Resource Sharing in Australian Fisheries Workshop - Progress to Date, Lessons Learnt and Next Steps towards a harmonised approach
There is an urgent need to reflect on the current state of fisheries resource sharing in Australia and how it can meet future demands. Over the past 20 years individual Australian jurisdictions have developed and implemented resource sharing arrangements. These generally apply to commercial and recreational fisheries, and in some cases indigenous cultural fishers. The resource sharing arrangements stem from the objectives of fisheries legislation in Australia which is based on the principles of ESD that include consideration of all fishery resource users in the management of fisheries. Understandably when management resources are limited the focus is on those having the greatest impact on fish stock which for most species is the commercial sector, and sometimes the recreational sector. The use of OCS provisions in fisheries legislation was both an effort to simplify commercial fisheries management and reduce the need to have resource sharing arrangements. While this was largely successful it has run its course due to the value of commercial rights ($billions) that have now accrued under current OCS agreements making it almost impossible to make further significant changes. Alongside these developments a component of the recreational fishing sector has been increasing its range and capacity to catch fish using larger boats and technology similar to that employed by some commercial fishers. This has led to traditionally commercial species being accessed by recreational fishers with growing concerns from the former sector about their fishing future. Various policies and statutes have been implemented by the states/NT in an effort to allocate the shares of a fish stock. This has become easier as a growing number of fish stocks are subject to TACs with the commercial fishers subject to ITQs and recreational fishers to increasingly stock-specific possession limits. Despite this those states/NT who have implemented resource sharing have experienced its contentious, costly and drawn out nature, and are only starting to confront stocks which cross both jurisdictions and fishing sectors. It is time to reflect on experience to date and find the best way to manage fisheries resource sharing in the future.
Workshop
Evaluation of nanobubble technology in aquaculture
Larval dispersal for Southern Rock Lobster and Longspined sea urchin to support management decisions
Potential transition of shark gillnet boats to longline fishing in Bass Strait - ecological, cross-sectoral, and economic implications
Assessing the benefits of sea urchin processing waste as an agricultural fertiliser and soil ameliorant
Assessing the biosecurity risk of uncooked whole and eviscerated barramundi and grouper in relation to exotic viruses
The Australian farmed Barramundi is estimated at over $37.1 million AUD with a production of over 3,772 tonnes annually (Savage, 2015). The value of the wild-catch sector was estimated to be $9.9 million AUD with 1,073 tonnes produced (Savage, 2015). These sectors of the industry as well as recreational and Indigenous fishers, are all at risk of being exposed to hazards potentially introduced by imported Barramundi and grouper products, which could pose significant consequences. The Australian Federal Department of Agriculture does not consider there is sufficient evidence to suggest that the import conditions for uncooked barramundi do not effectively manage the risk of pests and diseases of concern arriving in Australia. Until further evidence is generated to demonstrate that importation of uncooked barramundi products poses a risk that exceeds Australia's Appropriate Level of Protection, then regulatory actions to mitigate these perceived biosecurity risks are unlikely to be implemented. Risk mitigation requirements for importation of whole farmed barramundi include that the exporting country must, among other things, declare it has in place health surveillance and monitoring and that the fish were not derived from a population slaughtered as an official disease control measure. However, this self-declaration is not supported by rigorous testing to ensure compliance. There are current and have been no previous protocols in place to test for the target iridoviruses in imported barramundi and grouper product, so the efficacy of the existing import controls has not been subject to assessment at retail level. Sampling at retail outlets of uncooked whole and eviscerated barramundi and grouper commodities is proposed in order to better assess the efficacy of import conditions. This project will focus on determining the presence or absence of exotic virus genetic material in imported uncooked potential high risk barramundi and grouper commodity. Should any positive genetic material be detected confirmatory re-testing will be performed in order to reduce the risk of a false positive PCR test result and a subsequent project will be prepared o