Barramundi Lates calcarifer

Thor Saundersa, Stephen Newmanb and Olivia Whybirdc


Barramundi

Table 1: Stock status determination for Barramundi

Jurisdiction

Northern Territory

Western Australia

Stock

BF

KGBMF

Stock status

   

Sustainable

Sustainable

Indicators

Catch, CPUE, length and age frequencies, harvest rate

Catch, CPUE


BF = Barramundi Fishery (Northern Territory); CPUE = catch per unit effort; KGBMF = Kimberley Gillnet and Barramundi Managed Fishery (Western Australia)

 

Table 1 continued

Jurisdiction

Queensland

Stock

Southern Gulf of Carpentaria

(GOCIFFF)

Northern Gulf of Carpentaria

(GOCIFFF)

Princess Charlotte Bay

(ECIFFF)

North-east coast

(ECIFFF)

Mackay

(ECIFFF)

Central east coast

(ECIFFF)

South-east coast (ECIFFF)

Stock status

             

Sustainable

Sustainable

Sustainable

Sustainable

Sustainable

Sustainable

Negligiblea

Indicators

Catch, length and age frequencies, mortality rates

Catch

Catch

Catch, length and age frequencies, mortality rates

Catch, CPUE

Catch, length and age frequencies

Catch


CPUE = catch per unit effort; ECIFFF = East Coast Inshore Fin Fish Fishery (Queensland); GOCIFFF = Gulf of Carpentaria Inshore Fin Fish Fishery (Queensland)

a 'Negligible' means historically low catch; no stock status. There was no catch from the south-east coast in 2013: in the past 10 years, the average catch from this biological stock was 769 kg.


Stock Structure

Separate biological stocks of Barramundi exist at the scale of individual catchments across northern Australia1,2. However, the difficulty in obtaining relevant biological and catch-and-effort information to assess each individual biological stock has meant that Barramundi have been assessed as two separate management units (Northern Territory and Western Australia) and seven genetic biological stocks (Queensland: Southern Gulf of Carpentaria, Northern Gulf of Carpentaria, Princess Charlotte Bay, north-east Coast, Mackay, central east coast and south-east coast). The assessments of the management units are based on the biological stocks that receive the highest harvest rates, whose status is assumed to be representative of the highest level of exploitation that occurs on any biological stock within each unit. In Queensland, many catchments are stocked with fingerlings, particularly on the east coast. However, stocking is with fish from hatcheries using parents from the same genetic stock, so it is unlikely that this process has compromised the above stock structure.


Stock Status

Barramundi Fishery (Northern Territory) management unit

Commercial catches in the Barramundi Fishery (Northern Territory) are stable and well within historical levels, and monitored stocks have a healthy size and age distribution3. Catch rates have increased over the past 5 years. However, there was a substantial decrease in the 2013 rate, associated with a poor wet season and several experienced operators selling their licences. Recaptures from tagging programs suggest that the annual harvest rate from all sectors combined is consistently below 5 per cent. Abundance surveys indicate high levels of recruitment during high-rainfall wet seasons3. The above evidence indicates that the stocks in this management unit are unlikely to be recruitment overfished and that current catch levels are unlikely to cause the stocks to become recruitment overfished.

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

Kimberley Gillnet and Barramundi Managed Fishery (Western Australia) management unit

The harvest strategy for Barramundi in the Kimberley Gillnet and Barramundi Managed Fishery in the Kimberley region of Western Australia is based on a constant commercial catch policy where the annual commercial catches of Barramundi are allowed to vary within the target catch range, which is based on a historical catch range that has been shown not to impair recruitment. The threshold values have been calculated as being within the range 33–44 tonnes (t), with a limit reference range of 23–54 t4.

The Barramundi catch in 2013 was 52.1 t, above the target catch range but below the limit range. The increase in catch was due to an increase in fishing effort in two sectors of the fishery (the Kimberley Coast and Broome). The increased catch was obtained with high catch rates (kg/block day) across the fishery, indicating that it was not a direct result of a declining stock biomass for Barramundi. Furthermore, in 2013, two licences were removed from the Broome sector of the fishery4, which is now only open to recreational and Indigenous fishing. This effort removal is likely to reduce levels of catch in future years. The above evidence indicates that the biomass of the stocks in this management unit is unlikely to be recruitment overfished and that current levels of fishing mortality (catch) are unlikely to cause the stocks to become recruitment overfished.

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

Southern Gulf of Carpentaria biological stock

The southern Gulf of Carpentaria contributes almost the entire Gulf of Carpentaria Inshore Fin Fish Fishery (Qld) commercial harvest and receives the greatest fishing pressure5. Biological monitoring and anecdotal reports indicate good numbers of large fish present in the stock. Total mortality rate estimates are stable, and fishing mortality rates have been less than natural mortality rates for the past 4 years5. Commercial catches of Barramundi have been increasing since 1992 and reached record levels in 20115. However, the Barramundi commercial harvest in 2013 was almost 51 per cent lower than in 2011, and the lowest since 20055. This was likely to be due partly to poor seasonal river flows, which are known to affect catchability of Barramundi6. Age-structure monitoring indicates a stock with varied but continual recruitment. Low recruitment in 2012 and 2013, possibly due to low river flows in those years, prevented 3- and 4-year-olds from fully recruiting to the estuarine fishery6. Queensland size limits, and seasonal and spatial closures for Barramundi ensure that a large proportion of the spawning stock is protected. As a result, the biomass of the Southern Gulf of Carpentaria biological stock is not considered to be recruitment overfished, and current fishing mortality is unlikely to cause the biological stock to become recruitment overfished.

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

Northern Gulf of Carpentaria biological stock

Commercial catches of the northern Gulf of Carpentaria biological stock are small and variable, as the small river systems in this area are unlikely to support a large stock of Barramundi5. Biological evidence indicates that the growth rate of fish in this stock may be slower and fish mature earlier than in other stocks and management units7, such that the size limits protect a larger proportion of the spawning population5 . Catch from this stock has declined since 2010, mainly as a result of reductions in fishing effort for economic reasons5. There has been a rising trend in catch rate over the past 20 years, which indicates that the biomass of this stock is unlikely to be recruitment overfished (unpublished data from the Queensland Department of Agriculture, Fisheries and Forestry). The above evidence indicates that this stock is unlikely to be recruitment overfished and 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 biological stock is classified as a sustainable stock.

Princess Charlotte Bay biological stock

Commercial catches of the Princess Charlotte Bay stock are small (4 per cent of the catch of the East Coast Inshore Fin Fish Fishery)5. Numbers of commercial operators in the Princess Charlotte Bay region have halved since 2008 to just five operators reporting catches in 2013. Spatial closures introduced in 2009, seasonal closures and size limits protect significant parts of the Princess Charlotte Bay spawning stock from commercial fishing. The catch history since 1993 is relatively stable, and catch rates have increased5. The above evidence indicates that the biomass of the Princess Charlotte Bay biological stock is not considered to be recruitment overfished and current fishing mortality is unlikely to cause the biological stock to become recruitment overfished.

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

North-east coast biological stock

The north-east coast stock represents approximately 24 per cent of the 2013 Barramundi harvest on the Queensland east coast5. Summer rainfall and flow rates have had a positive effect on catches from this stock, both immediately on catchability and through a 3–4-year lag effect on enhanced recruitment8. Biological monitoring and anecdotal reports indicate relatively stable length and age structures over time, and good numbers of large fish are present in the stock5. Total mortality rate estimates are stable, and fishing mortality rates are less than natural mortality rates5. Although commercial catches have declined since 2011, this has been predominantly due to poor seasonal river flows. Queensland size limits, and seasonal and spatial closures for Barramundi ensure that a large proportion of the spawning stock is protected. As a result, the biomass of the north-east coast stock is not considered to be recruitment overfished, and current fishing mortality is unlikely to cause the biological stock to become recruitment overfished.

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

Mackay biological stock

Commercial catches in the Mackay stock represent around 20 per cent of the East Coast Inshore Fin Fish Fishery (Qld) catch5. The catch history has been relatively stable over time, with a slight increasing trend; catch rates show a similar but somewhat stronger upward trend5. Queensland size limits, and seasonal and spatial closures for Barramundi ensure that a large proportion of the spawning stock is protected. The above evidence indicates that the biomass of the biological stock is not considered to be recruitment overfished and current fishing pressure is unlikely to cause the Mackay biological stock to become recruitment overfished.

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

Central east coast biological stock

The central east coast is the major stock on the Queensland east coast, comprising 53 per cent of the 2013 East Coast Inshore Fin Fish Fishery (Qld) catch. In 2011, there was a fivefold increase in commercial catch, which has remained at high levels5. These high catches were due to stocked fish from Lake Awoonga moving into the Gladstone area following a flood in late 2010 to early 2011. Two subsequent high river flow years increased catchability in both the Gladstone area and Fitzroy River, with strong year-classes entering these systems during this time. Fishery-dependent monitoring shows stable length and age structures5. Queensland size limits, and seasonal and spatial closures for Barramundi ensure that a large proportion of the spawning stock is protected. The above evidence indicates that the biomass of the central east coast biological stock is not considered to be recruitment overfished and current fishing mortality is unlikely to cause 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 2: Barramundi biology7

Longevity and maximum size

35 years; 1500 mm TL

Maturity (50%)

Northern Territory: males 2–5 years, 730 mm TL; females 5–7 years, 910 mm TL

Queensland: males 2–5 years, 640 mm TL; females 5–7 years, 820 mm TL


TL = total length; estimates not available for Western Australia


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



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

Jurisdiction

Northern Territory

Queensland

Western Australia

Fishing methods

Commercial

Gillnet

Recreational

Rod and line

Spearfishing

Indigenousa,b

Spearfishing

Hand line

Management methods

Commercial

Size limits

Limited entry

Spatial zoning

Vessel restrictions

Catch limits

Spatial closures

Temporal closures

Gear restrictions

Recreational

Temporal closures

Licensing

Spatial closures

Size limits

Bag limits

Possession limits

Gear restrictions

Charter

Limited entry

Spatial zoning

Passenger restrictions

Size limits

Bag limits

Possession limits

Spatial closures

Seasonal closures

Indigenousa,b

Laws of general application

Active vessels

 

17 in BF

71 in southern Gulf of Carpentaria (GOCIFF)

<5 in northern Gulf of Carpentaria (GOCIFFF)

5 in Princess Charlotte Bay (ECIFFF)

68 in north-east coast (ECIFFF)

48 in Mackay (ECIFFF)

53 in central east coast (ECIFFF)

6 in KGBMF

Catch

Commercial

433 t in BF

492 t in southern Gulf of Carpentaria (GOCIFF)

Northern Gulf of Carpentaria (GOCIFFF) not reportablec

16 t in Princess Charlotte Bay (ECIFFF)

93 t in north-east coast (ECIFFF)

78 t in Mackay (ECIFFF)

211 t in central east coast (ECIFFF)

52 t in KGBMF

Recreational

155 t (2010)

181 ± 31 td (2010–11)9

2.1 –9 te (2011–12)10

Charter

34 t FTO (2012)

Included in recreational estimate

1–4 t

Indigenous

110 t (2000)

Unknown

Unknown

Markets

Domestic

Export


BF = Barramundi Fishery (Northern Territory); ECIFFF = East Coast Inshore Fin Fish Fishery (Queensland); FTO = Fishing Tour Operator (Northern Territory); GOCIFFF = Gulf of Carpentaria Inshore Fin Fish Fishery (Queensland); KGBMF = Kimberley Gillnet and Barramundi 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 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.

c Northern Gulf of Carpentaria catch is not reportable as fewer than five boats operated in the fishery in 2013.

d Survey of Queensland residents only9

e Recreational catch estimates for Barramundi will be underestimates as they were derived from boat-based fishers; shore-based fishers and boat-based fishers that fished only in fresh water were out of scope of the 2011–12 survey10.


Figure 2: Commercial catch of Barramundi in Australian waters, 1993 to 2013 (calendar years)
Figure 2: Commercial catch of Barramundi in Australian waters, 1993 to 2013 (calendar years)

Note: Northern Gulf of Carpentaria catch is not reportable from 2007 to 2011, and for 2013 because fewer than five boats operated in the fishery.




Effects of fishing on the marine environment
  • Commercial gillnets have limited direct impact on the environment and are quite selective, with bycatch making up only a small proportion of the catch11. However, commercial gillnets do interact with threatened, endangered and protected species. Although reported interactions are low, the impact on the populations of these species is unknown3,5,11.

Environmental effects on Barramundi
  • The duration, magnitude and timing of the wet season strongly drives biomass and harvest of Barramundi stocks, with large wet seasons resulting in higher recruitment than smaller wet seasons6,8,12.


a Department of Primary Industry and Fisheries, Northern Territory
b Department of Fisheries, Western Australia
c Department of Agriculture, Fisheries and Forestry, Queensland