Limited information is available on artisanal and subsistence shark fisheries across the Pacific. The aim of this study was to investigate Fiji’s inshore fisheries which catch sharks. In January and February 2013, 253 semi-directive interviews were conducted in 117 villages and at local harbours on Viti Levu, Vanua Levu, Taveuni, Ovalau and a number of islands of the Mamanuca and Yasawa archipelagos. Of the 253 interviewees, 81.4% reported to presently catch sharks and 17.4% declared that they did not presently catch any sharks. Of the 206 fishers that reported to catch sharks, 18.4% targeted sharks and 81.6% caught sharks as bycatch. When targeted, primary use of sharks was for consumption or for sale. Sharks caught as bycatch were frequently released (69.6%), consumed (64.9%) or shared amongst the community (26.8%). Fishers’ identification based on an identification poster and DNA barcoding revealed that at least 12 species of elasmobranchs, 11 shark and one ray species (Rhynchobatus australiae) were caught. This study, which is the first focused exploration of the shark catch in Fiji’s inshore fisheries, suggests that the country’s artisanal shark fisheries are small but have the potential to develop into larger and possibly more targeted fisheries.
Compared to industrial fisheries, there has been a paucity of research on small-scale and artisanal fisheries until the past decade1. Artisanal fisheries provide an important source of food and employment, particularly in low-income countries2,3,4,5. In stark contrast to industrial fisheries, they are small-scale, typically subsistence in nature and fishing effort is often unmonitored by regional fishery authorities due to a shortage of trained personnel and/or equipment (i.e. patrol boats) or more generally, a lack of resources6,7,8. As a result, the catch composition and biological characteristics of artisanal landings are often unknown and data on the extent and fate of bycatch is lacking9.
Sharks are an important component of marine ecosystems and are becoming increasingly threatened by overfishing10. Fishing pressure on sharks comes from both industrial and artisanal fisheries, which either target sharks or catch them, sometimes in substantial quantities, as bycatch. Several studies have reported that threatened elasmobranch species are caught as bycatch in artisanal fisheries11,12,13. Bycatch retained is often also a valuable source of income and, in some instances, can be a highly desirable component of the catch14. Whilst research efforts tend to focus on quantifying shark catches, catch composition and bycatch rates in industrial fisheries15,16,17, similar data are typically lacking for artisanal fisheries18. However, in developing countries, these small-scale artisanal fisheries can account for a substantial proportion of the overall fisheries capture production19.
Limited data on artisanal shark fisheries are available, at least for certain areas and specific fisheries, for the Saudi Arabian Red Sea20, the United Arab Emirates21, Mexico22,23,24, Indonesia11,25, Madagascar26,27,28 and Oman29,30. These studies highlight the importance of sharks and their products to these artisanal fisheries as well as the general lack of accurate catch and size composition data from these fisheries. Evidence from other parts of the world suggests that artisanal fishers profit from the sale of shark fins31,32,33. Since artisanal fishers comprise more than 95% of the world’s fishers34, there is an urgent need for baseline data on the extent of shark fishing on a global scale, both as target and as bycatch, in artisanal fisheries. If such data are not available, population declines are likely to go undetected and local authorities will have inadequate information for drafting management plans and implementing them in a timely manner.
Accurate species identification is one of the most significant issues needing to be addressed when assessing artisanal fisheries, particularly when only parts of the animals, e.g. shark fins, are retained. In these instances, molecular analyses have proven to be a powerful tool to assist identification of elasmobranch species by fishers35,36. One of the most widely used gene markers for species identification is cytochrome c oxidase 1 (CO1)36. In a study on 210 Australasian chondrichthyans, the CO1 gene permitted discrimination of 99% of these species36.
In the Pacific, subsistence and artisanal fishing including for sharks date back thousands of years37 and are vital to food security38. Throughout Oceania, many subsistence and small-scale commercial fisheries for sharks exist, but catches are generally poorly documented39. Fiji is no exception. The country’s subsistence and artisanal inshore coral reef fisheries target a wide range of vertebrate and invertebrate species typically using hand line, spear, gillnet, seine net, hookah (diving with surface supplied air) and reef gleaning40,41. Coastal fisheries production provides extensive benefits to Fijian communities, including employment and nutrition40. Sharks are fished both within the artisanal sector and taken as bycatch in the industrial tuna fishery42,43. While it is known that sharks are taken in offshore waters and the country exports shark fins to the international market44, there is limited information on how many sharks and of what species are caught in Fiji’s inshore reef fisheries43,45. This initial study aimed to provide baseline information on Fiji’s artisanal fisheries which catch sharks and rays. In addition to interviews conducted with fishers, we also used molecular species identification tools to determine and verify what shark species are caught, both as target and as bycatch.
Study Area and Interviews
The study area included the majority of the coastline of the main islands of Viti Levu and Vanua Levu and Taveuni, Ovalau and islands of the Mamanuca and Yasawa archipelagos (Fig. 1a). Information was gathered by means of semi-directive interviews46,47 with fishers in 117 villages and at local harbours in Suva and Lautoka in January and February 2013. Suva is the capital and Lautoka the second largest city of Fiji. Lautoka is in the west and Suva on the southeast coast of the island of Viti Levu, Fiji’s largest island (Fig. 1a). Both cities have regular fish markets with multiple stands located close to the respective harbour where fish are landed. Since fishers were the only target group, an opportunistic sampling procedure was applied. Opportunistic sampling is a type of non-probability sampling where interviewees are selected based on naturally occurring groups48.
One of the authors (K.G.) visited all 117 villages and local harbours in Suva and Lautoka. She was accompanied by a male for interviews on Viti Levu, a female for village visits on Vanua Levu, Taveuni and Ovalau and another female individual for interviews with fishers on the Mamanuca and Yasawa archipelagos. All three local Fijian collaborators were both fluent in English and Fijian (Bauan dialect). English is an official language in Fiji and interviews were conducted in English and Bauan, a common dialect which is used throughout Fiji. As per village protocol, permission was requested from village chiefs to interview fishers in their respective village. Chiefs would then designate fishers that could be interviewed. If no fishers were in the village at the time of our visit we were allowed to interview their wives who are fishing on a regular basis themselves and/or accompany their husbands. Like in many Pacific Island countries, in Fiji, women are the major contributors of subsistence food production49. The major fishing grounds for women are typically areas closer to shore compared to men who fish mostly from boats in deeper waters and do underwater diving50. Five female interviewees were interviewed by K.G. together with the male Fijian collaborator. All other interviews with females (n = 6) were conducted by female collaborators.
Before individual fishers were asked specific open-ended questions outlined in a questionnaire (see Supplementary Information S1 online), a casual conversation was initiated by the Fijian collaborator. Each interview was then started with an explanation about the main purpose of the survey. To facilitate and standardize the procedure, questionnaires included dichotomous and pre-categorized questions on target and bycatch shark fisheries, catch composition, fishing equipment and use of sharks caught (see Supplementary Information S1 online). Fishers, both in the villages and at harbours in Suva and Lautoka, were asked to identify the species they catch or sell on the basis of an illustrative identification poster of the most common inshore elasmobranch species that occur in Fiji (http://fijisharkcount.com/the-activity/all-materials/id-posters/). We did not use and/or record traditional names for shark species and/or fishing gear. Anecdotal evidence was collected when possible regarding the trade in sharks and their products.
The study was conducted under a permit provided by the Fijian Ministry of Fisheries and Forests. All methods and protocols were approved by and carried out in accordance with instructions by the Principal Research Officer of the Department of Fisheries. Due to widespread illiteracy, a formal written consent was not possible for the majority of interviewees and therefore not pursued. Verbal consent was documented for all interviews in the respective questionnaire. All interviewed fishers collaborated on a voluntary basis and data confidentiality and anonymity of each interviewee was assured.
Tissue Sampling and DNA Barcode Protocol
Fishers who reported to target sharks and who had specimens with them at the time of the interview were asked whether a fin clip could be taken for species identification/verification. From this, a total of 21 tissue samples were collected from Momi (n = 2), Navakacoa (n = 4), Vitogo (n = 13) and Waya Levu (n = 2). In addition, seven muscle tissue samples were collected at local fish markets in Suva (n = 6) and Lautoka (n = 1) (Fig. 1a). In total 28 samples were collected for DNA barcoding from the catch of 11 interviewees. In each case, the interviewee was asked to identify the species based on morphology (Table 1).
Muscle and fin tissue were excised and preserved in 99% isopropanol. DNA was extracted following standard Phenol-Chloroform extraction (1x phenol, 1x phenol-chloroform-isoamylalcohol, 1x chloroform, adapted from Sambrook & Russel51), followed by precipitation of DNA with 0.1 volume 3M NaOAc and 3 volumes Ethanol52. Tissue samples were barcoded by sequencing the Cytochrome Oxidase I gene53. A 652-bp fragment from the 5’ region of the cox1 gene from mitochondrial DNA was PCR amplified using FastStart Taq from Roche and FishF1 and FishR153 (FishF1-5′TCAACCAACCACAAAGACATTGGCAC-3′, FishR1-5′TAGACTTCTGGGTGGCCAAAGAATCA-3′). PCR products were sequenced directly or cloned using TOPO TA Cloning Kit from Invitrogen and sequenced using BigDye Chemistry from Applied Biosystems on an ABI 3130xl sequencer (Applied Biosystems). Resulting sequences were identified by BLAST54 (http://blast.ncbi.nlm.nih.gov/Blast.cgi).
Characterization of Artisanal Shark Fisheries in Fiji
A total of 253 interviews (11 females, 242 males) were conducted with interviewees between 18 and 80 years old (response rate = 100%). A total of 166 interviewees (65.6%) reported to have been fishing for between one (n = 1) and >60 years (n = 1), with slightly less than half (49.4%) for more than 20 years (see Supplementary Information S2 online).
Fishers reported catching sharks at all of the sites surveyed (Fig. 1a, c). Of the 253 interviewees, 206 (81.4%) reported to presently catch sharks and 44 (17.4%) declared that they did not presently catch sharks (Fig. 1c, d). One interviewee said that he stopped catching sharks and two said that they plan to catch sharks in the near future. Of the 206 fishers that reported to catch sharks, 38 (18.4%) targeted sharks and 168 (81.6%) caught sharks as bycatch (Fig. 1e, f). While sharks were caught as bycatch throughout Fiji (Fig. 1f), targeted shark fisheries primarily occurred on Viti Levu with the exception of the south coast and the Yasawa Islands (Figs. 1e and 2).
When asked about specific fishing grounds, of the 206 interviewees that reported to catch sharks (targeted and bycatch), 73.8% (n = 152) mentioned coral reefs, 45.6% (n = 94) the coastal zone, 38.4% (n = 79) beyond coral reefs, 4.4% (n = 9) rivers, 3.4% (n = 7) estuaries and 0.5% (n =1) mangroves (note double entries are possible). When asked how many sharks they catch, the majority of fishers that catch sharks as bycatch reported to catch two or three sharks per week. In contrast, the majority of those that targeted sharks reported to catch three to six animals per person per week.
While fishers reported to catch sharks with a variety of common fishing gears, gillnets and light to intermediate strength hand lines were the main gear types for the fishers that reported to catch sharks as bycatch (Fig. 3). In contrast, heavy lines, drumlines and handspears or spearguns were the main gear used to target sharks (Fig. 3). According to interviewees, spears and spearguns are ideal for catching mid-sized reef sharks as they are relatively abundant on coral reefs, whereas drumlines with catch capacities of around 150 to 250 kg are ideal for catching large sharks. Fishers stated that the use of a single drumline can lead to catches of up to 15–30 sharks per week.
Sharks caught as bycatch were reported to be utilised differently than those from targeted shark fisheries. Sharks that were targeted were used for local consumption and/or to sell (meat and fins; a few fishers mentioned that they also sell teeth and jaws) (Fig. 4). Six fishers (15.8%) reported to target/kill sharks to defend themselves and/or their catch. Sharks caught as bycatch were most frequently released dead or alive (69.6%), consumed (64.9%) or shared amongst the community (26.8%) and to a lesser extent sold (note double entries are possible) (Fig. 4). Fishers that reported to sell shark fins reported values of up to 300 FJD (161 USD) per kg of self-dried shark fins (Fig. 5). If sold, the revenues from sharks caught as bycatch were typically much lower than that from targeted shark fisheries (Fig. 5).
A total of 99 (46.7%) of the fishers that reported to either not catch sharks or catch them only as bycatch provided reasons for not targeting sharks. The majority were not interested in sharks for reasons such as sharks are taboo or because of religious beliefs (23.2%), they are prohibited from catching sharks, i.e. “authority regulations by government or village chiefs” (15.2%), they are Indo-Fijians (12.1%) or because they are interested in bony fishes and not sharks (12.1%) (Table 2).
Fijian fishers reported to catch at least 12 species of elasmobranchs, consisting of 11 sharks and one ray species (Rhynchobatus australiae). The main sharks caught were blacktip reef sharks Carcharhinus melanopterus, whitetip reef sharks Triaenodon obesus, various hammerhead shark species Sphyrna spp., bull sharks Carcharhinus leucas and tiger sharks Galeocerdo cuvier (Table 3). Whilst T. obesus and C. melanopterus were caught in all areas surveyed, C. leucas were caught predominantly around southern Viti Levu and Sphyrna spp. predominantly in the south, west and north of Viti Levu (see Supplementary Information S3 online). Importantly, 45 (21.8%) of the interviewees reported to catch juvenile sharks of various species, primarily on Viti Levu (Table 3). Carcasses of juvenile sharks were frequently found at markets (see Supplementary Information S4 online).
During interviews and at fish markets, 28 tissue samples were collected from 11 interviewees for molecular identification and for verifying fishers’ identifications (Table 1). In 17 cases (60.7%), the interviewee identified the species correctly (Table 1). Sharks sampled in the fish market in Suva were landed by Chinese longliners and molecular barcoding results identified them as the shortfin mako Isurus oxyrinchus, oceanic whitetip shark Carcharhinus longimanus, scalloped hammerhead Sphyrna lewini and silky shark Carcharhinus falciformis; the mako being twice identified correctly, but the latter three species not identified correctly by the interviewee (Table 1). Although the two truly oceanic species, C. longimanus and I. oxyrinchus, are less likely to be encountered by artisanal fishers, they have been included in this study as they are entering the same market stream as the artisanal catches. One sample collected at the fish market in Lautoka was identified by the interviewee and confirmed with molecular identification as S. lewini (Table 1). Carcharhinus albimarginatus and C. falciformis were the most likely to be misidentified, while T. obesus was correctly identified in all cases (Table 1).
Anecdotal Evidence Recorded During the Survey
Many fishers do not target sharks as they lack the knowledge on how to catch and process them, where to sell them and generally what shark fins are used for. This pattern is supported by interviewees saying that fishers that catch sharks as bycatch often discard the whole animal at sea or the parts that are not edible (fins, head, guts) because they have no value for them. Some Fijian fishers stated that mostly Indian fishermen catch sharks to sell them at local markets.
Seven interviewees reported middlemen (mostly Chinese) coming to villages to encourage fishers to catch sharks and/or to collect shark fins. Although two of the interviewees reported that their interest in shark fins was relatively consistent in recent years, four interviewees noted that interest in shark fins increased in recent years. Three interviewees in villages on Viti Levu, Vanua Levu and Taveuni said that middlemen were primarily interested in bêche-de-mer (dried sea cucumbers), but switched to shark fins if bêche-de-mer was not available. The main hubs for the shark (fin) trade in Fiji were reported to be Lautoka (local traders) and Suva (high sea fleets).
Anecdotal reports also suggested that seafood companies offer fishing and SCUBA diving gear to fishers to catch sharks in some instances. Interviewees also reported to receive hooks and lines from relatives that work on commercial fishing vessels. However, we also collected anecdotal reports that there was increasing awareness regarding sharks and their role in coastal ecosystems due to awareness programmes run by authorities and non-governmental organizations.
This study presents the first focused exploration of the shark catch in Fiji’s artisanal coastal fisheries and provides information on fishing gear used and motivations to catch or release sharks. The interviews were a rich source of information confirming that various reef shark species are regularly caught in inshore fisheries. The underlying motivations for shark fishing were found to be dynamic. Whereas some fishers target sharks, the majority take them as bycatch. Sharks are mainly used for personal consumption, but there is some anecdotal evidence which suggests that the international shark fin trade is possibly exerting an increasing amount of pressure on local reef shark stocks.
Sharks are not considered an important source of food in many parts of Fiji, mainly due to traditional food taboos which possibly serve to protect against dangerous marine toxins39,55. However, the meat from several species is known to be eaten in areas where it is not taboo56. Our findings show that domestic consumption is the main use of sharks caught both in targeted and bycatch shark fisheries. Taking sharks for personal consumption and/or selling them at local markets may be the result of local demand for alternative food fishes due to the loss of traditional fish stocks39. Hence, Fijian shark fisheries can be regarded as subsistence in nature, i.e. sharks are harvested for domestic consumption.
Anecdotal evidence was found in this study that Fijian artisanal fishers only recently began targeting sharks to sell their fins to Chinese middlemen who visit the villages or directly to seafood companies situated in and around Lautoka and Suva. This is similar to bêche-de-mer fisheries where bêche-de-mer collected at localities close to urban centres are more frequently directly sold to middlemen or to export companies7. Results from the interviews conducted in this study showed that the bêche-de-mer and shark fin trades are linked, i.e. the demand for shark fins was reported to increase when less dried sea cucumbers are available. Asian traders looking for new species and/or fishing grounds have been recorded as having instigated new fisheries7. Hence, it is reasonable to assume that the artisanal shark fisheries in Fiji are using the well-established trade chains of the bêche-de-mer fisheries7.
The shark species most commonly caught were C. melanopterus and T. obesus, both of them listed as Near Threatened on the IUCN Red List57. Carcharhinus melanopterus and T. obesus show pronounced long-term site fidelity to specific small-scale coastal or reef habitats58,59,60,61. Hence, even low fishing pressure may remove these apex predators permanently from particular reefs which may result in cascading effects62 since typically the largest reef fish, i.e. sharks, are especially vulnerable63.
The only ray species reported to be caught and confirmed by DNA barcoding, in this study was R. australiae. This species has been assessed by The IUCN Red List of Threatened Species as Vulnerable57. Rhynchobatus spp. are considered to be among the most vulnerable elasmobranchs (sharks, skates and rays) due to their life-history characteristics and high-valued fins64,65. Prior to this study, the presence of this genus from Fiji was only based on anecdotal accounts, so the sample of R. australiae collected in Momi on the western coast of Viti Levu is the first confirmed record of this species in Fiji’s inshore waters (see Supplementary Information S5 online).
Every person we approached agreed to be interviewed. This is a strong indication that we had acceptance and trust of the community, hence increasing our confidence in the survey responses. Nevertheless, one limitation of our study is that correct species identification by local fishers is an ongoing issue in most developing countries. Whereas using an illustrative identification poster may be helpful for fishers to identify the species correctly, not all the species that occur in the respective area may be featured on the poster. This highlights the need for regional specific guides which provide images of species and list the key features which separate similar species. Our study acts as a baseline from which such regional guides can and should be produced to alleviate the problems with correct shark species identification in Fiji. Although we cannot be sure that all interviewees identified species correctly in all cases (Table 3), by verifying a number of identifications using DNA barcoding, we were able to determine that the majority of fishers identified species correctly, in particular the most common ones (Tables 1 and 3). Hence, we are confident that we have captured a reliable picture of what shark species are caught most commonly in Fiji’s artisanal shark fisheries.
In Fiji, marine resources are traditionally controlled by local social units, such as clans and villages66. The country recently decided against a National Shark Sanctuary which would have prohibited commercial shark fishing, import, export and sale of shark products67. Hence, no management measures for sharks exist at the national level and artisanal shark fisheries remain to be managed at the community level on the basis of a well-established marine tenure system68,69,70. There is evidence that this system has been destabilized due to the commercialization of fishing activities, for example, by turning previously restricted coastal resources into open-access fisheries71.
Our study provides data on the extent of Fiji’s artisanal shark fisheries. In general, they are small but could possibly develop into larger and potentially more targeted fisheries. This is supported by our finding that fins from targeted shark fisheries reportedly fetch higher prices compared to fins sold from sharks caught as bycatch (Fig. 5). Higher revenues from targeted sharks may motivate fishers to catch specifically larger sharks with more valuable fins using the respective gear. In order to obtain more data to allow informed fishery management decisions, Fiji’s fisheries authorities should consider establishing monitoring programmes for sharks. Such programmes would provide much-needed information on changes in shark abundance and catch and size composition through active monitoring, e.g. market surveys. These programmes would also need to include socioeconomic assessments of the fishery in order to identify social drivers that may lead to the unsustainable use of local shark stocks. Changes in trade of various fish products, such as shark fin, can be the main driver for changes in artisanal fisheries. For example, a buyer with good export linkages can offer more money for dried shark fins and thus drive fishers to increase targeting of sharks. These data can be used to assess the impacts and risks of these fisheries and to determine their level of sustainability. The fact that juvenile S. lewini are often sold in local fish markets (see Supplementary Information S4 online) confirms that, for at least some species, all life stages from neonatal to adult sharks are affected by artisanal shark fisheries.
Two species observed for sale in fish markets in Fiji (S. lewini and C. longimanus) are listed on Appendix II of CITES as they are at the risk of becoming threatened with extinction unless trade is closely controlled. Another species (I. oxyrinchus) is listed on Appendix II of the Convention on the Conservation of Migratory Species of Wild Animals (CMS) which Fiji has been a party to since 2013. Careful monitoring of these species is necessary to ensure that the way these species are exploited and traded complies with the relevant CITES and CMS obligations and should be considered as a driver to improving national and regional management of these important apex predators.
Lastly, future studies on Fiji’s inshore shark fisheries should also include interviews with traders, exporters or market sellers. These other sources higher up the fisheries value chain could provide valuable data on the shark fishery and trade. Such data could also help to validate the main findings of our study about trade and fishery trends. Understanding the social, cultural and economic drivers that are the reasons people fish for, sell and trade in sharks in the way they do is vital in planning conservation and management.
How to cite this article: Glaus, K. B. J. et al. Characteristics of the shark fisheries of Fiji. Sci. Rep. 5, 17556; doi: 10.1038/srep17556 (2015).
Purcell, S. W. & Pomeroy, R. S. Driving small-scale fisheries in developing countries. Front. Mar. Sci. 2, 44 (2015).
Allison, E. H. & Ellis, F. The livelihoods approach and management of small-scale fisheries. Mar. Policy 25, 377–388 (2001).
Defeo, O. & Castilla, J. C. More than one bag for the world fishery crisis and keys for co-management successes in selected artisanal Latin American shellfisheries. Rev. Fish. Biol. Fish. 15, 265–283 (2005).
Mora, C. et al. Management effectiveness of the world’s marine fisheries. PLoS Biol. 7, e1000131 (2009).
Kittinger, J. N. Human dimensions of small-scale and traditional fisheries in the Asia-Pacific region. Pac. Sci. 67, 315–325 (2013).
Lewison, R. L., Crowder, L. B., Read, A. J. & Freeman, S. A. Understanding impacts of fisheries bycatch on marine megafauna. Trends Ecol. Evol. 19, 598–604 (2004).
Purcell, S. W. et al. (2013) Sea cucumber fisheries: global analysis of stocks, management measures and drivers of overfishing. Fish Fish. 14, 34–59 (2013).
Ruddle, K. Tropical small-scale fisheries–some interwove issues. SPC Trad. Mar. Res. Manage. Knowl. Inf. Bull. 34, 36–44 (2014).
Moore, J. E. et al. An interview-based approach to assess marine mammal and sea turtle captures in artisanal fisheries. Biol. Conserv. 143, 795–805 (2010).
Dulvy, N. K. et al. Extinction risk and conservation of the world’s sharks and rays. eLife 3, e00590 (2014).
White, W. T. & Cavanagh, R. D. Whale shark landing in Indonesian artisanal shark and ray fisheries. Fish. Res. 84, 128–131 (2007).
Hossain, M. A. et al. Sawfish exploitation and status in Bangladesh. Aquatic Conserv: Mar. Fresh. Ecosyst. (in press).
Moore, A. B. M. A review of sawfishes (Pristidae) in the Arabian region: diversity, distribution and functional extinction of large and historically abundant marine vertebrates. Aquatic Conserv: Mar. Fresh. Ecosyst. 25, 656–677 (2015).
White, W. T., Giles, J., Dharmadi & Potter, I. C. Data on the bycatch fishery and reproductive biology of mobulid rays (Myliobatiformes) in Indonesia. Fish. Res. 82, 65–73 (2006).
Baum, J. K. & Myers, R. A. Shifting baselines and the decline of pelagic sharks in the Gulf of Mexico. Ecol. Lett. 7, 135–145 (2004).
Baum, J. K. & Blanchard, W. Inferring shark population trends from generalized linear mixed models of pelagic longline catch and effort data. Fish. Res. 102, 229–239 (2010).
Worm, B. et al. Global catches, exploitation rates and rebuilding options for sharks. Mar. Policy 40, 194–204 (2013).
Lack, M. & Meere, F. Pacific Islands Regional Plan of Action for Sharks: Guidance for Pacific Island Countries and Territories on the Conservation and Management of Sharks (2009) Available at: http://www.sprep.org/publications/regional-action-plan-for-sharks. (Accessed: 19th October 2015)
Béné, C. Small-scale fisheries: assessing their contribution to rural livelihoods in developing countries. FAO Fisheries Circular No. 1008 (2005). Available at: http://www.fao.org/3/a-j7551e.pdf. (Accessed: 19th October 2015)
Spaet, J. L. Y. & Berumen, M. L. Fish market surveys indicate unsustainable elasmobranch fisheries in the Saudi Arabian Red Sea. Fish. Res. 161, 356–364 (2015).
Jabado, R. W., Al Ghais, S. M., Hamza, W. & Henderson, A. C. The shark fishery in the United Arab Emirates: an interview based approach to assess the status of sharks. Aquatic Conserv.: Mar. Freshw. Ecosyst. (in press).
Bizzarro, J. J., Smith, W. D., Hueter, R. E. & Villavicencio-Garayzar, C. J. Activities and catch composition of artisanal elasmobranch fishing sites on the eastern coast of Baja California Sur, Mexico. Bull. Southern California Acad. Sci. 108, 137–151 (2009).
Bizzarro, J. J., Smith, W. D., Márquez-Farías, J. F., Tyminski, J. & Hueter, R. E. (2009) Temporal variation in the artisanal elasmobranch fishery of Sonora, Mexico. Fish. Res. 97, 103–117 (2009).
Pérez-Jiménez, J. C. et al. Artisanal shark fishery at the “Tres Marias” Islands and Isabel Island in the Central Mexican Pacific. J. Northw. Atl. Fish. Sci. 35, 333–343 (2005).
Blaber, S. J. M. et al. Elasmobranchs in southern Indonesian fisheries: the fisheries, the status of the stocks and management options. Rev. Fish Biol. Fisher. 19, 367–391 (2009).
McVean, A. R., Walker, R. C. J. & Fanning, E. The traditional shark fisheries of southwest Madagascar: A study in the Toliara region. Fish. Res. 82, 280–289 (2006).
Doukakis, P., Hanner, R., Shivji, M., Bartholomew, C. & Chapman, D. Applying genetic techniques to study remote shark fisheries in northeastern Madagascar. Mitochondr. DNA 22 Suppl 1, 15–20 (2011).
Robinson, L. & Sauer, W. H. H. A first description of the artisanal shark fishery in northern Madagascar: implications for management. Afr. J. Mar. Sci. 35, 9–15 (2013).
Henderson, A. C., McIlwain, J. L., Al-Oufi, H. S. & Al-Sheili, S. The Sultanate of Oman shark fishery: Species composition, seasonality and diversity. Fish. Res. 86, 159–168 (2007).
Henderson, A. C., McIlwain, J. L., Al-Oufi, H. S., Al-Sheile, S. & Al-Abri, N. Size distributions and sex ratios of sharks caught by Oman’s artisanal shark fishery. Afr. J. Mar. Sci. 31, 233–239 (2009).
Campredon, P. & Cuq, F. Artisanal fishing and coastal conservation in West Africa. J. Coastal Conserv. 7, 91–100 (2001).
Sabetian, A. & Foale, S. Evolution of the artisanal fisher: Case studies from Solomon Islands and Papua New Guinea. SPC Trad. Mar. Res. Manage. Knowl. Inf. Bull. 20, 3–10 (2006).
Alfaro-Shigueto, J. et al. Where small can have a large impact: Structure and characterization of small-scale fisheries in Peru. Fish. Res. 106, 8–17 (2010).
Pauly, D. Major trends in small-scale fisheries, with emphasis on developing countries and some implications for the social sciences. Marit. Stud. 4, 7−22 (2006).
Velez-Zuazo, X., Alfaro-Shigueto, J., Mangel, J., Papa, R. & Agnarrson, I. What barcode sequencing reveals about the shark fishery in Peru. Fish. Res. 161, 34–41 (2015).
Ward, R. D., Holmes, B. H., White, W. T. & Last, P. R. DNA barcoding Australasian chondrichthyans: results and potential uses in conservation. Mar. Freshwater Res. 59, 57–71 (2008).
Weisler, M. I. & McNiven, I. J. Four thousand years of western Torres Strait fishing in the Pacific-wide context. J. Archaeol. Sci: Rep. (in press).
Bell, J. D. et al. Pacific communities, fisheries, aquaculture and climate change: An introduction in Vulnerability of Tropical Pacific Fisheries and Aquaculture to Climate Change (eds. Bell, J. D., Johnson, J. E. & Hobday, A. J. ) 1–4 (Secretariat of the Pacific Community, 2011).
Juncker, M. K., Robert, M. & Clua, E. Coastal shark fisheries in the Pacific: a brief overview of current knowledge. (2006) Available at: http://www.spc.int/DigitalLibrary/Doc/FAME/Reports/CRISP/ENG_2006_Coastal_Shark_Fisheries_Pacific.pdf. (Accessed: 19th October 2015)
Gillett, R., Lewis, A. & Cartwright, I. Coastal fisheries in Fiji: Resources, issues and enhancement of the role of the Fisheries Department (2014) Available at: http://www.gillettprestonassociates.com/GPA%20%20Review%20of%20Fiji%20Coastal%20Fisheries.pdf. (Accessed: 19th October 2015)
Rawlinson, N., Milton, D., Blaber, S., Sesewa, A. & Sharma, S. A survey of the subsistence and artisanal fisheries in rural areas of Viti Levu, Fiji. ACIAR Monograph No. 35 (1995) Available at: http://aciar.gov.au/files/node/2217/mn35_pdf_78957.pdf. (Accessed: 19th October 2015)
Rasalato, E., Maginnity, V. & Brunnschweiler, J. M. Using local ecological knowledge to identify shark river habitats in Fiji (South Pacific). Environ. Conserv. 37, 90–97 (2010).
Swamy, K. Shark fisheries in Fiji: their management and future issues of concern in Case studies of the management of elasmobranch fisheries (ed. Shotton, R. ) 580–607. FAO Fisheries Technical Paper No. 378, Part 2 (1999).
Lack, M. & Sant, G. An overview of shark utilisation in the Coral Triangle region. TRAFFIC & WWF (2012). Available at: http://www.wwf.se/source.php/1496117/-Shark%20coral%20triangle%202012.pdf. (Accessed: 19th October 2015)
The, L. C. L., The, L. S. L., Starkhouse, B. & Sumaila, U. R. An overview of socio-economic and ecological perspectives of Fiji’s inshore reef fisheries. Mar. Policy 33, 807–817 (2009).
Huntington, H. P. Observations on the utility of the semi-directive interview for documenting traditional ecological knowledge. Arctic 51, 237–242 (1998).
Huntington, H. P. Using traditional ecological knowledge in science: methods and applications. Ecol. Appl. 10, 1270–1274 (2000).
Boxill, I., Chambers, C. & Wint, E. (1997) Introduction to social research: With applications to the Caribbean (Canoe Press University of The West Indies, Jamaica, 1997).
Chapman, M. D. Women’s fishing in Oceania. Hum. Ecol. 15, 267–288 (1987).
Ram-Bidesi, V. Recognizing the role of women in supporting marine stewardship in the Pacific islands. Mar. Policy 59, 1–8 (2015).
Sambrook, J. & Russel, D. W. Purification of nucleic acids by extraction with phenol: chloroform. Cold Spring Harb. Protoc. 10.1101/pdb.prot4455 (2006).
Green, M. J. & Sambrook, J. Molecular Cloning. A Laboratory Manual. (Cold Spring Harbour Laboratory Press, 2012).
Ward, R. D., Zemlak, T. S., Innes, B. H., Last, P. R. & Hebert, P. D. DNA barcoding Australia’s fish species. Philos. T. Roy. Soc. B 360, 1847–1857 (2005).
Madden, T. The BLAST sequence analysis tool In The NCBI Handbook (eds. McEntyre, J. & Ostell, J. ) Internet (National Center for Biotechnology Information, Bethesda, 2002). Available at: http://www.ncbi.nlm.nih.gov/books/NBK21097/. (Accessed: 19th October 2015)
Henrich, J. & Henrich, N. The evolution of cultural adaptions: Fijian food taboos protect against dangerous marine toxins. Proc. R. Soc. B 277, 3715–3724 (2010).
Vannuccini, S. Shark utilization, marketing and trade. FAO Fisheries Technical Paper No. 389 (1999).
IUCN, The IUCN Red List of Threatened Species, Version 2014.3. (2014) Available at: http://www.iucnredlist.org/ (Accessed: 19th October 2015)
Whitney, N. M., Pyle, R. L., Holland, K. N. & Barcz, J. T. Movements, reproductive seasonality and fisheries interactions in the whitetip reef shark (Triaenodon obesus) from community contributed photographs. Environ. Biol. Fish. 93, 121–136 (2012).
Speed, C. W. et al. Spatial and temporal movement patterns of a multi-species coastal reef shark aggregation. Mar. Ecol. Progr. Ser. 429, 261–275 (2011).
Chin, A., Tobin, A. J., Heupel, M. R. & Simpfendorfer, C. A. Population structure and residency patterns of the blacktip reef shark Carcharhinus melanopterus in turbid coastal environment. J. Fish. Biol. 82, 1192–1210 (2013).
Mourier, J. & Planes, S. Direct genetic evidence for reproductive philopatry and associated fine-scale migrations in female blacktip reef sharks (Carcharhinus melanopterus) in French Polynesia. Mol. Ecol. 22, 201–214 (2013).
Heithaus, M. R., Frid, A., Wirsing, A. J. & Worm, B. Predicting ecological consequences of marine top predator declines. Trends Ecol. Evol. 23, 202–210 (2008).
Fenner, D. Fishing down the largest coral reef fishes. Mar. Pollut. Bull. 84, 9–16 (2014).
White, W. T. & McAuley, R. (2003) Rhynchobatus australiae. The IUCN Red List of Threatened Species. Version 2014.3. (2003) Available at: www.iucnredlist.org. (Accessed: 19th October 2015)
Dudley, S. F. J. & Cavanagh, R. D. (2006) Rhynchobatus djiddensis. The IUCN Red List of Threatened Species. Version 2014.3. (2006) Available at: www.iucnredlist.org. (Accessed: 19th October 2015)
Cinner, J. Socioeconomic factors influencing customary marine tenure in the Indo-Pacific. Ecol. Soc. 10, 36 (2005).
Zylich, K., O’Meara, D., Jacquet, J., Harper, S. & Zeller, D. (2012) Reconstruction of marine fisheries catches for the Republic of Fiji (1950–2009) In Fisheries catch reconstructions: Islands, Part III. Fisheries Centre Research Reports 20(5) (eds Harper, S. et al. ) 25–36 (University of British Columbia, Vancouver).
Cooke, A. J., Polunin, N. V. C. & Moce, K. Comparative assessment of stakeholder management in traditional Fijian fishing-grounds. Environ. Conserv. 27, 291–299 (2000).
Muehlig-Hofmann, A. Traditional authority and community leadership: Key factors in community-based marine resource management and conservation. SPC Trad. Mar. Res. Manage. Knowl. Inf. Bull. 21, 31–44 (2007).
Ruddle, K. A guide to the literature and traditional community-based fishery management in Fiji. SPC Trad. Mar. Res. Manage. Knowl. Inf. Bull. 5, 7–15 (1995).
DeMers, A. & Kahui, V. An overview of Fiji’s fisheries development. Mar. Policy 36, 174–179 (2012).
Funding for this work was provided by the Shark Foundation Switzerland. One of us (W.T.W.) was supported by the National Research Collections Australia (CSIRO).We thank the staff of Beqa Adventure Divers for logistical support and help with field work.
The authors declare no competing financial interests.
Electronic supplementary material
About this article
Cite this article
Glaus, K., Adrian-Kalchhauser, I., Burkhardt-Holm, P. et al. Characteristics of the shark fisheries of Fiji. Sci Rep 5, 17556 (2015). https://doi.org/10.1038/srep17556
Same species, different prerequisites: investigating body condition and foraging success in young reef sharks between an atoll and an island system
Scientific Reports (2019)
Marine Policy (2019)
Ecology and Evolution (2018)
Subsistence harvesting by a small community does not substantially compromise coral reef fish assemblages
ICES Journal of Marine Science (2017)
Fisheries-independent surveys identify critical habitats for young scalloped hammerhead sharks (Sphyrna lewini) in the Rewa Delta, Fiji
Scientific Reports (2017)