Assessing the impacts of trawl gear on sawfishes in the Northern Prawn Fishery with the aim to identify and test mitigation measures ensuring the long-term sustainability of Sawfish populations in northern Australia
Revisiting biological parameters and information used in the assessment of Commonwealth fisheries: a reality check and work plan for future proofing
Much effort has been placed over the last couple of decades on the development of harvest strategies, stock assessments, risk assessments and the strategic use of ecosystem models to facilitate meeting the needs of the Commonwealth’s Harvest Strategy Policy. A focus on modelling to improve fisheries management has required effort towards method development. However, little effort has been made towards revisiting and updating the biological parameters that fundamentally underpin such modelling (e.g. growth rates, age and size at maturity, natural mortality rates, dietary information, mixing rates and stock structure) and the tools or methods used to derive them. As a result, most models now rely on parameters and community dietary data derived from information collected during the 1970s-1990s, (e.g. available maturity ogives for blue-eye trevalla are over 20 years old), or information that is borrowed from other regions or species. Whether such old or borrowed values are now representative for commercial Australian fish species is unknown but many factors point to major changes occurring in our marine environment. Australian waters in the south east and south west are climate hotspots and, overall, Australian waters have warmed faster than the global average. Key components of the productivity of marine fish (growth, maturity, and recruitment) are expected to be undergoing directional changes under a changing climate and it is entirely possible that there have been changes in fundamental productivity parameters for some Australian stocks. The reliance of current assessments on what is likely to be out-of-date information leads to increased uncertainty, which propagates into management decisions. Without an understanding of any changes in biological parameters and how any change might impact assessment frameworks, determining whether current management measures are ensuring sustainability becomes highly uncertain.
Final report
Forecasting spatial distribution of Southern Bluefin Tuna habitat in the Great Australian Bight – updating and improving habitat and forecast models
This project is needed to continue supporting improved operational planning in the SBT purse-seine fishery for ranching operations in direct response to observed changes in fish distribution over the past 7 years. A habitat forecast system was developed as part of FRDC Project No. 2012/239 to deliver forecasts of suitable SBT habitat up to two months in future, and these forecasts have proven highly useful to industry to aid in their decision-making and planning of fishing operations. Unfortunately, the seasonal climate model currently being used to produce the habitat forecasts (POAMA) has been superseded by a new model (ACCESS-S), with POAMA scheduled to be decommissioned in 2019. This project will undertake the necessary migration of the current habitat forecasts to run using ACCESS-S. This will not only keep the forecast delivery website operational, but will also mean that a higher resolution, state-of-the-art forecasting model is being used (details of ACCESS-S and a system comparison with POAMA can be found at http://poama.bom.gov.au/general/access-s.html). Importantly, this project will also evaluate the skill of ACCESS-S forecasts in the GAB for the variable(s) of interest (currently sea surface temperature, SST). SST forecasts produced by POAMA were found to have useful skill in the GAB up to two months into the future during the months of interest, this needs to be assessed for ACCESS-S.
In addition, as part of this project, the habitat preference models will be updated using new archival tag data to determine whether SBT preferences have changed. As noted in the proposal for FRDC Project No. 2012/239, continual updates are essential to ensure the habitat forecasts remain relevant, particularly in the face of climate change and possible changes in fish behaviour in response to a wider distribution of warm waters. Furthermore, all available archival tag data will be used to evaluate if there are size-specific differences in habitat preferences of tuna in the GAB. This is a real need for industry now that SBT juvenile populations are increasing and the GAB is suitable for a wide range of age-classes.
Final report
Blue carbon and the Australian seafood industry: workshop
Cumulative impacts across fisheries in Australia's marine environment
The need for cumulative impact assessment (CIA) is increasingly being recognized. The development process for Australia's Harvest and Bycatch Policies, and their associated guidelines have reinforced the need for assessment of cumulative impacts, and the EPBC Act has also explicitly required consideration of cumulative impacts.
Where multiple activities occur or are planned, an understanding of their combined effects on the environment is necessary to address policy requirements and achieve sustainability. The concept of cumulative impact assessment is not new – indeed cumulative assessment has been recognized for many years, and a range of methods have been proposed around the globe. However, no methodology for undertaking cumulative assessments has been accepted nationally or globally. In addition to considering the impacts across all fishing sectors (commercial, recreational, indigenous, as required by recent changes to the Fisheries Administration Act 1991) and all fisheries, there is also an increasing need to consider other users of marine resources and coastal waters (e.g. renewable energy, shipping etc), especially where space crowding may be an issue.
Target species stock assessments typically consider the species of interest as well as other sources of fishing mortality (e.g. discards), but they do not usually consider their effects on other fisheries sectors or the effects of other sectors on the focal fishery. CIA methods therefore need to consider interactive and indirect effects. To date, interactive effects are often viewed as additive (simple linear addition of one impact to another) with little consideration given to synergistic, antagonistic or non-linear effects. While the ERAEF toolbox used for assessment of bycatch and protected species has some potential options for cumulative impacts (e.g. SAFE method), at this stage they are insufficient for moving to the scales and complexities across multiple fishing sectors and fisheries.
Thus, sustainable fisheries management requires new approaches that consider all sectors and all fisheries and how they impact the environment. Such CIAs will be challenging given that empirical data are often lacking - a dedicated research effort is needed.
Final report
Storm Bay Biogeochemical Modelling & Information System Supporting sustainable aquaculture expansion in Tasmania
Comparative evaluation of Integrated Coastal Marine Management in Australia - Workshop
There is widespread evidence, in Australia and internationally, of increased need for an improved, practical approach to integrated management (IM) of fisheries and other coastal marine activities that is able to fully embrace the social, economic and institutional aspects (the so-called ‘human dimensions), of management. Assessment and management systems traditionally neglect the human dimensions. Further, they treat sectors separately, often with different authorities managing diverse activities in different ways, resulting in inconsistencies in management across activities. The result is that there is almost no consideration of the cumulative social, economic or ecological impacts of multiple activities, and no way of informing trade-offs among activities in management decision-making.
Experience to date is that IM has been only partially successful. Management of multiple activities has been additive…squeezing one activity in among others (e.g aquaculture in light of others). While there are some examples of movement toward IM, these have resulted in partial or temporary success. There are examples where management has started toward IM, but progress has been stalled or has fallen back. In general, many preconditions exist, but it has been hypothesized that management is missing key aspects of intentional design that would allow IM to proceed.
The proposed workshop will bring together those with both the science knowledge and the operational knowledge of 8-10 Australian IM case studies and a few with international expertise, to evaluate and compare experience towards identifying key elements of success and failure of Integrated Management.