Moreton Bay Bug ​Thenus australiensisa, T. parindicus

Brad  Zellerb, Mervi  Kangasc, Justin Roachd and James Woodhamsd


Moreton Bay Bug - Thenus australiensis

Table 1: Stock status determination for Moreton Bay Bug

Jurisdiction

Queensland

Western Australia                 

Commonwealth

Stock

ECOTF

North-western                        NPF Australia
(EGPMF, OPMF, PFTF, SBPMF, SBSMF)

NPF

TSPF

Stock status

 

 

 

 

Sustainable

Undefined                               

Sustainable

Sustainable

Indicators

Catch, CPUE

Catch

Catch

Catch

CPUE = catch per unit effort; ECOTF = East Coast Otter Trawl Fishery (Queensland); EGPMF = Exmouth Gulf Prawn Managed Fishery (Western Australia); NPF = Northern Prawn Fishery (Commonwealth); OPMF = Onslow Prawn Managed Fishery (Western Australia); PFTF = Pilbara Fish Trawl Fishery (Western Australia); SBPMF = Shark Bay Prawn Managed Fishery (Western Australia); SBSMF = Shark Bay Scallop Managed Fishery (Western Australia); TSPF = Torres Strait Prawn Fishery (Commonwealth) ​


Stock Structure

Thenus australiensis (Reef Bug) and T. parindicus (Mud Bug) are known collectively as ‘Moreton Bay Bugs’. Moreton Bay Bugs are distributed along the tropical and subtropical coast of Australia from northern New South Wales to Shark Bay in Western Australia2. No studies have been carried out on the biological stock structure of Australian Moreton Bay Bugs. Given the uncertainty in biological stock structure, status is reported at the level of the management unit, and the two species are assessed together.


Stock Status

East Coast Otter Trawl Fishery (Queensland) management unit

No formal stock assessments exist for Moreton Bay Bugs in the East Coast Otter Trawl Fishery (Queensland). Areas open to trawling in the Great Barrier Reef Marine Park contribute approximately 88 per cent of the east coast commercial catch of Moreton Bay Bugs. However, components of the biomass of the eastern Queensland populations of Moreton Bay Bugs have been within permanent closures associated with the Great Barrier Reef Marine Park since the mid 1980s. Research3 estimated that closures in the Great Barrier Reef Marine Park included 54 per cent of the estimated biomass of T. australiensis and 45 per cent of the estimated biomass of T. parindicus in 20053. In addition, the catch per unit effort (CPUE) for Moreton Bay Bugs has shown an increasing trend over the past 10 years4. Given this level of historical protection and the trends in CPUE, Moreton Bay Bugs in this management unit are unlikely to be recruitment overfished.

T. australiensis and T. parindicus mature at approximately 5.2 and 5.8 cm carapace length, respectively. Hence conservative minimum legal size limits (7.5 cm carapace length) should allow Moreton Bay Bugs to spawn before they enter the fishery, provided that undersized animals caught survive post-capture. Square-mesh codends protect juveniles of both species from fishing mortality in the fishery4. These measures, combined with spatial closures, mean that fishing mortality is unlikely to cause Moreton Bay Bugs in this management unit to become recruitment overfished.

On the basis of the evidence provided above, the East Coast Otter Trawl Fishery (Queensland) management unit is classified as a sustainable stock.

North-western Australia (Western Australia) management unit

No formal stock assessments exist for Moreton Bay Bugs in north-western Australia. Moreton Bay Bugs are not specifically targeted in north-western Australia, and current commercial catch levels are low. Insufficient information is available to formally assess the status of this management unit. As a result, the north-western Australia management unit is classified as an undefined stock.

Northern Prawn Fishery (Commonwealth) management unit

An assessment of byproduct species in the Gulf of Carpentaria within the Northern Prawn Fishery (Commonwealth) was conducted in 20105. This assessment estimated the annual acceptable biological catch for Moreton Bay Bugs in the fishery at 1887 tonnes (t) (95 per cent confidence interval 1716–2057 t). This is well in excess of historical annual commercial catches (catch peaked at 120 t in 1998). As a result, Moreton Bay Bugs in the Northern Prawn Fishery management unit are unlikely to be recruitment overfished.

Fishing mortality has been low in recent years, and ecological risk assessments have suggested that the risk of stock depletion of Moreton Bay Bugs is low. A trigger limit of 100 t is also in place. If this limit is reached in a season, further analysis will be conducted to ensure that there are no sustainability concerns with the harvest level of Moreton Bay Bugs. Given the low level of catch in recent years, the Northern Prawn Fishery (Commonwealth) management unit is unlikely to become recruitment overfished.

On the basis of the evidence provided above, the Northern Prawn Fishery (Commonwealth) management unit is classified as a sustainable stock.

Torres Strait  Prawn Fishery (Commonwealth) management unit

No formal stock assessment has been carried out for Moreton Bay Bugs in the Torres Strait Prawn Fishery (Commonwealth). Moreton Bay Bugs are a byproduct species within this fishery, taken while targeting prawns. Trawl operations in the Torres Strait Prawn Fishery (Commonwealth) cover a small proportion—approximately 20 per cent6—of the Torres Strait Protected Zone. The coverage of the fishery is likely to have declined in recent years as a result of declining effort. Reported commercial catches of the species have been decreasing over the past decade. In 2010, approximately 4 t of Moreton Bay Bugs were reported. There is a minimum size limit for Moreton Bay Bugs of 7.5 cm carapace length in the Torres Strait Prawn Fishery (Commonwealth) that should provide an opportunity for individuals to spawn before they are retained by fishers, provided that animals survive post-capture.

A recent assessment of the seabed and associated biodiversity of the Torres Strait7 indicates that Moreton Bay Bugs are unlikely to have been exposed to high levels of fishing pressure in the Torres Strait Protected Zone. The assessment estimated that biomass of T. australiensis in 2007 was 124 t, 19 per cent of which was located within the area exposed to prawn trawling (2005 footprint of the fishery using vessel monitoring system data). The biomass of T. parindicus was estimated to be 151 t, with 18 per cent located in areas exposed to prawn trawling.

The current low levels of commercial catch and effort, and the protection offered by the minimum size limit, mean that it is unlikely that Moreton Bay Bugs in this management unit will become recruitment overfished. This being the case, it is also unlikely that the management unit is overfished.

On the basis of the evidence provided above, the Torres Strait Prawn Fishery (Commonwealth) management unit is classified as a sustainable stock.


Table 2: Moreton Bay Bug biology8–9

Longevity and maximum size

~7 years
T. australiensis: males 7.7 cm CL, females 8.9 cm CL
T. parindicus: males 6.1 cm CL, females 7.2 cm CL

Maturity (50%)

T. australiensis (female): 5.2 cm CL
T. parindicus (female): 5.8 cm CL

CL = carapace length (Not to be confused with carapace width. Carapace width is generally used for size limits in fan and slipper lobsters as it is a simple and rapid measure for use by commercial and recreational fishers.)


Figure 1: Distribution of reported commercial catch of Moreton Bay Bugs in Australian waters, 2010
Figure 1: Distribution of reported commercial catch of Moreton Bay Bugs in Australian waters, 2010

Main features and statistics for Moreton Bay Bug stocks/fisheries in Australia in 2010
  • Moreton Bay Bugs are predominantly taken using otter trawl gear while targeting prawns and/or scallops.
  • Fisheries are managed through various input and output controls:
    • Input controls include limited entry, seasonal closures, area closures, gear restrictions, bycatch reduction devices and effort limits.
    • Output controls include minimum size limits and the compulsory discarding of undersized individuals and berried females. The Northern Prawn Fishery (Commonwealth) employs a catch trigger of 100 t.
  • Numbers of commercial vessels that reported catch of Moreton Bay Bugs in 2010 were 241 in the East Coast Otter Trawl Fishery (Queensland), 28 in north-western Australia, 44 in the Northern Prawn Fishery (Commonwealth) and 22 in the Torres Strait Prawn Fishery (Commonwealth).
  • The total commercial catch of Moreton Bay Bugs in Australia in 2010 was 459 t, comprising 436 t in the East Coast Otter Trawl Fishery (Queensland), 16 t in Western Australia, and a total of 7 t in the Northern Prawn Fishery (Commonwealth) and Torres Strait Prawn Fishery (Commonwealth) combined. There is no reported recreational or Indigenous catch of Moreton Bay Bugs.

Figure 2: Commercial catch of Moreton Bay Bugs in Australian waters, 2000–10 (calendar year)

Figure 2: Commercial catch of Moreton Bay Bugs in Australian waters, 2000–10 (calendar year)


Catch Explanation

On average, East Coast Otter Trawl Fishery (Queensland) landings make up 95 per cent of the Australian Moreton Bay Bug commercial catch. In 2000 and 2001, catches were low compared with more recent catches; this was mainly the result of the East Coast Otter Trawl Fishery (Queensland) adjusting to management changes accompanying the introduction of a statutory management plan for the fishery in November 1999. A number of factors, including extensive spatial and temporal closures, mandatory use of compliant bycatch reduction devices, and more detailed catch-and-effort recording requirements, may have reduced the reported Moreton Bay Bug catch. Since 2001, annual landings in the East Coast Otter Trawl Fishery (Queensland) have averaged 429 t, ranging from 222 to 484 t. Fishing effort in the East Coast Otter Trawl Fishery (Queensland) decreased steadily from 2001 to 2008, but has steadied in recent years.


Effects of fishing on the marine environment
  • Trawling takes large quantities of bycatch, which can lead to a range of indirect ecosystem effects10. In 2001, the use of bycatch reduction devices (BRDs) became mandatory in the Northern Prawn Fishery (Commonwealth). Without bycatch reduction devices, the ratio of prawn product to bycatch is around 1:10; the use of BRDs can reduce this to 1:511.
  • The introduction of mandatory turtle excluder devices in 2010 has largely eliminated capture of most large bycatch species in the East Coast Otter Trawl Fishery (Queensland), including turtles, sharks and rays12. 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 2001)13.
  • Research shows that 9 cm square-mesh codend BRDs can reduce the quantity of bycatch and lower the incidental capture of Thenus australiensis in the scallop sector of the East Coast Otter Trawl Fishery (Queensland)14. A successful program to build and install square-mesh codends in trawl nets has led to their widespread adoption by fishers targeting Saucer Scallops in the East Coast Otter Trawl Fishery (Queensland)12.

Environmental effects on Moreton Bay Bug
  • There are suggestions that ocean acidification, changes in ocean current patterns (e.g. strengthening of the East Australian Current), and increased intensity of tropical storms associated with climate change may affect food availability, larval survival, dispersion and settlement patterns, abundance of Moreton Bay Bugs, and the distribution and level of catches15.
  • Increased rainfall and sea level rise have been identified16 as key impacts of climate change in the region of the Northern Prawn Fishery (Commonwealth). These impacts have the potential to modify the geographical distribution of Moreton Bay Bug stocks.


a This species has previously been confused with T. orientalis, which is now regarded as not occurring in Australia. The species are very difficult to separate using morphological characteristics1.
b Department of Agriculture, Fisheries and Forestry, Queensland
c Department of Fisheries, Western Australia
d Australian Bureau of Agricultural and Resource Economics and Sciences