Endeavour Prawns Metapenaeus endeavouri, M. ensis

Michelle Winninga, Mervi Kangasb, James Larcombec


Endeavour Prawn
Red Endeavour Prawn (M. ensis)

Table 1: Stock status determination for Endeavour Prawns

Jurisdiction

Commonwealth

Queensland

Stock

NPF

NPF

TSPF

ECOTF

Stock status

Blue Endeavour Prawn

Red Endeavour Prawn

Blue Endeavour Prawn

Blue and Red Endeavour Prawn

Sustainable

Undefined

Sustainable

Sustainable

Indicators

Spawning biomass, fishing mortality, catch

None

Biomass, effort, catch

Catch, effort


ECOTF = East Coast Otter Trawl Fishery (Queensland); NPF = Northern Prawn Fishery (Commonwealth); TSPF = Torres Strait Prawn Fishery (Commonwealth)

Table 1 continued

Jurisdiction

Western Australia

Stock

EGPMF

SBPMF

NCPMF

Stock status

Blue Endeavour Prawn

Blue Endeavour Prawn

Blue Endeavour Prawn

Sustainable

Undefined

Undefined

Indicators

Catch, survey catch rate

Catch

Catch


EGPMF = Exmouth Gulf Prawn Managed Fishery (Western Australia); NCPMF = North Coast Prawn Managed Fisheries (Western Australia); SBPMF = Shark Bay Prawn Managed Fishery (Western Australia)


Stock Structure

Endeavour Prawn fisheries are located in Shark Bay, in Exmouth Gulf, on the north coast of Western Australia, in the Gulf of Carpentaria, in the Torres Strait and on the east coast of Queensland. Little is known about the biological stock structure of the populations of Blue and Red Endeavour Prawns that make up these fisheries. Hence, status is reported at the management unit level. The majority of catch reported in this chapter is Blue Endeavour Prawn. Red Endeavour Prawn is represented in the East Coast Otter Trawl Fishery (Queensland), where it constitutes less than 20 per cent of the endeavour prawn catch1, and in the Northern Prawn Fishery (Commonwealth), where it constitutes 20–40 per cent of the annual endeavour prawn harvest.


Stock Status

Northern Prawn Fishery (Commonwealth) Blue Endeavour Prawn management unit

Blue Endeavour Prawn is assessed as part of the integrated bioeconomic model constructed for the Northern Prawn Fishery (Commonwealth) Tiger Prawn sector2. Commercial catch of Endeavour Prawn is disaggregated into separate species using a model incorporating historical fishery-independent survey data3. Blue Endeavour Prawn is assessed using a biomass dynamic model that estimated the spawner stock size at the end of 2012 to be 88.5 per cent of the spawner stock size (S) that would be required for maximum sustainable yield (SMSY)2. This is above the limit reference point of 50 per cent (0.5SMSY). As a result, the management unit is not considered to be recruitment overfished4. The commercial catch in 2012 (approximately 343 tonnes [t]) was below the estimate of maximum sustainable yield (base case 836 t). This level of effort 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.

Northern Prawn Fishery (Commonwealth) Red Endeavour Prawn management unit

Although stock assessments have been attempted for Red Endeavour Prawn, there is currently no reliable assessment to confidently classify the status of this stock4. Catches over recent years have been quite low compared with historical highs. This is most likely related to a fall in fishing effort directed at Tiger Prawn (Red Endeavour Prawn is a byproduct species from effort directed at Tiger Prawn), rather than any indication of a fall in Red Endeavour Prawn biomass. 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.

Torres Strait Prawn Fishery (Commonwealth) Blue Endeavour Prawn management unit

The most recent assessment5 for Blue Endeavour Prawn in the Torres Strait Prawn Fishery (Commonwealth) estimated that biomass in 2007 ranged from 71 to 85 per cent of the unfished (1967) level. Maximum sustainable yield was estimated at approximately 1100 t, and recent annual catches have been well below this level: catch in 2013 was 103 t, and catches since 2007 have been below 500 t. As a result, the management unit is not considered to be recruitment overfished6. Catch and effort levels, which have been well below maximum sustainable yield and maximum sustainable effort estimates for more than 10 years, are 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.

East Coast Otter Trawl Fishery (Queensland) Red and Blue Endeavour Prawn management unit

Since 1998, there has been a general upward trend in the nominal catch rate7 for Endeavour Prawns (species combined, as they are not differentiated in commercial logbooks) in the East Coast Otter Trawl Fishery (Queensland). Effort in this fishery stabilised in 2007 following management changes, marine park closures and the economic impact of rising operational costs. The average annual catch rate for the past 5 years (2009 to 2013) was 69 kg per day, which is 55 per cent higher than the long-term average (1990 to 2006). Current harvest levels are significantly lower than levels in 2001, when an assessment concluded that Endeavour Prawns were fully exploited8. The above evidence indicates that the biomass of the management unit is unlikely to be recruitment overfished. The average annual commercial harvest of Endeavour Prawns in the past 5 years (2009 to 2013) was 540 t, which is half the long-term average of 1112 t for the years 1990 to 2006. The fishing effort associated with the 2013 catch (7924 days) was only 30 per cent of the long-term average of 25 939 fishing days. This level of fishing pressure (catch and effort) 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) Blue Endeavour Prawn management unit

The Exmouth Gulf Prawn Managed Fishery (Western Australia) contributes the majority of the commercial landings of Blue Endeavour Prawns in Western Australia. There is no formal assessment for Blue Endeavour Prawn, which is a byproduct species whose distribution partly overlaps that of both Brown Tiger Prawn (Penaeus esculentus) and Western King Prawn (Melicertus latisulcatus); Blue Endeavour Prawns are caught when fishers are targeting these two species. Fishery-independent recruitment surveys of Brown Tiger Prawns and Western King Prawns (at standardised sites on separate key fishing grounds for the two species) also record the abundance of Endeavour Prawns on these grounds, providing an annual recruitment abundance index for this species. In 2013, the mean abundance index (catch rate) for Blue Endeavour Prawns on the Brown Tiger Prawn grounds of 9 kg/hour was below the 15 year mean (13 kg/hour), but within the range observed during these years (6–35 kg/hour). On the Western King Prawn grounds, the mean abundance index for Blue Endeavour Prawns of 7 kg/hour was also below the 6-year (2007 to 2012) mean of 14 kg/hour, but within the range observed during those years (2–38 kg/hour). There has been no declining trend in the fishery-independent survey catch rates over the periods sampled in either of these fishing grounds. As a result, the biomass of the management unit is not considered to be recruitment overfished.

With respect to fishing mortality, a target catch range is set at 120–300 t, based on historical catches between 1989 and 1998. Total catch in 2013 (85 t) was below the target catch range and below the average catch over the past 15 years (201 t)9. Low overall effort was expended in this fishery in 2013 (33 per cent less effort than the mean annual effort recorded between 2007 and 2011) due to low Brown Tiger Prawn stock abundance. The level of fishing effort on the Brown Tiger Prawn fishing grounds is normally around 60 per cent of the total annual effort; in 2013, it was only 25 per cent of total effort, and this reduced effort translated to a lower-than-average effort on Blue Endeavour Prawns. In the Exmouth Gulf Prawn Managed Fishery (Western Australia) management unit, the breeding biomass of Blue Endeavour Prawns is considered to be adequate because a significant portion of the breeding biomass is protected by the Brown Tiger Prawn spawning closures. As well, an additional portion of the Blue Endeavour Prawn biomass occurs inshore of the key fishing grounds for Brown Tiger Prawns, which are permanently closed. Hence, the current level of effort 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.

Shark Bay Prawn Managed Fishery (Western Australia) Blue Endeavour Prawn management unit

Blue Endeavour Prawns are landed in low numbers in the Shark Bay Prawn Managed Fishery (Western Australia), since they are not the target species. Therefore, catch-and-effort data cannot be used to determine the status of the species in this fishery. In 2013, 15 t were reported as landed, compared with a mean landing during the past 15 years of 9 t. 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.

 

North Coast Prawn Managed Fisheries (Western Australia) Blue Endeavour Prawn management unit

Blue Endeavour Prawns are landed in low numbers in the North Coast Prawn Managed Fisheries (Western Australia), since they are not the target species. Therefore, catch-and-effort data cannot be used to determine the status of the species in these fisheries. 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.


Table 2: Red and Blue Endeavour Prawn biology10–14

Longevity and maximum size

1–2 years
Blue Endeavour Prawn: 200 mm TL
Red Endeavour Prawn: 180 mm TL

Maturity (50%)

~6 months; females ~24-26 mm CL,
males ~18 mm CL

CL = carapace length; TL = total length


Figure 1: Distribution of reported commercial catch of Blue and Red Endeavour Prawns in Australian waters, 2013 (calendar year)
Figure 1: Distribution of reported commercial catch of Blue and Red Endeavour Prawns in Australian waters, 2013 (calendar year)



Table 3: Main features and statistics for Blue and Red Endeavour Prawn fisheries in Australia, 2013 (calendar year)

Jurisdiction

Commonwealth

Queensland

Western Australia

Fishing methods

Commercial

Demersal otter trawling

Recreationala,b

Cast net

None

Indigenousc

Cast net

None

Management methods

Commercial

Limited entry

Vessel restrictions

Gear restrictions

Effort limits

Spatial closures

Temporal closures

Recreationala,b

Possession limits

None

Indigenousc

Possession limits

None

Active vessels

52 in NPF

21 in TSPF

155 in ECOTF

6 in EGPMF

7 in NCPMF

18 in SBPMF

Catch

Commercial

507 t in NPF

103 t in TSPF

506 t in ECOTF

85 t in EGPMF

4 t in NCPMF

15 t in SBPMF

Recreationald

Negligible

0 t

Indigenous

Negligible

0 t

Markets

Domestic

Export


ECOTF = East Coast Otter Trawl Fishery (Queensland); EGPMF = Exmouth Gulf Prawn Managed Fishery (Western Australia); NCPMF = North Coast Prawn Managed Fisheries (Western Australia); NPF = Northern Prawn Fishery (Commonwealth); SBPMF = Shark Bay Prawn Managed Fishery (Western Australia); TSPF = Torres Strait Prawn Fishery (Commonwealth)

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 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.

c 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.

d In Queensland recreational fishers are permitted to catch Endeavour Prawns, but are unlikely to catch them in large amounts because of the distribution of this species group.


Figure 2: Commercial catch of Blue and Red Endeavour Prawns in Australian waters, 1990 to 2013 (calendar years)
Figure 2: Commercial catch of Blue and Red Endeavour Prawns in Australian waters, 1990 to 2013 (calendar years)



Effects of fishing on the marine environment
  • There is typically a high proportion of bycatch, relative to retained product, in otter trawl fisheries. Post-release survival of bycatch species is variable15.
  • The use of bycatch reduction devices is mandatory in all Australian tropical prawn trawl fisheries. Use of turtle excluder devices in the Northern Prawn Fishery (Commonwealth) reduced turtle bycatch from 5700 individuals per year before 2001 to approximately 30 per year after 200116. The introduction of turtle excluder devices in the Western Australia prawn trawl fisheries in 2003 reduced turtle bycatch by at least 95 per cent17.
  • Spatial closures afford some protection to the marine environment from the physical effects of trawling. In Queensland, the Great Barrier Reef Marine Park occupies 63 per cent of the East Coast Otter Trawl Fishery18, 34 per cent of which is open to trawling7. However, effort is highly aggregated, occurring within only a small fraction of the open area. 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 of the Exmouth Gulf, and less than 3 per cent of the north coast region. Fishing operations are restricted to areas of sand and mud, where trawling has minimal long-term physical impact19–22. The Northern Prawn Fishery (Commonwealth) uses a system of closures (spatial and seasonal) to manage the fishery, as well as other input controls (for example, limited entry, gear restrictions). A total of 2.1 per cent of the total managed area of the fishery is subject to permanent closures, while 8.3 per cent is subject to seasonal closures23. The Torres Strait Prawn Fishery (Commonwealth) also employs spatial and temporal closures to protect small prawns and important habitat areas, such as for breeding populations of turtles24.
  • An assessment of trawl-related risk in the Great Barrier Reef Marine Park found that the East Coast Otter Trawl Fishery (Queensland) posed no more than an intermediate risk of overfishing some species assemblages exposed to trawling25.
  • Interactions with species protected under the Environment Protection and Biodiversity Conservation Act 1999, such as sea snakes and seabirds, are routinely monitored.
  • The Northern Prawn Fishery (Commonwealth) has been certified by the Marine Stewardship Council since November 2012.

    Environmental effects on Endeavour Prawns
    • Nursery grounds (such as seagrass beds) are important for maintaining Endeavour Prawn stocks in the Northern Prawn Fishery (Commonwealth). Management strategies therefore involve the closure of significant nursery areas to trawling to protect stocks26.
    • Prawn distribution can be driven by environmental factors. For example, in a study on the distribution of Endeavour Prawns in the Gulf of Carpentaria, Blue Endeavour Prawns were found to be most abundant in the south-eastern gulf and shallower parts of the western gulf, where sediments were either sand or muddy sand. The highest abundance of Red Endeavour Prawns was in the north-eastern gulf and deeper areas of the western gulf, where sediments were more than 60 per cent mud27. However in the Torres Strait, Blue Endeavour Prawns were equally abundant on all substrate types13.


    a Department of Agriculture, Fisheries and Forestry, Queensland
    b Department of Fisheries, Western Australia
    c Australian Bureau of Agricultural and Resource Economics and Sciences