Western King Prawn Melicertus latisulcatus

Mervi  Kangasa  and Cameron Dixonb


Western King Prawn

Table 1: Stock status determination for Western King Prawn

Jurisdiction

Western Australia

South Australia

Stock

SBPMF

EGPMF

North coast prawn managed fisheries (BPMF, KPMF, NBPMF, OPMF)

SWTMF

SGPF

GSVPF

WCPF

Stock status

 

 

 

 

 

 

Sustainable

Sustainable

Sustainable

Sustainable

Sustainable

Sustainable

Transitional–
recovering

Indicators

Catch

Catch

Catch

Catch

Survey catch rates, catch

Survey catch rates, catch

Survey catch rates, catch

BPMF = Broome Prawn Managed Fishery (Western Australia); EGPMF = Exmouth Gulf Prawn Managed Fishery (Western Australia); GSVPF = Gulf St Vincent Prawn Fishery (South Australia); KPMF = Kimberley Prawn Managed Fishery (Western Australia); NBPMF = Nickol Bay Prawn Managed Fishery (Western Australia); OPMF = Onslow Prawn Managed Fishery (Western Australia); SBPMF = Shark Bay Prawn Managed Fishery (Western Australia); SGPF = Spencer Gulf Prawn Fishery (South Australia); SW TMF = South West Trawl Managed Fishery (Western Australia); WCPF = West Coast Prawn Fishery (South Australia)


Stock Structure

Western King Prawn is distributed throughout the Indo–West Pacific1. No assessment has been conducted on Western King Prawn biological stock structure in Western Australia, and status in Western Australia is therefore reported at the management unit level. In South Australia, one study of the genetic structure of Western King Prawn found no differences between the three fisheries2. However, each of the fisheries functions as an independent population, with distinct adult and juvenile habitats and independent variations in recruitment and abundance. Each fishery is therefore assessed and managed as a separate management unit.


Stock Status

Shark Bay Prawn Managed Fishery (Western Australia) management unit

Western King Prawns are the most resilient of the prawn species taken in this fishery. Therefore, the rates of fishing that maintain the spawning biomass of Tiger Prawns are well below the rates that could result in recruitment overfishing of Western King Prawns3. More than 40 years of catch-and-effor data support the assumption that this management unit has never been reduced to levels considered to be recruitment overfished4 and current effort levels are below those previously exerted. Analysis of catch-and-effort data in the 1970s to the 1990s provided no evidence of a stock–recruitment relationship for Western King Prawns4, suggesting that the Western King Prawn in this management unit was never reduced to levels where it would become evident. Consequently, at the levels of effort exerted during that period (which allowed for environmental variations that are likely to occur, including Leeuwin Current variations, and La Niña and El Niño events), sufficient breeding stock will be available to ensure ongoing recruitment levels. Furthermore, the introduction of seasonal, moon and area closures since this period further restricts the overall fishing effort, which increases protection for breeding populations of Western King Prawns. Therefore, historical catch and catch rates from the period (1989–98) when recruitment was known not to be affected by fishing effort were used as the basis for calculating target catch ranges for this management unit (1100–1600 tonnes [t])5 and mean catch rate (21 kg/hour; range 16–29 kg/hour).

The target catch range is currently being reviewed due to declines in the level of effort and shifts to targeting larger prawns. Total commercial catch for 2010 was 1122 t, with a catch rate of 27.5 kg/ hour; these are within historical target ranges. This evidence indicates that the biomass of Western King Prawn in this management unit is unlikely to be recruitment overfished, and that the current level of fishing mortality is unlikely to cause the management unit to become recruitment overfished. 

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

Exmouth Gulf Prawn Managed Fishery (Western Australia) management unit

Maintaining catches within historical ranges is used to ensure that the spawning stock and fishing mortality are kept at appropriate levels for the Exmouth Gulf management unit6. Production levels from the 1970s to the 1990s provide no evidence of a stock–recruitment relationship for Western King Prawns4. In 1983, the effort on Western King Prawns increased significantly, due to the requirement to reduce effort on Tiger Prawns. As a result, the annual production of Western King Prawns improved by around 40 per cent, on average. Although it would be expected that this increased production would have decreased the overall spawning stock, there was no decline in production other than the normal variations seen in recruitment strength associated with environmental factors. This suggests that Western King Prawn in this management unit has never been reduced to levels where the stock–recruitment relationship would become evident. This indicates that, at current effort levels and with variations in environmental conditions, sufficient breeding stock will be available to ensure adequate recruitment in the future.

Catch and catch-rate levels from 1989 to 1998 have been used as the basis for calculating a target catch range of 350–500 t5 and a catch rate of 12 kg/hour (range 8–14 kg/hour). The target catch range is currently being reviewed due to declines in the level of effort and shifts to targeting larger prawns. The commercial catch for 2010 of 254 t reflects these changes, although the catch rate (9.8 kg/hour) was within the target range. This evidence indicates that the biomass of Western King Prawn in this management unit is unlikely to be recruitment overfished, and that the current level of fishing mortality is unlikely to cause the management unit to become recruitment overfished.

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

North coast prawn managed fisheries (Western Australia) management unit

The north coast prawn managed fisheries management unit is made up of four separate fisheries but reported as one unit because of minimal catch. Western King Prawns form part of total prawn landings in these multispecies prawn fisheries. Only in the Broome Prawn Managed Fishery (Western Australia) are Western King Prawns the key target species. Current commercial catch compared with historical ranges is therefore used to assess the level of fishing mortality for these fisheries. Historical catch levels from periods when recruitment was known not to be affected by fishing effort (1991–98) have been used as the basis for calculating target catch ranges; these are 65–295 t5 for the north coast prawn fisheries combined. Total commercial catch for 2010 was less than 10 t, well below the target catch range and the long-term (20-year) average combined catch of 140 t. For the Broome Prawn Managed Fishery (Western Australia), the catch rate in 2010 was 24 kg/hour, within the target catch-rate range (19–43 kg/hour). The low catches are attributed to very low effort expended in these fisheries, as a result of the current low market value of Western King Prawns and high costs of fishing. This evidence indicates that the biomass of the management unit is unlikely to be recruitment overfished, and that the current level of fishing mortality is unlikely to cause the management unit to become recruitment overfished.

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

South West  Trawl Managed Fishery (Western Australia) management unit

Historical catch and catch-rate ranges are used to assess spawning stock and fishing mortality for the small prawn fisheries in the south-west region of Western Australia. Historical catch levels from periods when recruitment was known not to be affected by fishing effort (1990–99) have been used as the basis for calculating target catch ranges and catch rates. The target catch range is 10–40 t, and the target catch rate is 14–52 kg/day. Total commercial catch for 2010 was 12 t5, which is within the target catch range and below the long-term (20-year) average catch of 18 t. The 2010 catch rate was 60 kg/day, which is higher than the historical catch range. This evidence indicates that the biomass of the management unit is unlikely to be recruitment overfished, and that the current level of fishing mortality is unlikely to cause the management unit to become recruitment overfished.

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

Spencer Gulf Prawn Fishery (South Australia) management unit

The primary measures for stock status in Spencer Gulf are the average catch rates obtained during fishery-independent surveys conducted in February, April and November, which are used as indices of relative biomass. Since the fishery has maintained a long and stable history of commercial catches and recruitment7, the performance indicators for relative biomass aim to maintain survey catch rates within historical ranges. Mean catch rates for surveys conducted in February, April and November 2010 were 143 kg/hour, 214 kg/hour and 136 kg/hour, respectively8. These were above the limit reference points of 120 kg/hour, 160 kg/hour and 95 kg/hour, respectively8. This evidence indicates that the biomass is unlikely to be recruitment overfished. Combined with stable commercial catches, this suggests that the current level of fishing mortality is unlikely to cause the management unit to become recruitment overfished.

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

Gulf St Vincent Prawn Fishery (South Australia) management unit

The primary measures for stock status in Gulf St Vincent are the average catch rates obtained during fishery-independent surveys conducted in December, March, April and May, which are used as indices of relative biomass. Since surveys were first conducted, in December 2004, the fishery has maintained stable recruitment9. It is considered that maintaining survey catch rates above the historical minimum levels will ensure adequate egg production. Mean catch rates for surveys conducted in March, April, May and December 2010 were 57 kg/hour, 73 kg/hour, 70 kg/hour and 50 kg/hour, respectively9. These are above the historical lows of 45 kg/hour, 41 kg/hour, 45 kg/ hour and 35 kg/hour, respectively. This evidence indicates that the biomass of the management unit is unlikely to be recruitment overfished. Combined with levels of commercial catch in 2010 that were below the historical average, the current level of fishing mortality is unlikely to cause the management unit to become recruitment overfished.

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

West  Coast Prawn Fishery (South Australia) management unit

The West Coast Prawn Fishery harvests from an oceanic stock that experiences large fluctuations in recruitment and commercial catch10. The primary measures for stock status on the west coast are the total commercial catch and the average catch rates obtained during fishery-independent surveys conducted in February, June and November, which are used as indices of relative biomass. The fishery suffered a prolonged period of stock collapse from 2002 to 200711.

Comparisons of mean commercial catch and survey catch rates during this period provide the basis for assessment of status. During 2010, commercial catch (89 t) was higher than during the period of collapse (2002–07; mean = 16 t), but lower than during the previous period of stable catches (1995–2001; mean = 145 t)11. Mean survey catch rate (47 kg/hour) was also higher than during the period of collapse (mean = 30 kg/hour)11, suggesting a recovering stock. Commercial catch and effort were low in 2010, in the historical context. This level of fishing mortality should allow this management unit to recover from its recruitment overfished state.

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


Table 2: Western King Prawn biology3,6–7

Longevity and maximum size

2–3 years, maximum 4 years
Western Australia: males 4.8 cm CL, females 6.3 cm CL South Australia: males 6 cm CL, females 6.8 cm CL

Maturity (50%)

6–8 months; 2.3–2.7 cm CL

CL = carapace length


Figure 1: Distribution of reported commercial catch of Western King Prawn in Australian waters, 2010 (calendar year)
Figure 1: Distribution of reported commercial catch of Western King Prawn in Australian waters, 2010 (calendar year)

Main features and statistics for Western King Prawn stocks/fisheries in Australia in 2010
  • Fishing is primarily undertaken using demersal prawn otter trawl gear.
  • Management is primarily through input controls including limited entry, gear restrictions, spatial and temporal closures, total allowable effort and the use of bycatch reduction devices.
  • The number of commercial vessels that caught Western King Prawns in 2010 in Western Australia was 18 in the Shark Bay Prawn Managed Fishery, 9 in the Exmouth Gulf Prawn Managed Fishery, 18 in north coast prawn managed fisheries and 3 in the South West Trawl Fishery. In South Australia, 52 vessels caught Western King Prawns: 39 in the Spencer Gulf Prawn Fishery, 10 in Gulf St Vincent Prawn Fishery and 3 in the West Coast Prawn Fishery.
  • The total amount of Western King Prawn caught commercially in Australia in 2010 was 4241 t, comprising 1392 t in Western Australia (1122 t in the Shark Bay Prawn Managed Fishery, 254 t in the Exmouth Gulf Prawn Managed Fishery, 4 t in the north coast prawn managed fisheries and 12 t in the South West Trawl Fishery). In South Australia, catch included 2536 t in the Spencer Gulf Prawn Fishery, 224 t in Gulf St Vincent Prawn Fishery and 89 t in the West Coast Prawn Fishery. There is minor recreational catch of this species, and Indigenous catch is considered negligible.

Figure 2: Commercial catch of Western King Prawn in Australian waters, 2000–10 (calendar year)
Figure 2: Commercial catch of Western King Prawn in Australian waters, 2000–10 (calendar year)

Catch Explanation

The catch of Australian Western King Prawns has been relatively steady since 2000, with an average catch from 2000 to 2010 of 3700 t. The peak catch in 2001 and the low catch in 2003 reflected variation in the catch harvested from Spencer Gulf, driven primarily by large differences in recruitment to the fishery in these years.


Effects of fishing on the marine environment
  • The Spencer Gulf Prawn Fishery (South Australia) gained Marine Stewardship Council certification in 2011.
  • Fishing for Western King Prawns in Western Australia and South Australia is considered to be of low risk to the trophic structures of these regions. Although harvest rates are relatively high, Western King Prawns have very high natural mortality rates and make up only a small proportion of the total biomass on the trawl grounds. Predators of prawns have to be opportunistic because of the natural variations in prawn populations. Consequently, given the small areas and time periods now fished, it is considered unlikely that the commercial take of prawns impacts significantly on other trophic levels3,6.
  • Although trawling can impact on habitats, these effects for the Western King Prawn fisheries in Western Australia and South Australia are managed. In Western Australia, extensive permanent and temporary closures result in the fleet operating in only 7 per cent of the Shark Bay region, less than 30 per cent for Exmouth Gulf, and less than 3 per cent of the north coast region. In South Australia, trawl effort has decreased by more than 60 per cent from its historical peaks in all fisheries. Since the inception of the South Australian fisheries, permanent closures have included all waters less than 10 m deep to ensure protection of seagrass habitats. In Western Australia, these fishing operations are now essentially restricted to areas of sand and mud, where trawling has minimal long-term physical impact3,6,12.
  • All prawn trawlers operating in Western Australia must use bycatch reduction devices, including turtle excluder devices and hoppers to increase survival of returned fish. In South Australia, all boats use crab bags, and 49 of the 52 boats use hopper systems to ensure rapid return of bycatch to the water. In the Gulf St Vincent Prawn Fishery (South Australia), all boats recently adopted specialised mesh codends with rigid grids that substantially reduce bycatch volumes (SARDI, unpublished data).
  • Although trawling does capture a wide variety of byproduct and bycatch species, studies in Western Australia and South Australia found no significant difference in biodiversity between trawled and non-trawled areas12–13.

Environmental effects on Western King Prawn
  • The biomass of Western King Prawns can be highly variable, and is affected by environmental factors such as water temperatures, cyclones and broadscale oceanographic features such as the Leeuwin Current14.
  • Flooding events in Shark Bay during December 2010 and February 2011, associated with strong La Niña events in November 2010 and February 2011, could have had a significant effect on the prawn fishery15.
  • In South Australia, there is some evidence to suggest that strong El Niño conditions result in unfavourable upwelling in critical spawning grounds, which may result in recruitment failure16.



a Department of Fisheries, Western Australia
South Australian Research and Development Institute