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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24-37<br />
Restoration Of acropora Cervicornis At The Site Of The M/t Margara Grounding<br />
Tom MOORE* 1 , Bruce GRAHAM* 2 , Sean GRIFFIN* 3 , Kevin KIRSCH 4 , Craig<br />
LILYESTROM 5 , Michael NEMETH* 6<br />
1 Restoration Center, NOAA, St. Petersburg, FL, 2 CSA International, Stuart, FL,<br />
3 Lighthouse Technical Consultants, Aquadilla, Puerto Rico, 4 NOAA, St. Petersburg, FL,<br />
5 Puerto Rico DNER, San Juan, Puerto Rico, 6 Lighthouse Technical Consultants,<br />
Boqueron, Puerto Rico<br />
The M/T MARGARA, a 228-m (748-ft) tanker went aground on coral reef formation on<br />
27 April 2006. The impacted reef is located approximately 1 mile south-southeast of<br />
Bahia de Tallaboa along the south coast of Puerto Rico. The coral reef feature supports a<br />
relatively healthy epifaunal assemblage visually dominated by soft corals, sponges, and<br />
hard corals. Rapid response by PRDNER, NOAA and the Responsible Party resulted in<br />
the salvage and reattachment of over 10,000 hard and soft corals displaced during the<br />
grounding.<br />
A unique feature of the grounding location was the presence of a large thicket of<br />
Acropora cervicornis which has been designated as Threatened under the Endangered<br />
Species Act of 1972. Impact to the A. cervcornis thicket produced over 900 fragments<br />
ranging in size from 7.7 to 23 cm (3 to 9in) that were available for reattachment.<br />
The A. cervicornis restoration strategy utilized various techniques at four distinct<br />
locations within the grounding site. Techniques included the reattachment of grouped A.<br />
cervicornis fragments to 1) stainless-steel bolts projecting from pooled cement, 2) natural<br />
coral rubble projecting from pooled cement, and 3) secured frame of plastic-coated wire<br />
mesh. In all three reattachment techniques, fragments were secured using plastic cable<br />
ties. Additionally, fragments were attached directly in cement and secured with epoxy at<br />
some locations.<br />
Over the first year the reattached fragments grew vigorously, formed multiple new<br />
branches and generally had a high rate of survival. Branching fragments could be<br />
utilized for transplantation within the grounding site and/or as a source of fragments for<br />
additional reattachment locations. This talk will discuss initial results and lessons learned<br />
concerning these new field-tested techniques for restoring A. cervicornis resources.<br />
24-38<br />
Survival Of Coral Recruits in Relation To Substrate Stability Within Ship<br />
Grounding Sites.<br />
Stuart FIELD* 1<br />
1 <strong>University</strong> of Notre Dame, Perth, Australia<br />
Ship groundings cause discrete, small scale disturbances with defined boundaries and are<br />
characterised by a mosaic of disturbed areas varying in the extent of damage and the<br />
stability of the remaining substrate. Following a disturbance resulting from a ship<br />
grounding event, recovery of the coral community is dependent on the recruitment of new<br />
individuals to the denuded substrate created as a result of the disturbance. In this study<br />
juvenile corals were investigated for 24 months at four sites associated with ship<br />
grounding sites adjacent to the Straits of Tiran, Egypt. The density of juveniles within<br />
and adjacent to areas of disturbance were considered along with the diversity and size<br />
distribution of the juvenile coral community at each site. This investigation has enabled a<br />
greater understanding of early life history processes in the recovery of disturbed reefs.<br />
Increased densities of juvenile corals were recorded in disturbed areas, supporting<br />
findings of recruitment to artificial settlement tiles, however, there were also higher rates<br />
of juvenile mortality in disturbed areas, particularly in areas with mobile rubble,<br />
indicating that smothering and abrasion were likely causes of decreased survivorship in<br />
these areas. However, these rates of recruitment and survivorship were variable across the<br />
four sites investigated. These results suggest that while we can improve predictions of<br />
recovery rates by defining the mosaic of substrate classifications that characterise a ship<br />
grounding site, site-to-site variability in settlement and post-settlement mortality prevents<br />
predictions based solely on these initial site surveys and long-term monitoring is needed<br />
at each site to follow recovery over time.<br />
Oral Mini-Symposium 24: Reef Restoration<br />
24-39<br />
Natural Resource Damage Assessment And Restoration in The National Park Service:<br />
Coral Reef Vessel Grounding Case Studies in Biscayne National Park<br />
Amanda BOURQUE* 1<br />
1 Division of Resource Management, Biscayne National Park, Homestead, FL<br />
Natural Resource Damage Assessment (NRDA) is a process that allows authorized resource<br />
trustees to identify injured resources, recover damages from responsible parties, restore habitats<br />
and resources to pre-injury/exposure conditions (“primary restoration”), and compensate the<br />
public for the loss of ecological and/or visitor use services (“compensatory restoration”). The<br />
National Park Service is authorized by several statutes to implement the NRDA process in<br />
resource injury cases. Biscayne National Park (BISC) pursues damage recovery in vessel<br />
grounding cases under the authority of the Park System Resource Protection Act (PSRPA, 16<br />
USC 19jj). BISC is one of the largest marine parks in the National Park System, and protects<br />
the northernmost Florida Keys, seagrass meadows, mangrove forests, clear bay waters, and over<br />
twenty miles of the Florida reef tract. Submerged park resources holding significant ecological,<br />
cultural, and economic value are frequently impacted by vessel groundings. BISC is unique<br />
because it has the highest volume PSRPA cases in the National Park System, and these cases<br />
arise from one type of resource injury (i.e. vessel groundings). This presentation will provide<br />
an overview of how BISC applies the NRDA process in vessel grounding cases, with an<br />
emphasis on those cases that involve coral reef resources. Injury assessment techniques, injury<br />
classifications, restoration planning approaches, restoration alternatives for primary and<br />
compensatory projects, monitoring protocols, environmental compliance, and policy solutions<br />
will be discussed. Examples will be drawn from several BISC cases.<br />
24-40<br />
Coral Reef Metrics And Habitat Equivalency Analysis<br />
Shay VIEHMAN* 1 , Steven THUR 2 , Greg PINIAK 1<br />
1 Center for Coastal Fisheries and Habitat Research, NOAA, Beaufort, NC, 2 Office of Ocean and<br />
Coastal Resource Management, NOAA, Silver Spring, MD<br />
When coral reefs held in United States public trust are injured by anthropogenic injuries such as<br />
vessel groundings or oil spills, a natural resource damage assessment process is utilized to<br />
quantify the resource loss and determine the amount of restoration required to make the public<br />
whole from the injury. Habitat equivalency analysis (HEA) is used to equate resource losses<br />
from the injury with benefits from the compensatory project. Ecosystem services are<br />
represented in HEA using an indicator metric, typically coral cover for reef injuries. However,<br />
depending on the injury and habitat, alternative approaches such as composite metrics<br />
incorporating topographic complexity and other coral reef community members, or a resourcescale<br />
approach utilizing size-frequency distributions may more comprehensively represent lost<br />
services. We examine the robustness, flexibility, and application within HEA of these metrics<br />
to predict complex and compound (larger scale) results from the original injury. Careful<br />
selection of a metric appropriate to both the degree and extent of injury and of habitat type can<br />
serve as a vital link between the damage assessment, recovery modeling, compensatory<br />
calculations, and recovery monitoring.<br />
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