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Stock Status Overview
|New South Wales||East Coast||OTLF||Undefined||Biomass, standardised catch rates, fishery-dependent length and age frequency, estimates of total mortality rate, catch, effort, fishery-independent juvenile abundance|
- Ocean Trap and Line (NSW)
Snapper has a wide distribution in Australia, from the Gascoyne region on the west coast of Western Australia, around the south of the continent, and up to northern Queensland, around Hinchinbrook Island1. Within this broad distribution, the biological stock structure is complex.
Snapper on the east coast of Australia, from Proserpine in north Queensland to around Wilsons Promontory (Victoria), show little genetic differentiation and are considered to represent a single genetic stock2. Similarly, in Victoria, little genetic variation has been found for Snapper3. However, tagging and otolith chemistry data have indicated some separation between Snapper to the east of Wilsons Promontory (the East coast biological stock) and to the west, including Port Phillip Bay and Western Port (Western Victorian biological stock) and extending across western Victoria to near the Murray mouth in South Australia4–6.
Despite the separation of the Eastern and Western stocks in Victorian waters, Snapper are managed at a state-wide level in Victoria, with management arrangements that govern commercial fishing in specific regions such as bays and inlets, and offshore waters. Bag and size limits for the recreational sector are the same for the Western and Eastern stocks in Victorian waters. Recent changes to commercial fishing in Port Phillip Bay (Western stock) have resulted in removal of most of the fishing effort by net methods, and capping of catches for the remaining hook method operators. The Eastern stock, from Victoria to Queensland, is managed at a state level.
Further research has been undertaken to inform the level of stock sharing between Victoria and South Australia.
The South Australian fishery was originally divided into six management units, due to uncertainty about the extent of the movement of fish between different regional populations7. However, a recent study evaluated the stock structure and adult movement between regional populations of South Australia and western Victoria8 based on inter-regional comparisons of otolith chemistry and increment widths, as well as demographic features. The study differentiated three stocks. The Western Victorian stock extends from Wilsons Promontory westward into south-eastern South Australia. This stock depends on recruitment into, and subsequent emigration from, Port Phillip Bay in Victoria. As such, this is a cross-jurisdictional stock, although the components from the two states are still assessed and managed independently. The two further stocks are wholly located within South Australia. The Spencer Gulf/West Coast stock depends on recruitment into Northern Spencer Gulf from where fish emigrate to replenish the populations of Southern Spencer Gulf and the west coast of Eyre Peninsula. The third stock is the Gulf St. Vincent stock, which relies on recruitment into, and subsequent emigration from, Northern Gulf St. Vincent.
In Western Australia, Snapper is divided into six management units, some at small geographic scales (for example, there are three separate biological stocks located inside Shark Bay) and others that cover greater areas of oceanic waters in the Gascoyne, west and south coast regions9–13. The inshore Shark Bay biological stocks in the inner gulfs are predominantly fished by the recreational and charter sectors.
Here, assessment of stock status is presented at the biological stock level—Shark Bay inshore–Eastern Gulf, Shark Bay inshore–Denham Sound, Shark Bay inshore–Freycinet Estuary (Western Australia); East coast, Western Victorian, Spencer Gulf West Coast (South Australia) and Gulf St Vincent Fishery (South Australia); and the management unit level—South coast, Shark Bay oceanic and West coast (Western Australia).
The cross-jurisdictional East coast biological stock has components in Queensland, New South Wales and Victoria. Each jurisdiction assesses and manages the part of the biological stock that occurs in its waters. However, status is presented here for the entire East coast biological stock, considering evidence from the three jurisdictions. The total annual catch from the East coast biological stock has averaged around 307 t over the period 2011–15, of which Queensland 21 per cent, New South Wales contributed 75 per cent and Victoria four per cent.
The New South Wales part of the biological stock is assessed annually in terms of commercial harvest, catch rates and size composition of landings. Periodic sampling of age composition is used to generate mortality estimates. Snapper are currently assessed as being growth overfished in New South Wales waters, with yield from the stock being limited by harvesting at too small a size and at an excessive rate. Nominal commercial median catch rates (kg per day trapping) have more than doubled since the minimum legal length (MLL) was increased to 300 mm total length (TL) in 2001, although some declines have been observed during the past 2 years18. Catch rates in the recreational fishery remained stable between 2000–01 and 2013–1419. The size composition of Snapper in commercial landings has remained highly stable, with the average size between approximately 310 and 320 mm fork length each year since 200418. The most recent commercial age composition samples in 2013–14 and 2014–15 showed that the fishery continues to be dominated by fish aged between 3 and 6 years, with recent increases in the proportion of fish aged more than 5 years. The above evidence indicates that the biomass of this part of the stock is unlikely to be recruitment overfished.
Commercial landings in the New South Wales part of the biological stock in 2015 (around 150 t) were the lowest on record (noting that the catch records for 2015 may be incomplete at this time) and the reported number of fisher days in the trap fishery when Snapper were reported in 2015 was also at an all-time low of less than 5000 days. The New South Wales recreational harvest declined by 20 per cent between 2000–01 and 2013–1419, due largely to a reduction in fishing effort. The selectivity of the New South Wales demersal trap fishery means that it continues to harvest Snapper over a relatively narrow size range generally between 300 and 450 mm TL. Typical size compositions in 2015 suggest no large changes to the fishery. Since 2011–12, estimates of total mortality from the commercial line sector have been around twice natural mortality. The above evidence indicates that the current level of fishing pressure is unlikely to cause this part of the stock to become recruitment overfished.
Queensland assessed its jurisdictional component of the East coast Australian biological stock in 2009 (including data up until 2007) using a sex, age and length based stock assessment model20. The assessment estimated exploitable biomass to be around 35 per cent of unfished levels20, with biomass expected to decline further if fishing pressure remained unchanged. Since the completion of the stock assessment, no measurable improvement in biomass has been detected, and the standardised commercial catch rate has fallen a further 15 per cent21, to historically low levels. Decreases in the recreational and charter sector nominal catch rates were also observed between 2007 and 201521–24. Catch rates for all sectors indicate a further reduction in biomass. Increased harvest at the northern extent of the fishery (particularly the Swains Reef area, off Rockhampton, Queensland), the most northern distribution of this species, has increased the north’s relative importance and contribution to total commercial harvest21. Spatial expansion of the commercial fishery to fishing grounds further north and offshore may have occurred in response to declining catches and catch rates in other areas.
In 2015, average Queensland Snapper pre-recruit catch rates from fishery-independent trawl surveys were very low in comparison to previous years, showing a relative decrease of 57 per cent since 2014 and a decrease of 94 per cent since 201121, indicating a corresponding decrease in available biomass. Fishery-dependent monitoring shows commercial and recreational length structures dominated by fish within 150 mm of the current MLL21. This pattern has been consistent since monitoring began in 2007. Fishery-dependent monitoring shows truncated commercial and recreational age frequencies dominated by young fish; particularly in the recreational sector21. Relatively few older fish are present in the Queensland fishery. The above data raises further concerns about the level of Snapper biomass that remains, with evidence indicating that the Queensland component of the stock is likely to be recruitment overfished.
Between 2007 and 2015, harvest data show no indication of recovery or improvement in the Queensland component of the stock, with commercial, charter and recreational sectors all declining to, or below, historic lows21–24. Active commercial fishing licenses and fishing effort days continue to decrease21. Estimates of fishing mortality continue to remain high, and are the highest in 9 years, exceeding natural mortality in 201521. Despite protection of Snapper through a variety of mechanisms that aim to reduce fishing mortality, the data indicate that the current level of fishing pressure is too high to allow the Queensland component of the East coast Snapper stock to recover from being recruitment overfished.
An assessment of the status of the East coast biological stock of Snapper in Victorian waters was attempted in 201625. The assessment found that insufficient data were available. The catch of Snapper for this part of the state is substantially less than for Victoria’s Western biological stock, and only made up around one per cent (2.6 t) of the estimated total catch of 213 t from the East coast biological stock in 2015. For commercial fishers, Snapper in the Victorian part of the East coast biological stock has historically been considered to be a by-product species, and the majority of the catch is taken by Commonwealth licensed operators in the Danish seine fishery. The status of the Victorian component of the East coast biological stock is therefore undefined although, given the small contribution to catches, it is relatively uninfluential on the status of the whole stock.
On the basis of conflicting indicators for the Queensland and New South Wales components of this stock, the East coast biological stock is classified as an undefined stock.
|Species||Longevity / Maximum Size||Maturity (50 per cent)|
|Snapper||30–40 years; 1300 mm TL||2–7 years; 220–560 mm TL|
Distribution of reported commercial catch of Snapper
|New South Wales|
|Hand Line, Hand Reel or Powered Reels|
|Hand Line, Hand Reel or Powered Reels|
|Method||New South Wales|
|Section 31 (1)(c1), Aboriginal cultural fishing authority|
|New South Wales|
|35 in EGF, 46 in OTF, 170 in OTLF|
- Estuary General Fishery (NSW)
- Ocean Trawl Fishery (NSW)
- Ocean Trap and Line (NSW)
|New South Wales|
|Commercial||148.65t in OTLF|
|Recreational||148 t (in 2013–14)|
- Ocean Trap and Line (NSW)
a Victoria – Indigenous 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 Traditional Owner Settlement Act 2010 [Vic]) are exempt (subject to conditions) from the requirement to hold a recreational fishing licence, and can apply for permits under the Fisheries Act 1995 (Vic) 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 permits to access Snapper.
b Queensland – Indigenous Under the Fisheries Act 1994 (Qld), Indigenous fishers in Queensland are entitled 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.
c Western Australia – Recreational (management methods) In Western Australia, total recreational catch limits (that is, maximum catch limits) have been applied to stocks of Snapper in inner Shark Bay and the west coast, to aid recovery of stocks.
d New South Wales – Indigenous (management methods) Aboriginal fishing interim compliance policy (increased bag limits) – 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.
e New South Wales – Indigenous (management methods) Aboriginal cultural fishing authority - the authority that Indigenous persons can apply to take catches outside the recreational limits under the Fisheries Management Act 1994 (NSW), Section 37 (1)(c1), Aboriginal cultural fishing authority.
Commercial catch of Snapper
Effects of fishing on the marine environment
- Most of the fisheries that target adult Snapper use hook and line fishing techniques, which are likely to have little direct impact on benthic habitats. To date, limited research on the effects of fish traps on the benthic environment in New South Wales suggests only a minor influence (unpublished data, Department of Primary Industries, New South Wales).
- Snapper are generalist feeders and normally just one of a number of such species inhabiting continental shelf waters. Effects on the food chain from fishing for Snapper are considered to be low risk. This is supported by a recent study which found no evidence of material changes in finfish community structure over the past 30 years in the three Western Australian Bioregions where Snapper are captured32.
Environmental effects on Snapper
- A recent Fisheries Research and Development Corporation project identified two potential significant effects of climate change on Snapper populations33. First, there is an optimal temperature range of 18–22°C for the production and survivorship of Snapper larvae. Furthermore, peak spawning times vary with latitude, resulting in peak production corresponding to the optimal temperature range. Warmer projected sea surface temperature regimes in the future will alter the timing and/or length of these optimal conditions for spawning and larval survivorship in different regions. This might restrict opportunities for successful spawning and recruitment in the northern fisheries, but provide enhanced opportunities for some southern fisheries, and the opportunity for establishing new populations and fisheries further south. Such environmental changes might also affect spawning and recruitment for the populations in South Australia’s gulfs and Port Phillip Bay, Victoria.
- The second possible effect of climate change on Snapper populations is greater variation in recruitment of fish aged 0+ years33. Such variable recruitment already accounts for the population dynamics and variation in fishery productivity for a number of Australia’s southern Snapper fisheries. Variation in recruitment is driven by the survivorship of the larvae. Larval survivorship depends on the overlap of the optimal temperature window with periods of high larval prey concentrations. The latter depends on nutrient input to marine environments. The effects of climate change on the dynamics of nutrient supply in Snapper spawning areas are difficult to predict because the sources of such nutrients vary from place to place. Furthermore, current understanding of nutrient supply and the dynamics of planktonic food chains is limited.
- 1 Kailola, PJ, Williams, MJ, Stewart, PC, Reichelt, RE, McNee, A and Grieve, C 1993, Australian fisheries resources, Bureau of Resource Sciences, Department of Primary Industries and Energy and Fisheries Research and Development Corporation, Canberra.
- 2 Sumpton, WD, Ovenden, JR, Keenan CP and Street, R 2008, Evidence for a stock discontinuity of Snapper (Pagrus auratus) on the east coast of Australia, Fisheries Research, 94(1): 92–98.
- 3 Meggs, LB and Austin CM 2003, Low allozyme variation in Snapper, Pagrus auratus, in Victoria, Australia, Fisheries Management and Ecology, 10: 155–162.
- 4 Donnellan, SC and McGlennon D 1996, Stock identification and discrimination in Snapper (Pagrus auratus) in southern Australia, final report to the Fisheries Research and Development Corporation, project 94/168, South Australian Research and Development Institute, Adelaide.
- 5 Hamer, PA, Acevedo, S, Jenkins, GP and Newman, A 2011, Connectivity of a large embayment and coastal fishery: spawning aggregations in one bay source local and broad-scale fishery replenishment, Journal of Fish Biology, 78: 1090–1109.
- 6 Sanders, MJ 1974, Tagging study indicates two stocks of Snapper (Chrysophrys auratus) off south east Australia, Australian Journal of Marine and Freshwater Research, 8: 371–374.
- 7 Fowler, AJ, McGarvey, R, Burch, P, Feenstra, JE, Jackson, WB and Lloyd MT 2013, Snapper (Chrysophrys auratus) fishery, Fishery assessment report to Primary Industries and Regions South Australia (Fisheries and Aquaculture), South Australian Research and Development Institute (Aquatic Sciences) publication F2007/000523-3, SARDI research report series 713, SARDI, Adelaide.
- 8 Fowler, AJ 2016, The influence of fish movement on regional fishery production and stock structure for South Australia’s Snapper (Chrysophrys auratus) fishery. Final Report to FRDC (Project No. 2012/020). 181 pp.
- 9 Edmonds, JS, Steckis, RA, Moran, MJ, Caputi, N and Morita, M 1999, Stock delineation of Pink Snapper Pagrus auratus and Tailor Pomatomus saltatrix from Western Australia by analysis of stable isotope and strontium/calcium ratios in otolith carbonate, Journal of Fish Biology, 55: 243–259.
- 10 Jackson G 2007, Fisheries biology and management of Pink Snapper, Pagrus auratus, in the inner gulfs of Shark Bay, Western Australia, PhD thesis, Murdoch University, Perth.
- 11 Johnson, MS, Creagh, S and Moran, M 1986, Genetic subdivision of stocks of Snapper, Chrysophrys unicolor, in Shark Bay, Western Australia, Australian Journal of Marine and Freshwater Research, 37: 337–345.
- 12 Lenanton, R, St John, J, Keay, I, Wakefield, C, Jackson, G, Wise, B and Gaughan, D (eds) 2009, Spatial scales of exploitation among populations of demersal scalefish: implications for management, part 2, Stock structure and biology of two indicator species, West Australian Dhufish (Glaucosoma hebraicum) and Pink Snapper (Pagrus auratus), in the West Coast Bioregion, Fisheries research report 174, Western Australian Department of Fisheries, Perth.
- 13 Moran, M, Burton, C and Jenke, J 2003, Long-term movement patterns of continental shelf and inner gulf Snapper (Pagrus auratus, Sparidae) from tagging in the Shark Bay region of Western Australia, Marine and Freshwater Research, 54: 913–922.
- 14 Fairclough, D, Johnson C and Lai, E 2009, West Coast Demersal Scalefish Fishery, in WJ Fletcher and K Santoro (eds) 2009, State of the fisheries report 2008/09, Western Australian Department of Fisheries, Perth.
- 15 Fairclough, DV, Molony, BW, Crisafulli, BM, Keay, IS, Hesp, SA and Marriott, RJ 2014, Status of demersal finfish stocks on the west coast of Australia, Fisheries research report 253, Western Australian Department of Fisheries, Perth.
- 16 Wise, BS, St John, J and Lenanton, RC (eds) 2007, Spatial scales of exploitation among populations of demersal scalefish: implications for management, part 1, Stock status of the key indicator species for the demersal scalefish fishery in the West Coast Bioregion, Fisheries research report 163, Western Australian Department of Fisheries, Perth.
- 17 Norriss, JV, Fisher, EA, Hesp, SA, Jackson, G, Coulson, PG, Leary, T and Thomson AW (in press) Status of inshore demersal scalefish stocks on the South Coast of Western Australia Fisheries Research Report, Western Australian Department of Fisheries, Perth.
- 18 Stewart, J, Hegarty, A, Young, C, Fowler, AM and Craig, J 2015, Status of Fisheries Resources in NSW 2013-14, NSW Department of Primary Industries, Mosman: 391pp.
- 19 West, L.D, Stark, KE, Murphy, JJ, Lyle JM and Doyle, FA 2015, Survey of recreational fishing in New South Wales and the ACT, 2013/14. Fisheries Final Report Series
- 20 Campbell, AB, O’Neill, MF, Sumpton, W, Kirkwood, J and Wesche, S 2009, Stock assessment summary of the Queensland Snapper fishery (Australia) and management strategies for improving sustainability, Queensland Department of Employment, Economic Development and Innovation, Brisbane.
- 21 Henry, GW and Lyle, JM 2003, The National Recreational and Indigenous Fishing Survey, Fisheries Research and Development Corporation project 99/158, Australian Government Department of Agriculture, Fisheries and Forestry, Canberra.
- 22 Queensland Department of Agriculture, Fisheries and Forestry 2016, Queensland Stock Status Assessment Workshop 2016, 14–15 June 2016, Brisbane, Queensland DAF, Brisbane.
- 23 Taylor, S, Webley, J and McInnes, K 2012, 2010-11 Statewide Recreational Fishing Survey, Queensland Department of Agriculture, Fisheries and Forestry, Brisbane.
- 24 Webley, J, McInnes, K, Teixeira, D, Lawson, A and Quinn, R 2015, 2013-14 Statewide Recreational Fishing Survey, Queensland Department of Agriculture and Fisheries, Brisbane.
- 25 Hamer, P and Conron, S 2016, Snapper stock assessment 2016, Fisheries Victoria Science Report Series 10, Fisheries Victoria, Queenscliff.
- 26 Fowler, AJ, McGarvey, R, Carroll, J, Feenstra, JE, Jackson, WB and Lloyd MT 2016, Snapper (Chrysophrys auratus) fishery, Fishery assessment report to Primary Industries and Regions South Australia (Fisheries and Aquaculture), South Australian Research and Development Institute (Aquatic Sciences) in preparation.
- 27 Coutin, PC, Cashmore, S and Sivakumuran, KP 2003, Assessment of the Snapper fishery in Victoria, Fisheries Research and Development Corporation final report, project 97/128, Victorian Department of Primary Industries, Melbourne.
- 28 Stewart, J, Rowling, K, Hegarty, AM and Nuttall, A 2010, Size and age at sexual maturity of Snapper (Pagrus auratus) in New South Wales 2008/09, Fisheries research report series 27, Industry and Investment New South Wales, Cronulla.
- 29 Wakefield, CB 2006, Latitudinal and temporal comparisons of the reproductive biology and growth of Snapper, Pagrus auratus, in Western Australia, PhD thesis, Murdoch University, Perth.
- 30 Ryan, KL, Morison, AK and Conron, S 2009, Evaluating methods of obtaining total catch estimates for individual Victorian bay and inlet recreational fisheries, Fisheries Research and Development Corporation final report 2003/047, Department of Primary Industries, Victoria
- 31 Giri, K, and Hall, K, 2015, South Australian Recreational Fishing Survey. Fisheries Victoria Internal report Series No. 62.
- 32 Hall, NG and Wise, BS 2011, Development of an ecosystem approach to the monitoring and management of Western Australian fisheries, Fisheries Research and Development Corporation report 2005/063, Fisheries research report 215, Western Australian Department of Fisheries, Perth.
- 33 Pecl, G, Ward, T, Briceno, F, Fowler, A, Frusher, S, Gardner, C, Hamer, P, Hartmann, K, Hartog, J, Hobday, A, Hoshino, E, Jennings, S, Le Bouhellec, B, Linnane, A, Marzloff, M, Mayfield, S, Mundy, C, Ogier, E, Sullivan, A, Tracey, S, Tuck, G and Wayte, S 2014, Preparing fisheries for climate change: identifying adaptation options for four key fisheries in south eastern Australia, draft final report to the Fisheries Research and Development Corporation, project 2011/039.