Development of an ecosystem approach to the monitoring and management of Western Australian fisheries
There are currently no standard techniques that can be used to assess whether fishing has had significant impacts on ecosystem structure. The current round of EPBC assessments has demonstrated that a more robust assessment of ecosystem impacts will be required when the next application for export exemption is submitted in five years time. It is vital for WA's export fisheries that the types of changes in exploitation and/or environment that could cause marked changes in ecosystem structure are identified, the types of data necessary to assess whether such changes are occurring are determined, and cost-effective methods are developed to provide information on the level of ecosystem changes that have occurred.
Having appropriate techniques to assess whether fishing within a region is significantly modifying the ecosystem is seen as a national priority. At a recent workshop held by the Research Committee of the Australian Fisheries Managers Forum (AFMF) it was concluded that different types and levels of analysis are likely to be needed for different purposes and it would be “inappropriate to abandon any particular approach prematurely”. Given the potential costs associated with the collection of new or additional data at an ecosystem level, it is imperative that attempts are made to see if existing datasets, such as those currently maintained by fisheries agencies on catch and effort, are suitable for this purpose and to apply modelling approaches, such as those developed in FRDC 2000/311, to these refined datasets.
Completing routine ecosystem-level assessments will only be feasible when tools are available to simplify the complex process of analysing the multi-sector, multi-species databases that are present in WA (and most jurisdictions). There is a need, therefore, to identify and test a variety of statistical methods using these datasets to determine if any are suitable for detecting shifts in ecosystems or community structure.
Final report
Diversity and ecosystem-based indicators were calculated for commercial finfish fisheries from 1976 to 2005 for the West Coast, South Coast, Gascoyne, Pilbara and Kimberley bioregions. The ecosystem-based indices, which detect changes in the species composition of the food web within the ecosystem, were mean trophic level (1=herbivores to 5= peak predators), mean size of the fish in the catch (calculated using the maximum lengths for the species), and a Fishery-in-Balance (FIB) indicator. The latter adjusts the magnitude of annual catch to account for changes in observed mean trophic level to determine whether the scaled catch has increased or decreased relative to that within a reference year. The time series of ecosystem-based indices demonstrated that, in each bioregion, both the mean trophic level and the mean maximum length of catches have increased; possibly because the fisheries in some of these bioregions have developed and expanded spatially over the period from 1976 to 2005. In the West and South Coast bioregions, the series appear to have stabilized, but they continue to increase in the other bioregions. There is no evidence from the commercial fishery data that, from 1976 to 2005, there has been any reduction in trophic level or mean maximum length that would be expected from fishing down the food web, and thus, it appears that, at this time, ecosystem services have not been affected by fishing or other factors. It is possible that the indices are being maintained by continued spatial expansion of fishing and/or changes in targeting, and that, if exploitation increases and expansion is no longer possible, the ecosystem-based indices will stabilize and begin to decline.
Statistical analysis of the Western Australian (WA) data using the software package, Primer, demonstrated, however, that the species composition of the catches reported by fishers within each of the bioregions had changed over time. The species that most characterized the changes were identified. The analysis was unable, however, to distinguish whether change in species composition and abundance resulted from fishery practice, recording and reporting processes, management changes, changes in exploitation or targeting, environmental change or a combination of these factors. Thus, while change in species composition had occurred in each bioregion, it was possible that this was due simply to expansion of fisheries to exploit different species groups in different locations within each bioregion. It is also possible that improved reporting by fishers, i.e. reporting of catches at species rather than family level, may also have contributed to the apparent change in species composition.
This and other studies have demonstrated that data collected for key fished and non-fished stocks within an ecosystem should include time series of total catches and reliable relative abundance indices, samples of age, length and sex composition representative both of the catches of each fishing sector and of the wild stocks, and data from studies of population biology, i.e. growth, maturity, sex change, reproduction. Where appropriate and cost-effective, fishery-dependent data should be augmented by fishery-independent relative abundance, age composition and biological data. Limited recreational catch data are currently available, and current estimates of abundance, i.e. cpue data from commercial fishers, are likely to be influenced greatly by changes in fishing power and targeting by fishers.
Management strategies for the West Coast Bioregion were explored in this study. Results of this exploration demonstrated that the indicators, reference points and decision rules that have been adopted by the Department of Fisheries Western Australia for the demersal scalefish fisheries of the West Coast Bioregion are likely to be highly effective. Thus, for Western Australia’s finfish fisheries, fishing mortality estimates appear currently to be more reliable indicators of fishery status than abundance estimates, where the reference points for those indicators are those determined from the estimates of natural mortality for the different species. Reference points for spawning biomass such as maximum sustainable yield and virgin spawning biomass rely to a much greater extent on trends in relative abundance, estimates of which are unreliable due to a paucity of accurate abundance data.
Environmental change may affect the growth, reproduction, and carrying capacity of the various stocks. Changes in growth and reproduction can be monitored by appropriate data collection and analysis using traditional methods of fish population biology. Changes in carrying capacity will be more difficult to assess as determination of a stock-recruitment relationship is typically difficult to determine, even when this is assumed to be constant. Although it was not possible to distinguish between fishery and environmental effects, the study demonstrated that the management strategies, which had been accepted for use in the demersal scalefish fishery of the West Coast Bioregion, would be likely to continue to be effective if the species were affected by changes in biological characteristics or carrying capacity.
Keywords: Ecosystem, trophic level, mean maximum length, species composition.
Stock enhancement of the Western School Prawn (Metapenaeus dalli) in the Swan-Canning Estuary; evaluating recruitment limitation, environment and release strategies
The decline of the WSPs in the Swan-Canning Estuary was marked firstly in commercial catches in the 1970s and subsequently, a decline in recreational catches through to the late 1990s. Reasons for the decline are not well understood but coincide with actions to improve environmental conditions of the river system. This once abundant and iconic species is highly prized by recreational fishers in the region and is a core community value identified in surveys of river users. For this reason, addressing the population decline of the WSP is seen as priority for research under the SRT Healthy Rivers Action Plan. The WAFF project on the production and release of WSPs in the Swan-Canning Estuary, funded through WA Recreational Fishing Initiatives Fund, will work to develop production technologies for WSPs and engage the community but is not funded to fully evaluate the effectiveness of the restocking. This WAFF program needs to be supported by an investigative and evaluative program that can ascertain current population levels and factors limiting natural recruitment, optimize release strategies and evaluate cost-benefits, which forms the basis for this FRDC application.
The combination of the WAFF project with this FRDC proposal will also help evaluate the potential effectiveness of a major restocking program to rebuild the stocks of WSPs in the Swan-Canning estuary. The stock enhancement and associated community engagement program (PrawnWatch) have the potential to increase the numbers of recreational fishers in this fishery, the quality of their fishing experience and provide recreational fishers (and the broader community) with a greater understanding of the biology and ecology of WSPs and the environmental conditions of the system. The WAFF project, particularly the PrawnWatch component, also provides opportunities to engage fishers in improved stewardship of the fishery and the Swan-Canning Estuary.
Final report
Determining biological characteristics of the champagne crab (Hypothalassia armata) for management purposes
The importance to commercial and recreational fish species of the various habitats found in the nearshore marine waters and estuaries of south-western Australia
The urgent need for reliable quantitative data on the habitats which are used extensively by commercial and recreational fish species during one or more stages in their life cycles has been highlighted by Cappo et al. (1998) in their report to FRDC (95/055). That report identified a deficiency in a knowledge of the following:
1. Characteristics and locations of important fisheries habitats at scales useful for research and management.
2. Life history information for fish species, related to the types of habitats occupied throughout their life cycles, and data on the densities and/or biomass of those other biotic components of fish habitats, which provide food and/or protection for fish, such as invertebrates and aquatic vegetation.
3. Habitat dynamics and ecosystem processes, including food webs, habitat use and fisheries production in soft sediment substrata, such as beaches.
4. Fisheries-habitat links, including the influences of hydrodynamic and other processes on the recruitment of commercial and recreational fish species.
The above gaps in our knowledge were also highlighted by the FRDC in its “Research Priorities for Fisheries Ecosystem Protection”, when they listed two of its strategic R&D areas as “defining major habitats in the coastal exclusive economic zone” and “the roles of habitats in maintaining healthy fisheries production, ecosystem integrity and biodiversity”.
There is a particularly urgent need to fill the above gaps because the coastal and estuarine waters of Australia are becoming increasingly exposed to the effects of numerous coastal developments, e.g. the construction of harbours, marinas and groynes, and to the destruction of habitat through other forms of activity, e.g. dredging for sand and extreme forms of eutrophication. Information on which habitats are most important to commercial and recreational fish species in these waters are required by managers so that they can introduce appropriate plans for managing and conserving those habitats.