Yellowtail Kingfish Seriola lalandi

Michael Lowrya, Brett Molonyb, Malcolm Keagc and Andrew Penneyd


Yellow Kingfish

Table 1: Stock status determination for Yellowtail Kingfish

Jurisdiction

Commonwealth, New South Wales, Queensland, Commonwealth

Western Australia

Stock

Eastern Australian

(CTS, GHaTS, HSN, OTLF, RRFFF)

Western Australian

(JASDGDLMF, OA, SCEMF, WCDSIMF)

Stock status

   

Undefined

Undefined

Indicators

Commercial catch rates, fishing mortality, yield per recruit analysis

Catch


CTS = Commonwealth Trawl Sector; GHaTS = Gillnet, Hook and Trap Sector (Commonwealth); HSN = High Seas Non-Trawl (Commonwealth); JASDGDLMF = Joint Authority Southern Demersal Gillnet and Demersal Longline Managed Fishery (Western Australia); OA = Open Access (Western Australia); OTLF = Ocean Trap and Line Fishery (New South Wales); RRFFF = Rocky Reef Fin Fish Fishery (Queensland); SCEMF = South Coast Estuarine Managed Fishery (Western Australia); WCDSIMF = West Coast Demersal Scalefish (Interim) Managed Fishery (Western Australia)


Stock Structure

Yellowtail Kingfish is known to be a highly mobile and wide-ranging species, with a distribution extending throughout temperate waters of the Pacific and Indian Oceans1. In Australian waters, they are distributed from southern Queensland to central Western Australia, including the east coast of Tasmania, and around Lord Howe and Norfolk Islands. Results from the New South Wales gamefish tagging program, which has operated since 1973, suggest that New South Wales and Queensland populations are genetically mixed2–5. Recaptured Yellowtail Kingfish have shown extensive movements along the north-east coast of Australia, and between Australia and New Zealand. The most recent genetic evaluation of stock structure studies4 provided definitive evidence of separate east and west coast populations, but noted the need for further work to identify finer-scale population structure in the eastern and central region. Stock status in this chapter is reported at the level of the eastern Australian and western Australian biological stocks.


Stock Status

Eastern Australian biological stock 

The cross-jurisdictional eastern Australian biological stock occurs throughout Commonwealth waters, 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 the three jurisdictions.

Reported catch from the Queensland fishery is relatively minor, ranging from 3 to 11 tonnes (t) per year over the period 2004 to 2013. Recreational charter catch was estimated to be around 1 t, but limited information is available regarding the broader noncharter recreational catch.

Commonwealth fisheries comprise a relatively small catch of Yellowtail Kingfish across a number of fisheries. For the period 2000 to 2013, catch fluctuated between about 5 t and 64 t, averaging around 25 t per year. More than 80 per cent (23.6 t) of the catch in 2013 was taken using hook and line (dropline, autoline and bottom line) on the northern West Norfolk Rise, mainly when targetting Blue Eye Trevalla (Hyperoglyphe antarctica). A further 4.2 t (15 per cent of the catch in 2013) was caught as bycatch in the Commonwealth Trawl Sector, and less than 1 t was caught in the Commonwealth south-east Gillnet, Hook and Trap Sector. There are no specific management arrangements for Yellowtail Kingfish in Commonwealth fisheries. No data other than catch and effort are collected, and no Commonwealth assessment has been conducted for this stock.

Information on the eastern Australian stock is therefore primarily based on catch information from New South Wales. Catch rates and size compositions of commercial landings from the New South Wales component of the biological stock are assessed annually. Yellowtail Kingfish are currently assessed as being growth overfished in New South Wales waters, despite an increase in minimum legal length from 60 to 65 cm in 2007. However, New South Wales commercial landings in 2013 (around 83 t) are now substantially lower than the average during the late 1980s (more than 500 t per year). As well, commercial median catch rates (kilograms per day of line fishing) have increased from around 3 kg per day in the mid-1990s to an average of more than 22 kg per day since 2009. Although the fishery continues to be based largely on juveniles, the size composition in commercial landings has remained relatively stable since the 1990s, except for the effect of increasing the minimum legal length in 2007. The above evidence indicates that this stock is unlikely to be recruitment overfished.

However, there have been no age composition estimates since 20016. This analysis, which used age data from 1998 to 2000, indicated that fishing mortality was likely to be greater than natural mortality, and the spawning potential ratio was likely to be below the 20 per cent limit reference point 6. These estimates, which are based on data that are around 15 years old7, are outdated, but length composition data suggest that there have been no major changes to the fishery during the last 15 years. The limited information on the quantities or sizes of Yellowtail Kingfish harvested by the recreational fishery in New South Wales since 2000 results in considerable uncertainty around estimates of total fishing mortality. As a result of the conflicting evidence above, and the substantial uncertainty around total mortality levels, there is insufficient information available to confidently classify the status of this stock.

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

Western Australian biological stock 

Yellowtail Kingfish are not commonly encountered in Western Australia. As a result, there is no commercial targeting of Yellowtail Kingfish and limited recreational effort focused on this species in Western Australia. Commercial catches of Yellowtail Kingfish have always been low (less than 1 t), and an estimated 11 t was reported from the state in 2013 (1 t commercial; 10 t recreational). As a result, insufficient information is available to 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: Yellowtail Kingfish biology6,7

Longevity and maximum size

20+ years; 1900 mm FL

Maturity (50%)

5–10 years; 800–1250 mm FL


FL = fork length


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



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

Jurisdiction

Commonwealth

New South Wales

Queensland

Western Australia

Fishing methods

Commercial

Trolled baits

Lures

Rod and line

Trawl

Recreationala

Trolled baits

Lures

Rod and line

Spearfishing

Indigenousb,c

Trolled baits

Lures

Rod and line

Spearfishing

Management methods

Commercial

Limited entry

Size limits

Vessel restrictions

Spatial closures

Recreationala

Bag limits

Size limits

Spatial closures

Gear restrictions

Indigenousb,c,d,e

Bag limits

Size limits

Spatial closures

Gear restrictions

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

Active vessels

 

10 in CTS

7 in GHaTS

2 in HSN

148 in OTLF

58 in RRFFF

2 in JASDGDLMF

11 in OA

1 in SCEMF

5 in WCDSIMF

Catch

Commercial

4.2 t in CTS

0.7 t in GHaTS

23.6 t in HSN

83 t in OTLF

11 t in RRFFF

<0.1 t in JASDGDLMF

<0.1 t in OA

<0.1 t in SCEMF

<0.5 t in WCDSIMF

Recreationala

180 t (2000–01)

1 t

10 t

Indigenousb

Unknown

Unknown

Unknown

Markets

Domestic

Export


CTS = Commonwealth Trawl Sector; GHaTS = Gillnet, Hook and Trap Sector (Commonwealth); HSN = High Seas Non-Trawl (Commonwealth); JASDGDLMF = Joint Authority Southern Demersal Gillnet and Demersal Longline Managed Fishery (Western Australia); OA = Open Access (Western Australia); OTLF = Ocean Trap and Line Fishery (New South Wales); RRFFF = Rocky Reef Fin Fish Fishery (Queensland); SCEMF = South Coast Estuarine Managed Fishery (Western Australia); WCDSIMF = West Coast Demersal Scalefish (Interim) Managed Fishery (Western Australia)

a 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.

b 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.

c 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.

d 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.

e 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 (NSW), section 37(1)(c1) (Aboriginal cultural fishing authority).


Figure 2: Commercial catch of Yellowtail Kingfish in Australian waters, 2000 to 2013 (calendar years)
Figure 2: Commercial catch of Yellowtail Kingfish in Australian waters, 2000 to 2013 (calendar years)



Effects of fishing on the marine environment
  • Beyond the removal of fish, there is little evidence to suggest that the fisheries targeting Yellowtail Kingfish impact significantly on benthic or pelagic ecological communities in the area as a whole.

Environmental effects on Yellowtail Kingfish
  • Climate change and climate variability have the potential to impact fish stocks in a range of ways, including geographic distribution (for example, latitudinal shifts in distribution). Yellowtail Kingfish are known to respond rapidly to wind-induced shifts in current patterns. However, it is unclear how climate change may affect risks to sustainability of Yellowtail Kingfish.



a Department of Primary Industries, New South Wales
b Department of Fisheries, Western Australia
c Department of Agriculture, Fisheries and Forestry, Queensland
d Australian Bureau of Agricultural and Resource Economics and Sciences