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11th ICRS Abstract book - Nova Southeastern University

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18.674<br />

Monitoring Of Coral Recovery After 97-98 Mass Bleaching Event At,<br />

Naneng SETIASIH* 1<br />

1 Reef Check Foundation Indonesia, Denpasar, Indonesia<br />

The aim of the monitoring was to understand the ecological response of the 4 reef<br />

systems to the mass bleaching event in relation to different reef habitat and protection<br />

level.<br />

LIT up to taxa level 5 (Oliver et all, 2002) was conducted in all parks as the baseline<br />

methodology.<br />

Monitoring stations at BBNP and BNP had a diversity of protection level and natural<br />

resilience. As the consequences, the result showed a wide range of % hard coral<br />

(%HC). On the other hand, stations the other parks were located in a limited human<br />

presure areas in the open sea, resulted in almost similar %HC.<br />

All locations showed a good condition of reef. Stations at KSMP and KJMP had a higher<br />

%HC, probably indicated that they were not affected by bleaching at 1997-1998, or<br />

showed a good recovery. This was confirmed by the relatively large coral colony found<br />

and high coverage of Acropora which is highly susceptible to bleaching (Baird and<br />

Marshall, 2002).<br />

Despite being badly hit by bleaching and repeated Acanthaster outbreak, an increase from<br />

7% HC (1998) to 25%HC (2006) was noted at BBNP. There were also segments with<br />

large coral colonies (>1m) at the park.<br />

Moreover, BBNP and KJMP indicated a higher percentage of high reistant taxa. This is<br />

consistent with the development of reef system after a mass bleaching event (Coles and<br />

Brown, 2003, Hoeg-Guldberg, 1999, Hughes and Connell, 1999), suggested a community<br />

structure’s shifting.<br />

BNP located in a naturally higher resilience areas to the other parks. The condition plus<br />

the well manage park probably has led the area to be less affected by bleaching.<br />

18.675<br />

Distribution And Abundance Of Sponges Of Minicoy Island, Lakshadweep, India<br />

Anita G. MARY* 1 , Robert SLUKA 2 , S. LAZARUS 1<br />

1 Institute for Environmental Research and Social Education, Nagercoil, India,<br />

2 Millennium Relief & Development Services, Bellaire, TX<br />

We conducted a survey of the distribution and abundance of sponges of Minicoy Island<br />

which lead to the discovery of thirteen species representing eleven genera from nine<br />

families. They are Axinella donnani, A. manus, Dragmacidon agariciformis, Auletta<br />

aurnatiaca, Pseudoceratina purpurea, Hyrtios reticulates, H. erectus, Spongia (Spongia)<br />

ceylonensis, Terpios cruciatus, Haliclona (Gellius) aff. Cymacformis, Dysidea granulosa,<br />

Leucetta chagosensis and Callyspongia (Euplacella) mannarensis. The distribution of<br />

sponges were assessed by using line-intercept transect technique. This was a pioneer<br />

study for this area with the discovery of five species entirely new to India and eight<br />

species new to the Lakshadweep islands. Images of each species are included to facilitate<br />

field identification.<br />

Poster Mini-Symposium 18: Reef Status and Trends<br />

18.676<br />

Variability in Growth Form Of Gulf Of Kachchh Corals, India.<br />

Prasanna YENNAWAR* 1<br />

1 Zoological Survey of India, Marine Aquarium and Research Centre, Digha, India<br />

The coral reefs in the Gulf of Kachchh are one of major reefs in the Indian sub-continent, which<br />

is under much threat due extreme environmental conditions. The biophysical monitoring study<br />

of the coral reefs in the area shows that the corals in this region are mainly massive & submassive<br />

corals like Porites, Favia, Favites & Montipora spp.). Many coral species are now<br />

exterminated like branching corals. The huge reef flats are dominated by one or two species at<br />

an instance and are exposed to uniform climatic changes with variable substrates reflected<br />

zonation in growth forms. Various topographic zones were compared with dominant species<br />

and it is observed that ubiquitous species adopted different forms in different zones of the same<br />

reef area. This is because of drastic environmental conditions like high sedimentation rate,<br />

extreme temperature conditions, periodical exposure, etc. The area is also highly industrialized<br />

with many refineries, submerged oil & gas pipelines, ports, cement, salt, power, ship-wrecking,<br />

etc. industries. The paper describes the variability in the growth forms with reference to variable<br />

climatic impact.<br />

18.677<br />

Seasonal Bleaching Did Not Impede Coral Growth in Todos Os Santos Bay, Eastern<br />

Brazil<br />

Eduardo CHAVES 1 , Pedro MEIRELLES 1 , Ruy KIKUCHI 1 , Zelinda LEAO* 1<br />

1 Federal <strong>University</strong> of Bahia - Brazil, Salvador, Brazil<br />

The linear growth rate of the corals Siderastrea spp and Montastraea cavernosa, from Todos os<br />

Santos Bay, was evaluated in order to verify if there was a relationship between the observed<br />

coral growth with variations in the conditions of sea water parameters (temperature, salinity and<br />

nutrients), as well as with the occurrence of coral bleaching events. Seventeen colonies of the<br />

coral Siderastrea spp and nineteen colonies of the specie Montastraea cavernosa were marked<br />

and observed from December 2005 to April 2007. Coral growth was measured every 15 days<br />

using fixed nails on the top of the coral colonies. This technique shows more efficiency in<br />

measuring the growth rate of the coral Siderastrea spp, once the specie Montastraea cavernosa<br />

shows resistance to the presence of the nails on the first months of the experiment. Among the<br />

measured sea water parameters, only sea water temperature shows relationship with the growth<br />

rate of the measured corals. The analyzed coral species grew more during summer time when<br />

temperature of sea water reached values up to 29°C. The growth rate of Siderastrea spp varied<br />

from 0.39±0.51 mm/month during summer (in the southern hemisphere from October to March)<br />

to 0.24±0.45 mm/month in winter (from April to September) and of Montastraea cavernosa<br />

from 0.21±0.41 mm/month during summer to 0.13±0.29 mm/month in winter. Observed<br />

bleaching was mild, during summer time, and all affected colonies recovered. During the period<br />

of investigation, sea surface temperature anomalies that could have been the major cause of the<br />

occurrence of a bleaching event of major scale was not registered in the studied region.<br />

432

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