6 results

NCCP: Cyprinid herpesvirus 3 and its relevance to humans.

Project number: 2016-183
Project Status:
Completed
Budget expenditure: $23,362.00
Principal Investigator: Katrina Roper
Organisation: Australian National University (ANU)
Project start/end date: 9 Jul 2017 - 30 Aug 2017
Contact:
FRDC

Need

Carp (Cyprinus carpio) are an introduced fish that now dominate fish communities throughout many Australian inland waterways.[1] Recently, cyprinid herpesvirus 3, has been proposed as a potential biological control method for carp in Australia. [2] Reports have been published evaluating the susceptibility of non-target species [3]. However concerns remain around the ecological and environment impact of the release of the virus [4]. This proposal will provide from the published literature a risk assessment of the potential impact on human health from the release of the virus into Australian inland water systems. The psychosocial effects of a mass die off after release of the virus will also be considered in the context of comparison with similar events that have previously occurred.

A report will be provided to FRDC summarising the analysis of the literature.

1. Carp herpesvirus as a biological control for carp. Carp Factsheet CPFS7. PestSmart. March 2016.
2. Saudners G, Cooke B, McColl K, Shine R and Peacock T (2007) Modern approaches for the biological control of vertebrate pests: an Australian perspective. Biological Control 52: 288-295.
3. MColl K. (2016) Final report: Phase 3 of the carp herpesvirus project (CyHV-3). Invasive Animals CRC. Australian Government Department of Industry.
4. Lighten j and van Oosterhout C (2017) Biocontrol of common carp in Australia poses risks to biosecurity. Nature Ecology and Evolution 1:0087.

Objectives

1. To conduct a risk assessment via a systematic review on the potential impact on human health from the release of cyprinid herpesvirus 3 into Australian inland water systems.
2. To evaluate the potential psychosocial impact on the public from the mass fish die-off that will result from the release of the cyprinid herpesvirus-3.
3. To produce a discussion paper for FRDC summarising the findings of the first two objectives.

Final report

ISBN: 978-0-646-98525-1
Author: Katrina Roper and Laura Ford
Final Report • 2019-11-05 • 909.07 KB
2016-183-DLD.pdf

Summary

The present study, undertaken by the Australian National University, was developed to investigate the potential direct risks to human health of cyprinid herpesvirus 3 (CyHV-3), as a part of investigations into species specificity of the virus under the National Carp Control Plan (NCCP). The NCCP, tasked with determining the feasibility of potential use of CyHV-3 as a biocontrol for carp in Australia, was required to consider risks and potential impacts to human health as a key component of overall ecological, social, and soci-economic risks. Direct impacts to human health would signal immediate determination for non-feasibility of CyHV-3 as a biocontrol. At the time of the investigation, CyHV-3 has been identified in 33 countries, predominantly in aquaculture facilities, but with some wild outbreaks. In most of these countries, carp are consumed by humans as a food product. This study aimed to determine if any reports have been found which identify infection of human beings by CyHV-3, whether through ingestion or other forms of exposure. Psychosocial impacts were also considered in the review of literature, including grey literature.

Tactical Research Fund: Empowering Industry R,D&E: Transition to MEY goals for the Great Australian Bight Trawl Fishery

Project number: 2009-068
Project Status:
Completed
Budget expenditure: $72,697.00
Principal Investigator: Tom Kompas
Organisation: Australian National University (ANU)
Project start/end date: 31 Oct 2009 - 29 Jul 2010
Contact:
FRDC

Need

This project should prove to be a demonstration of how the judicious use of research and analysis can improve performance against the policy (CHSP).

Current assessments indicate that Bmsy for Bight redfish and deepwater flathead are 24% and 27% Bzero respectively. Applying the default Bmey = 1.2 Bmsy (as used in the Commonwealth and SESSF harvest strategy policy) would give target biomass levels of B28 and B32 respectively. These figures are uncertain due to an assumed stock recruitment relationship in the assessments and apparently cannot be used to estimate BMEY. As a result, the precautionary default B48 target is being used for both species. This is potentially resulting in many hundreds of tonnes loss to the fishery each year and the fishery operating at sub-optimal economic conditions.

There is an urgent need for estimates of Maximum Economic Yield (MEY) and fleet structure and efficiency in the GAB, to build on the proven sustainability, but also to ensure that profitability and efficiency targets are met as per the CHSP. This project has two components:

(1) Pursuing the CHSP through the calculation of MEY by incorporating economic information and calculations with fishery catch and effort information fitted to and projected by the existing biological stock assessment (built and maintained by CSIRO since 2006). A model that determines maximum economic yield requires a model structure that can iterate both the biological assessment and projections and also the economic calculations, and measures of profitability.

(2) Measures of efficiency to determine fleet structure and optimal combinations of inputs. An MEY target determines the most profitable level of overall catch but does not indicate the optimal number of fishing vessels and input configurations needed to secure that harvest. An MEY target combined with efficiency measures ensures profitability and maximum efficiency.

Objectives

1. Determine BMEY for the GABTF shelf multispecies trawl fishery targeting Bight redfish and deepwater flathead
2. Determine the optimal number of vessels and input configurations to harvest at MEY to ensure profitability and efficiency
3. Use the GABTF as a case study for the application of the CHSP to multi-species fishtrawl fisheries

The dynamics and distribution of food supplies for the Sydney rock oyster (Saccostrea glomerata) in southern NSW estuaries

Project number: 2004-224
Project Status:
Completed
Budget expenditure: $73,926.25
Principal Investigator: Ana Rubio
Organisation: Australian National University (ANU)
Project start/end date: 30 May 2004 - 28 Feb 2007
Contact:
FRDC

Need

A recent report by the Healthy Rivers Commission to the NSW Government has recommended that areas in estuaries suitable for the cultivation and safe harvesting of oysters should be identified and protected. Sydney rock oyster production in NSW and State wide average productivity (oysters/ha/y) has consistently declined since the late 1970’s despite the introduction of new technologies. The decline is not product demand-driven. Only one of the state’s 30 production estuaries shows an increasing trend in production over the past 10 years. The impact of diseases, acid sulfate soil drainage and the introduction of Pacific oysters into the Port Stephens estuary do not account for the overall decline. One hypothesis is that oyster production is decreasing because of limited food (seston) supplies. Oysters probably make up the largest fraction of the total biomass in NSW estuaries and process most of the primary production. Spatial variation in the quantity and quality of seston could limit cultured oyster growth. Farmers have identified the need to investigate oyster production decline and to identify food conditions required for optimum oyster growth and production. We propose to examine the components of seston, their spatial distribution and origin between oyster farming areas and their dynamics over time. The study will determine the spatial distribution of oyster growth rates in farming areas in response to resource availability and environmental conditions. This information will be used to assess the adequacy of food in estuaries, the identification of areas with optimal oyster growth rates and enable establishment of benchmark oyster growth rates for comparative analysis temporally and spatially. This will contribute to improving farming strategies and to identifying farming areas for protection. Oyster growth and food sources (which are intimately related to the concept of carrying capacities) in estuaries are a high priority in the ORAC 2000-2005 strategic plan.

Objectives

1. To characterize the food supply for oysters in selected NSW estuaries (quantity and quality).
2. To determine the spatial distribution and dynamics of seston in selected NSW estuaries
3. To identify the source of matter that supports oyster production and understand the trophic interactions in the aquaculture oyster system.
4. To assess oyster growth rates in terms of seston and nutrient levels
5. To develop a predictive ecological-trophic coupled model of oyster growth and productivity
6. To predict oyster growth based on oyster density and mortality levels, and size, achieving sustainable production parameters for the oyster industry
7. To integrate the above with GIS to map areas in terms of scales of food limitations
8. To transfer the results to the NSW oyster industry

Final report

Author: Ana Rubio
Final Report • 2008-10-20
2004-224-DLD.pdf

Summary

The primary outcome of this study has been to increase the understanding of the environmental drivers that influence the southern NSW Sydney rock oyster (SRO) industry, in particular in the Clyde and Crookhaven/Shoalhaven estuaries and to identify some of the factors that limit the production of SRO. Increased amounts of nitrogen and organic carbon are delivered by increased river flows following rain events and these were found to significantly enhance oyster growth in the two south NSW estuaries. During normal and/or dry conditions, the estuaries were nitrogen-limited suppressing primary production and, potentially, oyster growth. On the other hand, during heavy rain periods, large amounts of nitrogen entered the estuaries, which then became phosphorus-limited. Optimally an intermediate level of Nitrogen:Phosphorus ratio is desired for enhancing SRO production in the south coast of NSW so that neither nutrient is limiting.

An important outcome has been to identify the diet of the SRO in the Clyde River. Prior to this study, diet preferences for the SRO were assessed only under laboratory conditions and using a narrow range of food sources limited to some specific phytoplankton species. In this study a wider range of natural food sources were used as field experiments took place at the oyster cultivation grounds where oysters are exposed to a much wider array of food sources. Through the use of carbon and nitrogen isotopic signatures it was found that seagrass’ debris, its epiphytes and seasonal filamentous green macroalgae played little part in the SRO diet in the Clyde River. However, benthic diatoms were the main contributors of the diet. In addition, the signature of mangrove debris was found to be within the isotopic SRO diet range. Consequently, resuspension processes reflecting wind, currents and water depth play an important role in making benthic food sources accessible to the oysters and thus in coupling benthic and pelagic processes.

Another outcome of this study has been the identification of oyster condition index as an useful indicator of oyster performance in terms of stocking densities in order to assess production carrying capacity levels in an area. Condition index levels were found to decrease with increasing stocking density even when there was no statistically significant trend in oyster growth. These experiments suggested that the lowest experimental stocking density in the tray experiment (1 kg / m2) produced oysters with the highest condition index, at certain times up to 16% higher than the other two experimental stocking densities (2 and 3 kg / m2). The difference in oyster performance during winter was much lower (1%) as a result of oysters spawning at the end of autumn and due to drops in temperature levels. A similar relationship between condition index and oyster density was found in floating cylinders at the Shoalhaven/Crookhaven River. At densities above 0.5 kg / per cylinder there was a consistent and significant drop in condition index. Stocking densities used in this project were lower than the typical stocking density level used in NSW cultivations except for the highest level. However, biomass gain increased with stocking density without reaching a plateau. If a plateau would have been reached this would have indicated there would not be any advantage in having higher stocking densities.

The above environmental drivers were incorporated into a computer model that combined the hydrology and nitrogen levels in the Clyde River. The model was used to investigate the consequences of changes in phytoplankton levels, as the main component of the diet, and oyster growth. The output of this model suggested that an additional food source– a carbon source – in addition to phytoplankton was needed to reach the observed growth rates and that the nutrient deliveries into the estuary from rain events played an important role in enhancing oyster growth. 

In addition, a series of simple environmental indices were investigated to assess the carrying capacity of areas or estuaries. The indices chosen are easy to calculate by oyster growers and they can give an indication of when the ecological and production carrying capacity are exceeded. 

The above outcomes contribute to the ecological sustainability of SRO farming by identifying an optimum level of stocking density under which growers could maximize condition index of SRO. Overall, mud flat habitats, due to the presence of large biomass of benthic diatoms mainly, have been identified as a key parameter for maximizing oyster growth due to their contribution towards the SRO food source. 

Determination of patagonian toothfish age, growth and population characteristics based on otoliths

Project number: 1997-123
Project Status:
Completed
Budget expenditure: $22,850.00
Principal Investigator: John Kalish
Organisation: Australian National University (ANU)
Project start/end date: 29 Jun 1997 - 2 May 2001
Contact:
FRDC

Need

Data on fish age are essential to determine the production of fish stocks. Collection of age structure data early in the history of a fishery are particularly important to determine the natural mortality rate of a population. Data relating to the age structure of populations and growth rates can also be applied to the identification of stocks. Annual estimates of population age structure are employed to identify population responses to exploitation and environmental variability and can be used to develop more data intensive methods of population assessment (eg Virtual Population Analysis). Otoliths are the structures employed most often to estimate age of fishes and validation research at the ANU indicates that toothfish otoliths are suitable for this purpose.

A "stock" is the basic unit of management in most fisheries and identification of these units is a prerequisite to accurate assessment and effective management. There are no data on stock structure for Patagonian toothfish. As a result, we have no knowledge regarding the potential impacts of toothfish exploitation outside the AFZ on toothfish stocks within the AFZ.

Knowledge of toothfish biology is extremely limited. Given the lack of baseline biological data, it would be difficult to identify possible responses of toothfish stocks to exploitation or differences in life history characteristics among putative stocks. Identification of changes in basic life history characteristics such as age or size at maturity and timing of ontogenetic migrations are important to management of fish species within both a stock and ecosystem context.

Objectives

1. Validate otolith-based age estimates for Patagonian toothfish (Dissostichus eleginoides).
2. Establish routine age estimation procedures for Patagonian toothfish.
3. Determine growth rates for Patagonian toothfish.
4. Determine age structure of the toothfish populations from the AFZ surrounding Macquarie Island and other localities
5. Determine age structure from successive years of sampling to identify possible shifts in age structure or inconsistencies in the application of the age estimation method.
6. Liaise with groups involved with modelling the dynamics of toothfish populations.
7. Apply otolith morphometrics and otolith chemistry to discrimination of possible toothfish stocks.
8. Establish an inter-agency (international) program to determine if there is variation in the interpretation of toothfish otolith sections
9. Publish reports for immediate stock assessment and management purposes and peer-reviewed articles in international journals for dissemination of results.

Final report

Use of the bomb radiocarbon chronometer to validate fish age

Project number: 1993-109
Project Status:
Completed
Budget expenditure: $254,208.17
Principal Investigator: John Kalish
Organisation: Australian National University (ANU)
Project start/end date: 26 Jul 1993 - 26 Nov 2002
Contact:
FRDC

Objectives

1. Validate ages of SBT(Thunnus maccoyii), redfish(Centroberyx affinis), blue grenadier(Macruronus novaezelandiae), and school shark(Galeorhinus australis)
2. Determine the suitability of the radio carbon chronometer for age validation of oreo species
3. Determine other species suitable for age validation via the bomb radiocarbon chronometer

Determination of geographical structure of breeding population in several species of commercial fish

Project number: 1976-007
Project Status:
Completed
Budget expenditure: $0.00
Principal Investigator: Barry Richardson
Organisation: Australian National University (ANU)
Project start/end date: 28 Dec 1980 - 31 Dec 1980
Contact:
FRDC

Objectives

1. Gain a basic understanding of the genetic structure of certain fish populations and the relationships between fish stocks in different areas around Australia

Final report

Author: B.J. Richardson and M. MacDonald
Final Report • 7.71 MB
1976-007-DLD.pdf

Summary

The study collected liver tissue samples from Australian Salmon in various states to analyze their genetic variation and population structure. The results showed low levels of genetic diversity in western salmon and only one useful marker system for population structure analysis. The tests revealed no significant differences in genders or age classes, and no significant geographical heterogeneity. The coefficient of kinship was used to measure breeding and was plotted against geographic distance to obtain a visual summary of the salmon's spatial breeding structure. Overall, the study suggests that there is little genetic differentiation between populations of Australian salmon in different regions.
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