Torres Strait (Commonwealth) biological stock
A formal stock assessment of Spanish Mackerel in the Torres Strait Spanish Mackerel Fishery (Commonwealth) was conducted in 2006, informed by data to 2003 4. The assessment uses a sex-specific age-structured population dynamics model to estimate biomass. A range of biological and effort reference points were assessed to evaluate various potential management strategies for the fishery. The assessment estimated that biomass in 2006 was 37 per cent (range 26–67 per cent) of the unfished level. Results of the assessment indicated that the base-case maximum sustainable yield (MSY) for Spanish Mackerel in the Torres Strait was 169 tonnes (t) per year, and annual catches of around 150 t per year would achieve a fishing mortality target of half natural mortality. The stock assessment concluded that the stock was likely to be harvested at levels near or exceeding MSY up to 2003. Catches since 2007–08 have been below both the base-case (169 t) and lower risk estimates of MSY5. The stock is therefore not considered to be recruitment overfished 6, and the current level of fishing mortality is unlikely to cause the stock to become recruitment overfished6.
On the basis of the evidence provided above, the biological stock is classified as a sustainable stock.
East coast (Queensland) biological stock
The east coast biological stock extends from Cape York in Queensland waters to its southern extent in northern New South Wales7, although New South Wales catches are limited8. The most recent stock assessment9 indicated that the 2009 estimate of biomass ranged from 36 to 54 per cent of the unfished level. Recent research, using commercial catch-and-effort data, describes a contraction in the spatial and temporal presence of spawning aggregations on the main commercial fishing grounds10, which may be a result of the vulnerable nature of transient spawning aggregations that form each year11. Potential serial depletion of these spawning aggregations may be a concern for the reproductive potential and size of the stock. However, the overall evidence indicates that the biological stock is unlikely to be recruitment overfished.
Total landings for the combined commercial and recreational catch for Queensland and New South Wales over the past few years have been below the lowest sustainable yield estimate (yield that sustains 1.2BMSY in the hyperstable model case) of 956 t, as well as below the lowest risk management yield estimate of 715 t9. In Queensland, introduction in 2004 of a total allowable catch and individual transferable quotas for the commercial fishery substantially reduced participation; in 2013, fishing effort was around the lowest level recorded in the past 25 years. Fishery-dependent monitoring data indicate a varied but continuous pattern of recruitment, and the estimate of total mortality rate in 2012–13 is less than twice the natural mortality rate12. This level of fishing mortality is unlikely to cause the biological stock to become recruitment overfished. However, given the proximity of stock levels to relevant reference points, the fact that an average of only 51 per cent of available quota has been harvested in the past 9 years, and uncertainty around the levels of recreational harvest, future harvests will need to be closely monitored.
On the basis of the evidence provided above, the biological stock is classified as a sustainable stock.
Gulf of Carpentaria (Queensland) management unit
The Gulf of Carpentaria (Queensland) management unit has a line and net component—the Gulf of Carpentaria Line Fishery and the Gulf of Carpentaria Inshore Fin Fish Fishery, respectively. Catch rates for both fisheries have continued to increase since the mid-1990s. Age-composition data from routine monitoring of line catches since 2007 are now available. The data indicate relatively consistent recruitment and age composition in the fishery, with the majority of line catches since 2007 comprising fish between 2 and 6 years of age. This evidence indicates that the biomass of the stock is unlikely to be recruitment overfished.
Total commercial landings are within historical harvest levels (238 t in 2013), with the majority taken by the line fishery (76 per cent in 2013). Landings in the line fishery have been relatively stable over the last 2 years; there have been stable catches in the net fishery over the past 4 years. Fishing effort in the line fishery has decreased substantially to a historical low in 2013. This evidence indicates that the current level of fishing mortality is unlikely to cause the stock to become recruitment overfished.
On the basis of the evidence provided above, the management unit is classified as a sustainable stock.
Northern Territory
Spanish Mackerel stocks have been assessed at a territory-wide level, including information up to 2011. The results indicated that stocks declined substantially because of high Taiwanese catches in the 1970s and 1980s, but have since recovered as a result of more stringent management. In 2011, egg production was estimated at around 85 per cent of unfished levels, which is well within sustainable limits for a species such as Spanish Mackerel, and it was suggested that increases in catch could occur13,14. This assessment is supported by increased catch rates over the past 10 years, with the 2012 value being the highest recorded in the fishery15. The evidence provided indicates that the biomass of this management unit is unlikely to be recruitment overfished and the current level of fishing mortality is unlikely to cause this management unit to become recruitment overfished.
On the basis of the evidence provided above, Spanish Mackerel in the Northern Territory is classified as a sustainable stock.
Mackerel Managed Fishery (Western Australia) management unit
Fishing effort throughout the Mackerel Managed Fishery (Western Australia) has been relatively stable since 2006, following reductions due to management changes. The high catch rates for the two main fishery areas, both near record levels, indicate a relatively high abundance of Spanish Mackerel in these management areas. Catch rates in other areas have remained stable at relatively high levels since 2007. As the minimum legal size for Spanish Mackerel is 900 mm total length, which is similar to the size at maturity for this species16, the spawning stock is essentially the same as the exploited stock. Therefore, the status of the Spanish Mackerel spawning stock is measured using the catch rates for each area of the fishery. Catch rates are either continuing to increase or are stable at relatively high levels within each management area, suggesting that the overall spawning stock is increasing. Additionally, the total catches of Spanish Mackerel remain within the target range. Spanish Mackerel in Western Australia is not considered to be recruitment overfished, and the current level of fishing mortality is unlikely to cause the stock to become recruitment overfished.
On the basis of the evidence provided above, the management unit is classified as a sustainable stock.
Figure 1: Distribution of reported commercial catch of Spanish Mackerel in Australian waters, 2013 (calendar year)
Note: Commercial catch data for the east coast (Queensland) and Torres Strait biological stocks are for the financial year (2012–13).
Table 3: Main features and statistics for Spanish Mackerel fisheries in Australia, 2013 (calendar year)
Jurisdiction |
Commonwealth (Torres Strait)a |
Queenslanda |
Northern Territory |
Western Australia |
Fishing methods |
Commercial |
Trolled baits |
✓ |
✓ |
✓ |
✓ |
Lures |
✓ |
✓ |
✓ |
✓ |
Hand line |
✓ |
✓ |
✓ |
✓ |
Gillnet |
|
✓ |
✓ |
|
Trawl |
|
|
✓ |
|
Recreationalb |
Trolled baits |
|
✓ |
✓ |
✓ |
Lures |
|
✓ |
✓ |
✓ |
Hand line |
|
✓ |
✓ |
✓ |
Spearfishing |
|
✓ |
✓ |
✓ |
Indigenousc–e |
Trolled baits |
|
✓ |
|
✓ |
Lures |
|
✓ |
|
✓ |
Hand line |
|
✓ |
✓ |
✓ |
Management methods |
Commercial |
Limited entry |
✓ |
✓ |
✓ |
✓ |
Size limits |
✓ |
✓ |
|
✓ |
Vessel restrictions |
✓ |
✓ |
✓ |
✓ |
Catch restrictions |
✓ |
✓ |
✓ |
✓ |
Effort limits |
|
|
✓ |
|
Spatial closures |
✓ |
✓ |
|
✓ |
Recreationalb |
Size limits |
|
✓ |
|
✓ |
Bag limits |
|
|
|
✓ |
Possession limits |
|
✓ |
✓ |
✓ |
Spatial closures |
|
✓ |
✓ |
✓ |
Gear restrictions |
|
✓ |
✓ |
|
Licensing |
|
|
|
✓ |
Charterb |
Licensing |
|
✓ (vessel) |
|
✓ |
Spatial zoning |
|
|
✓ |
✓ |
Spatial closures |
|
✓ |
✓ |
✓ |
Size limits |
|
✓ |
|
✓ |
Bag limits |
|
|
|
✓ |
Possession limits |
|
✓ |
✓ |
✓ |
Indigenousc–e |
|
|
|
None |
None |
Active vessels |
|
135 Traditional Inhabitant (TIB)f
5 non-TIB in TSSMF |
169 in ECSMF
22 in GOCIFFF
15 in GOCLF |
6 in DF
11 in NTSMF
12 in ONLF |
11 in MMF |
Catch |
Commercial |
83 t in TSSMF (2012–13) |
261 t in ECSMF (2012–13)
57 t in GOCIFFF
181 t in GOCLF |
0.2 t in DF
205 t in NTSMF
17 t in ONLF |
277 t in MMF |
Recreationalb |
|
272 t (2010) |
27 t (2010) plus
4 t by FTO |
89 t (2011–12) |
Indigenousc,d |
|
Negligible |
Unknown |
Unknown |
Markets |
Domestic |
✓ |
✓ |
✓ |
✓ |
Export |
✓ |
|
✓ |
|
DF = Demersal Fishery (Northern Territory); ECSMF = East Coast Spanish Mackerel Fishery (Queensland); FTO = Fishing Tour Operators (Northern Territory); GOCIFFF = Gulf of Carpentaria Inshore Fin Fish Fishery (Queensland); GOCLF = Gulf of Carpentaria Line Fishery (Queensland); MMF = Mackerel Managed Fishery (Western Australia); NTSMF = Northern Territory Spanish Mackerel Fishery (Northern Territory); ONLF = Offshore Net and Line Fishery (Northern Territory); TSSMF = Torres Strait Spanish Mackerel Fishery (Commonwealth)
a The reporting period for the Commonwealth (Torres Strait) and Queensland (east coast [Queensland]) is the 2012–13 financial year.
b The Australian Government does not manage recreational fishing, including charter fishing, in Commonwealth waters. Recreational and charter fishing in Commonwealth waters is managed by the state or territory immediately adjacent to those waters, under its management regulations.
c The Australian Government does not manage non-commercial Indigenous fishing in Commonwealth waters, with the exception of the Torres Strait. In general, non-commercial Indigenous fishing in Commonwealth waters is managed by the state or territory immediately adjacent to those waters. In the Torres Strait, both commercial and non-commercial Indigenous fishing is managed by the Torres Strait Protected Zone Joint Authority (PZJA) through the Australian Fisheries Management Authority (Commonwealth); the Department of Agriculture, Fisheries and Forestry (Queensland); and the Torres Strait Regional Authority. The PZJA also manages non-Indigenous commercial fishing in the Torres Strait.
d 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.
e 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.
f Total number of TIB licences; this is not an indicator of licence activity.
Figure 2: Commercial catch of Spanish Mackerel in Australian waters, 2001 to 2013 (calendar years)
Note: Commercial catch for the east coast (Queensland) and Torres Strait biological stocks is reported by financial year, with data for the 2012–13 year plotted against 2013.