Developing a management procedure based recovery plan for southern bluefin tuna
There is an immediate and strategic need for the CCSBT to agree to an MP to guide the global catch setting to ensure the rebuilding of the SBT stock. For this to occur, an MP needs to be developed and agreed by the CCSBT; failure to do so will result in the global catch of SBT being reduced to 5000-6000 t, with a subsequent significant impact on the Australian SBT fishery. Australia in collaboration with Japanese and other CCSBT member scientists are responsible for the development and evaluation of the MP, which in the context of a Regional Fisheries Management Organisation (RFMO), such as CCSBT, is a unique and innovative concept that will establish a rebuilding pathway for the stock. Having a rebuilding strategy that has been rigorously and openly tested, is robust to the key fishery-specific issues and uncertainties, and establishes a process whereby decisions will be made and enforced will be a first in the tuna RFMO milieu.
As an effective recovery plan for SBT can only exist at the international level (given the shared nature of the resource) the development and adoption of the MP work can also be interpreted as a direct requirement of the current conservation dependent status of the stock. It is therefore essential to complete the MP development work for adoption by the Commission in 2011.
Improved fishery independent estimates of southern bluefin tuna recruitment through integration of environmental, archival tag and aerial survey data
The parental biomass of SBT remains at historically low levels, there is evidence from CPUE and VPA analyses that recruitment has continued to fall throughout the 1990’s, and there is significant disagreement within the CCSBT Scientific Committee on the prediction of population levels into the future.
It is therefore essential to know more about the recruitment dynamics of SBT, and in particular to reduce the uncertainty in the aerial survey estimates of surface abundance of juveniles in the GAB. These remain the only fishery independent source of abundance data on SBT, and as such their importance cannot be overstated.
To reduce the uncertainty in the current aerial survey estimates we need to investigate how environmental factors and surfacing behaviour influences what is seen during the surveys. If the current levels of uncertainty in the indices are reduced by incorporating these sources of variation into the indices, the value of the indices to the CCSBT will be substantially increased.
There is large variation in estimated surface abundance between survey replicates within a season and between seasons but there are also large differences between years in environmental conditions in the GAB (eg sea surface temperature), which confound the interpretation of changes in the index between years. It is possible that the apparent decline in surface abundance over the last 6 years is due to environmental and behavioural variation rather than indicating a true decline in the global abundance of juvenile SBT.
To adequately understand how environmental variation and the resulting behavioural responses of SBT affect the recruitment indices we require thorough analyses of:
1 the surfacing behaviour in SBT and its relationship with environmental variables, migration patterns and possibly also feeding behaviour,
2 the relationship between surface abundance (ie. what the aerial survey detects) and environmental variables,
3 the spatial variation in abundance of SBT in the GAB (incorporating both data on surface abundance from the aerial survey and data from archival and conventional tagging experiments).
The proposed project will use all existing data, collected over almost a decade, with funding from industry, FRDC, CSIRO and Japan. These data are an invaluable resource. The integration of behavioural, environmental and abundance data into an improved estimate of the surface abundance of SBT is listed under Priority 2 and 3 of STBMAC Research Priorities.
Final report
Next-generation Close-kin Mark Recapture: using SNPs to identify half-sibling pairs in Southern Bluefin Tuna and estimate abundance, mortality and selectivity
Annual estimates of SBT spawning stock abundance are required to assess the status and productivity of the stock. Prior to the original CKMR study, there was no direct index of abundance of the spawning population The majority of the difference in the estimates of spawning stock status between the 2011 and 2014 stock assessments was due to the influence of the CKMR data, in combination with the 1990’s conventional tagging data. This reduced the overall uncertainty in spawning biomass and natural mortality and, therefore, identified a number of unproductive (pessimistic) parameter combinations as implausible. These were removed from the reference set of OMs (Anon 2014)
The schedule of implementation of the CCSBT MP includes a full stock assessment is scheduled for 2017. As a result of decisions by CCSBT to discontinue the Aerial Survey and move to gene-tagging, the CCSBT will initiate development of a new MP in 2017. Candidate MPs will be tested (in 2018) and a final MP selected using the OMs reconditioned in 2017 as part of the full stock assessment. The aim of this FRDC project is to provide a time-series of absolute abundance estimates of spawning potential from 2002 to 2013 for direct use in the CCSBT OMs. This abundance trajectory of the spawning potential of the stock will be independent of CPUE and catch data from the main fisheries, and will be an important input to domestic and international consideration of the stock status and performance of the rebuilding plan.
If the CKMR information is not available for the 2017 assessment, it is highly unlikely to be incorporated for testing of Candidate MPs. This would mean the CCSBT MP used to recommend future global TACs would not be “calibrated” with the most recent information on the status and recent trend in the spawning stock.