11th ICRS Abstract book - Nova Southeastern University
11th ICRS Abstract book - Nova Southeastern University
11th ICRS Abstract book - Nova Southeastern University
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24-45<br />
Alternate Benthic Assemblages On Artificial Reef Restoration Structures And Their<br />
Effects On Coral Larval Settlement<br />
Margaret MILLER* 1 , Abel VALDIVIA 2,3 , K. Lindsey KRAMER 4 , Benjamin<br />
MASON 5 , Dana WILLIAMS 3,6 , Lyza JOHNSTON 5<br />
1 Southeast Fisheries Science Center, NOAA Fisheries, Miami, FL, 2 CIMAS, <strong>University</strong><br />
of Miami, Miami, FL, 3 Southeast Fisheries Science Center, NOAA Fisheries, Miami, 4 US<br />
National Park Service, Hilo, HI, 5 Marine Biology and Fisheries, <strong>University</strong> of Miami,<br />
Miami, FL, 6 CIMAS, <strong>University</strong> of Miami, Miam, FL<br />
Acute physical reef injuries are sometimes addressed by construction of on-site artificial<br />
structures to secure fractured framework and enhance architectural complexity of<br />
damaged sites. To characterize benthic assemblages, four restoration structures (RS)<br />
along with adjacent natural reef substrates (Reference) in the Florida Keys, USA (age<br />
range 6-13 yrs) were sampled via line-intercept transects. Multivariate clustering<br />
analysis indicated a high degree of divergence between RS and Reference samples, as<br />
well as among sites. RS had significantly higher cover of thick cyanobacterial turfs (up<br />
to 30% cover) than Reference substrates. Assemblage differences were primarily<br />
attributable to macroalgal and cyanobaterial groups with fast growth and turnover, rather<br />
than to slow-growing corals and crustose coralline algae. Thus, divergence of<br />
assemblages is not simply attributable to incomplete succession, but appears to be a<br />
persistent, possibly stable state.<br />
Since cyanobacteria have known ill effects on adult and larval corals, we tested if<br />
exudates of these distinct algal assemblages (RS and Ref) chemically inhibit coral larval<br />
settlement. Seawater exudates were prepared from 1m 2 of macroalgae, including turf,<br />
collected from RS and Reference substrates at two sites (Wellwood and Maitland).<br />
Competent larvae of three broadcast spawning scleractinian species were exposed to<br />
natural substrate in exudates or seawater controls and allowed three days to settle.<br />
Acropora palmata and Diploria strigosa larvae were subject to exudates from a single<br />
site (Wellwood) while Montastraea faveolata larvae were tested with exudates from both<br />
sites. Reference exudates from the Wellwood site displayed greatest settlement inhibition<br />
for all 3 species while, for M. faveolata, RS exudates from the Maitland site were more<br />
inhibitory than Maitland Reference exudates. A.palmata larvae displayed greater<br />
sensitivity than the other species with 100% mortality in the Wellwood Ref treatment.<br />
Both RS and Reference substrates in these locations appear to have compromised<br />
‘recruitment potential’ for spawning corals.<br />
24-46<br />
Natural And Enhanced Coral Reef Recovery After Injury<br />
Alison MOULDING* 1 , David GILLIAM 1 , Vladimir KOSMYNIN 2 , Richard DODGE 1<br />
1 National Coral Reef Institute, <strong>Nova</strong> <strong>Southeastern</strong> <strong>University</strong>, Dania Beach, FL, 2 Bureau<br />
of Beaches and Coastal Systems, Florida Department of Environmental Protection,<br />
Tallahassee, FL<br />
The coral reefs of Broward County, southeast Florida, USA are located offshore a highly<br />
urbanized area. Because of the close proximity of a major shipping port and its<br />
associated anchorage, Broward reefs have been impacted by more than 10 ship<br />
groundings over the last 15 years. These injuries usually require restoration to speed<br />
recovery and compensate for damage. However, the recovery process on injured sites is<br />
not well understood, and even less is known about how restoration aids in recovery. This<br />
study examines coral recruitment, growth, and mortality in permanent quadrats on injured<br />
sites to asses their potential for natural recovery. It also investigates substrate materials<br />
commonly used in reef restoration, including limestone, concrete, and terracotta, to<br />
determine their efficacy in attracting and retaining coral recruits. Lastly, transplantation<br />
of juvenile corals collected on settlement plates from areas of higher coral recruitment<br />
and of corals raised in the lab from the larval stage is examined as a potential method to<br />
enhance reef restoration. Preliminary results indicate coral recruitment rates to injured<br />
sites were higher compared to reference sites. Mortality rates at the injured sites were<br />
also higher than reference sites. After one year of deployment, more corals settled on<br />
limestone plates than on concrete or terracotta. Hence, recovery on injury sites may be<br />
hampered by high juvenile coral mortality rates, and the choice of substrate materials<br />
used in restoration may influence recovery.<br />
Oral Mini-Symposium 24: Reef Restoration<br />
24-48<br />
Recruitment Of The Temperate Scleractinian Coral, oculina Arbuscula, To Natural And<br />
Artificial Substrata On Reefs Of The South Atlantic Bight, U.s.a.<br />
Daniel GLEASON* 1 , Leslie SUTTON 1<br />
1 Department of Biology, Georgia Southern <strong>University</strong>, Statesboro, GA<br />
Similar to their tropical counterparts, temperate reefs have high biodiversity, but are in peril<br />
from anthropogenic impacts. Primary threats include commercial trawling, recreational fishing,<br />
ocean acidification, and increased sedimentation. Oculina arbuscula is a temperate, broadcast<br />
spawning coral and is the only structurally complex Scleractinian occurring on hard-bottom<br />
reefs of the South Atlantic Bight, U.S.A. Oculina arbuscula is an important contributor to reef<br />
rugosity in this ecosystem, but can be easily damaged by dredges and trawls. To investigate the<br />
sustainability of these coral populations on reefs off the Georgia coast we monitored<br />
recruitment of O. arbuscula to 30x30 cm plots over 3 years. Treatments consisted of 10<br />
replicates of each of the following: 1) unmanipulated natural substrata, 2) natural substrata<br />
initially cleared of all encrusting organisms, and 3) artificial substrata consisting of concrete<br />
paving tiles. These plots were photographed at least 13 times between July 2004 and June 2007<br />
using a digital camera mounted to a PVC frame to control for distance and exposure level.<br />
These images showed that O. arbuscula recruits throughout the year with peak recruitment<br />
exhibited in September/October. While recruitment rates were higher than death rates in all<br />
treatments and resulted in a net gain of O. arbuscula colonies, recruitment to artificial substrata<br />
far exceeded that found on natural surfaces. Competition with other sessile invertebrates, such<br />
as tunicates and sponges, appeared to contribute little to these differences because recruitment<br />
rates were similar on unmanipulated and cleared natural substrata. Likewise, the high<br />
recruitment rate observed on the artificial substrata rules out the possibility that maintenance of<br />
O. arbuscula populations is limited by larval supply. While the reasons are unclear currently,<br />
these results suggest that deploying artificial substrata, such as concrete paving tiles, may be<br />
useful as a mechanism of enhancing recruitment of O. arbuscula to damaged temperate reef<br />
structure.<br />
24-49<br />
Brazilian Corals Early Growth And Survival<br />
Clovis CASTRO* 1 , Bruna CASTRO 1<br />
1 Departamento de Invertebrados, Museu Nacional, Rio de Janeiro, Brazil<br />
Early growth and survival of coral recruits are crucial for the renewal of coral populations and<br />
restoration initiatives. In order to assess these parameters, we set up experiments with different<br />
recruitment plates (plastic and ceramic) and environmental conditions (open sea and tanks). In<br />
the laboratory, coral spats were recorded using a dissecting microscope. Each individual spat<br />
was measured and its position recorded using a coordinate system. Plastic plates were deployed<br />
in January, 2004, and initially kept in the Itacolomis Reefs (16°54’S, 039°04’W) for circa 15<br />
months. Censuses occurred in June, 2005 (T0) and March, 2006 (T1 – 9 months). This<br />
experiment started with 1762 live spats and ended with 574. Survival rates were higher in tanks<br />
(61%, excluding spats in lost plates, vs. 15% in open sea). Survival was also higher in larger<br />
spats, both in tanks and open sea. Growth rates were slightly higher in tanks. Larger spats grew<br />
faster than smaller ones. Ceramic tiles were deployed in March, 2006, and kept in the “Recife<br />
de Fora” (16°24’S, 038°59’W) for circa seven months. Censuses occurred in October, 2006<br />
(T0), March (T1 – 5 months) and October, 2007 (T2 – 12 months). This experiment started with<br />
1078 live spats. The last census showed 206 live spats, 19% of the original spats. Survival rates<br />
agreed with those from plastic plates. However, differences between tanks (T0-T1 = 48%; T1-<br />
T2 = 34%) and open sea (T0-T1 = 27%; T1-T2 = 5%), as well as in larger spat size classes,<br />
were more evident. Growth rates in tanks were substantially higher than in open sea (up to 7<br />
times higher in the same size class). These preliminary results suggest that rearing coral recruits<br />
in captivity may become an alternative for coral reef restoration in the long term.<br />
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