellates, therefore, the density of symbionts is directly
related to the amount of host tissue. Each coral may hold
different densitites and changes in the steady-state densities of
symbionts in host tissue may vary due to environmental varibales.
In addition, seasonal changes in solar radiation and sea temperature
occur throughout reefs worldwide. Research indicates that
seasonal changes affect the density of zooxanthellae in coral tissues
as well. Densities of symbionts are at their highest during cool
seasons with low levels of radiation, whereas densities are at their
lowest during very warm seasons with the high levels of radiation (Fitt, Brown, Warner, Dunne, August 2001, p. 54).
Although research shows that symbiotic dinoflagellates have less tolerance to increases in sea temperature and solar radiaton than their coral hosts, animal components of reef systems can be affected as well. "Bleaching is the result of relative tolerance of the algal versus the animal components" of the symbiotic relationship. Shedding of host issue that contains symbiotic algae is not prevalent, but laboratory experiments involve extreme temperature changes have induced animal stress bleaching. Stress on corals, the animal cells, could cause a release of algae, however, it is unlikely that animal stress bleaching would occur on a large scale (Fitt, Brown, Warner, Dunne, August 2001, p. 55).
Scientist
employ a variety of both intrusive and non-intrusive techniques to
determine what type of bleaching occurs on reefs. Although bleaching is reversible, corals die in great
numbers
following bleaching events. If a coral does recover, its health
is
compromised for hundred of years. Widespread coral bleaching has
many potential detrimental impacts on not only the health of coral reef
ecosystems, but the peoples who depend on them for their livelihood as
well.