Sea Mullet Mugil cephalus

John Stewarta, Andrew Prosserb and Kim Smithc


Sea Mullet

Table 1: Stock status determination for Sea Mullet

Jurisdiction

New South Wales, Queensland

Western Australia

Stock

Eastern Australian
(ECIFFF, EGF, OHF)

Western Australian
(EF, EGBSMNMF, SBBSMNMF, SCEMF, WCBBFNMF, WCEIMF)

Stock status

 

 

Sustainable

Sustainable

Indicators

Catch, CPUE, length and age frequencies

Catch, CPUE


CPUE = catch per unit effort; ECIFFF = East Coast Inshore Fin Fish Fishery (Queensland); EF = Estuaries Fisheries (Condition) (Western Australia); EGBSMNMF = Exmouth Gulf Beach Seine and Mesh Net Managed Fishery (Western Australia); EGF = Estuary General Fishery (New South Wales); OHF = Ocean Hauling Fishery (New South Wales); SBBSMNMF = Shark Bay Beach Seine and Mesh Net Managed Fishery (Western Australia); SCEMF = South Coast Estuarine Managed Fishery (Western Australia); WCBBFNMF = West Coast (Beach Bait Fish Net) Managed Fishery (Western Australia); WCEIMF = West Coast Estuarine (Interim) Managed Fishery (Western Australia)


Stock Structure

Results of extensive tagging studies1 suggest a single east coast biological stock of Sea Mullet, extending from central Queensland to eastern Victoria. The biological stock structure of Sea Mullet off Western Australia is likely to be complex, although limited tagging and genetic studies 2,3 suggest mixing of fish throughout the lower west coast region, where the majority of the catch is taken. Therefore, a single Western Australian biological stock is assumed here. Stock status for Sea Mullet is reported at the level of individual biological stocks.


Stock Status

Eastern Australian biological stock

The cross-jurisdictional eastern Australian biological stock has components in New South Wales and Queensland. Each jurisdiction assesses the 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 both jurisdictions.

The New South Wales component of the eastern Australian biological stock is assessed annually in terms of landings and catch rates in both the estuary and ocean fisheries4. The annual spawning run fishery on ocean beaches is assessed in terms of fish sizes and ages in landings. Commercial median catch rates have remained stable in the estuary fishery (kilograms per day of mesh netting) and increased slightly in the ocean fishery (kilograms per day of beach hauling) since the early 1980s. The size compositions of fish in ocean landings have remained stable, while the age composition of fish in this fishery is generally between 2 and 5 years, with some variations in year-class strength. The above evidence indicates that the biomass of this part of the stock is unlikely to be recruitment overfished.

Landings in New South Wales in 2013 (2133 tonnes [t]) were well below the long-term annual average (around 3000 t). The reported number of fisher-days in the ocean fishery in 2013 was at a historical low of approximately 650 days. Typical length-frequency compositions were found in landings in 2013. Age compositions in 2011 (the most recent year analysed for age compositions) suggest no large changes in the stock, with most fish being 3–5 years of age. The above evidence indicates that the current level of fishing pressure is unlikely to cause this part of the stock to become recruitment overfished.

The Queensland component of the eastern Australian biological stock has a long history of stable commercial landings. In 2013, 2109 t was reported landed, which is above the long-term average of around 2000 t. Length-frequency information from routine monitoring shows stable distributions of fish sizes harvested by the Queensland fishery. Age-frequency information shows that fish from 3 to 5 years of age dominate catches, but older fish are present. Recruitment has been consistent, with evidence of recent strong year-classes. The above evidence indicates that the biomass of the Queensland component of this stock is unlikely to be recruitment overfished.

Nominal effort in the Queensland component of the fishery has been stable at around 9000 days for the past 5 years, and the number of fishers reporting mullet (unspecified) catch has decreased from 319 fishers in 2009 to 285 fishers in 2013. This decline is expected to continue with planned net licence buy-backs. Length-frequency information shows stable patterns, and catch is well above minimum legal size. Age-frequency information shows continued recruitment to the fishery and evidence of strong year-classes. Estimates of fishing mortality are high compared with estimates of natural mortality, but show a stable trend in combination with consistent catches. The above evidence indicates that the current level of fishing pressure is unlikely to cause the Queensland component of the biological stock to become recruitment overfished.

On the basis of the evidence provided above, the entire biological stock is classified as a sustainable stock.  

Western Australian biological stock

Sea Mullet occurs in all coastal regions of Western Australia, but commercial targeting of the species is mainly restricted to waters from Shark Bay southwards. Sea Mullet is managed separately in the four Western Australian bioregions, although the level of connectivity between the different populations is unknown5. The total catch of Sea Mullet in Western Australia has declined since the 1990s, as a consequence of commercial effort reductions in coastal and estuarine areas, attributable to licence buy-backs and spatial closures. The above evidence indicates that the current level of fishing pressure is unlikely to cause the stock to become recruitment overfished.

The assessment for Sea Mullet is based on trends in catches and catch rates in the three main fisheries (Shark Bay Beach Seine and Mesh Net Managed Fishery, South Coast Estuarine Managed Fishery, and West Coast Estuarine [Interim] Managed Fishery) that capture around 80 per cent of the total commercial catch. Catch rates in these fisheries were relatively stable over the period 1980 to 2000, and have increased since 2000. These trends suggest long-term stability in Sea Mullet abundance in each bioregion, with a slight increase in recent years. The above evidence indicates that the biomass of this stock is unlikely to be recruitment overfished.

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


Table 2: Sea Mullet biology6–9

Longevity and maximum size

Eastern Australia: 16 years; 640 mm FL
Western Australia: males 8 years; females 12 years
790 mm FL

Maturity (50%)

Eastern Australia: males 330 mm FL; females 370 mm FL Western Australia: both sexes 370 mm TL

FL = fork length; TL = total length


Figure 1: Distribution of reported commercial catch of Sea Mullet in Australian waters, 2010
Figure 1: Distribution of reported commercial catch of Sea Mullet in Australian waters, 2013 (calendar year)



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

Jurisdiction

New South Wales

Queensland

Western Australia

Fishing methods

Commercial

Gillnet

Beach-seine net

Tunnel net

Haul net

Recreational

Rod and line

Bait trap

Nets

Cast netting

Bait (seine) netting

Indigenousa

Rod and line

Bait trap

Management methods

Commercial

Limited entry

Size limits

Gear restrictions

Temporal closures

Spatial closures

Vessel restrictions

Recreational

Bag limits

Possession limits

Size limits

Licensing

Gear restrictions

Spatial closures

Indigenousb,c,d

Bag limits

Size limits

Spatial closures

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

Gear restrictionsa

Active vessels

 

299 in EGF

53 in OHF

285 in ECIFFF

27 in open access

2 in EF

2 in EGBSMNMF

7 in SBBSMNMF

23 in SCEMF

1 in WCBBFNMF

10 in WCEIMF

Catch

Commercial

1140 t in EGF

1000 t in OHF

2109 t in ECIFFF

30 t in open access

4 t in EF

<1 t in EGBSMNMF

32 t in SBBSMNMF

32 t in SCEMF

<0.5 t in WCBBFNMF

68 t in WCEIMF

Recreational

Negligible

Negligible

<0.5 t

Indigenous

Unknown

Unknown

Unknown

Markets

Domestic

Export


ECIFFF = East Coast Inshore Fin Fish Fishery (Queensland); EF = Estuaries Fisheries (Condition) (Western Australia); EGBSMNMF = Exmouth Gulf Beach Seine and Mesh Net Managed Fishery (Western Australia); EGF = Estuary General Fishery (New South Wales); OHF = Ocean Hauling Fishery (New South Wales); SBBSMNMF = Shark Bay Beach Seine and Mesh Net Managed Fishery (Western Australia); SCEMF = South Coast Estuarine Managed Fishery (Western Australia); WCBBFNMF = West Coast (Beach Bait Fish Net) Managed Fishery (Western Australia); WCEIMF = West Coast Estuarine (Interim) Managed Fishery (Western Australia)

a 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.

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.


2a) a) Commercial catch of Sea Mullet in Australian waters, 2000–10 (calendar year)
Figure 2: Commercial catch of Sea Mullet in Australian waters, 2000 to 2013 (calendar years)



Effects of fishing on the marine environment
  • The main fisheries for Sea Mullet use beach seining. This fishing method is highly targeted and, as a result, there is very little bycatch in these fisheries10. In Queensland, byproduct caught in estuarine gillnets in the Sea Mullet fishery comprises less than 20 per cent by number, and much of this is retained and marketed11.


Environmental effects on Sea Mullet
  • Sea Mullet penetrate far up rivers, often into fresh water, and barriers to fish passage (such as weirs and dams) can reduce the amount of habitat available to the species. Being highly dependent on riverine and estuarine habitats, Sea Mullet populations are vulnerable to fluctuations in water quality. Eutrophication and hypoxia can cause significant fish kills.



a Department of Primary Industries, New South Wales
b Department of Agriculture, Fisheries and Forestry, Queensland
c Department of Fisheries, Western Australia