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Broadscale effects of bleaching
on the Great Barrier Reef
(2001-2003)
The AIMS Long-term Monitoring
Program surveys sites on NE flanks of reefs annually. Reefs are
surveyed at about the same time each year. Because of the area
involved, the surveys span a period between October and May.
Bleaching occurred in 2002 midway through the field sampling
season.
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Figure 1. Hotspot maps from NOAA show the warming water
around the GBR in January, 2002.
NOAA satellite imagery (fig 1.)
identified higher than average water temperature over the GBR
and much of the coral sea in January, 2002 and the GBRMPA
surveys confirmed that coral bleaching was occurring at this
time.
Aerial surveys of the GBR
indicated that more reefs were affected by bleaching than in
1998 (fig 2).
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Figure 2.
Proportion of inshore (top) and offshore (bottom) reefs
surveyed that were unaffected (<1% of reef affected) by bleaching
versus reefs with moderate (1-30% affected) to high (>30%
affected) bleaching in 1998 and 2002 click here to visit
www.gbrmpa.gov.au and read the
full report comparing 1998 and 2002 bleaching events.
As a simple measure of the
broadscale effects of the 2002 bleaching event, the total living
hard coral (from video transects (see
Methods)) at the 2001 surveys [well before bleaching] were
compared with equivalent data from the 2003 surveys [well after
bleaching]. Data were available for 49 reefs spread across the
GBR. The figure shows the average percent cover values on sites at
each survey reef, arranged by latitude and position across the GBR
lagoon [inshore to offshore]. For each reef, the darker blue bar
represents the mean hard coral cover at the 2001 survey. The paler
blue bar gives the same information for the 2003 surveys. Survey
methods are described in a number of documents available on the
AIMS web-page; it is important to note in this context that the
study sites are generally at 6-9 m depth.

Figure 3. Change in hard coral cover during the period
2001-2003 on LTMP survey reefs. Click on the map to enlarge.
Taking an arbitrary figure of 5%
change from pre-existing coral cover as the criterion for
substantial change:
- Survey sites on 6 of the reefs
lost more than 5% of the initial average coral cover over the
two years. Of these 6 reefs 4 had infestations of Crown of
Thorns starfish.
- Survey sites on 7 reefs gained
more than 5% of the initial coral cover in that period.
- Sites on 34 reefs showed little
average change (-4.9% to 4.9% of initial cover) over the two
years.
LTMP surveys show that at depths of
6-9 meters there was very limited impact on hard coral cover from
bleaching in 2002. Myrmidon Reef (declined from 35-24%) off
Townsville and Reef 19131 (declined from 40-33%) in the
Whitsundays were the only reefs where bleaching had a substantial
effect on hard coral cover. These results confirm that bleaching
does not always result in coral mortality. The extent of mortality
from bleaching is unpredictable in that there are many localised
factors that affect recovery. In general, as LTMP sites are
located on the NE flank water circulation would be expected to be
high. Recovery from bleaching would be enhanced in areas of higher
water flow and thus LTMP results may not be representative of
other reef zones. To date it would appear that mortality from
bleaching has been mostly confined to shallow water, or has been
very localised spatially.
Bleaching has additional
implications for reef growth apart from coral mortality. Sub
lethal effects such as reduced reproductive ability, reduced
calcification rate and increased susceptibility to stress have
been documented by numerous studies (eg see Hoegh-Guldberg (2004)
review). During the period of 1995-2003 there has been an
increase in the number of LTMP survey reefs experiencing little
change in percent cover over 2 year time intervals. This data
reflects the combined effects of all disturbances during the
survey period and represents a very short time frame in the
context of reef growth.

Figure 4. Magnitude of
change on LTMP survey reefs from 1995-2003.
December 18, 2008
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