Pale Octopus (2023)
Octopus pallidus
Date Published: June 2023
Summary
Pale Octopus is distributed from the Great Australian Bight around TAS to southern NSW. Stocks are classified as depleting in Tasmania, negligible in NSW and undefined in SA and VIC.
Stock Status Overview
Jurisdiction | Stock | Stock status | Indicators |
---|---|---|---|
New South Wales | New South Wales | Negligible | |
South Australia | South Australia | Undefined | |
Tasmania | Tasmania | Depleting | Catch, effort, CPUE, potlift surveys |
Victoria | Victoria | Undefined | Catch |
Stock Structure
Pale Octopus is distributed from the Great Australian Bight around Tasmania to southern New South Wales. There is evidence to suggest that Pale Octopus shows complex biological stock structure, with a number of discrete subpopulations in Bass Strait (less than 100 km apart) due to limited dispersal and isolation by distance [Doubleday et al. 2008; Higgins et al. 2013]. However, further information is required to confirm the overall stock structure across southern Australia. Here, assessments of stock status are presented at the jurisdictional level—New South Wales, Victoria, Tasmania and South Australia.
Stock Status
New South Wales
Stock status for the New South Wales stock is reported as Negligible due to historically low catches in this jurisdiction and the stock has generally not been subject to targeted fishing [Hall 2018, 2020]. The New South Wales commercial catch during 2017–18 to 2021–22 averaged only 4 t per year, and Pale Octopus is not a major component of recreational landings. At these negligible catch levels, fishing is unlikely to be having a negative impact on the stock.
South Australia
South Australia’s commercial catch of Pale Octopus over the past 23 years has averaged 11.4 t per year, and the species is not a major component of recreational landings. There is no published assessment of this species, and there are no data available to estimate biomass or exploitation rates. In addition, there is no knowledge on recruitment or harvestable biomass in South Australia, and there are no defined target or limit reference levels. These data and knowledge gaps prevent assessment of current stock size or fishing pressure. Consequently, there is insufficient information available to confidently classify the status of this stock.
On the basis of the evidence provided above, the South Australia Fishery management unit for this species is classified as an undefined stock.
Tasmania
In Tasmania, most fishing of Pale Octopus takes place on stocks located off the Northern coast and around King and Flinders Island. The stock status of Pale Octopus is assessed using data on commercial catch and catch per unit effort (CPUE; i.e. octopus per pot-lift). A 50-pot sampling program has been conducted in the fishery since November 2004, whereby fishers are required to collect data on the number and sex of all octopuses caught in 50 randomly selected pots from a single line per fishing day, resulting in data from approximately 4,000 pot lifts per fishing season.
Catch of Pale Octopus in the Tasmanian Octopus Fishery (TOF) has fluctuated around 60–100 t since 2005–06, reaching an initial peak of approximately 126 t in 2012–13. Catches of Pale Octopus were reduced to < 100 t again in the following seasons before reaching a new peak of approximately 154 t in the 2020–21 season. In 2021–22, catch was at 109 t, with catch now having exceeded 100t for four consecutive years. Fishing effort has fluctuated around 300,000 pot-lifts since 2006–07 before reaching a historic high of 448,000 pot-lifts in 2012–13 and then declining again to comparable levels fluctuating around 300,000 pot lifts over the last five fishing seasons [Fraser et al. 2022].
Standardised CPUE in the TOF, calculated using a general linear model based on total commercial catch and data from the 50-pot sampling program, fluctuated between roughly 50 and 90% compared to the reference year (2004–05) from 2011–12 to 2019–20. In the last two years standardised CPUE has risen significantly and now exceeds the reference year [Fraser et. al. 2022]. In stock assessments up until 2018–19, these fishery-wide trends in catch, effort and CPUE were used as primary indicators of stock status [Hill et al. 2020]. However, the recent redistribution of fishing effort and catch to areas further offshore initiated more in-depth analyses of local trends in catch, effort and CPUE in assessments carried out since 2019–20 [Krueck et al. 2021]. The results highlighted that some key traditionally fished areas are still productive, but that declining trends in CPUE are widespread and potentially concerning. CMSY analyses were conducted for a spatially consistent time series of catch data that excluded more recently exploited areas east of King Island. This indicated that traditionally fished areas east and west of Flinders Island might be depleted below 50% of BMSY however the stock is not yet considered to be recruitment impaired.
Broadscale trends in catch and CPUE do not indicate stock depletion. However, the ecology of Pale Octopus and the species’ interaction with fishing gear means that this is a high-risk fishery. There is evidence of regional biomass depletion in some traditionally fished areas, which suggests that previous levels of fishing pressure in these regions may have been unsustainable. Catches across the fishery have been high for the past four seasons, with notably higher catches and effort in a relatively small geographic area. This level of concentrated effort has the potential to be applied in the future, which could cause the fishery to become depleted. On the basis of this evidence, the Pale Octopus stock in northern Tasmania is classified as a depleting stock.
Victoria
A new, standalone commercial Octopus Fishery commenced in Victoria in August 2020. The fishery predominantly harvests Pale Octopus in Eastern Victoria using unbaited pots. Octopus fishing in central and western Victoria is less established and is managed through exploratory, temporary permits.
Pale Octopus have historically been caught by a variety of gears but was not differentiated from other species of octopus in catch and effort reporting.
Targeted octopus fishing with octopus pots took place from 1998–2003 and it is likely that some landings prior to this time were caught in pots but the gear was not accurately reported. Small amounts of octopus (less than 2 t per year ) were subsequently caught using traps up until 2015 when landings began to increase rapidly in eastern Victoria, reaching 113.5 t in 2021–22 [Bell et al. 2023].
Due to a lack of historic species specific reporting, the fact Pale Octopus represent an incidental byproduct of many fisheries and appear to have been discarded at times, and the relatively brief history of targeted fishing effort, there is considerable uncertainty about the current stock status of Victorian Pale Octopus. While targeted octopus catch rates remain stable, the fishery is expanding spatially so it is difficult to determine the extent to which this represents serial depletion and/or responsible fishing of the resource by spreading effort. In addition, the landings of other Victorian and Commonwealth fisheries are increasing as demand for the product increases. The above uncertainties make it difficult to determine whether current fishing practices could lead to recruitment impairment, though it appears unlikely that has already occurred.
On the basis of the evidence provided above, Pale Octopus in Victoria is classified as an undefined stock.
Biology
Pale Octopus biology [Leporati et al. 2007; Leporati et al 2008a, 2008b].
Species | Longevity / Maximum Size | Maturity (50 per cent) |
---|---|---|
Pale Octopus | 1.5 years, 1200 g | Females 473 g, Males < 250 g |
Tables
New South Wales | Victoria | Tasmania | South Australia | |
---|---|---|---|---|
Commercial | ||||
Otter Trawl | ||||
Various | ||||
Fish Trap | ||||
Net | ||||
Dredges | ||||
Unspecified | ||||
Traps and Pots | ||||
Pots and Traps | ||||
Recreational | ||||
Diving | ||||
Hand held- Implements | ||||
Spearfishing | ||||
Hand collection | ||||
Coastal, Estuary and River Set Nets | ||||
Rock Lobster And Crayfish Traps And Pots | ||||
Indigenous | ||||
Spearfishing | ||||
Hand collection | ||||
Coastal, Estuary and River Set Nets | ||||
Rock Lobster And Crayfish Traps And Pots |
Method | New South Wales | Victoria | Tasmania | South Australia |
---|---|---|---|---|
Commercial | ||||
Effort limits | ||||
Gear restrictions | ||||
Licence | ||||
Limited entry | ||||
Spatial closures | ||||
Indigenous | ||||
Bag and possession limits | ||||
Bag limits | ||||
Customary fishing permits | ||||
Recreational | ||||
Bag and possession limits | ||||
Bag limits | ||||
Gear restrictions | ||||
Licence | ||||
Spatial closures |
New South Wales | Victoria | Tasmania | South Australia | |
---|---|---|---|---|
Commercial | 4.30t | 53.72t | 105.01t | |
Indigenous | Unknown (No catch under permit) | Unknown | ||
Recreational | Confidential, Unknown | 1,143 unspecified octopus landed in 2012–13 |
Victoria – Commercial (Catch). Pale Octopus is not differentiated from other octopuses caught in Victorian commercial fisheries.
Victoria – Indigenous (Management Methods). A person who identifies as Aboriginal or Torres Strait Islander is exempt from the need to obtain a Victorian recreational fishing licence, provided they comply with all other rules that apply to recreational fishers, including rules on equipment, catch limits, size limits and restricted areas. Traditional (non-commercial) fishing activities that are carried out by members of a traditional owner group entity under an agreement pursuant to Victoria’s Traditional Owner Settlement Act 2010 are also exempt from the need to hold a recreational fishing licence, subject to any conditions outlined in the agreement. Native title holders are also exempt from the need to obtain a recreational fishing licence under the provisions of the Commonwealth’s Native Title Act 1993.
Tasmania – Commercial (Catch). Catches reported for the Tasmanian Octopus Fishery are for the period 1 March to end of February the following year. The most recent assessment available is for 2021–22.
Tasmania – Commercial (Management Methods). A general possession limit of 100 kg of octopus per day (all species combined) is in place for holders of a fishing licence (personal) and a scalefish licence. This limit does not apply to Tasmanian Octopus Fishery licence holders operating in northern Tasmania.
Tasmania – Recreational (Management Methods). In Tasmania, a recreational licence is required for fishers using rock lobster pots, along with nets, such as gillnet or beach seine. A bag limit of five octopus and a possession limit of ten octopus (all species combined) is in place for recreational fishers.
Tasmania – Indigenous. In Tasmania, Indigenous persons engaged in traditional fishing activities in marine waters are exempt from holding recreational fishing licences but must comply with all other fisheries rules as if they were licensed. For details, see the policy document 'Recognition of Aboriginal Fishing Activities” (https://fishing.tas.gov.au/Documents/Policy%20for%20Aboriginal%20tags%20and%20alloting%20an%20UIC.pdf).
References
- Bell, JD, Ingram, BA, Gorfine, HK and Conron, SD 2023, Review of key Victorian fish stocks — 20122 Victorian Fisheries Authority Science Report Series No. 38, First Edition, June 2023. VFA: Queenscliff. 111pp.
- Doubleday, ZA, Pecl, GT, Semmens, JM and Danyushevsky, L 2008, Stylet elemental signatures indicate population structure in a holobenthic octopus species, Octopus pallidus, Marine Ecology Progress Series, 371: 1–10.
- Fraser, K, Hartmann, K, Gardner, C, Krueck, N 2022, Tasmanian Octopus Assessment 2021/22. Institute for Marine and Antarctic Studies, University of Tasmania, Hobart, Tasmania.
- Hall, KC 2018, NSW stock status summary 2018 - Octopuses (Octopus australis, Macroctopus maorum, O. tetricus and O. pallidus), NSW Department of Primary Industries, Coffs Harbour, NSW
- Hall, KC 2020, NSW Stock status summary 2018/19 – Hammer Octopus (Octopus australis), NSW Department of Primary Industries, NSW Fisheries, Coffs Harbour, NSW
- Higgins, KL, Semmens, JM, Doubleday, ZA and Burridge, CP 2013, Comparison of population structuring in sympatric octopus species with and without a pelagic larval stage, Marine Ecology Progress Series, 486: 203–212.
- Hill, N, Krueck, N and Hartmann, K 2020, Tasmanian Octopus Fishery Assessment 2018/19, Institute for Marine and Antarctic Studies, University of Tasmania, Hobart, Tasmania.
- Krueck, N, Hill, N, Hartmann, K, and Fraser, K 2021, Tasmanian Octopus Fishery Assessment 2019/20, Institute for Marine and Antarctic Studies, University of Tasmania, Hobart, Tasmania.
- Leporati, SC, Pecl, GT and Semmens, JM 2007, Cephalopod hatchling growth: The effects of initial size and seasonal temperatures, Marine Biology, 151: 1375–1383.
- Leporati, SC, Pecl, GT and Semmens, JM 2008a, Reproductive status of Octopus pallidus, and its relationship to age and size, Marine Biology, 155: 375–385.
- Leporati, SC, Semmens, JM and Pecl, GT 2008b, Determining the age and growth of wild octopus using stylet increment analysis, Marine Ecology Progress Series, 367: 213–222.