11 results

Tactical Research Fund: Empowering Industry R&D: Trials of T90 mesh configuration for bycatch reduction and more efficient fishing in the Great Australian Bight Trawl Fishery

Project number: 2007-063
Project Status:
Completed
Budget expenditure: $72,064.46
Principal Investigator: Semi Skoljarev
Organisation: Great Australian Bight Fishing Industry Association Inc (GABIA)
Project start/end date: 14 Aug 2007 - 30 Jun 2008
Contact:
FRDC

Need

There is an obvious need to reduce bycatch in the fishery consistent with mandatory legislative and policy requirements (EPBC and FMA) and to develop more efficient harvest protocols. Consistent with this, GABIA has provided full support for the introduction of T90 mesh into their fishery through the mandatory use of T90 extensions and/or codends from 1 January 2007. Potentially, even greater benefits are possible with a move to T90 gear from the wingends to codend. Such nets have been tested and shown to be effective in some Icelandic fisheries.

Modifications to gear (particularly the very recent move to full T90 nets in some overseas fisheries) have been shown in other fisheries to be effective in reducing fuel consumption consistent with the need to reduce operating costs and to reduce greenhouse gas emissions in the fishing industry. This proposal aligns to priorities of reducing environmental impacts of trawl fisheries and of increasing operating efficiency and industry profitability.

Objectives

1. Run sea trials to compare catch composition of "standard" GABTF net design with the full T-90 net design
2. Obtain preliminary quantitative estimates comparing target species catch composition of each net design
3. Obtain preliminary quantitative estimates comparing bycatch species catch composition of each net design
4. Quantitatively compare and assess the towing efficiency of each net design
5. Qualitatively assess and compare differences in fish quality among net designs
6. Effectively convert the results into tangible benefits for the GABTF and AFMA's Bycatch Reduction Program

Final report

ISBN: 978-0-9805388-6-1
Author: Semi Skoljarev

A novel method for obtaining age compositions from ancillary biological data and it’s potential for cost reductions in stock assessments

Project number: 2005-023
Project Status:
Completed
Budget expenditure: $99,882.65
Principal Investigator: Simon Robertson
Organisation: Agriculture Victoria
Project start/end date: 30 Aug 2005 - 30 Jun 2009
Contact:
FRDC

Need

Age composition data provides the key information necessary to effectively manage fisheries. The proposal provides a mechanism where age composition data can be gained using length frequency data and age composition data from different years and sampling events, which has previously been impossible. The benefits will be a reduced need for production ageing, more timely age composition data and the ability to construct age composition data from historical length frequency data where no samples were collected for ageing.

Currently the Age-Length Key (ALK) is the most widely used numerical method for assessing the age composition in a large sample of length-frequency data. However, the application of ageing data in this approach is restricted to the original sample of length distribution (ageing data from the same year the length-frequency sample is taken). Due to this severe limitation, the ageing information must be regenerated for each new data sample. Using the Fredholm First Kind equations, previous years ageing data can be used to generate the underlying age composition from the current length-frequency data. Furthermore, the ageing data may be added to include many years, improving the robustness of the statistic which can then be used to decompose the underlying age distribution from the given length frequency.

As noted by a number of referees, the major problem with the current methods is variable recruitment. We have demonstrated that the technique is tolerant to the most extreme changes in age frequency (see accompanying text). These extreme changes in age frequency are greater than any changes that could occur naturally through recruitment. The issue of variable growth may affect the efficacy of the approach, but to our knowledge, has only been observed in two species. These are black bream and blue grenadier. It is proposed that the technique be demonstrated on blue grenadier in the first year.

The cost of collecting ageing data is high, with approximately $150,000 spent each year on ageing samples from commercially important species within the South East Fishery. Due to the cost, the number of species aged is not optimal and species are prioritised on a scientific and social-political basis. The cost-benefit of applying this approach is intuitively a large reduction in cost of ageing to industry and more timely information on the age structure of the population. A formal cost benefit analyses will need to be conducted on a species by species basis. This is a function of different cost structures for ageing different species, different numbers of samples that need to aged for each species. These different numbers of estimates that need to be made for each species is primarily due to longevity and stock structuring.

The age-structured data obtained from this project will benefit the South East Trawl Fishery, the Great Australian Bight Trawl Fishery and the Gillnet, Hook and Trap Fishery which are supported by The Integrated Scientific Monitoring Program (ISMP) and various other stock assessment programs that rely on age-structured data.

Further, age composition data will be able to be reconstructed historically from species where samples were not aged but length-frequency data were collected. This will enable age-structured population analysis where the lack of ageing data prevented these stock assessment techniques from being previously used. The net effect of this approach is to greatly improve the knowledge base from which species are managed. One of key advantages of this approach is, if successful, will at the very least compliment current methods and provide temporal and spatial coverage of age composition information which is currently cost prohibitive and only collected for a few, high value species.

The implication of a technique that can provide age-composition data free from the restriction of those associated with the ALK is more cost-effective resource management.

The proposal has been developed in two parts, the first component is a 'Proof of Concept Study' where the use of the Fredholm First Kind Equations to provide age compositions from length frequency data will be further examined. If this is not assessed as successful in a workshop environment, the project will be terminated at the end of the first year. The second and third year will examine a broad range of species.

Objectives

1. During first 12 months provide a Proof of Concept Study on two species. One of the species with a short longevity and stable age composition over time and the second, with variable recruitment and higher longevity. The proposed species for this objective will be school whiting and blue grenadier.
2. Using Central Ageing Facility data, determine which commercially important fish stocks and associated data provide sufficient information for estimation of the age composition from length frequencies
3. Apply limited length-at-age data with extensive length-frequency data to improve time series of age compositions for fish stock assessment.
4. Determine the appropriate sample size for collection of age data.
5. Examine robustness of the numerical methods to length-specific selectivity.
6. Compare the new techniques with existing numerical methods.
7. Develop user friendly software and data environment for numerical reconstruction of cohorts and age groups.
8. Disseminate method to a broad audience of end-users
9. Provide cost-benefit analysis for each species undertaken comparing the financial benefit of using the new technique to the cost associated using traditional techniques. The objective will be delivered as species are examined.

Final report

ISBN: 978‐1‐74264‐135‐5
Author: Simon Robertson

Age validation of deepwater flathead from the Great Australian Bight Trawl Fishery

Project number: 2005-008
Project Status:
Completed
Budget expenditure: $48,957.00
Principal Investigator: Kyne Krusic-Golub
Organisation: Agriculture Victoria
Project start/end date: 29 Jun 2005 - 30 Apr 2008
Contact:
FRDC

Need

Deepwater flathead (Neoplatycephalus conatus) is the dominant component of catches caught in the Great Australian Bight Trawl fishery (GABTF), increasing to and accounting for approximately 40-50% of landings. Most of the deepwater flathead catch is taken at depths of 100-200 m, and the majority of fish are between 45 and 60 cm. Very few individuals less than 35 cm TL are caught.

The Central Ageing Facility has been contracted to provide estimates of age for deepwater flathead for the GABTF. The standards/protocols for age estimation have been developed over time by a combination of pattern recognition of the otolith increment structure and the limited biological data available. No validation has been undertaken on the periodicity of increment formation and if they are formed annually. Providing repeatable and accurate age for this species is complicated by the poor increment clarity on the otoliths, uncertainty in the timing of the increment formation and potential temporal differences in otolith growth.

Further complicating the process of age estimation is the protracted spawning period for deepwater flathead. In the Great Australian Bight the spawning period last from October to March. Spawning activity in the western-central Bight peaks in late summer. The protracted and temporal variation in spawning within this fishery is likely to result in variable hatching times and consequently exhibit different patterns of growth on the otolith of juvenile specimens. A hatching event occurring 10 months prior to the formation of the first increment will be evident from the larger distance between the otolith primordium and the first increment than that of an individual hatched 4-5 months later. This difference can bias age estimates, even for an experienced reader. The correct identification of the first increment is particularly important when the catch is made up of younger samples as a bias of 1 year in the age estimation of a 4-year-old has disproportionately greater effects on the population parameter estimates than that of a 30-year-old.

Annual total allowable catches are heavily reliant on age estimates, as other biological data are limited. Unvalidated age estimates have produced a maximum age of 33 years for females and 28 years for males. The majority of the catch is comprised of 4 to 8 year-old-fish and age-at-recruitment is at approximately 3-5 years of age. Therefore accurate and precise (repeatable) age estimates of these younger age classes are essential for the ecologically sustainable development of this fishery. However, it is generally the youngest and the oldest fish which are the most difficult to age accurately and which are most influential in the estimates of growth, mortality and longevity.

Difficulties exist in the stock assessment of deepwater flathead due to the lack of contrast within the CPUE data. A better understanding of CPUE will greatly enhance the confidence in stock status and MSY. However in the absence of strong signal in the CPUE, stock assessment models rely on other information to provide some insight into stock status. The most important information available at the moment is catch at age data to provide some indicator of strength of recruitment into the fishable biomass and the loss of older proportion from the population. Accurate (ie validated) aging is therefore essential.

A simple equilibrium model was run by Brent Wise (BRS) to demonstrate the effect of uncertainty in aging has on MSY using the deepwater flathead biological parameters. This sensitivity analysis was based on the current ageing versus ageing that assumes that fish are in reality 2 years older. The analysis showed that there is a 30% decrease in available biomass if the current ageing is shown to be biased. A bias of 2 or moreyears in the age estimation could be a reality for this species due to the uncertainty in timing and the position of the first zone formation and timing of subsequent zone formations.

In the absence of accurate age data, management may be making decisions based on an estimated fishable biomass 30% higher (assuming 2 year bias) than the true fishable biomass. The effect of this would be unsustainable level of TAC from the key species within the GAB.

The objectives of this project will allow the timing of increment formation to be determined for age classes 4-8 years old and the validation/timing of the first growth increment. Additionally, through the validation of the first increment, information on juvenile growth can be examined. Information on juvenile growth is important because growth rates have been implicated as predictors of annual abundance of young fish. Growth differences may be different between areas and year classes depending on the time of hatching and the timing of first increment formation. A detailed analysis of variation in growth rates within the 0+ cohort will allow for the further refinement of age estimates. This will improve the assessments, which will assist managers in meeting the objectives for the sustainable use of the resource

Objectives

1. Validate the periodicity of increment formation from marginal increment data and daily age estimation to the first opaque zone.
2. Determine the count of presumed daily rings between the primordium of the otolith and the outside edge of the first opaque zone for young fish caught in different locations within the GAB
3. Implement standards on the age estimation of this species based on the timing of increment formation and the variability of 0+ age to the first increment formation.
4. Understand the variability in growth rates of juvenile deepwater flathead.

Final report

ISBN: 978-1-74326-201-6
Author: Kyne Krusic-Golub

Spawning and reproductive characteristics of Bight redfish and deepwater flathead in the Great Australian Bight trawl fishery

Project number: 2003-003
Project Status:
Completed
Budget expenditure: $89,975.00
Principal Investigator: Lauren P. Brown
Organisation: Agriculture Victoria
Project start/end date: 29 Jun 2003 - 3 Jun 2006
Contact:
FRDC

Need

Bight redfish (Centroberyx gerrardi) and deepwater flathead (Neoplatycephalus conatus) are the two principle commercial species captured along the continental shelf of the Commonwealth managed Great Australian Bight Trawl Fishery worth an estimated $7 million per annum.

Current assessments, based on available data, indicate that Bight redfish fishing mortality is rising and likely to reduce the biomass to below the trigger biological reference point. The outcomes of stock assessments are highly sensitive to the shape of the maturity ogive and fecundity-length/age relationships. Given the current high uncertainty about the validity of existing Bight redfish and deepwater maturity and fecundity relationships, GABFAG has recommended that these be determined with high priority. More scientifically defensible maturity ogives and fecundity-length and fecundity-age relationships will markedly reduce uncertainty in the stock assessments.

Objectives

1. Determine maturity ogives (against length/age) and sex ratios of spawning Bight redfish and deepwater flathead.
2. Describe gonad maturation cycles and determine the relationship between egg production (fecundity) and length/age in female Bight redfish and deepwater flathead
3. Conduct per recruit analysis to identify harvest strategies which allow optimum Bight redfish and deepwater flathead egg production (and therefore recruitment)
4. Provide Industry, GABMAC and stock assessment scientists with information on GABTF species biology.

Final report

ISBN: 978-1-74199-104-8
Author: Lauren Brown
Final Report • 2007-06-13 • 1.20 MB
2003-003-DLD.pdf

Summary

This project addressed some of the important information gaps identified during assessment workshops for Bight redfish and deepwater flathead.  Improved stock assessments, which incorporate the latest biological parameters (size-at-maturity, fecundity and sex ratio), has lead to the setting of accurate Bight redfish and deepwater flathead TACs.  Gear regulations have been proposed that include minimum mesh sizes and T90 extensions, which along with reducing discard species, allow small deepwater flathead to escape capture, and thereby increasing reproductive capacity of the flathead population.

This information has been provided to Great Australian Bight Fisheries Assessment Group (GABFAG) as part of formal and informal reporting arrangements.  It has also been distributed to the public via media releases.

Keywords: Bight redfish, Centroberyx gerrardi, deepwater flathead, Neoplatycephalus conatus, eggs per recruit, fecundity, reproduction, size- and age-at-maturity, spawning

Effects of Trawling Subprogram: assessment of bycatch in the Great Australian Bight Trawl Fishery

Project number: 2000-169
Project Status:
Completed
Budget expenditure: $97,770.00
Principal Investigator: Ian Knuckey
Organisation: Agriculture Victoria
Project start/end date: 16 Oct 2000 - 27 Nov 2002
Contact:
FRDC

Need

The GAB Management Advisory Committee (GABMAC) and the GAB Industry Association (GABIA) have raised concerns that they do not have the data necessary to assess the GABTF's compliance with ESD principles. If the core objectives of The National Policy on Fisheries Bycatch are to be implemented for the GABTF, there is an essential need for baseline data on bycatch to be gathered. Once this information is available, they will be able to determine if bycatch levels are acceptable or if there are particular times or regions in which the bycatch levels in the GABTF are deemed too high. When a comprehensive understanding of the nature of the bycatch issue in the GABTF is established, it will be then possible to investigate the most appropriate ways of reducing the levels of bycatch.

Objectives

1. Design an onboard sampling strategy which will provide a representative sample of the spatial and temporal dynamics of the total catch composition (retained and discarded) in the GABTF.
2. Undertake onboard sampling of commercial vessels and collect basic biological data (size, growth, age, maturity etc.) on the important species caught in the GABTF.
3. Based on the data collected during this project, provide Industry, the GABMAC and stock assessment scientists with information on GABTF species biology and bycatch composition appropriate to their specific needs.
4. Investigate the potential for Environment Australia to fund data collection from commercial vessels working within the GAB Marine Park which can be used in conjunction with or comparison to the CSIRO research cruise. (To be negotiated)

Final report

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