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Ocean Jacket (2023)

Nelusetta ayraud

  • Amy Smoothey (New South Wales Department of Primary Industries)
  • Stephen Bradshaw (Institute for Marine and Antarctic Studies, University of Tasmania)
  • Daniel Wright (Australian Bureau of Agricultural and Resource Economics and Sciences)
  • Michael Drew (South Australian Research and Development Institute)
  • Justin Bell (Victorian Fisheries Authority)

Date Published: June 2023

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Summary

Ocean Jackets are found along the southern half of Australia, with sustainable stocks in NSW, SA and Commonwealth waters. Stocks in VIC are undefined, with limited information available. Stocks are negligible in TAS.

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Stock Status Overview

Stock status determination
Jurisdiction Stock Stock status Indicators
New South Wales New South Wales Sustainable Catch, effort, CPUE
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Stock Structure

Ocean Jackets are distributed along the southern half of Australia from Cape Moreton in Queensland around to North West Cape in Western Australia, including northern Tasmania [Kailola et al 1993]. Throughout their distribution, Ocean Jackets are found in many habitats. As juveniles they are found in estuaries and sheltered bays amongst seagrass beds of Zostera sp. and Posidonia sp. [Grove-Jones and Burnell 1991, Jones and West 2005]. Sub-adults and adults are found in different habitats such as rocky reefs, sandy–mud benthos, or sponge–coralline algae gardens in waters from 2–250 m [Grove-Jones and Burnell 1991, Hutchins 1999], where they are known to aggregate seasonally in large schools.

Little is known about the biological structure of the Ocean Jacket stock. Here, assessment of stock status is presented at the management unit level—Commonwealth Trawl Sector, Great Australian Bight Trawl Sector (Commonwealth); and at the jurisdictional level—New South Wales, Victoria, Tasmania and South Australia.

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Stock Status

New South Wales

In New South Wales, Ocean Jackets have a long history of commercial exploitation from the use of oceanic demersal fish traps and demersal otter trawls. Records of reported landings indicate that substantial peaks of between 600 and 900 t per year occurred during the 1920s and the 1950s. These peaks were followed by large declines, suggesting that the species is vulnerable to over-exploitation. Between 2000–01 and 2006–07, annual commercial landings from oceanic demersal fish traps and demersal otter trawls increased from 134 to 430 t. Since then, the variability in catch has been less as it peaked in 2010 at 510 t and then declined to 163 t in 2021–22, with a five-year average of 228 t. Since 2009–10, CPUE has been relatively stable [Smoothey 2023].

Ocean Jacket is important to the New South Wales recreational and charter boat fishers. Since 2015–16, an average of 4,499 Ocean Jackets have been caught annually by charter boat fishers (range: 1,256–7,527 fish) [Hughes et al. 2023]. The most recent estimate during 2019–20 of the recreational harvest of Leather Jackets (all species combined) in New South Wales, based on a survey of Recreational Fishing Licence (RFL) Households, was approximately 38,111 with 52% released alive caught, with the majority landed using line fishing with bait [Murphy et al. 2022].  RFL households comprised at least one member who possessed a long-term (1 and 3 years duration) fishing licence and included other fishers resident within their households. The recent recreational fishing estimate from 2019–20 is down from previous estimates of 53,062 and 71,000 fish recorded during 2017–18 and 2013–14, respectively [West et al. 2015; Murphy et al. 2020].

The recent decreases in commercial and recreational catches, coupled with the boom-bust history of the fishery, may suggest that the biomass is declining. However, the above evidence indicates that the biomass of this stock is unlikely to be depleted and that recruitment is unlikely to be impaired.

Based on the evidence presented above, Ocean Jacket in New South Wales is classified as a sustainable stock.

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Biology

Ocean Jacket biology [Kailola et al. 1993; Miller et al. 2010; Miller and Stewart 2012]

Biology
Species Longevity / Maximum Size Maturity (50 per cent)
Ocean Jacket

at least 9 years, 790 mm FL New South Wales 6 years, 656 mm TL

New South Wales 2.5 years

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Distributions

Distribution of reported commercial catch of Ocean Jacket
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Tables

Fishing methods
New South Wales
Commercial
Otter Trawl
Various
Fish Trap
Indigenous
Spearfishing
Hook and Line
Recreational
Spearfishing
Hook and Line
Charter
Hook and Line
Management methods
Method New South Wales
Commercial
Fishing gear and method restrictions
Limited entry
Spatial closures
Indigenous
Customary fishing management arrangements
Recreational
Bag limits
Gear restrictions
Licence
Spatial zoning
Catch
New South Wales
Commercial 161.90t
Charter 1,256 fish during 2022–23
Indigenous Unknown
Recreational 53,062 fish during 2017–18, 71,000 fish during 2013–14

Commonwealth – Commercial (Management Methods/Catch). Data provided for the Commonwealth align with the Commonwealth Southern and Eastern Scalefish and Shark Fishery for the 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 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

New South Wales – Recreational (Catch). Murphy et al. [2022].

Victoria – Indigenous (Management Methods). A person who identifies as Aboriginal or Torres Strait Islander is exempt from the need to obtain a Victorian recreational fishing licence, provided they comply with all other rules that apply to recreational fishers, including rules on equipment, catch limits, size limits and restricted areas. Traditional (non-commercial) fishing activities that are carried out by members of a traditional owner group entity under an agreement pursuant to Victoria’s Traditional Owner Settlement Act 2010 are also exempt from the need to hold a recreational fishing licence, subject to any conditions outlined in the agreement. Native title holders are also exempt from the need to obtain a recreational fishinglicence under the provisions of the Commonwealth’s Native Title Act 1993.

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Catch Chart

Commercial catch of Ocean Jacket - note confidential catch not shown
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References

  1. AFMA 2021, Harvest strategy framework for the Southern and Eastern Scalefish and Shark Fishery 2009 (amended 2021), Australian Fisheries Management Authority, Canberra.
  2. Althaus, F, Thomson, R and Sutton, C 2021, Southern and Eastern Scalefish and Shark Fishery catches and discards for TAC purposes using data until 2020, CSIRO Oceans and Atmosphere, Hobart.
  3. Emery, T, Wright, D, Davis, K, Keller, K, Woodhams, J and Curtotti, R 2022, Commonwealth Trawl and Scalefish Hook sectors, in Patterson, H, Bromhead, D, Galeano, D, Larcombe, J, Timmiss, T, Woodhams, J and Curtotti, R (eds), Fishery status reports 2022, Australian Bureau of Agricultural and Resource Economics and Sciences, Canberra.
  4. Grove-Jones, RP and Burnell, AF 1991, Fisheries biology of the Ocean Jacket (Monacanthidae: Nelusetta ayraudi) in the eastern waters of the Great Australian Bight. South Australian Department of Fisheries. FIRDC Project DFS01Z, Final report 107 pp.
  5. Hughes, JM, Murphy, JJ, Ochwada-Doyle, FA and Taylor, MD 2023, NSW Charter Fishery Monitoring 2019/20, NSW DPI - Fisheries Final Report Series No. 162.
  6. Hutchins, BJ 1999. Leatherjackets. In Andrew, NL Under southern Seas. The ecology of Australia’s rocky reefs. University of New South Wales Press Ltd, Sydney. pp 195–202.
  7. Jones, MV and West, RJ 2005, Spatial and temporal variability of seagrass fishes in intermittently closed and open coastal lakes in southeastern Australia, Estuarine, Coastal and Shelf Science, 64: 277–288.
  8. Kailola, PJ, Williams, MJ, Stewart, PC, Reichelt, RE, McNee, A and Grieve, C 1993, Australian Fisheries Resources. Australian Bureau of Resource Sciences and the Fisheries Research and Development Corporation. Canberra.
  9. Klaer, N 2001, Steam trawl catches from southeastern Australia from 1918 to 1957: trends in catch rates and species composition. Marine and Freshwater Research, 52: 399–410.
  10. Knuckey, I, Koopman, M and Hudson, R 2018, Resource survey of the Great Australian Bight Trawl Sector 2018, report to AFMA, Fishwell Consulting, Queenscliff, and Australian Fisheries Management Authority, Canberra.
  11. Knuckey, I, Koopman, M and Hudson, R 2021, Resource survey of the Great Australian Bight Trawl Sector 2021, report to AFMA, Fishwell Consulting, Queenscliff, and Australian Fisheries Management Authority, Canberra.
  12. Knuckey, IA and Brown, LP 2002, Assessment of bycatch in the Great Australian Bight Trawl Fishery, final report to FRDC, report 2000/169, FRDC, Canberra.
  13. Miller, ME and Stewart, J 2009, The commercial fishery for ocean leatherjackets (Nelusetta ayraudi, Monacanthidae) in New South Wales, Australia, Asian Fisheries Science, 22: 257–264.
  14. Miller, ME and Stewart, J 2012, Reproductive characteristics of the ocean leatherjacket, Nelusetta ayraudi. Reviews of Fish Biology and Fisheries.
  15. Miller, ME, Stewart, J and West, RJ 2010, Using otoliths to estimate age and growth of a large Australian endemic monocanthid, Nelusetta ayraudi (Quoy and Gaimard, 1824). Environmental Bioliology of Fishes, 88: 263–271
  16. Moore, A, Keller, K and Tuynman, H 2022, Great Australian Bight Trawl Sector, in Patterson, H, Bromhead, D, Galeano, D, Larcombe, J, Timmiss, T, Woodhams, J, and Curtotti, R (eds), Fishery status reports 2022, Australian Bureau of Agricultural and Resource Economics and Sciences, Canberra.
  17. Moore, B, Lyle, J and Hartmann, K 2018, Tasmanian Scalefish Fishery Assessment 2016/17. Institute for Marine and Antarctic Studies, University of Tasmania.
  18. 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.
  19. Murphy, JJ, Ochwada-Doyle, FA. West, LD, Stark, KE, Hughes, JM and Taylor, MD 2022, Survey of recreational fishing in NSW, 2019/20. NSW DPI - Fisheries Final Report Series No. 161.
  20. Sharples, R, Cresswell, K, Hartmann, K and Krueck, N 2023, Tasmanian Scalefish Fishery Assessment 2021/22. Institute for Marine and Antarctic Studies, University of Tasmania.
  21. Smart, JJ, McGarvey, R, Feenstra, J, Drew, MJ, Earl, J, Durante, L, Beckmann, CL, Matthews, D, Matthews, JM, Mark, K, Bussell, J, Davey, J, Tsolos, A and Noell, C 2023, Assessment of the South Australian Marine Scalefish Fishery in 2021–22, Report to PIRSA Fisheries and Aquaculture. South Australian Research and Development Institute (Aquatic Sciences), Adelaide. SARDI Publication No. F2017/000427-6. SARDI Research Report Series No. 1184. 259pp.
  22. Smoothey, AF 2023. NSW Stock Status Summary 2021/22 – Ocean Jacket – (Nelusetta ayraudi). NSW Department of Primary Industries. Fisheries NSW. 7 pp.
  23. Sporcic, M 2021, Statistical CPUE standardisations for selected SESSF species (data to 2020), CSIRO Oceans and Atmosphere, Hobart.
  24. Sporcic, M, Bulman, CM and Fuller, M 2021, Ecological risk assessment for the effects of fishing: report for the Southern and Eastern Scalefish and Shark Fishery (Commonwealth Trawl Sector) – otter trawl subfishery 2012–2016, CSIRO Oceans and Atmosphere, Hobart.
  25. West, LD, Stark, KE, Murphy, JJ, Lyle, JM and Ochwada-Doyle, FA 2015, Survey of Recreational Fishing in New South Wales and the ACT, 2013/14. NSW DPI – Fisheries Final Report Series No. 149.

Downloadable reports

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