Grey Mackerel Scomberomorus semifasciatus

Anthony Roelofsa, Grant Johnsonb and Stephen Newmanc


Grey Mackerel

Table 1: Stock status determination for Grey Mackerel

Jurisdiction

Queensland

Queensland, Northern Territory

Northern Territory

Western Australia

Stock

Central east Queensland (ECIFFF)

North-east Queensland (ECIFFF)

Gulf of Carpentaria (GOCIFF, ONLF)

North-west Northern Territory (ONLF)

Western Australian

(MMF)

Stock status

         

Sustainable

Sustainable

Sustainable

Sustainable

Sustainable

Indicators

Quantitative stock assessment, biomass, fishing mortality, catch, catch rate

Quantitative stock assessment, biomass, fishing mortality, catch, catch rate

Stock reduction analysis, fishing mortality, catch, catch rate

Stock reduction analysis, fishing mortality, catch, catch rate

Catch, population dynamics, catch rate


ECIFFF = East Coast Inshore Fin Fish Fishery (Queensland); GOCIFF = Gulf of Carpentaria Inshore Fin Fish Fishery (Queensland); MMF = Mackerel Managed Fishery (Western Australia); ONLF = Offshore Net and Line Fishery (Northern Territory)


Stock Structure

There are at least five Grey Mackerel biological stocks across northern Australia, with a possible additional stock in the north-east Gulf of Carpentaria1–5. The five biological stocks are Western Australia, north-west Northern Territory (Timor/Arafura), Gulf of Carpentaria, north-east Queensland and central east Queensland. The status of Grey Mackerel has been determined at the level of these five biological stocks.


Stock Status

Central-east Queensland biological stock 

The central east Queensland biological stock is managed as part of a Queensland east coast–wide fishery. The most recent stock assessment6 did not detect any trend in east coast Grey Mackerel abundance that might indicate overfishing at the east coast–wide level, or find evidence to advocate against the current fishery-wide total allowable commercial catch (TACC) of 250 tonnes (t). The stock assessment (2011 data) for the central east Queensland stock estimated the maximum sustainable yield (MSY) at approximately 90 t (80 per cent confidence interval: 70 to 130 t) and recommended a TACC of 70 t. Grey Mackerel is primarily a commercial net-caught species6; an average of 3 per cent of catches each year since 2003 have been taken by line fishing. The stock assessment estimated that the biomass of the central east Queensland stock in 2011 was equal to the biomass associated with MSY (BMSY). Harvest levels for the commercial net fishery since 2011 (57 t in 2012; 53 t in 2013) were lower than the estimated MSY and the recommended TACC. Given this evidence, the biomass of the stock is not considered to be recruitment overfished.

Fishing pressure (days fished) on the central east coast has been low in recent years following the introduction of the current fishery-wide TACC of 250 t (an average of 93 net-fishing days from 2003 to 2009, and 61 days from 2010 to 2013). Fishery-dependent biological monitoring of central east Queensland Grey Mackerel indicates consistent recruitment in the fishery, with stable length and age frequencies6,7 . Estimates of fishing mortality are below natural mortality. This suggests stable levels of fishing pressure since 20086. This level of fishing pressure is unlikely to cause the stock to become recruitment overfished.

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

North-east Queensland biological stock 

The north-east Queensland biological stock is managed as part of a Queensland east coast–wide fishery. The most recent stock assessment6 did not detect any trend in east coast Grey Mackerel abundance that might indicate overfishing at the east coast–wide level and found no evidence to advocate against the current fishery-wide TACC. However, uncertainty in the model outputs, particularly for the north-east Queensland stock, prompted the authors to suggest a conservative approach to sustainable yield estimates and subsequent TACC for this stock. The stock model estimated that MSY for the north-east Queensland stock ranged from 100 to 150 t and recommended a TACC of 100 t. The authors also indicated that there was flexibility in the proposed TACC, given the level of model uncertainty. The stock assessment estimated that the biomass of the north-east Queensland stock in 2011 was at levels close to B MSY (noting the uncertainty in the model outputs). Commercial net harvest levels in 2013 (126 t) were above the recommended TACC but within the range of MSY, and average annual harvest levels since 2010 (113 t) of the north east Queensland biological stock have been close to the recommended TACC, following the introduction of the fishery-wide TACC of 250 t on 1 July 20097. Given this evidence, the biomass of the stock is not considered to be recruitment overfished.

Fishery-dependent biological monitoring indicates that length and age frequencies in the north-east stock have been stable since monitoring commenced in 20086. Estimates of total mortality have been below the threshold (double the natural mortality) since 2009. This suggests stable levels of fishing pressure since 20086, and it is unlikely that the current level of fishing pressure will cause the stock to become recruitment overfished.

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

Gulf of Carpentaria biological stock 

Grey Mackerel in the Gulf of Carpentaria is primarily a commercial net-caught species. Queensland and the Northern Territory share management of the Gulf of Carpentaria biological stock through the Queensland Fisheries Joint Authority. Queensland takes the majority of the commercial harvest (average 80–95 per cent).

There has been a rising trend in commercial catch rate since targeted fishing of Grey Mackerel began in the Gulf of Carpentaria in the late 1990s. Queensland catches and catch rates reached record levels in 2010 and 2012, respectively. Although the Queensland catch rate dropped in 2013, the rate (54 kg/100-m net) was still above the previous 10-year average (52 kg/100-m net)7. A stock reduction analysis of Grey Mackerel in the Gulf of Carpentaria, using Queensland and Northern Territory catches, concluded that the biomass in 2011 was at 74 per cent of the unfished biomass, and the harvest rate was 26 per cent of that required to achieve MSY8. The biomass of this stock is not considered to be recruitment overfished.

Queensland introduced changes to the net fishery at the beginning of the 2012 season to reduce pressure on Grey Mackerel. The measures decreased the total length of available net for the Queensland component of the stock by two-thirds, from 27 km to 9 km, in the offshore component of the fishery. Changes to the Queensland inshore fishery (within 7 nautical mile of the coast) also reduced the capacity for boats to target Grey Mackerel. Commercial catches and catch rates in 2013 were below the 5‑year average for the Queensland component of the Gulf of Carpentaria stock. Given this evidence, the current allowable level of fishing pressure is unlikely to cause the stock to become recruitment overfished.

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

North-west Northern Territory biological stock 

Grey Mackerel has been assessed at the jurisdictional level for the north-west Northern Territory stock8. Assessments indicate that Grey Mackerel stocks in the Northern Territory declined substantially as a result of high Taiwanese catches in the 1970s and 1980s, but have since recovered, with the cessation of foreign fishing and more stringent management of the domestic fishery. In 2010, egg production was estimated at 74 per cent of unfished levels, which is well within sustainable limits for productive species such as Grey Mackerel8. Supporting this assessment is that catch per unit effort has increased over the past 10 years, while catches have remained relatively consistent8–10. Grey Mackerel in the north-west Northern Territory stock 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 biological stock is classified as a sustainable stock.  

Western Australian biological stock 

Grey Mackerel is exploited as a component of the Mackerel Managed Fishery of Western Australia5. The primary target species of the Mackerel Managed Fishery is Spanish Mackerel (Scomberomorus commerson). Grey Mackerel is therefore assessed on the basis of the status of the indicator species (Spanish Mackerel), which represents the pelagic suite of species. A stock assessment of Spanish Mackerel—examining catch-and-effort data, biological information, biomass and yield per recruit modelling—indicated that this stock is sustainable11. In addition, Grey Mackerel are fast growing and have a young age at sexual maturity (less than 2 years) 4,12,13, indicating some resilience to fishing pressure.

Grey Mackerel catch levels in the Mackerel Managed Fishery from 2000 to 2013 have been relatively low and stable, ranging between 10 and 24 t, with catches reported from only a small area of the Grey Mackerel range11 . This level of catch is well below the TACC (60 t for each of the three management areas) for Grey Mackerel. The low levels of catch are likely to reflect the gear limitations (line only) that apply to the fishery. The biomass of the stock is not considered to be recruitment overfished, and the level of fishing mortality is unlikely to cause the stock to become recruitment overfished.

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


Table 2: Grey Mackerel biology4,12,13

Longevity and Maximum size

12 years; 1200 mm TL

Maturity (50%)

Females: 2 years; 700 mm TL

Males: 1–2 years; 660 mm TL


TL = total length


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



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

Jurisdiction

Queensland

Northern Territory

Western Australia

Fishing methods

Commercial

Nets

Hand line

Rod and line

Recreational

Hand line

Rod and line

Spearfishing

Indigenousa,b

Hand line

Rod and line

Spearfishing

Management methods

Commercial

Limited entry

Size limits

Gear restrictions

Vessel restrictions

Total allowable catchb

Fishery spatial closures

Marine park closures

Spatial zoning

Total allowable effort

Recreational

Licensing

Possession limits

Bag limits

Size limits

Gear restrictions

Marine park closures

Spatial zoning

Charter

Limited entry

Passenger restrictions

Possession limits

Bag limits

Size limits

Marine park closures

Spatial zoning

Indigenousa,b

No limits on customary catch

Laws of general application

Active vessels

86 net and 20 line in ECIFFF

24 net in GOCIFFF

7 in ONLF

4 in MMF

Catch

Commercial

194 t in ECIFFFc,d

485 t in GOCIFFF

355 t in ONLF

11 t in MMF

Recreational

Unknown14

~10 t15

Unknown16

Charter

Unknown

173 fish (<1 t)

64 fish (<0.4 t)

Indigenous

Unknown

Unknown

Unknown

Markets

Domestic

Export


ECIFFF = East Coast Inshore Fin Fish Fishery (Queensland); GOCIFFF = Gulf of Carpentaria Inshore Fin Fish Fishery (Queensland); MMF = Mackerel Managed Fishery (Western Australia); ONLF = Offshore Net and Line Fishery (Northern Territory)

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 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
Limits apply to the combined catch of the two Queensland east coast stocks.

d
Includes minor levels of catch from the Bowen region, which is not considered part of the north-east Queensland and central east Queensland biological stocks.


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



Effects of fishing on the marine environment
  • Commercial gillnets have almost no impact on coastal habitat and are quite selective, with bycatch making up only a small proportion of the catch17. However, commercial gillnets do interact with threatened, endangered and protected species. Although reported interactions are low, the impact on the populations of these species is unknown.


Environmental effects on Grey Mackerel
  • The duration and magnitude of the wet season is likely to affect the overall biomass of coastal stocks such as Grey Mackerel that are dependent on near-shore waters for breeding and feeding18,19. A widespread drought in the Gulf of Carpentaria region in 2013 is thought to have affected the abundance of a number of commercially important species, including Grey Mackerel. Low rainfall in the southern Gulf of Carpentaria resulted in decreased freshwater flows, turbidity and primary productivity in near-shore areas, which are critical to Grey Mackerel larval survival and juvenile/adult feeding19. For other species, research has shown that large wet seasons result in higher recruitment than smaller wet seasons20,21. The fine-scale stock structure evident on the Queensland east coast may limit the adaptability of Grey Mackerel to changing environmental conditions if stocks are unable to move in response to changing conditions19.



a Department of Agriculture, Fisheries and Forestry, Queensland
b Department of Primary Industry and Fisheries, Northern Territory
c Department of Fisheries, Western Australia