11th ICRS Abstract book - Nova Southeastern University
11th ICRS Abstract book - Nova Southeastern University
11th ICRS Abstract book - Nova Southeastern University
You also want an ePaper? Increase the reach of your titles
YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.
24.1051<br />
Mass Culture Of acropora Corals From Eggs And Larvae in The Republic Of<br />
Palau<br />
Makoto OMORI* 1 , Kenji IWAO 1 , Minoru TAMURA 1 , Hiroki TANIGUCHI 1 , Tadashi<br />
KIMURA 2<br />
1 Akajima Marine Science Laboratory, Okinawa, Japan, 2 Japan Wildlife Research Center,<br />
Tokyo, Japan<br />
The restoration techniques of coral reefs have recently draw international attention in<br />
response to the worldwide degradation of coral reefs. In this circumstance, Global<br />
Environmental Facility, the World Bank and others launched international research<br />
program, Coral Reef Targeted Research and Capacity Building for Management. The<br />
Restoration and Remediation Working Group is examining the state of restoration<br />
technique and is targeting investigations to test efficacy of a range of potential<br />
applications. The present research at Palau International Coral Reef Center (PICRC) in<br />
the Republic of Palau is being carried out since April 2006.<br />
We successfully obtained gametes of three Acropora species from neighboring water.<br />
The larvae of three species were cultured respectively, and in total about 168,000 juvenile<br />
corals (polyps) attached on the ceramic substrates. They were cultured in the mid-nursery<br />
cages suspended 3m below sea surface, together with juvenile top-shell, Trochus<br />
niloticus or another indigenous shell to control macroalgal growth on the substrates and<br />
cages. Only 1,240 colonies were remained after l year. The average diameter of A. tenuis<br />
was 2.0 cm (largest 6.8 cm). This significantly high mortality was due to miss selection<br />
of the site of mid-nursery where was suffered by heavy sedimentation. In April 2007,<br />
when a second mass culture was conducted at PICRC, we moved the mid-nursery site to<br />
offshore where transparency is much better than the previous one. The cost to produce<br />
one colony after one-year culture was US$20.6 in 2007, but we expect that it will be<br />
lowered considerably in 2008, as survival rate of the colonies seem to be better than the<br />
previous year.<br />
24.1052<br />
Coral Habitat Expansion Project Around Okinotorishima Island, Japan<br />
Wataru ANDO* 1 , Kouji WATANABE 1 , Ryota NAKAMURA 2 , Noboru ISHIOKA 1 ,<br />
Nobuo MIKAMI 3 , Akito SATO 4<br />
1 Fisheries Infrastructure Development Center, Chuoo-ku, Japan, 2 Fisheries Infrastructure<br />
Development Center, Zamami Village, Japan, 3 National Research Institute of Fisheries<br />
Engineering, Kamisu City, Japan, 4 Fishery Agency, Minister of Agriculture, Forestry and<br />
Fisheries of Japan, Chiyoda-ku, Japan<br />
Okinotorishima Island is a southernmost island of Japanese territory, approximately<br />
1,740 kilometers south-southwest from Tokyo. The island consists of coral lagoon, eastwest<br />
4km and north-south 1.7km. Around the island, coral reef is the main ecological<br />
community. However, there are only a few area with high coral cover degree. Therefore,<br />
Fisheries Agency of Japan started the Coral Habitat Expansion Project around the island<br />
from 2005. This project aims developing methods to maintenance and increase of coral<br />
ecosystem around the island. We have investigated the coral growing condition and<br />
natural environment around the island and we have carried out to develop seed<br />
production and propagation techniques.<br />
Until now, we have almost clarified dominant species of coral, distribution area and<br />
spawning period aloud the island. In addition, we succeeded to let the coral spawning in<br />
the water tanks on the ship and larval settlement on substrate tiles. We have been<br />
breeding the juvenile corals in the water tank of land institution (Akajima Coral Hatchery<br />
Center in Okinawa: ACHC). Moreover, we were able to perform the long-distance<br />
transportation of relatively large coral colonies from Okinotorishima to ACHT for more<br />
than 50 hours. These coral colonies spawned in the tank in 2007 early summer, and we<br />
have been breeding them in the tank. We have about 10 million Acropora juvenile corals<br />
at the end of 2007 in the water tanks of ACHC.<br />
We will report the development of coral reef restoration technologies in Okinotorishima<br />
Island.<br />
Poster Mini-Symposium 24: Reef Restoration<br />
24.1053<br />
Seed Production of Acropora Corals of Okinotorishima, Southernmost Island of Japan<br />
Ryota NAKAMURA 1 , Akira WATANUKI* 2 , Toru AOTA 3 , Michio KITANO 4 , Takayasu<br />
FUJITA 1<br />
1 Fisheries Infrastructure Development Center, Tokyo, Japan, 2 Alpha Hydraulic Engineering<br />
Consultants Co., Ltd., Tokyo, Japan, 3 Fudo Tetra Corporation, Ibaraki, Japan, 4 ECOH<br />
Corporation, Tokyo, Japan<br />
The Fisheries Agency of Japan has researched and studied corals of Okinotorishima Island to<br />
develop those propagation techniques since 2006. As a part of the research project, studies on<br />
coral seed production are carried out at Akajima Coral Hatchery in Okinawa. Target species are<br />
Acropora tenuis, A. globiceps? and A. sp. Broodstock were collected at Okinotorishima in<br />
August, 2006 and May, 2007, and placed in tanks with running seawater at the hatchery for<br />
long-term rearing. In 2007, spontaneous spawning events were observed in June for A. tenuis<br />
and July and August for A. globiceps? and A. sp. Peaks of the spawning occurred during waning<br />
moon periods. Seed production trials were carried out with a part of the eggs spawned. The eggs<br />
and larvae were kept in still seawater tanks, changing 3/4 of the water daily. After settlement,<br />
juveniles were transferred to running seawater tanks. The numbers and rates of larvae settled on<br />
substrates in A. tenuis, A. globiceps? and A. sp. were ca. 110,000 and 54.1%, ca. 660 and 1.9%,<br />
and ca. 1,700 and 2.3%, and the survival rates and mean longest diameter of the juveniles of<br />
each species at 3 months after spawning were 87% and 3.4mm, 94% and 2.8mm, and 97% and<br />
3.5mm respectively. Meanwhile, the larval settlement rates were 0.9% in A. globiceps? and<br />
1.7% in A. sp. in an experiment with eggs spawned by wild broodstock on a research vessel at<br />
Okinotorishima in July, 2007. The low settlement rates of these two species seem to result from<br />
some nature of the species. It may be necessary to develop mass seed production methods being<br />
suitable for each species.<br />
24.1054<br />
Plug your Reef, Recovery of Porites after extraction of cores<br />
Eric MATSON* 1<br />
1 Australian Institute of Marine Science, Townsville, Australia<br />
Long-lived, annually-banded massive corals, e.g. Porites, provide both valuable histories of<br />
climatic and environmental conditions on coral reefs and coral growth responses to changes in<br />
these conditions. To retrieve these records requires mechanical extraction of cores from large,<br />
healthy coral bommies. Cores are cut by forcing a rotating cutting head vertically down into the<br />
colony. Cores are typically ~50-70 mm in diameter and the holes left in the colony are<br />
commonly plugged using tapered concrete cylinders.<br />
The living coral tissue layer occupies only the outer ~1cm of the coral with unoccupied, dead<br />
skeleton below. Anecdotal reports suggest that the living tissue layer recolonises the surface of<br />
the concrete plug rapidly and the coral suffers no long-term damage as a consequence of core<br />
extraction.<br />
The impact of and recovery from coring was assessed in eight Porites bommies from the<br />
Whitsunday Islands, Great Barrier Reef, Australia. Eight recently cored corals were tracked<br />
over 30 months and each colony photographed at ~ 6-month intervals with the images including<br />
the 50mm diameter core hole, the concrete plug and the area around the plug.<br />
Within the first 6 months all colonies had begun to recover with living tissue extending over<br />
part of the surface of the concrete plug and by 30 months two colonies had fully recovered. The<br />
plug from one colony became dislodged after ~ 6 months providing a control hole which<br />
showed little or no recovery after 30 months.<br />
The results of this study demonstrate the importance of plugging holes after coral core<br />
extraction to ensure the ongoing health of the coral colony. The study also demonstrates that<br />
full recovery of corals from core extraction may take years rather than months.<br />
526