Giant Crab (2018)
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Giant Crab occurs from WA to TAS but it is considered a single biological stock. Nevertheless, stocks are classified separately for the four states. Stock is sustainable in WA, SA and VIC, and depleted in TAS.
Stock Status Overview
|South Australia||South Australia||GCF||Sustainable||CPUE, catch, effort, mean weight, pre-recruit abundance, sex ratio, spawning female abundance|
- Giant Crab Fishery (SA)
Giant Crab is considered to be a single biological stock from Western Australia to Tasmania because the species occurs is continuously distributed across this range. Planktonic larval duration is around 50 days, with larval release occurring along the edge of the continental shelf. The shelf is a high current area, facilitating dispersal, and oceanographic modeling has indicated that Giant Crab dispersal occurs over large spatial scales [Gardner 1998, Gardner and Quintana 1998, Williams et. al. 2009].
Previous Status of Australian Fish Stocks reports on Giant Crab provided an overall assessment for this assumed biological stock. However, there have been significant changes in the relative performance of the various fisheries operating across this stock since 2014. New information indicates that Giant Crab are now considered to be depleted in Tasmania but sustainable in Western Australia. It is difficult to reconcile these differences in regional depletion levels under an assumption of a single stock. But management arrangements also vary across jurisdictions and the fishing fleets in each jurisdiction consist of vessels with different characteristics, resulting in different patterns of exploitation.
Assessment of stock status is presented here at the jurisdictional level—Western Australia and South Australia; and the management unit level—Giant Crab Fishery (Victoria) and Giant Crab Fishery (Tasmania).
The South Australian Giant Crab Fishery (GCF) comprises three commercial fishing sectors: (1) the Miscellaneous Fishery sector; (2) the South Australian Rock Lobster Fishery (SARLF) quota sector (RL-quota); and (3) the SARLF byproduct sector (RL by-product). Fishing mortality in South Australia is managed through TACCs and a minimum legal size (MLS) (150 mm carapace length) to protect females up to spawning size. A recently adopted management policy for the fishery guides the classification of stock status relative to limit, trigger and target reference points defined for a CPUE-based performance indicator relating to relative stock biomass measured from 2000/01 to 2009/10 - a relatively stable period of data collection from Giant Crab catch logbooks. The five year average commercial catch rate (CPUE) of legal-size Giant Crab calculated from data collected from targeted Giant Crab fishing in the Miscellaneous Fishery and RL-quota sectors [PIRSA 2018] is the primary indicator for biomass and fishing mortality.
The most recent assessment was based on data to the end of the 2016–17 season (1 October 2016–31 May 2017) [McLeay 2018]. In 2016–17, 7 157 potlifts were used to catch a total of 16.3 t of Giant Crab, comprising 76.0 per cent of the 22.1 t TACC in that season.
Commercial CPUE increased from 2.42 kg/potlift at the start of the series in 2004–05 to reach a peak of 3.05 kg/potlift in 2008–09. CPUE then decreased to 2.62 kg/potlift in 2012–13, before decreasing further to 2.25 kg/potlift in 2013–14. Average CPUE over the period 2004–12 was 2.68 kg/potlift, above the target of 2.60 kg/potlift. Since then, commercial CPUE has been relatively stable above the trigger level, at approximately 83 per cent of the 2004–12 average and 85 per cent of the target [McLeay 2018]. Although these recent CPUE levels are lower than historical values, CPUE increased slightly between 2015–16 and 2016–17. The above evidence indicates that the biomass of this stock is unlikely to be depleted and that recruitment is unlikely to be impaired. Furthermore, the 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 presented above, Giant Crab in South Australia is classified as a sustainable stock.
Giant Crab biology [Gardner 1998, McGarvey et. al. 1999, Williams et. al. 2009,]
|Species||Longevity / Maximum Size||Maturity (50 per cent)|
|Giant Crab||≥ 30 years, > 200 mm CL , ~10 kg||125–140 mm CL, depending on region|
|Giant Crab Trap|
|Giant Crab Trap|
|Giant Crab Trap|
|Commercial||16.34t in GCF|
- Giant Crab Fishery (SA)
South Australian data are from quota holders in the 2016–17 fishing season (October 2016–May 2017), Victorian data are for the 2016–17 fishing season (November 2016–September 2017), Tasmanian data are for the 2017-18 fishing season (March 2017 – February 2018) and South Coast Deep Sea Crustacean Fishery (Western Australia) data are for the 2016–17 financial year. Victoria – Indigenous (management methods) In Victoria, regulations for managing recreational fishing may not apply to fishing activities by Indigenous people. Victorian traditional owners may have rights under the Commonwealth's Native Title Act 1993 to hunt, fish, gather and conduct other cultural activities for their personal, domestic or non-commercial communal needs without the need to obtain a licence. Traditional Owners that have agreements under the Traditional Owner Settlement Act 2010 (Vic) may also be authorised to fish without the requirement to hold a recreational fishing licence. Outside of these arrangements, Indigenous Victorians can apply for permits under the Fisheries Act 1995 (Vic) that authorise fishing for specific Indigenous cultural ceremonies or events (for example, different catch and size limits or equipment). There were no Indigenous permits granted in 2017 and hence no Indigenous catch recorded.
- Emery, T, Hartmann K and Gardner C, 2015, Giant Crab stock assessment report 2013/14, IMAS, Hobart.
- Fisheries Victoria 2010, Giant Crab Management Plan, Second Edition, ISBN 978-1-74264-478-3.
- Fogarty, MJ and Gendron, L 2004, Biological reference points for American lobster (Homarus americanus) populations: limits to exploitation and the precautionary approach, Canadian Journal of Fisheries and Aquatic Sciences, 61(8): 1392–1403.
- Gardner, C 1998, First record of larvae of the Giant Crab Pseudocarcinus gigas in the plankton, Papers and Proceedings of the Royal Society of Tasmania, 132: 47–48.
- Gardner, C and Quintana R 1998, Larval development of the Australian Giant Crab Pseudocarcinus gigas (Lamarck, 1818) (Decapoda: Oziidae) reared in the laboratory, Journal of Plankton Research, 20(6): 1169–1188.
- Gardner, C, Haddon, M, Hobday,D and McGarvey R 2007, Development of the tools for long term management of the Giant Crab resource: data collection methodology, stock assessment and harvest strategy evaluation, final report to the Fisheries Research and Development Corporation, Canberra.
- McGarvey, R, Matthews, JM and Levings, AH 1999, Yield-, value-, and egg-per-recruit of Giant Crab, Pseudocarcinus gigas, South Australian Research and Development Institute, Adelaide.
- McLeay, L 2018, Stock status report for the South Australian South Australian Giant Crab (Pseudocarcinus gigas) Fishery 2016/17. Fishery Status Report to PIRSA Fisheries and Aquaculture. South Australian Research and Development Institute (Aquatic Sciences), Adelaide. SARDI Publication No. F2011/000332-7. SARDI Research Report Series No. 976.
- PIRSA 2018, Management Policy for Commercial Fishing of Giant Crabs in South Australia. Primary Industries and Regions South Australia. Adelaide, Australia.
- Victorian Giant Crab Fishery Stock Assessment Report: 2015/16 Fishing Season.
- Williams, A, Gardner, C, Althaus, F, Barker, B and Mills D 2009, Understanding shelf-break habitat for sustainable management of fisheries with spatial overlap, final report to the Fisheries Research and Development Corporation, project 2004/066, CSIRO Marine and Atmospheric Research, Hobart.