of colonies affected by bleaching in a given area).
These parameters can be calculated at the site or
regional level (including all coral species in one reef-
wide average) or calculated by species, at a variety of
scales.
The degree of bleaching can be categorized by severity
(e.g., AGRRA)3,8:
0 = No bleaching,
1 = Pale (discoloration of coral tissue),
2 = Partly Bleached (patches of fully bleached or white
tissue), and
3 = Bleached (tissue is totally white, no zooxanthellae
Melanie McField / WWF
visible).
Data Needs
Bleached corals can be monitored for subsequent
mortality or disease.
Coral bleaching data are available from the MBRS
and AGRRA websites, along with various monitoring
Usefulness
Usefulness
program reports and research publications, some of
which may not be readily accessible in the region.
The coral bleaching signal depends on when
observations are made (i.e., during or after an event).
Although several monitoring programs assess coral
If a bleaching event is not monitored over time, it may
bleaching in the MAR, we recommend developing
be difficult to determine the extent of resulting tissue
a BleachWatch program, modeled on the existing
mortality. Coral bleaching varies depending upon coral
programs in the Great Barrier Reef and Florida
species (e.g., some species bleach earlier, and some
Keys28,29. These programs provide training, planning,
tend to stay bleached longer), water depth, reef type,
and rapid response monitoring teams to track the
physical environment (e.g., water clarity, proximity to a
progression of coral bleaching events (including
channel) and disturbance history.
any delayed mortality associated with coral disease
outbreaks). This approach would provide regionally
Coral bleaching is not an early warning signal.
consistent data and a better indication of the impacts
However, NOAA HotSpot maps do provide a good
following a bleaching event. Collaboration and training
alert to water-temperature conditions that may cause
could involve marine tour guides and divemasters,
bleaching. (See Indicator D14 - Coral Bleaching Index).
who can act as "first responders" to alert managers
Coral bleaching may be a good indicator of climatic
and scientists of signs of a bleaching event.
changes.
More research is needed on the response and
Status
Status
adaptability of corals and their algal symbionts,
bleaching effects on reproductive fitness and
The prevalence of coral bleaching will vary naturally
strategies of corals, and effects on calcification.
year to year. In summer 2000, which was not a mass
Additional research is needed on the resilience of reef
bleaching year, the average prevalence of bleaching in
areas to coral bleaching, and these findings need to
the MAR was 9%, with 11% bleached on the fore reef
be incorporated into MPA design and management.
and 7% on the reef crest9. This level is approximately
the amount expected for a non-bleaching-event year
In order to develop better benchmarks and targets
and may be related to a variety of smaller-scale
that encompass the ecological outcomes of bleaching,
stressors. However, the MBRS Synoptic Monitoring
the resiliency and potential susceptibility of various
Program (Mexico and Belize 2004/05, all habitats)
areas need to be evaluated, and an index similar to
found only 2.5% colonies bleached.
the "LD50" index of toxicology studies needs to be
developed for different levels of coral bleaching.
The most significant mass bleaching events in the
Such an index would encompass the severity (degree
MAR occurred in 1995 and in 1998 with ~50% to
of bleaching in each colony) and the prevalence
90% of corals bleaching in some areas25,26. Moderate
of bleaching (percent of corals affected in an given
bleaching (~30% to 40% of corals bleaching) occurred
area).
in some areas of the MAR in 200527.
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