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Sawsharks are a sustainable stock made up of three species. They occur around the southern and south-eastern coasts of Australia but are mainly caught in the Bass Strait.
Stock Status Overview
|New South Wales||Southern Australia||OTF||Sustainable||Catch, effort, standardised CPUE|
- Ocean Trawl Fishery (NSW)
This is a multispecies stock comprising three endemic species (Common Sawshark—Pristiophorus cirratus, Southern Sawshark—P. nudipinnis, and Eastern Sawshark—P. peroniensis). Common Sawshark (P. cirratus) range from Jurien Bay in Western Australia to southern New South Wales and Tasmania to depths of 310 m; Southern Sawshark (P. nudipinnis) ranges from the western Great Australian Bight to Bass Strait to depths of 70 m; and Eastern Sawshark (Pristiophorus sp., P. peroniensis) ranges from Bass Strait to central New South Wales at depths of 100–630 m [Last and Stevens 1994].
Biological stock structure is unknown for any of these species.
Sawsharks located to the south of the Victoria–New South Wales border are generally Common Sawshark and the Southern Sawshark, whereas the Eastern Sawshark is considered to be the predominant species found off NSW [Walker and Hudson 2005]. The majority of the historical catch has been taken in Bass Strait [Walker and Hudson 2005] and these species are primarily assessed and managed in the Commonwealth Southeast Scalefish and Shark fishery (SESSF).
Here, assessment of stock status is presented at the management unit level—Southern Australia.
Most of the reported commercial catch of Sawsharks is taken in the Commonwealth Trawl Sector (CTS) Great Australia Bight Trawl Sector (GABTS) and Gillnet Hook and Trap Sector (GHTS) of the Southeast Scalefish and Shark Fishery (SESSF). Total catch across all SESSF sectors in the 2017–18 fishing season was 205 tonnes (t). This is slightly below, but consistent with the average annual catch of the previous 10 years of around 210 t.
Minor catches of Sawsharks are taken in State waters by local commercial and recreational fishers. Sawshark catches in Western Australia are Negligible (< 10 t per year) [McAuley et al. 2015]. Sawshark catches in New South Wales were less than 13 t during 2017, which is a similar harvest for the past three years. The ten year average catch of around 19 t is driven by higher catches in the first half of the decade. The majority of New South Wales catch, around 10 t during 2017, are reported as Common Sawshark. No recreational or indigenous catches are reported for this species in New South Wales.
Within Tasmanian State waters, Sawsharks are taken in the multi-gear, multi-species Tasmanian Scalefish Fishery. Total commercial landings are low, with an average annual harvest of just 0.1 t over the last 10 years, with 0.02 t landed in 2017. Low numbers of Sawsharks are taken by recreational fishers using gillnets and setlines [Lyle and Tracey 2012a, Lyle and Tracey 2012b].
Sawsharks are rarely landed by South Australian State managed fisheries, which is partly a function of reductions in the use of demersal gillnets to target School and Gummy sharks, and the Offshore Constitutional Settlement that transferred management of fisheries operating in waters outside 3 nautical miles to the Commonwealth. No recreational or indigenous catches have been reported for Sawsharks in South Australia. Hence, stock status for this stock is informed by the standardised catch per unit effort (CPUE) analyses undertaken by the SESSF.
Historically, this stock has been assessed by the Commonwealth using commercial catch, effort and standardised CPUE data for the SESSF sectors. The most recent assessment of Sawshark was conducted in 2017 using data from the Commonwealth trawl sector up to 2016 [Haddon and Sporcic 2018]. The results indicate that current CPUE is above the target level and therefore well above the limit reference level. The tier 4 harvest control rule for the stock estimated an overall RBC (for all sectors) of 519 t. Known catches (commercial and recreational) in neighbouring states are deducted from the RBC in the calculation of the TAC for the Commonwealth fleet, resulting in a TAC for 2017–18 of 481 t. The landed catch of Sawshark in the 2017–18 season was 205 t, below the established TAC.
The above evidence indicates that the biomass of this stock is unlikely to be depleted, recruitment is unlikely to be impaired, and the current level of fishing mortality is unlikely to cause the stock to become recruitment impaired.
On the basis of the evidence above, the Southern Australia management unit is classified as a sustainable stock.
Sawshark biology [Last and Stevens 2009, Raoult et al. 2016]
|Species||Longevity / Maximum Size||Maturity (50 per cent)|
|SAWSHARKS||15 years, ~1 500 mm TL for Female common Sawshark, 1 180 mm for males 1 050 mm for female Southern Sawshark, 970 mm for males.||900 mm TL Common Sawshark mature around 800–900 mm TL Southern Sawshark mature around 700–900 mm TL|
|New South Wales|
|Method||New South Wales|
|Section 37 (1d)(3)(9), Aboriginal cultural fishing authority|
|New South Wales|
|37 in OTF|
- Ocean Trawl Fishery (NSW)
|New South Wales|
|Commercial||11.24t in OTF|
|Indigenous||Unknown but considered low|
|Recreational||Unknown but considered low|
- Ocean Trawl Fishery (NSW)
Commonwealth – Recreational 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.
Commonwealth – Indigenous The Australian Government does not manage non-commercial Indigenous fishing in Commonwealth waters, with the exception of the Torres Strait. In general, non-commercial Indigenous fishing in Commonwealth waters is managed by the state or territory immediately adjacent to those waters.Western Australia – Recreational (Management methods) A recreational fishing from boat licence is required for recreational fishing from a powered vessel in Western Australia.
New South Wales – no catch reported. Commercial fisheries with less than seven active fishers are not presented due to the Privacy Act.
New South Wales – Indigenous (Management Methods) (a) Aboriginal Cultural Fishing Interim Access Arrangement—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 for themselves; (b) The Aboriginal cultural fishing authority is the authority that Indigenous persons can apply to take catches outside the recreational limits under the Fisheries Management Act 1994 (NSW), Section 37 (1d)(3)(9), Aboriginal cultural fishing authority; and (c) In cases where the Native Title Act 1993 (Cth) applies fishing activity can be undertaken by the person holding native title in line with S.211 of that Act, which provides for fishing activities for the purpose of satisfying their personal, domestic or non-commercial communal needs. In managing the resource where native title has been formally recognised, the native title holders are engaged with to ensure their native title rights are respected and inform management of the State's fisheries resources.
Tasmania – Commercial (catch) Catches reported for the Tasmanian Scalefish Fishery are for the period 1 July to 30 June the following year. The most recent assessment available is for 2016/17.
Tasmania – Recreational (management methods) In Tasmania, a recreational licence is required for fishers using dropline or longline gear, along with nets, such as gillnet or beach seine.
Tasmania – Indigenous (management methods) In Tasmania, Indigenous persons engaged in aboriginal fishing activities in marine waters are exempt from holding recreational fishing licences, but must comply with all other fisheries rules as if they were licensed. If using pots, rings, set lines or gillnets, Indigenous fishers must obtain a unique identifying code (UIC). The policy document Recognition of Aboriginal Fishing Activities for issuing a Unique Identifying Code (UIC) to a person for Aboriginal Fishing activity explains the steps to take in making an application for a UIC.
- Haddon M and Sporcic M 2018, Draft Tier 4 assessments for selected SESSF shark species (data to 2016) CSIRO Oceans and Atmosphere, Castray Esplanade, Hobart, TAS, 7000
- Last PR and Stevens JD 2009, Sharks and rays of Australia, CSIRO Publishing, Australia.
- Lyle JM and Tracey SR 2012a, Recreational gillnetting in Tasmania – an evaluation of fishing practices and catch and effort. Institute for Marine and Antarctic Studies, University of Tasmania, Hobart.
- Lyle JM and Tracey SR 2012b, Preliminary survey of set-line usage in Tasmania. Institute for Marine and Antarctic Studies, University of Tasmania, Hobart.
- McAuley R, Braccini M, Newman SJ and O’Malley J 2015, Temperate Demersal Gillnet and Demersal Longline Fisheries Status Report. Pages 261–272 Status reports of the fisheries and aquatic resources of Western Australia 2014/15: The State of Fisheries
- Raoult V, Peddemors VM and Williamson JE 2016, Biology of angel sharks (Squatina sp.) and sawsharks (Pristiophorus sp.) caught in south-eastern Australian trawl fisheries. Marine & Freshwater Research, 68: 207–212.
- Ryan K, Hall N, Lai E, Smallwood C, Taylor S and Wise B 2017, Statewide survey of boat-based recreational fishing in Western Australia 2015/16. Fisheries Research Report No. 287, Department of Primary Industries and Regional Development, Western Australia.
- Walker TI and Hudson RJ 2005, Saw shark and elephant fish assessment and bycatch evaluation in the Southern Shark Fishery. Final Report to the FRDC. Project 1999/103.Primary Industries Research Victoria. 40 pp.
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