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Commercial Scallop

Pecten fumatus

  • Jayson Semmens (Institute for Marine and Antarctic Studies, University of Tasmania)
  • Corey Green (Department of Economic Development, Jobs, Transport and Resources, Victoria)
  • Nic Marton (Australian Bureau of Agricultural and Resource Economics and Sciences)

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

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Stock Status Overview

Stock status determination
Jurisdiction Stock Fisheries Stock status Indicators
Victoria Ocean Scallop Fishery OSF Undefined Catch
Victoria Port Phillip Bay Dive Scallop Fishery PPBDSF Sustainable Biomass surveys, size composition, catch
OSF
Ocean Scallop Fishery (VIC)
PPBDSF
Port Phillip Bay Dive Scallop Fishery (VIC)
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Stock Structure

There are several Commercial Scallop beds fished commercially in Commonwealth, Victorian and Tasmanian waters. These beds often contain different age classes of scallop and most have been fished at some stage in the past. Commercial Scallops in Port Phillip Bay (Victoria) are genetically distinct from those in the D’Entrecasteaux Channel (Tasmania), and also differ from conspecifics in most other locations in south eastern Australia1,2. The genetic structure of Commercial Scallops in Bass Strait is complex and unclear2,3.

Here, assessment of stock status is reported at the management unit level—Bass Strait Central Zone Scallop Fishery (Commonwealth), Ocean Scallop Fishery (Victoria), Port Phillip Bay Dive Scallop Fishery (Victoria) and Tasmanian Scallop Fishery.

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Stock Status

Many scallop fisheries have experienced repeated ‘boom and bust’ phases, with declines often resulting in prolonged fishery closures. Management arrangements for the three jurisdictions that harvest Commercial Scallop in Australian waters all include a minimum size limit (to allow adult scallops to spawn several times before harvest) and some means of capping fishing effort (through spatial and/or temporal closures) and overall catch (through a total allowable catch [TAC]). Estimating Commercial Scallop biomass by means of surveys is complicated by unpredictable and highly variable recruitment, which can result in scallops declining in one area and reappearing in another4.

Ocean Scallop Fishery

Approximately 7.6 t of Commercial Scallops were landed by the Ocean Scallop Fishery (Victoria) in the 2015–16 fishing season. This harvest is minor compared to that of the Tasmanian and Commonwealth scallop fisheries. Surveys of historically fished scallop beds in 200912 and 201213 found low scallop densities and negligible recruitment. Consequently, the TAC for the 2010–11, 2011–12 and 2012–13 fishing seasons was set at zero. A TAC of 135 t was set for the following three seasons to allow limited exploratory fishing and determine if there had been any stock recovery. However, low participation and catches during these seasons means that there is insufficient information available to confidently classify the status of this stock.

On the basis of the evidence provided above, the Ocean Scallop Fishery (Victoria) management unit is classified as an undefined stock.

Port Phillip Bay Dive Scallop Fishery

Dredging for Commercial Scallops in Port Phillip Bay ceased in 1997. A single licence was issued for the take of Commercial Scallop in a new Port Phillip Bay Dive Scallop Fishery in 2013. A survey conducted in 2014 estimated that the total harvestable biomass of Commercial Scallops within fishable areas of Port Phillip Bay was 3629 t14. A total allowable commercial catch (TACC), equating to four per cent of the estimated harvestable biomass (146 t) was then set for the 2015–16 fishing season (1 April–30 March). A conservative TACC, combined with the protection afforded by a minimum legal size (90 mm SL) ensures that fishing mortality within this management unit is low15.

Recreational fishing for Commercial Scallops is popular off the coast of the Bellarine Peninsula between Portarlington and St. Leonards, and to the north of the Mornington Peninsular from Point Nepean to Dromana16. While there are no current estimates of the recreational take of Commercial Scallop in Victorian waters, a survey in 2000–01 estimated that it was in the order of 5.7 t17. The above evidence indicates that the biomass of this stock is unlikely to be recruitment overfished, and that the current level of fishing pressure is unlikely to cause the stock to become recruitment overfished.

On the basis of the evidence provided above, the Port Phillip Bay Dive Scallop Fishery (Victoria) management unit is classified as a sustainable stock.

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Biology

Biology
Species Longevity / Maximum Size Maturity (50 per cent)
Commercial Scallop 7+ years; > 120 mm SH  SHell length  2 years; 70–80 mm SL, depending on region

Commercial Scallop biology1–3,18

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Distributions

Distribution of reported commercial catch of Commercial Scallop

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Tables

Fishing methods
Victoria
Commercial
Diving
Dredges
Indigenous
Diving
Recreational
Diving
Management methods
Method Victoria
Commercial
Gear restrictions
Limited entry
Size limit
Spatial closures
Total allowable catch
Indigenous
Bag limits
Spatial closures
Recreational
Bag limits
Spatial closures
Active vessels
Victoria
1 in OSF, 4 in PPBDSF
OSF
Ocean Scallop Fishery (VIC)
PPBDSF
Port Phillip Bay Dive Scallop Fishery (VIC)
Catch
Victoria
Indigenous Nil
Recreational Unknown

BSCZSF = Bass Strait Central Zone Scallop Fishery (Commonwealth), OSF = Ocean Scallop Fishery (Victoria), PPBDSF = Port Phillip Bay Dive Scallop Fishery (Victoria), TSF = Tasmanian Scallop Fishery

Commercial (Fishing methods)a Indigenous (management methods)b,c Commercial (catch)d

a In Victoria, the reporting period is fishing season, which runs from 1 April–30 March.

b In Victoria, regulations for managing recreational fishing are also applied to fishing activities by Indigenous people. Recognised Traditional Owners (groups that hold native title or have agreements under the Traditional Owner Settlement Act 2010 [Vic]) are exempt (subject to conditions) from the requirement to hold a recreational fishing licence, and can apply for permits under the Fisheries Act 1995 (Vic) that authorise customary fishing (for example, different catch and size limits or equipment). The Indigenous category in Table 3 refers to customary fishing undertaken by recognised Traditional Owners. In 2015, there were no applications for customary fishing permits to access Commercial Scallop.

c Subject to the defence that applies under Section 211 of the Native Title Act 1993 (Cth), and the exemption from a requirement to hold a Victorian recreational fishing licence, the non-commercial take by indigenous fishers is covered by the same arrangements as that for recreational fishing.

d To protect commercial confidentiality of data, the catch in the Ocean Scallop Fishery (Victoria) and Port Phillip Bay Dive Scallop Fishery (Victoria) cannot be reported because there are fewer than five licence holders.

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Catch Chart

Commercial catch of Commercial Scallop

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Effects of fishing on the marine environment

  • Commercial Scallops have been fished within the same regions repeatedly since the 1960s19, and the current impacts of dredging activities are considered less significant than those when the fishery began. This is because the long-term dredge fishery may have already resulted in benthic communities shifting in favour of those species that are less susceptible to dredging, or those most able to quickly recover20-22. Scallops are targeted where they are abundant and the effect on other species within the broader ecosystem tends to be minimal2, 23. An ecological risk assessment of the Bass Strait Central Zone Scallop Fishery found that none of the habitats assessed were at high risk24. Commercial Scallops, and associated benthic communities, are impacted by dredging over relatively brief periods of time and generally recover quickly25,26.
  • Selective harvesting by the Port Phillip Scallop Dive Fishery has minimal impact on the surrounding environment and other fisheries15. It is difficult to identify any scenario where this dive fishery would have a detrimental impact on the local snapper fishery27.
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Environmental effects on Commercial Scallop

  • Changes in Commercial Scallop community structure can be driven more by environmental effects than fishing25. Recruitment of Commercial Scallops is sporadic, intermittent and poorly understood4. Natural mortality of scallops is highly variable and depends on factors including (but not limited to) density-dependent food shortages, seabed bottom type, disease, environmental conditions and predation28. Stock relationships are heavily influenced by ocean currents2. Climate change-induced changes in ocean currents and/or upwelling events are expected to affect recruitment. Recent research has shown that seismic surveying may impact the health and increase the mortality rate of scallops29.
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References

  1. 1 Woodburn, L 1990, Genetic variation in southern Australian Pecten, in Proceedings of the Australasian Scallop Workshop. Tasmanian Government: Hobart.
  2. 2 Semmens, JM, et al 2015, Establishing fine-scale industry based spatial management and harvest strategies for the Commercial Scallop fishery in South East Australia, final report to the Fisheries Research and Development Corporation, project 2008/022. FRDC: Canberra.
  3. 3 Ovenden, JR, et al. 2016, Stirred but not shaken: population and recruitment genetics of the scallop (Pecten fumatus) in Bass Strait, Australia. ICES Journal of Marine Science: Journal du Conseil.
  4. 4 Peterson, CH, Summerson, HC and Fegley, SR 1988, Ecological consequences of mechanical harvesting of clams. Fishery Bulletin, 85(2): p. 281-298.
  5. 5 Australian Fisheries Management Authority 2007, Harvest strategy for the Bass Strait Central Zone Scallop Fishery. Australian Fisheries Management Authority: Canberra.
  6. 6 Australian Fisheries Management Authority 2012, Harvest strategy for the Bass Strait Central Zone Scallop Fishery. Australian Fisheries Management Authority: Canberra.
  7. 7 Australian Fisheries Management Authority 2014, Harvest Strategy for the Bass Strait Central Zone Scallop Fishery. Australian Fisheries Management Authority: Canberra.
  8. 8 Australian Fisheries Management Authority 2015, Harvest Strategy for the Bass Strait Central Zone Scallop Fishery. Australian Fisheries Management Authority: Canberra.
  9. 9 Australian Fisheries Management Authority 2015, Bass Strait Central Zone Scallop Fishery Resource Assessment Group (ScallopRAG) Meeting 23, Meeting Minutes; Date: 2 March 2015. AFMA: Canberra.
  10. 10 Knuckey, I, Koopman, M and Davis, M 2015, Bass Strait and Central Zone Scallop Fishery — 2015 Survey, project 2015/001291. Australian Fisheries Management Authority: Canberra.
  11. 11 Knuckey, I, Koopman, M and Davis, M 2016, Bass Strait and Central Zone Scallop Fishery – 2016 Survey, project 2016/0804. Australian Fisheries Management Authority: Canberra.
  12. 12 Harrington, J, Leporati, S and Semmens, JM 2010, 2009 Victorian Scallop Fishery Survey, final report to Fisheries Victoria. Tasmanian Aquaculture and Fisheries Institute, University of Tasmania: Hobart.
  13. 13 Semmens, JM and Jones, N 2012, Victorian scallop fishery survey final report. Institute for Marine and Antarctic Studies, University of Tasmania: Hobart.
  14. 14 DEPI 2014, Commercial Scallop Dive Fishery (Port Phillip) – Survey Results for 2014. Fisheries Victoria: Melbourne
  15. 15 DEDJTR 2016, Draft Port Phillip Scallop Dive Fishery Management Plan. Fisheries Victoria: Melbourne.
  16. 16 DEPI 2013, Commercial Scallop Dive Fishery (Port Phillip Bay) Baseline Management Arrangements. Fisheries Victoria: Melbourne.
  17. 17 Henry, GW and Lyle, JM 2003, The National Recreational and Indigenous Fishing Survey - project 99/158 FRDC: Canberra.
  18. 18 Young, P and Martin, R 1989, The scallop fisheries of Australia and their management. Reviews in Aquatic Sciences, 1(4): p. 615-638.
  19. 19 Gwyther, D, et al. 1991, Fisheries and Aquaculture: Australia, in Scallops: Biology, Ecology and Aquaculture, Editors: Shumway, SL and Parsons, GJ. Elsevier: New York.
  20. 20 Jennings, S and Kaiser, MJ 1998, The Effects of Fishing on Marine Ecosystems, in Advances in Marine Biology, Editors: Blaxter, JHS, Southward, AJS and Tyler PA. Academic Press. p. 201-352.
  21. 21 Kaiser, MJ, et al. 2002, Modification of marine habitats by trawling activities: prognosis and solutions. Fish and Fisheries, 3(2): p. 114-136.
  22. 22 Young, P, et al. 1988, Variability in spatfall and recruitment of commercial scallops (Pecten fumatus) in Bass Strait, in Proceedings of the Australian Scallop Workshop. Tasmanian Government: Hobart.
  23. 23 Haddon, M, Harrington, J and Semmens, JM 2006, Juvenile scallop discard rates and bed dynamics: testing the management rules for scallops in Bass Strait, final report to the Fisheries Research and Development Corporation, project 2003/017. FRDC: Canberra.
  24. 24 Hobday, A, et al. 2007, Ecological risk assessment for the effects of fishing: Bass Strait Central Zone Scallop Sub-Fishery, report to the Australian Fisheries Management Authority. Australian Fisheries Management Authority: Canberra.
  25. 25 Currie, DR and Parry, GD 1999, Impacts and efficiency of scallop dredging on different soft substrates. Canadian Journal of Fisheries and Aquatic Sciences, 56(4): p. 539-550.
  26. 26 Harrington, J, Haddon, M and Semmens, JM 2008, Facilitating industry self-management for spatially managed stocks: A scallop case study, final report to the Fisheries Research and Development Corporation, project 2005/027. FRDC: Canberra.
  27. 27 Kennelly, S 2013, Review of potential interactions between snapper and the proposed commercial scallop dive fishery in Port Phillip Bay. Fisheries Victoria: Melbourne.
  28. 28 Gwyther, D and McShane, PE 1988, Growth rate and natural mortality of the scallop Pecten alba tate in Port Phillip Bay, Australia, and evidence for changes in growth rate after a 20-year period. Fisheries Research, 6(4): p. 347-361.
  29. 29 Ryan D. Day, RD, McCauley, RD, Fitzgibbon, QP, Hartmann, K  and Semmens, JM 2016, Assessing the impact of marine seismic surveys on southeast australian scallop and lobster fisheries, final report to the Fisheries Research and Development Corporation, project 2012/008. FRDC: Canberra

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