Reef Fish Aggregations in Sabah, East Malaysia. A report on stakeholder interviews conducted for the Society for the Conservation of Reef Fish Spawning Aggregations.
Tim Daw Dept. Geography, Politics & Sociology, University of Newcastle, Newcastle upon Tyne, NE1 7RU, UK [email protected]
Western Pacific Fisher Survey Series: Society for the Conservation of Reef Fish Aggregations. Volume 5 April 2004
Acknowledgements This study was entirely reliant on the cooperation and assistance of many individuals and organisations within Sabah. Particular thanks go to the many fishers, traders, divers, videographers and researchers who graciously shared their time and expertise during interviews. The study was conducted in conjunction with WWF Malaysia’s Sulu Sulawesi Marine Ecoregion programme. Robecca Jumin sponsored the research permit while Marcel Eging and Leonardo Daim contributed to surveys and assisted with translation. Sabah Fisheries Department were also instrumental for logistical, political and advisory support, particularly Rooney Biusing, Alfred Karom, Ruzlee Jumatin, Amla bin Emta, Talip Hassan, Abd Manaf Datu Unjung and Baram on Selakan. From UMS, thanks to Dr Annadel Cabanban for general support as well as field survey assistance in Banggi and to Leela Rajamani, Basrun Bin Kasim and Azlin for help with accommodation and boat transport in Banggi. Borneo Divers kindly provided accommodation and assistance for interviews on Mabul and Sipadan (thanks to Randy Davis). Thanks also to Tim Burns from Greenforce and Dr Nick Pilcher. Mohd Asri bin Barail was an excellent field assistant and translator for interviews in Banggi and Kudat. Yvonne Sadovy is thanked for advice and helpful comments on drafts of this report.
Contents Executive Summary .......................................................................................................1 1. Introduction............................................................................................................2 1.1. Coral Reefs of Sabah .....................................................................................2 1.2. Reef Fisheries of Sabah .................................................................................3 1.2.1. Composition of fishing communities in the areas surveyed. .................4 1.2.2. Management...........................................................................................4 1.3. Reef Fish Spawning Aggregations (FSAs) ....................................................4 1.4. The Society for the Conservation of Reef Fish Aggregations .......................5 2. Aims.......................................................................................................................5 3. Methodology ..........................................................................................................6 3.1. Use of Fishers’ Knowledge............................................................................6 3.2. Interviews with fishers...................................................................................6 3.2.1. Fisher interview method and identification of FSAs .............................6 3.2.2. Identification of FSA locations and timings ..........................................8 3.2.3. Indications of magnitude of aggregations..............................................8 3.2.4. Sampling ................................................................................................9 3.2.5. Practicalities of interviews.....................................................................9 3.2.6. Verification and assessment of reliability............................................10 3.3. Informal discussions ....................................................................................11 3.4. Interviews with divers..................................................................................11 3.4.1. Analysis and synthesis of interview information.................................12 3.5. Use of secondary data and reports ...............................................................13 3.6. Direct observations ......................................................................................13 4. Regional Summaries ............................................................................................14 4.1. Kota Kinabalu (KK).....................................................................................14 4.1.1. Background ..........................................................................................14 4.1.2. Work Conducted ..................................................................................14 4.1.3. Findings................................................................................................14 4.1.4. Potential Future Research and Partners ...............................................15 4.2. Kudat Area ...................................................................................................15 4.2.1. Background ..........................................................................................15 4.2.2. Work Conducted ..................................................................................16 4.2.3. Findings................................................................................................16 4.2.4. Potential Future Research and Partners ...............................................17 4.3. Banggi Area .................................................................................................17 4.3.1. Background ..........................................................................................17 4.3.2. Work Conducted ..................................................................................17 4.3.3. Findings................................................................................................18 4.3.4. Potential Future Research and Partners ...............................................18 4.4. Semporna Area.............................................................................................19 4.4.1. Background ..........................................................................................19 4.4.2. Work Conducted ..................................................................................19 4.4.3. Findings................................................................................................20 4.4.4. Potential Future Research and Partners ...............................................20 4.5. Lahad Datu...................................................................................................21 4.5.1. Background ..........................................................................................21 4.5.2. Work Conducted ..................................................................................21
4.5.3. Findings and Data Appraisal................................................................22 4.5.4. Potential Future Research and Partners ...............................................22 5. Overall Findings and Recommendations .............................................................23 5.1. Results..........................................................................................................23 5.1.1. Fisheries Statistics................................................................................23 5.1.2. Main species reported as aggregating in Sabah ...................................24 5.1.3. Seasonality of FSAs in Sabah ..............................................................24 5.1.4. Status of FSAs in Sabah.......................................................................25 5.1.5. Attitudes of fishers to conservation and aggregations .........................26 5.2. Research Recommendations ........................................................................27 5.3. Management Recommendations..................................................................28 6. References............................................................................................................30 Appendix I. List of People met and Contact Details................................................32 Appendix II. Itinerary............................................................................................37 Appendix III. Interview Schedule...........................................................................38 Appendix IV. Summaries of interviews by village.................................................41 Appendix V. Village locations ..............................................................................46 Appendix VI. Sample of Fisheries Department catch statistics..............................47 Appendix VII. Local vocabulary useful for FSA research or used in this report ....48 Appendix VIII. Local names of fish species collected during surveys .................49 Appendix IX. Plates ................................................................................................52
Executive Summary Spawning aggregations of reef fish are becomingly increasingly recognised as important for the sustainable management of reef fisheries. In E. Malaysia, where reef fish catches have been declining for several years, there was little information available on the existence of spawning aggregations or whether they are exploited by fisheries. In January 2004 Tim Daw was contracted by the Society for the Conservation of Reef Fish Aggregations (SCRFA) to conduct interviews with a variety of stakeholders (largely fishers) to investigate the existence, status and use of reef fish spawning aggregations (FSAs) within Sabah. Ninety-two interviews in the Kudat, Banggi, Semporna, Kota Kinabalu and Lahad Datu areas uncovered evidence of exploited spawning aggregations, mostly of serranids (groupers) including Plectropomus and Epinephelus species. Trends of catch per unit effort (CPUE) from the memories of fishers indicated that most of these aggregations had declined substantially and some had either ceased to exist or declined to such an extent that fishers no longer bothered to exploit them. Lyang Lyang in the Spratley Islands and Sipadan Island in the Semporna Region are exceptions due to the strict control of fishery activities which have allowed spawning aggregations of endangered maming (Cheilinus undulatus) to persist. Protection of Sabah’s remaining FSAs should be seen as an important priority for sustaining the valuable fishery for reef species. However, further research to determine and confirm the locations and times of FSAs and collaborative research and awareness-raising within local fishing communities are prerequisites to effective management of Sabah’s reef fish stocks.
1. Introduction 1.1.
Coral Reefs of Sabah
Sabah is one of two Malaysian states on the island of Borneo in the Southeast Asian Indo-Malay Archipelago. East Malaysia also includes the state of Sarawak to the south and the small Federal Territory of Labuan off the west coast of Sabah (Figure 1). The small Sultanate of Brunei lies on the coast between Sabah and Sarawak while the southern three-quarters of Borneo form the Indonesian region of Kalimantan. Sabah contains the largest concentration of coral reefs in Borneo due to the large river systems which preclude extensive coral growth along the coastlines of Sarawak and Kalimantan (Oakley et al. 2000). The southeast and northeast shores of Sabah and the Spratley islands in the South China Sea are most notable for coral reef development. Image generated from Reefbase GIS www.reefbase.org
S. China Sea Palawan Spratley Islands
P. Balabac P. Lyang Lyang
P. Banggi P. Malawali
- Coral reefs - Mangroves - Town/city
P. Cagayan Kudat
200 km P. Labuan
Proposed Sempona Islands Park
INDONESIA P. Sipadan (Malaysian)
Figure 1. Sabah, showing the main islands and areas visited during this survey. The Semporna area and Darvel Bay form part of a chain of reefs and islands which continue into the Philippine Sulu Archipelago and lie between the Sulu and Sulawesi Seas. Pulau Banggi and Pulau Balambangan, at the northern extent of Sabah lying between the Sulu and South China Seas have good reef development extending through a series of reefs and small islands south towards Sandakan, out into the Sulu Sea towards the Philippine island of Cagayan and North towards Balabac and Palawan in the Philippines. The 100 oceanic coral islands and reefs of the Spratley Archipelago in the central South China Sea are jointly claimed by Malaysia, China, the Philippines, Taiwan and Vietnam (Oakley et al. 2000). Malaysia has an established presence on the most accessible and well studied of these atolls, Lyang Lyang in the southern part of the group, in the form of a naval base and exclusive dive resort.
Sabah lies within a highly biodiverse region and coral surveys in northern Sabah and near Semporna have suggested that the reefs there should be included in the “coral triangle”, the heart of the World’s marine biodiversity (MCS; Fenner 2001). In a review of the status of the reefs of East Malaysia, Pilcher and Cabanban (2001) painted a general picture of decline as a result of destructive fishing with bombs and cyanide (Plate 3). Lyang Lyang and Sipadan were identified as exceptions, with high fish diversity and live coral cover.
Reef Fisheries of Sabah
Reef fisheries make an important contribution to the fisheries of Sabah and accounted for 10% of landings between 1980-1990 (Cabanban and Biusing 1999). Catches of demersal hook and line fisheries (those most relevant to most species highlighted in this report) in 1999 amounted to 17,849 tonnes according to Fisheries Department statistics (Biusing 2001). Reef fish landings are highest in Semporna, Tawau, Sandakan, Kudat and Kota Kinabalu (Cabanban and Biusing 1999). Fisheries for reef species are conducted by a range of vessels from small canoes paddled or powered by pump engines or outboards to larger inboard engine vessels (Plate 5) which may have a compressor on board or act as a mothership for small dugout canoes (Plate 7) or pump-boats in more distant operations. Handlines (pancing), bamboo, wire or plastic mesh traps (bubu, Plate 9), homemade bombs (bom), gill nets (pukat), sodium cyanide solutions (sujum) and fish corrals (kelong, Plate 8) are all widely used to catch reef species commercially and for subsistence while spears (panat) are used for subsistence fishing. The lucrative export trade in live reef fish (largely for Hong Kong) specifically targets reef dwelling groupers (Serranidae, Plate 1) and certain species of wrasse (Labridae, Plate 2) and snappers (Lutjanidae). Official statistics indicate that the live reef fish trade (LRFT) has been in Sabah since the mid 1980s (Biusing et al. 1999) although individual fishers in the Kudat region have reported selling live fish as early as the 1970s (Daw et al. 2002a). Blast and cyanide fishing are illegal in Malaysia but have been widely reported for schooling species and large piscivorous fishes respectively (Wood 1979; Oakley et al. 1999; Fisher 2000; Harding et al. 2000; Pilcher and Cabanban 2001; Daw et al. 2002a; Daw et al. 2002b). These have been blamed for declining reef condition and loss of coral cover (Plate 3) around Sabah (Pilcher and Cabanban 2001) and extremely low densities and a lack of reproductively mature adults of targeted species on all unprotected reefs throughout Sabah (Oakley et al. 1999) and in South-eastern Banggi (Daw et al. 2002b). Analysis of catches of coral reef fish families in Sabah by Cabanban and Biusing (1999) indicated more than a 50% decline in both yields and catch per unit effort (CPUE) from the 1980s until the early 1990s.
1.2.1. Composition of fishing communities in the areas
surveyed. In Northern Sabah, the local fishermen are comprised mainly of the Suluk, Ubian and Orang Sungai ethnic groups. Some transient fishermen and illegal immigrants from the Philippines also occur in this region, employed either as crewmembers of the commercial fishing fleet based in Kudat town or engaged in traditional fishing in the Banggi Group of islands. Fishermen in southeastern Sabah are comprised of local Orang Sungai, Suluk, Bugis and Bajau and transient fishers from the Philippines (Bajau Laut or Suluk). Fisheries in Kota Kinabalu and Tuaran on Sabah’s west coast are dominated by Bajaus and Ubians (Biusing 2001). All the fishing communities surveyed in this study were Muslim. 1.2.2. Management
The conservation, management and development of fisheries in Malaysia is governed by the federal Fisheries Act 1985 (revised 1993). This act has provisions for licensing, technical conservation measures, prohibition of destructive fishing gears and fishing zones defined by vessel size, engine power and method of fishing. The Act also contains provisions for the establishment of marine parks and reserves aimed at the conservation and rehabilitation of fish stocks and the environment. (http://agrolink.moa.my/dof/Regulation/Fisheries_Act/fisheries_act.html). Sabah Fisheries Department is responsible for developing and managing fisheries within Sabahan waters including licensing fishing vessels for specific gears (although it is acknowledged that not all small scale fishers have licences) monitoring landings, conducting research on target species and assisting the development of fisheries through gear, boat and engine distribution to fishing cooperatives, and research and development of aquaculture (including fish cage culture and seaweed farming). In an attempt to control effort, no new capture fishery licences have been issued since 20001. Dead fish landings are monitored in the main landing ports through a standardised sampling scheme and live reef fish trade is also monitored on a port by port basis (see section 5.1.1). Licences are issued for holding and export of live fish but as yet, no controls or limits have been placed on the trade.
Reef Fish Spawning Aggregations (FSAs)
Many of the valuable species targeted for the live and dead fish trade within Sabah are thought to aggregate at specific times and locations for the purpose of spawning. Due to their predictable nature and the unusual concentrations of fish present, these reef fish spawning aggregations (FSAs) present the opportunity for fishers to make extraordinary catches and have been traditionally targeted in many societies. During recent decades, increased commercial fishing pressure, efficient fisheries technology and extremely high market demand for certain species have pushed some of these species and their aggregations to decline with the possibility of local extinctions in extreme cases (Colin et al. 2003). Hence, careful management of FSAs is increasingly being recognized as important for the sustainability of reef fisheries. The call to action
Personal communication, Mr Manaf Datu Unjung, Head of Kudat Fisheries Office
adopted at the Second International Tropical Marine Eco-systems Management Symposium held in Manila in 2003, stated that: “Many commercially valuable reef fishes are particularly vulnerable to over-exploitation because they form spawning aggregations that are highly predictable in time and location … The evidence is unequivocal that spawning aggregations can be decimated rapidly by heavy fishing, resulting in serious declines in the fish populations ... Evidence is growing of aggregation depletions in SE Asia and the western Pacific…Fish spawning aggregations should be conserved, through robust management strategies … to ensure persistence of the populations that form aggregations, the integrity of reef ecosystems and the livelihoods and food supply of communities that depend on aggregating species.” Sustainable management of FSAs is generally limited by a lack of information on their location, timing, extent and exploitation status. This is particularly true in Sabah where local ecological knowledge of fishers is one of the only sources of information and a starting point for their study and management.
1.4. The Society for the Conservation of Reef Fish Aggregations The Society for the Conservation of Reef Fish Aggregations (SCRFA) was formed in 2000 to promote and facilitate scientifically informed conservation and management of FSAs. Since 2002, SCRFA has funded aggregation surveys in the western Pacific to identify management issues and potential actions on a country by country basis. The data is also collated in a database, which allows the global trends and patterns in aggregations to be assessed and public access to the information collected. The precise locations of aggregations are not released however, to avoid the possibility of accelerating their exploitation.
2. Aims The aim of this study was to compile a database on the reef fish aggregations of East Malaysia covering: • • • •
species, locations and seasonal timing of aggregations as well as the current and historical fishing activity including level of effort, gears used and type of exploitation. management of aggregation sites or management of any reef species currently in place or being planned planned or existing tourism associated with spawning aggregations cultural and general attitudes to conservation, as well as any perceived problems or misconceptions in respect of conservation and management.
This database was to be compiled through interviews with as wide a range of stakeholders as possible and consultation with available reports, statistics and existing research on FSAs. The fisheries department statistics or reports could not be used to
identify spawning periods of reef fishes or the presence of spawning aggregations (see section 5.1.1).
3. Methodology 3.1.
Use of Fishers’ Knowledge
The general crisis in World fish stocks (FAO 1998) has lead to more openness by many fisheries scientists towards new approaches to the assessment and management of fishery resources (Pitcher et al. 1998). Meanwhile, traditional and local ecological knowledge of resource users has been increasingly recognised as having the potential to inform attempts at sustainable management. For example, indigenous knowledge was recognised in the 1992 Convention on Biological Diversity (Berkes et al. 2000). Within fisheries science it has been suggested that fishers’ knowledge could play an important role by filling some of the gaps in the scientific understanding and management of fisheries, especially in the case of identifying FSAs and in the extensive but poorly studied expanses of tropical shallow water ecosystems (Johannes 1998; Neis and Felt 2000). Fishers’ knowledge can encompass various forms of information from hard facts and observations, to implicit understanding or perception of the marine ecosystem. The use of fishers’ knowledge can have advantages over conventional fisheries science in terms of cost effectiveness, efficiency, spatial resolution, length of time series and non-reliance on previously conceived hypotheses and models. Fishers’ knowledge can also complement more conventional scientific approaches providing basic data, a yardstick for comparison, hypotheses for subsequent investigation or a context for interpretation of data or trends observed by scientists. Fishers can also provide valuable knowledge about their own activities and likely responses to interventions and regulations. Bringing fishers’ expertise to bear on the design and implementation of fisheries management could ensure measures were appropriate, effective and acceptable to fishing communities due to their participation in the planning process. With regards to fisheries like the rapidly expanding live reef fish trade in relatively poorly studied areas of Sabah, fishers knowledge can be particularly useful due to the scarcity of conventional scientific information on stock condition and behaviour.
Interviews with fishers
Nearly all information collected during this study was obtained from interviewing stakeholders throughout Sabah between 7th and 30th January 2004. The main focus was placed on active fishers, but divemasters, fisheries officers and fish traders were also interviewed (Plates 11-14). Summaries of general fisheries information from these interviews is organised by village in Appendix IV. 3.2.1. Fisher interview method and identification of FSAs
Interviews generally comprised a brief introduction, questions about the fishing activities of the interviewee and then specific questions on the interviewee’s knowledge of spawning aggregations. To maximise the likelihood that any knowledge
of spawning aggregations would be related to the questions and be brought to light, several approaches were used. Fishers were asked in turn: • • • • • •
whether (and when) there was a season in which they could catch most reef fish whether they had ever seen or caught an unusually large group of one species whether they had caught any fish with eggs and which species whether they had ever seen more than one or two groupers or humphead wrasse together whether they knew of any pullak or mullak (bajau words for fish aggregations) and whether they knew how, when or where fish reproduced.
If any of these approaches yielded memories apparently of spawning aggregations, details of each were requested. Finally, questions were asked about general trends in catches, the occurrence of humphead wrasse (Cheilinus undulatus) and the interviewee’s opinions regarding the reasons for any declines in fish stocks. Interviewees often responded dari kecil (from when they were small) when asked when they started fishing. In this case the assumption was made that they started at age 15 and their years of experience was calculated as their age minus 15 years. The structure of the interview varied according to the circumstances. Most fisher interviews followed a planned schedule (Appendix III) although this was often shortened or edited if time was very limited or the interviewee appeared uncomfortable answering certain questions. For example, fishers who appeared to use illegal fishing gears like bombs or sodium cyanide were not probed on their fishing techniques unless they were obviously very trusting of the survey team. If time was limited or the interviewee was apparently unwilling to spend much time on the interview, questions would focus on their knowledge of aggregations as this was priority for this study. Most interviews took between 20 and 45 minutes. Most interviews were conducted in Malay although specific fishing information and fish names were often conferred using local Ubian or Bajau words and phrases. Tim Daw could speak elementary Malay sufficient to ask and understand most of the interview but in all cases, except those interviews towards the end of the study in Lahad Datu and Kota Kinabalu, a fluent Malay, Ubian or Bajau speaker was present to assist with probing or explaining more complicated questions and answers. Some specific vocabulary useful for FSA research in Sabah is included in Appendix VI and local fish names collected during the survey are listed in Appendix VII. Although individual interviews were preferred, situations often involved the team talking to groups of fishers. Curious observers often accumulated around the interviewer and onlookers often contributed to interviews. In Karakit on P. Banggi a meeting with interested fishers was organised through the president of the local fishing cooperative and the chief clerk of the Sub-District Office. For data collection purposes this was operated like a focus group meeting and was recorded on minidisc for later extraction of information.
3.2.2. Identification of FSA locations and timings
It was not possible during this trip to visit any locations to obtain GPS-derived positions. Positions were usually indicated by interviewees by the use of a familiar place name or on a marine chart of the area obtained from Sabah Marine Department. If the fisher used a name which was unclear or unknown, they were asked to indicate the position on a chart in more detail. Before fishers were asked to use the chart, the interviewers were careful to orient the chart correctly and indicate several well known features (islands, villages, obvious reefs etc) to allow the fishers to get a sense of the scale and the way the chart was drawn. Fishers generally did not have any problem relating to and understanding the charts, indicated by their consistent pointing out of known reefs in their correct locations. The Malay word batu translates as “rock” and the translation of coral is batu karang. However it is common for fishers to refer to coral as merely batu (as shown by use of the phrase batu hidup, “live rock”). Therefore interview responses describing the substrate at an aggregation site as batu were interpreted as meaning coral. Fishers referred to seasonal events according to the distinct monsoonal seasons (north wind and south wind) or naming specific months of the Gregorian calendar. The Islamic calendar is widely used in the communities interviewed. This was of limited use for describing seasonal trends (as it shifts each year relative to the Gregorian calendar) but, being a lunar calendar, was excellent for identifying synchrony between FSAs and the phases of the moon. Fishers were specifically asked which day of the Malay (Islamic) month aggregations occurred on. 3.2.3. Indications of magnitude of aggregations
Although fishers were asked how many fish they believed were in an aggregation, it was usually only diving fishers who could give an estimate of actual numbers. Where aggregations were in the form of many small groups of fish spread over a wide area, fishers would often state the number of fish in any one group. In some cases this created a discrepancy between one interview which reported a small number of fish (per group) and others which reported very high numbers of fish in an entire aggregation. Catch per unit effort (CPUE) was normally used as a relative indicator of fish density at aggregations (and as an indicator of general fish abundance during times when FSAs did not occur). Catches were related in terms of numbers or weight of fish. In the case of rare or valuable species like those used for the live fish trade, fishers often referred to individual numbers (ekor, literally meaning “tails”). When relating large numbers they would typically refer to the number of kilograms or full ice boxes (pikul). One pikul was taken to be equivalent to 100 kg. The old Chinese unit of katis (0.5 kg) was occasionally used for older memories of catches. Sometimes extremely large catches were remembered in terms of how much effort was required to fill a whole boat. Indications of effort varied widely from interview to interview according to what seemed most simple and appropriate in each situation. Where possible effort included 8
a measure of numbers of fishers, time period and fishing method (e.g. one boat with 3 handline fishers over one week). Emphasis was placed on trying to establish a constant measure of effort to allow comparison through the fishers’ memories rather than an absolute CPUE figure which could be compared between interviews. Comparing CPUE between interviews may be problematic due to the different way in which fishers integrate their naturally fluctuating catches. For example, one fisher may give a maximum value saying, “One a lucky day I could catch up to…” when another, experiencing the same catch rates, might give a lower figure to reflect more of an average catch. The use of CPUE measures as absolute measures to be compared between interviews also has the problem of being susceptible to subtle differences in the skill, commitment, typical fishing pattern and technique of individual fishers. 3.2.4. Sampling
Logistical or security concerns often limited the team to one-day trips to a particular village or island. In this event interviewees had to be selected opportunistically amongst those fishers who were at home at the time. Each village visit began by seeking out the Ketua Kampong (village headman), if available, the JKKK (chair of the security and development committee, Jawatankuasa Kemajuan dan Keselamatan Kampung) or the next most senior member of the community in order to explain the purpose of the visit, ask permission to conduct surveys and request recommendations of knowledgeable fishers who would be good to interview. The Ketua Kampong was himself often one of the most senior fishers and thus supplied the first interview. Personal contacts of the survey team or fishers who had been cooperative with previous investigations were sought out, especially in communities in which cooperation was impeded by fear of authorities or suspicion of the team’s activities. No attempt was made to obtain a representative sample of any of the communities as the sample sizes were inevitably too small to achieve this and the objective was to obtain as much reliable information as possible on spawning aggregations within the limited time available. 3.2.5. Practicalities of interviews
Fieldwork was occasionally constrained by security concerns in the light of recent kidnappings of both tourists and locals from islands and communities on the east coast of Sabah by guerrillas from the Philippines and occasional incidences of piracy in northern Sabah. The survey team generally returned to a larger population centre each night. In the Banggi region (where Tim Daw had spent 1.5 years working previously), Sabahan authorities have recently increased their efforts to control illegal fishing activities (particularly blast fishing) and remove people who do not have official Malaysian identity cards. The frequency of operations aiming to arrest illegal immigrants and dismantle their dwellings and the enforcement of a ban on the use of the ubiquitous pump-boats (a widely used wooden canoe of varying sizes powered by one or more water-pump engines) seemed to have led to a climate of fear and suspicion of outsiders and officials, which in some cases hampered attempts to interview fishers. If interviewees were obviously uncomfortable, efforts were made to direct the interview away from fishing techniques used and to emphasise the purely
biological nature of the study and the survey team’s independence from Sabah Fisheries Department. In some cases only first names or no names were asked. 3.2.6. Verification and assessment of reliability
A major constraint of the use of fishers’ knowledge is the difficulty of assessing the reliability and accuracy of information collected. Data collected during this study are therefore subject to an unknown level of errors and inaccuracies. Potential reasons for these errors are listed below, roughly in order of their significance as perceived from the experience of conducting the interviews. Potential Sources of error 1. Incorrect recollections or confusion between different memories/experiences or between different species 2. Purposefully lying specifically to disguise illegal activities (although this would only affect responses to questions about fisheries). 3. General reluctance to cooperate with interview as a result of suspicion/fear of the team’s affiliation and motives 4. Misunderstanding in the communication of either the questions or the answers as a result of translation issues. 5. Confusion, or misinterpretation of observations made 6. Secrecy about sites and timings to maintain exclusive access to aggregations2 7. Optimistic assessments of the health of stocks to discourage management controls being imposed Surprisingly perhaps, the last two problems did not appear to be the most significant even though they were most anticipated. When a fisher had information on more than one aggregation, it was often difficult (both in the memory of the fisher and in the course of the interview) to clearly distinguish which parameters related to which aggregation. Every attempt was made to make clear distinctions between different aggregations but only the most patient fishers were willing or able to focus on the tedious repetition of the same detailed questions for each aggregation separately. Fishers would sometimes respond that the details were the same for all the aggregations while others would constantly refocus on different aggregations perhaps indicating the difficulty of remembering specific information about similar aggregations. Naturally, this was particularly problematic when fishers were talking about aggregations that had occurred or been observed long ago and between different aggregations of the same species.
It was not felt that this was as important as the first 5 error sources because of the way in which fishers freely spoke of aggregations when they knew them. They would often nonchalantly state that “everyone knows them” when asked how they learnt about an aggregation and state that many boats from other communities would often fish the aggregation. Both these points suggest that the “secret was out” so that withholding information from the survey team in order to protect exclusive knowledge and access to aggregations would have been futile. A small number of interviewees did say that they didn’t share information on aggregations with other fishers but it would have been clear that the survey team was not likely to come back and compete with them in their fishery. Nor would it have been likely for competing fishers to read the scientific report of the team.
A standard practise to assist with verification of information obtained from stakeholders is to ask “test questions”, the answers to which are already known by the investigator (Johannes 1981; Colin et al. 2003). This technique was found to be somewhat problematic in practice for the following reasons: •
Fishers may have a good knowledge of one aspect but not of another. For example, many fishers believed that groupers gave birth through their mouths. Although this is not compatible with scientific understanding of grouper reproductive biology, it does not devalue their memories of times or locations where they observed aggregations. Interviewees may incorrectly answer some questions in order to disguise illegal methods but be honest about others. For example a fisher may claim to catch mostly maming (Cheilinus undulatus) using hook and line. This is known to be unlikely from interviews and experience in the region but would not necessarily mean that other aspects of the interview would be unreliable.
Thus, it was not possible to use one individual test question to assess the accuracy of an interview, general impressions were made from all answers given along with the consistency of answers, the team’s familiarity with the interviewee, and a subjective impression of the interviewee’s attitude and body language. These impressions were often checked between members of the survey team for agreement. The reliability of each interview was then summarised on a three point scale as Good, Medium or Poor and further notes were made on the interview where necessary.
During the course of the survey, conversations were held with many different individuals and sometimes relevant comments or stories would be related in the course of conversation. It was not always possible to formally interview these individuals but the comments and any further details were noted down as soon as possible.
Interviews with divers
Two days were spent interviewing divemasters and instructors on resorts in the Semporna region. The interview format was similar to that used for fishers covering the career history and usual dive sites and frequency of diving of the diver before focussing on eliciting any details of potential spawning aggregations they had witnessed. Photographers were generally more useful than Divemasters as they were looking out for unusual footage rather than taking guests round usual sights. Interviews with divers were generally conducted in English. On Sipadan, divers tend to always dive at the same time of day and follow the sun around the island. Therefore they are on the east side in the morning and the west in the afternoon and usually dive at 08:30, 10:30 and 15:30. They would, therefore, miss any spawning activity which did not occur at these places and times. Night dives are only conducted off the Drop Off on the northeast side of the island.
3.4.1. Analysis and synthesis of interview information
Following the fieldwork, information from all interviews was entered into a hierarchically structured Access database. Each interview constituted a record with personal details and notes on the interviewees, their typical fishing behaviour, opinions on the status of stocks and the reasons for any declines and notes on the circumstances and perceived reliability of each interview. These were linked to information on individual aggregations from each survey which constituted single records stored in a separate table along with coordinates of aggregation locations (to the nearest minute of latitude and longitude) read from the charts used in interviews. Individual aggregation records were assessed and grouped by location and species in order to identify those which appeared to relate to the same aggregation. These cases were then agglomerated into a single aggregation record in a separate table. In the event of disagreement on aggregation details between interviews, responses were usually summed non-exclusively rather than discarding the details from one interview in preference for another. For example, if one interviewee claimed that an aggregation occurred from February till April while another claimed March till July, the agglomerated record would be entered as February till July. If contributing records directly contradicted each other, the interview with the highest confidence rating or the most information in other fields would be used. Finally these aggregation records had to be disaggregated by species to create individual species/aggregation records which were compatible with the SCRFA format (Figure 2). Fields which related individually to one species (for example, fishers sometimes reported different timing of aggregation for different species) were edited at this stage to try to ensure that parameters which had been stated for one species were not inherited by all species present at that aggregation A qualitative assessment was made of the likelihood that any individual species presence at an aggregation genuinely represented a spawning aggregation (very likely, maybe, none) based on the quality and number of interviews relating the information the species involved and signs of spawning related by the fishers. Only those records that were deemed very likely to represent spawning were entered into the SCRFA database. Each aggregation record was categorised according to relative measures of CPUE (catch per unit effort) through time as Stable, Moderate Decline (<50% decline in CPUE), Severe decline (>50% reduction in CPUE), Extinct (when fishers had actually claimed that the aggregation no longer occurred) or Unknown.
Individual RFAIndividual records RFAIndividual records RFAIndividual records RFA record
Individual RFAIndividual records RFAIndividual records RFA record
Individual RFA record
Individual RFA record
Individual RFAIndividual records RFAIndividual records RFA record
Individual RFAIndividual records RFA record
Individual RFAIndividual records RFA record
Agglomerated RFA record
Agglomerated RFA record
Agglomerated RFA record
Agglomerated RFA record
Individual species RFA Individual Individual record speciesforRFA species RFA SCRFA record for record for database SCRFA SCRFA database database
Individual species RFA record for SCRFA database
Individual Individual species RFA species RFA record for record for SCRFA SCRFA database database
Individual species RFA record for SCRFA database
Figure 2. Responses from individual interviews had to be disaggregated, sorted and agglomerated into different RFAs and finally disaggregated by species to generate records for the SCRFA database.
Use of secondary data and reports
Official statistics collected by the Sabah Fisheries Department were examined and interviews were held with data collectors, regional fisheries officers and Fisheries Department research staff to understand and appraise the available data with regards to its potential use for identifying the targeting of spawning aggregations.
On one occasion the opportunity was taken to make direct observations, using SCUBA, of a group of maming (Cheilinus undulatus) which had been observed by divemasters. Video equipment was not available at such short notice so notes documenting the behaviour of the fish were made immediately after the dive and
following corroboration with the dive buddy’s memories. A number of still photographs were taken.
4. Regional Summaries 4.1.
Kota Kinabalu (KK)
Although there are limited reefs in the KK immediate area it is the base port for several vessels which fish in the Malaysian South China Sea. As the capital and first city of Sabah it also has the headquarters for the State Fisheries Department, several fish exporters and traders and WWF Malaysia’s Sabah office. There were 551 traditional fishers registered in KK in 2000 and demersal hook and line landings in 1999 amounted to 979 tonnes. 4.1.2. Work Conducted
On arrival in KK, meetings were arranged with WWF Malaysia’s marine team in Sabah, the Director, Deputy Director and senior staff of Sabah Fisheries Department, Dr Annadel Cabanban from the University Malaysia Sabah (UMS) and Dr Nicolas Pilcher from the Marine Research Foundation. The SCRFA survey was introduced and the opportunity was taken to request relevant data and reports, solicit contacts and generally discuss the status of reef fisheries and spawning aggregations in Sabah. Arrangements were made with WWF for collaboration with their field officers while conducting surveys in the Kudat and Semporna regions. Towards the end of the project a meeting was also held with staff of the Research Division of the Fisheries Department to discuss the survey, fisheries statistics and potential future research into reef fish reproductive biology. A limited number of fishers and traders were interviewed while in KK but this activity was constrained by the timing (following Chinese New Year), which led to the absence of many traders and key contacts within the Fisheries Department. Experienced underwater photographers and divers were also interviewed opportunistically about any observations or memories of aggregation behaviour. 4.1.3. Findings
It appears that several live fish trade vessels operating in the Spratley Islands, Labuan, Mantanani and off the coast of Sarawak are based in KK. They sell their catches to nearby holding facilities by Pulau Gaya or in Tuaran. Several sources told of these vessels making large single-species catches of up to 3-4 tonnes suggesting that they target (or at least inadvertently encounter) reef fish aggregations These are probably some of the most significant aggregations in Sabahan waters due to their remoteness and the large areas of reefs available.
However despite the expansive and remote nature of these reefs, declines have been evident during the 1990s with one aggregation apparently no longer worth fishing at. These findings are necessarily preliminary due to the small number of interviews conducted in KK. However, information relating to the existence of large aggregations in the Spratley Islands came from many different sources. The atoll of Lyang Lyang is protected from commercial fishing by the Naval Base there. Divers and scientists have observed both maming (Cheilinus undulatus) and pamantan (Plectropomus laevis) aggregations around this island, which presumably experience exceptionally low levels of exploitation.3 4.1.4. Potential Future Research and Partners
The vast area covered by KK fleets in the S. China Sea coupled with several reports of significant aggregations warrant further investigation. More interviews with vessel captains and owners would be worthwhile and large catches may be detectable in records of individual operations. Mr Chio Fui Lin of the Sabah Fisheries Department Marine Branch has a good knowledge of these operations and familiarity with the vessel owners. During the meeting in KK he discussed the possibility of observers (perhaps staff of Greenforce) accompanying some of the relevant boats to document the aggregations. WWF Malaysia are actively studying the live fish trade as part of their programme “Understanding the Live Reef Fish Trade in Sabah” under the SuluSulawesi Marine Ecoregion initiative and already have some contact with traders operating from Tuaran. Live fish from KK and Kudat based operations are exported by air from Kota Kinabalu, generating fairly detailed export records (licences are required for export) which are due to be analysed (for trends in maming, Cheilinus undulatus, exports initially) by Rooney Biusing of the Fisheries Department. Sabah’s first marine park, Tunku Abdul Rahman Park is based around the islands close to Kota Kinabalu and is managed by Sabah Parks. It is unlikely that major spawning aggregations currently exist in this area as mature carnivorous fish have been eradicated from the area by artisanal fishing, and habitat condition (live coral cover) has declined significantly (Pilcher and Cabanban 2001).
Kudat is the most northern major town in Sabah and the administrative centre for a district which includes the Kudat peninsula, P. Banggi and surrounding islands. This makes it a natural centre for the exploitation and trading of marine resources from Banggi and even the Philippine islands around Balabac and Cagayan. Live and dead fish from small scale fishers in the islands are transported to Kudat for sale, while many larger Kudat-based vessels fish throughout the surrounding islands and reefs from the South China to Sulu Sea and sometimes into Philippine waters (Daw et al. 3
Steve Oakley, Pers comm.
2002a; Cooke 2003). Many fishing communities around Kudat are composed of recent migrants from the islands (Cooke 2003) who often maintain links with friends and relatives on their original islands. Kudat district had 1,531 registered traditional fishers in 2000. Fisheries statistics indicate that the hook and line catch of demersal fishes for the district was 4,800 tonnes in 1999 (Biusing 2001). Seventy tonnes of live fish were reportedly traded through Kudat in 2001 (official Fisheries Department statistics) but this may be a considerable underestimate (Daw et al. 2002a). Workers and traders in the live fish trade during this survey indicated that volumes had dropped considerably during that time due to declining catches. 4.2.2. Work Conducted
Meetings were held with Mr Abd. Manaf Datu Unjung, the head of the Kudat Fisheries office, Mr Chin, who is largely responsible for monitoring the live fish trade, and Mr Adnan Amna, who is responsible for collection of landings data. Two live fish traders, Mr Ho and Mr Stephen were interviewed about their feelings about fish aggregations in the area and any other observations from their perspective that were relevant to the study (Plate 13). Two strategies were used to meet fishers in Kudat to conduct interviews. Captains of vessels delivering fish to the live-fish cages (which in Kudat are collected together along two side-by-side jetties, Plate 6) or moored up at the main wet-fish quay were asked for interviews on the quay, in the nearby cafe or on their vessel. This strategy sampled local fishers as well as fishers from further afield who came to Kudat to sell fish and/or collect supplies. In addition, fishers were sought in their homes in the Kudat suburb of Tanjung Kapor, where it was known that many fishers lived. Individuals recommended by other interviewees were sought out in their homes and people in the community were also simply asked where vessel captains lived. The UK volunteer-driven NGO Greenforce has a project in Sabah, which recently moved from Banggi to a base on the West Coast of the Kudat peninsula. A short visit was made to the camp to meet the scientific staff and discuss the SCRFA project and how their research could contribute. 4.2.3. Findings
Aggregation sites suggested by the Kudat interviews ranged from the Spratley islands to a large area of reefs called “Herot” east of P. Jambongan. More than half of the cited aggregations related to Plectropomus species, perhaps reflecting the predominance of hook and line fisheries for the live fish trade which target these species. Interviews also collected aggregation records from in the South China Sea and Banggi (described in sections 4.1 and 4.3 respectively). The remoteness and complexity of the Herot reef system and lack of well-known islands and communities made it impossible to pinpoint individual aggregations. Thus information on aggregations were more in the form of general descriptions of the area. 16
Accompanying vessels to get GPS locations would be necessary to identify individual aggregations. 4.2.4. Potential Future Research and Partners
Sabah fisheries department have a branch based in Kudat who were collaborative and interested in the survey but have limited resources to conduct additional research or monitoring. WWF has no permanent presence in Kudat but have an interest in the region through their Sulu-Sulawesi Marine Ecoregion Project. Mr Leonardo Daim is the officer largely responsible for marine activities in Kudat and Banggi and is familiar with many of the fishers and traders in the area. Greenforce have two scientific staff, logistical facilities and trained volunteers to conduct reef surveys along the west coast of the Kudat Peninsula and possibly further a field in collaboration with the Fisheries Department. During the survey, the chief scientist on the camp was Mr Tim Burns, although he is due to hand over to a successor in early 2004. They also regularly visit Kudat fish market and thus are in a position to observe seasonal trends or peaks of abundance of reef species. The constant supply of live and dead fish to Kudat from the outlying regions of Banggi and beyond could be used to cost-effectively sample for studies of seasonal patterns of reproductive behaviour in the main species (e.g. Plectropomus leopardus). If coupled with detailed interviews and perhaps even GPS monitoring of the activities of trusted fishers, a picture could be built up of spawning times and areas.
The Pulau Banggi region lies to the north of Sabah between Borneo and the Philippine islands of Balabac and Palawan and between the basins of the Sulu and South China seas. Pulau Banggi is the largest island in Malaysia and is surrounded by approximately 70 other islands including 33 that are inhabited (Biusing 2001). The total area of the Banggi group of islands is 270 square miles. Despite the size of the Banggi area, it remains poorly developed economically with most of the communities relying on exploitation of coastal and marine resources including selling live and dead fish, seaweed farming and mangrove cutting (Cooke 2003). 4.3.2. Work Conducted
From a base at the UMS seaweed culture project house in Karakit, interviews were conducted in the communities of Karakit, Lok Tohog, Lumais, Padang and Kobong Laut on P. Banggi itself, Tanjung Malawali on P. Malawali, Batu Siri on P. Balambangan and Sibogo near P. Bankawan (see Appendix V, Plates 11, 17 and 18). A focus group was organised with the aid of the local government chief clerk and the local fishermen’s cooperative in Karakit (Plate 10) and an extensive discussion was 17
held with the village headman of Tg. Malawali. All interviews were assisted by Mohd Asri bin Barail, a Bajau Ubian resident from Karakit who had contributed to previous survey work in the area. Mr Leonardo Daim from WWF Malaysia and Dr Annadel Cabanban from the Borneo Marine Research Unit at University Malaysia Sabah also took part in some interviews (Plate 18). 4.3.3. Findings
Fishers in Karakit reported that annually for one month, tuntungan (Blacktip reef sharks, Carcharhinus melanopterus) aggregate in shallow waters at various sites around southern Banggi and are caught in large numbers by gillnets set overnight. This is not a major fishery but is important for a small group of fishers who specialise in gill netting and catch the majority of their annual catch during this month. They believed that the aggregations were for spawning as it is also the only season when they find a lot of eggs inside. As this is a live-bearing species it is not clear whether this interpretation is incorrect or whether they were using the word telur (egg) to mean embryos. Most aggregations cited in this region related to kut kut (small species of Epinephelus) and sunoh (Plectropomus spp). P. leopardus, P. areolatus where most prevalent in records but P. maculatus and P. laevis also featured. Aggregations had generally shown moderate to severe declines during the 1980s or 1990s. Batta (E. ongus) aggregations appeared to be most persistent in the region with some showing no changes in catches and some showing moderate to severe declines. Some observations of groups of Maming (Cheilinus undulatus) were reported which could relate to spawning aggregations but generally fishers said that large adults of this species were rare or extinct. 4.3.4. Potential Future Research and Partners
WWF Malaysia is active in the region as part of their Sulu-Sulawesi Marine Ecoregion project and have funded studies of the live fish trade in the Kudat area and community use of coastal resources as well as holding fisheries stakeholder workshops in Karakit and Kudat. They have a community education centre in Karakit and a staff member in the KK office allocated to primarily work in the region who is familiar with key members and representatives of the fishing communities in Banggi. They are interested in the management and conservation of marine resources in the region, actively supported this SCRFA survey, and would be interested to support further work (for information on current and future activities contact Ms Robecca Jumin or Mr Leo Daim at the Sabah office of WWFM). A long discussion was held with Panglima Akmdju Bin Unding, the headman of the village of Tanjung Malawali, in which he related many carefully made observations of reef fish ecology and fisheries in the area and asked about the reproductive ecology of reef fish. In response to explanations about aggregations, pelagic larvae, increasing fecundity with age, sex change and late maturation of more valuable reef species, he expressed strong support for the establishment of small marine protected areas (MPAs) for the protection of local fish populations. He could be a key contact for the
understanding of the local fisheries situation, implementation and design of conservation measures and a means of communicating with the people in his village. The fisheries department used to have an officer based in the Banggi sub-district office in Karakit but since he was transferred to KK in 2002, Banggi has been remotely administered from the Kudat branch of the fisheries office. The whole area of Banggi and surrounding islands is proposed to become the Tun Mustapha Marine Park which will be the largest marine park in Sabah. The management proposal for a zoned, multi-use marine area is being prepared by the Borneo Marine Research Institute at the University Malaysia Sabah (contact Prof Ridzwan Abdul Rahman or Dr Annadel Cabanban).
The south western district of Semporna is important both as a centre for fishing and trading activities, and due to it’s wealth of coral reef areas that are heavily utilised by the dive tourism and fishing industries. Seine fisheries for pelagic resources dominate the marine fisheries activities of this district but there is also a significant population (861 in 2000) of traditional fishers. The demersal fish catch from hook and line fisheries in 1999 was 1,100 tonnes (Biusing 2001). An extensive live reef fish trade involving several holding cages and traders also operates in Semporna. This accounted for 742 tonnes of live fish in 2002 according to Fisheries Department statistics. Blast fishing was responsible for severe decline of reef condition in this region (Pilcher and Cabanban 2001) but according to Sabah Fisheries department blast fishing has declined since 2000 due to stronger enforcement. This generally agreed with the stated views of both fishers and divers. However, at least one blast was clearly heard during this survey. 4.4.2. Work Conducted
Initial work in Semporna was conducted with the aid of Mr Marcel Eging, the WWF Malaysia field staff for Semporna4. He assisted with arranging meetings and travel logistics and accompanied Tim Daw on all of the interviews conducted in fishing villages in Semporna (Plate 14). Meetings were also held with Mr Ruzlee Jumatin, head of Sabah Fisheries Department’s Semporna office and various staff to introduce the project and solicit advice and any experience or opinions relevant to the aims of the survey. Official statistics of live and dead fish landings for the region were also made available (see Appendix VI). With the assistance of the Fisheries Department, in particular Mr Alfred Karom, head of the seaweed aquaculture project, communities on the islands of Bum Bum,
Marcel has since moved on from WWF Malaysia and has been replaced by Ms Nazmahwati Walli
Omadal, Menampilik and Selakan were visited to conduct interviews (Plates 12, 15 and 16). During the Chinese New Year celebrations (which disrupted other survey activities) Borneo Divers provided logistical support to interview divemasters and instructors on the dive resort islands of Sipadan and Mabul. During this period sightings of potential maming (Cheilinus undulatus) spawning activity were reported on the Southern tip of Sipadan reef and a single dive was conducted to make first-hand observations. 4.4.3. Findings
Around the Semporna area several fishers told of large aggregations of groupers which had been exploited for generations in the area of the Semporna Islands Park in the southeast of Darvel Bay, Ligitan reef and at reefs along the Ligitan Channel. Plectropomus areolatus (known in the region as sunoh bodoh or “stupid coralgrouper”) was the most commonly cited species but Epinephelus fuscoguttatus, P. laevis, E. ongus and P. leopardus also featured. Nearly all of these large aggregations of groupers had declined severely or ceased to occur in the 1980s and 1990s. Large monthly aggregations of Belais (Siganidae) in shallow water still occur on many reefs but often these had apparently also declined to a certain extent as a result of bomb fishing in during the 1980s. One rare example was a site within the proposed Semporna Islands Park which had annual aggregations of E. fuscoguttatus, E. ongus and Lutjanids. These had personally been protected from outside fishers by the owner of the adjacent land and are now somewhat protected by the Park staff. The islands of Sipadan, Mabul and Kapali now operate as de-facto reserves due to the high intensity of dive tourism in the area and the extensive patrolling by the Malaysian military following kidnaps of tourists from the area in 2000 and 2001. Divemasters on Sipadan island reported regularly observing Siganids group spawning and rarer observations which may be indicative of spawning amongst P. areolatus, bumphead parrotfish (Bolbometopon muricatum) and humphead wrasse (Cheilinus undulatus). During a dive on 24/1/04 at 11:00 am Tim Daw saw a loose group of 5-6 individuals including two mature males and watched apparent courtship behaviour (swimming out together 10-20m from reef) of a large (1.5m) male and a smaller (50cm) fish presumed to be a female (Plate 19). Actual spawning was not observed however. 4.4.4. Potential Future Research and Partners
A clearer picture of aggregations could be obtained by further interviews in communities on other islands and within Semporna town itself not covered during this survey. These could include interviews within the Bajau Laut community and captains of larger vessels which are based in Semporna but fish on the surrounding reefs and islands. Live fish traders in Semporna could provide insights into temporal fluctuations in supply which may indicate the targeting of FSAs as well as links with larger, more commercial fishing operators amongst their suppliers. 20
The many dive operators around Semporna may be natural partners for any further FSA research in the area in terms of logistical support as well as making observations. Mr Randy Davis, Director of Borneo Divers, who kindly assisted with the logistics of interviews and observations on Sipadan and Mabul islands, was interested in the work of SCRFA and may be willing to provide further support in the future. Two main videographer companies have operations embedded within the resorts (and throughout Sabah) and collect a huge quantity of underwater footage each week. Mr Eric Madeja, operation manager of Treasure Images within the Borneo Divers resort on Sipadan discussed the possibility of making an arrangement for them to look out for and film particular fish behaviour which could then be sent regularly to SCRFA for analysis. Scubazoo Images is another large organisation with videographers located on many resorts throughout Sabah and an interest in marine conservation. The Semporna Islands Project, with the involvement of Sabah Parks, WWF, the UK Marine Conservation Society and funded by European Union funds has prepared a detailed management plan for the Semporna Islands Park (http://www.mcsuk.org/semporna/header_nav/headerframes.htm) which is in the process of being gazetted. Many activities have already been undertaken including the employment of park staff, surveys of the natural resources and human settlements of the area, and discussion and awareness raising amongst local communities. A zoning scheme is proposed for the park including no-take and limited-use zones and the development of diving based tourism is envisaged (MCS). The Semporna area falls within WWF’s Sulu-Sulawesi marine Ecoregion programme. They have already conducted an preliminary assessment of the live reef fish trade in the Semporna and Tawau areas (Suliansa 2002).
Lahad Datu is the urban centre for a large district which encompasses all the scattered islands in the north of Darvel Bay. Fisheries statistics cite a population of 451 traditional fishers in 2000, and demersal hook and line catch of 4,666 tonnes in 1999 (Biusing 2001). There is also an active live fish trade. One large holding operation was visited which transports about 12-17 tonnes of live fish to Hong Kong by boat per year5. The area apparently has suffered from intensive blast fishing activity which is largely blamed on the sizeable illegal immigrant population (Biusing 2001). 4.5.2. Work Conducted
On arrival I was met by Mr Amla bin Emta, a member of staff with the Lahad Datu Fisheries Department office who had arranged boat and road transport to conduct interviews in the area. Only four fisher interviews were made in the Lahad Datu area due to the limited time available and time required to travel between islands. These were made in Lok Terusan and Kg Teruakan near P. Sakar and in Lamak near Silam. 5
A worker on the cage (owned by Mr Abadi and near Silam) claimed that 2-3 shipments of about 7 tonnes were made to Hong Kong per year or a single shipment of about 12 tonnes would be made once per year.
A large live fish holding facility (Plate 4) and the Fisheries Department office were visited and the officer responsible for collecting fisheries statistics for the area was interviewed. 4.5.3. Findings and Data Appraisal
Little information on aggregations was uncovered during the brief time spent conducting interviews in the Lahad Datu area. None of the fishers interviewed provided specific details about individual aggregations although they were aware of monthly peaks of abundance of rabbitfish. One fisher did state that seasonality in catches of Sunoh (Plectropomus) had been evident in the past but had not been discernable since the populations declined in the 1980s. All the fishers reported significant declines in catches, especially those of LRFT species. 4.5.4. Potential Future Research and Partners
More interviews in the region could well be worthwhile and would be likely to uncover more information. The large fishing community of Silam would be a readily accessible and potentially interesting area to conduct more interviews. The Fisheries Department office in Lahad Datu was interested in the SCRFA work and extremely cooperative but would have limited resources to conduct any additional research. There is also a small Fisheries office in Kunak, in the south west of Darvel Bay. P. Tambisan near the most Eastern point of Sabah apparently has a form of community management in operation6. It would be worthwhile to interview fishers from this community to see whether this management coupled with the more remote location of the island had allowed aggregations to persist in the area.
Personal communication, Robecca Jumin and Marcel Eging, WWF Malaysia
5. Overall Findings and Recommendations 5.1.
5.1.1. Fisheries Statistics
Official statistics are collected by regional offices of Sabah Fisheries Department according to the SMPP (Sistem Maklumat Pengurusan Perikanan, Fisheries Information Management System). These data were examined in the Fisheries offices of Semporna (see Appendix VI), Lahad Datu and Kudat but they proved to be of limited use for detecting the targeting of spawning aggregations for several reasons: •
Lack of taxonomic resolution – Landing statistics were usually grouped into very broad categories (e.g. Serranidae) which were sometimes broader than their strictly scientific meaning. For example while some local officers recorded Sunoh (Plectropomus spp) and Maming (Cheilinus undulatus) separately, others grouped them in a general Kerapu (Groupers) category. Fisheries officers were of the opinion that whereas the statistics gave a good representation of overall total landings, individual species based data were relatively poor; Availability of temporal spread – Within the offices visited there were generally only one or two years of data readily available making it difficult to corroborate apparent seasonal trends in CPUE. Longer time series would be available from the central Fisheries Department statistical branch in KK; Lack of or unreliable measures of effort – There was some discrepancy between offices as to how (or whether) reliable measures of effort were recorded. Extensive use of illegal gears (bombs and cyanide) confuses the picture further as it is unknown under which legal gear category these catches are usually recorded; Inaccuracies related to inadequate sampling – Officers responsible for collecting data for the SMPP have very limited resources to conduct extensive sampling of landings. One or two officers are generally responsible for sampling many different gear types and thus often rely on declarations from fishers rather than direct measurements or observation. Some fishers or vessel owners are believed to misreport catches for tax reasons.
Live fish landings are not included in the SMPP and are collated by the fisheries department from declarations of traders and cage owners. These may also be inaccurate or misrepresentative for tax reasons. For example a previous study of the trade in the Kudat region suggested that official landing statistics of 70 tonnes in 2001 were underestimated by over 50% (Daw et al. 2002a). Export statistics for the live fish trade are also available which may provide a more useful indication of seasonal trends in the catches of more valuable and easily identified species. These data are held by the Fisheries Department and Rooney Biusing (Deputy Director) is in the process of analysing this information, particularly for maming (Cheilinus undulatus).
5.1.2. Main species reported as aggregating in Sabah
Nearly half of the 75 records likely to represent actual spawning aggregations were of Plectropomus species and 36% were Epinephelus7. Fourteen species were included in these records and the number of records corresponding to each are shown in table 1. Siganids were also mentioned, particularly in the Semporna region but it was not always possible to identify them to species. Table 1. Species featuring in interviews which were “very likely” to represent spawning (see the SCRFA database for details, www.scrfa.org) Species No of Records 10 Plectropomus areolatus 10 Epinephelus ongus 9 Plectropomus leopardus 5 Plectropomus oligocanthus 5 Cheilinus undulatus 5a Carcharhinus melanopterus 3 Plectropomus maculatus 3 Epinephelus fuscoguttatus 2 Epinephelus fasciatus 1 Siganus guttatus 1 Epinephelus quoyanus 1 Epinephelus polyphekadion 1 Epinephelus merra 1 Bolbometopon muricatum a NB. The 5 aggregation records for black tipped reef sharks (Carcharhinus melanopterus) were all described during one interview.
5.1.3. Seasonality of FSAs in Sabah
The interviews gave some indication of the periodicity of spawning of some species. Figure 3 shows the number of spawning aggregation records that related to each month for 5 of the most commonly cited species within each region. The trends are quite different for each of the species with April being the most important month when all of the species are considered.
The large number of grouper (Serranidae) species aggregations reported may partially be a result of the data collection procedures. As groupers and mameng (Cheilinus undulatus) are not normally shoaling species, it was possible to ask fishers if they had ever seen large groups of them and assume that any responses indicated unusual aggregations. This particular question could not be used in this way for rabbitfish (Siganidae), mullets (Muglidae) or snappers (Lethrinidae) because these are commonly shoaling families, so a positive response would not necessarily indicate any unusual aggregation of fish.
Epinephelus ongus, N=10
Cheilinus undulatus, N=5
4 2 3 2 1 1 0
No of records
JAN FEB MAR APR MAY JUN
JUL AUG SEP OCT NOV DEC
Plectropomus leopardus , N=9
JAN FEB MAR APR MAY JUN
JUL AUG SEP OCT NOV DEC
Plectropomus areolatus, N=10
5 3 4 3
2 1 1 0
0 JAN FEB MAR APR MAY JUN
JUL AUG SEP OCT NOV DEC
JAN FEB MAR APR MAY JUN
JUL AUG SEP OCT NOV DEC
Plectropomus oligocanthus , N=5 4
S. China Sea West Banggi East Banggi Jambongan/Sulu Sea Darvel Bay Omadal-Sulawesi Sea
0 JAN FEB MAR APR MAY JUN
JUL AUG SEP OCT NOV DEC
Figure 3. Plots of months of spawning for 5 of the most well represented species from the survey with records separated by region. (Only records where spawning was thought to be very likely are included) 5.1.4. Status of FSAs in Sabah
Aggregations which had been observed at Sipadan and on Lyang Lyang atoll were unusual in being fully protected from fishing. If all other aggregation sites disclosed during interviews (i.e. at fished sites) are considered, only 20% appeared to be stable and more than half of all aggregations in which a trend could be discerned were either extinct or suffering severe (>50%) declines (Figure 4).
Status of unprotected aggregations N=76 ("very likely" records only)
Moderate Decline 25% Steady 20%
Severe Decline 24%
Figure 4. Status of aggregations identified in Sabah (Moderate decline: <50% decline in CPUE, Severe decline: >50% decline in CPUE). 5.1.5. Attitudes of fishers to conservation and aggregations
In agreement with previous studies in the Banggi region (Fisher 2000; Daw et al. 2002a; Cooke 2003) nearly all fishers agreed with the view that stocks and catches of reef fish have declined. In a few notable exceptions, fishers in the Semporna region claimed that there were more fish now since fish bombing had been reduced. Where a decline was observed, fisheries reasons were commonly cited. However, no clear consensus seemed to exist on the need to curtail fishers’ own fishing practises. Some fishers appeared unconcerned with the declines, pointing out that prices had increased to such an extent that they were actually better off now even with lower catches, as well as the range of other species which could be collected in order to survive. Others seemed to think that declines were inevitable or caused by other parties (outsiders or commercial fisheries). It must be emphasised that these findings are very preliminary due to the small, unrepresentative sample taken during this study but it should be made clear that fishers in Sabah may not be easily convinced of the need or desirability of protecting spawning aggregations, especially in cases where overall catches have declined and aggregations may be the only opportunity to make sizeable catches. Fisher (2000), Daw et al. (2002a) and especially Cooke (2003) should be consulted for a more thorough analysis of fishers’ perceptions in Banggi.
Table 2. Perceived reasons why fish stocks have declined? (N=61) No. responses 39 15 14 13 6 1
Percentage of responses 64% 25% 23% 21% 10% 2%
Reason Lots fishers Blast fishing Trawlers, purse seiners Cyanide use Outsiders Echo-sounders
Effective management and conservation of reef fish stocks and FSAs within Sabah will depend on a certain knowledge of the species which aggregate and how and when these FSAs occur. Although this survey gives some preliminary information, research on FSAs within East Malaysia should be extended both in terms of the geographical area examined and the range and detail of investigations. The limited time available for this study constrained its geographic coverage. Many other areas within East Malaysia could be important for FSAs and it would be worth extending interviews with fishers to those areas. A preliminary list of these would include: Kuching Bintulu, Miri Pulau Labuan Spratley Islands Pulau Mantanani Pulau Mandidarah, Pulau Tigabu, Pulau Jambongan Pulau Lankayan, Pulau Bilean Kunak area All of the records of FSAs “discovered” during this survey must be considered provisional as they have not been confirmed by first-hand observation of actual spawning. An obvious initial follow-up to this study would be to attempt to confirm the records of aggregations suggested by interviews through direct underwater observations at described times. To avoid conflicts with fishers who use the aggregations, this should be conducted in collaboration with them and alongside further information and explanation of why the research is being conducted and its importance. The density of dive resorts in some of the popular areas of Sabah leads cumulatively to very intensive underwater observation of certain reefs. Many resorts (e.g. Manatanani, Sipadan, Lyang Lyang) have resident videographers who may be interested to assist in FSA research by putting aside footage which they (after brief training) thought represented spawning behaviour. This could then be sent to outside experts for analysis and confirmation.
Regular catches of reef fish and delivery fresh to Sabah’s fish markets (particularly Kudat, Semporna, KK and Sandakan) creates the opportunity to purchase regular samples of fish from the surrounding reefs and monitor biological signs of spawning activity. Analysis of gonadosomatic index (GSI see Colin et al. (2003) for explanation) and/or gonad maturation stage could help identify spawning seasons in each region. Sabah Fisheries Department are already conducting reproductive research on some pelagic species and thus have some personnel with experience in the sexing and staging of fish gonads8. This research would be more effective if it were supported by the collaboration of fishers who were willing to share information on the geographical location of the source reefs on a trip by trip basis.
There is conclusive evidence from many studies that stocks of reef fish (especially predators) are in steep decline on Sabah’s reefs and management measures are needed to sustain catches of these valuable fish (Cabanban and Biusing 1999; Oakley et al. 1999; Fisher 2000; Harding et al. 2000; Pilcher and Cabanban 2001; Daw et al. 2002a; Daw et al. 2002b). Aggregations could specifically be protected by spatial or temporal closures. Marine protected areas (MPAs) which are closed to all fishing are one measure which can be used to sustain populations of reproductively mature stocks which could replenish fished areas. These areas should be planned to include spawning sites in cases where they have been confirmed as present and where the necessary community support and enforcement capacity exists. Issues of enforcement are likely to be a serious constraint on the ability to protect aggregations, especially in remote reasons and there may be little point in the legislative protection of aggregations in the absence of these factors. In such cases, programmes of joint research and awareness raising with the communities involved would be the first stage of long-term management and sustainability. During this study, if fishers were interested enough to learn some key facts about reef fish biology they generally became more supportive of the idea of MPAs on the condition that the areas were small enough or located in such a way that they did not loose substantial proportions of their fishing grounds. These key facts to describe to them included: • • • • •
Fish continue to grow throughout their lives; A few larger fish produce many times more eggs than many small fish; Fish do not stop producing eggs when they are old – in fact they produce more; Many species mature late and change sex so that fish of a certain age are necessary for a reproductively viable population; Fish eggs and larvae are generally planktonic and can drift from reef to reef whereas adults normally remain on one reef.
Even very reomote communities in Sabah often have video or VCD facilities, so the production of an information VCD in simple Malay or local languages could be a useful way to efficiently disseminate these facts to many fishing communities. This could include interviews with fishers and scientists as well as graphical representation
Personal communication, Dr Ahemad Sade, Mr Irman Isnain, Research Division, Sabah Fisheries Department.
of the concepts. Good quality underwater footage of valuable species would no doubt be of great interest to the fishers and encourage them to watch the VCD. Virtually all the results of this SCRFA survey has been dependent on the goodwill of the communities and fishers involved who were willing to share their knowledge of fish aggregations. This leads to an ethical question if the resultant management measures led to economic hardship of those very same fishers by restricting their activities. This issue may be reconciled by further communication with the communities involved if they can agree that the aggregations which they have identified should be protected for the long term benefit of themselves as well as outside conservation interests.
6. References Berkes, F., J. Colding and C. Folke (2000). Rediscovery of traditional ecological knowledge as adaptive management. Ecological Applications 10(5): 12511262. Biusing, R. E. (2001). Assessment Of Coastal Fisheries In The Malaysian - Sabah Portion Of The Sulu Sulawesi Marine Ecoregion (SSME). Kota Kinabalu, WWF Malaysia, 719 pp. Biusing, R. E., M. Phillips and A. S. Cabanban (1999). The cage culture of coral reef fishes and other fishes in Sabah, Malaysia. Proceedings of the Workshop on Aquaculture of Coral Reef Fishes and Sustainable Reef Fisheries, Kota Kinabalu, Sabah, Malaysia, Institute for Development Studies (Sabah). p 7486. Cabanban, A. S. and R. E. Biusing (1999). Coral reef fisheries in its contribution to marine fish production in Sabah. Proceedings of the Workshop on Aquaculture of Coral Reef Fishes and Sustainable Reef Fisheries, Kota Kinabalu, Sabah, Malaysia, Institute for Development Studies (Sabah). p 8796. Colin, P. L., Y. J. Sadovy and M. L. Domeier (2003). Manual for the Study and Conservation of Reef Fish Spawning Aggregations. Hong Kong, Society for the Conservation of Reef Fish Aggregations, 98 pp. Cooke, F. M. (2003). Living at the Top End: Communities and Natural Resource Use in the Kudat/Banggi Region of Northern Sabah. Kota Kinabalu, WWF Malaysia, 45 pp. Daw, T. M., L. J. Daim and M. A. bin Ali (2002a). Preliminary Assessment of the Live Reef Fish Trade in the Kudat Region. Kota Kinabalu, WWF Malaysia, 47 pp. Daw, T. M., H. Wesson, S. Harding and C. Lowery (2002b). Pulau Banggi Project for Coral Reef Biodiversity. 2nd Annual Report (October 2000 - October 2001). Kudat, Sabah, Malaysia, Greenforce, 80 pp. FAO (1998). Status of Marine Fisheries. Rome, FAO. Fenner, D. (2001). Reef corals of Banggi area reefs. Kudat, Malaysia, Greenforce, 13 pp. Fisher, H. (2000). A Socio-Economic Assessment of Coastal Communities of Pulau Banggi Sabah, East Malaysia. MSc thesis, University of Minnesota.
Harding, S., C. Lowery, H. Wesson, M. Colmer and S. Oakley (2000). The Pulau Banggi Project for Coral Reef Biodiversity. 1st Annual Report (July 1999 September 2000), Greenforce, 98 pp. Johannes, R. E. (1981). Words of the Lagoon. Berkely, University of California Press. Johannes, R. E. (1998). The case for data-less marine resource management: examples from tropical nearshore finfisheries. Trends in Ecology and Evolution 13(6): 243-245. MCS Semporna Islands Project and Development of the Management Plan, Marine Conservation Society. http://www.mcsuk.org/semporna/header_nav/headerframes.htm (accessed: 13th April, 2004). Neis, B. and L. Felt, Eds. (2000). Finding Our Sea Legs: Linking Fishery People and Their Knowledge with Science and Management. St. Johns, ISER. Oakley, S., N. Pilcher, K. Atack, C. Digges, S. Enderby, G. Mackey, R. Clubb, K. Stapelton, T. Mei, C. Huet and T. Morton (1999). Reefs under attack: the status of coral reefs of Sabah, East Malaysia. 4th International Conference on the Marine Biology of the South China Sea, Quezon City, Philippines. Oakley, S., N. Pilcher and E. Wood (2000). Chapter 77: Borneo. Seas at the Millennium: An Environmental Evaluation. C. R. C. Sheppard. Oxford, Pergamon. p 361-379. Pilcher, N. and A. S. Cabanban (2001). The Status of Coral Reefs in Eastern Malaysia. Global Coral Reef Monitoring Network Status Report. Townseville, AIMS. Pitcher, T. J., P. J. B. Hart and D. Pauly, Eds. (1998). Reinventing Fisheries Management. London, Kluwer Academic Publishers. Suliansa, M. S. b. (2002). Understanding the Live Food Fish Trade: A Preliminary Assessment in SSME3, Semporna and Tawau Area. Kota Kinabalu, WWF Malaysia, 30 pp. Wood, E. (1979). Ecological study of coral reefs in Sabah, WWF Project Malaysia No. 15, 163 pp.
List of People met and Contact Details
Government Datuk Lamri Ali*, Director Sabah Parks Blok K, Lot 3 Sinsuran Complex P.O.Box 10626 788806 Kota Kinabalu, Sabah, Malaysia Business: 60 88 211881 Other Fax: 60 88 211001 Rayner Datuk Stuel Galid, Director Sabah Fisheries Department 8th Floor, Menara Khidmat, 88628 Kota Kinabalu, Sabah, Malaysia Rooney Biusing, Deputy Director Sabah Fisheries Department 8th Floor, Menara Khidmat, 88628 Kota Kinabalu, Sabah, Malaysia Business: +60 (88) 235966 Mobile: +60 (13) 8509902 Other Fax: 60 88 425890 Business Fax: +60 (88) 240511 E-mail:[email protected]
Ahmad Mokthar Shahul Hamid Macro Economic & Evaluation Section Block B5, Level 4, Economic Planning Units Prime Minister's Department 62502, Putrajaya, Malaysia E-mail: [email protected]
Mr Talip Hassan*, Head of Lahad Datu Office Sabah Fisheries Department Pejabat Perikanan Daerah, PO Box 61014 91118 Lahad Datu, Sabah, Malaysia Tel/fax: 089 881 566 Irman Isnain, Head of Fisheries Resources Unit Sabah Fisheries Department, Fisheries Reasearch Centre 89400 Likas Kota Kinabalu, Malaysia Tel: 428415 /6 Business Fax: 425890 E-mail: [email protected]
Ruzlee Jumatin, Head of Semporna Office Sabah Fisheries Department, Pejabat Perikanan Daerah PO Box 133, 91308 Semporna Sabah, Malaysia Business: +60 (89) 781706 E-mail: [email protected]
Mr Alfred Karom, Project Manager of Seaweed Aquaculture Project Sabah Fisheries Department, Projek Pengkulturan Rumpai Laut Pejabat Perikanan Daerah, PO Box 133 91308 Semporna, Sabah, Malaysia Business: +60 (89) 784864 Goddfrey Kissey, Head of Marine Branch Sabah Fisheries Department 8th Floor, Menara Khidmat, 88628 Kota Kinabalu, Sabah, Malaysia Chio Fui Lin, Fisheries Officer Sabah Fisheries Department 8th Floor, Menara Khidmat, 88628 Kota Kinabalu, Sabah, Malaysia Mobile: 016-819-8167 Abd Rahman Ottman*, Former Fisheries Officer in Charge, Banggi Region Sabah Fisheries Department, 8th Floor, Menara Khidmat, 88628 Kota Kinabalu, Malaysia Business: 088 671 439 Mobile: 010 871 1954 Other Fax: 088 671 439 E-mail: [email protected]
Dr Ahemad Sade, Head of Reasearch section Sabah Fisheries Department, Fisheries Reasearch Centre 89400 Likas Kota Kinabalu, Malaysia Main Phone: 428415 /6 Business Fax: 425890 E-mail:[email protected]
Abd Manaf Datu Unjung, Head of Kudat Fisheries Office Sabah Fisheries Department, Pejabat Perikanan Kudat Peti Surat 195, 89058 Kudat, Sabah, Malaysia Main Phone: 088 611 832 Business Fax: 088 611 832 E-mail:[email protected]
Academic Prof Dr Ridzwan Abdul Rahman*, Head Borneo Marine Research Institute, University Malaysia Sabah, Locked Bag 2073, 88999 Kota Kinabalu, Sabah, Malaysia Phone: 088-435204 Phone 2: 088-320121 Fax: 6088-436204 E-mail:[email protected]
Dr Annadel Cabanban, Associate Professor Borneo Marine Research Institute, University Malaysia Sabah, Locked Bag 2073, 88999 Kota Kinabalu, Sabah, Malaysia Phone: 58 88 438440 Fax: 58 88 435204 E-mail: [email protected]
E-mail 2: [email protected]
Dive Industry Eljer Aranjuez, Divemaster Borneo Divers, 9th Floor, Menara Jubili, 53 Jalan Gaya 88000 Kota Kinabalu, Sabah, Malaysia E-mail:[email protected]
Rudy Chin, Resort Manager Sipadan Dive Centre A1103, 11th Floor, Wisma Merdeka, Jalan Tun Razak, 88000 Kota Kinabalu, Sabah, Malaysia Business: +60 (88) 240 584 Business Fax: +60 (88) 240 415 E-mail:[email protected]
Randy Davis, Director Borneo Divers and Seasports Labuan, Malaysia E-mail:[email protected]
Simon Enderby Scubazoo Images PO Box 15475, 88864 Kota Kinabalu, Sabah, Malaysia Company Main Phone: (+ 6) 088 232 068 Business Fax: (+6) 088 237 068 E-mail:[email protected]
Alexander Ho, Dive Instructor Sipadan Water Village, Mabul PO Box 62156, 62156 Tawau, Sabah, Malaysia E-mail:[email protected]
Leonard Lai, Dive manager & Resort supervisor Sipadan Water Village, Mabul PO Box 62156, 62156 Tawau, Sabah, Malaysia E-mail:[email protected]
Robert Lo, Managing Director Sipadan Mabul Resort (SMART) PO Box 15571, 88000 Kota Kinabalu, Sabah, Malaysia Business: +60 (88) 784800 Business 2: +60 (88) 254723 Business Fax: +60 (88) 242003 E-mail:[email protected]
Eric Madeja, Operation Manager and videographer Treasure Images Sdn Bhd, Sipadan Island 4th Floor, Room 422-424, Wisma Sabah, 88300 Kota Kinabalu, Sabah, Malaysia Business: +60 (88) 253651 Business Fax: +60 (88) 251667 E-mail:[email protected]
Lim Chun (John) Min, Divemaster SMART Divers, Mabul PO Box No 124, 91308 Semporna, Sabah, Malaysia Business: 784 800 Mobile: 089 782 421 Chris Tan, Underwater Photographer Scubazoo Images PO Box 15475, 88864 Kota Kinabalu, Sabah, Malaysia Business: +6 (088) 232068 Business Fax: +6 (088) 237 068 E-mail:[email protected]
Jeremy Van Houten*, Resort Executive Borneo Divers, 9th Floor, Menara Jubili, 53 Jalan Gaya 88000 Kota Kinabalu, Sabah, Malaysia Business: +60 (88) 222226 Jojo Vismanos, Divemaster Borneo Divers, Sipadan Island Borneo Divers, 9th Floor, Menara Jubili, 53 Jalan Gaya 88000 Kota Kinabalu, Sabah, Malaysia
NGOs Tim Burns, Chief Scientist (Left project in early 2004) Greenforce Borneo c/o Sri Mahiruddin, PO Box 526, 89058 Kudat Sabah, Malaysia E-mail:[email protected]
Robecca Jumin, Head of Marine Section World Wide Fund for Nature Malaysia (Sabah Office) PO Box 14393, 88850 Kota Kinabalu, Sabah, Malaysia. Main Phone: 088 262 420 Business Fax: 088 242 531 E-mail:[email protected]
Leonardo Jeffrey Daim (staff responsible for marine interests in Kudat/Banggi region World Wide Fund for Nature Malaysia (Sabah Office) PO Box 14393, 88850 Kota Kinabalu, Sabah, Malaysia Main Phone: 088 262 420 Business Fax: 088 242 531 E-mail:[email protected]
Nazmahwati Walli*, Staff responsible for marine activities in Semporna region World Wide Fund for Nature Malaysia (Sabah Office) E-mail:[email protected]
Dr Nick Pilcher, Executive Director Marine Research Foundation 1-3A-7 The Peak, Lorong Puncak 1 88400 Kota Kinabalu, Sabah, Malaysia Business: 60 88 243000 Main Phone: 60 88 243000 Other Fax: 60 88 243000 Business Fax: 60 88 243000 E-mail:[email protected]
Dr Elizabeth Wood*, Coral Reef Conservation Officeer Marine Conservation Society, UK 9 Glocester Road, Ross-on-Wye, Herefordshire, HR9 5BU UK E-mail:[email protected]
* contacts marked with an asterisk were not met in person during this survey but are relevant to the management of fish spawning aggregations in Sabah and known from previous work and communications.
Appendix II. Date 30/12/03 31/12/03 – 4/1/04 5/1/04 6/1/04 7/1/04 8/1/04 9/1/04 9-11/1/04 11/1/04 12-13/1/04 14/1/04 15/1/04 16/1/04 17/1/04 18/1/04 19/1/04 20/1/04 21/1/04 22/1/04 23/1/04 24/1/04 25/1/04 26/1/04 27/1/04 28/1/04 29-31/1/04 1/2/04
Itinerary Location/Activity Arrive Kuala Lumpur - Collect research pass, travel to Kota Kinabalu Kota Kinabalu – Organise research visa, meetings Travel to Tawau & Semporna meet Marcel Eging Meetings in Semporna, travel to P. Bum Bum and start interviews with Marcel Eging Interviews on P. Omadal with Marcel Eging, return to Semporna Interviews on P. Menampilik with Marcel Eging Meeting Fisheries Department in Semporna Interviews on P. Selakan with Marcel Eging Return to Kota Kinabalu Meetings and interviews in Kudat with Leo Daim Travel to Banggi, Interviews in Lok Tohog with Leo Daim & Asri bin Barail Interviews on Malawali and Focus group with fishers in Karakit with Leo Daim & Asri bin Barail Interviews in Batu Siri, Balambangan with Dr Annadel Cabanban & Asri bin Barail Interviews in Sibogo with Dr Annadel Cabanban & Asri bin Barail Interviews in Lumais with Asri bin Barail Interviews in Padang and Kobong with Asri bin Barail Interviews in Karakit with Asri bin Barail Travel to Kudat, interviews in Kudat with Asri bin Barail Interviews in Kudat with Asri bin Barail, Visit Greenforce project camp Interviews in Longgom Kecil, Travel to Kota Kinabalu Travel to Semporna & P. Sipadan, interviews on Sipadan Observation on Sipadan, Travel to & interviews on P. Mabul Return to Semporna, Travel to Lahad Datu Interviews around Lahad Datu with Amla bin Emta Interviews around Lahad Datu with Amla bin Emta, Return to KK Interviews and meetings in KK Leave Malaysia
SCRFA E. Malaysia Reef Fish Aggregation Survey Fisher interview schedule METADATA Interview number:
Location: FISHER DETAILS Bilakah kamu mula-mula tankap ikan? (When did you start fishing?) Macam mana kita tankap ikan? (How do you fish?) Apa jenis ikan yang paling banyak tankap? (Which species do you mostly catch?) Kaedah? (gear) Jenis? (species)
Apa jenis bot yang kamu pakai untuk tangkap ikan? (what kind of boat do you use?) Apa jenis enjin? (what kind of engine?) Berapa orang dalam bot? (How many people in the boat?) Berapa kali turun ke laut dalam satu bulan? (How many times to sea in a month?) Berapa lama di laut? (How long do you stay at sea?) Kalau kapal besar...(if large boat)
Siapa kapten kapal? (who is captain?) Kapal ada CAS? (does it have echosounder?) Kapal ada GPS? (does it have GPS?)
Di mana tankap ikan? (where do you fish?)
AGGREGATION QUESTIONS Apa musim ada yang paling bagus untuk tangkap banyak ikan takat? (Which season is the best for catching reef fish?) Pernah kah kamu tangkap ikan yang ada telur? (Have you ever seen fish with eggs?) Pernah kamu tangkap ikan dalam kumpulan besar? (Mullak?/Pullak) (Have you ever seen fish aggregations?) For the above Qs. Apa jenis? (What species?) Bila? Bulan apa? (When, Which month?) Dalam hari Bulan Melayu apa tarikh? (Which day in Malay Calendar?(moon state)) Pagi/Malam...? (Morning/Evening?) Di mana? (Where?) Apa nama itu kawasan? (What is the place name?) Kamu boleh menyatakan mana atas peta ini? Apa arah petunjuk? Berapa kilometer dari sini? (Can you show on this chart? Which direction? How many km from here?) Berapa meter dalam, itu kawasan? (How deep is that place?) Ada batu karang/pasir/batu batu besar? (Is there coral/sand/large rocks...?) Berapa besar itu kawasan? (How big is the place?) Berapa banyak ikan dalam kumpulan kamu angar? (How many fish are in the aggregation?) Bila kali pertama kamu tankap ikan dari kumpulan ikan itu? (When was the first time you went there?) Macam mana kamu boleh jumpa/tahu itu kumpulan ikan? (How did you find/know it?) Berapa banyak ikan kamu dapat dari kumpulan ikan itu pada duluh/sekarang? (How many fish could you catch there before/now?) Berapa nelayan tangkap ikan dari itu kumpulan dulu/sekarang? (How many fishers were catching fish there before/now?) Nelayan dari mana? (Fishers from where?)
Macam mana nelayan tankap ikan dari itu kumpulan duluh/sekaran? (What gears did fishers use there?) Adakah size ikan berubah sejak dulu? Macam mana? Lebih kecil/sama/besar? (Has the size of fish in the aggregation changed from before?) Kimu tidak risau dengan keadaan ini? (Do you worry about /regret this?) [If yes] Apa yang perlu di lakulkan? (What could be done about this?) GENERAL TRENDS Biasanya berapa banyak kamu Sekarang 5 tahun (Other time depending experience & dapat tankap dalam satu ? (Now?) dulu? (5 on minggu/trip etc? (Normally, how years ago?) memory) much fish do you catch in one week/trip etc?) Pendapat kamu, kenapa ada kurang ikan sekarang? (In your opinion why is there less fish now?) Apa jenis jenis ikan yang paling kurang sekarang? (Which species has declined the most?) Masi ada maming di sini? (Is there still C. undulatus here?) Masi ada lankawit di sini? (Are there still large adult C. undulatus here?) PERSONAL INCOME Selain daripada tangkap ikan, kamu ada sumer pendapatan lain? (Other than fishing do, you have other sources of income?) daripada Berapa banyak kamu Jual ikan hidup? Jual ikan mati? Selain dapat dari... (How (...selling live (...selling dead tankap ikan? (...other than catching fish?) fish) much/what proportion fish?) do you get from...) Apa bangsa kamu? (What ethnicity are Berapa umur? (How old?) you?) Reliability of interview? Other Notes:
Summaries of interviews by village Species Caught
Mgmt & concerns
Catches of maming (Cheilinus undulatus)
Batu Putih, Karakit
Plectropomus sp, Cuttlefish, Carangidae, Types of Mixed reef fish,
live fish catches have halved since 90s
Declines blamed on CN and Blast fishing. Outside fishers useed CN since late 90s.
declines of 70+% in nos maming. Sizes smaller.
Batu Siri, Balambangan
Trolling. Hook & Line, Gill net
Epinephelus fuscoguttatus, Brown patterned Epinephelus, Small brown Epinephelus spp (E. merra, ongus etc), Plectropomus leopardus, Plectropomus sp, Plectropomus maculatus, Caranx sexfasciatus, Carangoides fulvoguttatus, Caranx ignobilis, Alectus indicus, Alectus ciliaris, Atropus atropus, Atule mate, Types of Mixed reef fish, Argyrops spinifer, Lutjanidae, Scomberomorus sp,
One fisher thought all catches halved another thought catches of reef fish same as 10yrs ago but that now got 1-2 spanish mackerel as opposed to 4 10 yrs ago.
blast fishing and many outsider fishers blamed
adult male caught in 2003
Caesio cuning, Plectropomus leopardus, Plectropomus maculatus, Types of Mixed reef fish,
catches less than half of previously - now 1-2 live fish per day
large no of fishers, CN and bomb fishing blamed for decline. Belive that fish would come back if just hook and line
significant declines. No adults any more due to CN fishing
Plectropomus leopardus, Plectropomus maculatus,
declines of 50% or more in catches of live and general reef fish
large no of fishers blamed for declines
rarely catch maming in this area. Too shallow for adult males
Plectropomus leopardus, Plectropomus sp, Plectropomus maculatus, Carangidae, Types of Mixed reef fish, Scomberomorus sp,
most fishers cited declines of >60-80% in live fish catches to from 50 to 10-20 pcs per time collecting traps. One fisher claimed no change
Increase in fishing pressure. Higher prices and more fishers
catches/day of one fisher declined from 5 to 1 individual/trip
Trolling, Spear Hook & Line, Fish Trap
Hook & Line, Gill net
Caesio cuning, Carangidae, Atule mate, Siganidae, Dasyatidae,
Hook & Line, Compress or
Brown patterned Epinephelus, Plectropomus leopardus, Plectropomus sp, Plectropomus maculatus, Types of Mixed reef fish, Unidentified fish, Cheilinus undulatus,
Hook & Line, Gill net, Fish Trap
Hook & Line
Mgmt & concerns
Catches of maming (Cheilinus undulatus)
live fish catches have declined from 15 (20yrs ago) to 10 (5yrs ago) to 2-3 pcs
Lots of people catching live fish. Some people using CN for ~20 yrs.
live fish catches declined from 20 to 4-5 pcs/day since 10yrs ago. General reef fish catches down to 10-20 kg/day/person from 100 kg/day/person. Steady declines since 1981 Significant declines (30-50 to 5 kg/day) in live fish catches
No. fishers and industrial vessels blamed.
Less fish now but prices have gone up
catches have declined due to fishing pressure but still some adults around
Plectropomus sp, Plectropomus maculatus, Types of Mixed reef fish,
All catches declined. Blast fishing yields declined from tonnes to 50kg
Prices have increased so decline in catches is ok. But Headman concerned by increase in no fishers, actions of trawlers and use of echosounders, CN & dive compressors. Blast fishing used sicne WWII. Weather and seasonality of catches has become unpredictable
Used to have aggregations of maming in 60s & 70s. Not seen adults for years. Used to catch 5-7 individuals/day. Now 1 per month if lucky.
Cromileptes altivelis, Plectropomus leopardus, Plectropomus sp, Lutjanidae, Scomberomorus sp, Cheilinus undulatus,
One team of CN divers could get 100kg live fish & lobster per trip in 1990. Declined ever since to 5 - 6 kg now. Epinephelus lanceolatus has declined the most.
Numbers of fishers, trawlers and destructive fishing blamed for declines
rarely caught and only occasionaly see adults in deep places
still catch some but decline from 10 pcs/day 5 yrs ago to 6 pcs/month now.
Years Fishing No Interviews
Mgmt & concerns
Inarunto ng, Pitas
Lethrinidae, Plectropomus sp,
Live fish catch declined from 70 to 50 kg/trip in good season over last 10 years.
not sure of why declines
Kg Layak Lyak, Pitas Kg. Bingolon
Gill net catches have declined
concerned about no. of fishers and competition with large industrial boats
Hemirhamphidae, Carangidae, Liza vaigiensis, Liza subviridis, Unidentified mullet, Gerreidae, Types of Mixed reef fish, Lutjanidae, Unidentified Sharks, Scomberomorus sp, Tunas, Unidentified scombrid,
catch half amount of pelagics in on trip compared to one night 5 years ago. Spanish mackerel especially has declined
Blame declines on industrial purse seiners
Lok Linkan, Pitas
Plectropomus sp, Lutjanidae,
Plectropomus per week declined from 100 kg to 50 kg in 10 yrs. Lobster declined from 50kg to 20kg in last 5 yrs.
Longgo m Kecil
Epinephelus fasciatus, Epinephelus coioides, Carangidae, Siganidae, Nemipterus sp,
Gill net catches have declined from 50 kg/night to 10-20 kg/night since 1990s
blame lots of fishers. Follow unsafe diving practises. Interviewee had many friends who had died and had been hospitalised himself. Prawn trawlers and purse seiners blamed. Sometimes conflicts with fishers from other villagers
Tajau Laut, Kudat
Hook & Line, Diving
Hook & Line, Compre ssor
Lethrinidae, Caesio cuning, Plectropomus oligocanthus, Brown patterned Epinephelus, Plectropomus leopardus, Plectropomus sp, Plectropomus maculatus, Carangidae, Types of Mixed reef fish, Lutjanidae,
200 kg reef fish/day in 80s to 20 kg/day now. Plectropomus most affected
Blame lots of fishers.
50-70% decline in live fish CPUE over 5 years. Also declines in dead fish catch though not quite as severe
Blame lots of fishers primarily. Also bombs, CN, echosounders. CN used since 90s.
Catches of maming (Cheilinus undulatus) from 7/day 5yrs ago to 12/day now
v. rarely caught
Massive decline since 80s. One fishers used to catch 50-100 kg/trip in 70s now "might not see one in 10 trips". Rarely see adults but one 30kg fish caught in 2003.
Spear Hook & Line, Fish corral, Gill net
Lethrinidae, Brown patterned Epinephelus, Crabs, Carangidae, Siganidae, Types of Mixed reef fish, Lutjanus bohar,
declines in catches since before
Feel catches are recovering due to better control of blast fishing
Hook & Line
Types of Mixed reef fish, Scomberomorus sp, Tunas,
declines in Plectropomus catches from 10/day to 1-2/day since 1980s
Several exclusive dive resorts on island. Community collaborates with police to stop destructive fishing. Only hook and line allowed on fringing reefs around Mabul
Hook & Line, Gill net, Fish Trap
Brown patterned Epinephelus, Crabs, Lobsters, Types of Mixed reef fish, Lutjanidae,
Reef fish catches down from 5-10 yrs ago but improving since reduction in use of bombs
Have novel community managmement of Mullet aggregation around island. Protect fringing reefs from outsiders using destructive fishing. All interviewees believed this was improving their catches. Bombing in this area since 70s but less in last couple of years.
Long line, Hook & Line, Gill net, Fish Trap
Major (80%+) declines in catches in last 5 years. Large groupers very rare now.
Blame commercial purse seiners too close to shore & lots of fishers
Spear, Hook & Line, Gill net, Fish Trap
Lethrinidae, Brown patterned Epinephelus, Plectropomus sp, Plectropomus maculatus, Carangidae, Types of Mixed reef fish, Dasyatidae, Cheilinus undulatus, Lethrinus nebulosus, Lethrinidae, Brown patterned Epinephelus, Mullidae, Carangidae, Chanos Chanos, Unidentified mullet, Siganidae, Symphorus nematophorus, Plectorhynchus celebicus, Haemulidae, Scomberomorus sp, Tunas, Rays,
80-95% declines in catches reported over 10yrs.
Blame blastfishing and lots of effort, particularly from outsiders including Filippinos. Bajau Laut (Sea Gypsies) keen to see destructive fishing controlled. Sabah Islands Park will include many of these islands in zoned scheme. Core areas around Bohadulong apparently in good condition.
Mgmt & concerns
Catches of maming (Cheilinus undulatus)
generally no adults seen since 80s but apparently two at nearby island
Long line, Gill net, Fish Trap
Epinephelus bleekeri, Epinephelus fuscoguttatus, Brown patterned Epinephelus, Epinephelus lanceolatus, Epinephelus quoyanus, Plectropomus leopardus, Epinephelus coioides, Plectropomus maculatus, Epinephelus sexfasciatus, Carangidae, Lutjanidae,
Live fish per 25 traps declined from 30kg to 5kg in 5 years. Whole catch declined from 100kg to 50kg in same period. Declines noticable since 1990.
Blame lots of fishers
Purse seine Hook & Line, Kelong / Fish corral, Gill net, Driftnets, Fish Trap
Sphyraena sp, Brown patterned Epinephelus, Unidentified clupeid, Crabs, Lobsters, Carangidae, Unidentified mullet, Siganidae, Types of Mixed reef fish, Lutjanidae, Dasyatidae, Scomberomorus sp, Tunas, Unidentified fish,
handline catches declined by over 50% since 80s. Plectropomus declined even more in same period
Blame lots of fishers. Worried about demersal spp but believes pelagics are inexhaustable.
Used to see adults in 70s and 80s in central Darvel Bay
Lok Terusan, Nr. P. Sakar
Kelong / Fish corral, Fish Trap
Caesio cuning, Plectropomus oligocanthus, Epinephelus fuscoguttatus, Brown patterned Epinephelus, Plectropomus leopardus, Carangidae, Siganidae, Lutjanus jonii, Lutjanidae,
declines of trap catches of up to 90% described since 60s
declines blamed on lots of fishers, CN, commercial fishing with lights, trawlers, drifnets, bombs. Can't fish traps on productive soft grounds any more because of trawlers.
still catch some but not targetted.
Kg Teruakan, Nr. P. Sakar
Mgmt & concerns
Catches of maming (Cheilinus undulatus)
NB. Due to the small numbers of interviews at each village and the non-representative sampling design, these summaries cannot be assumed to represent each whole village.
Appendix V. Village locations P. BANGGI P. BALAMBANGAN
Batu Siri Lok Tohog Kobong Laut
villages visited during the survey home villages of fishers interviewed in Kudat
Batu Putih Karakit
Inaruntong Longgom Kecil Kg Tajau Laut Layak Layak PITAS DISTRICT
Tg Kapor Kudat
Kg Teruakan Lok Terusan
Selakan Gusung Melantas Semporna Omadal Menampilik Mabul
Figure 5. Approximate position villages visited and referred to in Appendix IV in the Kudat/Banggi region (top) and the Semporna/Lahad Datu region (lower).
Appendix VI. Sample of Fisheries Department catch statistics The following data was supplied from the Semporna branch of Sabah Fisheries Department and had been collected according to the SMPP (Sistem Maklumat Pengurusan Perikanan, Fisheries Information Management System). Fisheries staff survey a sample of vessels using each type of gear to record catch volume, number of trips/month and number of days fishing then multiply this sample up by the number of vessels known to operate that gear from the port. This was used to generate a mean catch per unit effort (CPUE) for each month for hook and line fisheries (Figure 6). Potential inaccuracies in the data combined with the coarse level of identification preclude the use of this data for identification of the targeting of spawning aggregations.
Ikan batu (reef fish)
0 Jan 03 Feb 03 Mar 03 Apr 03 May 03 Jun 03 Jul 03 Aug 03 Sep 03 Oct 03 Month
Figure 6. Monthly mean catch per unit effort (CPUE) of reef fish species from hook and line operations landing in Semporna in the first ten months of 2003.
Appendix VII. Local vocabulary useful for FSA research or used in this report Apah Bubu JKKK
Kampung Kapal Kelong Ketua Kampung Mancing Mullak Panat Pancing Pehak Piskadul Pukat Pulau Pullak Sampan Sujum Sungai Telur Timbak daing
Male fish gonads Fish box trap Jawatankuasa Kemajuan dan Keselamatan Kampung. Committee (or chair of committee) for the security and development of the village Village (abbreviated to Kg.) Larger, inboard engine fishing boat Fish corral Village headman Fishing (usually with hook and line) Aggregation of fish (Bajau word) Spear Hook, hook and line gear Female fish gonads Mother-dory fishing operations in which the captain pays each fisher for the fish that he catches during the trip Gill net Island (abbreviated to P.) Aggregation of fish (Bajau word) Small one man canoe used in Mother-dory fishing operations Sodium cyanide River or (in a marine context) estuary (abbreviated to Sg.) Eggs Fish bomb (Bajau)
Appendix VIII. Local names of fish species collected during surveys Local Name Alu Alu Anoupin Anupin Asli Baculan Bagaha Bagaha Palu Palu Bagahak Baguan Bakuku Batta Batta Batta Batu Batu Bauiluu Bawal hitam Belais Belais Belanak Belanak Belanak Belaning Belawis Belawis Belawis Bolong Bukan Bulong Bumpheads Dag Dag Dapak Flagtail Grouper Footballer groupers Groupers Haan Haan Ikan Batu Ikan Batu Ikan Merah Ikan Puteh Ikan Putih Ikan Putih Jenis ikan batu Kalui Kalui Katumbak
Scientific Name Sphyraena sp Lethrinus nebulosus Lethrinus nebulosus Plectropomus leopardus Unidentified scombrid Epinephelus fuscoguttatus Epinephelus malabaricus
Family Sphyraenidae Lethrinidae Lethrinidae Serranidae Scombridae Serranidae Serranidae
Epinephelus fuscoguttatus Plectropomus areolatus Plectorhinchus chaetodonoides Epinephelus merra Epinephelus quoyanus Epinephelus ongus Types of Mixed reef fish Argyrops spinifer Chanos Chanos Formio niger Siganus javus Siganidae Liza vaigiensis Liza subviridis Unidentified mullet Tunas Siganus javus
Serranidae Serranidae Haemulidae Serranidae Serranidae Serranidae
Siganidae Siganus guttatus Choerodon anchorago Siganus guttatus Bolbometopon muricatum Siganus vulpinus Siganus virgatus Lutjanus gibbus Cephalopholis urodeta Plectropomus laevis Plectropomus areolatus Lutjanus bohar Types of Mixed reef fish Lutjanidae Lutjanidae Carangidae Caranx ignobilis Carangidae Types of Mixed reef fish Plectropomus oligocanthus Plectropomus sp Lethrinidae
Sparidae Chanidae Formionidae Siganidae Siganidae Muglilidae Muglilidae Muglilidae Scombridae Siganidae Siganidae Siganidae Siganidae Labridae Siganidae Scaridae Siganidae Siganidae Lutjanidae Serranidae Serranidae Serranidae Lutjanidae Lutjanidae Lutjanidae Carangidae Carangidae Carangidae Serranidae Serranidae Lethrinidae
No. times used 1 1 1 1 1 3 1 1 2 1 1 1 4 17 1 2 1 1 8 1 1 4 1 1 1 2 2 1 1 1 1 2 1 1 1 1 1 3 1 2 1 1 2 1 3 1 2
Local Name Kayu Kelabutan Kelawi Kembong Kerapu Kerapu Kerapu Kerapu Kerapu Keratong Kerisi Kerusi Ketam Ketamback Ketambak Ketumbak Ketumbak Ketumbak sokong Ku'au Kubal Kubal Kubing Kumai Kut Kut Kut Kut Kut Kut Kut kut (Batta) Kut Kut Gusing Kut Kut Pasir Lahusu Lampet Lankawit Lanohan Lepe Lepe Leppa Li Pan Licin Lumahan Malapisang Mameng Mamin Maming Mangilap Manila Manila Manila Manila Manksa Meangud Merah Napoleon Obon Ogos
Scientific Name Tunas Cuttlefish Plectropomus oligocanthus Unidentified fish Epinephelus bleekeri Epinephelus fasciatus Brown patterned Epinephelus Epinephelus microdon Epinephelus coioides Epinephelus lanceolatus Lutjanidae Nemipterus sp Crabs Lethrinidae Lethrinidae Lethrinus ornatus Lethrinidae Lutjanidae
Family Scombridae Invertebrates Serranidae Unknownus Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Lutjanidae Nempipteridae Invertebrates Lethrinidae Lethrinidae Lethrinidae Lethrinidae Lutjanidae
Epinephelus areolatus Carangidae Cromileptes altivelis Naso sp Brown patterned Epinephelus Small brown Epinephelus spp (E. merra, ongus etc) Epinephelus quoyanus Epinephelus ongus Epinephelus merra Epinephelus merra Lethrinus miniatus Cheilinus trilobatus Cheilinus undulatus Carangidae Plectrorhinchus sp Haemulidae Plectorhinchus flavomaculatus Epinephelus areolatus Cheilinus undulatus Carangidae Symphorus nematophorus Cheilinus undulatus Cheilinus undulatus Cheilinus undulatus Siganus chrysopilos Plectorhynchus celebicus Plectorhynchus goldmanni Plectorhynchus diagrammus Plectorhynchus lineatus Caranx ignobilis Hemigymnus melapterus Lutjanidae Cheilinus undulatus Epinephelus polyphekadion Scaridae
Serranidae Carangidae Serranidae Acanthuridae Serranidae Serranidae
1 1 1 1 1 3
Serranidae Serranidae Serranidae Serranidae Lethrinidae Labridae Labridae Carangidae Haemulidae Haemulidae Haemulidae Serranidae Labridae Carangidae Lutjanidae Labridae Labridae Labridae Siganidae Haemulidae Haemulidae Haemulidae Haemulidae Carangidae Labridae Lutjanidae Labridae Serranidae Scaridae
2 1 1 1 1 1 1 1 1 1 1 1 5 3 1 5 1 1 1 1 1 1 1 1 1 6 1 1 1
No. times used 2 1 1 1 1 1 16 1 2 1 1 1 3 1 3 1 2 2
Local Name Pari Pari Pasinko Puteh Putih Putih Putih Putih Putih Putih Putih Putih Salai Salai Selar kuning Sulig Sulig Sunoh Sunoh Sunoh Sunoh Sunoh Sunoh Sunoh Asli Sunoh Baguan Sunoh batu Sunoh Bodoh Sunoh hitam Sunoh Kalui Sunoh merah Sunoh negro Sunoh tai sing Sunoh taising Surgeonfish Taballung Tabong Tai sing Taising Tamban Tamudol Tangalla Temanu Temenong Tengerri Tenggeri Timbungan Tokek Tulisan Tutungan Udang Yu
Scientific Name Dasyatidae Rays Plectorhynchus celebicus Carangidae Caranx sexfasciatus Carangoides fulvoguttatus Caranx ignobilis Alectus indicus Alectus ciliaris Atropus atropus Carangidae Atule mate Carangoides fulvoguttatus Atule mate Caesio cuning Caesionidae Plectropomus oligocanthus Plectropomus leopardus Plectropomus sp Plectropomus laevis Plectropomus maculatus Plectropomus areolatus Plectropomus leopardus Plectropomus areolatus Plectropomus leopardus Plectropomus areolatus Plectropomus leopardus Plectropomus oligocanthus Plectropomus leopardus Plectropomus leopardus Plectropomus maculatus Plectropomus maculatus Acanthuridae Trunkfish spp Lutjanus jonii Plectropomus maculatus Plectropomus maculatus Unidentified clupeid Epinephelus ongus Epinephelus fasciatus Atule mate Unidentified fish Scomberomorus sp Scomberomorus sp Mullidae Unidentified Bamboo Sharks Plectorhynchus celebicus Carcharhinus melanopterus Lobsters Unidentified Sharks
Family Dasyatidae Haemulidae Carangidae Carangidae Carangidae Carangidae Carangidae Carangidae Carangidae Carangidae Carangidae Carangidae Carangidae Caesionidae Caesionidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Serranidae Acanthuridae Ostraciidae Lutjanidae Serranidae Serranidae Clupeidae Serranidae Serranidae Carangidae Unknownus Scombridae Scombridae Mullidae Hemiscyllidae Haemulidae Carcharhinidae Invertebrates Carcharhinidae
No. times used 3 1 1 1 1 1 1 2 1 1 12 1 1 1 4 1 5 5 25 3 2 3 1 1 1 2 4 1 11
2 5 3 1 1 1 8 2 1 1 1 2 1 2 6 2 1 1 2 2 1
Appendix IX. Plates
photo: Tim Daw
Plate 1. Epinephelus fuscoguttatus and Epinephelus coioides on sale in a live fish restaurant in Kudat.
Plate 2. Live Cheilinus undulatus for sale in a Kudat restaurant. photo: Tim Daw 52
photo: Tim Daw
Plate 3. Heavily degraded reef in Banggi region with likely damage from blast fishing.
photo: Tim Daw
Plate 4. Large life reef fish holding facility near Lahad Datu
photo: Tim Daw
Plate 5. Larger fishing vessel of the type used for mother/dory operations unloading live fish to a floating cage in Sibogo, Banggi
photo: Tim Daw
Plate 6. The Live Fish Holding facilities at Kudat Esplanade
photo: Tim Daw
Plate 7. Paddled canoes (sampans) used during mother-dory operations equipped for handline fishing for serranids.
photo: Tim Daw
Plate 8. A small kelong or fish corral.
photo: Tim Daw
Plate 9. New plastic bubu (fish traps) supplied to fishers in Selakan by the Fisheries Department
photo: Asri bin Barail
Plate 10. Focus group meeting with fishers in Karakit, Banggi
photo: Asri bin Barail
photo: Tim Daw
Plate 11. Checking identification of local names with a fisher in Palak, Banggi.
photo: Tim Daw
Plate 12. Interviews with Bajau Laut fishers on P. Selakan assisted by the headman of Selakan.
photo: Leo Daim
Plate 13. Interviewing Mr Ho, Life fish trader in Kudat.
photo: Tim Daw
Plate 14. Marcel Eging from WWF with interviewees Kurasia and Laguna on P. Selakan
photo: Tim Daw
Plate 15. Approaching P. Selakan, Semporna Islands Park
photo: Tim Daw
Plate 16. Village at P. Menampilik, Semporna Region
photo: Tim Daw
Plate 17. Village at P. Malawali, Banggi
photo: Tim Daw
Plate19. Pair of adult maming (Cheilinus undulatus) observed separating from a larger group and swimming together off the Sipadan Island reef.
photo: Tim Daw
Plate 18. Dr Annadel Cabanban from UMS and Mhd. Asri bin Barail during transport by local pump boat between stilt villages in Sibogo, Banggi.