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Common Jack Mackerel (2020)

Trachurus declivis

  • Tim Ward (South Australian Research and Development Institute)
  • Jeremy Lyle ( Institute for Marine and Antarctic Studies)
  • Rocio Noriega (Australian Bureau of Agricultural and Resource Economics and Sciences)
  • John Stewart (Department of Primary Industries, New South Wales)

Date Published: June 2021

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Summary

Common Jack Mackerel is one of Australia’s small pelagic fish species and stocks are sustainable. The eastern stock is caught in NSW, TAS and Commonwealth waters. The western stock is caught in TAS and Commonwealth waters.

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Stock Status Overview

Stock status determination
Jurisdiction Stock Stock status Indicators
Tasmania Eastern Sustainable Catch, effort, spawning biomass, exploitation rate
Tasmania Western Sustainable Catch, effort, spawning biomass, exploitation rate
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Stock Structure

A study conducted to provide a basis for establishing management zones in the Commonwealth Small Pelagic Fishery (SPF) concluded that there was evidence for at least two biological stocks of Common Jack Mackerel in Australian waters: one off eastern Australia and the other extending from western Tasmania to southern Western Australia [Bulman et al. 2008]. Evidence supporting these conclusions included morphological, meristic and genetic differences between fish from these two areas  [Lindholm and Maxwell 1988, Richardson 1982] and a lack of genetic difference between fish from eastern Tasmania and New South Wales [Smolenski et al. 1994]. There is some evidence that more than one stock may occur off eastern Australia, however further studies are required to address this issue [ Richardson 1982, Smolenski et al. 1994]. Recent studies also demonstrate that spawning occurs off both the east and west coasts of Tasmania and in Bass Strait during summer, suggesting that Bass Strait may not effectively separate the eastern and western stocks [Ward et al 2016, 2018]. Currently in the SPF, Common Jack Mackerel and other target species are managed as separate Eastern and Western biological stocks [AFMA 2009].

Here, assessment of stock status is presented at the biological stock level—Western and Eastern.

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Stock Status

Eastern

The most recent assessment of the Eastern stock of Common Jack Mackerel was completed in 2020 using fishery data for 2019–20 [Ward and Grammer 2018, 2021] and an application of the Daily Egg Production Method (DEPM) undertaken in 2019 [ Ward et al. 2020]. Population modelling has also been undertaken to assess the status of the stock [Punt et al. 2016]. The primary stock status indicators are spawning biomass and exploitation rate.

The spawning biomass of Eastern Common Jack Mackerel during 2019 was estimated to be 156 292 t (95 per cent confidence interval 49 120–263 496 t) using the DEPM [Ward et al. 2020]. This estimate is considered robust because it was based on reliable estimates of critical DEPM parameters such as egg production, spawning area and spawning fraction. It is also similar to the estimate of spawning biomass off eastern Australia obtained in 2014 of 157 805 [Ward et al. 2016].

Total annual catches of Common Jack Mackerel off eastern Australia did not exceeded 3 000 t between 2003–04 and 2014–15 [Ward and Grammer 2018].  The total annual catch reached 6 849 t in 2015–16 when a mid-water trawler with onboard freezer facilities operated in the SPF, but decreased to 2 849 t in 2016–17 when the vessel left. In 2017–18 and 2018–19, the catch was between 4 000 and 4 500 tones and reached 7 852 t in 2019–20 (Ward and Grammer 2021). Recent catches have been less than 6 per cent of the estimated spawning biomass [Ward et al. 2016], and less than half the sustainable exploitation rate of 12 per cent proposed as a target for this species [Smith et al. 2015].

The above evidence indicates that the biomass of this stock is unlikely to be depleted and that recruitment is unlikely to be impaired. Furthermore, the above evidence indicates that the current level of fishing mortality is unlikely to cause the stock to become recruitment impaired.

On the basis of the evidence provided above, the Eastern biological stock of Common Jack Mackerel is classified as a sustainable stock.

Western

The most recent assessment of the Western stock of Common Jack Mackerel was completed in 2020 using fishery data for 2019–20 [Ward and Grammer 2021] and an application of the Daily Egg Production Method (DEPM) undertaken in 2016–17 [Ward et al. 2018]. The primary biological performance indicators are spawning biomass and exploitation rate.

The spawning biomass of Common Jack Mackerel West during 2016–17 was estimated to be at least 30 000 tonnes (t) using the DEPM [Ward et al. 2018]. Historically, total annual catches of Common Jack Mackerel West have been very low [< 100 t per annum]. Catches of between 600 t and 700 t per annum were taken in from this stock in 2015–16 and 2016–17 (Ward and Grammer 2018. No catch was taken in the West sub-area of the SPF in 2017–18 or 2018–19 , with only small catches taken by other Commonwealth fisheries (AFMA 2019).

Low catches of Common Jack Mackerel from the Western stock reflect low fishing effort, rather than low abundance. Recent catches have been less than 3 per cent of the estimated minimum spawning biomass, and less than a quarter of the sustainable exploitation rate of 12 per cent proposed as a target for this species [Smith et al. 2015].

The above evidence indicates that the biomass of this stock is unlikely to be depleted and that recruitment is unlikely to be impaired. Furthermore, the above evidence indicates that the current level of fishing mortality is unlikely to cause the stock to become recruitment impaired.

On the basis of the evidence provided above, the Western biological stock of Common Jack Mackerel is classified as a sustainable stock.

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Biology

Common Jack Mackerel biology [Lyle et al. 2000, Marshall et al. 1993, Webb 1976; Ward and Grammer 2018]

Biology
Species Longevity / Maximum Size Maturity (50 per cent)
Common Jack Mackerel 17 years, 470 mm FL 5–6 years, 315 mm FL 
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Distributions

Distribution of reported commercial catch of Common Jack Mackerel

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Tables

Fishing methods
Tasmania
Commercial
Unspecified
Recreational
Gillnet
Handline
Management methods
Method Tasmania
Commercial
Bag limits
Catch limits
Limited entry
Mesh size regulations
Spatial closures
Vessel restrictions
Indigenous
Bag limits
Recreational
Bag limits
Spatial closures
Catch
Tasmania
Commercial 168.00kg
Indigenous Unknown
Recreational 5.2 t (2012–13)

Commonwealth – Commercial (management methods) Historically, no restrictions on vessel hold capacity have been in place in the Small Pelagic Fishery (Commonwealth). However, in 2012, an interim declaration was made to prevent factory trawlers greater than 130 m in length with on-board fish processing facilities, and storage capacity for fish or fish products in excess of 2 000 t, from entering this fishery for a two year period.

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 data is presented for 2017.

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.

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

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Catch Chart

Commercial catch of Common Jack Mackerel - note confidential catch not shown.

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References

  1. AFMA 2009, Small Pelagic Fishery Management Plan 2009. Australian Fisheries Management Authority, Canberra, Federal Register of Legislative Instruments F2010L00081. 51 pp.
  2. Bulman, C Condie, S Findlay, J Ward B and Young J 2008, Management zones from small pelagic fish species stock structure in southern Australian waters, Final report to the Fisheries Research and Development Corporation and Australian Fisheries Management Authority (FRDC Project No 2006/076), CSIRO, Hobart Australia
  3. Lindholm, R and Maxwell, JGH 1988, Stock separation of jack mackerel Trachurus declivis (Jenyns, 1841), and yellowtail T. novaezealandiae (Richardson, 1843) in southern Australian waters using principal component analysis, Australian CSIRO Marine Laboratories report 189, CSIRO, Hobart.
  4. Lyle, JM, Krusic-Golub, K and Morison, AK 2000, Age and growth of Jack Mackerel and the age structure of the Jack Mackerel purse seine catch, final report to the Fisheries Research and Development Corporation, project 1995/034, FRDC, Canberra.
  5. Marshall, J, Pullen, G and Jordan, A 1993, Reproductive biology and sexual maturity of female Jack Mackerel, Trachurus declivis (Jenyns), in eastern Tasmanian waters, Australian Journal of Marine and Freshwater Research, 44: 799–809.
  6. Punt, AE, Little, LR and Hillary, R 2016, Assessment for Eastern Jack Mackerel. Report to the Australian Fisheries Management Authority.
  7. Richardson, BJ 1982, The geographical distribution of electrophoretically detected protein variation in Australian commercial fishes. I. The Jack Mackerel (Trachurus declivis Jenyns), Australian Journal of Marine and Freshwater Research, 33: 917–926.
  8. Smith, ADM, Ward, T, Hurtado, F, Klaer, N, Fulton, E and Punt, AE 2015. Review and update of harvest strategy settings for the Commonwealth Small Pelagic Fishery: Single species and ecosystem considerations. Final Report of FRDC Project No. 2013/028. CSIRO Oceans and Atmosphere Flagship, Hobart. 74 pp.
  9. Smolenski, AJ, Ovenden, JR and White, RWG 1994, Preliminary investigation of mitochondrial DNA variation in Jack Mackerel (Trachurus declivis, Carangidae) from south-eastern Australian waters, Australian Journal of Marine and Freshwater Research, 45: 495–505.
  10. Ward, T. M. and Grammer, G. L. (2018). Commonwealth Small Pelagic Fishery: Fishery Assessment Report 2017. Report to the Australian Fisheries Management Authority. South Australian Research and Development Institute (Aquatic Sciences), Adelaide. SARDI Publication No. F2010/000270-9. SARDI Research Report Series No. 982. 114pp
  11. Ward, T. M. and Grammer, G. L. (2021). Commonwealth Small Pelagic Fishery: Status Summary Report 2020. Report to the Australian Fisheries Management Authority. South Australian Research and Development Institute (Aquatic Sciences), Adelaide. SARDI Publication No. F2010/000270-10. SARDI Research Report Series No. 1021. 7 pp.
  12. Ward, T. M., Grammer, G. L. Ivey, A. R. and Keane, J. (2020). Spawning biomass of Jack Mackerel (Trachurus declivis) in the East sub-area of the Small Pelagic Fishery during summer 2019. Report to the Australian Fisheries Management Authority. South Australian Research and Development Institute (Aquatic Sciences), Adelaide. SARDI Publication No. F2020/000206-01. 42pp.
  13. Ward, TM, Burnell, O, Ivey, A, Sexton, SC Carroll, J, Keane, JB and Lyle, J 2016, Spawning biomass of jack mackerel (Trachurus declivis) off eastern Australia: critical knowledge for managing a controversial fishery. Fisheries Research, 179: 10-22
  14. Ward, TM, Grammer, GL, Ivey, AR, Smart, JJ and Keane, P 2018, Spawning biomass of Jack Mackerel (Trachurus declivis) and Sardine (Sardinops sagax) between western Kangaroo Island, South Australia and south-western Tasmania. Report to the Australian Fisheries Management Authority. South Australian Research and Development Institute (Aquatic Sciences), Adelaide. SARDI Publication No. F2018/000174-1. SARDI Research Report Series No. 983. 51pp.
  15. Webb, BF 1976, Aspects of the biology of Jack Mackerel Trachurus declivis (Jenyns) from south east Australian waters, Tasmanian Fisheries Research, 10: 1–17.

Downloadable reports

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