Southern Sand Flathead Platycephalus bassensis

James Andrewsa, Jeremy Lyleb, Justin Bellb and Anthony Fowlerc


Southern Sand Flathead
Southern Sand Flathead

Table 1: Stock status determination for Southern Sand Flathead

Jurisdiction

Victoria

Tasmania

South Australia

Western Australia

Stock

Victoria

(CIF, ITF, OF, PPBF)

Tasmania

(SF)

South Australia

Western Australia

Stock status

Negligiblea

Negligibleb

Undefined

Undefined

Indicators

Catch, biomass, CPUE

Catch


CIF = Corner Inlet Fishery (Victoria); CPUE = catch per unit effort; ITF = Inshore Trawl Fishery (Victoria), OF = Ocean Fishery (Victoria); PPBF = Port Phillip Bay Fishery (Victoria); SF = Scalefish Fishery (Tasmania)

a 'Negligible' means historically low catch; no stock status. The species is rare in South Australia; catch is unknown but very low, possibly zero. The catch history for all flathead combined was reviewed, and the annual catch has ranged from 1.5 to 5.7 tonnes over the past 13 years without apparent trend.

b 'Negligible' means historically low catch; no stock status. The species is rare in Western Australia; catch is unknown but very low, possibly zero.


Stock Structure

Southern Sand Flathead (Platycephalus bassensis) is endemic to Australia and distributed from the central New South Wales coast, around Tasmania to South Australia, and to Bremer Bay in Western Australia1. Southern Sand Flathead inhabit bays, inlets, estuaries and shallow coastal waters to a depth of about 100 metres2. There is some evidence of regional differences in physical characteristics and growth rates for Southern Sand Flathead (for example, fish from Port Phillip bay are 30 per cent smaller than fish from Bass Strait and 20 per cent smaller than fish from south-east Tasmania)3, but the biological stock structure has not been studied. In the absence of information about stock structure, and because each of the jurisdictions has different management arrangements for Southern Sand Flathead, status is reported at the jurisdictional level.


Stock Status

Victoria 

Southern Sand Flathead historically comprised a significant component of the commercial catch in Victoria, with more than 200 tonnes (t) taken annually for several years until the 1950s from Port Phillip Bay2. This species has also been an important component of the recreational fishery, with an estimated 322 t caught during 2000–013,4. Using three independent measures of abundance (biomass estimates from fishery-independent trawls, commercial longline catch per unit effort and recreational catch per unit effort), an 80–90 per cent decline in stock size was detected over the period 2000 to 20103. By 2013, stocks had recovered to 30 per cent of 1990s levels, but the abundance of zero-plus aged fish has remained very low since 1994.

Very little is known about the catch of Southern Sand Flathead from Victorian waters outside of Port Phillip Bay, except that they are taken as bycatch and generally not targeted by commercial fishers. Some targeting offshore by recreational anglers is known to occur.

There is no formal management plan and no limit reference point for Victorian Southern Sand Flathead. Despite the substantial decline in biomass for the period 2000 to 2013 and the significant decline in recruitment for Port Phillip Bay populations3, there is no evidence that these trends are caused by the removal of catch. The above evidence indicates that the biomass of this stock has been deteriorating but is not likely to be recruitment overfished.

Recruitment in Port Phillip Bay is heavily influenced by climatic conditions2,3,5, and for many years it was suggested that existing levels of fishing pressure had little influence on spawning success5. This is partly because a portion of the population will not grow to a size at which they become vulnerable to fishing (that is, they will not reach the legal minimum size). A more recent study, undertaken in response to angler concerns about the decline in Southern Sand Flathead abundance, found that, despite the decline in abundance, stock exploitation levels between 2000–01 and 2006–07 remained stable, at 15–30 per cent of the stock biomass3. This study found that the magnitude of the decline was, however, unprecedented over the history of the fishery and that, under these circumstances, fishing pressure can contribute to a more rapid decline or potentially affect the recovery rate of the stock. Consequently, the study evaluated management options to assist the recovery of the fishery in Port Phillip Bay.

The current level of fishing pressure is considered to be relatively low from the commercial sector, and is unknown for the recreational sector. The proportion of the population that exceeds the current minimum legal size limit (27 cm) has steadily increased from 1990 to 2011. In the early 1990s, the percentage of legal sized fish was less than 10 per cent of the population. This proportion was more than 30 per cent by the early 2000s and remained above 20 per cent until 2011. The remaining 70–80 per cent of the population are too small to be harvested by recreational fishers. From the above evidence, it is not clear whether the current level of fishing pressure is likely to cause the stock to become recruitment overfished. Hence, there is insufficient information available to confidently classify the status of this stock.

On the basis of the evidence provided above, Southern Sand Flathead in Victoria is classified as an undefined stock.  

Tasmania 

In Tasmanian waters, Southern Sand Flathead are mainly landed commercially by hook-and-line fishers, with minor catches taken by gillnet and Danish-seine. Total landings are low, typically less than 15 t per year6. Recreational catches of Southern Sand Flathead are substantially higher (around 300 t); the species dominates the recreational fishery in terms of overall catch numbers and weight7. Catch-curve analysis suggests that exploitation rates of legal sized fish are highest in the south-east of the state, and there are anecdotal reports of declining catch rates in some areas. However, juvenile fish appear to be abundant, and the legal minimum length is set well above the size at maturity to prevent recruitment overfishing 6. Because of a lack of quantitative commercial fishing data and uncertainty surrounding the activities of the recreational fishery, there is currently insufficient information available to confidently classify the status of this stock.

On the basis of the evidence provided above, Southern Sand Flathead in Tasmania is classified as an undefined stock.


Table 2: Southern Sand flathead biology8–10

Longevity and maximum size

23 years (both sexes); males 370 mm TL; females 480 mm TL

Maturity (50%)

Males 2.5–3.5 years, 210 mm TL; females 2.6–5.2 years, 235 mm TL


TL = total length


Figure 1: Distribution of reported commercial catch of Southern Sand Flathead in Australian waters, 2013 (calendar year)
Figure 1: Distribution of reported commercial catch of Southern Sand Flathead in Australian waters, 2013 (calendar year)



Table 3: Main features and statistics for Southern Sand Flathead fisheries in Australia, 2013 (calendar year)

Jurisdiction

Victoria

Tasmania

Fishing methods

Commercial

Gillnet

Haul seine

Trawl

Danish-seine

Hand line

Longline

Recreational

Rod and line

Diving

Indigenousa

Hand line

Management methods

Commercial

Limited entry

Vessel restrictions

Spatial closures

Size limits

Recreational

Bag limits

Size limits

Indigenousa

Bag limits

Size limits

Active vessels

4 in CIF

8 in ITF

1 in OF

15 in PPBF

55 in SF

Catch

Commercial

<4.0 t in CIF

1.0 t in ITF

<0.1 t in OF

1.3 t in PPBF

6.2 t in SF

Recreational

115 t (2006–07)

279 t (2007–08)

Indigenous

None

None

Markets

Domestic

Export


CIF = Corner Inlet Fishery (Victoria); ITF = Inshore Trawl Fishery (Victoria); OF = Ocean Fishery (Victoria); PPBF = Port Phillip Bay Fishery (Victoria); SF = Scalefish Fishery (Tasmania)

a In Victoria, regulations for managing recreational fishing are also applied to fishing activities by Indigenous people. Recognised Traditional Owners (groups that hold native title or have agreements under the Victorian Traditional Owner Settlement Act 2010) are exempt (subject to conditions) from the requirement to hold a recreational fishing licence, and can apply for permits under the Fisheries Act 1995 that authorise customary fishing (e.g. different catch and size limits, or equipment). The Indigenous category in Table 3 refers to customary fishing undertaken by recognised Traditional Owners. In 2012–13, there were no applications for customary fishing permits to access Southern Sand Flathead.


Figure 2: Commercial catch of Southern Sand Flathead in Australian waters, 2000 to 2013 (calendar years)
Figure 2: Commercial catch of Southern Sand Flathead in Australian waters, 2000 to 2013 (calendar years)



Effects of fishing on the marine environment
  • Because most of the catch (95 per cent) is taken by recreational anglers using hand lines, and rods and reels, the effects of fishing on the marine environment are relatively low.

Environmental effects on Southern Sand Flathead
  • A recent review concluded that declining recruitment from the mid-1990s onwards led to the decline of Southern Sand Flathead stocks in Port Phillip Bay from 2000 onwards. This decline in recruitment coincided with a prolonged drought in Victoria from 1997 to 2009, characterised by substantially lower rainfall and river flows3. The authors found that recruitment in Port Phillip Bay was significantly correlated with Yarra River flows during November and December, when the majority of Southern Sand Flathead larvae occur in the water column. It is suggested that climatic effects on this stage of the life cycle may be driving variations in recruitment.



a Department of Environment and Primary Industries, Victoria
b Institute for Marine and Antarctic Studies, University of Tasmania
c South Australian Research and Development Institute