14 results
Environment
PROJECT NUMBER • 2017-141
PROJECT STATUS:
COMPLETED

New tools to assess visual fish health

In 2018 Infofish Australia Pty Ltd undertook a trial in Gladstone Harbour using machine learning tools to assess photos for fish health issues. The project was commissioned by the Fisheries Research and Development Corporation (FRDC) and the Gladstone Healthy Harbour...
ORGANISATION:
Infofish Australia Pty Ltd
Environment
PROJECT NUMBER • 2017-109
PROJECT STATUS:
COMPLETED

Development of Fish Health Indicators for the Gladstone Harbour Report Card

As the link between land and sea environments, estuaries are complex ecosystems vulnerable to human impacts, which directly and indirectly affect plants and animals, including fish. Fish are key biological indicators of environmental contamination, as they are water breathers, common in aquatic...
ORGANISATION:
CQUniversity (CQU) Gladstone

Developing and testing a multi-species, automated fish in-feed system for a production line to add-value and supply large local markets, replacing imports

Project number: 2015-225
Project Status:
Completed
Budget expenditure: $140,000.00
Principal Investigator: Brad L. Duncan
Organisation: Lakes Entrance Fishermans Cooperative Ltd
Project start/end date: 30 Jun 2015 - 29 Sep 2017
Contact:
FRDC

Need

Commercial in confidence. To know more about this project please contact FRDC.

Objectives

Commercial in confidence

Revitalising estuaries and wetlands for carbon sequestration, biodiversity, fisheries and the community

Project number: 2012-036
Project Status:
Completed
Budget expenditure: $400,000.00
Principal Investigator: Colin Creighton AM
Organisation: Colin Creighton
Project start/end date: 29 Jun 2012 - 29 Jun 2013
Contact:
FRDC

Need

Business as usual has caused the problem we seek to address. Australian estuaries and wetlands have been under-valued and much of their ecological function has been lost due to a multitude of small, past decisions coupled with a lack of understanding of their importance and community benefits.

Connectivity loss is an issue across Australia - eg road bridges, causeways, tidal barrages, culverts, ponded pastures, bund walls. As an example, GBRMPA has mapped in excess of 1500 barriers to fish passage just in the Burdekin catchment.

These various barriers have been constructed in times past when knowledge was lacking. We now as a community appreciate the many values of coastal ecosystems and generally the community supports their repair as a means of addressing the legacy of past decisions.

At the same time, a note of caution is necessary. in many cases there has been irrevocable loss. The art form in this Australia-wide Plan will be to identify the "easy wins" - where other public or private assets are not substantially at risk, the benefits well outweigh the costs and the overwhelming community asttitude supports repair works.

Objectives

1. Use case studies in NSW and Qld that build on previous activities and that demonstrate the multiple benefits and opportunities for further investment in connectivity & wetland repair
2. Develop an Australia-wide business plan suitable for 5 year investment that focuses on the remedial works, activities, planning, institutional arrangements and legislation to retain and repair ecological function in estuarine and wetland ecosystems
3. Present within 12 months the business case to a wide range of government, industry and community stakeholders so that understanding and support is fostered for the proposed investment initiative
4. Capitalise on a whole host of prior research and wetland mapping activities so that the Australia-wide business case is well foundered and demonstrates the return on investment from repair activities

Final report

ISBN: 978–0–992366–2-2
Author: Colin Creighton
Final Report • 2013-11-10 • 1.91 MB
2012-036-DLD.pdf

Summary

This project puts forward the proposal that stakeholders and government should concentrate on repair of the more developed coastal catchments around Australia where major investment and Australian Government leadership is required to re‐establish estuary productivity.

It seeks to deliver multiple benefits to the Australian community – to increase fisheries productivity, improve coastal water quality, enhance catchment hydrology, repair coastal biodiversity, finetune flood control, re‐establish carbon sequestration and reinforce foreshore buffering against extreme events.

The business case sets out the rationale and the priority opportunities for investment, to repair and restore, under a 'no regrets' policy, estuary and inshore wetland and floodplain areas. It seeks to maximise community benefits from these important parts of our landscape while minimising costs and impacts upon adjacent land users of the coastal zone.

It builds upon the Australian love of coastal landscapes and the resources they provide and the Australian community’s and political commitment to implement major natural resources initiatives such as the Natural Heritage Trust, Caring for our Country and the Biodiversity Fund. Like Reef Rescue and the National Action Plan for Salinity and Water Quality, the business case proposes a major focus, in this case on estuaries and their wetland ecosystems.

Most importantly, through ongoing fisheries productivity, the proposed once‐off five‐year Australian Government investment will return economic benefits year in and year out that will far outweigh the $350M costs of repairing these key estuary assets. Our estimates suggest a break‐even for investment is well less than five years and from then on benefits exceed costs forever.

Further repair and management investment will be required following the proposed once‐off five‐year agenda‐setting Australian Government investment. This business plan recognises this ongoing investment need. Similar to already successful schemes in USA and UK and building on schemes already underway in NSW and Victoria, this plan proposes various instruments and systems to ensure overall benefits can be incentivised into the future. This includes empowering industry groups, private landholders, Local Governments and communities to continue the repair of coastal assets and their management.

Keywords: climate change, estuaries, business case, coastal catchments, coastal zones, fisheries productivity

Project products

Report • 23.61 MB
2012-036-revitalising Great Barrier Reef estuaries and coastal wetlands.pdf

Summary

This proposal aims to increase fisheries productivity, improve coastal water quality, enhance catchment hydrology, repair coastal biodiversity and flood control, and re-establish carbon sequestration and foreshore buffering.
 
The business case sets out the rationale and the priority opportunities for investment, to repair and restore, under a 'no regrets' policy, estuary and inshore wetland areas. It seeks to maximise community benefits from these important parts of our landscape while minimizing costs and impacts upon adjacent land users of the coastal zone.
 
It builds upon the excellent cooperation and commitment across the Great Barrier Reef community in implementing major initiatives such as Reef Rescue. It proposes a five-year government investment that will repair key assets for maximum public benefit. Equally importantly, this investment will identify how best to ensure overall benefits can be incentivised into the future, empowering industry groups, private landholders, local governments and regional natural resource management groups to continue the repair of coastal assets and their management.

Assessing the impacts of gillnetting in Tasmania: implications for by-catch and biodiversity

Project number: 2010-016
Project Status:
Completed
Budget expenditure: $390,623.79
Principal Investigator: Jeremy Lyle
Organisation: University of Tasmania (UTAS)
Project start/end date: 22 Jun 2010 - 14 Feb 2013
Contact:
FRDC

Need

Commercial and recreational fishers are permitted to use gillnets in Tasmania. There are several classes of gillnet distinguished by mesh size - commercial gillnets include, small mesh, graball and shark nets, while recreational gillnets include mullet and graball nets. During the past 5 years around 150 commercial operators each year have reported gillnet use, for an average catch of 200 tonnes of scalefish. Recent information for the recreational sector is limited though recreational netting remains popular, with over 10,000 net licences issued in 2009. Previous surveys indicate that recreational fishers target much the same species as commercial operators.

Over the past decade there have been several management initiatives, including a prohibition on night netting for most areas and, more recently, the introduction of maximum soak times. These initiatives have been designed to improve gillnetting practices, and reduce wastage and impacts on non-target species. Despite this, there have been conspicuous declines in the abundance of several key gillnet species along with increasing community concern about the ecological impacts of gillnetting. This concern has been particularly evident in the debate surrounding the introduction of marine protected areas, with gillnetting identified as a key threat to biodiversity. Furthermore, in the 2009 Scalefish Fishery review DPIPWE identified the need to develop strategic policy in relation to no-netting areas to address issues including resource sharing, wildlife interactions and stock management.

In view of the above, there is an urgent need to better understand how recent management initiatives have influenced netting practices, and to objectively assess the risks and impacts on target and non-target species. Ultimately such an understanding will be pivotal in informing the on-going debate over the future management of gillnetting in Tasmania.

Objectives

1. Synthesise available gillnetting information, with particular reference to links between operational parameters and catch composition
2. Determine catch composition and levels of by-catch associated with the main commercial gillnet fisheries
3. Assess implications of recent management changes on recreational netting practices
4. Assess the relationships between gillnet soak times, capture condition and by-catch survival
5. Evaluate the impacts of gillnetting on the biodiversity of key inshore ecosystems and potential strategies to mitigate these impacts

Developing targeted strategies for improving product quality through selected low value seafood supply chains

Project number: 2006-209
Project Status:
Completed
Budget expenditure: $325,270.00
Principal Investigator: Thomas Riley
Organisation: Western Australian Fishing Industry Council Inc (WAFIC)
Project start/end date: 29 Sep 2006 - 1 Jan 2011
Contact:
FRDC

Need

Surveys have identified a market absence and yet consumer demand for well-presented, well-priced, top quality fresh and frozen WA seafood products. The market value of WA seafood may be further enhanced by the development of high quality value-added convenience products. These products may be developed using innovative processing technologies that ensure that taste and texture quality equivalent to a fresh product are achieved. Documented attention to food safety and environmental issues should also be addressed as these have been identified in consumer surveys as of importance to the discerning purchaser. Such value-adding, resulting in an extended shelf-life, may also result in export opportunities not currently available to WA suppliers.

To modify current industry practices, and develop new processing protocols to meet these emerging markets, there is a need for species specific, whole of supply chain microbiological and biochemical research, aligned with product quality assessment. Low value seafood with generally short shelf-lives will be chosen as the target sectors to maximize the potential increase in profit by extending shelf-life or by developing new product lines.

There have been no investigations to identify specific spoilage organisms that are found on seafood along the WA coast. Virtually nothing is known about any of the microflora of WA marine species. In terms of finfish in other parts of Australia, cool water fish are generally spoiled by Shewanella putrefaciens and similar pseudomonads, but the situation in warm water species is less clear with Pseudomonas fragi having been reported. The occurrence of these on WA species is unknown, but without this knowledge it will not be possible to design appropriate preservation, storage and packaging strategies to deal with spoilage organisms.

Objectives

1. To complete microbiological, biochemical and temperature analyses of six seafood supply chains.
2. To determine the impact of specific spoilage organisms/products on product quality through the test supply chains.
3. To identify and validate supply chain intervention and/or value-adding protocols which improve shelf-life or enable the development of new products.

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.

Environmental flows for subtropical estuaries: understanding the freshwater needs of estuaries for sustainable fisheries production and assessing the impacts of water regulation

Project number: 2001-022
Project Status:
Completed
Budget expenditure: $535,588.54
Principal Investigator: Julie B. Robins
Organisation: Department of Primary Industries (QLD)
Project start/end date: 23 Jul 2001 - 30 Jul 2007
Contact:
FRDC

Need

Freshwater allocations to sustain fisheries

The 1994 COAG Water Reform Agreement and various state legislation (e.g. Water Act 2000 in Queensland) requires managers to allocate water to maintain downstream ecosystem health. One aspect of ecosystem health is estuarine and coastal fisheries production. Information on the role of freshwater in maintaining the productivity of commercial and recreational fisheries is needed to ensure that estuaries and their stakeholders are duly represented in the water allocation processes. Natural resource managers (fisheries and water) need to be made aware of the fishing industry’s vulnerability to the impacts of non-fishing activities, such as water regulation. This issue has been identified as a challenge for the fishing industry in reaching sustainable production (see Challenge 1 of FRDC’s R&D Plan 2000, page 59).

Logical frameworks for research leading to new procedures and methods

A logical framework needs to be developed for investigating the role of freshwater flows in estuaries. Procedures to assess the impacts of current and proposed water infrastructure in Australian coastal rivers on estuarine fisheries need to be developed. Methods for monitoring biological responses to environmental flows are needed to provide feedback to managers as to whether desired fisheries-related outcomes are being achieved under current water allocations.

Enhancing the research outcomes - integrating across research disciplines

An integrated research program is needed to develop a robust sampling proceedures that can investigate the role of freshwater flows in estuaries and the impacts of modified flows on fisheries production. The CZCRC offers the opportunity to integrate flow-influenced fisheries data with other hydrological (i.e. costal modelling) and primary productivity (i.e. nutrient cycling) research projects that will provide greater insight into ecosystems processes.

Objectives

1. To develop a logical framework for investigating (i) the role of freshwater flow, and (ii) the effects of modified flows, on estuarine fisheries production.
2. To review the current knowledge of the relationship between freshwater flows and estuarine fisheries production.
3. To correlate historical flow and fisheries production data of subtropcial Queensland estuaries.
4. To develop procedures for assessing the changes in estuarine fisheries production that result from water abstraction and regulation.
5. To develop and communicate guidelines on environmental flows for estuarine fisheries to water managers, water users, the fishing industry and the general community.

Final report

ISBN: 978-0-7345-0364-0
Author: Julie Robins
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