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Silverlip Pearl Oyster

Pinctada maxima

  • Anthony Hart (Department of Fisheries, Western Australia)
  • Anthony Roelofs (Department of Agriculture and Fisheries, Queensland)
  • Thor Saunders (Department of Primary Industry and Resources, Northern Territory)

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Stock Status Overview

Stock status determination
Jurisdiction Stock Fisheries Stock status Indicators
Queensland Queensland ECPF Sustainable Catch, effort
ECPF
East Coast Pearl Fishery (QLD)
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Stock Structure

Pinctada maxima or the Silverlip Pearl Oyster is the largest species in the pearl oyster family1, and produces the largest pearls. It is distributed within the central Indo-Pacific region, bounded by the Bay of Bengal to the west, Solomon Islands to the east, Taiwan to the north, and Northern Australia to the south2, at depths from the shallow sub-tidal to more than 50 m. Within Australia, the population genetic distribution has been investigated in Western Australia and Northern Territory3. The biological stock structure is uncertain; however, Western Australian stocks are generally considered to be one stock (with the possible exception of a localised population in Exmouth Gulf), separate from stocks in the Northern Territory. The biological stock structure for Queensland is unknown.

 

Here, assessment of stock status is presented at the jurisdictional level—Western Australia, Northern Territory and Queensland.

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Stock Status

Queensland

The East Coast Pearl Fishery (Queensland) is a small-scale, wild-harvest fishery that licences operators to collect live adult pearl oyster shell as broodstock for the pearl aquaculture industry. The general demand for wild-harvested pearl oysters is very low as the aquaculture industry produces the majority of its broodstock needs from its own hatcheries. Catches have been low in recent years, rarely exceeding 500 shells per year and 50 days of effort. There has been a long history of low catches and effort and there were no Silverlip Pearl Oyster collected in 2015. The above evidence indicates 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, Silverlip Pearl Oyster in Queensland is classified as a sustainable stock.

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Biology

Biology
Species Longevity / Maximum Size Maturity (50 per cent)
Silverlip Pearl Oyster 30 years; 250 mm DVM  Males: 2–3 years; 110 mm DVM Females: 7–8 years: 175 mm DVM

Silverlip Pearl Oyster biology6

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Distributions

Distribution of reported commercial catch of Silverlip Pearl Oyster

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Tables

Fishing methods
Queensland
Commercial
Diving
Indigenous
Diving
Recreational
Diving
Management methods
Method Queensland
Commercial
Gear restrictions
Limited entry
Size limit
Spatial closures
Catch
Queensland
Indigenous Unknown
Recreational Unknown

Indigenousa

 

a. In Queensland, under the Fisheries Act 1994 (Qld), Indigenous fishers are able to use prescribed traditional and non-commercial fishing apparatus in waters open to fishing. Size and possession limits, and seasonal closures do not apply to Indigenous fishers. Further exemptions to fishery regulations may be applied for through permits.

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Effects of fishing on the marine environment

  • Pearl oyster fishing removes only a small proportion of the biomass of pearl oysters on the fishing grounds and is considered to have negligible impact on the food chain in the fishing area. Pearl divers have minimal contact with the habitat during fishing operations and the main habitat contact is by pearl oysters held in mesh panels on holding sites following capture. However, these sites cover a very small proportion of the habitat and the activity concerned is unlikely to cause any lasting effect.
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Environmental effects on Silverlip Pearl Oyster

  • Environment plays an important role in population variability in the Silverlip Pearl Oyster. In Western Australia, the effect of sea surface temperature, wind direction and rainfall have shown to be influential in determining the settlement density of young-of-the-year (0+ years) pearl oysters4. Other studies on pearl oysters, for example the Black-lipped Pearl Oyster, also highlight the close relationship between exceptional year classes and environment7.
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References

  1. 1 Shirai, S1994, Pearls and pearl oysters of the world. Marine Planning Co. Japan. 95 pp. (in Japanese and English).
  2. 2 Southgate PC, Strack E, Hart AM, Wada KT, Monteforte M, Carino M, Langy S, Lo C, Acosta-Salmon H and Wang A 2008, Chapter 9: Exploitation and Culture of Major Commercial Species. pp. 303–56. In: The Pearl Oyster, Eds Southgate PC and Lucas J, Elsevier London.
  3. 3 Benzie, JAH and Smith-Keune, C 2006, Microsatellite variation in Australian and Indonesian pearl oyster Pinctada maxima populations. Marine Ecology Progress Series. 314: 197–211.
  4. 4 Hart AM, Thomson AW and Murphy D 2011, Environmental influences on stock abundance and fishing power in the silver-lipped pearl oyster fishery. ICES Journal of Marine Science. 68(3): 444–53.
  5. 5 Knuckey, IA 1995, The Northern Territory Pearl Oyster Fishery. FRDC final report 1991/14. 47 pp.
  6. 6 Hart, AM and Joll, L 2006, Growth, mortality, recruitment, and sex ratio in wild stocks of the silver-lipped pearl oyster Pinctada maxima (Jameson) (Mollusca: Pteriidae) in Western Australia. Journal of Shellfish Research. 25 (1): 201–210.
  7. 7 Oengpepa, C, Hawes, I, Lane, I, Friedman, K and Bell, J 2006, Long-term variability in spat collections of the blacklip pearl oyster (Pinctada margaritifera) in Solomon Islands. Journal of Shellfish Research, 25: 955–58.

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