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Correlation of Predation with Diseases
and Tumors in Hawaiian Corals Cynthia L.
Hunter Waikiki Aquarium, University of Hawaii, 2777 Kalakaua Avenue, Honolulu, HI 96815
Although many reef areas in Florida and
the Caribbean have suffered losses in
living coral over the last two decades as a result of disease epidemics, no
outbreaks of such magnitude have yet been recorded in the Pacific. An outbreak of black band disease at Looe
Key, Florida, in 1986 was found to be associated with high temperatures,
eutrophication, and sedimentation (Santavy and Peters 1997). However, outbreaks of other diseases to date
do not appear to be consistently ascribable to known anthropogenic stressors
(e.g. pollutants, proximity to urban centers, global warming). Background rates of tissue loss as a result
of disease (i.e. non-outbreak occurrence levels) and their relationship to
subsequent phase shifts are currently unknown for any reef ecosystem. At least three types of disease have been
identified and commonly occur on Hawaiian reefs (Hunter and Peters 1992, Hunter
1994). Often, such disease is preceded
by injury or tissue damage from a suite of common predators: parrotfish, blennies, puffers, damselfish,
butterflyfish, and various invertebrates--most notably crown-of-thorns
seastars. Necrotic coral tissue can be
rapidly invaded by fine filamentous (turf) algae and cyanobacteria. There appear to be three resultant outcomes
of this invasion 1) a successional
change from turf to crustose coralline algae on which new coral recruits may
become established, 2) recovery and overgrowth by healthy, adjacent coral
tissues, or 3) persistence of the turf community and a profound change from
coral to algal domination of the affected colonies. It is of critical importance to determine the biotic and abiotic
factors that control these outcomes.
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