[Coral-List] Bermuda bleaching event
Samantha de Putron
sputron at bbsr.edu
Fri Nov 21 16:50:43 EST 2003
Dear Coral List colleagues
The following is a report of the bleaching event witnessed in Bermuda this
summer.
Coral bleaching was witnessed this summer on the outer rim reefs and
lagoonal patch reefs of Bermuda (32 20N, 65 50W). Surveys of 2 sites at
each reef type were conducted by the Benthic Ecology Research Program of
the Bermuda Biological Station for Research (BBSR) at the end of
August/beginning of September (28/08/03 03/09/03) and again at the end of
September/beginning of October (19/09/03 06/10/03), looking at the
occurrence of bleaching and disease. The Rim Reef sites are at the edge of
the Bermuda platform approximately 17 km from shore, at a depth of 2-8m.
Inshore of the Rim Reef is the enclosed lagoon. The lagoonal patch reefs
monitored in this study are approximately 9km from land, at a depth of
1-4m. Each survey consisted of 12 x 20m long 2 m wide transects. The
surveys recorded the percentage cover as well as the occurrence of
bleaching and disease of the primary reef building and most abundant coral
species in Bermuda: Diploria labyrinthiformis, Diploria strigosa,
Montastraea cavernosa, Montastraea franksii and Porites astreoides. The
fire coral Millepora alcicornis was included as well as the gorgonians
Pseudoplexaura porosa Gorgonia ventalina. General observational notes were
made for other species, which are not included in this report. Please
contact us if you would like information on a particular species not
included here.
Of all the coral colonies recorded on the initial survey, 21% were bleached
at the rim reef sites and 19% were bleached at the lagoonal sites. Water
temperatures were at a maximum and had remained so for longer periods of
time than is typical (see below for temperature information). The second
surveys, when water temperatures had decreased, showed a decrease in total
bleaching to 13% at both sites. The fire coral, Millepora alcicornis was
the coral species most affected by bleaching this summer, with 94% of the
colonies being bleached to some degree on the rim reefs in early
September. On the lagoonal reefs at this time, 77% of M. alcicornis
colonies showed some sort of bleaching. Bleaching of M. alcicornis reduced
to 70% occurrence on the rim reefs, and to 49% on the lagoonal reefs, one
month later by the time of the second survey. In this species, the
bleaching on the rim reefs was mainly composed of completely bleached
(white) colonies or recently dead colonies (white skeleton with no fouling
of algae). At the time of the initial survey 35% of the total M. alcicornis
colonies on the rim reef were recently dead. This increased to 43% by the
time of the second survey. On the lagoonal reefs, the majority of bleached
M. alcicornis were classed as pale or blotchy and only 4% of the total
colonies were initially recorded as recently dead. This reduced to 3% by
the time of the follow up survey. A total of 60% of M. alcicornis colonies
were classed as pale or blotchy initially; this reduced to 43% by the
time of the second survey. Other colonies that were bleached at both sites
were (in order of prevalence) Montastrea franksi, Diploria strigosa, M.
cavernosa, D. labyrinthiformis and Porites asteroides. It should be noted
that many Agaricia fragilis colonies were extensively bleached in areas on
the outer rim reef, although this species was not included in these surveys.
Average temperature over the week in which the initial survey was performed
(28/08/03 03/09/03) was 28.9 ºC at the rim reef and 29.5ºC at the lagoonal
reefs. The maximum temperatures recorded from the sites were 30ºC at the
rim reef, and 30.7ºC at the lagoonal patch reef. The average temperature
during the week in which the second surveys were performed
(19/09/03 06/10/03) was 26.7ºC at the rim reef and 26.9ºC at the lagoonal
reefs. Bleaching was therefore more prevalent at the Rim Reef sites
compared to the Lagoonal sites even though the temperature maximum was
greater at the latter. This is similar to past observations in Bermuda
(Cook et al., 1990: Coral Reefs 9:45-49; McKinney et al, 1998: BBSR
unpublished data) and is understood to relate to a combination of increased
turbidity in the lagoon reducing irradiance, and/or the prior thermal
history at each site causing the adaptation (and therefore sensitivity) of
the coral populations to local conditions.
The incidence of disease was very low, with a total of only 1.5% of the rim
reef colonies, and 0.1% of the lagoonal corals being diseased on the
initial survey. Disease, however, increased slightly by the time of the
second survey at both sites, to 1.9% at the rim reefs, and 0.9% at the
lagoonal sites. The most commonly witnessed diseases on the scleractinians
were a White Plague type disease observed on Diploria labyrinthiformis,
Diploria strigosa, Montastrea cavernosa, Montastrea franksi, and Porites
asteroides on the rim reefs, and on all these colonies with the exception
of Montastrea cavernosa on the lagoonal reefs. Black Band Disease was
observed only on D. strigosa on the rim reefs, and on D. strigosa, M.
cavernosa and M. franksi on the lagoonal reefs. Aspergillosis was observed
on a low percentage of the sea fan Gorgonia ventalina (0% and 1.5%
initially at the rim and lagoonal reefs respectively, and 10% and 1.2% at
the rim and lagoonal reefs by the time of the second survey). We also
collected data on the incidence of hyperplasmic tumours (seen in the
Diploria species only) and fish biting (primarily of P. astreoides). Algal
galls were sporadically seen on the sea rod Pseudoplexaura porosa.
Please contact us if you require any further information.
Regards,
Helen Brylewska
Samantha de Putron Ph.D.
Graham Webster M.Sc.
Matt Strong
Dr Samantha de Putron
-----------------------------------------------------------
Bermuda Biological Station for Research
Ferry Reach, St Georges GE 01,
Bermuda
Tel: (441) 297 1880 x 261
Fax: (441) 297 8143
www.bbsr.edu
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