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Mirror Dory (2023)

Zenopsis nebulosa

  • Krystle Keller (Australian Bureau of Agricultural and Resource Economics and Sciences)
  • Geoffrey Liggins (New South Wales Department of Primary Industries)

Date Published: June 2023

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Summary

Mirror Dory is a sustainable species found throughout the southern Pacific Ocean at depths of 30–800 m.

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Stock Status Overview

Stock status determination
Jurisdiction Stock Stock status Indicators
Commonwealth, New South Wales South Eastern Australia Sustainable

CPUE, Catch

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Stock Structure

Mirror Dory is found throughout the southern Pacific Ocean at depths of 30–800 m. A single stock of Mirror Dory in the Southern and Eastern Scalefish and Shark Fishery (SESSF) area and adjacent waters off the north coast of New South Wales is assumed for management purposes [AFMA 2022]. Separate analyses for eastern and western units are undertaken to support management. Here, assessment of stock status is presented at the biological stock status level—South Eastern Australia.

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Stock Status

South Eastern Australia

This cross jurisdictional stock has components in the Commonwealth and New South Wales. The stock status classification reported here is based on analyses conducted for the Southern and Eastern Scalefish and Shark Fishery (SESSF), which includes state catches.

Mirror Dory is predominantly a by-product species in the SESSF and is mainly caught east of Bass Strait. The catch has ranged between 100 tonnes (t) and 700 t per year since 1986.

The annual commercial catch from New South Wales waters has been between 0.002 t and 6.0 t during the last decade, representing up to 1.9% of fishing mortality on the stock. Annual catches during the last 5 years have all been less than 0.1 t. Similarly, fishing effort and the number of fishers taking Mirror Dory in New South Wales waters have been low. Consequently, assessment status for the component of the Mirror Dory stock under New South Wales jurisdiction is based on the Commonwealth assessment.

Mirror Dory in Commonwealth fisheries is managed as a Tier 4 stock under the SESSF Harvest Strategy Framework [AFMA 2021a]. The stock is divided into an eastern unit (New South Wales and eastern Tasmania) and a western unit (western Tasmania and part of Victoria and South Australia) for analyses [Sporcic 2021]. Although the 2020 Tier 4 analyses [Sporcic 2020] informed the management of the stock for the 2021–22 fishing season, new Tier 4 analyses were undertaken in 2021 [Sporcic 2021]. 

The Tier 4 analyses in 2020 [Sporcic 2020] and 2021 [Sporcic 2021] only included discards for the eastern unit, because discards are low for the western unit. Standardised catch-per-unit-effort (CPUE) for the east generally declined from 2009 to 2015 and fluctuated between the target reference point (TRP) and the limit reference point (LRP) between 2016 and 2019. Since 2012, standardised CPUE for the west followed a cyclical pattern, fluctuating between the TRP and the LRP [Sporcic 2020, 2021]. Although the standardised CPUE estimate in the most recent year (2020) for the eastern unit was below the LRP, the 4-year average standardised CPUE was above the LRP for both the east and west units. The above evidence indicates that the biomass of the stock is unlikely to be depleted and that recruitment is unlikely to be impaired.

The Tier 4 harvest control rule, based on the 2020 analyses, resulted in a recommended biological catch (RBC) of 146 t for the east and 62 t in the west respectively [Sporcic 2020]. The total RBC for the eastern and western units combined was 207 t. The South East Resource Assessment Group (SERAG) recommended an RBC for the 2021–22 fishing season of 207 t [AFMA 2021b]. 

The Tier 4 harvest control rule, based on the 2021 Tier 4 analyses resulted in an RBC of 113 t for the east and 56 t for the west [Sporcic 2021]. SERAG recommended a combined RBC of 169 t for the 2022–23 fishing season [AFMA 2021b].

Commonwealth-landed catch (east and west) in 2021–22 was 107 t, based on catch disposal records. Data on discards and state catches are not yet available for 2021–22. Discards in the east have been estimated to be 14.9 t in the east and 3.3 t in the west based on the weighted average of the previous four calendar years (2017–2020) [Althaus et al. 2021]. There were no reported state catches in the east or west.

For the 2021–22 fishing season, total catch and discards for both stocks combined is estimated to be 125.2 t, which is below the combined RBC of 207 t for 2021–22 and the updated combined RBC of 169 t calculated for 2022–23 [AFMA 2021b, Emery et al. 2022]. 

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 South Eastern Australia biological stock is classified as a sustainable stock.

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Biology

Mirror Dory biology [May and Maxwell 1986; Parin et al. 1988; Tilzey 1995; Knuckey and Curtain 2001; Bray 2008]

Biology
Species Longevity / Maximum Size Maturity (50 per cent)
Mirror Dory

12 years, 700 mm TL

4–7 years

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Distributions

Distribution of reported commercial catch of Mirror Dory

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Tables

Fishing methods
Commonwealth New South Wales
Commercial
Demersal Longline
Demersal Gillnet
Danish Seine
Otter Trawl
Midwater Trawl
Charter
Hook and Line
Rod and reel
Indigenous
Hook and Line
Rod and reel
Recreational
Hook and Line
Rod and reel
Management methods
Method Commonwealth New South Wales
Charter
Bag and possession limits
Gear restrictions
Licence
Marine park closures
Commercial
Catch limits
Gear restrictions
Limited entry
Marine park closures
Mesh size regulations
Quota
Spatial closures
Total allowable catch
Vessel restrictions
Indigenous
Customary fishing management arrangements
Recreational
Bag and possession limits
Gear restrictions
Licence
Marine park closures
Catch
Commonwealth New South Wales
Commercial 79.19t 2.50kg
Indigenous Negligible (2019–20)
Recreational Negligible (2019–20)

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 Commonwealth 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 and Recreational Catch estimates of “Negligible” are based on zero catches of Mirror Dory recorded during the 201920 survey of the catch of 13 year recreational licence holders in NSW [Murphy et al. 2022].

New South Wales – Indigenous Cultural Fishing Management Arrangements. See https://www.dpi.nsw.gov.au/fishing/aboriginal-fishing.

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Catch Chart

Commercial catch of Mirror Dory - note confidential catch not shown

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References

  1. AFMA 2021a, Harvest strategy framework for the Southern and Eastern Scalefish and Shark Fishery 2009 (amended 2021), Australian Fisheries Management Authority, Canberra.
  2. AFMA 2021b, South East Scalefish and Shark Fishery South East Resource Assessment Group (SERAG) meeting 2, minutes, 19–20 October 2021, Australian Fisheries Management Authority, Canberra.
  3. AFMA 2022, Southern and Eastern Scalefish and Shark Fishery species summaries 2022, Australian Fisheries Management Authority, Canberra.
  4. 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.
  5. Bray, DJ 2008, Family Zeidae, in Gomon, MF, Bray, DJ and Kuiter, RH (eds), Fishes of Australia's Southern Coast, Sydney: Reed New Holland, pp 438–440.
  6. 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.
  7. Knuckey, IA and Curtain, JM 2001, Estimation of the current age structure of mirror dory and ocean perch, Final report to the Australian Fisheries Management Authority, ARF Project R99/0377, Queenscliff, Marine and Freshwater Resources Institute, Victoria
  8. May, JL and Maxwell, JGH 1986, A field guide to trawl fish from the temperate waters of Australia, CSIRO Division of Fisheries Research (2nd Edition, revised).
  9. Murphy, JJ, Ochwada-Doyle, FA, West, LD, Stark, KE, Hughes, JM and Taylor, MD 2022, Survey of recreational fishing in NSW, 2019/20 – Key Results, NSW DPI – Fisheries Final Report Series No. 161, ISSN 2204-8669.
  10. Parin, NV, Pavlov, YP and Andrianov, DP 1988, Ecology of the Mirror Dory Zenopsis nebulosis, of the Submarine Nasca Ridge, Journal of Ichthyology, 28: 707–16.
  11. Sporcic, M 2020, Draft Tier 4 assessments for selected SESSF species (data to 2019), CSIRO Oceans and Atmosphere, Hobart.
  12. Sporcic, M 2021, Draft Tier 4 Assessments for selected SESSF species (data to 2020), CSIRO Oceans and Atmosphere, Hobart.
  13. Tilzey, RDJ 1995, The South East Fishery: a scientific review with particular reference to quota management. Bureau of Resource Science Bulletin.

Downloadable reports

Click the links below to view reports from other years for this fish.