Pipi ​Donax deltoides

Greg Fergusona, Daniel Johnsonb and James Andrewsc


Pipi

Table 1: Stock status determination for Pipi

Jurisdiction

South Australia

Victoria

New South Wales

Stock

South Australia

(LCF, MSF)

Victoria

(BF, OF)

New South Wales

(EGF)

Stock status

Sustainable

Undefined

Undefined

Indicators

Fishery-independent relative abundance, size frequencies

Catch

Catch, CPUE


BF = Bait Fishery (Victoria); CPUE = catch per unit effort; EGF = Estuary General Fishery (New South Wales); LCF = Lakes and Coorong Fishery (South Australia); MSF = Marine Scalefish Fishery (South Australia); OF = Ocean Fisheries (Victoria)


Stock Structure

Pipi is common on high-energy sandy beaches from southern Queensland to the mouth of the Murray River in South Australia1.

High genetic variation between populations on either side of Bass Strait suggests at least two biological stocks, with the East Australian Current and South Australian Current acting as key drivers of gene flow on the east and south coasts of Australia, respectively2. This was supported by a study of Pipi from Fraser Island, Queensland, to southern New South Wales, suggesting a single biological stock with genetic mixing driven by ocean currents associated with the East Australian Current; however, the timescale over which patterns in genetic variation may have occurred is unknown 1. For locations west of Bass Strait in South Australia and western Victoria, no evidence of genetic structuring of Pipi has been detected2. The degree of larval mixing is thought to be related to spawning and larval duration, although these are poorly understood 2–5. Although no genetic differences were detected among Pipi populations on beaches along the east coast of Australia, in any given year most recruits are likely to be self-seeded or come from nearby, adjacent beaches1. This is likely also the case for the fisheries located to the west of Bass Strait.

Despite the work outlined above, there is still too much uncertainty around the biological stock delineation of Pipi to determine stock status at the biological stock level. Hence, status is reported at the jurisdictional level for South Australia, Victoria and New South Wales.


Stock Status

South Australia

Indigenous Australians have occupied the Coorong region in south-eastern South Australia for at least 16 000 years and have harvested Pipi (also known as Goolwa Cockles in South Australia) for the past 10 000 years6. Middens in the vicinity of the Murray River mouth in South Australia are composed almost exclusively of the shells of adult Pipi7.

Fishers with quota for Pipi from the Lakes and Coorong Fishery, and the Marine Scalefish Fishery operate on the ocean beaches of Younghusband Peninsula, adjacent to the Coorong. Quota holders from the Marine Scalefish Fishery are subject to the same management arrangements (including the annual total allowable commercial catch) as the Lakes and Coorong Fishery. Combined fishery-dependent data from these two fisheries and annual fishery-independent estimates of relative biomass of Pipi on Younghusband Peninsula provide the key performance indicators for these fisheries. A minimum legal length of 35 mm is in place to allow spawning to occur at least once before recruitment to the fishery3. In 2006, available information suggested that the Pipi resource was depleted during the mid to late 2000s8. Since 2007, the fishery has been managed under an annual total allowable commercial catch. From 2009, increasing mean annual relative biomass and increasing complexity of size structures suggest recovery of the resource, probably as a result of conservative total allowable commercial catches that have been in place since 20093. The above evidence from the South Australian commercial fisheries indicates that the biomass of this stock is not recruitment overfished and that the current level of fishing pressure is unlikely to cause the stock to become recruitment overfished.

Estimates of recreational catch are available from telephone-based surveys in the 2000 and 2007 financial years. In 2000, the National Recreational and Indigenous Fishing Survey estimated recreational catch from South Australia to be 22.9 tonnes (t)9, representing 1.8 per cent of the total recreational and commercial catch of Pipi. In 2007, the South Australian Recreational Fishing Survey estimated that recreational catch was 5 t, representing 0.8 per cent of the total recreational and commercial catch10. The small catch of Pipi from the recreational fishery is unlikely to affect the overall status classification in South Australia.

On the basis of the evidence provided above, Pipi in South Australia is classified as a sustainable stock.

Victoria

The presence of middens is evidence that Pipi was harvested historically by Indigenous communities along the Victorian coastline6. The harvesting of fish for customary purposes is managed under permit in Victoria, and no permits have been issued for Pipi in recent years. Since 2013, a size limit of 35 mm has applied to the waters of south-western Victoria to the west of Lake Yambuk. In addition to the size limit, management of the recreational fishery includes daily catch limits.

Until recently, the commercial and recreational fisheries of Pipi were directed towards the supply of bait, and fewer than five commercial licences were generally active in any one year. Commercial catches from Discovery Bay have increased over the past few years, but little information is available on the commercial Pipi fishery in Victoria. In 2000, the National Recreational and Indigenous Fishing Survey estimated recreational harvest (numbers) from Victoria to be 638 401 Pipi11, but an estimate of harvest weight was not available. The impacts of recreational harvesting are thought to be localised around beach access points12. Insufficient information is available to confidently classify the status of this stock.

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

New South Wales

The harvest of Pipi in New South Wales is shared between commercial, recreational and Indigenous fishers. Commercial landings have declined from more than 500 t in 2004 to less than 65 t in recent years, despite a significant increase in price over this period. In 2011, a 6-month closure of the commercial fishery and output controls limiting catch to 40 kg per fisher per day were implemented in an attempt to stabilise the fishery. A minimum legal length of 45 mm is in place to allow spawning to occur before recruitment to the fishery13. Recreational catch was estimated at 7 t in 2000, based on the National Recreational and Indigenous Fishing Survey11. There are no recent estimates of recreational or Indigenous landings of Pipi. Insufficient information is available to classify the status of this stock.

On the basis of the evidence provided above, Pipi in New South Wales is classified as an undefined stock.


Table 2: Pipi biology3,4,13

Longevity and maximum size

South Australia: 3–5 years; 61 mm

New South Wales: 1–2 years; 75 mm

Maturity (50%)

South Australia: ~10 months; 28 mm

New South Wales: 1 year, 37 mm


Figure 1: Distribution of reported commercial catches of Pipi in Australian waters, 2012 (financial year)
Figure 1: Distribution of reported commercial catches of Pipi in Australian waters, 2012 (financial year)



Table 3: Main features and statistics for Pipi fisheries in Australia, 2012 (financial year)

Jurisdiction

South Australia

Victoria

New South Wales

Fishing methods

Commercial

Pipi rake

Hand gathering

Dip net

Recreational

Pipi rake/bait spade/fork

Hand gathering

Indigenousa,b

Pipi rake/bait spade/fork

Hand gathering

Management methods

Commercial

Catch limits

Size limits

Trip limits

Gear limits

Limited entry

Spatial closures

Temporal closures

Recreational

Size limits

Bag limits

Possession limits

Seasonal closures

Spatial closures

Gear restrictions

Indigenousb,c

Size limits

Bag limits

Section 37(1)(c1), Aboriginal

cultural fishing authority

Active vessels

Commerciald

20 licences in LCF

2 licences in MSF

2 fishers in BF

7 fishers in OF

30 licences in EGF

Catch

Commerciale

443 t in LCF and MSF

76 t in BF and OF

63 t in EGF

Recreational

22.9 t (in 2000)

5 t (in 2007)

Unknown

Unknown

Indigenous

Unknown

Unknown

Unknown

Markets

Domestic

Export


BF = Bait Fishery (Victoria); EGF = Estuary General Fishery (New South Wales); LCF = Lakes and Coorong Fishery (South Australia); MSF = Marine Scalefish Fishery (South Australia); OF = Ocean Fisheries (Victoria)

a 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 Pipi.

b The Aboriginal Fishing Interim Compliance Policy allows an Indigenous fisher in New South Wales to take in excess of a recreational bag limit in certain circumstances—for example, if they are doing so to provide fish to other community members who cannot harvest themselves.

c The Aboriginal cultural fishing authority is the authority that Indigenous persons can apply to to take catches outside the recreational limits under the New South Wales Fisheries Management Act 1994, section 37(1)(c1) (Aboriginal cultural fishing authority).

d Because Pipi is collected from beaches, ‘vessels’ are not used. Hence, numbers of licences and fishers are presented here instead of vessel numbers. Licences refer to the number of licence holders with an endorsement to take Pipi for sale.

e Catches from the MSF in South Australia, and the BF and OF in Victoria cannot be reported separately for confidentiality reasons as there are fewer than five licences.


Figure 2: Commercial catch of Pipi in Australian waters, 2002–03 to 2012–13 (financial years)
Figure 2: Commercial catch of Pipi in Australian waters, 2002–03 to 2012–13 (financial years)

Note: For Victoria, there were no catches from 2002–03 to 2007–08, and catches for 2009–10 are not reported for confidentiality reasons as there were fewer than five licences.




Effects of fishing on the marine environment
  • Since Pipi are collected by hand or using hand rakes, the fishery has limited physical impact on the environment. The impacts of mechanical grading of Pipi are unknown. Relatively high levels of recreational vehicle traffic (more than 20 vehicles per day) have been identified as having the potential to affect populations of Pipi on sandy beaches on the eastern Australian coast14. In South Australia, relatively low levels of vehicle traffic (fewer than 10 vehicles per day, including commercial vehicles) occur on Younghusband Peninsula where the commercial fishery is located.


Environmental effects on Pipi
  • Mortality events have been recorded for populations of Pipi. For example, in 1984, an estimated 2.5 million mostly adult Pipi were found dead on Goolwa beach, west of the mouth of the Murray River15. It was postulated that an extended period of low salinity following flooding from the Murray River may have resulted in mortality due to osmotic stress or starvation15,16.

  • During the peak spawning season (September–October), the prevailing currents in south-eastern South Australia flow in a north-westerly direction 4. Because larvae may remain in the plankton for at least 14 days after spawning5, changes to the nearshore currents during the spawning period may impact recruitment to the beach.



a South Australian Research and Development Institute
b Department of Primary Industries, New South Wales
c Department of Environment and Primary Industries, Victoria