Coral Trout Plectropomus spp., Variola spp.

Malcolm Keaga, Stephen Newmanb, Nic Martonc and Thor Saundersd


Coral Trout
​Common coral trout (Plectropomus leopardus)

Table 1: Stock status determination for Coral Trout

Jurisdiction

Commonwealth

Northern Territory

Queensland

Western Australia

Stock

TSFF

Northern Territory

(CLF, FTO, TRF)

CRFFF

Gulf of Carpentaria

(DFFTF, GOCLF)

Western Australia (NDSMF, PFTIMF, PTMF, WCDSIMF)

Stock status

         

Sustainable

Undefined

Sustainable

Undefined

Undefined

Indicators

Management strategy evaluation

Catch

Quantitative stock assessment, catch

Catch, CPUE

Catch, CPUE


CPUE = catch per unit effort; CLF = Coastal Line Fishery (Northern Territory); CRFFF = Coral Reef Fin Fish Fishery (Queensland); DFFTF = Developmental Fin Fish Trawl Fishery (Queensland); FTO = Fishing Tour Operation (Northern Territory); GOCLF = Gulf of Carpentaria Line Fishery (Queensland); NDSMF = Northern Demersal Scalefish Managed Fishery (Western Australia); PFTIMF = Pilbara Fish Trawl Interim Managed Fishery (Western Australia); PTMF = Pilbara Trap Managed Fishery (Western Australia); TRF = Timor Reef Fishery (Northern Territory); TSFF = Torres Strait Finfish Fishery (Commonwealth); WCDSIMF = West Coast Demersal Scalefish (Interim) Managed Fishery (Western Australia)


Stock Structure

Assessments of Coral Trout take into account a species complex in the Commonwealth and Queensland jurisdictions. This complex comprises Common Coral Trout (Plectropomus leopardus), Barcheek Coral Trout (P. maculatus), Bluespotted Coral Trout (P. laevis), Passionfruit Coral Trout ( P. areolatus), Yellow-edge Coronation Trout (Variola louti) and White-edge Coronation Trout (V. albimarginata). In Western Australia, the Coral Trout species complex comprises Common Coral Trout, Barcheek Coral Trout, Yellow-edge Coronation Trout and White-edge Coronation Trout. The biological stock structure of Coral Trout species is spatially complex1–4 and remains uncertain; hence, status is reported at the management unit level rather than for individual biological stocks.


Stock Status

Torres Strait Finfish Fishery (Commonwealth) management unit

No formal stock assessment has been conducted in the Torres Strait Finfish Fishery (Commonwealth), but a management strategy evaluation5 tested four model simulations. All models estimated that biomass in 2004 was greater than 60 per cent of the unfished level, and that biomass would be greater than 70 per cent of the unfished level by 2025 at 2007 fishing levels. Catch in recent years has been below historical catch levels and well below the lowest catch level simulated in the management strategy evaluation (80 tonnes [t] per year). A catch simulation at 80 t suggested that Coral Trout biomass in the fishery would increase to greater than 80 per cent of the unfished biomass within 20 years5. Catch in the Torres Strait Finfish Fishery has declined from historical highs following a voluntary surrender process for all non-Traditional Inhabitant commercial operators in the Torres Strait Finfish Fisheries in 2005. In addition, complications with supply logistics (consistent supply of product to a point of landing) are likely to have negatively affected profitability and interest in the Torres Strait Finfish Fishery. Because fishers have limited access to freezing capacity, supply to processors has been inconsistent, leading to a negative impact on marketability and, in turn, prices and catches. The closure of a freezing facility on Murray Island in late 2010 contributed to this problem (Torres Strait Regional Authority, pers. comm., 2011).

The above evidence indicates that the biomass of this management unit stock is unlikely to be recruitment overfished6. The level of fishing pressure in recent years is unlikely to cause the management unit to become recruitment overfished6.

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

Northern Territory

The status of Coral Trout in the Northern Territory is unknown. Only small catches are reported from the Fishing Tour Operator sector, Coastal Line Fishery and Timor Reef Fishery7 .

On the basis of the evidence provided above, Coral Trout in the Northern Territory is classified as an undefined stock.  

Coral Reef Fin Fish Fishery (Queensland) management unit

Common Coral Trout dominates catches in the Coral Reef Fin Fish Fishery (Queensland)8. The most recent assessment of Common Coral Trout 8 estimated that the biomass in 2012 was 60 per cent of the unfished (1962) levels in areas open to fishing. Given this current biomass ratio of the predominant target species in the species complex, the Coral Trout stock is not considered to be recruitment overfished.

The most recent assessment8 estimates that current catch levels are lower than the estimated maximum sustainable yield for the stock. This 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.  

Gulf of Carpentaria (Queensland) management unit

Coral Trout is not a target species in Queensland-managed commercial fisheries in the Gulf of Carpentaria. They are taken as byproduct in the Developmental Fin Fish Trawl Fishery (Queensland) and Gulf of Carpentaria Line Fishery (Queensland), but only small catches are reported. Coral Trout is a popular recreational species for Gulf of Carpentaria residents and visiting fishers. Catch information was reported during the latest recreational survey; however, harvest levels were unreliable as a result of survey limitations (unpublished data from the Queensland Department of Agriculture, Fisheries and Forestry). Insufficient information is 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.  

Western Australia

Coral Trout is not a target species in the demersal fisheries of Western Australia but is landed as byproduct. Only small catches of Barcheek Coral Trout and Common Coral Trout are reported, and very small catches are reported for Yellow-edge Coronation Trout and White-edge Coronation Trout9 . Insufficient information is available to confidently classify the status of the Western Australian stock.

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


Table 2: Coral Trout biology10–14

Longevity and maximum size

17 years; ~800 mm FL

Maturity (50%)

~280 mm FL (female)
The species are protogynous hermaphrodites (born female and become male), with sex change occurring around 500 mm FL.

FL = fork length


Figure 1: Distribution of reported commercial catch of Coral Trout in Australian waters, 2013 (calendar year)
Figure 1: Distribution of reported commercial catch of Coral Trout in Australian waters, 2013 (calendar year)
Note: Data for the Northern Territory and Western Australia align with the 2013 calendar year, whereas data for the Commonwealth and Queensland align with the 2012–13 financial year.



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

Jurisdiction

Commonwealtha

Northern Territoryb

Queenslanda

Western Australiab

Fishing methods

Commercial

Hand line

Dropline

Rod and line

Fish trawl

Fish trap

Recreationalc

Hand line

Rod and line

Spearfishing

Indigenousd–f

Hand line

Rod and line

Spearfishing

Management methods

Commercial

Limited entry

Gear restrictions

Total allowable effort

Spatial zoningg

Size limits

Vessel restrictions

Catch restrictions

Spatial closures

Temporal closures

Recreationalc

Licensing

Gear restrictions

Possession limits

Size limits

Spatial closures

Temporal closures

Charter

Licensing

✓ (vessel)

Limited entry

Passenger restrictions

Spatial zoningg

Gear restrictions

Possession limits

Bag limits

Size limits

Spatial closures

Temporal closures

Indigenousd–f

Laws of general application apply

Spatial closures

Active vessels

1 in TSFF

9 in CLF

114 in FTO (2012)

8 in TRF

181 in CRFFF

1 in DFFTF

0 in GOCLF

7 in NDSMF

3 in PFTIMF

2 in PTMF

22 in WCDSIMF

Catch

Commercial

22 t in TSFF

0.2 t in CLF

0.6 t in TRF

750 t in CRFFF

<1 t in DFFTF

0 t in GOCLF

7 t in NDSMF

5 t in PFTIMF

3 t in PTMF

2 t in WCDSIMF

Recreationalc

2.8 t (2010)

0.7 t in FTO (2012)

196 000 fish (~200 t) (2010)

9034 fish (~22 t) (2011–12)16

Charter

61 t

1915 fish (~5 t)

Indigenousd,e

Negligible

Unknown

Unknown

Markets

Domestic

Export


CLF = Coastal Line Fishery (Northern Territory); CRFFF = Coral Reef Fin Fish Fishery (Queensland); DFFTF = Developmental Fin Fish Trawl Fishery (Queensland); FTO = Fishing Tour Operation (Northern Territory); GOCLF = Gulf of Carpentaria Line Fishery (Queensland); NDSMF = Northern Demersal Scalefish Managed Fishery (Western Australia); PFTIMF = Pilbara Fish Trawl Interim Managed Fishery (Western Australia); PTMF = Pilbara Trap Managed Fishery (Western Australia); TRF = Timor Reef Fishery (Northern Territory); TSFF = Torres Strait Finfish Fishery (Commonwealth); WCDSIMF = West Coast Demersal Scalefish (Interim) Managed Fishery (Western Australia)

a Data provided for the Commonwealth and Queensland align with the 2012–13 financial year.

b Data provided for the Northern Territory and Western Australia align with the 2013 calendar year.

c The Australian Government does not manage recreational fishing in Commonwealth waters. Recreational fishing in Commonwealth waters is managed by the state or territory immediately adjacent to those waters, under its management regulations.

d The Australian Government does not manage noncommercial Indigenous fishing in Commonwealth waters (with the exception of the Torres Strait). In general, noncommercial Indigenous fishing in Commonwealth waters is managed by the state or territory immediately adjacent to those waters. In the Torres Strait, both commercial and noncommercial Indigenous fishing is managed by the Torres Strait Protected Zone Joint Authority (PZJA) through the Australian Fisheries Management Authority (Commonwealth); the Department of Agriculture, Fisheries and Forestry (Queensland); and the Torres Strait Regional Authority. The PZJA also manages non-Indigenous commercial fishing in the Torres Strait.

e 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.

f 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.

g In Western Australia, different zones within fisheries may have different effort allocations.


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

Figure 2: Commercial catch of Coral Trout in Australian waters, 2000 to 2013 (calendar years)
Note: Data for the Northern Territory and Western Australia are reported by calendar year, whereas data for the Commonwealth and Queensland are by financial year




Effects of fishing on the marine environment
  • There were no reported interactions with protected species by the Torres Strait Finfish Fishery (Commonwealth) in 2013, or the Coral Reef Fin Fish Fishery (Queensland) in the 2012–13 fishing season, indicating that the impact of these fisheries on protected species is low.

  • Line fishing for Coral Trout is likely to have little direct effect on the marine environment17. However, there is evidence that the removal of predators (including Coral Trout) can lead to an increase in the abundance of their prey species, which is indicative of food web changes17. The impacts of this are unknown.

  • Commercial trawl gear used in the Northern Territory has the potential to impact on the benthic habitat. However, trawl nets in the Northern Territory have been designed to fish off the seabed, reducing interaction with benthic habitats18. The trawl fishery in the Northern Territory comprises a very small fleet and only fishes about 7 per cent of the available area18.


Environmental effects on Coral Trout
  • The most recent Queensland Coral Trout stock assessment8 notes the impact of cyclones on reducing Coral Trout catch rates. Tobin et al. (2010)19 reported on the effects of three tropical cyclones on the Coral Reef Fin Fish Fishery industry, including a decrease in Coral Trout catch rates of around one-third in regions with the most structural reef damage. The destruction, scouring and displacement of reef habitat were significant and widespread across large areas of the reef. In addition to the structural reef damage, commercial fishers reported reduced catch rates of all species throughout the directly impacted areas19. The analysis identifies depressed catch rates for 12–24 months in affected areas following cyclones.

  • Climate change impacts are a concern for coral reef ecosystems. Climate change has been linked to changes in ocean chemistry, and increases in the frequency and extent of coral bleaching events20. These events can also affect the replenishment rates of coral reef fin fish populations, individual growth rates21 and spawning output22,23 , and may influence the geographic distribution of coral reef species (for example, latitudinal shifts in distribution).



a Department of Agriculture, Fisheries and Forestry, Queensland
b Department of Fisheries, Western Australia
c Australian Bureau of Agricultural and Resource Economics and Sciences
d Department of Primary Industries and Fisheries, Northern Territory