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"Hotspots" in Fiji

Findings of an Expedition to the Lomaiviti Group

WWWF - SOUTH PACIFIC CURRENTS
October-November 2001 edition

By Sangeeta Mangubhai
PO Box 10135, Bamburi, Mombasa, KENYA
smangubhai@africaonline.co.ke

Fiji holds 3-4% (i.e. 10,020km2) of the world's coral reefs, placing it in the top 10 of the 80 countries and geographical locations with reefs (UNEP-WCMC 2001). While the exact number of coral reefs is currently unknown, it is believed that there are at least one thousand different reefs in Fiji's waters (Zann, 1992). Most authors find it difficult to describe Fiji's coral reefs because of the scattered and very limited scientific data available. However, a number of scientists have recognised Fiji's coral reefs as being of high ecological significance from a biodiversity standpoint (Zann et al. 1997).

The Fiji Government drafted a National Biodiversity Strategy Action Plan (NBSAP) in 1999 to meet Fiji's obligations under the international Convention on Biological Diversity, and demonstrate its commitment to preserving the country's biodiversity. The draft NBSAP specifically provides for the protection of marine biodiversity and has listed a number of sites that are considered of 'national significance'. However, many of these sites listed may represent areas where the reefs are more known or where scientists have chosen to study in the past due to their accessibility, rather than those that are truly important from a national biodiversity perspective. The relevance of sites nominated for Marine Protected Area (MPA) status needs to be re-examined nationally, especially in the aftermath of mass coral bleaching event in the year 2000 (Cumming et al. review).

Coral bleaching is a term used to describe the "whitening" of coral during periods of stress (such as persistent high seawater temperatures), and can lead to decrease survivourship of the coral and death. Coral bleaching has become the primary threat to coral reefs around the world (Wilkinson 2000; Goreau et al. 2000). Fiji experienced its first bleaching event in 2000, during the months February to June, when seawater temperatures remained above the 28.3ºC expected maximum. These elevated temperatures resulted in the bleaching of corals on reefs around Viti Levu and south of Vanua Levu. The state of Fiji's reefs following this bleaching is still not fully described.

While it can be argued that bleaching is a natural response to stress, it has not been witnessed on the spatial scale as we have witnessed within the last 3-4 years. The World Wide Fund for Nature (WWF) has focused its conservation efforts both globally and in the Pacific in promoting the value of biodiversity and the management tools available to address increasing threats to coral reefs. The development of any sort of management regime requires an understanding of the components and functioning of the ecosystem itself, its limitations and its ability to respond to threats such as wide-scale bleaching events.

To support in-country efforts to identify marine areas of high national significance following the 2000 bleaching, WWF coordinated and assisted in undertaking rapid assessment surveys in April 2001, in the poorly studied Lomaiviti Group located east of the main island of Fiji, south of Vanua Levu. The geographical location, size and overall logistics makes access to this island group difficult and costly from a research perspective, requiring an innovative approach, partnering conservation science and dive tourism, to open up access to remote locations. WWF, in collaboration with NAI'A Cruises Fiji (a live-aboard dive operation), undertook a 7-day expedition to collect scientific information on the biodiversity and status of coral reefs in Fiji's Lomaiviti Group.

To obtain as larger a coverage of reefs as possible, rapid assessment techniques were used to record the diversity and health of reef habitats and reef life in the Lomaiviti Group, in the aftermath of the 2000 bleaching event. The information obtained will also allow comparisons with more studied reefs such as the Great and North Astrolabe Reefs in the Kadavu Province, for which recent baseline data was also collected (Obura and Mangubhai, in prep.).

Surveys were conducted on SCUBA at 18 sites located in Eastern Bligh Waters (Vatu-I-Ra Passage), Namena Barrier Reef and waters surrounding Wakaya and Gau Islands. The study found highly diverse and a complex range of reef types including seamounts, bommies, barrier reefs, pinnacles and more typical reefs types, such as patch and channel-edge reefs. Fan and tree-shaped soft corals dominated vertical walls, steep slopes and deeper sites, while carpeting soft coral forms dominated shallower waters. The variety of shapes, textures and colours reflected the richness of soft coral species found in the Lomaiviti group. Unfortunately, the taxonomic complexity and difficulty in identifying soft corals prevented an estimation of the species diversity of this group and hence requires further studies.

Hard corals, in comparison dominated shallow and horizontal surfaces with 127 species recorded during 7 days of diving. This figure is consistent with species numbers in other parts of Fiji. Coral mortality resulting from the 2000-bleaching event was evident by the amount of dead skeletons (0-50%), the high coverage of coralline algae, turf algae and rubble. However, hard corals in this island group appeared to have been more resilient to the 2000 bleaching event relative to other reefs in Fiji, where mortality rates of 60%, and as high as 100%, were recorded. Some bleaching (<10%) was recorded in these 2001 surveys though with low to zero mortality.

According to scientists from the University of the South Pacific, the algae community was taxonomically typical of Fijian reefs with all 46 species previously recorded for Fiji. Mobile invertebrate populations (e.g. sea cucumbers, giant clams and other molluscs, starfish, lobsters) were generally low reflecting the types of habitat available and possibly high rates of predation from healthy fish populations. Sedentary invertebrates such as sponges, ascidians, and bivalves were abundant. Fish populations were generally large and diverse, with abundant schooling plankton-feeding and pelagic fish, indicating low fishing pressure. The presence of a diversity and abundance of fish species is likely to have played an important role in the control of the proliferation of algae following the 2000 bleaching. Sharks and large groupers were generally low, though significant grey reef shark aggregations were observed at two sites. Only four hawksbill turtles were observed during the surveys.

Ten of the 19 sites surveyed during this expedition were identified as being important for one or more of the animal groups that were surveyed. Along with the great range of reef types recorded, this indicates that the region as a whole has a complex assemblage of coral reefs and reef fauna, and that further surveys of this nature, and of more systematic ecological nature, are necessary to adequately sample the diversity of the area.

The findings of this study supports the importance of the reefs of the Lomaiviti group nationally, and the need to develop a conservation and management regime, involving customary resource owners, managers, national decisions makers, the tourism sector and other stakeholders, to ensure the long-term protection of the biodiversity in this region. Of particular significance in the national context, the reefs in the Lomaiviti Group displayed a certain level of resilience to bleaching, are hence is likely to play an important role in providing refugia and reseeding adjacent reefs in Fiji more widely damaged by coral bleaching and global climate change. Key hard coral sites such as those found in the Lomaiviti Group may require some level of conservation management as an "insurance policy" against climate change related degradation such as happened in 2000, and was repeated on a lesser scale in 2001.

While low human population numbers and geographic isolation of the Lomaiviti Group have helped to maintain the ecological integrity of coral reefs in the area, local communities are facing the challenge of adapting to the new forces of development and globalisation, and climatic impacts such as mass coral bleaching. The greatest long-term security for the communities of the Pacific will be achieved through sustainable, adaptive local management.

REFERENCES

Cumming, R.L., Toscana, M.A., Lovell, E.R., Carlson, B.A., Dulvy, N.K., Hughes, A., Koven, J.F., Quinn, N.J., Sykes, H.R., Taylor, O.J.S., and Vaughan, D. (under review) Mass Coral Bleaching in the Fiji Islands, 2000.

Goreau, T., McClanahan, T., Hayes, R. and Strong, A. 2000. Conservation of coral reefs after the 1998 global bleaching event. Conservation Biology, 14, 5-15.

Obura, D.O. and Mangubhai, S. (in prep.) Coral reef biodiversity in the Ono tikina, Kadavu Province, Fiji - Great and North Astrolabe Reefs.

Salm, R., Smith, S. and Llewellyn, G. (2001) Mitigating the impact of coral bleaching through Marine Protected Area design. In Coral Bleaching: Causes, Consequences, and Response. Papers presented at the 9th International Coral Reef Symposium session on "Coral Bleaching: Assessing and Linking Ecological and Socioeconomic Impacts, Future Trends and Mitigation Planning." March 2001. Coastal Management Report #2230. H. Schuttenberg (ed.). Coastal Resources Center, Narragansett, RI. Xx-xx.

UNEP-WCMC. 2001. World Atlas of Coral Reefs. Mark Spalding, C. Ravilious, and E. P. Green (eds.). University of California Press, Berkeley, USA.

Wilkinson, C. 2000. Global Coral Reef Monitoring Network. Australian Insitute of Marine Science,Townsville.

Zann, L.P. 1992. The State of the Fiji's Marine Environment, National Environmental Management Project Report. TA No. 1206. Department of Town and Country Planning, Government of Fiji.

Zann, L.P., Vuki, V.C., Lovell, E., N'Yeurt, A. and Seeto, J. 1997. Biodiversity of Fiji's Marine Environment. Paper presented to the VII Pacific Science Congress, 13-19 July 1997, University of the South Pacific, Suva Fiji.

 

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