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11th ICRS Abstract book - Nova Southeastern University

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24.1063<br />

Successful Reef Rehabilitation Through Coral Transplantation At Hikkaduwa<br />

Marine Park, Sri Lanka<br />

Suki EKARATNE1, Sithara JINENDRADASA* 2<br />

1 2<br />

Zoology, <strong>University</strong> of Colombo, Colombo, Sri Lanka, International Water<br />

Management Institute, Colombo, Sri Lanka<br />

Coral transplantation with Acropora ‘fragments’ in the reef lagoon at Hikkaduwa Marine<br />

National Park , Sri Lanka, following mass coral mortality in April 1998, and monitored<br />

over 8 years, including after the tsunami event, tested eight transplantation techniques in<br />

areas that previously had live coral stands. These were cut-nubbins, horizontal untethered<br />

and tethered fragments, upright tethered fragments, branched fragments attached to<br />

rubber bases and to concrete grid-blocks, branched fragments in sand and shaded/exposed<br />

fragments, where transplantation success was assessed using Anova on monthly linear<br />

growth, branching and survival.<br />

Transplanted cut-nubbins grew at 0.30±0.027mm.day -1 with branching by the first month<br />

of transplantation, but suffered 100% loss due to fish cropping. Horizontal untethered<br />

fragments incremented at 0.05±0.016mm.day -1 with 60% mortality and drupellid<br />

colonization, branching commenced at one month. Horizontal tethered fragments<br />

incremented at 0.01±0.046mm.day -1 with 47% mortality and light attachment within a<br />

month. Upright tethered fragments showed negative growth (-0.36±0.100mm.day -1 ).<br />

Branched fragments attached to rubber mat-base grew at 0.03±0.011mm.day -1 , without<br />

any mortality. Branched fragments attached to concrete grid-blocks grew at<br />

0.08±0.010mm.day -1 showing alternating slower and faster growth periods, and without<br />

any mortality. Branched fragment in sand showed 0.2±0.040mm.day -1 growth and no<br />

mortality, but their basal regions became buried with sediment deposition. Shaded and<br />

exposed fragments grew at 0.07±0.100mm.day -1 and 0.03±0.054mm.day -1 , respectively,<br />

with no mortality.<br />

Since transplantation of branched fragments onto concrete grid-blocks yielded best longterm<br />

results, 4’ by 4’ areas transplanted by this method were monitored over 8 years and<br />

proved successful, attracting a variety of fish, with no loss even from the forces of the<br />

tsunami. Sediment accumulation, common with degraded reefs, passed into holes of its<br />

gridded design. Transplanted fragments, being placed horizontally, also withstood<br />

cropping pressure.<br />

24.1064<br />

Comparison Of Fish Assemblages Between Mitigation Boulder Reef And<br />

Neighboring Natural Hardbottom in Broward County, Florida, Usa<br />

Jessica FREEMAN* 1,2 , T. Patrick QUINN 1,3 , Lance K. B. JORDAN 1,2 , Kirk<br />

KILFOYLE 1,2 , Richard SPIELER 1,4<br />

1 Oceanographic Center, <strong>Nova</strong> <strong>Southeastern</strong> <strong>University</strong>, Dania Beach, FL, 2 National Coral<br />

Reef Institute, Dania Beach, 3 Biological Resources Division, Broward County<br />

Environmental Protection Department, Plantation, 4 National Coral Reef Institute / Guy<br />

Harvey Research Institute, Dania Beach<br />

A beach renourishment project was initiated in May 2005 and completed in February<br />

2006 to restore 11.1 km of shoreline in Broward County, Florida, USA. For mitigation of<br />

predicted nearshore hardbottom burial, a boulder reef totaling 3.6 ha was deployed in<br />

2003. To examine the replacement value of the mitigation relative to fishes, this study<br />

compared fish assemblages on boulder reef to those on adjacent natural hardbottom.<br />

Twenty-five natural hardbottom sites and twenty-five boulder reef sites were surveyed<br />

six times between March 2005 and August 2007. Two non-destructive visual census<br />

methods, a transect count (30 m long x 2 m wide x 1 m high) and a 20 minute rover diver<br />

count (approximately 30 m x 30 m), were conducted at each site to assess abundance and<br />

species richness. On transect counts 7,117 fishes of 96 species were counted on natural<br />

hardbottom, while 11,769 fishes of 119 species were counted on boulder reef. Across<br />

both survey types, a total of 271 species was recorded. Significant differences among reef<br />

fish assemblages were found in both abundance and species richness (p

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