Eastern Australian Salmon (Arripis trutta)
Table 1: Stock status determination for Eastern Australian Salmon
Jurisdiction |
New South Wales, Tasmania, Victoria |
Stock |
Eastern Australian (CIF, GLF, OF, OHF, OPSF, PPBP, SF) |
Stock status |
|
Sustainable |
Indicators |
Catch, catch rates |
CIF = Corner Inlet Fishery (Victoria); GLF = Gippsland Lakes Fishery (Victoria); OF = Ocean Fishery (Victoria); OHF = Ocean Hauling Fishery (New South Wales); OPSF = Ocean Purse Seine Fishery (Victoria); PPBF = Port Phillip Bay Fishery (Victoria); SF = Scalefish Fishery (Tasmania)
Table 2: Stock status determination for Western Australian Salmon
Jurisdiction |
South Australia, Victoria, Western Australia |
Stock |
Western Australian (CIF, GLF, LACF, MF, MSF, NZRLF, OF, PPBF, SCSF, SWCSF, SZRLF) |
Stock status |
|
Sustainable |
Indicators |
Catch, catch rates |
CIF = Corner Inlet Fishery (Victoria); GLF = Gippsland Lakes Fishery (Victoria); LACF = Lakes and Coorong Fishery (South Australia); MF = Miscellaneous Fishery (South Australia); MSF = Marine Scalefish Fishery (South Australia); NZRLF = Northern Zone Rock Lobster Fishery (South Australia); OF = Ocean Fishery (Victoria); OPSF = Ocean Purse Seine Fishery (Victoria); PPBF = Port Phillip Bay Fishery (Victoria); SCSF = South Coast Salmon Managed Fishery (Western Australia); SWCSF = South West Coast Salmon Managed Fishery (Western Australia); SZRLF = Southern Zone Rock Lobster Fishery (South Australia)
There are two species of Australian Salmon: Eastern Australian Salmon (Arripis trutta) and Western Australian Salmon (A. truttaceus). Each species represents a single biological stock. The Eastern Australian Salmon biological stock is distributed from southern Queensland down the east coast of Australia to western Victoria and Tasmania. The Western Australian Salmon biological stock is distributed from Kalbarri in Western Australia southwards to South Australia, Victoria and the west coast of Tasmania. Both species have spawning areas that allow eggs and larvae to be dispersed by the prevailing currents—southwards by the East Australian Current (Eastern Australian Salmon), and southwards and then eastwards by the Leeuwin Current (Western Australian Salmon). The fish then grow and mature before moving back towards their spawning areas, which occur at the northern (up-current) parts of their distributions.
Eastern Australian Salmon biological stock
The Eastern Australian Salmon cross-jurisdictional biological stock has components in New South Wales, Tasmania and Victoria. Each jurisdiction assesses that part of the biological stock that occurs in its waters. The status presented here for the entire biological stock has been established using evidence from all jurisdictions.
For the New South Wales part of the biological stock, commercial landings are influenced largely by market demands. Annual landings have varied substantially since the mid-1990s in response to these demands. Catch rates (median catch per day hauling) have increased steadily during the past decade. The size and age compositions of fish in commercial landings have remained similar since the late 1970s1. The above evidence indicates that the biomass of this part of the stock is unlikely to be recruitment overfished. Australian Salmon in northern New South Wales are lightly fished commercially because fishing in this area is restricted to servicing of the commercial bait market, with an annual catch limit of 224 tonnes (t) in place. Estimates of overall fishing mortality are similar to estimates of natural mortality1. The above evidence indicates that the current level of fishing pressure is unlikely to cause this part of the stock to become recruitment overfished.
For the Victorian part of the biological stock, commercial landings have varied between 300 and 700 t annually, with a peak during the mid-2000s. The annual catch in 2013 was relatively low (235 t) compared with the previous year (more than 730 t). The most recent assessment of this part of the stock indicates that, until 2011, there was little change in the size and age composition of fish in landings1. Little information is available after this time. However, the fishery continues to target mainly adolescent fish, and the level of effort has remained steady. This evidence indicates that the Victorian part of the Eastern Australian Salmon biological stock is unlikely to be recruitment overfished and that the current level of fishing pressure by the Victorian fishery is unlikely to cause this part of the biological stock to become recruitment overfished.
For the Tasmanian part of the biological stock, the most recent assessment investigated catches up to 20122. Biomass was not estimated in this assessment. Although catches are at an all-time minimum, catch per unit effort remains high; the low catches are a result of a decline in effort, driven by decreased demand for Southern Rock Lobster bait2. The above evidence indicates that the biomass of this part of the stock is unlikely to be recruitment overfished. In Tasmania, Eastern Australian Salmon are landed by a large number of vessels using a variety of methods. However, more than 80 per cent of landings are by beach-seine vessels, and therefore the fishing patterns of these vessels dictate the catch patterns. The above evidence indicates that the current level of fishing pressure is unlikely to cause this part of the stock to become recruitment overfished.
On the basis of the evidence provided above, the biological stock is classified as a sustainable stock.
Western Australian Salmon biological stock
The Western Australian Salmon cross-jurisdictional biological stock has components in South Australia, Victoria and Western Australia. Each jurisdiction assesses that part of the biological stock that occurs in its waters. The status presented here for the entire biological stock has been established using evidence from all jurisdictions.
In Western Australia, total commercial landings have declined since the mid-1990s, with the strongest declines since 20043. Since 2004, fishing effort has followed a similar downward trend, as a result of weak market demand and low wholesale prices (landings in Western Australia are mainly sold as bait). These catch and effort declines mainly reflect changes in the south coast fishery, where the majority of annual landings occur. Total commercial fishing effort directed towards Australian Salmon in Western Australia is currently very low compared with historical levels, and the reduction in effort accounts for much of the catch decline since 2004. However, a decline in commercial catch rate, and anecdotal reports from commercial and recreational fishers suggest a possible decline in stock abundance over the past decade that may also have contributed to the catch decline. Pronounced ocean warming around south-western Australia, and changes in the strength and seasonality of the Leeuwin Current over the past decade are among the environmental factors that may have negatively impacted on the breeding success of Australian Salmon, and resulted in a lower stock level. Fishery-independent monitoring annually since 1996 in Western Australia, and from 1981 to 2000 in South Australia has confirmed highly variable recruitment by this species, with variations in recruitment associated with fluctuations in the Leeuwin Current3–5. Despite the possibility of low stock abundance at present, the Western Australian recruitment index was relatively high in 2013, suggesting that the breeding stock level was adequate to maintain recruitment. The above evidence indicates that the biomass of this part of the stock is unlikely to be recruitment overfished. Very low levels of fishing effort are currently directed towards Western Australian Salmon across all jurisdictions. The above evidence indicates that the current level of fishing pressure is unlikely to cause this part of the stock to become recruitment overfished.
For the South Australian part of the biological stock, total commercial landings have declined markedly since the mid-1990s. However, commercial effort has declined similarly. The current commercial fishing effort directed towards Western Australian Salmon in South Australia is very low compared with historical levels, and, although variable, catch rates have not decreased6. This evidence indicates that the South Australian part of the Western Australian Salmon biological stock is unlikely to be recruitment overfished and that the current level of fishing pressure by the South Australian fishery is unlikely to cause this part of the biological stock to become recruitment overfished.
For the Victorian part of the biological stock, total commercial landings are very low compared with those in other states and compared with landings of Eastern Australian Salmon in Victoria. The low commercial landings of Western Australian Salmon relative to the catches taken by other jurisdictions indicate that the current level of fishing pressure by the Victorian fishery is low. This evidence indicates that the Victorian part of the Western Australian Salmon biological stock is unlikely to be recruitment overfished and that the current level of fishing pressure by the Victorian fishery is unlikely to cause this part of the biological stock to become recruitment overfished.
On the basis of the evidence provided above, the biological stock is classified as a sustainable stock.
Table 3: Eastern (Arripis trutta) and Western (A. truttaceus) Australian Salmon biology1,7
Longevity and maximum size |
Eastern Australian Salmon: 12 years; 810 mm FL Western Australian Salmon: 12 years; 850 mm FL |
Maturity (50%) |
Eastern Australian Salmon: 2–4 years; 300–400 mm FL Western Australian Salmon: 3–5 years; 600–650 mm FL |
FL = fork length
Figure 1: Distribution of reported commercial catch of Australian Salmon (both species) in Australian waters, 2013 (calendar year)
Table 3: Main features and statistics for Australian Salmon fisheries in Australia, 2013 (calendar year)
Jurisdiction |
New South Wales |
Victoria |
Tasmania |
South Australia |
Western Australia |
Fishing methods |
Commercial |
Purse-seine nets |
✓ |
✓ |
✓ |
✓ |
|
Beach-seine nets |
✓ |
✓ |
✓ |
|
✓ |
Gillnet |
|
✓ |
✓ |
✓ |
|
Ring nets |
|
✓ |
|
✓ |
|
Trolling |
|
|
|
✓ |
|
Recreational |
Rod and line |
✓ |
✓ |
✓ |
✓ |
✓ |
Gillnet |
|
|
✓ |
|
|
Indigenous |
Rod and line |
✓ |
|
|
|
|
Management methods |
Commercial |
Limited entry |
✓ |
✓ |
✓ |
✓ |
✓ |
Gear restrictions |
✓ |
✓ |
✓ |
✓ |
✓ |
Size limits |
|
✓ |
✓ |
✓ |
|
Trip limits |
✓ |
|
|
|
|
Spatial zoning |
✓ |
|
|
|
✓ |
Vessel restrictions |
|
|
|
|
✓ |
Recreational |
Bag limits |
✓ |
✓ |
✓ |
✓ |
✓ |
Size limits |
|
✓ |
✓ |
✓ |
✓ |
Gear restrictions |
✓ |
✓ |
✓ |
✓ |
✓ |
Spatial closures |
✓ |
✓ |
✓ |
|
✓ |
Licensing |
|
|
|
|
✓(boat based) |
Indigenousa–d |
Bag limits |
✓ |
|
✓ |
|
✓ |
Size limits |
|
|
✓ |
|
✓ |
Spatial closures |
✓ |
|
|
|
|
Gear restrictions |
✓ |
|
|
|
|
Section 37(1)(c1), Aboriginal cultural fishing authority |
✓ |
|
|
|
|
Gillnet restrictions |
|
|
✓ |
|
|
Licensing |
|
|
|
|
✓ (boat based) |
Active vessels |
|
127 in OHF |
18 in CIF
9 in GLF
13 in OF and OPSF combined
31 in PPBF |
37 in SF |
2 in LACF
1 in MF
68 in MSF
2 in NZRLF
4 in SZRLF |
7 in SCSF
2 in SWCSF |
Catch |
Commercial |
841 t in OHF |
20.8 t in CIF
2.9 t in GLF
305.4 t in OF and OPSF combined
28.3 t in PPBF |
236 t in SF |
0.02 t in LACF
5 t in MF
54 t in MSF
0.4 t in NZRLF
0.1 t in SZRLF |
138 t in SCSF
93 t in SWCSF |
Recreational |
181 t8 (NRIFS in 2000–01) |
Unknown |
48.1 t (2007–08) |
91 t9 (2007–08) |
11 t10 (boat-based sector onlye) |
Indigenous |
Unknown |
None |
Unknown |
Unknown |
Unknown |
Markets |
Domestic |
✓ |
✓ |
✓ |
✓ |
✓ |
Export |
|
|
|
|
|
CIF = Corner Inlet Fishery (Victoria); GLF = Gippsland Lakes Fishery (Victoria); LACF = Lakes and Coorong Fishery (South Australia); MF = Miscellaneous Fishery (South Australia); MSF = Marine Scalefish Fishery (South Australia); NRIFS = National Recreational and Indigenous Fishing Survey; NZRLF = Northern Zone Rock Lobster Fishery (South Australia); OF = Ocean Fishery (Victoria); OHF = Ocean Hauling Fishery (New South Wales); OPSF = Ocean Purse Seine Fishery (Victoria); PPBF = Port Phillip Bay Fishery (Victoria); SCSF = South Coast Salmon Managed Fishery (Western Australia); SF = Scalefish Fishery (Tasmania); SWCSF = South West Coast Salmon Managed Fishery (Western Australia); SZRLF = Southern Zone Rock Lobster Fishery (South Australia)
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 (e.g. 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 Australian Salmon.
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 Subject to the defence that applies under section 211. of the Native Title Act 1993 (Cth), and the exemption from a requirement to hold a recreational fishing licence, the non-commercial take by indigenous fishers is covered by the same arrangements as that for recreational fishing.
e Western Australian boat-based recreational catch from 1 March 2011 to 29 February 201210

Figure 2: Commercial catch of Australian Salmon in Australian waters, 2001 to 2013 (calendar years)
- The fishing methods used to target Australian Salmon around Australia are highly selective and targeted. As a result, there is little bycatch in these fisheries1,3.
- The life cycles of Eastern and Western Australian Salmon are strongly linked to the prevailing currents throughout their distributions. The East Australian, Leeuwin and Capes currents appear to influence the distribution of spawning, larval dispersal, the strength and distribution of juvenile recruitment, and the distribution of fishery landings3,5. Environmentally driven changes to these currents may affect recruitment, and the distribution and abundance of both species.
a Department of Primary Industries, New South Wales
b South Australian Research and Development Institute
c Institute for Marine and Antarctic Studies, University of Tasmania
d Department of Environment Primary Industries, Victoria
e Department of Fisheries, Western Australia