11th ICRS Abstract book - Nova Southeastern University

11th ICRS Abstract book - Nova Southeastern University 11th ICRS Abstract book - Nova Southeastern University

24.12.2012 Views

24.1112 Coral Recruitment On Reef Ball Structures At The Benete Bay, Sumbawa Island, Indonesia Imam BACHTIAR* 1 , Windy PRAYOGO 2 1 Biology Education, Universitas Mataram, Mataram, Indonesia, 2 Environment, PT Newmont Nusa Tenggara, Mataram, Indonesia Reef ball structure is a popular artificial reef that has been invested in many countries. Publication on its efficacy in promoting coral recruitment however remains lack of study or publication. This present study is aimed to examine the pattern of coral recruitment on reef ball structure at the Benete Bay of Sumbawa Island, Indonesia. Thirty big size reefballs were censuses after three years of deployment. All of these structures were deployed on a sandy bottom location in a sheltered bay. The results show that nearly all coral colonies grow on the vertical surface and upper side of the reef balls. Recruit number varies among depths, between 1-69 colonies per unit reef balls. Most recruits are belonging to the Family Acroporidae, which contribute about 76% to the whole recruitment. Branching acroporid is the most abundant colonies (55%). Pocilloporidae and Faviidae both contribute about 9% to the total recruitment, while Poritidae contributes about 3%. Other coral families only has

24.1116 A Newly Established Coral Reef Ecosystem At The Northern Tip Of The Gulf Of Aqaba -Jordan Salim AL-MOGHRABI* 1 , Khaled SOKHNY 2 1 Aqaba Special Economic Zone Authority, Aqaba, Jordan, 2 Environmental Center for Arab Towns, Dubai, United Arab Emirates The coastal area of Jordan extends over 27Km at the northeastern tip of the Gulf of Aqaba, where fascinating coral reefs of the fringing type thrive and flourish as the most northern latitudinal limit of reefs distribution, worldwide. Jordan's northern-most third tip of the Gulf is characterized by featureless sandy seabed. This very limited coast is Jordan’s only maritime access and it is currently home to many users adding to the natural stress exerted over corals. The Regional Organization for the Conservation of the Environment of the Red Sea and Gulf of Aden (PERSGA) and the Aqaba Special Economic Zone Authority (ASEZA) funded the establishment of an artificial reef in August 2004. It is composed of two hundred blocks, ranging in height from 1-4m, caste according to 12 different design structures and deployed over 40000m2 of the sandy area from 9-22 m depth. Two days after blocks deployment fish started laying their eggs over the blocks. Two soft corals (Anthelia glauca and Xenia umbellata) colonized the structures less than two months after deployment, while it took the hard coral larvae about a year before they were first noticed. Underwater cleanup dives were realized along the coastal area and orphan coral colonies growing over the garbage were collected, fixed to PVC substrate and buoyant weight. The adopted coral saplings were transplanted to the artificial reef site and fixed over the blocks. The artificial reef provided a proper foraging ground, a safe shelter and an appropriate spawning place. Nowadays, hundreds of fish, soft and hard corals, and other species inhabit the artificial reef structures creating a new coral reef ecosystem at the northern tip of the Gulf of Aqaba. 24.1117 The Coral Trays, a Simple Method to Create Large Sustainable Artificial Reefs Thomas LE BERRE* 1 , Cedric GUIGNARD 1 1 Seamarc Pvt. Ltd., Male', Maldives Transplantation has been widely used to artificially propagate corals. A simple, cost effective technique, the coral trays, is used to propagate the corals rescued from coastal development areas. The present technique, based on very workable protected metallic rebars is very versatile. It has been successful in relatively large scale experiments (>500 m2) in a shallow sandy reef flat on the exposed and lee side of the island of Landaa Giraavaru for recreational activities and aesthetics. The success of the technique is mostly owed to a good water flow and decreased effects of sedimentation. The height from the sea bed makes abrasion less than for other types of structures. The structure also enables relatively high densities of transplants decreasing the predation pressure. Ease of deployment and rapidity of transplanting are enabling operational advantages. Applications of such sustainable artificial reefs further needs to be developed and the monitoring process is an integral part of the reef development as the initial stock is used to always develop new structures from “cultured” fragments. Self sustainability is achieved after a short time. The process already involves local communities and could provide alternative livelihoods in the rural parts of the Maldives. Compared with the sandy reef flat nearby, they are the location of high fish biodiversity and abundance, providing shelter to large array of fish life from pipefish and blennies to snappers and angelfishes. Prospective development of large reefs are similar to those include sediment creation and erosion control. It would favorably replace dead coral rock structures in wide use, increasing biodiversity and overall resilience of the system, and be used for the restoration of damaged or dredged areas. Poster Mini-Symposium 24: Reef Restoration 24.1118 Reef Ball Pilot Project in Hastings, Barbados Andre MILLER* 1 , David GILL 1 , James BLADES 1 1 Barbados Marine Trust, St. Michael, Barbados Reef Balls are artificial reef structures designed to create new or enhance existing reef habitats. They consist of a long-lasting marine concrete mix which allows for growth of benthic biota such as corals and a suitable habitat for fish. Previous observations suggest that they can also serve as fish recruiting devices, but much debate exists as to whether an increased presence of fish at reef ball locations is a result of direct recruitment or population redistribution (i.e. aggregation vs. production). The Barbados Marine Trust in 2004 deployed 30 Reef Balls off the South Coast of Barbados in a sandy channel located between two patch reefs. The pilot project sought to determine the propriety of reef balls for Barbados’ reefs, and to ascertain its effect on fish abundance, distribution and diversity at the test site and its reef environs. The Bohnsack and Bannerot Fish Census Method (1986) was employed which involves a survey of all fish observed within a water column 15m in diameter over a ten (10) minute period. This was executed several times over an 18-month period. Three neighbouring control sites (two reef sites, one sand site) were designated to be compared and contrasted against the experimental reef ball site. The overall observation findings indicate that the placement of the artificial reef structures into the barren location has resulted in an increase in both the abundance and diversity of fish within the same location – initially due to redistribution, but subsequently from direct recruitment. The reefs balls have also demonstrated marked stability in unstable water conditions (after the passage of Hurricane Ivan), proving that they can maintain high structural integrity in such conditions and thus can be used as shoreline defense mechanisms or for reef rejuvenation in high energy environs. 24.1119 Benthic Colonization And Ecological Successional Patterns On A Planned Nearshore Artificial Reef (Ar) System in Broward County, Se Florida Adrienne CARTER* 1 , Stacy PREKEL 1 1 Marine Science & Biological Research, Coastal Planning & Engineering, Inc., Boca Raton, FL Nearshore marginal reefs are frequently impacted from beach restoration activities. Beach nourishment, in particular, can impact nearshore hardbottom through burial and subsequent habitat degradation. In response to increased beach nourishment activities, reef restoration projects have increased immensely over the last decade. In Southeast Florida, the deployment of artificial reefs (ARs) as mitigation for nearshore habitat loss has become routine. To determine the success of ARs as appropriate nearshore habitat replacement, long-term AR colonization studies are essential to evaluate ecological processes and succession rates in shallow marine environments. This paper reports on a four-year study of the development, seasonal recruitment and ecological succession rates of macrobenthic communities on a mitigative AR system located in Broward County, Florida. Pioneering organisms and community composition were evaluated via the Coastal Planning & Engineering, Inc. Benthic Environmental Assessment for Marginal Reef (BEAMR) method. Benthic communities were sampled at 9-, 12-, 18-, 24-, 36- and 48-month post-construction. By use of multivariate analyses both spatial and temporal fluctuations of colonizing organisms were assessed, as well successional stages of contemporary organisms. Preliminary results indicate a typical colonization pattern in which biotic cover and diversity increased on the AR system progressively from 9 to 48 months postconstruction. Results also indicate that equilibrium was not attained by functional groups due to frequent physical disturbances. 542

24.1116<br />

A Newly Established Coral Reef Ecosystem At The Northern Tip Of The Gulf Of<br />

Aqaba -Jordan<br />

Salim AL-MOGHRABI* 1 , Khaled SOKHNY 2<br />

1 Aqaba Special Economic Zone Authority, Aqaba, Jordan, 2 Environmental Center for<br />

Arab Towns, Dubai, United Arab Emirates<br />

The coastal area of Jordan extends over 27Km at the northeastern tip of the Gulf of<br />

Aqaba, where fascinating coral reefs of the fringing type thrive and flourish as the most<br />

northern latitudinal limit of reefs distribution, worldwide. Jordan's northern-most third tip<br />

of the Gulf is characterized by featureless sandy seabed. This very limited coast is<br />

Jordan’s only maritime access and it is currently home to many users adding to the<br />

natural stress exerted over corals.<br />

The Regional Organization for the Conservation of the Environment of the Red Sea and<br />

Gulf of Aden (PERSGA) and the Aqaba Special Economic Zone Authority (ASEZA)<br />

funded the establishment of an artificial reef in August 2004. It is composed of two<br />

hundred blocks, ranging in height from 1-4m, caste according to 12 different design<br />

structures and deployed over 40000m2 of the sandy area from 9-22 m depth. Two days<br />

after blocks deployment fish started laying their eggs over the blocks. Two soft corals<br />

(Anthelia glauca and Xenia umbellata) colonized the structures less than two months after<br />

deployment, while it took the hard coral larvae about a year before they were first<br />

noticed. Underwater cleanup dives were realized along the coastal area and orphan coral<br />

colonies growing over the garbage were collected, fixed to PVC substrate and buoyant<br />

weight. The adopted coral saplings were transplanted to the artificial reef site and fixed<br />

over the blocks. The artificial reef provided a proper foraging ground, a safe shelter and<br />

an appropriate spawning place. Nowadays, hundreds of fish, soft and hard corals, and<br />

other species inhabit the artificial reef structures creating a new coral reef ecosystem at<br />

the northern tip of the Gulf of Aqaba.<br />

24.1117<br />

The Coral Trays, a Simple Method to Create Large Sustainable Artificial Reefs<br />

Thomas LE BERRE* 1 , Cedric GUIGNARD 1<br />

1 Seamarc Pvt. Ltd., Male', Maldives<br />

Transplantation has been widely used to artificially propagate corals. A simple, cost<br />

effective technique, the coral trays, is used to propagate the corals rescued from coastal<br />

development areas. The present technique, based on very workable protected metallic<br />

rebars is very versatile. It has been successful in relatively large scale experiments (>500<br />

m2) in a shallow sandy reef flat on the exposed and lee side of the island of Landaa<br />

Giraavaru for recreational activities and aesthetics. The success of the technique is mostly<br />

owed to a good water flow and decreased effects of sedimentation. The height from the<br />

sea bed makes abrasion less than for other types of structures. The structure also enables<br />

relatively high densities of transplants decreasing the predation pressure. Ease of<br />

deployment and rapidity of transplanting are enabling operational advantages.<br />

Applications of such sustainable artificial reefs further needs to be developed and the<br />

monitoring process is an integral part of the reef development as the initial stock is used<br />

to always develop new structures from “cultured” fragments. Self sustainability is<br />

achieved after a short time. The process already involves local communities and could<br />

provide alternative livelihoods in the rural parts of the Maldives.<br />

Compared with the sandy reef flat nearby, they are the location of high fish biodiversity<br />

and abundance, providing shelter to large array of fish life from pipefish and blennies to<br />

snappers and angelfishes. Prospective development of large reefs are similar to those<br />

include sediment creation and erosion control. It would favorably replace dead coral rock<br />

structures in wide use, increasing biodiversity and overall resilience of the system, and be<br />

used for the restoration of damaged or dredged areas.<br />

Poster Mini-Symposium 24: Reef Restoration<br />

24.1118<br />

Reef Ball Pilot Project in Hastings, Barbados<br />

Andre MILLER* 1 , David GILL 1 , James BLADES 1<br />

1 Barbados Marine Trust, St. Michael, Barbados<br />

Reef Balls are artificial reef structures designed to create new or enhance existing reef habitats.<br />

They consist of a long-lasting marine concrete mix which allows for growth of benthic biota<br />

such as corals and a suitable habitat for fish.<br />

Previous observations suggest that they can also serve as fish recruiting devices, but much<br />

debate exists as to whether an increased presence of fish at reef ball locations is a result of<br />

direct recruitment or population redistribution (i.e. aggregation vs. production).<br />

The Barbados Marine Trust in 2004 deployed 30 Reef Balls off the South Coast of Barbados in<br />

a sandy channel located between two patch reefs. The pilot project sought to determine the<br />

propriety of reef balls for Barbados’ reefs, and to ascertain its effect on fish abundance,<br />

distribution and diversity at the test site and its reef environs.<br />

The Bohnsack and Bannerot Fish Census Method (1986) was employed which involves a<br />

survey of all fish observed within a water column 15m in diameter over a ten (10) minute<br />

period. This was executed several times over an 18-month period. Three neighbouring control<br />

sites (two reef sites, one sand site) were designated to be compared and contrasted against the<br />

experimental reef ball site.<br />

The overall observation findings indicate that the placement of the artificial reef structures into<br />

the barren location has resulted in an increase in both the abundance and diversity of fish within<br />

the same location – initially due to redistribution, but subsequently from direct recruitment. The<br />

reefs balls have also demonstrated marked stability in unstable water conditions (after the<br />

passage of Hurricane Ivan), proving that they can maintain high structural integrity in such<br />

conditions and thus can be used as shoreline defense mechanisms or for reef rejuvenation in<br />

high energy environs.<br />

24.1119<br />

Benthic Colonization And Ecological Successional Patterns On A Planned Nearshore<br />

Artificial Reef (Ar) System in Broward County, Se Florida<br />

Adrienne CARTER* 1 , Stacy PREKEL 1<br />

1 Marine Science & Biological Research, Coastal Planning & Engineering, Inc., Boca Raton, FL<br />

Nearshore marginal reefs are frequently impacted from beach restoration activities. Beach<br />

nourishment, in particular, can impact nearshore hardbottom through burial and subsequent<br />

habitat degradation. In response to increased beach nourishment activities, reef restoration<br />

projects have increased immensely over the last decade. In Southeast Florida, the deployment of<br />

artificial reefs (ARs) as mitigation for nearshore habitat loss has become routine. To determine<br />

the success of ARs as appropriate nearshore habitat replacement, long-term AR colonization<br />

studies are essential to evaluate ecological processes and succession rates in shallow marine<br />

environments. This paper reports on a four-year study of the development, seasonal recruitment<br />

and ecological succession rates of macrobenthic communities on a mitigative AR system<br />

located in Broward County, Florida. Pioneering organisms and community composition were<br />

evaluated via the Coastal Planning & Engineering, Inc. Benthic Environmental Assessment for<br />

Marginal Reef (BEAMR) method. Benthic communities were sampled at 9-, 12-, 18-, 24-, 36-<br />

and 48-month post-construction. By use of multivariate analyses both spatial and temporal<br />

fluctuations of colonizing organisms were assessed, as well successional stages of<br />

contemporary organisms. Preliminary results indicate a typical colonization pattern in which<br />

biotic cover and diversity increased on the AR system progressively from 9 to 48 months postconstruction.<br />

Results also indicate that equilibrium was not attained by functional groups due<br />

to frequent physical disturbances.<br />

542

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