Golden Snapper Lutjanus johnii

Thor Saundersa, Stephen Newmanb, Malcolm Keagc and Chris Erritya


Golden Snapper

Table 1: Stock status determination for Golden Snapper

Jurisdiction

Northern Territory

Western Australia

Queensland

Stock

Northern Territory

(CLF, DF, FTO, TRF)

Western Australia

(NDSMF, PTMF)

Gulf of Carpentaria

(GOCDFFTF, GOCLF)

East coast

(ECIFFF)

Stock status

       

Overfished

Undefined

Undefined

Undefined

Indicators

Catch, biomass, egg production

Catch

Catch, standardised CPUE, observer surveys

Catch, performance indicators


CLF = Coastal Line Fishery (Northern Territory); CPUE = catch per unit effort; DF = Demersal Fishery (Northern Territory); ECIFFF = East Coast Inshore Fin Fish Fishery (Queensland); FTO = Fishing Tour Operator (Northern Territory); GOCDFFTF = Gulf of Carpentaria Developmental Fin Fish Trawl Fishery (Queensland); GOCLF = Gulf of Carpentaria Line Fishery (Queensland); NDSMF = Northern Demersal Scalefish Managed Fishery (Western Australia); PTMF = Pilbara Trap Managed Fishery (Western Australia); TRF = Timor Reef Fishery (Northern Territory)


Stock Structure

Golden Snapper is a widespread Indo–Pacific species that is found from the Pilbara region in Western Australia across Northern Australia to the east coast of Queensland. The biological stock structure for this species is currently under investigation and undefined. As a result, status in this chapter is reported at the jurisdiction level for the Northern Territory and Western Australia, and the management unit level for Queensland. In Queensland, the Gulf of Carpentaria is considered a single management unit, comprising two separate fisheries.


Stock Status

Northern Territory 

The most recent assessment (2011) estimated biomass of Golden Snapper in the Northern Territory to be approximately 25 per cent of unfished spawning stock biomass, which is below conventional target levels, and egg production to be at approximately 10 per cent of unfished levels, which is below conventional limit levels1. The assessments are driven by the populations that receive the highest harvest rates, so the status for the Northern Territory can be assumed to be representative of the highest level of exploitation that occurs on any population. The immediate area of concern is in waters around Darwin, where most of the fishing pressure occurs and where abundance, catch and catch rate have substantially declined over the past 10 years2. It is likely that populations of Golden Snapper exist in the Northern Territory that are not overfished because they have been subject to low fishing pressure. However, these still require identification in the current stock structure study for this species. Until this knowledge is gained, the modelling for Golden Snapper has been carried out assuming a single stock for the jurisdiction; hence the stock status is reported at this scale. Subsequent reports are likely to include a number of different stocks, with a variety of status classifications, within the Northern Territory. This precautionary approach has been taken because Golden Snapper has vulnerable life history traits (slow growth, late maturity, high longevity) and is highly susceptible to barotrauma when caught in waters deeper than 10 metres2,3. All of this evidence indicates that the stock is likely to be recruitment overfished. Declining catch rates at low stock size indicate that the current level of fishing pressure is likely to prevent the stock recovering from a recruitment overfished state.

On the basis of the evidence provided above, Golden Snapper in the Northern Territory is classified as an overfished stock.  

Western Australia 

Golden Snapper is not a commercial target species in the demersal fisheries of Western Australia, but is landed in small quantities as byproduct. Golden Snapper are landed by recreational and charter fishers, primarily in the Kimberley region of Western Australia, but only in small quantities 4 . Because of the low level of take of Golden Snapper in Western Australia, which occurs across a limited area of the distribution of the species, it is unlikely that Golden Snapper in Western Australia is recruitment overfished, or that the level of fishing mortality is likely to cause the stock to become recruitment overfished. However, insufficient information is available to confidently classify the status of this stock.

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

Gulf of Carpentaria (Queensland) management unit 

In the Gulf of Carpentaria management unit, Golden Snapper is mainly harvested by the commercial sector. There is no reliable estimate of recreational harvest. Harvest from the adjacent Northern Territory jurisdiction has been low in recent years.

Queensland commercial catches remained stable at 20–35 tonnes (t) over the decade to 2011, with most fish taken by the Gulf of Carpentaria Developmental Fin Fish Trawl Fishery rather than the Gulf of Carpentaria Line Fishery, where participants primarily target Spanish Mackerel. Fish trawl effort in the Gulf of Carpentaria declined markedly in 2012 as a result of trawl effort being transferred to areas in the Northern Territory (outside the Gulf).

No stock assessment has been undertaken to estimate current biomass in relation to unfished biomass. However, standardised catch rates (calculated to 2009) in the trawl fishery showed significant declines after 2006, to approximately half the long-term average5. Observer surveys over the period 2004 to 2006 showed that most Golden Snapper caught in the Gulf of Carpentaria Developmental Fin Fish Trawl Fishery were also smaller than the size at maturity (unpublished data). Overall, there is insufficient information available to confidently classify the status of this stock.

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

East coast (Queensland) management unit  

No stock assessment has been undertaken to estimate current biomass in relation to unfished biomass in the Queensland east coast management unit. Golden Snapper is mainly harvested by the recreational sector.

Recreational harvest remained stable between estimates derived in 2000 (approximately 15 000 fish) and 2010 (approximately 14 000 fish)6. According to the 2010 survey, almost as many recreationally caught fish were released as were retained. Given the issues with barotrauma raised above, the actual harvest by this sector is likely to be higher.

The species is taken as byproduct in the East Coast Inshore Fin Fish Fishery, predominantly by net. Annual commercial catches increased from less than 1 t per year from 2000 to 2008, to a peak of 8 t in 2011. Catches in 2012 and 2013 declined from this peak, and in 2013 the catch was approximately 1 t.

No indices of abundance have been estimated, and insufficient information is available to confidently classify the status of the stock.

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


Table 2: Golden Snapper biology7,8

Longevity and maximum size

30 years; 900 mm TL, 15 kg

Maturity (50%)

Northern Territory: males 520 mm TL (7 years), females 560 mm TL (8 years)

Cape York: males 620 mm FL (9 years), females 640 mm (6 years)

North Queenslanda: males 590 mm (6 years), females 690 mm (10 years)


FL = fork length; TL = total length

a North Queensland refers to samples from Cairns to Townsville.


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

Note: Queensland east coast catch is reported by financial year.




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

Jurisdiction

Northern Territory

Queensland

Western Australia

Fishing methods

Commercial

Fish trawl

Fish trap

Hand line

Rod and line

Recreational

Rod and line

Spearfishing

Indigenousa,b

Hand line

Management methods

Commercial

Limited entry

Spatial zoning

Size limits

✓ (not in GOCDFFTF)

Vessel restrictions

Gear restrictions

Total allowable catch

✓ (GOCDFFTF)

Total allowable effort

Effort limits

Spatial closures

Recreational

Licences

Possession limits

Bag limits

Size limits

Spatial closures

Charter

Licences

✓ (vessel)

Limited entry

Spatial zoning

Passenger restrictions

Possession limits

Size limits

Bag limits

Spatial closures

Indigenousa,b

Laws of general application

Active vessels

 

9 in CLF

9 in DF

8 in TRF

7 in ECIFFF

1 in GOCDFFTF

1 in GOCLF

1 in NDSMF

1 in PTMF

Catch

Commercial

7 t in CLF

22 t in DF

2 t in TRF

1.5 t in ECIFFF

0.2 t in GOCDFFTF

0.2 t in GOCLF

<0.1 t in NDSMF

<0.1 t in PTMF

Recreational

72 t (2010)

33 t (2010)

1490 fish (2011–12); ~2 t9

Charter

10 t in FTO

0.2 t

2598 fish; ~4 t

Indigenous

Unknown

Unknown

Unknown

Markets

Domestic

Export


CLF = Coastal Line Fishery (Northern Territory); DF = Demersal Fishery (Northern Territory); ECIFFF = East Coast Inshore Fin Fish Fishery (Queensland); FTO = Fishing Tour Operator (Northern Territory); GOCDFFTF = Gulf of Carpentaria Developmental Fin Fish Trawl Fishery (Queensland); GOCLF = Gulf of Carpentaria Line Fishery (Queensland); NDSMF = Northern Demersal Scalefish Managed Fishery (Western Australia); PTMF = Pilbara Trap Managed Fishery (Western Australia); TRF = Timor Reef Fishery (Northern Territory)

Note: ECIFFF catch is reported by financial year.

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.  


Figure 2: Commercial catch of Golden Snapper in Australian waters, 1999 to 2013 (calendar years)
Figure 2: Commercial catch of Golden Snapper in Australian waters, 1999 to 2013 (calendar years)

Note: Queensland east coast catch is reported by financial year.




Effects of fishing on the marine environment
  • Golden Snapper is mainly targeted in all sectors by fishers using hand lines, and rod and lines. Beyond the catch of target and a small quantity of bycatch species, there is little evidence to suggest that this gear significantly impacts on benthic or pelagic ecological communities.

  • Commercial trawl gear used in the Northern Territory and Queensland has the potential to impact on the benthic habitat. However, trawl nets in these waters have been designed to fish off the seabed, reducing interaction with benthic habitats4. Additionally, the trawl fleet is very small and only fishes about 7 per cent of the available area10.


Environmental effects on Golden Snapper
  • The impact of environmental factors on Golden Snapper stocks is largely unknown. However, the juvenile and larval phases of this species inhabit estuaries and coastal bays, making these phases of the life cycle vulnerable to changes in ocean current, strength and direction; rainfall; river flow; water temperature; salinity; and pH3.



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