Table 1: Stock status determination for School Prawn
Jurisdiction |
New South Wales |
Victoria |
Queensland |
Stock |
New South Wales
(EGF, EPTF, OTF-PS ) |
Victoria
(ITF) |
Queensland
(ECTF) |
Stock status |
|
|
|
Sustainable |
Undefined |
Undefined |
Indicators |
Catch, CPUE, environmental models, length frequencies |
Catch |
Catch, CPUE |
CPUE = catch per unit effort; ECTF = East Coast Trawl Fishery (Queensland); EGF = Estuary General Fishery (New South Wales); EPTF = Estuary Prawn Trawl Fishery (New South Wales); ITF = Inshore Trawl Fishery (Victoria); OTF-PS = Ocean Trawl Fishery–Prawn Sector (New South Wales)
School Prawn fisheries occur in New South Wales, Victoria and Queensland. Although recent genetic work on the biological stock structure of this species is limited, genetic differentiation has been reported between populations from southern Queensland (from the Noosa River and Tweed River) and populations from different estuaries in New South Wales (all of which were genetically homogeneous) 1 . Comparable genetic information for Victorian populations is limited. Since the biological stock structure of School Prawns remains largely unknown throughout their distribution, and a sample from any one location cannot always be considered as genetically representative of the species, stock status classifications for this species are reported at the jurisdictional level.
New South Wales
Despite a peak in median ocean prawn trawling catch rates during 2010–11, the median commercial catch rates of School Prawn in New South Wales have been relatively steady for the past 5 years (especially for the Estuary Prawn Trawl Fishery) and greater than in the previous 5 years (Figure 1). This species is commercially fished throughout most of its geographic range in New South Wales, although there has been limited harvest between latitudes 35 and 36°S in recent years.
Landings in New South Wales in 2013 (731.3 tonnes [t]) were similar to the long-term annual average (788.2 t) (Figure 1). The reported number of fisher days in 2013 in the Ocean Trawl Fishery–Prawn Sector (approximately 1389 days), the Estuary Prawn Trawl Fishery (approximately 3856 days) and the Estuary General Fishery (3562 days, summed across methods) were some of the lowest levels observed historically. Typical size compositions in landings in 2012–13 suggest little change in the stock. Although slightly fewer large prawns have been caught in the past 2 years, this shift is likely related to interannual changes in environmental conditions. Recent research and modelling have established that environmental factors (river flows) influence School Prawn landings 2 . The above evidence indicates that the biomass of this stock is unlikely to be recruitment overfished and that the current level of fishing pressure is unlikely to cause the stock to become recruitment overfished.
On the basis of the evidence provided above, School Prawn in New South Wales is classified as a sustainable stock.
Victoria
Since 2000, the total annual catch of School Prawn in Victoria has usually been between 5 and 15 t. Catches were relatively high (approximately 50 t) during 2011 and 2012, but returned to more average levels (16.7 t) in 2013 (Figure 1). Nearly all the catch is landed by vessels belonging to the Inshore Trawl Fishery, and, since 2008, a maximum of 10 vessels have participated in the fishery. The relatively low but variable levels of catch, and the absence of reliable estimates for current biomass and sustainable yield mean that there is insufficient information to confidently classify the status of this stock.
On the basis of the evidence provided above, School Prawn in Victoria is classified as an undefined stock.
Queensland
Long-term catch levels are variable (Figure 1), and nominal catch rates are fairly stable. There have been occasional very high catch and catch-rate years (for example, 2009) 3 . A recent ecological risk assessment found that School Prawn was at low risk of being overfished at 2009 effort levels 4 . Although the species appears to be resilient (that is, it has a high capacity to recover from a decline in abundance) 4 and fishing pressure is low in most years 4 , catches have been at or near historical lows since 2009, when a record catch of 305 t was taken (more than three times the long-term average). Without a reliable estimate of current biomass or sustainable yield, there is insufficient information to confidently classify the status of this stock.
On the basis of the evidence provided above, School Prawn in Queensland is classified as an undefined stock.
Table 2: School Prawn biology5,6
Longevity and maximum size |
Female: 32 months; 39.4 mm CL
Male: 32 months; 31.8 mm CL |
Maturity (50%) |
~1.17 cm CL |
CL = carapace length
Figure 1: Distribution of reported commercial catch of School Prawns in Australian waters, 2013 (calendar year)
Table 3: Main features and statistics for School Prawn fisheries in Australia, 2013 (calendar year)
Jurisdiction |
New South Wales |
Victoria |
Queensland |
Fishing methods |
Commercial |
Set pocket nets |
✓ |
|
|
Dip nets |
✓ |
|
|
Prawn stake nets |
|
✓ |
|
Prawn trawl |
✓ |
✓ |
✓ |
Recreational |
Hand-held nets |
✓ |
✓ |
|
Cast nets |
|
|
✓ |
Seine nets |
✓ |
|
✓ |
Bait nets |
|
✓ |
|
Indigenousa |
Hand-held nets |
✓ |
|
|
Cast nets |
|
|
✓ |
Seine nets |
✓ |
|
✓ |
Management methods |
Commercial |
Limited entry |
✓ |
✓ |
✓ |
Gear restrictions |
✓ |
✓ |
✓ |
Vessel number restrictions |
✓ |
✓ |
✓ |
Temporal closures |
✓ |
|
✓ |
Spatial closures |
✓ |
✓ |
✓ |
Bycatch reduction devices |
✓ |
|
✓ |
CPUE limits |
✓ |
|
|
Recreational |
Bag limits |
✓ |
✓ |
|
Possession limits |
|
|
✓ |
Indigenousa–d |
Bag limits |
✓ |
|
|
Section 37(1)(c1), Aboriginal cultural fishing authority |
✓ |
|
|
Active vessels |
|
166 in EGF
80 in EPTF
69 in OTF-PS |
9 in ITF |
33 in ECTF |
Catch |
Commercial |
243.1 t in EGF
308.9 t in EPTF
179.3 t in OTF-PS |
16.7 t in ITF |
16.7 t in ECTF |
Recreational |
<30 t (2000–01) |
Unknown |
Unknown |
Indigenous |
Unknown |
Unknown |
Unknown |
Markets |
Domestic |
✓ |
✓ |
✓ |
Export |
|
|
|
CPUE = catch per unit effort; ECTF = East Coast Trawl Fishery (Queensland); EGF = Estuary General Fishery (New South Wales); EPTF = Estuary Prawn Trawl Fishery (New South Wales); ITF = Inshore Trawl Fishery (Victoria); OTF-PS = Ocean Trawl Fishery–Prawn Sector (New South Wales)
a In Victoria, management of fishing activities by Indigenous people is grouped with the recreational fishing sector in terms of collecting data, undertaking stock assessments and implementing management responses. Recognised Traditional Owners (groups that hold native title or have agreements under the Victorian Traditional Owner Settlement Act 2010) can apply for permits under the Fisheries Act 1995 that authorise customary fishing (for example, different catch and size limits or equipment). The Indigenous category in Table 3 refers to customary fishing undertaken by recognised Traditional Owners. In 2013, there were no applications for customary fishing permits to access School Prawn.
b 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.
c 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, section 37(1)(c1) (Aboriginal cultural fishing authority).
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.

Figure 2: Commercial catch of School Prawns in Australian waters, 2001 to 2013 (calendar years)
Species caught incidentally by trawl nets are discarded because they either have low market value or are not permitted to be retained. Bycatch consists mainly of small fish, crabs, other penaeid prawns and numerous other bottom-dwelling invertebrate species, including sponges, sea stars and gastropod shellfish. Improvements in technology and the mandatory use of bycatch reduction devices has been shown to reduce bycatch in the trawl fisheries in New South Wales7,8.
Fishing methods used for school prawns pose a risk to habitats because repeated trawling can lead to depletion of sedentary species, such as sponges, that are habitat forming9 . However, recent research has shown that trawling in Queensland does not have a significant effect on the biodiversity or distribution of benthic species relative to nontrawled areas10.
Climate change may have a significant effect on the distribution of School Prawns. Under a scenario of increasing sea surface temperatures and a strengthening East Australian Current, the distribution of School Prawns may shift southwards, potentially affecting the timing of their spawning and migration, and decreasing variability in their recruitment11. As well, recent environmental models indicate that the growth and movement of School Prawns are affected by rates of river discharge. If climate change results in lower river discharges for some New South Wales estuaries, as some of the literature suggests12, lower catches and a lower stock biomass of this species may be a consequence 2.
a Department of Primary Industries, New South Wales
b Department of Agriculture, Fisheries and Forestry, Queensland
c Department of Environment and Primary Industries, Victoria