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SILVER TREVALLIES (2018)

Pseudocaranx georgianus, Pseudocaranx sp. "dentex" & Pseudocaranx wrighti, Pseudocaranx dinjerra

  • Ashley Fowler (Department of Primary Industries, New South Wales)
  • Rowan Chick (Department of Primary Industries, New South Wales)
  • Bradley Moore (Institute for Marine and Antarctic Studies, University of Tasmania)
  • David Fairclough (Department of Primary Industries and Regional Development, Western Australia)
  • Brent Womersley (Victorian Fisheries Authority)
  • Lee Georgeson (Australian Bureau of Agricultural and Resource Economics and Sciences)
  • Luke Albury (Department of Agriculture and Fisheries, Queensland)
  • Paul Rogers (South Australian Research and Development Institute)

You are currently viewing a report filtered by jurisdiction. View the full report.

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Summary

Silver Trevally inhabits estuarine and coastal waters throughout southern temperate Australia. Of the seven separate Australian stocks, five (in WA, SA, VIC, TAS and the Commonwealth) are sustainable. The NSW stock is depleting and the QLD stock is undefined.  

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Stock Status Overview

Stock status determination
Jurisdiction Stock Fisheries Stock status Indicators
Queensland Queensland CRFFF, ECIFFF, RRFFF Undefined Catch
CRFFF
Coral Reef Fin Fish Fishery (QLD)
ECIFFF
East Coast Inshore Fin Fish Fishery (QLD)
RRFFF
Rocky Reef Fin Fish Fishery (QLD)
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Stock Structure

Silver Trevallies comprises a complex of species that inhabits estuarine and coastal waters (depths of 10–230 m) throughout southern temperate Australia, from southern Queensland, south through New South Wales, Tasmania, Victoria, South Australia and southern and central Western Australia [Smith-Vaniz and Jelks 2006].

The biological stock structure of Silver Trevallies is uncertain. Fisheries are based on a species complex that varies by region, with Pseudocaranx georgianus present in all jurisdictions except Queensland, P. wrighti present in all jurisdictions except Queensland and New South Wales, P. dinjerra only present in Western Australia, and P. sp. ‘dentex’ only present in Queensland [Smith-Vaniz and Jelks 2006, Gomon et al. 2008]. There have been no investigations of potential genetic structure within these species. Investigations of population connectivity and post-settlement movement are also limited. Despite fast swimming ability, tag-recapture studies in Western Australia, New South Wales and New Zealand indicate restricted post-settlement movement of P. georgianus, potentially leading to ecological stock structuring over moderate (hundreds of kilometres) spatial scales [James 1980, Fairclough et al. 2011, Fowler et al. 2018].

Here, assessment of stock status is presented at the jurisdictional level—Commonwealth, Western Australia, Queensland, New South Wales, Victoria, Tasmania and South Australia.

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Stock Status

Queensland

Catch and effort data for Silver Trevallies (P. sp. ‘dentex’) in Queensland are poor. Commercial and charter catches of Silver Trevallies are not reported specifically, and the species is included as part of a broader ‘Trevally-unspecified’ category. Although species identification may be uncertain, Silver Trevallies is reported specifically in recreational fishing surveys and in 2013–14 approximately 2000 fish were landed [Webley et al. 2015]. It is unlikely that the combined commercial and recreational catches exceeded 10 t in 2017. Silver Trevallies are not subject to size restrictions, although a combined recreational possession limit of 20 applies to members of the Carangidae family. There is insufficient information available to confidently classify the status of the stock.

On the basis of the evidence provided above, Silver Trevallies in Queensland is classified as an undefined stock.

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Biology

Silver Trevallies biology [Rowling and Raines 2000]

Biology
Species Longevity / Maximum Size Maturity (50 per cent)
Silver Trevally 13–18 years, 690–938 mm TL 190–200 mm TL 
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Distributions

Distribution of reported commercial catch of Silver Trevallies

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Tables

Fishing methods
Queensland
Commercial
Hook and Line
Net
Indigenous
Hook and Line
Recreational
Hook and Line
Management methods
Method Queensland
Charter
Possession limit
Spatial closures
Commercial
Fishing gear and method restrictions
Limited entry
Spatial closures
Recreational
Possession limit
Spatial closures
Active vessels
Queensland
129 in CRFFF || ECIFFF || RRFFF, 0 in GOCDFFTF, 0 in GOCIFFF, 1 in GOCLF
CRFFF || ECIFFF || RRFFF
Coral Reef Fin Fish Fishery, East Coast Inshore Fin Fish Fishery, Rocky Reef Fin Fish Fishery (QLD)
GOCDFFTF
Gulf of Carpentaria Developmental Fin Fish Trawl Fishery (QLD)
GOCIFFF
Gulf of Carpentaria Inshore Fin Fish Fishery (QLD)
GOCLF
Gulf of Carpentaria Line Fishery (QLD)
Catch
Queensland
Indigenous Unknown
Recreational ~2 t

Commonwealth – Recreational The Australian Government does not manage recreational fishing in Commonwealth waters. Recreational fishing in Commonwealth waters is managed by the state or territory immediately adjacent to those waters, under its management regulations. Commonwealth – Indigenous The Australian Government does not manage non-commercial Indigenous fishing in Commonwealth waters, with the exception of the Torres Strait. In general, non-commercial Indigenous fishing in Commonwealth waters is managed by the state or territory immediately adjacent to those waters. Western Australia – Recreational (management methods) In Western Australia, a licence is required to recreationally fish from a powered vessel.

Western Australia – Recreational (Catch) Shore based catches are unknown, thus landings would be underestimated.

Queensland – Indigenous (management methods) In Queensland, under the Fisheries Act 1994 (Qld), Indigenous fishers are able to use prescribed traditional and non-commercial fishing apparatus in waters open to fishing. Size and possession limits, and seasonal closures do not apply to Indigenous fishers. Further exemptions to fishery regulations may be applied for through permits.

New South Wales – Indigenous (a) The Aboriginal Cultural Fishing Interim Access Arrangement allows an Indigenous fisher in New South Wales to take in excess of a recreational bag limit in certain circumstances—for example, if they are doing so to provide fish to other community members who cannot harvest themselves; (b) The Aboriginal cultural fishing authority is the authority that Indigenous persons can apply to take catches outside the recreational limits under the Fisheries Management Act 1994 (NSW), Section 37 (1d)(3)(9), Aboriginal cultural fishing authority; and (c) In cases where the Native Title Act 1993 (Cth) applies fishing activity can be undertaken by the person holding native title in line with S.211 of that Act, which provides for fishing activities for the purpose of satisfying their personal, domestic or non-commercial communal needs. In managing the resource where native title has been formally recognised, the native title holders are engaged with to ensure their native title rights are respected and inform management of the State's fisheries resources.

Victoria – Indigenous

In Victoria, regulations for managing recreational fishing may not apply to fishing activities by Indigenous people. Victorian traditional owners may have rights under the Commonwealth's Native Title Act 1993 to hunt, fish, gather and conduct other cultural activities for their personal, domestic or non-commercial communal needs without the need to obtain a licence. Traditional Owners that have agreements under the Traditional Owner Settlement Act 2010 (Vic) may also be authorised to fish without the requirement to hold a recreational fishing licence. Outside of these arrangements, Indigenous Victorians can apply for permits under the Fisheries Act 1995 (Vic) that authorise fishing for specific indigenous cultural ceremonies or events (for example, different catch and size limits or equipment). There were no Indigenous permits granted in 2017 and hence no Indigenous catch recorded.

Tasmania – Recreational (management methods) In Tasmania, a recreational licence is required for fishers using dropline or longline gear, along with nets, such as gillnet or beach seine. The species is subject to a minimum size of 20 cm in Tasmanian waters. A bag limit of 10 individuals and a possession limit of 20 individuals is in place for recreational fishers.

Tasmania – Indigenous (management methods) In Tasmania, Indigenous persons engaged in aboriginal fishing activities in marine waters are exempt from holding recreational fishing licences, but must comply with all other fisheries rules as if they were licensed. Additionally, recreational bag and possession limits also apply. If using pots, rings, set lines or gillnets, Indigenous fishers must obtain a unique identifying code (UIC). The policy document Recognition of Aboriginal Fishing Activities for issuing a UIC to a person for Aboriginal Fishing activity explains the steps to take in making an application for a UIC.

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References

  1. Conron, S, Giri, K, Hamer, P and Hall, K 2016, Gippsland Lakes Fishery Assessment 2016, Fisheries Victoria Science Report Series No. 14. The Department of Economic Development, Jobs, Transport and Resources, Melbourne.
  2. Conron, S, Green, C, Hamer, P, Giri, K and Hall, K 2016, Corner Inlet- Nooramunga Fishery Assessment 2016, Fisheries Victoria Science Report Series No. 11. The Department of Economic Development, Jobs, Transport and Resources, Melbourne.
  3. Fairclough, D, Walters, S, Holtz, M 2018, West Coast Demersal Scalefish Resource Status Report 2017. In Status reports of the fisheries and aquatic resources of Western Australia 2016/17: The state of the fisheries, eds DJ Gaughan and K Santoro. Department of Primary Industries and Regional Development, Western Australia, pp. 60–65.
  4. Fairclough, DV, Potter, IC, Lek, E, Bivoltsis, AK and Babcock, RC 2011, The fish communities and main fish populations of the Jurien Bay Marine Park, Centre for Fish and Fisheries Research, Murdoch University, Perth.
  5. Fowler, AM, Chick, RC, Stewart, J 2018, Patterns and drivers of movement for a coastal benthopelagic fish, Pseudocaranx georgianus, on Australia’s southeast coast. Scientific Reports, 8(1), 16738.
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