WCPFC Harvest Strategy
Harvest Strategy CMM 2014-06
I. Introduction
326.23 KB) and a revision was adopted in 2022 (CMM 2022-03). The objective of the CMM 2022-03 is "To agree that the Commission shall develop and implement a harvest strategy approach for each of the key fisheries or stocks under the purview of the Commission according to the process set out in CMM 2022-03."Table 1. Summary of progress towards implementing the harvest strategy elements for key WCPFC stocks and fisheries.
* CMM 2022-01 Conservation and Management Measure on a Management Procedure for WCPO Skipjack Tuna
# SC19-MI-WP-02 Monitoring the WCPO skipjack management procedure
For the development of a harvest strategy framework, the Scientific Committee noted three expert consultation workshop reports on management strategy evaluation: 1) SC12-MI-WP-05 Report of the Expert Consultation Workshop on Management Strategy Evaluation, 2) SC15-MI-IP-03 Report of the Second Expert Consultation Workshop on Management Strategy Evaluation, and 3) SC16-MI-IP-11 Report on the third external MSE review: Developments in the South Pacific albacore MSE framework).
In December 2021, WCPFC18 noted the importance and need for a Science-Management Dialogue to expedite the progress of implementation on the Indicative Workplan for the Adoption of Harvest Strategies. In August 2022, back-to-back with SC18, WCPFC conducted its 1st Science-Management Dialogue (SMD01). The objectives of the First Science-Management Dialogue Meeting (SMD01) can be viewed in WCPFC-SMD01-2022/BP-01. The second Science-Management Dialogue meeting (SMD-02) is scheduled on 10-12 September 2024.
The following information largely follows the structure and contents of the progress in developing harvest strategies for WCPFC stocks and fisheries (WCPFC-SMD01-2022/BP-02).
II. Skipjack tuna in the WCPO
1. MSE framework for WCPO skipjack
The technical details of the MSE framework for WCPO skipjack were described in SC16-MI-IP-08. This paper outlined the analyses undertaken to develop the operating models (OMs) that comprise the MSE uncertainty grid and sets the range of scenarios across which candidate management procedures (MPs) will be tested. A selected MP is the combination of an agreed data collection program, estimation model and harvest control rule. A description of the generation of simulated data within the framework that will feed into the MP is in SC16-MI-IP-10.
The operating models are divided into a reference set and a robustness set. The reference set is considered to reflect the most plausible hypotheses of fishery and stock dynamics and forms the primary basis for selecting the ‘best performing’ MP. The robustness set comprises scenarios that are considered less likely though still plausible and are used to give a secondary indication of the performance of a reduced subset of MPs. Work continues to finalise the outstanding elements of the OMs that will comprise the robustness set for WCPO skipjack (SC15-MI-WP-06 Considering uncertainty when testing and monitoring WCPFC harvest strategies).
It is considered best practice to identify separate sets of OMs corresponding to a reference set and a robustness set. The reference set of OMs (Table 2.) comprises scenarios considered most plausible and is the priority consideration for the initial selection process when identifying a preferred MP.
Table 2. Skipjack OM uncertainty grid (reference set, 96 scenarios)
Performance indicators (PIs) measure the expected performance of each MP in relation to defined management objectives. They allow managers to identify and select the best performing MP. PIs are calculated from the evaluations across the range of scenarios included in the reference set. The methods for the calculation of the PIs are described in SC14-MI-WP-04 (Performance indicators for comparing management procedures using the MSE modelling framework). The skipjack MSE results are presented for a subset of six PIs (see SC17-MI-WP-04/WCPFC18-2021-13 Evaluations of candidate management procedures for skipjack tuna in the WCPO). Four performance indicators, requested by members, remain under consideration pending further discussion on how they might best be calculated.
Table 3. Performance indicators used to measure the expected success of candidate management procedures for WCPO skipjack at achieving defined objectives
The interim target reference point for skipjack (CMM 2015-06) has been reviewed by SC17 and WCPFC18 (WCPFC18-2021-10 Further updates to WCPO skipjack tuna projected stock status to inform consideration of an updated target reference point: update of SC17-MI-WP-02). This paper includes examination of candidate revised interim skipjack TRPs between 36% and 50% of SBF=0 and requests of the TTMW1 (Tropical Tuna Measure Workshop 1) for estimated fishing mortality under each candidate depletion level.
Management procedures can be broadly classified as either empirical (in which the estimate of stock status is based on relatively unprocessed data e.g., CPUE trends) or model-based (in which the estimate of stock status is determined from an analytical stock assessment). Given the challenges associated with the interpretation of purse seine CPUE, the development of MPs for WCPO skipjack have focused on model-based approaches. The details of the MP for WCPO skipjack are provided in the appendices of SC17-MI-WP-04 (Evaluations of candidate management procedures for skipjack tuna in the WCPO), and the development, testing and performance of the EM is described in SC16-MI-IP-09 (Developing management procedures for WCPO skipjack: The Estimation Model). The evaluation of candidate management procedures for WCPO skipjack are described in SC17-MI-WP-04 and the results are available online for viewing and interrogation using the PIMPLE application (https://ofp-sam.shinyapps.io/pimple2022/), to aid interrogation of the results and the selection of preferred options. The range of MPs for which results are presented has been modified from previous years and the numbering of the harvest control rules (HCRs) has changed. Note also the very recent addition of an extra MP (HCR9) based on a hybrid form of HCRs 2 and 6.
The design of the skipjack MPs and the structure of the evaluation framework comprise a number of features:
- A 3 year management period is assumed (based upon the output of the management procedure the level of fishing is set for a 3 year period, before the MP is again run to define the level of fishing for the next 3 year period);
- All fisheries, except longline and archipelagic fisheries, are subject to control by the MP;
- Purse seine fisheries are managed through effort controls and all other fisheries are managed through catch controls;
- The reference year for catch and effort scaling 2012;
- For some HCRs, constraints apply that limit the change in catch or effort between management periods.
2. Monitoring strategy
The monitoring strategy: 1) collects the necessary data from the fishery to calculate performance indicators (PIs) that are the same as (or as close as possible to) the PIs calculated from the evaluations, and routinely checks that the observed performance of the management procedure is consistent with expected performance from the evaluations (SC16-MI-IP-02); and 2) monitors the collection of new data to ensure that the basis of the evaluation framework and scenarios included in the uncertainty grid remain valid and appropriate.
As part of the monitoring strategy a stock assessment may be conducted. This stock assessment is different from the very tightly specified assessment that is conducted as part of the MP. Its purpose is to calculate PIs that are generated from stock assessment outputs (e.g. SB/SBF=0) and to check that the evaluation framework continues to adequately represent the stock and fishery dynamics.
3. Summary of harvest strategy development status
SMD01 agreed on the following activities for the skipjack management procedures (MPs):
- retain HCRs 1, 2, 5, 6, 9 for skipjack MPs, and provide equivalent results, with a 10% constraint in place for all of these, noting CCMs’ differing preferences.
- analyse the use of effort controls for the pole and line fishery, rather than using catch, and assume a baseline of the 2001-2004 average.
- use P&L effort for TRP presentations to WCPFC19.
- analyse the status of small-scale fisheries (<2000 MT) and fisheries in territorial waters within MP controls.
SMD01 further agreed that SSP would do the following additional work prior to WCPFC19:
- Run MPs (HCRs) 6 & 9 with a 10% constraint.
- Perform specific robustness set runs (see SC outcomes).
- Perform evaluations with effort-based P&L control.
- Provide performance indicators for P&L CPUE in PIMPLE.
III. South Pacific albacore tuna in the WCPO
Interim target reference point for South Pacific albacore
WCPFC15 agreed on an interim target reference point (TRP) for South Pacific (SP) albacore at 56% of spawning stock biomass in the absence of fishing (0.56SBF=0) with the objective of achieving an 8% increase in CPUE for the southern longline fishery as compared to 2013 levels. If a future stock assessment indicates that this interim TRP will not result in the desired longline CPUE, then the interim TRP will be revised in order to meet this objective. The TRP shall be reviewed every 3 years, consistent with the SP albacore assessment schedule. In order to manage the required reduction in catches, the timeline for achieving the interim target reference point shall be no later than 20 years.
As requested by the SC17, SPC-OFP recalibrated the WCPFC interim TRP that would on average achieve the agreed objective of an 8 % increase in vulnerable biomass (CPUE proxy) for the southern longline fishery as compared to 2013 levels, and undertook projections to estimate the constant catch levels that would achieve the recalibrated TRP, on average, over the long-term. The results of the requested analyses are in WCPFC18-2021-17 (Recalibration of SP albacore TRP).
Trajectories to achieve the South Pacific albacore interim TRP
As requested by WCPFC15, the SC15 reviewed performance of stochastic stock projections across the grid of 72 assessment models under future fishery scenarios to examine their performance in recovering the stock to the TRP (SC15-MI-WP-02, Alternative trajectories to achieve the South Pacific albacore interim TRP). This paper was updated for the WCPFC16 (WCPFC16-2019-19) and for SC16 (SC16-MI-IP-01) considerations. Given the new stock assessment agreed at SC17, and the corresponding TRP recalibration, trajectories to achieve a recalibrated TRP will be the subject of further discussion.
1. MSE framework for South Pacific albacore tuna
An initial MSE framework for South Pacific albacore was first outlined in SC15-MI-WP-08 (South Pacific albacore management strategy evaluation framework) and the MSE framework was externally reviewed in SC16-MI-IP-11 (Report on the third external MSE review: Developments in the South Pacific albacore MSE framework). The modeling framework, including conditioning of the OMs and the elements of the MSE uncertainty grid for South Pacific albacore may be reviewed in the light of the most recent stock assessment (SC17-SA-WP-02 and SC17-SA-WP-02a) and could be revised if the current ranges of uncertainty are considered insufficient or inappropriate. The derivation and calculation of performance indicators for South Pacific albacore is detailed in SC15-MI-WP-03 (Performance indicators for comparing management procedures for South Pacific albacore using the MSE modelling framework).
Recent work has focused on resolving a number of key technical challenges, most notably the process for generating simulated catch and effort data that sufficiently reflect the level of variability observed in real data. Unlike skipjack, the assessment of South Pacific albacore is heavily reliant on available CPUE information. A CPUE hindcasting analysis to examine how effectively catch and effort can be simulated within the South Pacific albacore evaluation framework was outlined in SC16-MI-IP-04 and is further developed in SC17-MI-IP-01. It highlights the difficulty in generating realistic nominal CPUE at the fishery level but indicates that, for some model regions, simulated CPUE for standardised index fisheries may be used as a basis for testing empirical MPs. However, it will also be necessary to develop candidate model-based management procedures (MPs) for South Pacific albacore following the recent testing of a range of empirical approaches.
2. Candidate management procedures
Under the initial technical workplan for developing harvest strategies for South Pacific albacore (SC14-MI-WP-02 Technical aspects of a potential South Pacific albacore harvest strategy), the primary focus was to develop empirical MPs using longline CPUE as the indicator of stock status that is input to the HCR. SC16-MI-IP-05 (HCR design considerations for South Pacific albacore) presented the results of South Pacific albacore MSE analyses conducted for empirical MPs along with a number of design considerations for HCRs that take either CPUE or size composition data as input. SC15-MI-WP-07 (CPUE analysis for South Pacific albacore) examined CPUE data and standardisation approaches (both traditional CPUE analysis and geostatistical analysis) to inform this process.
Analyses conducted to date have demonstrated the relative advantages and disadvantages of empirical MPs. On the one hand, they are very simple in concept, often require minimal processing of input data and can be more closely aligned with economic objectives related to catch rates and vessel profitability. On the other, they rely heavily on having a CPUE index that reliably tracks overall stock abundance. Such indices can be difficult to identify for a very widely dispersed stock for which multiple assessment regions are considered. Model-based approaches can address some of these issues (below) and a next step in the development of harvest strategies for South Pacific albacore would be to develop and test model-based MPs that use relatively simple biomass dynamic assessment models.
CPUE for South Pacific albacore
Noting the comments of CCMs concerning the stability of the simulated CPUE for South Pacific albacore, a retrospective forecasting was performed to test model predictions using existing historical data (SC16-MI-IP-04 Retrospective CPUE forecasting for the South Pacific albacore), which was updated in SC17-MI-IP-01 (Retrospective forecasting of CPUE for South Pacific albacore). Retrospective forecasting or hindcasting is a method for testing the performance of a predictive model using existing historic data. Results from the retrospective analysis showed evidence of a trend for underestimation of adult biomass with successive removal of years from the data in some model regions. However, in some instances, the forecasted standardized CPUE time-series showed potential to be used as a stock status indicator in the harvest strategy of South Pacific albacore.
Further work is required to test the performance of MPs using CPUE as a stock status indicator to drive future fishing opportunities, and it was recommended that alternative approaches to estimating stock status within the MP using simple models (i.e. biomass dynamic model) be explored and compared with the empirical CPUE approach.
3. Monitoring strategy
The monitoring strategy for South Pacific albacore has received relatively little attention to date, although much of the work undertaken to develop the monitoring strategy for skipjack can be similarly applied to South Pacific albacore, particularly in situations where the management objectives and hence performance indicators for the stocks and fisheries are similar.
4. Summary of harvest strategy development status
For South Pacific albacore, it may be necessary to re-visit the conditioning of the operating models and structural uncertainties in the light of the most recent assessment, although this depends to a large extent on the outcome of the stock assessment modeling work, the development on model-based MPs, and the considerations of the Scientific Committee. Following the initial investigation of empirical management procedures, that used estimates of stock status determined from longline CPUE as inputs to the harvest control rule (SC15-MI-WP-08), current work focusses on the development of model-based management procedures.
SMD01 agreed that additional work to be conducted by the SSP to support decision-making on SPA MPs. Regarding the geographic application of the SPA MP, SMD01 asked SSP to include the EPO for work done between now and WCPFC19, to include the entire area south of the equator, and to use the 2021 stock assessment, and regarding the application of the SPA MP to fisheries, to examine how large an impact the troll fishery.
IV. Bigeye and yellowfin tunas in the WCPO
WCPFC12 agreed to a workplan for the adoption of harvest strategies for WCPO skipjack, bigeye, yellowfin and South Pacific albacore tuna. These four stocks are caught by an overlapping mix of fisheries. Management measures for one stock will impact fisheries that catch other stocks. An important consideration when developing harvest strategies for these stocks is to account for mixed fishery interactions.
1. TRPs for bigeye and yellowfin tuna
At SC15, risk-based TRPs for bigeye and yellowfin tuna were introduced (SC15-MI-WP-01, Minimum Target Reference Points for WCPO yellowfin and bigeye tuna consistent with alternative LRP risk levels, and multispecies implications) and the ‘minimum’ spawning-biomass-depletion-based TRPs for yellowfin and bigeye tuna were updated for WCPFC16 by applying the 2019 skipjack tuna stock assessment (WCPFC16-2019-15, Minimum target reference points for WCPO yellowfin and bigeye tuna consistent with alternative LRP risk levels, and multispecies implications).
Noting the request from WCPFC16 to provide advice on the formulation of TRPs for bigeye and yellowfin tuna (paragraphs 273-275, WCPFC16 Summary Report), SC16 reviewed SC16-MI-WP-01 (Further consideration of candidate target reference points for bigeye and yellowfin tuna in the WCPO) and requested the Scientific Services Provider undertake the analyses for bigeye and yellowfin tuna according to the criteria outlined in the Paragraph 211-212 of the SC16 Summary Report. Accordingly, WCPFC17 reviewed WCPFC17-2020-12 (SC16-requested analyses to inform WCPFC17 discussions on candidate target reference points for WCPO bigeye and yellowfin tuna), and agreed that it would be difficult to identify TRPs for bigeye and yellowfin during WCPFC17 and to continue its consideration in the future. SC17 reviewed SC17-MI-WP-01 (Updated WCPO bigeye and yellowfin TRP evaluations), noting that impacts on skipjack tuna depletion associated with relative changes to fishing levels to achieve a candidate bigeye tuna TRP are contingent on the proportion of fishing scalars related to purse seine fishing that target skipjack tuna.
This paper was updated in WCPFC18-2021-11 (Updated WCPO bigeye and yellowfin TRP evaluations with considerations for SP albacore) by presenting results of analyses, requested by SC16, WCPFC16 and SC17, to assist WCPFC18 in the identification of interim target reference points for WCPO bigeye and yellowfin tuna stocks and to consider the implications of candidate bigeye and yellowfin TRPs for all four key tuna stocks.
2. Mixed fishery framework
The mixed fishery framework involves developing stock specific MPs for skipjack, South Pacific albacore and bigeye, in line with the agreed WCPFC harvest strategy workplan. The interaction of these MPs, as well as their impact on yellowfin, would then be evaluated using a combined evaluation framework. An implementation of this approach for skipjack, bigeye and yellowfin is described in the latest document SC17-MI-WP-05 (Mixed-fishery harvest strategy developments) which demonstrates an initial attempt at considering multi-species and mixed fisheries interactions based on single stock operating models (OMs) for skipjack, bigeye and yellowfin.
This proof of concept analysis demonstrates that the technical challenges involved in implementing the multi-species modeling framework can be addressed and the conceptual approach remains tractable. The initial results are sufficiently encouraging to support the continued development of this approach.
3. Summary of harvest strategy development status
The approach of the harvest strategy workplan has been to concentrate initially upon the two stocks which is the subject of primarily ‘stand-alone’ fisheries, being skipjack (purse seine/pole and line) and South Pacific albacore (southern longline/troll). This provided a technically tractable approach to the development of corresponding management procedures.
However, the activities of most fishing gears have impacts on other tuna stocks. It is therefore important to consider mixed fishery interactions when developing harvest strategies. SC15 agreed to consider the technical multi-species modelling framework for initial development of mixed fishery harvest strategies. Under this framework, fisheries are managed through single stock management procedures for skipjack, bigeye and South Pacific albacore. This approach should be regarded as an initial attempt at considering multispecies and mixed fisheries. If this approach is found to be unsuccessful in terms of achieving objectives for all four stocks, alternative approaches will need to be developed.
V. Stakeholder engagement and capacity building
The roles of scientists and managers and the key decisions and areas for advice from both the Scientific Committee and the Commission have been outlined in previous reports (SC14-MI-WP-05 Key decisions for managers and scientists under the harvest strategy approach for WCPO tuna stocks and fisheries). SPC-OFP provided a number of web-based tools in SC17-MI-IP-02 (Capacity building and stakeholder engagement activities for WCPFC harvest strategies) related to capacity building, decision making, and a harvest strategy Moodle course.
1. Capacity building tools
Interactive R-Shiny training tools allow users to explore the development and performance of HCRs and MPs:
-
- Introduction to Harvest Control Rules (https://ofp-sam.shinyapps.io/amped-intro-hcr/)
- Introduction to Performance Indicators (https://ofp-sam.shinyapps.io/amped-intro-indicators/)
- Comparing Performance of Management Procedures (https://ofp-sam.shinyapps.io/amped-comparing-performance/)
2. Decision making tools
A key component of the harvest strategy process is selection of preferred MPs using performance indicators. To help facilitate this process, interactive decision making tools have been developed by SPC.
These tools allow stakeholders and managers to explore the results of the skipjack and South Pacific albacore MSE simulations and compare the relative performance of the candidate MPs. Manuals and cheat-sheets for these tools are available via the tool websites.
-
- PIMPLE for skipjack (https://ofp-sam.shinyapps.io/pimple2022/)
- SPAMPLE for South Pacific albacore (https://ofp-sam.shinyapps.io/spample/)
Additional tools may be necessary to explore the results of the mixed-fishery MSE simulations. Conditioning of operating models (OMs) is an important component of the MSE development process. An interactive tool has been developed to explore the diagnostics of the OMs currently used in the skipjack evaluation process: Hierophant (https://ofp-sam.shinyapps.io/hierophant/). Similar tools can be developed for the OMs of the other stocks.
3. Harvest strategy Moodle course
Moodle is a widely used on-line learning platform that facilitates the delivery of training materials in multiple formats. An ‘Introduction to Harvest Strategies’ training course is being developed using the SPC’s Moodle site. It is anticipated that this will become a key source of reference and learning material for WCPFC members and currently contains information on many aspects of harvest strategies, including management objectives, performance indicators, reference points, MPs and MSE.
It is possible to access the course (still under development) from the main page by using a ‘guest’ login (https://spc.learnbook.com.au/login/index.php).
4. Others
Pacific Island Fisheries Professionals (PIFP) are one year positions at SPC where the PIFP works alongside SPC staff on a specific project, before returning to their home country. The PIFP positions provide a longer-term type of capacity building for a small number of people. SPC has had one PIFP (in 2020) focused on harvest strategies, and aims to have another PIFP working in this area in 2022.
SPC are also running training workshops with fisheries agencies throughout the region, that have so far involved over 260 people across 17 workshops.
A harvest strategy poster will soon be distributed to members and stakeholders to help raise awareness of the process. This will be followed up by short information leaflets that focus on particular harvest strategy components. A series of short information films are being produced that will complement the other engagement material, the first training movie can be accessed here (https://www.youtube.com/watch?v=zM3B9DLmtZg).
Prior to the first Science-Management Dialogue meeting (SMD01) in August 19th and 22nd, 2022, two WCPFC harvest strategy capacity building seminars were held in June and July this year. The purpose of these seminars is to build members’ capacity to enable them to fully participate in the harvest strategy discussions during the SMD01.
The first capacity building seminar was conducted virtually on the 8th June 2022 that was hosted and facilitated by the Secretariat in collaboration with SSP and was attended by around 92 CCM participants including the Secretariat. The first seminar provided a general overview of the harvest strategy approach including key management objectives and their associated performance indicators, the design and testing of alternative candidate management procedures, and methods for monitoring the performance of a management procedure once implemented. The SSP gave their presentations on the various topics covered, and enough time was allocated for discussions, questions, clarifications and answers.
The second seminar was held on Thursday, 07 July 2022, which will focus on the methods for selecting a preferred management procedure including the consideration of mixed fishery performance indicators.
A harvest strategy Slack group has been set up to provide an informal communication channel with members. There are now over 70 members. Please contact Dr. Finlay Scott at SPC (finlays@spc.int) if you would like to join. For enquiries to SPC on the technical work supporting the development of harvest strategies or training workshops, please contact: fame-harvest-strategies@spc.int
VI. Limit reference points (LRPs)
WCPFC8 approved a number of the SC7 recommendations related to limit reference points.
1) The agreed working definition for LRPs is to be based on the following principles:
- they define a state of the fishery that is considered to be undesirable and which management action should avoid;
- the probability of breaching an LRP should be very low;
- management actions should be taken before the fishery falls below or is at risk of falling below an LRP.
2) The hierarchical approach (as outlined in SC7-MI-WP-03) to identify key LRPs for key target species in the WCPFC is as follows:
|
Level |
Condition |
LRPs |
|
Level 1 |
A reliable estimate of steepness is available |
FMSY and BMSY |
|
Level 2 |
Steepness is not known well, if at all, but the key biological (natural mortality, maturity) and fishery (selectivity) variables are reasonably well estimated. Applied species: bigeye, yellowfin and South Pacific albacore |
FX%SPRo and either X%SBo or X%SBcurrent,F=0 |
|
Level 3 |
The key biological and fishery variables are not well estimated or understood. Applied species: skipjack |
X%SBo or X%SBcurrent,F=0 |
Note: SPR refers to the spawning-potential-per-recruit, and SBrecent,F=0 refers to the estimated average spawning biomass over a recent period in the absence of fishing).
SC10 noted that the Commission endorsed SC’s recommendation for a 10 year time window in relation to the LRP 20%SBF=0, t1-t2 based on the years t1=ylast-10 to t2=ylast-1 where ylast is the last year used in the assessment. It was also note that the Commission had not seen the need to adopt an equivalent F-based reference point as this was seen as redundant given the adoption of a biomass-based LRP.
Discussions of biological limit reference points for other stocks (billfish, sharks) are ongoing at Scientific Committee (see SC16-MI-IP-21, SC17-MI-WP-07, SC17-MI-WP-08).
VII. Acceptable risk level of exceeding LRP
At WCPFC12, the Commission noted that the SC10 had considered levels of risk associated with breaching the LRP within the range 5-20% and that the identification of acceptable risk is a management issue. The Commission agreed to identify the level of acceptable risk which should be applied to breaching a LRP for the key target species, noting that the UN Fish Stocks Agreement states that the risk of exceeding LRPs should be very low.
At WCPFC13 (Paragraph 296, WCPFC13 Summary Report), the Commission agreed to:
a) not specify, at this time, acceptable levels of risk of breaching the limit reference point for each stock;
b) consider any risk level greater than 20 percent to be inconsistent with the LRP related principle in UNFSA (as referenced in Article 6 of the Convention) including that the risk of breaching limit reference points be very low; and
c) determine the acceptability of potential HCRs where the estimated risk of breaching the limit reference point is between 0 and 20%.
VIII. North Pacific striped marlin - Stock Rebuilding Plan
The Commission at WCPFC16 adopted the Interim Rebuilding Plan for North Pacific Striped Marlin (Attachment L, WCPFC16 Summary Report).
IX. Links to WCPFC MOW and HSW materials and outcomes
Four WCPFC workshops have been held on Management Objectives and Harvest Strategies from 2012 - 2014. These workshops were held as informal meetings of stakeholders with an interest in WCPO tuna fisheries, that were convened by the Commission to facilitate and support the development of harvest strategies by Commission Members. Links to the relevant meeting pages and reports:
- MOW1: 28 - 29 November 2012, Manila, Philippines: https://www.wcpfc.int/meetings/wcpfc-management-objectives-workshop
- MOW2: 28 November 2013, Cairns, Australia: https://www.wcpfc.int/meetings/wcpfc-management-objectives-workshop-2
- MOW3: 28 November 2014, Apia, Samoa: https://www.wcpfc.int/meetings/wcpfc-management-objectives-workshop-3
- MOW4/HSW: 30 November - 1 December, Bali, Indonesia: https://www.wcpfc.int/meetings/wcpfc-harvest-strategy-workshop
Northern Stocks
North Pacific Albacore
Harvest Strategy for North Pacific Albacore Fishery
At the sixth session of the Northern Committee (NC6) in 2010, and consistent with Article 6 (Application of the precautionary approach) of the WCPFC Convention, Canada submitted a paper (NC6-DP-02) on the development of a precautionary approach based fishery management regime for the northern stocks. Building on this paper, NC7 agreed to incorporate this development into its Work Program for 2012-2015.
The NC9 determined that it was best to delay discussions on the framework until the completion of the 2014 North Pacific albacore stock assessment. In July 2014, the International Scientific Committee for Tuna and Tuna-like Species in the North Pacific Ocean (ISC) concluded that the North Pacific albacore stock is “healthy and that current productivity is sufficient to sustain recent exploitation levels, assuming average historical recruitment in both the short and long term”. The ISC also provided further advice regarding candidate limit and target reference points.
Based on the advice from the ISC, the NC10 in 2014 recommended, and the 11th regular session of the Commission (WCPFC11) adopted a Precautionary Management Framework for North Pacific Albacore. In December 2017, the Commission (WCPFC14) adopted an Interim Harvest Strategy for North Pacific Albacore Fishery (HS-2017-01) as recommended by the NC13, which replaced the Precautionary Management Framework for North Pacific Albacore. After five years, the Commission adopted an updated harvest strategy HS 2022-01 and recently adopted HS 2023-01 (Harvest Strategy for North Pacific Albacore Fishery) in December 2023. Refer to the latest version for the detailed elements of harvest strategy for this fishery.
Pacific Bluefin Tuna
Harvest Strategy for Pacific Bluefin Tuna Fisheries
The Connission adopted a Harvest strategy for Pacific Bluefin Tuna Fisheries (HS-2017-02) in 2017, and adopted a revision HS 2022-01 at WCPFC19, and recently adopted HS 2023-02 at WCPFC20.
Refer to the latest version HS 2023-02 for the details of harvest strategy elements for Pacific bluefin tuna fisheries.
North Pacific Swordfish
The NC14 agreed to adopt the following management objectives for NP swordfish; “The management objective is to support thriving swordfish fisheries in the North Pacific while maintaining the stock size at levels capable of producing maximum sustainable yield. The Northern Committee will develop more refined management objectives.” In December 2019, the Commission accepted the recommendation from the NC15 on the Harvest Strategy for North Pacific Swordfish Fisheries (HS 2016-01).
In 2022, the Commission adopted CMM for North Pacific Swordfish (CMM 2022-02), which was revised in 2023 (CMM 2023-03). Refer to CMM 2023-03 (CMM for NP Swordfish) for CCM’s responsibilities.
Key Documents