In the second half of 2005, the Caribbean region experienced a
widespread coral bleaching episode. As such episodes have previously
caused widespread mortality amongst reef building corals, there
was a great deal of concern amongst the scientific community, fisherfolk,
tourism organisations and other interested stakeholders. In order
to determine the extent and nature of the impacts of the episode
on the reefs of their island, the Buccoo Reef Trust (BRT) and the
Tobago House of Assembly (THA) decided to invite a team of 5 scientists
from Coral Cay Conservation (CCC) to assist in undertaking targeted
surveys of the coral bleaching in Tobago.
Over a three week period commencing in October 2005, a two-phase
campaign was launched: in Phase 1 the reefs were assessed to establish
the extent and severity of the coral bleaching on Tobago’s
main reef systems, in Phase 2, an appropriate long-term monitoring
programme was designed and installed to examine the recovery of
bleached corals. The content of this report deals mostly with Phase
1, as the data from Phase 2 will not be complete until May 2006.
Overall mean bleaching of hard
corals was found to be 66% (71% on deep transects and 63% on
shallow sites)
Phase 1 involved surveys of 22 discreet sites, which were assessed
using a Point Intercept Transect method, utilising a 20m transect
chain marked at 25cm intervals. At each site, two deep and two shallow
surveys were completed, producing over 7000 data points from 88
transects. Overall mean bleaching of hard corals was found to be
66% (71% on deep transects and 63% on shallow sites). Bleaching
by geographic region was found to be largely consistent, with sites
exhibiting greater than 85% bleaching dispersed throughout the target
area. However, of the 9 transects exhibiting less than 20% bleaching,
5 were located near Speyside in the northeast of Tobago, perhaps
indicating either localised tolerance to bleaching or superior water
quality (lower temperatures, less silt and fewer nutrients).
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Bleaching by species was found to be highly variable, both between
and within species. Agaricia agaricites (‘leaf’)
and Siderastrea radians (‘rough starlet’) were
the most impacted species, with 93% of the observations for both
species being bleaching. Madracis mirabilis (‘yellow
pencil’) and Acropora palmata (‘elkhorn’)
were the least impacted species (3% and 0% respectively). Although
the low number of observations recorded for A. palmata (n=7) reflects the low abundance of the species, many additional
stands were observed by the surveyors during the campaign and all
appeared to be unbleached. Very high variability was found amongst
the species of the Montastrea annularis complex (‘boulder/mountainous
star’), which demonstrated overall bleaching impacts of 73%.
For example, at one site in Buccoo Reef, two adjacent stands of M. annularis (annularis) exhibited 97% and 6% bleaching
impacts respectively, implying the existence of bleaching resistant
combinations of the coral species, its algal symbionts, or both.
It is not possible to predict the nature and extent of any subsequent
mortality/recovery to the reefs of Tobago. Whilst cyanobacterial
overgrowth was observed on the colonial zoanthids of the Palythoa genus, there were no recorded observations of coral disease, tissue
necrosis or turf-algal/cyanobacterial overgrowth on bleached scleractinian
corals. However, the incidence of opportunistic coral diseases may
be expected to peak at the end of the warm season, and thus remain
to be quantified. The monitoring programme installed during Phase
2 has been designed to gather these data.
Phase II
Eight monitoring stations were established on representative coral
reefs around Tobago, only one of which was located on the Atlantic
coast (Cove) because of the generally rough and dangerous conditions
on this side of the island. Each station consisted of a 20 metre
long transect that followed the reef along the 10 metre depth contour,
and was marked at each 5 metre interval with a sub-surface float
tied 6ft above the seabed. Along each of the 20 metre transects,
20 coral colonies were randomly selected and individually tagged
with an engraved plastic tag that was nailed to the adjacent reef
substrate. The tagged corals were monitored by scuba surveys using
an underwater digital camera (Sony Cybershot 5.1 megapixel) mounted
on a PVC photoquadrat (50 cm x 50 cm). Each tagged colony was photographed
on the 20th November 2005, 18th January, 3rd April and 2nd September
2006 (+ or - 2 days). The sea temperatures at four of the sites
were logged using HOBBO© waterproof pendant dataloggers.
Digital photographs of the tagged colonies were examined for changes
in colour level using the CORALWATCH
Coral Health Chart, using seven categories ranging from; 6 =
fully pigmented to 0 = totally unpigmented (white). The average
pigmentation of the entire colony was used when blotches or spots
were present. Tagged colonies were also analysed for changes in
their live surface area (partial mortality). This was done visually
using the following seven categories; 6 = 0% partial mortality (no
change in live surface area); 5 = 1-20% partial mortality; 4 = 21-40%;
3 = 41-60%; 2 = 61-80%; 1 = 81-99%; 0 = 100% mortality. Attempts
to use image analysis software to calculate partial mortality proved
impractical because of the 3 dimensional shape of the colonies.
Results
At all sites, pigmentation returned to the colonies rapidly, with
most gains occuring between November and April, with little or no
gain between April and September 2006. The site where corals showed
the slowest colour recovery was Cove on the Atlantic coast, where
water temperatures remained initially close to 1°C warmer than
sites on the Caribbean coast.
Between the 20/11/05 and the 2/09/06 the level of survival of the
all the tagged coral colonies was high, with only 11 colonies or
6.9% suffering 100% mortality. All of these 11 mortalities were
from the category of 58 tagged corals that were severely bleached
or “Totally Unpigmented”, equivalent to a mortality
rate of 19% for this category. Of the 11 colonies that died there
was a noticeable majority of Brain corals; 6 Diploria strigosa (16%, n=37) and 2 Diplora labyrinthiformis (10%, n=20).
The other 3 mortalities were 1 Porites astreoides ( 20%,
n=5), 1 Agaricia agaricites (1 or 50%, n=2), and 1 Montastrea
annularis (2.4%, n=42).
Of the colonies that survived, 32.5% (52 individuals) suffered
some level of partial mortality (or a reduction in the surface area
of living tissue). Levels of partial mortality were highest among
colonies that lost all or most of their pigmentation during the
bleaching event of 2005 (Colour categories 1, 2 and 3 on the CORALWATCH
Health Chart). Colonies that experienced little or no bleaching
in 2005 (Colour categories 4, 5 and 6) suffered very little loss
of living surface area. The level of partial mortality was highly
variable between colonies, and often appeared to be associated with
an outbreak of coral disease.
The level of partial mortality varied between sites, with the
highest level occurring at Mt Irvine (mean 50% partial mortality)
and the lowest at Kariwak (12%). Both these sites are located close
inshore in close proximity to tourism and residential developments
and are known to be affected seasonally by high levels of nutrients
and silt. There was no correlation between level of partial mortality
and the distance between the shore and the site.
Conclusion
The data (approx. 8,000 data points) gathered during this study
showed that the bleaching event of 2005 observed in Tobago was both
severe and widespread. An average of 66% of the hard coral cover
in Tobago was visibly affected, with levels over 85% observed at
many sites. All reefs on the Caribbean coast were badly affected,
while those at Speyside showed greatly reduced levels of bleaching
for reasons that are still unknown. The lack of bleaching in this
extensive reef system emphasises the need to implement urgently
the THA’s plans to establish a Marine Protected Area at Speyside
and to improve the management of the surrounding watersheds in order
to minimise siltation and pollution impacts on this important “upstream
reservoir” of coral biodiversity.
The majority of tagged corals recovered their pigmentation between
November 2005 and April 2006, giving rise to optimism among many
observers that the worst was over. However, closer inspection of
these corals until September 2006 revealed that partial mortality
was evident in 32.5% of the tagged colonies, with a further 6.9
% suffering total mortality. The level of partial mortality was
greatest in corals that had been severely bleached, and this was
often associated with symptoms of tissue necrosis and coral diseases.
Brain corals (Colpophyllia natans, Diploria strigosa and Diploria labyrinthiformis), which account for 21% of
the corals observed, were particularly badly affected and accounted
for 73% of the observed total mortalities. This suggests that these
slow-growing massive species may be more vulnerable to bleaching
than other corals found in Tobago’s waters.
In order to understand the long-term effects of bleaching events,
monitoring of coral diseases will be particularly important. The
risk of disease spreading to other colonies highlights the need
to urgently improve coastal water quality and reduce other stressors
on Tobago’s reefs. Particular attention must be given to reducing
land-based sources of pollution, such as inadequately treated sewage
and domestic grey water, as well as contaminated storm run-off and
silt. Local management initiatives that improve the health of coastal
ecosystems will give corals a better chance of successfully overcoming
future coral bleaching events and adapting to the environmental
changes that lie ahead.

