5 results

Golden fish: evaluating and optimising the biological, social and economic returns of small-scale fisheries

Project number: 2016-034
Project Status:
Completed
Budget expenditure: $378,994.00
Principal Investigator: James Tweedley
Organisation: Murdoch University
Project start/end date: 30 Sep 2016 - 29 Sep 2019
Contact:
FRDC

Need

Fish and crustacean stocks are under pressure from a range of sources, such as a growing population, increased fishing pressure and anthropogenic changes. These pressures, and the small-scale nature of many fisheries in terms of their economic return, highlight the need to develop cost-effective tools for assessing and valuing these fisheries. Such tools should be able to estimate the social and economic contribution of commercial and recreational fisheries to communities (FRDC 2014/008). However, FRDC 2012/214 has highlighted that ‘poor quality data’ on the economic value of recreational and indigenous fishing limits the development of optimal policies for these fisheries. Advances in aquaculture provide ‘new’ options for managers and the ability to restore or enhance target populations by releasing cultured individuals. Increasing interest from recreational fishers in enhancing fishing experiences and the development of government policies for release programs in WA, NSW and Victoria, combined with the creation of Recreational Fishing Initiatives Funds (RFIF), have focussed attention on restocking/stock enhancement as a potential management option. To maximise the likelihood for success, tools are needed to evaluate the potential effectiveness of any release program in increasing target populations. Combining the results of release program bioeconomic models with social and economic data, such as the increased catch (revenue) generation for commercial fishers and the economic returns and social values of recreational fishing, provides managers with improved decision making abilities based on an understanding of the social and economic implications of those decisions. The ability to assess the social values and economic contributions of fisheries to communities also provides much needed information, particularly on the catch, effort and motivations of recreational fishers, which are currently lacking in WA and can be used in the harvest strategy component of the Marine Stewardship Council certification process and to develop social and economic performance indicators for fisheries (FRDC 2014/008). Recfishwest has committed $100,000 from the WA RFIF to this proposal in recognition of the need for this research.

Objectives

1. Determine the motivations for using a fishery and the beliefs, attitudes and perceived benefits of release programs and other management options.
2. Determine the total economic value of the recreational and commercial sectors of each selected fishery.
3. Investigate the benefits of release programs in contributing to the optimisation of biological, social and economic objectives for those fisheries
4. Training for the next generation of fisheries and social scientists and fishery economists (Honours, PhD students and early-career researchers) and community engagement and education.

Final report

ISBN: 978-0-646-87654-2
Authors: James Tweedley Clara Obregón Michael Hughes Neil Loneragan Alan Cottingham Denis Abagna Malcolm Tull Sarah Beukes and Anne Garnett
Final Report • 12.73 MB
2016-034-DLD.pdf

Summary

This project investigates recreational and commercial fisher motivations for using a fishery and the beliefs, attitudes and perceived benefits of aquaculture-based enhancement programs and other management options. It also determines the total economic value for recreational fishing for Blue Swimmer Crabs (Portunus armatus) and Black Bream (Acanthopagrus butcheri) in a range of estuaries in south-western Australia and investigates the benefits of release programs in contributing to the optimisation of biological, social and economic objectives for those fisheries. Finally, it provides training for the next generation of fisheries and social scientists and fishery economists and project members engaged in community engagement and education.
Work was focused on two iconic small-scale estuarine fisheries in south-western Australia, i.e. those for Blue Swimmer Crabs and Black Bream. A two-phase approach to elicit common recreational fisher beliefs using semi-structured interviews (phase 1) and then sample a broader pool of respondents using closed-question online surveys (phase 2). Analyses demonstrated that motivations for recreational fishing were markedly different for the two fisheries, even when operating in the same system. Aquaculture-based enhancement was universally supported by the recreational sector as a fishery management approach as they believed it would enhance stocks and catches, and, although it may cause negative impacts, they were considered unlikely. Commercial fishers were less supportive of this management intervention. Enhancement of stocks was estimated to increase the economic value of recreational fishing through increased visitation. Biological modelling highlights that stocking could provide substantial benefits to the biomass of the target stocks, particularly Black Bream, but the parameters of any future stocking the need to carefully considered to ensure maximum benefits and the mitigation of density-dependent effects on wild stocks. Advice on the numbers and size-at-release for Blue Swimmer Crabs in the Peel-Harvey and Black Bream in the Blackwood River Estuary are provided to optimise the biological, social and economic dimensions of these fisheries.

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.

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

Factors required for the successful aquaculture of black bream in inland water bodies - extension to project 1997/309

Project number: 1999-320
Project Status:
Completed
Budget expenditure: $284,424.00
Principal Investigator: Ian Potter
Organisation: Murdoch University
Project start/end date: 6 Sep 1999 - 7 Mar 2004
Contact:
FRDC

Need

From the information in B2, there is, for the following reasons, clearly a need to develop a recreational inland fishery in south-western Australia utilising the euryhaline black bream.
1. To provide, for local residents and tourists in rural areas, access to an outstanding angling and food fish species that occurs naturally in Western Australia and which is both hardy and adapted to living in a wide range of salinities and temperatures.
2. To increase for rural areas, which, during recent years have suffered economic decline through land degradation and salinisation, the potential for tourism.
3. To reduce the fishing pressure on natural populations of black bream, the abundance of which in some estuaries has declined precipitously during the last 20 years, presumably through overfishing (FRDC 93/082).
4. To determine whether the very different growth rates recorded for geographically isolated natural populations of black bream are due to genetic differences or differences in the environments in which they live. Such data are important for ascertaining whether it is necessary to select carefully the populations used as broodstock.
5. To explore the possibility that inland water bodies could be used for producing black bream economically on a limited commercial scale.
6. To provide an angling species in inland saline water bodies of south-western Australia which occurs naturally in the region.

Objectives

1. The ultimate objectives of the proposed study are to determine the suite of conditions, in inland water bodies, that are required for rearing black bream to a size that is suitable for angling and to be able to demonstrate to potential stockers of black bream that such fish can then be readily caught on rod and line. This information will also be invaluable to those property owners who, in the future, wish to use their properties for producing small amounts of black bream for commercial puroposes. The above overall objectives will be attained by achieving the following individual objectives
2. Determine the relationship between the relative abundance and types of potential food that are naturally present in inland saline water bodies and those that are ingested by different sizes of black bream.
3. Determine whether yabbies constitute an appropriate live food source for particularly the larger black bream and where appropriate, self sustaining populations of yabbies can either established in inland water bodies or provided in a cost effective manner.
4. Determine, under controlled laboratory conditions, which of the currently available commercial fish feeds lead to optimal growth of black bream, and then, using the most cost effective of these feeds, determine the appropriate rate of feeding under field conditions over an extended grow-out period (12 months).
5. Determine the effectiveness of introducing underwater cover to reduce the predation of black bream by cormorants in inland water bodies.
6. Determine the effectiveness of using cages to house young black bream until they reach a size at which they are far less susceptible to predation by cormorants.
7. Determine whether the very different growth rates of black bream in the Swan and Moore River estuaries are paralleled by comparable differences when black bream from these two systems are cultured in the laboratory under identical salinity, temperature and food conditions.
8. Determine whether black bream are able to spawn successfully in inland water bodies and, if so, the broad characteristics of those water bodies where spawning occurs.
9. To provide information to farmers that will enable them to grow black bream successfully and thus constitute an extra source of revenue through charging for access to fishing on their land.

Final report