Indonesian Tuna Protocol Sampling. Case Study on Catch Monitoring in Benoa Port, Bali, Indonesia

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Indonesian Tuna Protocol Sampling CCSBT-ESC/1708/Info 03 (ESC Agenda item 4.1) Case Study on Catch Monitoring in Benoa Port, Bali, Indonesia Irwan Jatmiko 1), Zulkarnaen Fahmi 1), Bram Setyadji 1) and Fathur Rochman 1) 1) Research Institute for Tuna Fisheries, Bali Introduction Indonesia plays an important role in the world's tuna fisheries. In 2011, the world's tuna production amounted to 6.8 million tons and in 2012 it increased to more than 7 million tons (ISSF, 2015). The average production of tuna, skipjack and neritic tuna in Indonesia from 2005-2012 amounted to 1,033,211 tons. Thus, Indonesia supplies more than 16% of the world's tuna production. Furthermore, in 2013, the export volume of tuna, skipjack and neritic tuna reached about 209,410 tons with a value of USD $ 764.8 million (P2HP, 2014). In addition, Indonesia is also the largest contributor of production among 32 member countries of the Indian Ocean Tuna Commission (IOTC) with an average production from 2009-2012 at 356,862 tons/year (25.22%) (IOTC, 2015). Moreover, the production of tuna has contributed significantly to Indonesian capture fishery production. With total tuna, skipjack and neritic tuna species production from 2005-2012 with average of 1,033,211 tons/year tuna fishery contribute about 20% of total national fishery production (DGCF, 2015). Fishery data is an important aspect for understanding basic biology, species distribution and fish stock population dynamics. According to the source, data can be divided into two types, dependent data and independent data. Dependent data can be collected from ship logbooks, interviews, company records processing, port inspections, etc. While independent data is collected from systematic scientific samples such as: scientific monitoring program, underwater visual census, acoustic method etc. The advantages of each data may differ in terms of quality, quantity and cost. The key benefit of fisheries data is to provide information for decision makers to manage sustainable fisheries management strategies (King, 2010).

As a member of the world food organization Food and Agricultural Organization (FAO), Indonesia adopted the Code of Conduct for Responsible Fisheries (CCRF). One of the purposes of this code of conduct is to implement national policies in the context of responsible fisheries resources management and conservation (FAO, 1995). This goal is implemented by the Indonesian government into the national fisheries law No. 45/2009 which states that the utilization of fisheries is based on the principles of benefit, justice, partnership, equity, integration, openness, efficiency and sustainable conservation (Fisheries Act, 2009). Therefore, it is essential to provide tuna fishery protocol sampling to collect information and monitoring to support proper management strategy for tuna fisheries. Protocol Sampling The enumerator (data collector) shall be obliged to monitor and record in detail coverage all the basic information of each landing vessel. All tuna landing from catcher or a collecting vessels were observed in the following way: 1. Enumerator cooperates with the local Marine and Fisheries Resources Control Officer (PSDKP) to obtain data on the vessels name and its catch; 2. Enumerator cooperate with fishing company (processing plant); 3. Enumerator directly monitors and records the vessels name, the total number of landed vessels and total catch per vessel per day. During measurement, enumerator should record the total catch data of each species (the number and weight of all species including non-tuna species) and information on the fishing effort of all landed tuna longline. Data on catches and fishing efforts can be obtained from Marine and Fishery Resources Control Officers (PSDKP) or from interview with captains or fishermen of fishing companies. Such information should be recorded on the Vessel Landing Form. Data on the total number of catches of each tuna must be obtained regardless of whether the vessel is sampled or not. This data is required to provide important and

accurate information on the total volume of catches of tuna longline vessels and will be used to obtain accurate estimates of catch per species when combined with sampled data. The following instructions are used to enumerate tuna longline fishing vessels and collecting vessels that landed their catch at the fishing port: 1. Record the number of all vessels and the vessels name which landed their daily catches into the Vessels Landing Form; 2. In the planning to sampled catch of tuna longline, the target coverage is at least 30% of the number of landed longline tuna in each fishing company. The unit of recording of catches of tuna longline vessel is one ship unit. For example, if within one month there are 12 vessels landed their catch, then 3 vessels should be sampled their catches of the fishing company; 3. Determined a longline tuna longline vessel to be sampled. The sampling priority is the lowest percentage of the number of landed vessels divided by the number of sampled vessels in each fishing company; 4. The most important thing to verify is that every individual fish that represents all the fish caught from the tuna longline must be recorded. If the weight per individual of tuna cannot be recorded, it is not allowed to make an estimate of the data itself. Registration of individual weights for all tuna longline catches, will ensure that there is no bias in terms of sorting data by weight or by species; 5. Length measurements are conducted using calipers that have a precision of up to 0.5 cm. Length sizes are shown in order of priority according to international measurement standards. If not possible to measure the length of all fish catches, then measuring the length of the rejected fish can already be recorded as a random sampled (IOTC, 2002). Several data collected are important to monitor and support management strategies, i.e.:

1. Number of landed and sampled vessels (Appendix 1). This information can be used to estimate the total production. 2. Information about catch condition (Appendix 2). 3. Catch composition per species (number) (Appendix 3). 4. Length and weight information that used to determine percentage of length distribution (Appendix 4), length distribution (Appendix 5) and length-weight relationships (Appendix 6). 5. Length information can also be used to determine some population parameters such as length infinity, growth coefficient and natural mortality etc. using datalimited tools approach. Estimation of total production can be calculated using formula modification from IOTC (2012): CM = LM * AVM Where: CM LM : Estimation of total production per month (ton) : Number of landed vessels per month which landed SBT (unit) AVM : Production from sampled vessels per month which landed SBT (ton)/number of total vessels per month per processing plant which landed SBT (unit) References Directorate General Capture Fisheries (DGCF). 2015. Fisheries Management Plan: Tuna, Skipjack, Neritic tuna. Directorate General Capture Fisheries, Ministry of Marine and Fisheries Affairs. Jakarta, Indonesia. Food and Agricultural Organization (FAO). 1995. Code of conduct for responsible fisheries. Rome, Italy. 41 pp.

Indian Ocean Tuna Commission (IOTC). 2002. Field manual for data collection on tuna landings from longliners. Secretariat of IOTC. Seychelles. 21pp. Indian Ocean Tuna Commission (IOTC). 2015. Report of the 18 th Session of the IOTC Scientific Committee. Bali, Indonesia, 23-27 November 2015. IOTC-2015-SC18- R[E]. International Seafood Sustainability Foundation (ISSF). 2015. ISSF Tuna Stock Status Update, 2015: Status of the world fisheries for tuna. ISSF Technical Report 2015-03A. International Seafood Sustainability Foundation, Washington, D.C. USA. King, M. (2010). Fisheries Biology, Assessment and Management, Second Edition (p. 381). Oxford, England: Blackwell Publising Ltd. Undang-Undang Republik Indonesia. 2009. Undang-Undang Republik Indonesia Nomor 45 Tahun 2009 tentang Perubahan Atas Undang-Undang Nomor 31 Tahun 2004 tentang Perikanan.

Appendix 1. Number of sampled and landed vessels and its proportion at Benoa Port in 2016. Month Landed vessels Sampled vessels Percentage (%) January 50 34 68.00 February 46 26 56.52 March 72 37 51.39 April 66 37 56.06 May 54 36 66.67 June 98 47 47.96 July 47 29 61.70 August 63 38 60.32 September 64 35 54.69 October 87 59 67.82 November 42 33 78.57 December 31 23 74.19

Appendix 2. Catch condition of SBT production at Benoa Port in 2016. 44% 56% Frozen Fresh

Species Code Appendix 3. Catch composition at Benoa Port in 2016. BET YFT ALB SBT BSH MON LEC SWO OIL WAH BUK ALH CDF SFA TUN SSP HEE TST BUM MLS MSO BLM SKJ OCS TCR SSH 4.32% 3.95% 2.25% 1.06% 0.69% 0.52% 0.48% 0.34% 0.33% 0.32% 0.26% 0.20% 0.18% 0.17% 0.15% 0.13% 0.08% 0.06% 0.05% 0.05% 0.00% 6.95% 11.89% 17.20% 22.21% 26.15% 0% 5% 10% 15% 20% 25% 30% Percentage

Number of fish Unit: Number of fish Code Common name Scientific name Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Total BET Bigeye Thunus obessus 2,524 2,440 2,423 2,918 2,621 2,711 2,057 4,237 3,675 4275 2466 2068 34,415 YFT Yellowfin Thunnus albacares 1,337 670 2,029 4,150 4,804 4,368 3,864 2,563 1,036 2384 1156 868 29,229 ALB Albacore Thunnus allalunga 81 240 1,375 3,206 2,924 2,596 935 628 4,583 4834 863 378 22,643 SBT Southern bluefin tuna Thunnus maccoyii 1,146 1,276 1,956 1,181 194 42 125 71 1,750 3723 1416 2773 15,653 BSH Blue shark Prionace glauca 273 2 254 1,044 672 150 311 9 2,171 2356 630 1276 9,148 MON Moon fish Lampris guttatus 380 10 33 168 391 392 564 2,090 1401 86 175 5,690 LEC Escolar Lepidocybium flavobrunneum 277 61 302 503 221 86 415 361 1,212 1435 136 192 5,201 SWO Swordfish Xiphias gladius 124 72 276 270 179 87 172 306 581 564 126 209 2,966 OIL Oilfish Ruvettus pretiosus 46 93 57 76 34 25 64 31 370 384 132 82 1,394 WAH Wahoo Acanthocybium solandri 39 25 99 100 65 46 99 119 98 183 3 37 913 BUK Butterfly king fish Gasterochisma melampus 49 278 32 40 9 117 118 38 2 683 ALH Slickheads nei Alepocephalus spp 2 57 53 43 127 204 99 45 6 636 CDF Common dolphinfish Coryphaena hippurus 8 31 26 13 9 47 70 120 107 6 8 445 SFA Sailfish Istiophorus platypterus 10 1 64 44 44 4 56 37 77 50 14 39 440 TUN Juvenile tuna Thunnus sp. 38 21 11 295 1 5 21 28 2 422 SSP Shortbill Spearfish Tetrapturus angustirostris 3 22 4 4 13 37 48 202 4 337 HEE Long nose chimaeras Harriotta spp 4 5 8 39 3 70 106 12 18 265 TST Sickle pomfret Taractichthys steindachneri 2 2 9 5 10 35 12 39 107 7 10 238 BUM Blue marlin Makaira mazara 9 15 58 36 17 4 14 18 19 16 1 12 219 MLS Stripped Marlin Tetrapturus audax 35 23 15 2 3 4 31 21 34 2 31 201 MSO Mako sharks Isurus oxyrhynchus Is 4 11 23 2 4 26 61 8 27 166 BLM Black Marlin Makaira indica 15 14 10 24 8 1 5 10 15 7 2 111 SKJ Skipjack tuna Katsuwonus pelamis 3 3 1 53 11 2 6 79 OCS Oceanic whitetip shark Carcharhinus longimanus 13 13 11 2 3 9 1 1 4 8 1 66 TCR Pomfret Taractes rubescens 5 1 5 26 2 16 4 3 62 SSH Silky Shark Carcharinus falciformis 2 0 2

Appendix 4. Percentage of length distribution of southern bluefin tuna (T. maccoyii) landed at Benoa Port in 2016. 11% <= 150 cm > 150 cm 89%

80 90 100 110 120 130 140 150 160 170 180 190 200 210 Frequency Appendix 5. Length frequency of southern bluefin tuna (T. maccoyii) landed at Benoa Port in 2016. 400 350 300 250 200 150 100 50 0 Fork length (cm)

Weight (kg) Appendix 6. Length-weight relationship of southern bluefin tuna (T. maccoyii) landed at Benoa Port in 2016. 200 180 160 140 120 100 80 60 40 20 0 y = 2E-05x 2.9928 R² = 0.8274 100 120 140 160 180 200 220 Fork length (cm)