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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24.1092<br />
Lessons Learned On Demonstration Sites For Coral Reef Restoration in Thailand<br />
Thamasak YEEMIN* 1 , Makamas SUTTHACHEEP 1 , Nipat SOMKLEEB 1 , Chaiyaporn<br />
LOCHAYA 1 , Nisit RUENGSAWANG 2<br />
1 Department of Biology, Faculty Of Science, Ramkhamhaeng <strong>University</strong>, Bangkok,<br />
Thailand, 2 Biology, Rajamangkala <strong>University</strong> of Technology Krungthep, Bangkok,<br />
Thailand<br />
There are numerous documentations of coral reef restoration methods in the last decade.<br />
The objective of this paper is to provide lessons learned on demonstration sites for coral<br />
reef restoration in Krabi Province, the Andaman Sea and Mu Koh Chang, the Gulf of<br />
Thailand. The demonstration sites for coral reef restoration were carried out in limited<br />
demonstration areas where they can be easily controlled and managed for the benefit of<br />
ecotourism, education, raising public awareness, ecosystem restoration and research.<br />
Local communities, government agencies, private sector and NGOs have participated<br />
actively in the planning and implementation processes for their direct and indirect<br />
benefits from the projects. Natural coral fragments were used in order to increase the<br />
survival of natural coral fragments that might otherwise have had low survival because<br />
they were susceptible to being buried. Several coral reef restoration methods showed at<br />
the demonstration sites such as; i) additional substrates for coral recruitment by using<br />
clusters of cylindrical concretes lay in a triangle model; ii) attaching branching Acropora<br />
spp. with screws to designed PVC pipe frames in the coral nursery area; iii) additional<br />
substrates for coral recruitment and attaching coral fragments by using clusters of<br />
concrete blocks fused in horizontal and vertical directions; and iv) attaching branching<br />
fragments to dead branching corals by means of plastic straps. We suggest that<br />
government agencies, tourism businessmen and local communities encourage and<br />
strengthen collaborative management of the demonstration sites for coral reef restoration<br />
in order to develop key features of long-term successful management systems.<br />
24.1093<br />
Rehabilitation Reef Habitat With Coral Transplantation To Increase Resilience Of<br />
Reef Habitat And Community Economic<br />
Hery YUSAMANDRA 1 , Hery YUSAMANDRA* 1 , Hery YUSAMANDRA 2<br />
1 -, Reef Check Indonesia Foundation, Denpasar, Indonesia, 2 -, Hayati Lestari Foundation,<br />
Padang, Indonesia<br />
The activity to rehabilitate coral reef have been done in Sungai Pisang village on West<br />
Sumatera Province since 2005. Location selected are coral reef habitat which has damage<br />
after mass bleaching event in 1997 and destroyed area as consequence of destructive<br />
fishing activity using cyanide and bomb by fisherman around there. Objective of this<br />
activity are to rehabilitate reef habitat which has damage by coral transplantation and<br />
increasing public awareness by creating artificial reef garden with local community in<br />
Sungai Pisang village. Method used is by farming the fragment coral on “small-ball”<br />
concrect substrat. Corals fragment is glued to substrate by using special glue from cement<br />
powder. After one month that substrat planting to the three type of permanent substrat<br />
are build from concrect artificial reef, iron plate and coral rubble. Corals species that<br />
collected based on dominant species around location are Acropora spp., Millepora sp.,<br />
Pocillopora spp., Euphyllia glabrescent, Galaxea fasciata and Seriatopora sp. The<br />
artificial reef building and corals cultivation rack had been laying down in two depths<br />
that are 6-9 meters and 10-12 meters. Based on the research shown that growth of coral in<br />
depth 6-9 meters better than 10-12 meters. Life survival rate of coral fragment in depth 6-<br />
9 meters equal to 80.5% while in depth 10-12 meters equal to 65%. Expected, in the<br />
future this technique can be replicate to another area that suitable as coral rehabilitation<br />
site because this technique are not expensive and easy to apply by community. In the<br />
long term it can help increase diversity of the reef habitat become more resilience and<br />
also increase resilience of community economics with alternative livelihood by<br />
ecotourism activity.<br />
Poster Mini-Symposium 24: Reef Restoration<br />
24.1094<br />
Reef Restoration at Laughing Bird Caye National Park, Belize, Central America<br />
Lisa CARNE* 1<br />
1 Independent, Placencia, Belize<br />
Laughing Bird Caye National Park (LBCNP) has been re-seeded with 20 Elkhorn coral<br />
(Acropora palmata) fragments transplanted from naturally recurring stands in Gladden Spit and<br />
the Silk Cayes Marine Reserve (GSSCMR). Elkhorn coral was prevalent at LBCNP until<br />
1997/98. LBCNP is a World Heritage Site located approximately 12 miles east of Placencia, in<br />
Southern Belize, Central America. GSSCMR is an additional 10 miles to the east, on the outer<br />
barrier reef. All fragments demonstrated new tissue growth within 2-4 weeks of placement;<br />
many have already grown onto their new substrate. This methodology establishes a restorative<br />
technique for decimated A. palmata populations in Belize, and can be utilized in response to<br />
future hurricane events, ship groundings and/or anchor damage. It is estimated that this coral’s<br />
abundance has been reduced by 98% Caribbean-wide, in the last three decades. All of the<br />
Acroporid spp. found in the Caribbean were recently listed as “Threatened” under the<br />
Endangered Species Act in the US.<br />
Elkhorn coral is known to be fast growing (5-6 inches per year) in ideal conditions. Elkhorn<br />
coral is structurally important, providing protection to fragile cayes during storms, allows reef<br />
growth to keep pace with changing sea levels and provides essential habitat for over 100’s<br />
species of fish and invertebrates, including the commercially important spiny lobster, Panulirus<br />
argus. No other Caribbean reef building coral species are able to fulfill these essential<br />
ecosystem functions. Mapping has begun for this species in Southern Belize and should be<br />
continued nationwide, to establish sources of A. palmata transplants in the event of future<br />
hurricanes or ship groundings.<br />
The potential long-term conservation and economic benefits are enormous as both the tourism<br />
and fishing industry rely on the health of Belize’s marine eco-system.<br />
24.1095<br />
Characteristics Of Seagrass Beds in Coral Reef Area And Their Restoration<br />
Takahiko INOUE* 1 , Sayuko NINOMIYA 1 , Takashi MASUMOTO 1 , Yoshikatsu NAKANO 2 ,<br />
Makoto TSUCHIYA 2<br />
1 TOKYO KYUEI CO., Ltd, Kawaguchi, Japan, 2 <strong>University</strong> of the Ryukyus, JAPAN, Nishihara,<br />
Japan<br />
In Okinawa, southern Japan, well-developed coral reefs are extending, and seagrass beds<br />
composed of several seagrass species are distributed in moats. Seagrass beds are known to have<br />
important roles as the spawning and/or nursery grounds of marine fishes and invertebrates and<br />
as the feeding field of dugongs. Nevertheless, the areas of seagrass beds are reducing due to<br />
shore protection works and reclamation. Recently, the restoration of seagrass beds is being<br />
attempted. The distribution of such seagrass beds associated with coral reefs are not restricted<br />
in Okinawan waters but are widely distributed in other tropical and sub-tropical regions in the<br />
world, and therefore, techniques for the protection and/or cultivation of seagrass beds are<br />
strongly desired for their ecological importance. We have been observing seagrass beds in<br />
Okinawa. It was found that although a seagrass bed was macroscopically formed as the mixture<br />
of several coexisting species, the distributions of different species segregated according to their<br />
ecological preference on current environment and substrate type. Two component species of a<br />
seagrass bed, Cymodocea serrulata and Halodule uninervis, developed their rhizomes only near<br />
the surface of the sea bottom, and thus they could entirely be swept away by flushing currents<br />
generated by a strong typhoon. On the other hand, Thalassia hemprichii, that extends its<br />
rhizome deep into the sea bottom to settle, might not easily be swept by such strong currents.<br />
The species could form more stable meadows in areas where substrate contained large coral<br />
gravel in high proportion. T. hemprichii also formed a stable meadow in a combined<br />
community with live Montipora digitata. Based on the above findings, we introduce effective<br />
techniques, including some prospects, for seagrass bed restoration suitable to the ecological<br />
characteristics of each species.<br />
536