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Yellowtail Scad (2023)

Trachurus novaezelandiae

  • Matt Broadhurst (New South Wales Department of Primary Industries)
  • Rocio Noriega (Australian Bureau of Agricultural and Resource Economics and Sciences)
  • Jeff Norriss (Department of Primary Industries and Regional Development, Western Australia)
  • Brad Zeller (Department of Agriculture and Fisheries, Queensland)

Date Published: June 2023

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Summary

Yellowtail Scad have an Australian distribution from southern Queensland to northern Western Australia. The eastern stock of Yellowtail Scad occurs in Queensland, New South Wales and Commonwealth waters and is classified as sustainable. Catches off Western Australia are limited, and the stock is also sustainable.

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Stock Status Overview

Stock status determination
Jurisdiction Stock Stock status Indicators
Western Australia Western Australia Sustainable

Catch

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Stock Structure

Yellowtail Scad have an Australian distribution from southern Queensland to northern Western Australia (Stewart and Ferrell, 2001), and also occur off New Zealand (Horn, 1993; Horn and Maolagáin, 2020). Their biological stock structure remains unknown; but in New South Wales there is some evidence of geographical differences in growth rates which might indicate subpopulations (Stewart and Ferrell, 2001). Similar population variability has been observed for Yellowtail Scad off New Zealand (Horn, 1993).

Here, assessment of stock structure is presented at the biological stock level for eastern Australia. The Western Australia stock status remains jurisdictional.

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Stock Status

Western Australia

Most of the Western Australia catch of yellowtail scad is taken by the commercial purse seine sector, which targets sardines and operates in limited areas, usually in coastal bays (e.g., King George Sound and Cockburn Sound). Thus, Yellowtail Scad is vulnerable to the fishery only when they enter these waters and comprise a negligible component of the sector’s total catch. The purse seine nominal annual catch rates (kg/boat day) fluctuate interannually, but the latter's decadal average in the 1980s, 1990s and 2000s ranged from 5 to 7 kg/boat day. It then increased to 11 kg/boat day in the 2010s, and in 2021/22 was 9 kg/boat day day from an annual catch of 7 t. The boat based annual recreational catch was estimated to be < 1 t from a survey during 2020–21 [Ryan et al. 2022].

An ecological risk assessment [Blazeski et al. 2021] has rated all fishing to be a negligible risk to the Western Australia stock, and so it is classified as a sustainable stock.

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Biology

Yellowtail Scad biology [Stewart and Ferrell 2001; Broadhurst et al. 2018]

Biology
Species Longevity / Maximum Size Maturity (50 per cent)
Yellowtail Scad 24 years, 330 mm FL 2–4 years, 200–220 mm FL 
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Distributions

Distribution of the reported commercial catch of Yellowtail Scad

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Tables

Fishing methods
Western Australia
Commercial
Hand Line, Hand Reel or Powered Reels
Gillnet
Purse Seine
Net
Charter
Unspecified
Rod and reel
Indigenous
Unspecified
Recreational
Unspecified
Management methods
Method Western Australia
Charter
Bag limits
Licence
Limited entry
Spatial closures
Commercial
Fishing gear and method restrictions
Limited entry
Spatial zoning
Total allowable catch
Vessel restrictions
Recreational
Bag limits
Licence (boat-based sector)
Possession limit
Spatial closures
Catch
Western Australia
Commercial 9.94t
Charter Unknown
Indigenous Unknown
Recreational Unknown, Insufficient data

Commonwealth – Commercial (Catch). Commonwealth data are presented for 2021–22 financial year

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). A ‘recreational-fishing-from-boat license’ is required when using a powered boat to fish, or transport catch or fishing gear to, or from, a land-based fishing location. Shore based catches are largely unknown.

Queensland – Indigenous (Management Methods). For more information see Traditional fishing | Department of Agriculture and Fisheries, Queensland (daf.qld.gov.au)

Queensland – Commercial (Management Methods). Harvest strategies are available at: https://www.daf.qld.gov.au/business-priorities/fisheries/sustainable/harvest-strategy

Queensland – Commercial (Catch). Commercial and charter data have been sourced from the commercial fisheries logbook program. Further information is available through the Fisheries Summary Report

Queensland – Recreational Fishing (Catch). Data are based at the whole of Queensland level and derived from state-wide recreational fishing surveys. Where possible, estimates have been converted to weights (tonnes) using best known conversion multipliers. Conversion factors may display regional or temporal variability. In the absence of an adequate conversion factor, data are presented as the number of fish.

New South Wales – Recreational (Catch). Data have been sourced from surveys: Henry and Lyle [2003]; West et al. [2015]; Murphy et al. [2020, 2022].

New South Wales – https://www.dpi.nsw.gov.au/fishing/aboriginal-fishing.

New South Wales – Indigenous (Management Methods). (https://www.dpi.nsw.gov.au/fishing/aboriginal-fishing

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Catch Chart

Commercial catch of Yellowtail Scad - note confidential catch not shown

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References

  1. Blazeski, S, Norriss, J, Smith, KA and Hourston, M 2021, Ecological Risk Assessment for the State-Wide Small Pelagic Scalefish Resource. Fisheries Research Report No. 320 Department of Primary Industries and Regional Development, Western Australia. 115 pp.
  2. Broadhurst, MK 2023, Stock assessment summary report 2019 – Yellowtail Scad (Trachurus novaezelandiae). NSW Department of Primary Industries. Fisheries NSW, Port Stephens Fisheries Institute. 7 pp
  3. Broadhurst, MK and Millar, RB 2022, Validating a narrow codend cover and improving selectivity in south-eastern Australian fish trawls targeting eastern school whiting, Sillago flindersi. Fish. Res. 251, 106302.
  4. Broadhurst, MK, Kienzle, M and Stewart, J 2018, Natural mortality of Trachurus novaezelandiae and their size selection by purse seines off south-eastern Australia. Fisheries Management and Ecology 25: 332–338
  5. Dawson, G, Suthers, IM, Brodie, S and Smith, JA 2020, The bioenergenetics of a coastal forage fish: Importance of empirical values for ecosystem models. Deep-Sea Res II. 175 (104700).
  6. Henry, GW and Lyle, JM 2003, The national recreational and indigenous fishing survey. Australian Government Department of Agriculture, Fisheries and Forestry, Canberra, Australia. ISSN 1440–3544.
  7. Horn, PL 1993, Growth, age structure, and productivity of jack mackerels (Trachurus spp.) in New Zealand waters. New Zealand Journal of Marine and Freshwater Research, 27: 145–155.
  8. Horn, PL and Maolagáin, CÓ 2020, The growth and age structure of Chilean jack mackerel (Trachurus murphyi) following its influx to New Zealand waters. J. Fish. Biol. 98: 1144–1154.
  9. Kennelly, SJ, Liggins, GW and Broadhurst, MK 1998, Retained and discarded by-catch from ocean prawn trawling in New South Wales, Australia. Fisheries Research, 36: 217–236.
  10. Lowry, M, Steffe, A and Williams, D 2006, Relationships between bait collection, bait types and catch: A comparison of the NSW trailer-boat and gamefish-tournament fisheries. Fisheries Research, 78: 266–275.
  11. Murphy, JJ, Ochwada-Doyle, FA, West, LD, Stark, KE and Hughes, JM 2020, The NSW Recreational Fisheries Monitoring Program - survey of recreational fishing, 2017/18. NSW DPI - Fisheries Final Report Series No. 158.
  12. Murphy, JJ, Ochwada-Doyle, FA, West, LD, Stark, KE, Hughes, JM and Taylor, MD 2023, Survey of recreational fishing in NSW, 2019/20 - Key results. NSW DPI - Fisheries Final Report Series No. 161.
  13. Neira, FJ 2009, Provisional spawning biomass estimates of yellowtail scad (Trachurus novaezelandiae) off south-eastern Australia. New South Wales Department of Primary Industries Report, 32 pp
  14. Neira, FJ, Perry, RA, Burridge, CP, Lyle, JM and Keane, JP 2015, Molecular discrimination of shelf-spawned eggs of two co-occurring Trachurus spp. (Carangidae) in southeastern Australia: a key step to future egg-based biomass estimates. ICES Journal of Marine Science, 72: 614–624.
  15. Ryan, KL, Lai, EKM and Smallwood, CB 2022, Boat-based recreational fishing in Western Australia 2020/21. Fisheries Research Report No. 327. Department of Primary Industries and Regional Development, Western Australia. 221pp.
  16. Stewart, J and Ferrell, DJ 2001, Age, growth and commercial landings of yellowtail scad (Trachurus novaezelandiae) and blue mackerel (Scomber australasicus) off the coast of New South Wales, Australia. New Zealand Journal of Marine and Freshwater Research, 35: 541–551.
  17. Stewart, J, Ferrell, D and Andrew, NL 1999, Validation of the formation and appearance of annual marks in the otoliths of yellowtail (Trachurus novaezelandiae) and blue mackerel (Scomber australasicus) in New South Wales. Marine and Freshwater Research, 50: 389–395.
  18. Teixeira, D, Janes, R, and Webley, J 2021, 2019–20 Statewide Recreational Fishing Survey Key Results. Project Report. State of Queensland, Brisbane.
  19. West, LD, Stark, KE, Murphy, JJ, Lyle, JM and Doyle, FA 2015, Survey of recreational fishing in New South Wales and the ACT, 2013/14. Fisheries Final Report Series No. 149. ISSN 2204-8669.

Downloadable reports

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