Traditionally, catch per unit of effort (CPUE) is used to monitor the health of the fishery and indicate the success or otherwise of management practices. Under current input controls CPUE is based on fishers maximising their total catch. In contrast, under output controls where catch is predetermined fishers will alter their catching scenarios to maximise the return (dollars per kilogram) from their catch. In southern rock lobster fisheries there is significant potential to alter fishing patterns to maximise economic return, especially through seasonal shifts in effort. As this change occurs, the value of using CPUE data to continue monitoring the fishery will be eroded. As such, both fisheries independant means of monitoring the fishery and new monitoring methods will become increasing important.
Both exploitation rates and biomass estimates are important stock assessment parameters and biological reference points in sustainable management of fisheries resources.
This project will evaluate fishery independant means of deriving these estimates and by determining the precision of derived estimates, demonstrate their suitability as biological reference points.
In a report to the Department of Industry, Technology and Commerce titled "Oceans of Wealth?", the Review Committee on Marine Industries, Science and Technology stated in their conclusion, 'The knowledge gained from scientific research into fish stocks and the impacts of the environmental and harvesting factors is a necessary but not sufficient element in the conservation of productive fish stocks. A vital element in both scientific assessments is the availability of reliable information about exploitation levels'. This project is aimed at addressing this need for southern rock lobster.
Exploitation rate is an important fishery assessment parameter linking catch to legal-sized biomass, the portion of the stock available for harvest. Relative change in legal-sized biomass is a crucial performance indicator for the fishery as it measures the success of management outcomes. Under the recently introduced Individual Transferable Quota Management System (ITQMS) in the Tasmanian rock lobster fishery, rebuilding of legal-sized biomass is a key management objective. The assessment model that produces biomass estimates for this fishery is primarily dependent on commercial catch and effort data.
The use of commercial catch and effort data for stock assessment relies on its de facto relationship with stock abundance. However, the relationship between catch and effort data and abundance is not always constant or linear. Improvements in fishing gear and technology can result in greater catch for a given amount of effort, unrelated to changes in the biomass. Management changes and fishers’ behaviour can also affect the relationship between catch rates and biomass. Under the new ITQMS introduced in 1998, catch is fixed and improved profits can be made by improving the return per unit of fish caught rather than by increasing the amount of catch through increased effort. Thus fishing during periods when catch rates are low but price is high can change the catch effort relationship independent of biomass change.
Fishery independent surveys, using established sampling protocols and standardised fishing gear are a way in which catch rates can be standardised irrespective of gear efficiencies or fisher’s behaviour. If these surveys can also produce accurate estimates of exploitation rate then accurate estimates of biomass can be achieved, provided the exploitation rate estimates are representative of the fishing grounds. Fishery independent estimates of exploitation rate are thus a valuable way of validating model biomass estimates especially with the introduction of an ITQMS where the relationship between catch rates and legal-sized biomass was likely to change pre- and post-quota.
This project aimed to trial change-in-ratio (CIR) and index-removal (IR) techniques to obtain estimates of exploitation rate and biomass from broad scale regions in the fishery.
Keywords: southern rock lobster, change-in-ratio, index-removal, exploitation rates, tagging.
Length-at-age data are an important input to the fully age-structured fishery assessment models used by SharkFAG for stock advice to SharkMAC.
School sharks and gummy sharks are currently aged by counting growth-increment bands on the articular faces of vertebrae stained with alizarin red. This method is only partly validated on captive sharks and requires further work. There is a need to validate the assumption that the bands of alizarin red stain are annual and that they provide reliable estimates of age. Appropriate methods for undertaking this validation were developed as part of the completed 'Southern Shark Age Validation Project' (FRDC 91/037). The recently completed 'Southern Shark Tagging project' (FRDC 93/066) was ideally timed to provide sufficient samples to properly undertake this validation.
The project ‘Age Validation from Tagged School and Gummy Sharks Injected with Oxytetracycline’ (FRDC Project 97/110) follows on from four successfully completed projects. These are the ‘Southern Shark Age Validation’ (FRDC Project 91/037), ‘Southern Shark Nursery’ (FRDC 93/061), ‘Southern Shark Tagging’ (FRDC Project 93/066), and ‘Southern Shark Tag Database’ (FRDC Project 96/162). The present project makes use of vertebrae collected from sharks tagged, injected with oxytetracycline, and released into the wild as part of these projects. These vertebrae were collected for the purpose of further age validation.
The present report provides the results of analysis of samples of oxytetracycline marked vertebrae collected and processed in the laboratory by the end of the year 2000. Most available vertebra samples were collected from sharks at liberty for 1–2 years after being tagged and released; only a small number were collected from sharks at liberty 3–5 years. The longer an animal is at liberty, the more valuable it is for age validation purposes. This is because bias and imprecision in counting growth-increment bands are more significant for sharks at liberty for short periods than for those at liberty for long periods. Although the number of vertebra samples continuing to be collected is low, those that are returned in the future will be particularly valuable because of their long periods at liberty. These will be processed from time to time in the future for updating the analyses.
Keywords: Shark vertebra age validation, alizarin stain, microradiography, fishery monitoring.
The need for special research projects and individual stock assessments is detailed by the South East Fishery Assessment Group (SEFAG) and endorsed by SETMAC. The development of stock assessments for blue grenadier, and ling are high priority. Other species with high priority for quality stock assessment include blue warehou, redfish, blue-eye trevalla, and (following SETMAC 55) tiger flathead.
Blue grenadier is a species for which new data have become (or are becoming) available and for which there is a conflict between the relatively optimistic scientific advice (based primarily on an acoustic and an egg production estimate) and the more pessimistic view of several industry representatives. The stock assessment for this species will be accorded first priority. The other two species to be assessed wil be determined based on discussions with SETMAC, its research sub-committee and AFMA.
Managers need to be provided with information that will ensure that fishing mortalities remain below the appropriate biological reference points for the key species.
To provide this information, knowledge is required of the relationship between fishing effort and fishing mortality. An experimental approach which provides a clearly measurable level of fishing mortality will achieve this. The fish in the 100-200m depth zone are schooling species and commercial effort will naturally be targeted on schools, so commercial catch rates cannot be used for the abundance measures required to calculate fishing mortality. There is a need therefore for survey fishing before and after the period of intense commercial fishing and for research personnel to oversee the survey fishing, gather samples and information on the survey cruises, process these at the laboratory and analyse the results. Monitoring of the fishing effort through research logbooks during the commercial fishing period is also required.
The eastern king prawn is the Australian east coast's single most valuable fish species. On the basis of previous experience and existing data, the risk of overfishing this stock is unquantified but appreciable. Obtaining data which can be used to advise fisheries managers on the necessity of intervention can only be obtained from a focussed, directed multi agency study.
In order to establish stock status, supply accurate advice and recommendations on management and monitor effectiveness of management intervention if need be, there are needs to develop procedures which;
(a) allow definition of the relationship between parent stock and recruitment levels in eastern king prawns, using fishery independent surveys as a means of determining recruitment levels.
(b) determine the status of the species and evaluate the potential risk of over-fishing.
(c) develop methods which can be used to evaluate the effectiveness of management intervention, if and when such intervention occurs.
In order to establish stock status, supply accurate advice and recommendations on management and monitor effectiveness of management intervention if need be, there is a need to develop procedures which
a) allow definition of the relationship between parent stock and recruitment levels in commercial prawn species, using fishery independant surveys as a means of determining recruitment levels
b) determine the status of these species and evaluate the potential risk of overfishing
c) develop methods which can used to evaluate the effectiveness of management intervention, if and when such intervention occurs.
There is potential for significant growth of blue crab fisheries in South Australia and other crab-producing states driven by demand of export markets. However, the industry and resource managers lack reliable information on the productivity and likely sustainable harvests of blue crabs. Since June 1996, the blue crab fishery has been managed under both output (catch quotas) and input (pot limits) controls. A lack of biological information and concern about the uncertainty of the stock's capacity to withstand increased fishing effort have prompted a precautionary approach to management. Information on the fisheries biology of blue crabs is necessary to augment the fisheries dependent information collected in South Australia. Such information will promote bolder, more entrepreneurial management strategies with concomitant opportunities for increased economic wealth and industry development.
After presenting a full research report proposal for blue crab in 1995, the South Australian Research and Development Board recommended that additional supportive research program necessary for the management of this fishery would augment basic research funded by the blue crab fishing industry. Under these circumstances, the basic research program was tailored to provide the information urgently needed to initiate management processes. The basic research program started in July 1996. The proposed research will complement this basic program and research in other states consistent with the national strategy (Kumar 1997b).
This proposal addresses a need for cost-effective assembly of research information. The applicants recognise that the current landed value of blue crabs in Australia is not large enough to support a resource intensive program and seek to augment current research conducted in South Australia and in other states by proceeding with a collaborative program of research aimed at gaining biological information relevant to the assessment of blue crab stocks. The research will concentrate on determining the key biological parameters influences recruitment, growth, movement, and survival and identify the main sources of variation in those parameters. Finally, an important outcome will be the development of a spatially explicit production model that will allow managers to confidently evaluate the consequences of alternative management strategies.