Mulloway Argyrosomus japonicus

Jason Earla, Julian Hughesb, Anthony Roelofsc, David Faircloughd and James Andrewse


Mulloway

Table 1: Stock status determination for Mulloway

Jurisdiction

Western Australia

South Australia

Victoria

Stock

Western Australia

(GDSMF, JASDGDLFM1, JASDGDLFM2, OA, SBBSMNMF, SBPMF, SCEMF, SWTMF; WCDGDLIMF, WCDSIMF, WCEIMF)

LCF

MSF

Victoria (PPBF)

Stock status

       

Undefined

Sustainable

Undefined

Undefined

Indicators

Catch

Catch, CPUE, age structure

Catch, CPUE

Catch


CPUE = catch per unit effort; GDSMF = Gascoyne Demersal Scalefish Managed Fishery (Western Australia); JASDGDLFM1 = Joint Authority Southern Demersal Gillnet and Demersal Longline Managed Fishery Zone 1 (Western Australia); JASDGDLFM2 = Joint Authority Southern Demersal Gillnet and Demersal Longline Managed Fishery Zone 2 (Western Australia); LCF = Lakes and Coorong Fishery (South Australia); MSF = Marine Scalefish Fishery (South Australia); OA = Open Access – fishing not formally managed (Western Australia); PPBF = Port Phillip Bay Fishery (Victoria); SBBSMNMF = Shark Bay Beach Seine and Mesh Net Managed Fishery (Western Australia); SBPMF = Shark Bay Prawn Managed Fishery (Western Australia); SCEMF = South Coast Estuarine Managed Fishery (Western Australia); SWTMF = South-west Trawl Managed Fishery (Western Australia); WCDGDLIMF = West Coast Demersal Gillnet and Demersal Longline Interim Managed Fishery (Western Australia); WCDSIMF = West Coast Demersal Scalefish (Interim) Managed Fishery (Western Australia); WCEIMF = West Coast Estuarine (Interim) Managed Fishery (Western Australia)

 

Table 1 continued

Jurisdiction

New South Wales

Queensland

Stock

New South Wales

(EGF, OFTF, OHF, OPTF, OTLF)

Queensland

(ECIFFF)

Stock status

 

Overfished

Undefined

Indicators

Catch, catch rates, length and age structure, mortality rates

Catch

ECIFF = East Coast Inshore Fin Fish Fishery (Queensland); EGF = Estuary General Fishery (New South Wales); OFTF = Ocean Fish Trawl Fishery (New South Wales); OHF = Ocean Hauling Fishery (New South Wales); OPTF = Ocean Prawn Trawl Fishery (New South Wales); OTLF = Ocean Trap and Line Fishery (New South Wales)


Stock Structure

Mulloway is widely distributed in estuaries and near-shore coastal waters (less than 200 m depth) of the Pacific and Indian Oceans, including subtropical and temperate waters of Australia1–3. In Australia, it occurs along the south coast from Exmouth in Western Australia to the Burnett River in
Queensland4.

Attempts to understand the biological stock structure of Mulloway in Australia have yielded differing results1,3,5. It has been suggested that a single panmictic population of Mulloway occurs in Australia5, but this is not supported by studies that suggest substructuring between populations in New South Wales, South Australia and Western Australia1,3,6. As a result, stock status is reported at the jurisdictional level for Western Australia, Victoria, New South Wales and Queensland. For South Australia, status is reported for two functionally independent management units that reflect spatial patterns in commercial fishing6.


Stock Status

Western Australia

In Western Australia, commercial catches have steadily declined from around 60 tonnes (t) in 2002 to 12 t in 20137. This progressive decline in catch is likely to be related to reductions in fishing effort resulting from changes during that period to the management of some fisheries—for example, the West Coast Demersal Scalefish (Interim) Managed Fishery and Gascoyne Demersal Scalefish Managed Fishery. The lack of biological information and time series of catch-and-effort or catch-rate data for Mulloway in Western Australia limits our understanding of recruitment patterns that could otherwise identify a trend of declining or increasing biomass. As such, there is insufficient information available to confidently classify status in Western Australia.

On the basis of the evidence provided above, Mulloway in Western Australia is classified as an undefined stock.  

Lakes and Coorong Fishery (South Australia) management unit

The Lakes and Coorong Fishery management unit has traditionally been the most important of the South Australian fisheries for Mulloway, accounting for an average of around 91 per cent of the state’s total catch since 2000. From 2003 to 2011, catches of Mulloway by the Lakes and Coorong Fishery were relatively low (less than 45 t per year), reflecting low levels of targeted effort and low catch per unit effort (CPUE)—an available estimate of relative abundance for Mulloway in the Coorong estuary8. Since that period, catch has increased sharply, to around 115 t in 2013, and mean annual CPUE has increased to historically high levels. Age-structure analysis revealed that the recent high catches and catch rates were due mainly to the recruitment of a large biomass of juvenile (3–6‑year old) fish to the fishery (J Earl, South Australian Research and Development Institute, personal communication). The information provided above suggests that the biomass of Mulloway harvested by the Lakes and Coorong Fishery is unlikely to be recruitment overfished. Furthermore, the current level of fishing pressure is unlikely to cause the stock to become recruitment overfished.

On the basis of the evidence provided above, the management unit is classified as a sustainable stock.  

Marine Scalefish Fishery (South Australia) management unit

The Marine Scalefish Fishery (South Australia) management unit has traditionally provided much lower catches than the Lakes and Coorong Fishery (South Australia). Catches were historically low through the mid- to late 2000s, as a result of historically low targeted fishing effort. However, since the early 1990s, commercial CPUE has followed an increasing trend, indicating a possible gradual increase in fishable biomass8. The lack of age data for Mulloway harvested by the Marine Scalefish Fishery limits our understanding of recruitment patterns that could otherwise confirm inform trends in biomass in this management unit. As such, there is insufficient information available to confidently classify the status of this management unit.

On the basis of the evidence provided above, the management unit is classified as an undefined stock.  

Victoria

Commercial catches in Victoria have mostly been landed from Port Phillip Bay, and from Western Port until Western Port was closed to commercial net fishing in 2008. Most of the catch was taken using mesh nets and haul seines. Over the past 10 years, annual catch by the commercial sector has been less than 0.6 t.

Recreational fishing for Mulloway has become increasingly popular over the past few years. The fishery is distributed throughout Victorian estuaries, rivers and nearby beaches. No assessment or review of the data available for this species has been conducted in recent years. The lack of biological information and time series of catch-and-effort or catch-rate data for Mulloway in Victoria limits our understanding of recruitment patterns and our ability to make a meaningful assessment. As such, there is insufficient information available to confidently classify the status of this stock.

On the basis of the evidence provided above, Mulloway in Victoria is classified as an undefined stock.  

New South Wales

Commercial landings in New South Wales steadily declined from almost 400 t in the mid-1970s to 37 t in 2008–09. Commercial landings have been less than 100 t per year since the mid-1990s. In 2013, the total commercial catch for New South Wales was 65 t. Nominal commercial catch rates for Mulloway have declined during the past 20 years in both the ocean and estuarine fisheries (unpublished data from New South Wales Department of Primary Industries). The average lengths of Mulloway landed by the commercial fishery have declined since the mid-1990s3,9. The age composition of fish in commercial landings in the early 2000s was indicative of a heavily fished stock (98 per cent of catch was less than 5 years old)3,9. Fishing mortality is estimated to be greater than natural mortality3,9. The spawning potential ratio for Mulloway was estimated to be between 4 and 14 per cent3,10, which is below the threshold reference point of 25 per cent. This indicates that there may be a high risk of recruitment failure11,12. The above evidence indicates that the stock is likely to be recruitment overfished.

In 2013, a recovery program for Mulloway was introduced in New South Wales to arrest the decline in commercial and recreational Mulloway fisheries. Management changes to the recreational Mulloway fishery consisted of an increase in legal minimum size from 45 to 70 cm (the approximate size-at-maturity for female Mulloway in New South Wales3,9,13) and a 40 per cent reduction in the bag limit. Management changes to the commercial Mulloway fishery consisted of the above increase in legal minimum size (with bycatch limits for the estuarine mesh net fishery) and a 500 kg trip limit for the beach-hauling net sector. The above evidence indicates that current fishing pressure is constrained by management to a level that should allow the stock to recover from its recruitment overfished state. However, measurable improvements are yet to be detected.

On the basis of the information provided above, Mulloway in New South Wales is classified as an overfished stock.  

Queensland

Mulloway are predominantly taken by recreational anglers in Queensland, with an estimated 133 t caught in 2010–1114. The East Coast Inshore Fin Fish Fishery (Queensland) contributes minimal quantities (5‑year average of 2 t) to the overall Queensland harvest of Mulloway. The legal size limit (75 cm total length) protects a proportion of spawning fish from fishing, while a conservative recreational bag limit (two fish) reduces fishing pressure on the stock. There are anecdotal reports of incidental mortality of Mulloway below the legal minimum size from commercial net fisheries; however, this has not been quantified. Insufficient information is available to confidently classify the status of this stock.

On the basis of the evidence provided above, Mulloway in Queensland is classified as an undefined stock.


Table 2: Mulloway biology1,13,15,16

Longevity and maximum size

42 years; 2000 mm TL

Maturity (50%)

2–6 years; 510–1070 mm TL


TL = total length


Figure 1: Distribution of reported commercial catch of Mulloway in Australian waters, 2013 (calendar year)
Figure 1: Distribution of reported commercial catch of Mulloway in Australian waters, 2013 (calendar year)



Table 3: Main features and statistics for Mulloway fisheries in Australia, 2013 (calendar year)

Jurisdiction

Western Australia

South Australia

Victoria

New South Wales

Queensland

Fishing methods

Commercial

Haul nets

Beach-seine nets

Trawl nets

Swinger nets

Longline

Mesh (gill) nets

Rod and line

Recreational

Rod and line

Mesh (gill) nets

Spearfishing

Indigenousa,b,c

Rod and line

Mesh (gill) nets

Spearfishing

Traditional apparatus

Management methods

Commercial

Limited entry

Size limits

Gear restrictions

Spatial closures

Vessel restrictions

Catch limits

Effort limits

Temporal closures

Bycatch limitsd

Recreational

Licence

e

Gear restrictions

Spatial closures

Temporal closures

Bag limits

Possession limits

Size limits

Indigenousa,b,f,g

Licence

e

Gear restrictions

Spatial closures

Temporal closures

Bag limits

Size limits

Section 37(1)(c1), Aboriginal cultural fishing authority

Active vessels

10 in GDSMF

2 in JASDGDLFM1

9 in JASDGDLFM2

2 in OA

2 in SBBSMNMF

4 in SBPMF

6 in SCEMF

2 in SWTMF

2 in WCDGDLIMF

22 in WCDSIMF

1 in WCEIMF

28 in LCF

16 in MSF

2 in PPBF

226 in EGF

16 in OFTF

19 in OHF

20 in OPTF

78 in OTLF

18 in ECIFFF

Catch

Commercial

3 t in GDSMF

2 t in JASDGDLFM1

3 t in JASDGDLFM2

<1 t in OA

<1 t in SBBSMNMF

<1 t in SBPMF

<1 t in SCEMF

<1 t in SWTMF

<1 t in WCDGDLIMF

4 t in WCDSIMF

<1 t in WCEIMF

115 t in LCF

3 t in MSF

<1 t in PPBF

41 t in EGF

<1 t in OFTF

8 t in OHF

<1 t in OPTF

15 t in OTLF

2 t in ECIFFF

Recreational

6 t (2011–12)

38 t (2007–08)

11 t (2000–01)

274 t (2000–01)

133 t (2010–11)

Indigenous

Unknown

Unknown

None

Unknown

Unknown

Markets

Domestic

Export


ECIFF = East Coast Inshore Fin Fish Fishery (Queensland); EGF = Estuary General Fishery (New South Wales); GDSMF = Gascoyne Demersal Scalefish Managed Fishery (Western Australia); JASDGDLFM1 = Joint Authority Southern Demersal Gillnet and Demersal Longline Managed Fishery Zone 1 (Western Australia); JASDGDLFM2 = Joint Authority Southern Demersal Gillnet and Demersal Longline Managed Fishery Zone 2 (Western Australia); LCF = Lakes and Coorong Fishery (South Australia); MSF = Marine Scalefish Fishery (South Australia); OA = Open Access – fishing not formally managed (Western Australia); OFTF = Ocean Fish Trawl Fishery (New South Wales); OHF = Ocean Hauling Fishery (New South Wales); OPTF = Ocean Prawn Trawl Fishery (New South Wales); OTLF = Ocean Trap and Line Fishery (New South Wales); PPBF = Port Phillip Bay Fishery (Victoria); SBBSMNMF = Shark Bay Beach Seine and Mesh Net Managed Fishery (Western Australia); SBPMF = Shark Bay Prawn Managed Fishery (Western Australia); SCEMF = South Coast Estuarine Managed Fishery (Western Australia); SWTMF = South-west Trawl Managed Fishery (Western Australia); WCDGDLIMF = West Coast Demersal Gillnet and Demersal Longline Interim Managed Fishery (Western Australia); WCDSIMF = West Coast Demersal Scalefish (Interim) Managed Fishery (Western Australia); WCEIMF = West Coast Estuarine (Interim) Managed Fishery (Western 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 Mulloway.

b In Queensland, under the Fisheries Act 1994 (Qld), Indigenous fishers in Queensland are able to use prescribed traditional and noncommercial 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 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.

d Fishers using meshnets in the New South Wales commercial Estuary General Fishery are permitted a bycatch allowance of 10 mulloway, between 45 and 70 cm per day.
e In Western Australia, a recreational fishing licence is required for boat-based fishing only.

f 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.

g 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).


Figure 2: Commercial catch of Mulloway in Australian waters, 2000 to 2013 (calendar years)
Figure 2: Commercial catch of Mulloway in Australian waters, 2000 to 2013 (calendar years)



Effects of fishing on the marine environment
  • Mulloway are targeted by commercial fisheries using mainly gill nets, hauling nets and line fishing. These activities are considered to pose a low risk to the physical environment (for example, substratum and benthic habitats)7,17.

  • Some bycatch may be expected from mesh nets used to target Mulloway, including the capture of small individuals of some species18,19. However, gill nets are relatively selective17.


Environmental effects on Mulloway
  • Estuaries are important nursery areas for Mulloway through the first 3–8 years of their life history16. The quality and availability of habitat and trophic resources for Mulloway in estuaries are largely dependent on the quality, magnitude, frequency and timing of seasonal freshwater inflows to estuaries, which affect recruitment and the availability of fish to estuarine-based fisheries.



a South Australian Research and Development Institute
b Department of Primary Industries, New South Wales
c Department of Agriculture, Fisheries a Forestry, Queensland
d Department of Fisheries, Western Australia
e Department of Environment and Primary Industries, Victoria