44 results

Aquatic Animal Health Subprogram: further research and laboratory trials for diagnostic tests for the detection of A invadans (EUS) and A astaci (Crayfish Plague)

Project number: 2004-091
Project Status:
Completed
Budget expenditure: $75,200.00
Principal Investigator: Nicky Buller
Organisation: Murdoch University
Project start/end date: 29 Jun 2004 - 11 Feb 2008
Contact:
FRDC

Need

A twelve-month extension of project 2001/621 is required to complete validation of the PCR primers for A. invadans and to continue testing the primers for A. astaci.
The primers for A. invadans (Epizootic Ulcerative Syndrome – EUS) are specific when tested on DNA from other Oomycete fungi, however need to be tested on tissue samples and wax-embedded tissue. The development of the fluorescent in-situ hybridization method (FISH) also needs to continue. Two isolates previously identified as A. invadans and used in research performed at other laboratories, do not amplify or produce a weak amplicon with the primers designed for A. invadans. This area needs investigation to determine the true identity of these two isolates.
The development and specificity of the primers for A. astaci (Crayfish Plague) needs to be completed. Sequence information for the chitinase and trypsin protease virulence genes of A. astaci were used to design a number of sets of primers including nested primers, which provide greatly increased sensitivity. However, product has not been amplified and we need to investigate this. We are confident with the DNA extraction technique, which can amplify fungal DNA from formalin-fixed crayfish using universal primers, therefore it is not known why the virulence genes cannot be amplified from the infected formalin-fixed crayfish tissue.
The primers will be assessed by trialing them at selected laboratories within Australia and overseas. Once this is completed the primers along with negative and positive controls can be developed into kits.
To ensure that reliable and robust diagnostic tests are developed for EUS and Crayfish Plague, this project needs to continue so that further research can be carried out to achieve these aims. Trialing the kits and assessing feedback from laboratories will greatly improve the uptake of these tests and also add to user confidence in these kits.

Objectives

1. Complete validation of A. invadans PCR on fresh tissue and wax-embedded tissue
2. Complete research to develop specific PCR for A. astaci (Crayfish Plague)
3. Complete research to develop FISH tests for A. invadans and A. astaci
4. Complete trial of PCR and FISH tests at Australian and overseas laboratories
5. Analyse feedback from Participating Laboratories on PCR tests and FISH
6. Complete writing of method for the Australian and New Zealand Standard Diagnostic Tests Manual and FRDC Report

Final report

ISBN: 978-0-646-48785-4
Author: Dr. Nicky Buller
Final Report • 2010-06-16 • 2.92 MB
2004-091-DLD.pdf

Summary

Crayfish plague and epizootic ulcerative syndrome are two fungal diseases that affect freshwater crayfish and freshwater finfish, respectively. Crayfish plague, which is caused by Aphanomyces astaci, is exotic to Australia, but is capable of causing massive stock losses of up to 100% which would be catastrophic should the disease occur in Australia. It is present in North America where the native freshwater crayfish are largely resistant to the disease and can act as carriers of the fungus. Crayfish plague was transferred to Europe in the 1870’s through infected stock and has wiped out many of the native freshwater crayfish in a number of countries. Epizootic ulcerative syndrome (EUS), caused by infection with Aphanomyces invadans, is endemic in many fish in river systems throughout Australia. The disease causes economic losses to the freshwater finfish aquaculture industry and affects local native stocks. Both diseases are almost impossible to eradicate. 

Both diseases are difficult to diagnose, especially if laboratory personnel are not sufficiently skilled in recognising or differentiating the diseases. The culture and identification of both fungal species can be difficult and prolonged. Isolation and identification may be hampered by overgrowth from other fungi that contaminate the lesion or the isolation medium. Culture is tedious and may take up to 15 days before fungal growth is seen. It can then be difficult to identify the fungus species and often requires the culture being sent to a specialist laboratory for confirmation of identification. Examination of histological samples requires expertise and although the presence of hyphae of 7-10 µm in width is suggestive of Aphanomyces, it is not definitive. 

Early detection and diagnosis of the disease is crucial to ensure rapid disease response and containment, particularly for crayfish plague, which is exotic to Australia and the Asian region. Therefore, there was a need to improve diagnostic capabilities of Australian laboratories in line with the Federal Budget Initiative “Building a National Approach to Animal and Plant Health” funding to improve disease diagnosis in aquaculture. 

The research undertaken in this project sought to provide two diagnostic tests for each disease based on molecular (DNA) biological techniques, polymerase chain reaction (PCR) and fluorescent in-situ hybridization (FISH) using peptide-nucleic acid probes. In both techniques, identification is based on detection of a DNA sequence that is unique to the target organism. The uniqueness of the DNA sequence is demonstrated by testing specificity against other genetically similar organisms or those that may be found in the same ecological location. For detection and identification of A. invadans the tests were applied to fungal culture material, fresh tissue and formalin-fixed paraffin-embedded tissue. For A. astaci the tests were applied to formalin-fixed paraffin-embedded material.  

Optimal extraction of DNA from samples is of prime importance for achieving an accurate and sensitive result. Two commercial methods were suitable; the DNAzol reagent (Invitrogen, Life Technologies) and the DNeasy mini plant tissue kit (Promega). 

A PCR that was specific to A. invadans was developed. The PCR can be used on culture material and fresh fish tissue using primers AIF14 + AIR10. The test is specific and does not show cross-reaction with closely related oomycete fungi such as Saprolegnia species or fungal species that are likely to occur as plate contaminants on laboratory media, such as Aspergillus species and Penicillium species. The primers, which produce an amplicon of 554 base pairs (bp), were unable to amplify the DNA from paraffin-embedded tissue. This is most likely due to the effect of the formalin fixative on the DNA, which in the process of fixing the tissue cross-links amino acids groups. This cross-linking makes it difficult for primers that produce a large amplicon (greater than 500 bp) to amplify the DNA. A different fixative may be needed for these types of samples. 

Four of the thirteen primers designed to amplify a sequence from the virulence genes (chitinase and trypsin proteinase) produced strongly staining amplicons. These were validated against two primer pairs published previously (Oidtmann et al., 2004, 2006). Primers 525f and 640 r published in 2004 were more sensitive and had the advantage that they detected DNA from formalin-fixed paraffin-embedded sections. However, they were not as specific as the primers developed in this project. Primers published in 2006 were specific but because they produced a large amplicon they were not tested on paraffin-embedded tissue. Further work is required before a specific and sensitive PCR for A. astaci can be recommended for diagnostic laboratories. 

Peptide nucleic acid probes (PNA) for use in the fluorescent in situ hybridisation (FISH) method were developed for both A. invadans and A. astaci. The PNA-FISH for A. invadans was specific and successfully applied to fresh cultured hyphae. Tests on aged hyphae in samples such as formalin-fixed paraffin-embedded sections yielded a reduced fluorescent signal. The PNA-FISH for A. astaci could only be tested on paraffin-embedded sections and the same reduced fluorescent signal occurred with this species. Further work needs to be done to optimise the PNA-FISH for both fungal species using paraffin-embedded material.

Keywords: PCR, fluorescent in-situ hybridization, FISH, epizootic ulcerative syndrome (EUS), Crayfish plague, Aphanomyces astaci, Aphanomyces invadans.

Aquatic Animal Health Subprogram: Identification and Distribution of an intracellular ciliate in pearl oysters

Project number: 2004-086
Project Status:
Completed
Budget expenditure: $110,984.33
Principal Investigator: Shane Raidal
Organisation: Murdoch University
Project start/end date: 29 Apr 2005 - 29 Jul 2008
Contact:
FRDC

Need

One of the key objectives of the WA Dept of Fisheries Business Plan is to ensure ecological and environmental sustainability of the pearling industry. The proposed project will be of direct benefit to the Western Australian pearling industry in that it will document the existence of the ciliate and its effect on an economically very important oyster species, it will establish whether the parasite is in the wildstock oysters in Zone 1 and it will establish whether the parasite has a reservoir host. This information is required by pearling companies in assessing their level of risk of getting or transmitting the parasite, given that, for environmental reasons, translocation of infected oysters out of Zone 1 is currently not permitted.

There is an international shortage of pathologists with expertise in molluscan pathology and a National need for research projects that are suitable for the postgraduate training of aquatic animal health specialists.

The Aquatic Animal Health Committee (AAHC), National Aquatic Animal Health Technical Working Group (NAAHTWG) and the Federal Government through the Aquaplan Initiative have all recognised a need for Australian veterinary education institutions to participate in specialised postgraduate training programmes in aquatic animal health.

Objectives

1. Train a postgraduate in molluscan and aquatic animal health pathology
2. Describe what the parasite is doing to the cells in the oyster including host-ciliate interactions and host specificity.
3. Survey other species of bivalves occurring within an affected farm, i.e. determine the site of the ”index case”.
4. Survey piggyback spat collected from Zone 1 during the Department of Fisheries piggyback spat research project, for the parasite.
5. Formally describing the intracellular ciliate parasite, its ultrastructure, life cycle and giving it a scientific name.

Biological parameters required for managing Western Blue Groper, Blue Morwong and Yellowtail Flathead

Project number: 2004-057
Project Status:
Completed
Budget expenditure: $233,684.00
Principal Investigator: Ian Potter
Organisation: Murdoch University
Project start/end date: 29 Jun 2004 - 1 Mar 2008
Contact:
FRDC

Need

Successful management of a fishery for any species requires a thorough understanding of how that species will respond to different levels of exploitation. Such an understanding depends on managers possessing certain crucial biological data that have been acquired using an appropriate sampling regime, laboratory techniques and analysis of the results. The key biological data that are required for a species are as follows: (a) age and size compositions, growth curves and age and length at maturity for both sexes, (b) length and age at sex change in the case of hermaphroditic species, (c) location and duration of spawning, (d) fecundity and (e) estimates of mortality. These data enable scientists to assess the status of the stock(s) and thereby provide advice to managers, who are then in a strong position to formulate appropriate management strategies.

The following three species have been identified as “indicator” species for management purposes: western blue groper Achoerodus gouldii, queen snapper Nemadactylus valenciennesi and bar-tailed flathead Platycephalus endrachtensis (Fisheries Management Paper 153; Report of 2003 RFAC/RecFishWest research planning meeting). However, there are no reliable data on the crucial biological characteristics listed above for any of these species in Western Australian waters (e.g. FishBase). Managers thus require these data for management purposes.

Since the results of many of the age and growth studies of fish species in various regions are not of the standard required to produce reliable data for management purposes, there is a need to produce guidelines on the extent and quality that are required of such studies for management purposes.

Objectives

1. Determine the size and age compositions, growth, reproduction and mortality of western blue groper Achoerodus gouldii, queen snapper Nemadactylus valenciennesi and the bar-tailed flathead Platycephalus endrachtensis.
2. Supply the above data to the Department of Fisheries, Western Australia, in a format that can readily be used for management purposes.
3. Use the results of the above studies to highlight the essential elements of age and growth studies that will produce data of the required quality for management.

Final report

ISBN: 978-0-86905-932-6
Author: Ian Potter

Relationships between fish faunas and habitat type in south-western Australian estuaries

Project number: 2004-045
Project Status:
Completed
Budget expenditure: $480,277.85
Principal Investigator: Fiona Valesini
Organisation: Murdoch University
Project start/end date: 29 Jun 2004 - 31 Dec 2008
Contact:
FRDC

Need

Since estuaries constitute such an important environment for many recreational and commercial fish species, plans for their management must be based on reliable data if they are to be useful in protecting and, if necessary, restoring crucial estuarine fish habitats. Managers thus require the following.
1. Sound quantitative data on the ways in which commercially and recreationally-important fish species and their different life cycle stages are distributed among the different types of habitat found in south-western Australian estuaries.
2. An ability to identify rapidly and reliably the type of habitat to which any site in an estuary should be allocated and therefore also to predict the likely composition of the fish fauna at that site.
3. Knowledge of the extent and distribution of the various habitat types within and amongst different estuaries which can serve as benchmarks against which the impacts of future environmental changes on the fish faunas can be gauged.
4. An understanding of the relationships between the benthic invertebrate components of the fauna, particularly those that make major contributions to the diets of fish, and the different types of habitat in estuaries. This will facilitate an assessment of the broader implications of changes in the estuarine environment on the fauna as a whole.

This project is necessary to underpin the following conservation planning and programmes. Western Australian Marine Conservation Reserve Program under the CALM Act (1984), the Comprehensive Management Plan (parts c, d) in the Environmental Protection Policy for Swan and Canning Rivers (Government Western Australia 2003), the Peel Development Commission in sustaining environmental health of the Peel-Harvey Estuary, the Recfishwest Policy detailing their Guiding Principles for Responding to Coastal, Marine, Riverine and Impoundment Development Proposals, and the Fish and Fish Habitat Protection Program undertaken by the Department of Fisheries WA.
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.

Objectives

1. Determine the suite of environmental criteria that are most useful for readily and quantitatively assigning any site in a particular estuary in south-western Australia to its appropriate habitat type.
2. Determine statistically how the compositions of the fish and benthic invertebrate assemblages in particular south-western Australian estuaries are related to habitat type.
3. Formulate a readily usable and reliable method for predicting which fish species are likely to be abundant at any particular site in an estuary.

Final report

Estimation of natural and fishing mortality using length composition data

Project number: 2003-041
Project Status:
Completed
Budget expenditure: $318,426.18
Principal Investigator: Norman G. Hall
Organisation: Murdoch University
Project start/end date: 28 Sep 2003 - 1 Sep 2008
Contact:
FRDC

Need

Sound estimates of natural and fishing mortality form the basis of fishery stock assessment and modelling. Without these data, the extent to which the spawning biomass has been reduced or the effectiveness of management measures in sustaining wild fish stocks cannot be determined. These estimates of mortality are crucial if the commonly-used reference points for fishing mortality and biomass are to be used in managing fisheries. Considerable advances have been made in obtaining estimates of mortality when data on the age composition of the annual catch are available. However, when there are only data on the length composition of the catches, analyses become more complex and the algorithms are not as well defined. Although information is usually available within the biological and fishery data that allows estimation of total mortality, the information on natural mortality must usually be obtained from empirical models that relate natural mortality to characteristics of the life history for other fish species or by estimating the relationship between total mortality and fishing effort, thereby obtaining an estimate of natural mortality by subtraction. Furthermore, there is a need to understand how natural mortality varies with size. Although the study of mortality deserves to be a primary focus of fishery research, it is difficult and thus often set aside. For many of Australia’s finfish stocks, there is a need to develop length-based methods to estimate mortality, which can be used to monitor the stock status of the recreational fisheries, and to obtain improved estimates of natural mortality that can be used in assessing sustainability. The project falls within FRDC’s Natural Resources Sustainability Program and is intended to increase and apply knowledge of stock assessment methods by developing methods of estimating mortality using length composition data which, compared with age composition data, are relatively inexpensive to collect.

Objectives

1. To develop methods for estimating natural, fishing and total mortality from length composition data and, in particular, to enable the following objectives to be achieved.
2. To estimate total mortality by applying Length Frequency Analysis (LFA) methods to length composition data.
3. To estimate total mortality by applying a length-based method of relative abundance analysis to length composition data from consecutive years.
4. To estimate natural mortality from the changes in length composition data that accompany a change in minimum legal length.
5. To estimate natural mortality using a length-based fishery model
6. To determine whether these length-based methods can be used to estimate a size-dependent (rather than constant) natural mortality.

Final report

ISBN: 978-0-86905-988-3
Author: Norm Hall
Final Report • 2017-09-29
2003-041-DLD.pdf

Summary

The objectives of this project were to develop length-based approaches for estimation of natural, fishing and total mortality, and to explore the application of these methods to the data from selected fisheries. The methods that were developed were essentially length-based versions of age-based approaches that are typically applied for stock assessment when appropriate and when representative age samples are available from either research or catch sampling. 
 
The study explored several methods to estimate mortality from length samples.  The simpler of these approaches assume that, as fishing mortality increases, fewer fish will survive to reach larger sizes.  Accordingly, the size composition becomes increasingly truncated at the right when fishing mortality increases.  Length FrequencyAnalysis and length-based catch curve analysis assess the extent to which the shape of the right-hand tail of the size distribution is reduced, and taking growth into account, use this information to estimate total mortality. The problem becomes more complicated, however, when annual recruitment varies. Relative Abundance Analysis attempts to track peaks and troughs in the length compositions in successive years, thereby identifying strong and weak year classes. By taking year class strength into account, the decline in the right-hand tail of the length distribution can be assessed more reliably, thereby improving the accuracy of the estimate of total mortality. An increase in minimum legal size allows smaller fish that would previously have been caught to survive and grow to the new minimum size.  If there are adequate data and the change in minimum size is sufficiently great, the change in the length compositions before and after the change in minimum size can be used to estimate the natural mortality. Finally, by analyzing the combined set of time series of fishery data, length and age samples, and attempting to track year classes through the catch-per-unit-of-effort, age-composition and length-composition data in successive years, it is possible to obtain estimates of both natural and fishing mortality. The precision of the estimates is dependent of the information content of the data, however.  This last analysis was extended to assess whether, for Tailor, there was evidence of length-dependent natural mortality.
 
The methods and software developed in this project were applied to length data for the Western Yellowfin Bream in Shark Bay, Tarwhine, Breaksea Cod, Dhufish, Snapper from NSW, Mud Crabs, King George Whiting, and Tailor.  The data for King George Whiting and Mud Crabs were found to be inappropriate for analysis using the approaches developed in this study. Although catch curve and relative abundance analysis produced highly inconsistent estimates of mortality for Breaksea Cod, reasonable and realistic estimates of mortality were produced for the other species. For Tailor, it was found that the assumption of constant natural mortality  resulted in a better fit of the fishery model than that which was obtained by using the length-dependent natural mortality assumption.
 
The analyses that were undertaken in this study demonstrated that the length-based approaches, while less precise and reliable than age-based methods, had potential for use in stock assessment. This is particularly the case for recreational fisheries, for which length samples are likely to be more readily available than age samples.
 

Aquatic Animal Health Subprogram : exotic disease training manual

Project number: 2002-645
Project Status:
Completed
Budget expenditure: $48,780.00
Principal Investigator: Shane Raidal
Organisation: Murdoch University
Project start/end date: 19 Oct 2002 - 15 Dec 2005
Contact:
FRDC

Need

In recent years, demand for high quality seafood world-wide has increased significantly and continues to increase. This demand cannot be met by wild capture fisheries and has led to expansion of the world's aquaculture industries. In Australia, aquaculture is also growing. In the past 5 years the value of Australian aquaculture has doubled to approximately $700 million (ABARE 2001) and is expected to increase to $2.5 billion by 2010 (ACIL Consulting 1999). As the industry expands and intensifies the risk of infectious disease outbreaks also increases and there is a need for an increased level of expertise nation-wide on aquatic animal diseases.

As the range of aquaculture species expands so, too, will the range of diseases. Disease diagnosis and control will become an even higher priority than in the past. There will be a requirement to maintain and improve disease diagnostic capability. Increased diagnostic services will be required in these specialised areas, and training of personnel in aquatic animal pathology, bacteriology, virology, parasitology and mycology will be essential.

Currently, research on, and diagnosis of, aquatic animal diseases is undertaken with some limitations by State laboratories, private veterinary laboratories, universities, research institutes, and CSIRO divisions including AAHL Fish Diseases Laboratory (AFDL) at CSIRO Livestock Industries. It is essential to build on these resources to become better prepared for the anticipated growth in industry.

Training courses for diagnosticians and fish health specialists will be required to maintain Australia's proficiency to detect and diagnose aquatic animal diseases, and maintain the confidence of our trading partners. Due to increased world trade and travel, the threat of exotic disease is increasing. This project is aimed at providing information and training to aquatic animal health specialists to assist in recognition of exotic disease, and management of disease emergencies.

References
1. ABARE 2001. Australian Fisheries Statistics 2000, Canberra, ACT.
2. ACIL Consulting 1999. Aquaculture beyond 2000. Facilitator’s Report, prepared by Denis Hussey, Senior Associate, ACIL Consulting on a workshop, Changing Direction, held 23-24 August 1999, Canberra.

Objectives

1. To produce a training resource that can be used by tertiary education organisations, animal health professionals and other interested members of the public that outlines in some detail the background to exotic disease diagnosis and control in Australian aquatic animals.
2. Prepare material to be used in providing a training course in recognition and management of exotic disease outbreaks.
3. Organise and provide a training course in recognition and management of exotic disease outbreaks, based at AAHL.

Final report

ISBN: 0-86905-847-9
Author: Shane Raidal

Development and testing of a dynamic model for data from recreational fisheries

Project number: 2002-075
Project Status:
Completed
Budget expenditure: $112,210.00
Principal Investigator: Norman G. Hall
Organisation: Murdoch University
Project start/end date: 19 Oct 2002 - 30 Jun 2005
Contact:
FRDC

Need

Models are urgently required that will allow stock assessment for fisheries in which a significant component of the catch is taken by recreational fishers, where these models will rely on abundance indices from the commercial fishery, occasional length or age composition samples from the total catch and occasional estimates of total catch. Given the expense associated with recreational surveys, there is a need for the development of an approach that would allow determination of an appropriate frequency for such creel censuses in order that they might provide the data necessary to achieve a specified level of precision from the resulting stock assessment. A method is required that will allow an assessment of the value of data derived from commercial fisheries statistics for use in assessing the stocks that are shared by recreational and commercial fishers, prior to making final management decisions on catch re-allocation from the commercial to the recreational fishing sector.

Objectives

1. To develop a dynamic fishery model that uses those types of data, which are typically available for recreational fisheries.
2. To assess the suitability of the model in providing a tool that fisheries agencies might use to investigate the trade-off between the cost and the resultant benefit for stock assessment associated with different frequencies of such surveys.
3. To assess the suitability of the model in providing an approach that might be used by fisheries agencies to investigate the consequences for subsequent stock assessment of reducing the proportion of the catch that is allocated to the commercial fishing sector.

Impact of environmental changes on the biota of Western Australian south coast estuaries

Project number: 2002-017
Project Status:
Completed
Budget expenditure: $125,374.00
Principal Investigator: Ian Potter
Organisation: Murdoch University
Project start/end date: 29 Jun 2002 - 15 Dec 2006
Contact:
FRDC

Need

Environmental and fisheries managers urgently need reliable data to underpin strategies to conserve or improve the ecosystems of normally-closed estuaries in the central region of the south coast of Western Australia. These managers thus need:

1. An understanding of the current status of the fish fauna of the highly-degraded Culham Inlet, and particularly of its population of black bream, and how that status has been influenced by extreme environmental perturbations in the recent past.

2. Reliable information on the extent to which the extreme environmental conditions experienced in certain of the last ten to fifteen years influenced either the spawning success and/or survival of the 0+ age class of black bream in Culham Inlet.

3. An understanding of the current status of the fish fauna of Stokes Inlet, which is less degraded than Culham Inlet but is still the subject of concern for local residents and visitors, and of Hamersley Inlet in whose catchment the vegetation has been the subject of only a relatively low level of clearing.

4. An ability to predict, qualitatively, the extent to which continuing degradation of any normally-closed estuary in the central region of the south coast of Western Australia will affect the fish faunas of those estuaries and, in particular, their recreational and commercial fish species. This information is required by the Department of Fisheries WA for developing its overall plan for managing the recreational and commercial fisheries in these estuaries (R. Lenanton, pers. comm.) and by other governmental authorities for developing strategies for conserving or restoring the quality of the important environments afforded by these estuaries.

Objectives

1. Determine, on a seasonal basis, the compositions of the fish fauna of the basin and riverine regions of Culham, Stokes and Hamersley inlets and ascertain whether pools upstream act as a refuge for black bream.
2. Relate any differences in the compositions of the fish faunas in the three estuaries to differences in the environmental characteristics within and between these estuaries, and in particular of salinity, dissolved oxygen and water levels.
3. Use age composition data to determine the variations in annual recruitment of black bream in Culham, Stokes and Hamersley inlets in recent years, and relate these to environmental conditions, and particularly to the relative estimated strength of freshwater discharge and whether or not the bar at the estuary mouth had been breached.
4. Compare the growth rates of black bream in the three estuaries and relate any differences that are detected to the environmental conditions that are experienced within each system.
5. Provide to environmental and fisheries managers an assessment of the levels at which salinity and dissolved oxygen influence the abundance of the main fish species and how those critical levels vary amongst those species

Final report

Synthesis and gap assessment of fish dietary data required for modelling ecosystems in south-western Australia

Project number: 2002-016
Project Status:
Completed
Budget expenditure: $114,894.00
Principal Investigator: Margaret Platell
Organisation: Murdoch University
Project start/end date: 19 Oct 2002 - 30 Dec 2005
Contact:
FRDC

Need

Through the research being undertaken in FRDC Project 2000/311, “Development of research methodology and quantitative skills for integrated fisheries management in WA”, it has been recognised that the dietary data available for Western Australian fish are limited and may result in an imprecise specification of the food web. An urgent need to collate the existing dietary data in order to assess their adequacy in developing information on the extent to which fish species predate upon fish and invertebrates, or ingest plant material, has been identified. Ecosystem modelling and monitoring of the “health” of the non-landed prey species will require the development and maintenance of a database containing consistent and comprehensive details of the relative proportions of the prey species in the diets of their predators. Gaps within the resulting database need to be determined and the research methods, that are required to fill these gaps, need to be identified. Without such data on dietary compositions, it will be impossible to ascertain accurately the relationships between species, thereby hampering the development of accurate ecosystem models. The utility of the existing data sets will be considerably enhanced by their collation and synthesis, and the resulting data are considered to be essential for the development of ecosystem models capable of providing the information required to manage fisheries in accordance with the principles of ESD.

Objectives

1. Develop a comprehensive database for the abundance, size composition and diets of the fish fauna in the estuaries and marine waters of south-western Australia.
2. Describe the diets of the various fish species.
3. Identify where dietary and other relevant data are lacking.
4. Determine appropriate sampling methods to obtain data for those areas where information is lacking.

Final report

ISBN: 86905-884-3
Author: Margaret Platell

Determination of biological parameters for managing the fisheries for mulloway and silver trevally in Western Australia

Project number: 2002-004
Project Status:
Completed
Budget expenditure: $214,217.00
Principal Investigator: Ian Potter
Organisation: Murdoch University
Project start/end date: 29 Jun 2002 - 30 Mar 2006
Contact:
FRDC

Need

The progressive rise in the number of recreational fishers in Western Australia is increasing the fishing pressure on the most sought-after recreational fish species in this State. The potential thus exists for these species to become exploited at levels that exceed those that are sustainable. The absence of biological data for mulloway, an icon recreational species, and silver trevally, the third most frequently-caught recreational fish species, has meant that the existing and proposed regulations, that were aimed at conserving and managing the stocks of these very important species, were not based on appropriate biological criteria. There is thus a strong need to develop a sound database for these species, which encompasses such crucial features as size and age compositions, growth, length and age at first maturity, fecundity and the location and time of spawning. Since the sand trevally, which is also fished recreationally, is morphologically so similar to silver trevally that it is very frequently confused with this species, and indeed is currently considered collectively with this species for management purposes, there is a need to understand the significance of those differences that are likely to exist between the habitats and biology of these two species.

The urgent need to acquire biological data on mulloway and silver trevally to underpin management plans has been highlighted by both RFAC and RecFishWest.

Objectives

1. To obtain the biological data that are required by managers to develop plans to conserve the stocks of mulloway and silver trevally in Western Australia. This will thus require determining the following characteristics of both of these species:
2. Size and age compositions, growth rates and the sizes and ages at which maturity is first reached.
3. Locations and periods of spawning, and whether they are multiple spawners.
4. Batch fecundity.
5. Estimates of mortality.
6. To elucidate the patterns of distribution of the silver and sand trevally, and thereby determine the ways in which they differ.

Final report

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