Commercial Scallop ​​Pecten fumatus

Jayson Semmensa, Harry Gorfineb, Nic Martonc, David Jarvisd and Justin Bella


Commercial Scallop

Table 1: Stock status determination for Commercial Scallop

Jurisdiction

Commonwealth

Tasmania

Victoria

Stock

Commonwealth(BSCZSF)

Tasmania
(TSF)

Victoria
(VSF)

Stock status

 

 

 

Undefined

Undefined

Undefined

Indicators

Proportion of spawning stock protected by spatial closure, minimum size limits, survey results

Proportion of spawning stock protected by spatial closure, minimum size limits, survey results

Proportion of spawning stock protected by spatial closure, minimum size limits, survey results

BSCZSF = Bass Strait Central Zone Scallop Fishery (Commonwealth); TSF = Tasmanian Scallop Fishery; VSF = Victorian Scallop Fishery


Stock Structure

Multiple Commercial Scallop beds are fished commercially in Commonwealth, Tasmanian and Victorian waters. Commercial Scallops in Port Phillip Bay (Victoria) and the D’Entrecasteaux Channel (Tasmania) are genetically distinct from each other, as well as from scallops in most other locations in south-eastern Australia1,2. Although Commercial Scallops in Bass Strait are considered a single stock, they do show some genetic variation, most likely due to nonrandom dispersal and subsequent settlement of larvae1. Given this complex genetic mosaic, Commercial Scallops have been assessed at the jurisdictional level.


Stock Status

Management of scallop fisheries is complex, with all three jurisdictions using slightly different management strategies. Scallop stocks have shown repeated ‘boom and bust’ phases in the past, with the busts often resulting in extended fishery closures. Sustainability objectives are strongly reliant on the minimum size limit in each jurisdiction—an area is only open to fishing if less than 20 per cent of the scallops are under the minimum size. Estimating the biomass of Commercial Scallops is difficult because of highly variable recruitment3. In Victoria, the fishery may also be closed if average meat weight falls below 10 grams.

Commonwealth

Commercial Scallops in the Bass Strait Central Zone Scallop Fishery were considered recruitment overfished until 2007. Following 3 years of closure due to low scallop abundance and concerns about overfishing, the Bass Strait Central Zone Scallop Fishery was reopened in 2009 under a new harvest strategy4. Commercial Scallops experienced a reported die-off in 2010. In 2012, the harvest strategy was revised to provide more flexibility5.

Elements of the Commonwealth harvest strategy include:

  • surveys to estimate biomass and determine areas of high density
  • a set of decision rules that are used to open an area to fishing, including a minimum size limit of 90 mm shell length and a maximum discard rate (20 per cent) of animals below this size
  • identification of at least two viable fishing areas, with a minimum of 40 per cent of the combined pool of viable areas closed to fishing
  • a requirement that closed viable fishing areas contain a minimum of 500 tonnes (t) of estimated biomass in total.

Abundance surveys in 2013 estimated around 4000 t of Commercial Scallop across two beds, but only around 650 t were densely aggregated. These beds also contained a high proportion (31–71 per cent) of undersized scallops. The fishery was opened with an exemption from the 90 mm minimum size limit, and a temporary 85 mm limit applied instead. The latter size limit is still within the size range for scallops that are 3 years or older6. Only 189 t of the 1500 t total allowable catch (13 per cent) was harvested by the 13 active vessels in 2013.

Although management measures for the Bass Strait Central Zone Scallop Fishery are designed to prevent the stock from becoming recruitment overfished, it is not clear whether the stock biomass has recovered from its previous recruitment overfished state. Also unknown is the impact of the reported die-off in 2010 on total biomass and recruitment. As such, insufficient information is available to confidently classify the status of this stock7.

On the basis of the evidence provided above, Commercial Scallop in the Commonwealth is classified as an undefined stock.

Tasmania

The harvest of Commercial Scallops in Tasmanian waters is regulated through a minimum size limit of 90 mm shell length, which is a proxy for animals aged 3 years or older that have spawned at least twice6. The minimum size limit can be changed for specific areas of the fishery, if appropriate.

The Tasmanian fishery is managed similarly to the Bass Strait Central Zone Scallop Fishery. The main difference is that there is no requirement to close a proportion of the beds found during abundance surveys. This is because refuge for scallops is provided by the prohibition of fishing in waters less than 20 m deep, and the large number of dredge-prohibited areas around the state that protect scallop habitat.

The Tasmanian fishery was closed to fishing in 2009 and 2010 because of low scallop abundance and a high proportion of undersized animals. In 2013, industry statewide surveys generally found low levels of scallop abundance but did identify two beds containing commercial quantities that met the harvest strategy guidelines: one on the state’s north-west coast and the other on the east coast. These areas were subsequently opened for fishing, with a lower size limit of 85 mm applied to the north-west bed. This was considered appropriate given historically slow growth rates in this region and the fact that the revised size limit is still within the size range of scallops aged 3 years or more6.

Part of the east coast bed was voluntarily closed by industry in July 2013 when a large proportion of juveniles were discovered in the northern section. By the end of 2013, 1260 t of the 1489 t total allowable catch across both beds (85 per cent) had been taken by 13 vessels (half the number of vessels operating a decade earlier). Although harvesting is managed to prevent the stock becoming recruitment overfished, the historical status of the Tasmanian stock is unclear. In particular, it is not known whether the stock is recruitment overfished, and there is insufficient information available to confidently classify the status of this stock.

On the basis of the evidence provided above, Commercial Scallop in Tasmania is classified as an undefined stock.

Victoria

Surveys undertaken in 20098 and 20129 of the historically fished scallop beds found low scallop densities and negligible recruitment. Consequently, the total allowable catches for the 2010–11, 2011–12 and 2012–13 fishing seasons were set at zero. Landings and participation were also very low for the 2013–14 season, when 1.5 t per licence was allocated to facilitate exploratory fishing to collect information, in lieu of a more expensive biomass survey. Insufficient information is available to confidently classify the status of this stock.

On the basis of the evidence provided above, Commercial Scallop in Victoria is classified as an undefined stock.


Table 2: Commercial Scallop biology1,2,6 

Longevity and maximum size

7 years; 120 mm SL

Maturity

2 years; 70-80 mm SL, depending on region

SL = shell length


Figure 1: Distribution of reported commercial catch of Commercial Scallop in Australian waters, 2013 (calendar year)

Figure 1: Distribution of reported commercial catch of Commercial Scallop in Australian waters, 2013 (calendar year)




Table 3: Main features and statistics for Commercial Scallop fisheries in Australia, 2013 (calendar year)


Jurisdiction

Commonwealth

Tasmania

Victoria

Fishing methods

Commercial

Dredge

Recreationala

Diving

Indigenousb

Unknown

Unknown

Management methods

Commercial

Limited entry

Size limits

Gear restrictions

Total allowable catch

Spatial closures

Temporal closures

Abundance estimation

Recreationala

Bag limits

Size limits

Spatial closures

Temporal closures

Indigenousb,c

Bag limits

Size limits

Spatial closures

Seasonal closures

Active vessels

13 in BSCZSF

13 in TSF

2 in VSF

Catch

Commercial

189 t in BSCZSF

1260 t in TSF

Confidential in VSFd

Recreationala

Unknown

Unknown

Indigenousb,c

Unknown

Markets

Domestic

Export


BSCZSF = Bass Straight Central Zone Scallop Fishery (Commonwealth); TSF = Tasmanian Scallop Fishery; VSF = Victorian Scallop Fishery

a 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.

b The Australian Government does not manage noncommercial Indigenous fishing in Commonwealth waters, with the exception of the Torres Strait. In general, noncommercial Indigenous fishing in Commonwealth waters is managed by the state or territory immediately adjacent to those waters.

c 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 Victorian Traditional Owner Settlement Act 2010) are exempt (subject to conditions) from the requirement to hold a recreational fishing licence, and can apply for permits under the Fisheries Act 1995 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 2012–13, there were no applications for customary fishing permits to access Commercial Scallop.

d To protect commercial confidentiality of data, the catch in the VSF cannot be reported because there are fewer than five licence holders.


Image of commercial catch

Figure 2: Commercial catch of Commercial Scallop in Australian waters, 2000 to 2013 (calendar years)
Note: To protect commercial confidentiality of data, the catch in Victoria from 2010 to 2013 cannot be reported because there were fewer than five licence holders.




Effects of fishing on the marine environment
  • Scallops are targeted where they are abundant, and the effect on other species within the broader ecosystem tends to be minimal1,10. An ecological risk assessment of the Bass Strait Central Zone Scallop Fishery found that none of the habitats assessed were at high risk of irreversible disturbance11. Commercial Scallops and associated benthic communities generally recover very quickly from dredging operations12,13. Commercial Scallops have been fished within the same regions repeatedly since the 1960s14 and so the effect of dredging on the current community structure is expected to be less significant than when the fishery began. The long-term dredge fishery may have already driven a shift in benthic community structure in favour of species that are less susceptible to dredging or can recover quickly15–17.

Environmental effects on Commercial Scallop
  • Changes in Commercial Scallop community structure can be driven by environmental factors as well as fishing12. Recruitment of Commercial Scallops is intermittent and poorly understood3. Scallops often exhibit highly variable natural mortality, which is attributable to density-dependent food shortages, seabed bottom type, disease, environmental conditions, predation and unknown causes18. Stock relationships are heavily influenced by ocean currents1. Climate change–induced shifts in ocean currents and/or upwelling events are expected to affect recruitment.


a Institute for Marine and Antarctic Studies, University of Tasmania
b Department of Environment and Primary Industries, Victoria
c Australian Bureau of Agricultural and Resource Economics and Sciences
d Department of Primary Industries, Parks, Water and Environment, Tasmania