Balmain Bug Ibacus alticrenatus, I. brucei, I. chacei, I. peronii

John Stewarta and Brad  Zellerb


True Balmain Bug (I. Peronii)
True Balmain Bug (I. Peronii)

Table 1: Stock status determination for Balmain Bug

Jurisdiction

New South Wales, Queensland

Victoria

South Australia

Western Australia

Stock

East coast

(ECOTF, OTF-FS, OTF-PS)

Victorian

South Australian

Western Australian

Stock status

Negligiblea

Negligibleb

Negligiblec

Sustainable

Indicators

Catch rates, size structure


ECOTF = East Coast Otter Trawl Fishery (Queensland); OTF-FS = Ocean Trawl Fishery – Fish Sector (New South Wales); OTF-PS = Ocean Trawl Fishery – Prawn Sector (New South Wales)

a 'Negligible' means historically low catch; no stock status. Victorian catch ranged from 5 to 15 t between 2006–07 and 2011–12.

b 'Negligible' means historically low catch; no stock status. South Australian catch ranged from 1.1 to 8.1 t between 2001–01 and 2012–13.

c 'Negligible' means historically low catch; no stock status. Catch from the South West Trawl Managed Fishery and the South Coast Trawl Fishery in 2013 was 127 kg; in the past 10 years, the average catch from the Western Australian management unit was 106 kg.


Stock Structure

The common name ‘Balmain Bug’ refers to four similar species of fan lobster: Ibacus alticrenatus, I. brucei, I. chacei and I. peronii1. These species overlap in their distributions on the east coast of Australia and have evolved different life-history strategies. They are treated as a single biological stock in this report because they are rarely distinguished by fishers or fish marketers. Landings of I. peronii and I. alticrenatus in the jurisdictions of Victoria, South Australia and Western Australia are very low and the stock status is not assessed. The true Balmain Bug (I. peronii) is widely distributed around the southern half of the continent, from around the Queensland – New South Wales border (latitude 28°S) to central Western Australia (latitude 29°S), including the east coast of Tasmania and Bass Strait. The true Balmain Bug is mainly found close to shore, in waters less than 80 m deep. Given the prevailing influence of the East Australian Current and a protracted (around 80 days) pelagic larval life, I. peronii along the east coast is thought to be a single biological stock1. Landings in Victoria, South Australia and Western Australia are thought to be true Balmain Bugs (I. peronii). However, the stock structure across these jurisdictions is unknown. Consequently, the stock status for Balmain Bugs is presented on a management unit basis for these jurisdictions.

The Smooth Bug (I. chacei) is distributed between northern Queensland (latitude 17°S) and southern New South Wales (latitude 36°S), although it is rarely caught south of Sydney (latitude 34°S). It is most abundant on the mid-continental shelf in depths of 50–150 m. Given the prevailing influence of the East Australian Current in these depths, a pelagic larval phase and a northerly migration of older stages, Smooth Bugs are thought to be a single biological stock1.

The Honey Bug (I. brucei) is distributed between central Queensland and northern New South Wales. It is most abundant on the outer continental shelf and upper slope in waters 120–300 m deep. Given the prevailing influence of the East Australian Current in these depths and a pelagic larval phase, Honey Bugs are thought to be a single biological stock1.

The Deepwater Bug (I. alticrenatus) is distributed throughout southern Australian and New Zealand waters. It is most abundant at depths of 200–400 m on the upper continental slope1.

 


Stock Status

East Coast biological stock

This cross-jurisdictional, multispecies biological stock has components in New South Wales and Queensland. Each jurisdiction assesses the part of the biological stock that occurs in its waters. The status presented here for the entire biological stock has been established using evidence from both jurisdictions.

In New South Wales, Balmain Bugs (true Balmain Bugs and Smooth Bugs) are trawl target species, and have been assessed in terms of their commercial catch rates and length compositions in landings. Median catch rates (kg/day of trawling) have fluctuated but show no overall trends, while the size compositions in landings have remained stable for both species. The above evidence indicates that the biomass of this part of the stock is unlikely to be recruitment overfished. Current landings are at historically low levels as a result of a large reduction in fishing effort, with the number of days fished in 2013 being less than 30 per cent of those fished in 2000. This reduction in fishing effort, in combination with stable size compositions in landings, strongly suggests that fishing mortality is constrained in New South Wales waters. The above evidence indicates that the current level of fishing pressure is unlikely to cause this part of the stock to become recruitment overfished.

In Queensland, Balmain Bug fishing mortality is managed by a prohibition on taking egg-bearing females, conservative minimum legal sizes (which were updated in 2009), and mandatory use of turtle excluder devices since the early 2000s—these have been shown to reduce the incidental catch rates of scyllarid lobsters, including Balmain Bugs2,3. In addition, the spawning stock is partly protected from fishing during an annual seasonal closure. Although nominal catch rates have declined since 2011, and the 2013 catch was relatively low4, this is likely to be an indication of the more conservative minimum legal sizes for I. chacei and fisher behaviour, rather than declining abundance. Fishers harvest Balmain Bug as low-value byproduct of fishing for Eastern King Prawn. Given their low value, it is suspected that Balmain Bug fishing mortality is also likely to be low.

Balmain Bugs were considered in a recent species risk assessment of the Queensland East Coast Otter Trawl Fishery, based on a qualitative method that combines biological resilience properties with fishery impact susceptibility5. It found a low risk of the Queensland part of the east coast Balmain Bug stock becoming recruitment overfished at the 2009 effort level south of the Great Barrier Reef Marine Park6, where the majority (83 per cent, on average) of catch is taken. Fishing effort has declined in that area by 10 per cent since 2011, further reducing the risk of the stock becoming recruitment overfished. The risk of recruitment overfishing within the Great Barrier Reef Marine Park was intermediate to high7, based on perceived differences between this area and the area south of the Great Barrier Reef Marine Park, in terms of fishery interaction throughout the Balmain Bug life cycle, marketability and access to refugia. Fishing effort in the Great Barrier Reef Marine Park has declined by 23 per cent since 2009, also reducing risk for this part of the stock.

The above evidence indicates that the biomass of the Queensland part of the stock is unlikely to be recruitment overfished and the current level of fishing pressure is unlikely to cause this part of the stock to become recruitment overfished.

On the basis of the evidence provided above, the entire biological stock is classified as a sustainable stock.


Table 2: Balmain Bug biology1,8–12                                                                                  

Longevity and maximum size

Balmain Bug: 15 years; 86 mm CL

Smooth Bug: 5–7 years; 80 mm CL

Honey Bug: longevity largely unknown; maximum CL in Queensland samples is 72 mm for females and 66 mm for males

Deepwater Bug: longevity largely unknown; maximum CL in Queensland samples is 55 mm for both females and males

Maturity (50%)

Balmain Bug: 2 years; 50 mm CL

Smooth Bug: 2 years; 55 mm CL

Honey Bug: 47 mm CL 

Deepwater Bug: 45 mm CL

CL = carapace length (not to be confused with carapace width, which is generally used for size limits in Balmain Bugs as it is a simple and rapid measure for use by commercial and recreational fishers13)


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



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

Jurisdiction

New South Wales

Queensland

Fishing methods

Commercial

Trawl

Recreational

Diving

Indigenous

Diving

Management methods

Commercial

Limited entry

Size limits

Vessel restrictions

Recreational

Bag limits

Size limits

Spatial closures

Indigenousa,b,c

Bag limits

Size limits

Spatial closures

Section 37(1)(c1), Aboriginal cultural fishing authority

Active vessels

 

22 in OTF-FS

66 in OTF-PS

150 in ECOTF

Catch

Commercial

1.5 t in OTF-FS

23.0 t in OTF-PS

65.1 t in ECOTF

Recreational

Unknown

Unknown

Indigenous

Unknown

Unknown

Markets

Domestic

Export


ECOTF = East Coast Otter Trawl Fishery (Queensland); OTF-FS = Ocean Trawl Fishery – Fish Sector (New South Wales); OTF-PS = Ocean Trawl Fishery – Prawn Sector (New South Wales)

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 Aboriginal Fishing Interim Compliance Policy allows an Indigenous fisher in New South Wales to take in excess of a recreational bag limit in certain circumstances—for example, if they are doing so to provide fish to other community members who cannot harvest themselves.

c The Aboriginal cultural fishing authority is the authority that Indigenous persons can apply to to take catches outside the recreational limits under the New South Wales Fisheries Management Act 1994, section 37(1)(c1) (Aboriginal cultural fishing authority).


Figure 2: Commercial catch of Balmain Bugs in Australian waters, 2001 to 2013 (calendar years)

Figure 2: Commercial catch of Balmain Bugs in Australian waters, 2001 to 2013 (calendar years)




Effects of fishing on the marine environment
  • The East Coast Otter Trawl Fishery (Queensland) interacts with a number of protected species, including turtles and sea snakes14,15. Turtle excluder devices and bycatch reduction devices are deployed by all boats to reduce the amount of bycatch16. Fisher compliance with legislated design principles and best-practice use of these devices is mandatory to ensure that the devices function effectively to limit capture of turtles and sea snakes. Interactions with these species are monitored through ‘Species of Conservation Interest’ logbooks17.

    Environmental effects on Balmain Bug
    • The major environmental factor influencing the Balmain Bug biological stock is likely to be the southerly flow of the East Australian Current. The impact of changes in the East Australian Current on recruitment of these species is currently unknown1,9. Extreme major weather events associated with the recent protracted La Nĩna event are thought to have modified recruitment patterns of a number of oceanic fishery species, possibly including Balmain Bug.


    a Department of Primary Industries, New South Wales
    b Department of Agriculture, Fisheries and Forestry, Queensland