Fiji
Fiji
Fiji’s extensive pastures of seagrass are a significant resource for green turtles in the central south Pacific region. Green turtles spend most of their adult life foraging in Fijian waters, occupying home ranges averaging 27 km2, taking only brief migrations (up to 1066km) to French Polynesia, American Samoa, Tonga and Cook Islands to nest6. The seagrass foraging areas in Fiji may well be providing foraging habitat for over half of the adult greens in the central South Pacific. This is possibly a consequence of lower availability of turtle food east of Fiji where most islands are small, steep and have limited areas suitable for seagrass. The need to protect such foraging areas is becoming widely recognized as a critical part of sea turtle conservation.
Six seagrass species and one subspecies are reported from the Fiji Islands: Halodule pinifolia, Halodule uninervis, Halophila ovalis,, Halophila decipiens Syringodium isoetifolium and Ruppia maritima7. Records of Thalassia hemprichii, Cymodocea serrulata, Halophila minor, and Halophila ovata credited to Fiji are possibly erroneous.
Seagrass meadows (veivutia) are found intertidal and in the shallow subtidal waters of protected and soft shores throughout Fiji. They play an important role in maintaining coastal water quality and are vital in supporting coastal marine communities and maintaining diverse flora and fauna.
Seagrasses have high biological productivity, are efficient recyclers of nutrients and support a large biomass of consumers, especially those of fisheries importance. It has been suggested that 400 square metres of seagrass (10 metres long and 40 metres wide) can support 2000 tonnes of fish a year. Fiji’s coastal fisheries productivity depends greatly on seagrass habitats. For example, juvenile Emperors live in the shallow, inshore areas such as seagrass and mangrove before they move to deeper water as adults 1. The ark shell although patchily distributed, are common in seagrass meadows of Laucala Bay2. It has been suggested that kaikoso recruits into sand/seagrass areas, though it can live in mud where the sediment is dynamic (due to floods and other causes) when older2.
Seagrass is also a nursery habitat for the witch prawn. Post-larvae settle into seagrass meadows on the intertidal mudflats in June and November of each year, after adults spawn in the deep channels of Laucala Bay3. The post-larvae grow in the nursery grounds for approximately 5 months, until as juveniles they move offshore into the adult stocks, eventually mating and spawning in October-November3. Seagrass are also important habitats for moci (mangrove prawns/shrimps – Palaemon sp.) and octopus (kuita, sulua – Octopus sp.)4,5. Seagrass is also one of the food items of rock lobsters (e.g., uraukula, uraudina, urautamata – Panulirus spp)4.
Fiji’s extensive pastures of seagrass are also a significant resource for green turtles in the central south Pacific region. Green turtles spend most of their adult life foraging in Fijian waters, occupying home ranges averaging 27 km2, taking only brief migrations (up to 1066km) to French Polynesia, American Samoa, Tonga and Cook Islands to nest6. The seagrass foraging areas in Fiji may well be providing foraging habitat for over half of the adult greens in the central South Pacific. This is possibly a consequence of lower availability of turtle food east of Fiji where most islands are small, steep and have limited areas suitable for seagrass. The need to protect such foraging areas is becoming widely recognized as a critical part of sea turtle conservation.
Six seagrass species and one subspecies are reported from the Fiji Islands: Halodule pinifolia, Halodule uninervis, Halophila ovalis,, Halophila decipiens Syringodium isoetifolium and Ruppia maritima7. Records of Thalassia hemprichii, Cymodocea serrulata, Halophila minor, and Halophila ovata credited to Fiji are possibly erroneous.
Halodule pinifolia is generally found in the high intertidal to upper subtidal areas of sheltered bay, reef platforms and in high energy locations. H. pinifolia often forms homogenous patches or occasionally intermixes with other seagrass species including H. uninervis7. They are easily distinguishable in the field by their much narrower blade size compared with that of H. uninervis (1 mm versus 4 mm)8. Waycott et al.10 suggested that H. pinifolia and H. uninervis are conspecific, recognising that the plasticity of blade size is attributed to local conditions. Nevertheless, in Fiji they are retained as separate entities, as there is no sufficient evidence from Fijian material to support this merger8.
Halodule uninervis is found from intertidal to 6m in sheltered or exposed coral reefs, in creeks and mangroves. H. uninervis often forms dense meadows at some sites, or is patchy and intermixed with other seagrass species (eg H. pinifolia, S. isoetifolium, or Halophila spp.)7.
Halophila ovalis is the most eurythermic of all seagrasses in Fiji and extends from the intertidal to 10-12m deep. First reported in Fiji in 1874 from Viti Levu, there are both bullate (blister or pucker-like) and smooth leaf forms7,11. The bullate form is recognized as a subspecies H. ovalis ssp. bullosa because it appears sufficiently distinct9. However the synonymy adopted here follows Waycott et al.10 who consider H. ovalis to be a complex of closely related entities whose leaves are highly plastic especially in relation to blade size, shape, colour, and texture12. The bullate forms have only been reported from Samoa, Tonga and the Fiji islands. H. ovalis forms dense meadows in some locations, but is frequently encountered in small patches. It tolerates a wide variety of substrata from fine muddy sand to coarse sand, mixed sandy-rubble or large boulders with sandy patches.
Halophila decipiens is a recent addition to the seagrass inventory in Fiji. It is no surprise that it occurs in Fiji, as the species is pan tropical and has been reported in New Caledonia and Tahiti from the mid-late 1800’s11. Globally, H. decipiens is a sciophilous species which occurs from the water surface to a depth of 85m (Cargados Carajos Shoals, Mascarene Islands in the Indian Ocean). In the Fiji Islands it occurs from 10–25 m depth and has only been found growing in the fine muddy/sandy substratum along the reef channels of the Great Sea Reef 8. The plants form sparse patches and grow to 40 mm tall. H. decipiens is distinguished from H. ovalis and its subspecies bullosa by the presence of marginal serrations and hairs on either side of the leaf blade.
Syringodium isoetifolium is usually found in the shallow subtidal areas (1–6 m depth), with some meadows are occasionally exposed during extreme low tide on reef flats. Earliest records are from 1926 in Suva Bay11. Syringodium is known to be more tolerant of oxidized substrata than other seagrass species and it has been reported that Syringodium will take over as a pioneer after a disturbance13 S. isoetifolium also has the ability to utilise a very high proportion of the available dissolved inorganic carbon compared to other seagrass species. Such an environment provides S. isoetifolium with a competitive advantage, especially when combined with disturbances that remove existing seagrass species.
Ruppia maritima only occurs in estuarine habitats in Viti Levu and is reported from brackish water pools or along the banks of the Rewa, Penang and Sigatoka Rivers7
A number of general parameters are critical to whether seagrass will occur along any stretch of coastline. These include physical parameters that regulate the physiological activity of seagrasses (temperature, salinity, waves, currents, depth, substrate and day length), natural phenomena that limit the photosynthetic activity of the plants (light, nutrients, epiphytes and diseases), and anthropogenic inputs that inhibit the access to available plant resources (nutrient and sediment loading). Various combinations of these parameters will permit, encourage or eliminate seagrass from a specific location. In Fiji, seagrasses are distributed throughout the Islands and local conditions may often determine which seagrass species are present.
Seagrass-Watch in Fiji
To provide an early warning of change, long-term monitoring has been established in Fiji as part of the Seagrass-Watch, Global Seagrass Observing Network (www.seagrasswatch.org). Establishing a network of monitoring sites in Fiji provides valuable information on temporal trends in the health status of seagrass meadows in the region and provides a tool for decision-makers in adopting protective measures. It encourages local communities to become involved in seagrass management and protection. Working with both scientists and local stakeholders, this approach is designed to draw attention to the many local anthropogenic impacts on seagrass meadows which degrade coastal ecosystems and decrease their yield of natural resources.
McKenzie, L.J. and Yoshida, R.L. (2020) Over a decade monitoring Fiji's seagrass condition demonstrates resilience to anthropogenic pressures and extreme climate events. Marine Pollution Bulletin 160111636. doi.org/10.1016/j.marpolbul.2020.111636 [8.5Mb] | |
McKenzie, L.J., Yoshida, R.L., Aini, J.W., Andréfouet, S., Colin, P.L., Cullen-Unsworth, L.C., Hughes, A.T., Payri, C.E., Rota, M., Shaw, C., Tsuda, R.T., Vuki, V.C. and Unsworth, R.K.F. (2021). Seagrass ecosystems of the Pacific Island Countries and Territories: a global bright spot. Marine Pollution Bulletin 167, 112308. doi.org/10.1016/j.marpolbul.2021.112308 |
Location
Cawaci (Ovalau Island)
Monitoring: ongoing, ad hoc
Principal watchers: Seagrass-Watch HQ
Occasional and past watchers: Masao Yoshida, Nicolette Yoshida, Shaun Ashley, Charlene Ashley, Jo Qalo, Kathey Foi, Evan Naqiolevu & Venoma Yoshida
Location: fringing reef flat in front of St John’s College
Site code: CW1, CW2
Issues: Sewage effluent, land runoff & limestone extraction
Comments: The fringing reef has large intertidal meadows of Halodule uninervis, Halodule pinifolia, Syringodium isoetifolium and Halophila ovalis ssp. bullosa. In recent years the reef has experienced blooms of green algae (seaweed) and physical disturbance from extraction activities. The fringing reef is popular at low tide with villagers fishing and gleaning.
CW2 is beside a small creek into which untreated effluent from the boys dormitories is discharged. The site is also adjacent to coral extraction activity by the Public Works Department
- Sites appear to be showing a typical season pattern of seagrass abundance (higher in late spring-summer than winter). Sites are similar in species composition and abundance.
- CW2 has generally higher abundance and greater canopy height than CW1
- CW1 showed a dramatic increase in abundance in mid 2003, which may have been a consequence of extraction activities on the reef flat which possibly released nutrients into the water column.
- When monitoring began, the abundance of epiphytes was significantly higher at CW2 than CW1, however, now both sites have relatively low epiphyte cover (<10%).
Seagrass cover, species composition and canopy height
Location
Denarau Island (Viti Levu)
Monitoring: ongoing, ad hoc
Principal watchers: Seagrass-Watch HQ
Location: On the intertidal flats of Denarau Island, Nadi, in front of Hilton Resort.
Site code: DN1
Issues: Sewage effluent, development and land runoff
Comments: The site was established on the intertidal flats of Denarau Island, Nadi, in 2007. The island, 684 arces, is located west of Nadi town. Denarau is a reclaimed mangrove island is connected to Viti Levu via a small causeway.
- meadow is comprised of Halodule pinifolia, Halophila ovalis and Syringodium isoetifolium
Seagrass cover, species composition and canopy height
Location
Nadroga Navosa (Viti Levu)
Monitoring: ceased, data archived
Principal watchers: Seagrass-Watch HQ
Occasional and past watchers: Alfred Ralifo
Location: On intertidal banks of lagoon separating Cuvu village and Shangri-la Fiji Resort
Site code: NN1, NN2
Issues: Sewage effluent, development and land runoff
Comments: Nadroga Navosa located on the southern coast of the main island of Viti Levu, 11 Km west of the town of Sigatoka. There are very large seagrass meadows in Cuvu Bay, but they are threatened by turbid flood waters from the Voua river. Monitoring sites were situated close to a locally managed marine protected area monitored by WWF and the Foundation for the Peoples of the South Pacific.
At low tide, villagers fish and glean the intertidal flats. Children from the adjacent village often catch fish in the shallow pools, which remained in the seagrass meadow at low tide. Evidence that the meadows were still productive even when in a poor condition.
- Monitoring has ceased at this location (last monitoring was June 2007).
- Seagrass abundance decreased significantly in 2004 and 2005, possibly a consequence of high turbidity and sedimentation which appeared to be impacting the meadow from nearby streams.
- At cessation of monitoring in 2007, seagrass abundance had increased and was not significantly different from 2003 abundances.
- The site was heavy bioturbated by shrimps (callianassids) and acorn worms over the monitoring period.
- Macro-algal and epiphyte cover remain low (<10%) over the monitoring period.
Seagrass cover, species composition and canopy height
Location
Natadola (Viti Levu)
Monitoring: ongoing, ad hoc
Principal watchers: Seagrass-Watch HQ
Location: On intertidal reef flat in front of Natadola beach
Site code: ND1
Issues: Sewage effluent, development and land runoff
Comments: Natadola Beach (about 40 minutes from Nadi) is one of Fiji’s best, for the sand, swimming, snorkelling and the sunsets
- meadow is comprised of Halodule uninervis, Halodule pinifolia and Halophila ovalis ssp bullosa.
- despite fluctuations between years, no long-term trend is evident in seagrass condition
- Macro Algae is very low and indicator of relatively low levels of elevated nutrients
- Epiphyte cover has seen fluctuations between the years.
Seagrass cover, species composition and canopy height
Location
Suva (Viti Levu)
Monitoring: ongoing, ad hoc
Principal watchers: Seagrass-Watch HQ
Location: on intertidal banks in front of Nasese Education Precinct and easily accessed by foot.
Site code: SV1, SV2
Issues: Sewage effluent, Industry pollution & land runoff
Comments: Suva is located on the south east coat of the main island of Viti Levu and has a population of approx 167,975 (1996 census). A significant part of the city centre, is built on reclaimed mangrove swamp.
Rapid population growth and urbanisation of the city and corridors has put increasing environmental pressure on the region. Environmental degradation is largely due to domestic waste and sewage disposal dumped in mangrove habitat and water ways. Industry in the area discharge their waste directly into rivers and coastal waters, which significantly reduces water quality in the near-shore waters around Suva. Often little or no regard is paid to the importance of mangroves and seagrasses in the marine food chain or the problem of leaching of pollutants during periods of high rainfall.
High concentrations of nutrients (sewage) also cause algal blooms that are destructive to the ecology of the harbour waters. A study undertaken by the University of the South Pacific indicated that the general water quality of Suva harbour gave cause for concern. Pollution is obviously effecting the biology in the area, as fish caught off Suva harbour sometimes have an oily, kerosene flavour, while marine life in the harbour has been degraded. Shellfish found in coastal areas of Suva absorb sewerage waste and the population of Suva has been advised not to eat the local shellfish because of the danger of hepatitis. Nevertheless, Suva harbour and Laucala Bay remain a major source of food for low-income residents (source www.unescap.org & www.sprep.org.ws).
- Seagrass cover is generally between 10 and 45%, and not significantly different in 2009 to 2006.
- A seasonal trend may be present (higher abundance in the earlier months of each year), however due to the paucity it cannot be confirmed.
- Canopy heights are similar at each site.
- Macro-algal abundance is relatively low at both sites and fluctuates greatly. There is insufficient data to identify any trends in epiphyte abundance.
- Seagrass cover is generally between 10 and 45%, and not significantly different in 2009 to 2006.
- A seasonal trend may be present (higher abundance in the earlier months of each year), however due to the paucity it cannot be confirmed.
- Four seagrass species are found at Nasese: Halodule uninervis, Halodule pinifolia, Halophila ovalis spp. bullosa, and Syringodium isoetifolium.
- Sites are dominated by either Halodule uninervis or Halodule pinifolia. The composition of Halophila ovalis spp. bullosa fluctuates and may be a seasonal response. Syringodium isoetifolium composition fluctuated over the monitoring period.
Seagrass cover, species composition and canopy height
Location
Tagaqe (Viti Levu)
Monitoring: ongoing, ad hoc
Principal watchers: Seagrass-Watch HQ
Location: On intertidal fringing reef in front of Hideaway Resort
Site code: TQ1
Issues: Sewage effluent & land runoff
Comments: Tagaqe is located, on the Coral Coast, approximately 130 kilometers (80 miles) west of the capital of Suva.
In the heart of the Coral Coast is Tagaqe village and the Ridges Resort, who are working together to preserve and regenerate the local coal reefs. Tagaqe village has designated part of the reef in front of Ridges Resort as “tabu” protected. This is a Marine Protected Area (MPA) to provide a safe environment for the coral and marine life to grow and flourish.
To help assess the condition of the reef ecosystem, Seagrass-Watch was granted permission to map the extent of seagrass resources within and adjacent to the tabu area in front of Hideaway Resort, and to establish a monitoring site. In early May 2006, Seagrass-Watch HQ scientists mapped 1.6 hectares of predominately Halodule pinifolia meadows and established a monitoring site. Just over 20% of the meadows were within the designated tabu area.
- no sampling has been conducted since June 2007
- insufficient data to determine seagrass condition
- Four seagrass species are found in the Seagrass-Watch monitoring site.
- The most noticeable feature of the seagrass condition within the site was the high amount of epiphyte cover on the leaves. High epiphyte can be a natural occurrence, however at some locations it can be an indicator of elevated water column nutrients.
Seagrass cover, species composition and canopy height
Location
Rotuma
Monitoring: ongoing, annual
Principal watchers:LäjeRotuma
Location: reef flat Maka Bay (Motusa)
Site code: RT1
Issues: Sewage effluent & land runoff
Comments: Rotuma, a volcanic island of approximately 43 sq. km, is located 465 km north of Fiji.
The LäjeRotuma Initiative established in late 2001, consists of young Rotumans residing in Fiji who wanted to give something back to their community and Rotuma. The name LäjeRotuma literally translates to “coral reefs Rotuma”. Due to the island’s isolation and small size, its marine and terrestrial resources are susceptible to over exploitation. The main aim of LäjeRotuma Initiative is to create awareness amongst Rotumans on the island about their natural surroundings, heritage, limited resources and how to protect and use these resources sustainably.
- Seagrass abundance appeared to decline in 2007 but increased back to 2005 and 2006 levels in 2008
- Syringodium isoetifolium is the only species of seagrass found in Rotuma.
- Seagrass meadow appears to be generally stable, an indication that the seagrass meadow is relatively healthy.
- There has also been a reduction in the percentage epiphytic algae and macroalgae in the seagrass meadow.
- The mean number of animals found on the seagrass meadow increased slightly from 2004 to 2005 and directly correlates to the increase in the seagrass cover.
- This seagrass meadow provides a lot of shellfish, fish and seaweed to the villages close by.