Southern Garfish Hyporhamphus melanochir

Mike Steera, Corey Greenb, Jeremy Lylec and Kim Smithd


Southern Garfish

Table 1: Stock status determination for Southern Garfish

Jurisdiction

South Australia

Stock

West coast

(MSF)

Southern Spencer Gulf

(MSF, NZRLF)

Northern Spencer Gulf

(MSF)

Southern Gulf St Vincent

(MSF, SZRLF)

Northern Gulf St Vincent

(MSF, SZRLF)

South-east

(MSF, SZRLF)

Stock status

Undefined

Undefined

Transitional–depleting

Undefined

Transitional–depleting

Undefined

Indicators

None

None

Harvest fraction, egg production, biomass

None

Harvest fraction, egg production, biomass

None


MSF = Marine Scalefish Fishery (South Australia); NZRLF = Northern Zone Rock Lobster Fishery (South Australia); SZRLF = Southern Zone Rock Lobster Fishery (South Australia)

 

Table 1 continued

Jurisdiction

Western Australia

Victoria

Tasmania

Stock

West coast

(CSFNMF)

South coast

(OA, SCEMF)

Victoria

(CIF, OF, PPBF)

SF

Stock status

       

Undefined

Undefined

Sustainable

Undefined

Indicators

Catch, CPUE

None

Catch, effort, CPUE trends

Catch, effort, CPUE trends, age composition


CIF = Corner Inlet Fishery (Victoria); CPUE = catch per unit effort; CSFNMF = Cockburn Sound Fish Net Managed Fishery (Western Australia); OA = Open Access (Western Australia); OF = Ocean Fishery (Victoria); PPBF = Port Phillip Bay Fishery (Victoria); SCEMF = South Coast Estuarine Managed Fishery (Western Australia); SF = Scalefish Fishery (Tasmania)


Stock Structure

Southern Garfish has a wide distribution in Australia, extending from Lancelin in Western Australia along the southern coast of mainland Australia and up the east coast to Eden in southern New South Wales, as well as the surrounding waters of Tasmania1.

A multidisciplinary otolith-based study (otolith chemistry and morphometrics) identified at least five biological stocks in South Australia: west coast, northern Spencer Gulf, southern Spencer Gulf, northern Gulf St Vincent and southern Gulf St Vincent2. Given the level of spatial separation of Southern Garfish observed within the gulfs, it was assumed that Southern Garfish from the south-east also comprised a distinct biological stock. From recent stock assessments, most of the biomass exists in the northern gulfs: northern Spencer Gulf and northern Gulf St Vincent. The remaining biological stocks have generally produced relatively low catches. For South Australia, status is reported at the level of the six individual biological stocks.

Differences in size and age composition between the north and east coasts of Tasmania suggest that there may be multiple biological stocks; however, no firm evidence exists at present, and current stock assessments assume a single statewide biological stock3. Status for Southern Garfish in Tasmania is reported at the level of this assumed single biological stock.

There has been no research into the stock structure for Western Australian populations of Southern Garfish. However, given the limited dispersal capabilities of Southern Garfish, and the large spatial separation between the west and south coasts of Western Australia, it is likely that the west and south coast host separate biological stocks of this species. Furthermore, the majority of west coast landings are from Cockburn Sound, and the majority of south coast landings are from Wilson Inlet. Garfish spawn within Wilson Inlet, thus maintaining a self-sustaining population within this estuary, which is usually separated from the ocean by a sand bar. Hence, status is reported at the level of the west and south coast biological stocks.

There has been no research into the stock structure for Victorian populations of Southern Garfish. Therefore, Southern Garfish in Victoria is assessed at the jurisdictional level.


Stock Status

West coast (South Australia) biological stock 

A negligible amount of Southern Garfish is landed by the commercial sector on the west coast of South Australia, with the contribution to the statewide catch rarely exceeding 2 per cent. Consequently, there is insufficient information available to confidently classify the status of this stock.

On the basis of the evidence provided above, the biological stock is classified as an undefined stock.  

Southern Spencer Gulf (South Australia) biological stock 

Large areas of southern Spencer Gulf have been closed to commercial hauling-net fishing, with the most recent closure implemented in 2005. Consequently, the hauling-net sector has been effectively removed from this region, which is now mainly fished by commercial dab netters. The relative contribution of this region to the statewide catch has decreased to less than 5 per cent. Fishing effort has also substantially decreased (47 per cent) in the dab net sector over the past 4 years. Given the relatively small size of this regional fishery, it is difficult to access meaningful quantities of Southern Garfish to ascertain trends in the local population demography. Hence, there is insufficient information available to confidently classify the status of this stock.

On the basis of the evidence provided above, the biological stock is classified as an undefined stock.  

Northern Spencer Gulf (South Australia) biological stock 

The northern Spencer Gulf biological stock has been the most productive for Southern Garfish in South Australia since 1983, typically contributing to more than half of the statewide catch. This stock is exclusively commercially fished by the hauling-net sector. The most recent assessment4 assessed three types of performance indicators: commercial catch rates; age-length frequency distributions; and model-based assessments of exploitation rate, egg production and fishable biomass. Catch rates have trended upwards since 1999. The composition of the commercial harvest is dominated by 1 year old plus and 2 year old plus Southern Garfish, indicating that the population structure has remained severely truncated as a result of sustained levels of high exploitation (higher than 65 per cent). Despite this, both fishable biomass and egg production remained relatively stable at moderate levels from 2003 to 2011. Consequently, the stock is not yet considered to be in a recruitment overfished state. However, the current level of fishing pressure has the potential to cause the stock to become recruitment overfished. New statewide harvest strategies have recently (2012) been implemented to promote the recovery of the stock, by reducing the harvest fraction and increasing egg production through a combination of effort (spatial closures) and gear-based (increased hauling-net mesh size) restrictions. It is too early to assess the flow-on effects of these strategies. Proportional strategies are currently being developed for the recreational sector.

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

Southern Gulf St Vincent (South Australia) biological stock 

Before 1993, the commercial catch of Southern Garfish from southern Gulf St Vincent was equally shared among the hauling-net and dab-net sectors. Since then, the hauling-net sector has declined, with a steady reduction in fishing effort, and, by 2006, dab nets had become the dominant gear type. This dominance was accelerated by the implementation of a voluntary net buy-back scheme and spatial netting closures in 2005. Before this management restructure, the commercial Southern Garfish catch from the region rarely exceeded 10 per cent of the statewide harvest; after its implementation, catch decreased to less than 5 per cent. Like southern Spencer Gulf, little is known about the size and age structures of the commercial catch of Southern Garfish in southern Gulf St Vincent, as it is difficult to access adequate biological samples from this relatively small regional fishery. Hence, there is insufficient information available to confidently classify the status of this stock.

On the basis of the evidence provided above, the biological stock is classified as an undefined stock.  

Northern Gulf St Vincent (South Australia) biological stock 

Northern Gulf St Vincent has historically been the second most productive region in the state, accounting for an average of 35 per cent of South Australia’s annual Southern Garfish catch. The most recent assessment4 used three types of performance indicators: commercial catch rates; age-length frequency distributions; and model-based assessments of exploitation rate, egg production and fishable biomass. Like the adjacent Northern Spencer Gulf biological stock, the Southern Garfish population in northern Gulf St Vincent is severely truncated as a result of sustained levels of exploitation (higher than 60 per cent). The recent trends in fishable biomass and egg production have remained relatively stable over the past decade, indicating that the stock is not yet considered to be recruitment overfished. However, this continued level of fishing pressure has the potential to cause the stock to become recruitment overfished. New statewide harvest strategies have recently (2012) been implemented to promote the recovery of the stock, by reducing the harvest fraction and increasing egg production through a combination of effort (spatial closures) and gear-based (increased hauling-net mesh size) restrictions. It is too early to assess the flow-on effects of these strategies. Proportional strategies are currently being developed for the recreational sector.

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

South-east (South Australia) biological stock 

Very few Southern Garfish are landed by the commercial sector in the south-east; the statewide contribution rarely exceeds 0.3 per cent. Consequently, there is insufficient information available to confidently classify the status of this stock.

On the basis of the evidence provided above, the biological stock is classified as an undefined stock.  

West coast (Western Australia) biological stock 

From 2009 to 2013, 87 per cent of west coast commercial landings of Southern Garfish were from Cockburn Sound. This represented 47 per cent of total Western Australian commercial landings of this species. The Southern Garfish catch and catch per unit effort (CPUE) in Cockburn Sound followed a declining trend from 2002 to 2013. Both catch and CPUE reached a historically low level in 2013 (that is, the lowest since the early 1970s, when the fishery commenced). Catch and CPUE indicators suggest that stock abundance is currently relatively low in Cockburn Sound. A new assessment, based on age-structure information, is under way to provide a better understanding of the status of this stock. Currently, insufficient information is available to confidently classify the status of this stock.

On the basis of the evidence provided above, the biological stock is classified as an undefined stock.  

South coast (Western Australia) biological stock 

From 2009 to 2013, 58 per cent of south coast commercial landings of Southern Garfish were from Wilson Inlet. This represented 27 per cent of total Western Australian commercial landings of this species. Over this period, the catch in this estuary ranged from 3 to 10 tonnes (t) per year. The remainder of south coast landings each year comprised multiple small catches from other estuarine and coastal fisheries. From 2002 to 2013, the annual catch in Wilson Inlet followed an increasing trend, suggesting that the biomass has remained stable and that this stock is unlikely to be recruitment overfished. However, insufficient information is available to confidently classify the status of this stock.

On the basis of the evidence provided above, the biological stock is classified as an undefined stock.  

Victoria 

The commercial catch rate for Southern Garfish in Victoria has been relatively stable for the past 35 years. The majority (58 t) of the commercial catch of Southern Garfish comes from Corner Inlet, where catch rates vary annually but have been relatively stable since the early 1990s5. The majority of the recreational catch of Southern Garfish comes from Port Phillip Bay. In 2000–01, it was estimated that 25 t was taken by the Victorian recreational fishery, constituting 3.4 per cent of the statewide recreational catch in marine waters6. Recreational catch rates of Southern Garfish by avid and non‐avid anglers in Port Phillip Bay have declined slightly since 20045. Available fishery and scientific data indicate that the fishery is performing within its historical range, based on total annual catch and catch rate. The above evidence indicates that the biomass of this stock is unlikely to be recruitment overfished and the current level of fishing pressure is unlikely to cause the stock to become recruitment overfished.

On the basis of the evidence provided above, Southern Garfish in Victoria is classified as a sustainable stock.  

Scalefish Fishery (Tasmania) biological stock 

From 1995–96 to 2005–06, commercial catches in the Scalefish Fishery (Tasmania) were stable and typically between 80 and 100 t. They have generally been less than 60 t in the past 6 years3. This coincides with a decline in average size and truncation of age classes of the catch, which may have resulted from heavy fishing pressure and/or a period of poor recruitment3. As a result, seasonal closures were introduced in 2009 to protect spawning fish. Since then, there has been an increase in the size of Southern Garfish captured, a greater variety of age classes present in the catch and increasing CPUE. This provides some evidence that the stock is recovering. At present, however, insufficient information is available to confidently classify the status of this stock.

On the basis of the evidence provided above, the biological stock is classified as an undefined stock.


Table 2: Southern Garfish biology7

Longevity and maximum size

South Australia: 10 years; 380 mm TL

Tasmania: 9.5 years; 460 mm TL

Maturity (50%)

Western Australia: 19 months; 230 mm TL

South Australia: 18 months; 190 mm TL

Victoria: 19 months; 210 mm TL

Tasmania: 22 months; 200 mm TL


TL = total length


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



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

Jurisdiction

Western Australia

South Australia

Victoria

Tasmania

Fishing methods

Commercial

Hauling nets (seine)

Beach seine

Mesh (gill) net

Dab (landing) nets

Hand line

Recreational

Rod and line

Hand line

Dab (landing) nets

Beach seine

Indigenousa

Hand line

Unknown

Unknown

Dab nets

Unknown

Unknown

Management methods

Commercial

Limited entry

Size limits

Gear restrictions

Vessel restrictions

Effort limits

Spatial closures

Temporal closures

Recreational

Licensing

Bag limits

Size limits

Gear restrictions

Indigenousa,b

Bag limits

Size limits

Active commercial vessels

 

1 in CSFNMF

18 in OA

17 in SCEMF

91 in MSF

6 in NZRLF and SZRLF combinedc

16 in CIF

2 in OF

23 in PPBF

22 in SF

Catch

Commercial

4 t in CSFNMF

3 t in OA

11 t in SCEMF

249.7 t in MSF

0.7 t in NZRLF and SZRLF combinedc

58 t in CIF

Confidential in OFd

6 t in PPBF

48.8 t in SF

Recreational

2 t (vessel based only)

75 t (2007–08 survey)

21 t (2006–07)

2 t (in 2007–08 survey)

Indigenousa

Unknown

Unknown

Unknown

Markets

Domestic

Export


CIF = Corner Inlet Fishery (Victoria); CSFNMF = Cockburn Sound Fish Net Managed Fishery (Western Australia); MSF = Marine Scalefish Fishery (South Australia); NZRLF = Northern Zone Rock Lobster Fishery (South Australia); OA = Open Access (Western Australia); OF = Ocean Fishery (Victoria); PPBF = Port Phillip Bay Fishery (Victoria); SCEMF = South Coast Estuarine Managed Fishery (Western Australia); SF = Scalefish Fishery (Tasmania); SZRLF = Southern Zone Rock Lobster Fishery (South Australia)

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 Garfish.

b Subject to the defence that applies under section 211. of the Native Title Act 1993 (Cth), and the exemption from a requirement to hold a recreational fishing licence, the non-commercial take by indigenous fishers is covered by the same arrangements as that for recreational fishing.

c Data for the Northern Zone Rock Lobster Fishery (South Australia) and the Southern Zone Rock Lobster Fishery (South Australia) have been combined because of confidentiality requirements.

d To protect commercial confidentiality of data, the catch in the OF cannot be reported because there are fewer than five licence holders.


Figure 2: Commercial catch of Southern Garfish in Australian waters, 2003 to 2013 (calendar years)
Figure 2: Commercial catch of Southern Garfish in Australian waters, 2003 to 2013 (calendar years)

Note: Western Australian data were not provided at the level of the individual stocks reported in the Southern Garfish chapter. To protect commercial confidentiality of data, the catch in the OF (Victoria) cannot be reported because there are fewer than five licence holders.




Effects of fishing on the marine environment
  • The hauling nets used to target Southern Garfish are typically lightweight, and consist of a ‘pocket’ end and lateral ‘wings’. The wings, which generally have a smaller mesh size than the pocket, are specifically designed to herd fish inhabiting surface waters into the pocket of the net, rather than enmesh them throughout the entire water column. Fish that accumulate within the pocket are manually brailed out with a hand-held net, and are released or retained at the discretion of the fisher. The design and performance of these hauling nets ensures that post-release mortality of incidental bycatch is reduced, as nontargeted species can be released alive and in relatively good condition8. There is no indication that these lightweight nets adversely interrupt the normal ecological processes of fish and invertebrates that occupy shallow seagrass habitats 9.


Environmental effects on Southern Garfish
  • The impact of environmental factors on Southern Garfish stocks is unknown.


a South Australian Research and Development Institute
b Department of Environment and Primary Industries, Victoria c Institute of Marine and Antarctic Studies, Tasmania d Department of Fisheries, Western Australia