SITE INFORMATION Site Description FIJI: Fiji lies in the heart of the Pacific Ocean midway between the Equator and the South Pole and between longitudes 1740 East and 1780 West of Greenwich and latitudes 12 o S and 22o South. 'Fiji's Exclusive Economic Zone contains approximately 330 islands of which about a - third are inhabited. This covers about a 1.3 million sq.km of the South Pacific Ocean. Fiji's total Land area is 18,333 sq.km. There are two major islands - Viti Levu which is 10,429 sq.km and Vanua Levu 5,556 sq.km. Other main islands are Taveuni 470 sq.km, Kadavu 411 sq.km, Gau 140 sq.km, Koro 140 sq.km. Indigenous Fijians own 87.9% of the land while 3.9% is State Land. Freehold land comprises of 7.9% and Rotuman land is 0.3% The capital is Suva and it is one of the two cities in Fiji. The other is Lautoka City and both are located on the island of Viti Levu. (Fiji Islands Bureau of Statistics (Fiji facts and Figures) 2008: 3,4) & http://www.statsfiji.gov.fj/Publication/Reports.htm Fiji has 14 provinces and out of these 14 provinces, 12 are members of the Fiji Locally Managed Marine Area Network (FLMMA). There are three provinces that have been very successful in the setting up of the Yaubula Management Support Teams (YMST) in their provinces which is a step forward that FLMMA is looking to decentralization its projects and efforts from the main city towards the project sites. These 3 provinces are Kadavu, Macuata and Cakaudrove. The focus for Kadavu for this Campaign will not be as focused as will be done in Macuata and Cakaudrove. The campaign focus for Kadavu is more awareness campaigns and media awareness where as for both sites in Macuata and Cakaudrove, there will be focused conversations done and surveys conducted with the communities and “poachers” identified from the main centres and from the nearby communities within the two sites. (www.googleearth.com) Cakaudrove and Macuata are both located on the second largest island in Fiji, Vanua Levu.CAKAUDROVE: � 1/14 provinces in Fiji; 1/3 of Vanualevu � 15 districts � land area 2,816 km2; population 49, 339 (2007 Census) � ~133 villages mostly coastal � Urban center – Savusavu Hidden Paradise � ~35 nai qoliqoli � Diverse land mass � Rich in flora and fauna � Potential tourism development sites � Few community based MPA’s (Meo.S.2008) MACUATA: (Upper Macuata Area) Nadogo : 3 coastal villages and 4 inland , population is 900, Customary Fishing Right Areas (CFRA)1 are Vanua Nadogo and Sawana. Main sources of income are fishing, farming and copra. 1 CFRA: Customary Fishing Right Areas: The right to fish in waters is termed as fishing rights that are communally owned by a yavusa which consist of many mataqali. The fishing area is called qoliqoli. Fishing rights mean a great deal to the Fijians both traditionally and economically.The boundaries are defined with reference to proximity to its settlement. (Singh. A: 1997) Namuka: 8 coastal and 3 inland villages, population is 700, CFRA is Vanua Namuka and Dogotuki , Main sources of income are Fishing, Farming and Copra. Dogotuki: 5 coastal and 4 inland, population is 600 , CRFA is Vanua Namuka and Dogotuki. Main sources of income are fishing, farming and copra. Udu: 5 coastal villages, population is 590, CFRA is Vanua Udu and Macuata-i-wai. Main sources of income are fishing, farming and copra. (Fong, S: 2008) Macuata 1 (WWF SITE). Source: WWF Fiji Country Program Macuata (WWF SITE) Macuata: 17 sites/LMMA’s , 46 villages , Size of LMMA’s = 1,580.97 sq km² , Size of MPA = 40.7 sq.km²Population (Census 2008) = 72,441 The districts of Dreketi, Macuata, Mali and Sasa, in the province of Macuata on Vanua Levu, the 2nd largest island in Fiji, contains 37 of the poorest coastal communities, where livelihoods are virtually entirely dependent on fishing and subsistence farming. MACUATA (IAS SITE) (Source: Fong,S:IAS) (Source: Tokalauvere,L: IAS) Site History Cakaudrove: ( Meo, S: 2008) There were a lot of events that led up to the beginning of the Cakaudrove Yaubula Management Support Team (CYMST) and Cakaudrove Conservation Initiatives. In 1998, Resort Support2 initiated and worked at setting up the Waitabu Marine Park in Bouma, Taveuni. Last year, 2008 marked their 10 years of working within their site at Waitabu. 2 Resort Support established in 1998 to fill a need within the tourism industry for outsourced expertise in management marketing and development in the context of small medium tourism properties in Fiji. Marine Ecology is the sister company which is now the leading company in Fiji for Marine Assessments and Guest Interpretation and education programs in major resorts around Fiji. Resort Support is a partner of the FLMMA Network and has been very active in Waitabu, Taveuni. In 2001, there was an escalating interest in tourism on the island of Taveuni and within the province of Cakaudrove itself with the set up of the Tourism Resource Owners Association (TROA). The set-up of the first MPA was in 2002 was in the District of Saqani in the village of Naboutini with a follow up of a Management Planning Workshop in 2004 for the district of Nasavusavu, Navatu, Naweni and Nukubalavu.In April of the same year, CYMST concept was presented to and endorsed by the Cakaudrove Provincial Council. A means to integrate these initiatives and develop a learning framework for resource conservation in Cakaudrove is one of the driving forces behind the creation and establishment of the CYMST. There was full endorsement and support by Cakaudrove Provincial Council in Somosomo, Taveuni in April, 2005. A conceptual model of CYMST is to: Assist communities to manage the Yaubula Managing traditional knowledge and scientific knowledge Voluntary facilitators (potential for school leavers) CYMST is made up of members from government departments, non-government organizations and private institutions like from the University of the South Pacific (USP) that are based in Savusavu. Roles and responsibilities of the CYMST are: Ensure rehabilitation of I qoliqoli status, enhancing livelihood and sources of income. Ensure a safe place to raise family-food security. Restore pride for Cakaudrove Awareness and education workshop Facilitate development and implementation of Community Management Plan. Identify common resource threat sand management issue. Achievements: CYMST has completed Resource Management Plans for 7 districts in Cakaudrove. Established 25 Marine Protected Areas and 2 forest reserves. Have confirmed structural framework and communication. Some of the lessons learned by CYMST are: Cautious approach in setting up support team can be site specific. Anticipation and pride for local involvement Management of action planning is a sensible basis for development Adaptive management is easily adopted CYMST fosters change in Government services machinery. Alternative income and other project need critical thinking with linkages and its impact to address the issues. Business plan and operational guidelines. Money can be the root of fragmentation. Wealth of information on traditional knowledge and documentation Wear and tear principles prevalent, Macuata: (Fong: S: 2008) The LMMA project covers all 32 villages in the districts of Udu, Dogotuki, Namuka and Nadogo. Collaborative conservation work by the Macuata Provincial Office, Fisheries and Forestry Departments in Labasa, IAS and the local community. LMMA started work in the Namuka and Dogotuki I qoliqoli in 2004. WWF started work in the same year with the Districts of Mali, Sasa, Macuata and Dreketi. In 2005, the remaining districts along the Macuata coast of (Udu and Nadogo) made requests through the Tikina (District) meetings. In 2006, through the communication between the Macuata Provincial Office(MPO) and the Institute of Applied Sciences (IAS), the idea of extending and consolidating the LMMA work in Namuka and Dogotuki (where we incorporate the Provincial set up of YMST) concept, but this has yet to be modified to suit the project region settings. In 2007, the concept was presented to the MPO and 3 recommendations were endorsed . They were: Approval of the Council for the MPO to co-ordinate the project. Incorporate existing conservation work in the province of Macuata into the project especially those in the 4 Districts covered by the project. Some of the achievements noted are: Management action plan workshops for the 4 districts. Development of village based action plans. Establishment of a network of 15 marine reserves, 2 forest reserves and 3 river/watershed system reserves. Reviving some initiatives no longer practiced-district competitions. There has also been a formation of a core project team, establishment of district support team-already follow up in each village collaboration between the different institutions involved. Some of the lessons learned over the 4 years of the project: (i) Proper planning with clear objectives is critical prior to establishment of this concept. (ii) Project ownership by the community-locals in the (iii) (iv) (v) district support team and core project team. Implementation of action plan need frequent visitation. Continuous capacity building for sustainable initiatives. Partnership and collaborative still proves to work. What else needs to be done? Capacity building in areas critical to the success and sustainability of the initiative (e.g: village governance, waste management, financial management) Development of awareness materials, especially posters. Funding of the 4 districts support team Funding of some management action activities, e.g: seedlings, construction of incinerator. Alternative livelihood development. WWF Site: (Socio-Economic Baseline Report: 2006) In December 2003, WWF organized the Fiji Islands Marine Ecoregion Priority Setting for Conservation Workshop where global, regional and national marine hot spots for conservation were identified by scientists and local experts on marine biodiversity. Accordingly given the biomass, diversity and endemism of marine species in the marine environment, the stretch of reefs and mangrove islands on the northeastern part of Vanua Levu were identified as globally significant. The Great Sea Reef covers approximately 202,700square kilometers. The total land area of the project site is approximately 110,300 ha , or 1103 square kilometers. In November 2004 the traditional leaders and chiefs of the 37 villages of the districts of Mali, Dreketi, Sasa and Macuata collectively voiced their concerns about the increasing environmental issues threatening the existence and extent of marine and terrestrial biodiversity resources in a community workshop facilitated by members of Fiji Locally Managed Marine Areas (FLMMA), representatives of partner organization and communities, of which WWF Fiji Country Programme is a member. The main problems identified by participants were over-fishing and the degradation of fishing areas which resulted in reduced fish catches. Many contributing factors to the two problems were identified, which included illegal fishing (fishing without licence), use of small mesh nets (driftnets), destructive fishing practices (use of plant poisons, gas & compressor), use of gear such as scuba diving in night and day fishing and motorized boats enabling harvests in large quantities of fish at one time and more frequently. In addition, siltation from inappropriate landuse practices and from exposed surfaces induced by burning, industrial discharges into rivers and waterways from commercial entities and sand mining in the qoliqoli reef areas. A number of actions were recommended to address these factors towards reducing the problems. This included the setting aside of ten (10) marine areas as community based marine protected areas. It is intended that these areas will act as breeding areas to restock the wider qoliqoli in due time. In total these widely dispersed areas cover 82square kilometres. Three (3) were identified following district level planning meetings in June 2005. Biodiversity Summary Macuata:( WWF site) & IAS site The Fiji Islands Marine Ecoregion (FIME) is of particular biological significance in global terms because of the extent and remoteness of its shallow tropical marine habitats. Created by the tectonic convergence of several oceanic plates, the uplifted shallow platform is surrounded on all sides by deep, oceanic conditions, making it a likely significant repository for medium to high levels of marine diversity and endemism. Fiji’s reefs have had relatively few scientific c assessments but early investigations indicate high levels of cryptic speciation. Recently, WWF-Fiji lead an expedition to assess the biological diversity of the Great Sea Reef to the north of Vanua Levu, known locally as Cakaulevu, which was identified as an area of global biodiversity importance during the biological visioning workshop. In addition, a biological survey of the Kubulau coast of Bua by the Wildlife Conservation Society (WCS) was completed in 2005, generating further information. Further research is likely to reveal a much greater level of biodiversity complexity than previously recognized. Tropical marine biodiversity levels drop away steeply to the east of Fiji, which again indicates that within the Western Pacifi c, the reefs of Fiji are an important repository of biodiversity in a region characterised by isolated oceanic islands and atolls. (Nair, V:2003) The Fiji Islands also offers an enormous wealth of coral reef habitat, covering an estimated 10,020 square kilometers of the Fiji archipelago, and representing 9.0 % of the coral reefs of the Pacific and 3.5 % of the total area of coral reefs in the world. While some of the reefs within the country have been studied extensively in terms of their ecology and biodiversity, the vast proportion remains poorly known. Species numbers for coral reef biota are high. Currently, at least 298 species of scleractinian coral have been recorded along with 475 species of mollusc and some 60 species of ascidian. A total of 1,208 species of fish have been recorded within Fiji, the majority of these are associated with coral reefs. Algal flora is also reasonably well documented with 448 species known. 6 major habitat types: outer barrier reefs, back barrier reefs, channels, mangrove island fringing reefs, rocky island fringing reef and submerged patch reefs. • The diversity of marine biota on the Great Sea Reef and its associated habitats was revealed to be of high importance on a global, regional, national and local scale. This survey alone documented the reef to have approximately 55% of the known coral reef fish in Fiji (with a predicted actual value of 80%), 74% of the known corals found in Fiji and in total 40% of all the known marine flora and fauna in the Fiji Islands. In addition, 117 species of sponges, 31 species of coelenterate and 12 species of ascidian were collected. The number of species recorded where highest of any other reef area surveyed in Fiji. • Populations of at least 12 species listed on the 2004 IUCN Redlist of threatened species were observed including 10 species of fish, the IUCN endangered green turtle (Chelonia midas) and the spinner dolphin (Stenella longirostris). • The survey also revealed populations of the nationally endangered bumpheaded parrotfish (Bolbometopom muricatum), previously presumed locally extirpated; one new fish species (Pomacentrus sp.); and one presumed new record (Chromis opercularis) only previously known in the Indian Ocean. 44% of the known endemic reef fish in Fiji were observed. • Within the hard corals, 43 new records were documented for Fiji. Of these, two were new genera and three were believed to be geographic range extensions, Echinomorphanishihirai (Veron, 1990) and Turbinaria heronensis (Wells,1958). • Sixteen species were found to be new additions to the flora of the Fiji Archipelago. Two possible new species, Ceramium sp. and Crouania sp., were also recorded. • Habitats of primary importance to the diversity and abundance of marine biota of conservation significance were generally found to be the outer barrier reefs, channels and mangrove island fringing reefs. Increasing levels of intactness were recorded with distance from population centres, land based siltation, pollution and extractive activities. • Unusual distant offshore mangrove island fringing reef habitats were found to be of surprisingly high diversity and productivity. These highly dynamic, tidally influenced systems are considered to be "keystone habitats " of crucial importance to maintaining the ecological integrity of the entire coastline. • The most damaged sites in terms of siltation and trash were observed to be in the general vicinity of the Labasa Township. • Overall, commercially important fish were found in very low numbers and small sizes. Fish important for local subsistence were found in higher numbers, but this varied greatly from site to site. Fishing pressure, as indicated by discarded fishing lines, was greatest around the vicinity of Labasa. (Fiji’s Great Sea Reef Survey:2007) Cakaudrove: Cakaudrove as one of the three provinces on the island of Vanua Levu, little is known and recorded about the overall status of biodiversity in this province. There are a number of sites within Cakaudrove that have been identified as rich ecosystem sites due to a species richness/diversity and richness, habitats, This group encompassed the zone in transition from being strictly marine to terrestrial and includes coastal littoral vegetation, small offshore islands, soft sedimentary shoreline habitats, coastal substrate, brackish water habitats, mangroves, lagoons, coastal lakes, inland pools, sand dunes, breeding grounds for important species such as crabs, sea snakes, birds, turtles and freshwater fish species. The areas mentioned below in Cakaudrove were identified in this zone mainly for their uniqueness, endemism and representation of habitats, species and processes. On the island of Taveuni, this is a volcanic island with lowland and montane rainforests in the centre the east of the island, in which a lake, mountain stream and other freshwater habitats are located. The islands has a rocky coastlines and scattered fringing reefs. Taveuni has representative and unique mangrove assemblages. (pg 19) Qaloqalo salt lake, Natewa Bay, Lat: 16.460S Long: 179.310E, Approximate land area: 150 ha, Estimated population density: 16/ km2 Description of area: The salt lake is located on a narrow isthmus south of Natewa Bay; rich in marine species. The lake has tidal flushing and is surrounded by a wide band of mangrove forest. (pg:21) Approximate land area: unknown Etimated population density : 48.21 / km2 Description of area: The Buca and Nala River systems are amongst the most pristine and intact sites identified, notable for their high amphidromous fi sh species (at least 6 species) and high levels of endemism (pg: 21) Naweni Approximate land area: 2816 km2 Estimated population density: 4 / km2 Description of area: Two saltwater limestone pools fringed with mangroves, hosting endemic red prawns. (pg: 23) It is estimated that there are around one thousand coral reefs in Fiji. Reef sizes vary from less than 50 m to 370 km long. The diversity of reef types include patch, fringing, barrier, platform, oceanic, ribbon, drowned, atolls and near-atolls. The most common reef types are fringing reefs and barrier reefs. The reefs are historically healthy but are currently under threat from environmental stressors such as bleaching, pollution, physical damage from unsustainable fishing practices and unsustainable harvesting for the aquarium trade. Based on existing information, the Group the following sites in Cakaudrove to be an outstanding or priority areas for coral reefs. Estimated reef area: unknown Known reef state: Moderate Information status: Low Type of information: physical features, soft corals (pg: 25) Namena/Savusavu Estimated reef area: unknown Known reef state: Healthy Information status: Moderate Type of information: physical and oceanic conditions, taxa biodiversity(pg: 26) Cakaudrove was also identified as one of the 27 sites as a priority for coral reef fish by. These are reef areas with high abundance, richness, endemism and diversity of reef fish. Natewa/ Vuna Description of area: reef walls and promontories are found around this limestone island Known status of fish abundance and diversity: low State of knowledge on fish aggregation: low, but includes sightings of hammerhead sharks, Sphyrna leweni (pg: 31) Somosomo Strait between Taveuni and Vanua Levu Description of area: the channel lies on the east to southwest axis and is prone to cyclones during October-March. Known status of fish abundance and diversity: low State of knowledge on fish aggregation: low (shark population) (pg: 35) The inshore environment provides important feeding and breeding habitats. It is usually an area of high conservation, cultural, medicinal and economic importance. Inshore habitats include mudflats and soft bottom sedimentary environments, seaweed (algae), seagrass. Species associated with the inshore environment include white cowries (Cypreaea spp), emperor fish (Lethrinus spp.), kanace (mullet) (Mugilidae), nuqa (rabbitfi sh) (Siganids), seahorses (Syngnathidae), silver biddy (gerridae), ponyfish, seasnakes (Laticauda spp.), turtles species, seabirds, Venus clams (Cyclena sinensis), fi ddler crabs (Uca vocans); mud crabs (also known as mangrove crabs) (Scylla serrata, qari in Fijian), mud lobsters (Thalassina anomala, mana in Fijian), sting rays (Himantura spp.), eels (Order anguilliformes), polychaete Marine Tenure ( i qoliqoli system) Ownership worms, small fi sh (detritus feeders), goatfish (Mullidae), pufferfish (Tetradontidae) and hammerhead sharks (Sphyrna leweni). Thirteen significant areas were identified as being representative, unique or areas that provide the feeding and breeding grounds for species of cultural, economic or conservation value. Cakaudrove also being one of the sites, specifically Natewa bay. (pg: 36) Marine tenure in Fiji is, in the majority of cases, well defined and registered. Customary understandings on marine resource use allow for accesto and ownership of fishing grounds and rights to all foreshore and shore areas up to the outer reef (kanakana and I qoliqoli). Kanakana is the subsistence fishing area, which usually refers to the immediate shore area adjacent to a village and includes all mangroves, mudflats, sandflats, lagoons and reefs. I qoliqoli refers to the total fishing area, including the areas beyond the kanakana. Legal access allows customary owners proprietary fishing rights over their I qoliqoli while the state has ownership rights of waters up to the high-water mark. Thus, there exists dual ownership and understanding of resource use. Customary owners in both instances still have significant rights over their coastal areas, so that any marine resource management initiative must involve the community. This dual ownership is at times a source of conflict and concern for customary owners. There are 410 I qoliqoli areas in Fiji, more than 200 of which have been surveyed and registered by the Native Lands and Fisheries Commission. Most of those that have not been registered are rivers and creeks. Ownership or user rights of I qoliqoli areas are at a higher level than the yavusa or vanua (land). Therefore the liuliu ni yavusa, or chief of a yavusa has ownership rights. Unlike land tenure in Fiji, which is mataqali or clan owned, demarcation of specific I qoliqoli areas has always been disputed. In many cases the communal ownership of the I qoliqoli is complex. Sometimes the paramount chief who has the I qoliqoli ownership can sign fishing licenses or make agreements with coral harvesters or other outside investors, for example, without the knowledge of the several villages and districts under his or her jurisdiction. In addition to the complexity surrounding ownership and user rights, there is also a dual administrative or control system for the people. The government administrative system and the traditional system both come into play when working with people in communities. This is important because any work in communities still uses both systems. In the village for example there is a village headman who is the administrative head or village headman. The headman may have no high traditional positions. The village traditional head or liuliu ni yavusa is different from the village headman or turaga ni koro. The village headman then liases or works with the traditional leaders in projects. Their roles are mostly administrative and they are contact persons for government or other external contacts or developments. A review of the Fijian Affairs Board is currently being undertaken. The question is whether the restructure will take into account the aspirations of all Fijians, including urban-based Fijians. This is important for many resource owners with decisionmaking powers now reside away from their communities. Thus, there remains a sort of remote control over resources and the people using them. People living away from home may also have very different views of how resources should be used, developed or managed as they have different lifestyles and aspirations. The models above depict a simple process that people should be able to work with, but in some situations, elders or leaders in communities have migrated to urban areas and there is a new leadership at the community level. The challenge, therefore, is how the restructuring of the Fijian Affairs Board will take into account these changes, and how best they plan communities’ future direction and linkages to the modern administration.(Vunisea, A, 2002: pg7-8) Main Livelihoods and Income The people of Macuata and Bua provinces in Vanua Levu have traditional fishing rights over the Great Sea Reef (GSR_Macuata) and associated marine systems and continue to depend heavily on the functioning and biological diversity of these systems for their subsistence and commercial livelihoods. The following data was accumulated through the SocioEconomic Survey conducted by WWF of the Tikina Dreketi,Mali, Sasa,Macuata and this section will focus on the household economics and main sources of income within the 4 Districts. “The purpose of this study, household economics specifically refers to household income generation and spending patterns, material wealth and housing. This information provides a baseline for monitoring the economic trends over time associated with the set-up of marine reserves and management of qoliqoli in the targeted Macuata community. In view of the fact that most rural households do not have or keep proper records of income and have a tendency to recall based on recent occurrences; households were asked total income per month and trends over the year to guarantee accuracy in figures. Many households earned an income at varying intervals over a year based on seasonality, social, economic and environmental factors, the mean and standard error of the mean were then used as basis of analysis.” The following are just 4 examples of income generating activites and the frequency of number of households listed as their main source of income: Farming-242, Fishing-234, Copra – 41, Sale of handicrafts – 13. Given the lack of income generation options of sampled coastal and terrestrial communities, the majority of the households depend entirely on the environment for sustenance and livelihood with fishing and agriculture being the major economic activities. Agriculture was recorded as the most widespread economic activity among populace with 35% of the households listing sugarcane, cash crops, kava, rice and forestry as their main sources of income, followed by fishing (33%) and paid employment (13%). Seventy five percent (75%) of households derived income from the extraction of natural resources. Households earning from outside sources in the forms of remittances and social welfare accounted for earnings in 5.5% of sample households while income generated from other sources including land leases, casual work and timber logging payment was included in 1.9% of households. The reliance on natural resources is further emphasized when examining the economic returns of each earning activity. The least important source of income noted from sample were payments from Social-Welfare, returns from land lease and small business. Incomes sourced from these activities are often additional to main income sources (fishing, farming or paid employment) (WWF, 2006:17-19) Climate Fiji enjoys a tropical South Sea maritime climate without great extremes of heat or cold. The islands lie in area which 'is occasionally traversed by tropical cyclones, and mostly confined between the months of November to April every year. Temperatures average 22 degrees Celsius for the cooler months [May to October] while November to April temperatures are higher with heavy down pours. Fiji Islands Bureau of Statistics (Fiji facts and Figures) 2008: 3,4) & http://www.statsfiji.gov.fj/Publication/Reports.htm The island of Vanua Levu has a moderate, tropical climate with a distinct wet season, generally recognized as the cyclone season, between November and April. Fiji experiences about 10 to 15 cyclones per decade, two to four of which cause severe damage including extensive wind damage, flooding, storm surges and occasional landslides (Chandra & Mason, 1998). Rainfall is highly variable, even in the wet season, and is predominantly influenced by the prevailing southeast trade winds and local topography. The mountains of Vanua Levu create a wetter zone on the windward side and a drier rain shadow on the leeward side. Annual rainfall averages 1.78 to 2.03 cm on the leeward side and 2.92 to 3.18 cm on the windward side, with weak seasonality. Long-term averages of annual rainfall for the Macuata area (as recorded since 19772000) are in the range of 2.2 to 2.5 cm. Temperatures range from 19.8 oC to 30.6 oC (Fiji Meteorological Office). The average yearly temperature is about 25oC with a slightly lower average on the windward side and higher average on the leeward side. The humidity is usually high, ranging from 75 to 80 %. (http://www.met.gov.fj/climatefiji.html) Demography Fiji as of the last census in 2007 has seen a dramatic increase in her major races and the overall population has increased from 775, 077 in 1996 to 837, 271 ion 2007. The two major races in Fiji had all contrasting differences. Fijians increased from 393,575 ion 1996 to 475,739 in 2007. Indians actually decreased from 338,818 in 1996 to 313,798 in 2007. The Incidence of Poverty (%) using differentiated values for the Basic Needs Poverty Line (BNPL), which is the monetary value of the minimum cost of living. For Fiji it was 35%, Cakaudrove was 51% and Macuata was 50%. Total live birth increased from 18,394 in 2006 and 19,298 in 2007. Infant mortality rate (per 1000 live births) decreased from 19.50 in 2006 to 18.40 to 2007. Average Household Income and Expenditure Survey shows that the Fijians are 12,972 followed by Indians at 11,902 and others at 19,105 Cakaudrove: Cakaudrove has 134 villages, there are 14 districts. Total population count for Cakaudrove Province = 49,339. Fijians make up 35,967, Indians make up 7,927 and Others are 5,445. Macuata: Macuata Total Population: 72, 441 with Fijians = 28,193, Indians = 42, 554 and Others = 1,694 WWF sites (4 districts): Population = 4056 IAS site (4 districts): Population = 1037 Conservation Values Fiji has an extensive and diverse range of marine habitats including, estuaries, mangroves, wetlands, sea grass, macroalgal assemblages, protected and exposed soft shores, lagoons, sand dunes and coral reefs. Fiji falls within the top 10 countries or geographical locations with globally significant coral systems and hosts the world’s third longest barrier reef system. Some of the impressive biodiversity includes; fish, crabs, lobsters prawns, sharks, sea snakes, giant clams, turtles (green, hawksbill, leatherback, and olive ridley turtles - all of which are listed under CITES), endemic sea birds such as the Fiji petrel, and over a dozen migratory shorebirds that use Fiji’s mudflats for feeding. Even though there is low endemism within Fiji, important marine habitats provide essential migratory routes and breeding grounds for many endangered species such as whales, turtles, tuna, humphead wrasse and the world's largest parrotfish, the bumphead parrotfish, Bolbometapon muricatum, is also found here. The Ecoregion (which comprises Fiji’s EEZ) is also part of the world’s richest fishing ground for tuna, contributing to about 15% of Tuna catches in the region.(pg: 4) The marine biodiversity and conservation status of the marine systems within the GSR3 are very poorly understood and are becoming increasingly threatened by burgeoning human populations, associated industrial and coastal development, and the rising international and local demand for tropical reef products. The lagoon side of the GSR is an extensive and complex system of submerged and emergent coral reefs, mangrove and rocky islands, seagrass beds and other marine ecosystems. These systems provide substantial fisheries resources and important the geophysical functions of shoreline stabilization and prevention of wave damage. The coastal and island mangroves also act as sediment and pollutant filters for these coastal areas, and provide essential nursery areas for various organisms that inhabit the near shore marine systems. The province’s resources need to be managed to support natural processes, maintain biological diversity, and protect natural features. The resources offer opportunities for food security, wilderness recreation, environmental education, and research. Agriculture, forestry, tourism and other resourcebased industries are economically important and depend on a 3 GSR: Great Sea Reef sustained supply of natural resources. In addition to providing societal benefits, the natural environment has significant intrinsic value Known threats Economic Activities Fiji’s economy is highly dependent on the exploitation of marine resources. With a growing population and rising poverty, the acute need for better economic growth has led to the pursuit of large-scale economic development activities at the national level that may potentially place these resources under greater pressure Mining: Mining activities often have enormous negative impacts on coastal areas through siltation and polluted runoff . There is considerable interest in the mineral resources of Fiji, and currently mining companies are active in many areas , including Namosi, Wainivesi, Qalimare, and areas inVanua Levu( Mineral Resources Department 2002). There is further interest from mining developers in prospects for expanding activities in Fiji, and many other areas are under mining tenements, and the Fijian government appears to be supportive of this trend. Agriculture There are a number of agricultural activities that have a negative impact on coastal areas, with associated problems of increased soil erosion leading to high levels of sedimentation. Many streams and rivers and coral habitats are experiencing siltation from terrestrial run-off. Increasing incidences of runoff are a direct consequence of farming practices used during the production of sugar cane, ginger, pineapples and pine seedlings, with a large number of farming areas being based in or near coastal areas This problem is magnified by the fact that these activities have been extended to marginal land due to lack of arable land. Specific areas that have been severely affected have been documented in a number of places in Viti Levu and Kadavu. Tourism and its associated developments: Problems associated with the tourism industry include coastal over-development, anchor damage and the reclamation of mangrove areas for resort developments. For example, the development of a marina complex in Nadi Bay involving the dredging of a harbour and the use of soil for land reclamation resulted in the smothering of seagrass habitats adjacent the site is a key sector of interest in Fiji’s overall development, and the current National Strategic Plan (2002-2004) has a focus on developing the tourism industry into a billion dollar industry by 2007. Some of the targets include; over 448,000 visitors by 2004, new 3 to 5star hotels completed by 2005 and the establishment of Nadi Bay and the Mamanucas as a Pilot Tourism Development Area by 2005. General and tourism related development activities such as land reclamation, coastal infrastructure development, channel blasting, dredging and coral sand mining (e.g. from beaches, lagoons) are likely to have profound effects on the physical environment. Hotels and other developments come with associated environmental problems such as waste disposal and pollution . Expansions at the scale proposed for the tourist industry without the appropriate environmental planning could pose significant threats to marine habitats. Aquaculture developments Aquaculture developments have the potential to take pressure off wild stocks, but activities can often mask the over-harvesting of wild stocks and come with range of environmental problems, especially with regards to the pollution of marine areas. Direct exploitation of marine resources and poor management practices Coral harvesting: The export of coral from Fiji began in 1984. The extraction of coral reef products such as hard and soft corals for the marine aquarium and curio trades in Fiji has attracted international attention and concern due to the perceived largescale increase in trade in these products. There is now legislation to regulate the harvest and trade in accordance with the provisions of CITES, and it is government policy that all industry members be certified by the Marine Aquarium Council (MAC). There is currently a moratorium on new companies entering the trade, and presently there are only 6 companies operating in Fiji. The ability of the Department of Fisheries to monitor the extraction of coral and other aquarium products is limited by low capacity and financial resources. Over-exploitation of coral reef resources for commercial purposes The over-harvesting of specific reef species for lucrative niche markets poses a serious threat to persistence of these resources. Examples include the harvesting of beche-de-mer, trochus and giant clams for the curio and aquarium industries, and fish for the aquarium and live food fish industries. The unwavering demand for Beche-de-mer from East-Asian markets continues to fuel unsustainable extraction rates in Fiji. Problems with the acute over-harvesting of giant clams have already been recognised, and the export of wild giant clams from Fiji is now prohibited. However, there is a general lack of understanding surrounding the level of regulatory control needed to deal with this issue, and the challenge is to come up with timely and appropriate responses. In other countries, compressors used for harvesting beche-de-mer have been reported as also being used in the harvest of other coral reef resources. Thus activities surrounding the pursuit of key species may have more far reaching effects, increasing harvesting pressures on other, non-target species. Unsustainable and destructive fishing practices Subsistence fishing is of great importance to the livelihoods of the people of Fiji, with estimations of as much as 17,000 tonnes of subsistence catch being removed from reef systems annual. With increasing populations, subsistence activities are beginning to strain marine resource capacities, and it is noted that the abundance of fin-fish species is declining in coastal areas near highly populated towns and centres. (Declines in mullet, stout chub mackerel and trevally species have all been noted by fisher). Although legislation bans the use of explosives and poisons (e.g. traditional poisons such as derris roots and modern poisons such as herbicides and pesticides) for fishing, these practices are still prevalent and widespread in Fiji. Such fishing methods are non selective, and can wipe out entire communities of marine organisms, having detrimental effects on reef systems. The introduction of apparatus such as SCUBA gear has increased the effectiveness of fishing efforts, and thus the intensity of pressure on marine resources, and shellfish species have been particularly affected by this trend . Environmental and ecological threats Land-based pollution With most development and economic activity occurring in coastal areas, associated environmental problems can have far-reaching and profound impacts on the coastal environment. Studies conducted on the coastal waters of Viti Levu have found areas where nitrate levels exceed those deemed safe for corals (Mosley and Aalbersberg, 2001). Sources of pollution include sewage, mining, industrial discharges, litter and refuse disposal, fertiliser, pesticide and urban run-off, siltation from agricultural practices, and logging and clearing of riparian vegetation. Sources of pollution include major food and chemical industries, rubbish dumps, mining and agricultural activities and improper waste management in residential and tourist developments (Vuki et al., 2000). The pollution affecting the Suva harbour area has been well documented, and poor disposal practices have lead to high levels of nutrients, chemicals, heavy metals and it is noted that the levels of tributyl tin are higher than those documented in the literature for any other port in the world. Sea-based pollution The extent of this threat is unknown, but includes oil spills, toxic spills and ballast water discharges. The latest being the sinking of the ship the Ovalau in August 2003, which contained caustic soda on board. Climate change Climate change related impacts are likely to have profound affects on weather activity and oceanic conditions that will have huge implications on the coastal environment. Climate change is predicted to exacerbate natural variations in Pacific weather patterns, leading to slight changes in mean range changes for factors such as rainfall, and result in extreme weather events of a greater intensity. These changes in physical and meteorological processes will translate into corresponding changes in ecological systems and biodiversity. Coral reef systems, with their narrow temperature range tolerance, will be severely affected by predicted increases in sea temperatures (IPCC 2001). It is known that the periodic temperature increases experienced in El Niño years are responsible for coral bleaching, and it is accepted that climate change will exaggerate the temperature extremes elicited by El Niño events leading to a greater incidence of coral bleaching. Rising levels of atmospheric carbon dioxide are thought to adversely affect the ability of reef organisms to synthesise reef building limestone, and a decline in calcification rates are predicted. Mangrove forests, as well as coral reefs, may also be threatened by predicted rises in sea level. It is recognised that climate change will have a more pronounced negative effect on the biodiversity of small islands than in continental areas, and thus climate change emerges as a huge challenge for Fiji. Mass coral bleaching in March-April affected many of Fiji’s reefs, with the exception of those in the far north with more than 40% of colonies dead at many sites. There was also variable bleaching in 2001 and 2002, except for intense bleaching in 2002 in very shallow areas. Many affected reefs are making a strong recovery e.g increasing densities of Acropora recruits at sites around Suva. The 2000 mass bleaching event catalysed the first major GCRMN activity in the region when 6 independent research groups collaborated to assess bleaching at 19 sites throughout Fiji. Since 1996, the GCRMN has assisted with the seawater temperaturemonitoring programme at the University of the South Pacific to record temperatures throughout Fiji. Data on about 100 Fiji reefs comes from researchers, tourist resorts, and reef based tourist operations, such as the Fiji Dive Operators Association, Greenforce and Coral Cay conservation. A campaign to involve tourist resorts in monitoring their local reefs was initiated in 2002 at 7 permanent GCRMN and Reef Check sites around Suva timed in March/April to coincide with the potential bleaching season. Crown-of-thorns starfish The infestation of reef systems with crown-of-thorns starfish (Acanthaster planci) is a well documented phenomenon in Fiji, and A. planci outrbreaks can result in large areas of reefs being destroyed. The exact reasons behind why A. planci proliferate in certain areas and not other are not well understood. Whippy-Morris and Pratt (1998) noted the following on A. planci outbreaks: • In southern Viti Levu (in 1967-70) first documented outbreak • A second outbreak occurred in l979-83 in Suva, the Coral Coast and inner Mamanucas. • A third outbreak occurred in 1986-88 in the Suva area, Beqa Island reef, Coral Coast, Naigani Island and other areas. • A. planci were recently found on the reefs of the Mamanuca group, which are important for the tourist industry in this area. • Anecdotal information collected from fishers in the Suva area indicate that A. planci were common from the 1920's to the 1960's. Accounts recalled from elders indicated that an intensive outbreak probably occurred before the 1920-30's with a smaller outbreak in the 1940's. • On intensively fished reefs in Southern Kadavu, Suva reefs, Kabara and Lakeba in the Lau Group, (Nair, V:2003, 26-31) Summary of pertinent management strategies Macuata: Improved management processes will help to achieve the following: - Decentralizing the management of natural resources - Improved transparency in decision-making and information sharing - A holistic approach to increase equitable participation of stakeholders in decision-making processes from village to district and national level - Better enforcement of government policies and laws. -Stakeholders would be the Provincial Office, District Councils, Qoliqoli Committees, Resorts, WWF, Fisheries, NLTB, NLFC, Communities, Police, Chiefs. Cakaudrove: Cakaudrove as a province has 7 districts (tikinas). The only other province that has an endorsed and established Yaubula Management Support Team (YMST). The environment is important to Cakaudrove and the Cakaudrove people recognize the link between healthy communities and a healthy environment. Maintaining a healthy environment for current and future generations requires the collaboration of communities, organizations, businesses, and all levels of government. Using a balanced, coordinated approach, we can protect the health, prosperity, and environmental integrity of our communities. Summary of legislation and governmental policies (Erika J. Techera, “Customary law and community based conservation of marine areas in Fiji” (Paper presented to the Environmental Justice and Global Citizenship Conference, July 2007) Constitution (Amendment) Act, 1997 The Constitution does not offer a blanket recognition of customary law; instead, the Constitution (Amendment) Act 1997 recognizes customary law and traditional rights to terrestrial land, provided they are not inconsistent with any law or governing principle of the state. Article 6(b) preserves ownership of Fijian land according to Fijian custom. Section 38 guarantees that the law applies to every person equally, however it also exempts certain laws and administrative actions regarding customary land, and fishing rights from the equality provision. Section 186 of the Constitution makes provision for the application of customary laws and for dispute resolution in accordance with Fijian tradition, but this will depend statute law (ie. customary laws do not apply automatically and must be expressly recognized in a piece of national legislation in order to be recognized by the government). Native Lands Act, 1978, and Native Land Trust Act, 1985 Under the customary system of land tenure, terrestrial lands and coastal marine areas are the exclusive property of the community. Terrestrial lands were traditionally held by the vanua (district) until 1880, when the Great Council of Chiefs (GCC) resolved that native lands should be owned communally by the mataqali (clan). This is different to the ownership system in place for coastal marine areas, which are the property of the yavusa (tribe), or in some cases the vanua. The Native Lands Act was first enacted in 1880 and, following the resolution of the GCC, duly vested customary lands with the mataqali. The Native Land Trust Act, provides the legal framework for administering native lands in Fiji. Under the customary system of land tenure, terrestrial lands and coastal marine areas are the exclusive property of the community. Terrestrial lands were traditionally held by the vanua (district) until 1880, when the Great Council of Chiefs (GCC) resolved that native lands should be owned communally by the mataqali (clan). This is different to the ownership system in place for coastal marine areas, which are the property of the yavusa (tribe), or in some cases the vanua. The Native Lands Act implements Article 6 of the Constituion. It states that “[n]ative lands shall be held by native Fijians according to native custom as evidenced by usage and tradition” and provides for the registration of land. A Native Land Commission determines the rightful owner of land if there is a dispute. The Native Land Trust Act (NLTA) provides that native lands cannot be alienated even by customary owners, and it vests administrative control of native land in the Native Land Trust Board (NLTB). So although the Indigenous people have nominal ownership rights, the control and management of land is vested in the NLTB for the benefit of the traditional owners. Strengths: Communal ownership of native lands is constitutionally entrenched and reflected in the statutory framework under the Native Lands Act and Native Land Trust Act. This is both a strength and a weakness however, as the national law recognizes customary ownership in terms of the right to use the land, and does not recognize full title to the land (see below). Weaknesses: Ownership of terrestrial lands and the coastal marine zones is an unresolved issue at law. While customary owners assert their ownership interest in their traditional lands, the laws of Fiji maintain that the government owns the land with only user rights for indigenous people. Section 19 of the Native Lands Act, for example, states that all lands left vacant by the discontinuance of a mataqali landholding unit will revert to the Crown. Without legal recognition of title to the coastal zones, indigenous people with customary rights to an area are not guaranteed the opportunity to make important decisions on planning and development of their traditional lands. Fisheries Act, 1991 The Fisheries Act enables limited community involvement in coastal marine management via provisions that require community consent over commercial and subsistence fishing in their customary fishing rights areas (qoliqoli). The law allows for the involvement of communities in the governance of the coastal zones and the application of customary laws to regulate the qoliqoli in some circumstances. The Act also creates the position of honorary fish wardens, who are community members appointed to protect the jurisdiction of customary rights holders in the qoliqoli areas. Section 13 of the Fisheries Act is the window through which customary law may be applied to govern the coastal marine areas. The provision requires commercial and non-commercial harvesters to obtain a permit from the customary owner of the qoliqoli, with a few exceptions. Section 13 and Regulation 4 of the Fisheries Regulations require both commercial and noncommercial harvesters to obtain a permit to fish on any reef or shellfish bed in a registered qoliqoli, with a few exceptions. For commercial harvesters, this is a precondition on obtaining a license to fish in the area. An exception is contained in the Act for non-commercial harvesters who use a hook and line, spear or portable fish trap that can be handled by one person. Strengths: The licensing and permit system under Section 13 allow customary owners to exercise jurisdiction over the qoliqoli. Any fishing by harvesters from outside the community must obtain a permit from the District Commissioner, which in practice must be based on the approval of the local chief. While fishing cannot be completely prohibited by the Fisheries Act and Regulations, this may be a good thing as it ensures subsistence indigenous fishing rights in a country where the main source of protein for rural people is from marine resources. Weaknesses: Under the current Fisheries Act, it is legally impossible to establish a marine protected area where fishing is strictly prohibited. While both commercial and subsistence harvesters need a license or permit to enter a qoliqoli, the exceptions under the Fisheries Act for certain methods mean that it is legally impossible for a community to set up a protected area without ministerial designation. This gap in the law has led to many complications related to enforcement by the community of both customary and national fisheries laws. In addition, though the definition of “fish” under the Fisheries Act is broad, non-living marine resources seem to be beyond the ambit of the Act, and so may not benefit from protections under the Act. National Trust of Fiji Act, 1970 This law establishes the National Trust of Fiji, with an overall purpose to provide for the sustainability of Fiji’s natural and cultural heritage. In discharging its mandate the National Trust is empowered to enter into conservation agreements with landowners. Strengths: The mandate of this statutory body is broad and includes the protection, preservation and management of any site deemed significant to Fiji’s natural and cultural heritage. Weaknesses: Under the Act, landowners may enter into agreements or accept covenants to preserve a heritage area, but no role for landowners in terms of protection or management of these sites is stipulated under the Act. Past environmental education work There have been numerous organizations including Government Departments that have initiated environmental education in terms of health, education, agriculture , fisheries in all forms- workshops, discussions, forums, school visits, drama, festivals, showcases, Open Days. Not only restricted at the sites for the Campaign but throughout Fiji. Numerous organizations: Live and Learn , Ministry of Education, Fiji Red Cross, Ministry of Health, UNICEF, WHO, UNEP, UNDP just to name a few. Potential partners Ministry of Fisheries & Forests (Fisheries Department), World Wildlife Fund for Nature (WWF), Wildlife Conservation Society (WCS), Institute of Applied Sciences (IAS/USP), SEAWEB, Department of Environment, Department of Tourism, Fijian Affairs Board, Resort Support, Burebasaga Confedaracy Community rep., Kubuna Confedaracy Community rep., Tovata Confedaracy Community rep., National Trust of Fiji, IUCN, CI, Police Legal Team, Macuata Qoliqoli Committee, CYMST rep, KYMST rep., commercial fishermen and Wholesalers (Fish suppliers). Your organization and your background LEAD AGENCY: The Locally-Managed Marine Area (LMMA) Network is a group of practitioners involved in various marine conservation projects around the globe who have joined together to increase the success of our efforts. The LMMA Network is learning network, meaning that participating projects use a common strategy and work together to achieve goals. The Network is interested in learning under what conditions using an LMMA strategy works, doesn’t work, and why. Network members share knowledge, skills, resources and information in order to collectively learn how to improve marine management activities and increase conservation impact. The Network's membership consists largely of conservation projects that are using (or planning on using) an LMMA approach, and includes: Community members Traditional leaders Conservation staff Academics and researchers Donors Decision-makers The FLMMA Network aims to build capacity to implement and effectively manage an overall LMMA strategy. There are a number of specific tools (strategies or actions) that can be used to manage resources and counter threats, including: • Full Reserve – complete protection of all natural resources within a defined area. Often called a “sanctuary,” “no-take zone,” or “fully-protected area.” • Species-Specific Harvest Refugia – a ban on harvesting one or more species or individuals of a certain size and/or sex within a defined area. • Effort, Gear or Behavioral Restrictions – rules limiting harvesting effort or particular uses within a defined area. These can include fishing gear restrictions, fishing effort limitations (e.g. number of fishers, number of boats, catch quotas, etc.), type of behavior allowed/disallowed (e.g. recreational diving, no anchoring), and licensing limitations. • Seasonal Restrictions – rules limiting what time of year overall fishing or species-specific harvesting may take place. These tools may be used in any combination and/or over a period of time and spatial scales depending on the particular situation to achieve the best results. The four major theme areas that FLMMA are targeting are: Capacity building Education and awareness campaigns Monitoring effectiveness of ecological, socio-economic and governance aspects of LMMAs. Transfer of new technologies and approaches across the LMMA network. The Network's membership consists largely of conservation projects that are using (or planning on using) an LMMA approach. A 'member' may consist of one or any combination of individuals, communities, land-owning groups, traditional leaders, government representatives, conservation organization staff, elected decision-makers, university scientists and researchers, and/or donors working together to achieve specific goals related to the conservation or sustainable management of biodiversity, and who are working to implement or enhance an LMMA strategy at one or more specific sites. LMMA works closely with: WCS, Conservation International, WWF, Wetlands International, Birdlife, and other conservation organizations. Private industry groups and relevant government departments (Fisheries, Tourism, Environment, Fijian Affairs). Currently there are 16 member organizations. CAMPAIGN MANAGER: Margaret is currently a Fisheries Assistant with the Fisheries Department and is working in the Research Section as part of the Survey Team that undertakes biological and socio-economic baseline surveys for Fiji's 410 fishing grounds. She is also the FLMMA Secretariat based also at the Fisheries Department. She is currently the Co-ordinator of the "International Year of the Reefs" 2008 Fiji Campaign. She is a graduate of the University of the South Pacific with a Bachelor of Arts in Geography and Marine Affairs. She was also contracted to the Department of Environment as a Research Assistant for an Economic Analysis of the Rural Waste in the Province of Rewa from October 2005-October 2006. She also holds a Open Water Diver Certificates. She is involved in community workshops addressing the specifics of Fisheries Act (Legislation) and promoting sustainable resource management tools. She is also part of the Communications and Awareness Working Group of FLMMA Network. Margaret bring together the following core qualities that will support her doing an excellent job as Campaign Manager. These include: Deep understand of the LMMA network, partners and cultural traditions in Fiji. Strong academic background for a Pride Campaign Manager. Direct communications experience – both locally and in the region. Joint support from key government and non-governmental entities – in particular, FLMMA, Fisheries Department and the Institute of Applied Sciences. Bibliography 1. Fiji Facts n Figures: 1st July, 2008. Bureau of Statistics.www.statsfiji.gov.fj 2. Nair, V: Nov 2003.Fiji islands Marine Ecoregion Reconnaissance Report. WWF SPPO , Suva , Fiji.pg 15 3. Fong, S: 28th March, 2008. “IAS Macuata YMST Seminar Presentation.” 4. WWF SPPO.18th May, 2007.”Great Sea Reef Survey.”pgs 7-8 5. Meo, S. 3rd May, 2008. “ IAS CYMST Seminar Presentation”. 6. Singh, A.1997.”Customary Fishing Rights”.Unpublished paper. 7. WWF Eco-system based Project.2006.”Socio-Economic Baseline Survey of Qoliqoli Cokavata Areas-Districts of Mali,Dreketi, Sasa and Macuata”. WWF SPPO, Suva, Fiji, pg 4 8. (Erika J. Techera, “Customary law and community based conservation of marine areas in Fiji” (Paper presented to the Environmental Justice and Global Citizenship Conference, July 2007) 9. Fiji Meteorological Office. (http://www.met.gov.fj/climatefiji.html) 10. Nair, V, 2003. “Setting Priorities for Marine Conservation in Fiji Islands Marine Ecosystem (FIME).WWF South Pacific Program. 11. Vunisea, A. 2002. “Community based Marine resources management in Fiji: The Challenges” IN SPC Women In Fisheries Bulletin #11.