*

Dusky Whaler (2023)

Carcharhinus obscurus

  • Matias Braccini (Department of Primary Industries and Regional Development, Western Australia)
  • Victor Peddemors (New South Wales Department of Primary Industries)
  • Michael Drew (South Australian Research and Development Institute)
  • Michael Usher (Department of Industry, Tourism and Trade, Northern Territory)
  • Brooke D'Alberto (Australian Bureau of Agricultural and Resource Economics and Sciences)
  • Ian Jacobsen (Department of Agriculture and Fisheries, Queensland)

Date Published: June 2023

You are currently viewing a report filtered by jurisdiction. View the full report.

Toggle content

Summary

Dusky Whaler is a common, large-bodied whaler shark shark found throughout tropical and temperate waters of Australia.  In Western Australia stocks are recovering and there is a sustainable stock in eastern Australia.

Toggle content

Stock Status Overview

Stock status determination
Jurisdiction Stock Stock status Indicators
Northern Territory Western Australia Recovering Catch, CPUE, direct estimates of fishing mortality, demographic analysis, risk assessment
Toggle content

Stock Structure

Dusky Whaler has a tropical to warm-temperate distribution and is found off the west, south and north coasts of Australia, mostly between latitudes 18°S and 36°S [McAuley et al. 2007; Rogers et al. 2013a], and off the east coast, where the full extent of the species' geographic distribution is unclear. Electronic and conventional tagging studies have shown Dusky Whalers move between South Australia and Western Australia [Simpfendorfer et al. 1999; Rogers et al. 2013b; Huveneers et al. 2014, 2021] and between Queensland, New South Wales, Victoria and Tasmania [Huveneers et al. 2021], and genetic analyses suggest there is restricted gene flow between Dusky Whaler off eastern and western Australia [Geraghty et al. 2014]. Therefore, Dusky Whaler in South Australian, Western Australian and Northern Territory  waters are considered to form a single biological stock (the Western Australia stock). This biological stock exhibits a high degree of ontogenetic segregation, with juveniles most common in temperate latitudes and adults in warmer northern latitudes [McAuley et al. 2007, 2015].

Here, assessment of stock status is presented at the biological stock level—western Australia and eastern Australia.

Toggle content

Stock Status

Western Australia

The cross-jurisdictional Western Australia Dusky Whaler stock is taken in fisheries managed by the Commonwealth, Western Australia, Northern Territory and South Australia. This biological stock is most abundant in waters between north-west and southern Western Australia (to longitude 120°E). The whaler shark species composition in South Australia's commercial multispecies, multi-gear and multi-sectoral Marine Scalefish Fishery (MSF) is not resolved in log-books. Onboard sampling showed carcharhinid catches by the MSF largely comprised juvenile Bronze Whalers (C. brachyurus) [Rogers et al. 2013a; SARDI unpublished data]. The presence of Dusky Whalers in catches in South Australian waters is seasonally and spatially variable [Jones 2008; Rogers et al. 2013a]. 

The Commonwealth commercial catch in the Gillnet, Hook and Trap Sector (GHTS) of the Southern and Eastern Scalefish and Shark Fishery (SESSF) of Western Australia Dusky Whaler stock averaged less than one t per year during 2017–18 to 2021–22 financial years and no catch in the 2021–22 financial year. 

 Catches of Dusky Whaler in Western Australia’s Joint Authority Southern Demersal Gillnet and Demersal Longline Managed Fishery, and the West Coast Demersal Gillnet and Demersal Longline Fishery have historically consisted of neonate (young of the year) and one-to-two year-old sharks. Collectively, these age classes accounted for 89% of the observed catch during the 1990s [Simpfendorfer et al. 2002, McAuley and Simpfendorfer 2003]. The status of this stock was initially assessed using demographic modelling techniques, fishing mortality rates estimated from a tagging study in the 1990s, and contemporary catch and catch per unit effort (CPUE) data [McAuley et al. 2007; Simpfendorfer 2010]. A 2005 assessment confirmed that recorded catches of young juvenile sharks in the target fisheries have been sustainable since the mid-1990s. However, the assessment model also predicted that very low levels of fishing mortality (1–2% per year) applied to sharks older than 10 years would result in recruitment overfishing [McAuley et al. 2007]. Previous assessments therefore concluded that the declining trend observed in the effective Dusky Whaler CPUE series between the mid-1990s and 2004–05 indicated that the breeding biomass, and hence recruitment, had been gradually depleted by poorly quantified levels of intrinsic (e.g., WA Rock lobster fishery) and extraneous fishing mortality, including fisheries operating in other jurisdictions [ Jones 2008; Rogers et al. 2013a; McAuley et al. 2015; Marshall et al. 2016; Braccini et al. 2021]. Based on the above lines of evidence the stock was considered to be depleted and recruitment impaired [McAuley et al. 2015]. As a result, comprehensive measures to mitigate cryptic mortality of older Dusky Whalers within all Western Australian managed commercial fisheries, and to reduce catches of juveniles to below the levels determined to be sustainable in the mid-1990s, have been introduced since 2006–07. An increasing trend in the effective CPUE from 2006–12 was interpreted as improved recruitment and a recovering stock, suggesting that management arrangements were suitably precautionary to ensure that the biological stock continued to recover [McAuley et al. 2015].

In 2018, a stock assessment was conducted based on a risk-based weight of evidence approach using all available lines of evidence, including simulated biomass trajectories derived from a combination of demographic modelling and catch-only modelling [Braccini et al. 2018]. This assessment estimated a “Medium” current sustainability risk from fishing for the Dusky Whaler stock  [Braccini et al. 2018].

Updated stock assessments using a range of catch-only methods, state-space biomass dynamics models (JABBA, Winker et al. [2018]), integrated age-structured models (Stock Synthesis, Methot and Wetzel [2013]), and time-series of reconstructed catches, catch rates, abundance and length composition are underway (Braccini et al. unpublished). Preliminary findings, based on catch-only methods and the state space biomass dynamics model, indicate that for the last 10 years total catches have been below those required for MSY and that the recent biomass trajectory has considerably increased. In addition, fishery independent surveys of the adult component of the stock in northern western Australia show a strong increasing trend since 2016.

The above evidence indicates that the biomass of this stock is likely to be depleted and that recruitment is likely to be impaired. However, for the period 2016 to 2022 these indicators suggest a recovering stock. The above evidence indicates that the current level of fishing mortality should allow the stock to recover from its recruitment impaired state.

On the basis of the evidence provided above, the Western Australia biological stock is classified as a recovering stock.

Toggle content

Biology

Dusky Whaler biology [Simpfendorfer et al. 2002; McAuley et al. 2007; Geraghty et al. 2013, 2016; Kyne et al. 2021]

Biology
Species Longevity / Maximum Size Maturity (50 per cent)
Dusky Whaler

Females > 40 years, 2 890 mm FL Males > 32 years, 3 560 mm TL (~2 920 mm FL)

Females 27–35 years, 2 540 mm FL  (Western Australia)

Females 15.5 years, 2811 mm TL (Eastern Australia)

Toggle content

Distributions

Distribution of reported commercial catch of Dusky Whaler

Toggle content

Tables

Fishing methods
Northern Territory
Commercial
Unspecified
Recreational
Hook and Line
Management methods
Method Northern Territory
Commercial
Gear restrictions
Processing restrictions
Quota
Catch
Northern Territory
Commercial 840.00kg
Indigenous Undetermined but likely to be negligible
Recreational Undetermined but likely to be negligible

Commercial (catch) Western Australian (state) and Eastern Australia biological stock is for Dusky Whaler only. However, South Australian catches are reported as undifferentiated whaler sharks and are therefore not presented.

Commonwealth – Commercial Data provided for the Commonwealth align with 2021–22 financial year.

Commonwealth – Recreational 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.

Commonwealth – Indigenous 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.

Western Australia – Recreational (Management Methods) A recreational fishing from boat licence is required for recreational fishing from a powered vessel in Western Australia.

New South Wales – Indigenous (Management Methods) https://www.dpi.nsw.gov.au/fishing/aboriginal-fishing

Northern Territory - Indigenous (management methods) The Fisheries Act 1988 (NT), specifies that: “Unless expressly provided otherwise, nothing in this Act derogates or limits the right of Aboriginal people who have traditionally used the resources of an area of land or water in a traditional manner to continue to use those resources in that area in that manner.”

Queensland – Commercial QLD commercial and charter data has been sourced from the commercial fisheries logbook program.  Further information available through the Fisheries Summary Report (https://www.daf.qld.gov.au/business-priorities/fisheries/monitoring-research/data/queensland-fisheries-summary-report)  

Queensland – Indigenous (management methods) for more information see https://www.daf.qld.gov.au/business-priorities/fisheries/traditional-fishing

Toggle content

Catch Chart

Commercial catches of Dusky Whaler - note confidential catch not shown

Toggle content

References

  1. Blower DC, Riginos, C and Ovenden, JR. 2019. NeOGen: A tool to predict genetic effective population size (Ne) for species with generational overlap and to assist empirical Ne study design. Molecular Ecology Resources 19: 290-271.
  2. Blower, D. C. 2020. Estimating contemporary abundance, demography, and vulnerability to change for long-lived species with effective population size and population simulation. PhD thesis. School of Biological Sciences, p. 257. The University of Queensland.
  3. Braccini, M, Blay, N, Hesp, A, and Molony, B 2018. Resource Assessment Report Temperate Demersal Elasmobranch Resource of Western Australia. Department of Primary Industries and Regional Development. Fisheries Research Report No. 294 Department of Primary Industries and Regional Development, Western Australia. 149 pp
  4. Braccini, M, Kangas, M, Jaiteh, V and Newman, S 2021, Quantifying the unreported and unaccounted domestic and foreign commercial catch of sharks and rays in Western Australia. Ambio, 50(7), 1337-1350
  5. Continental-Scale Network Reveals Cross-Jurisdictional Movements of Sympatric Sharks With Implications for Assessment and Management. Frontiers in Marine Science 8: 697175
  6. Geraghty PT, Macbeth WG and Williamson JE 2016, Aspects of the reproductive biology of dusky, spinner and sandbar sharks (Family Carcharhinidae) from the Tasman Sea, Marine and Freshwater Research, 67: 513–525
  7. Geraghty PT, Macbeth, WG, Harry, AV, Bell, JE, Yerman, MN and Williamson, JE 2013, Age and growth parameters for three heavily exploited shark species off temperate eastern Australia, ICES Journal of Marine Science, 71: 559–573.
  8. Geraghty, PT, Williamson, JE, Macbeth, WG, Blower, DC, Morgan, JAT, Johnson, G, Ovenden, JR and Gillings, MR 2014, Genetic structure and diversity of two highly vulnerable carcharhinids in Australian waters, Endangered Species Research, 24: 45–60.
  9. Huveneers, C, Rogers, P and Drew, M 2014, Monitoring shark species of conservation concern within the Adelaide metropolitan and Gulf St Vincent regions, final report to the Adelaide and Mount Lofty Ranges Natural Resources Management Board, South Australian Research and Development Institute (Aquatic Sciences), SARDI publication F2013/000716-1, SARDI research report series 754, SARDI, Adelaide, 89.
  10. JABBA: Just Another Bayesian Biomass Assessment. Fish. Res. 204, 275–288
  11. Jones, K 2008, Review of the fishery status for whaler sharks (Carcharhinus spp.) in South Australian and adjacent waters, report to the Fisheries Research and Development Corporation, FRDC project 2004/067, South Australian Research and Development Institute (Aquatic Sciences) publication F2007/000721-1, SARDI research report series 154, SARDI, Adelaide.
  12. Kyne, P. M., Heupel, M. R., White, W. T. & Simpfendorfer, C. A. (2021). The Action Plan for Australian Sharks and Rays 2021. National Environmental Science Program. Hobart, Australia.
  13. Macbeth, WG, Geraghty, PT, Peddemors, VM and Gray, CA 2009, Observer-based study of targeted commercial fishing for large shark species in waters off northern New South Wales, Cronulla Fisheries Research Centre of Excellence, New South Wales Industry and Investment, Cronulla.
  14. Marshall, L, Giles, J and Johnson, GJ 2016, Catch composition of a traditional Indonesian shark fishery operating in the MOU Box, northwestern Australia: Results of shark fin identification from Operation Snapshot (May 2015), 2016/001375, Australian Fisheries Management Authority, Canberra.
  15. McAuley, R and Simpfendorfer, C 2003, Catch composition of the Western Australian Temperate Demersal Gillnet and Demersal Longline fisheries, 1994–1999, Fisheries research report 146, Western Australian Department of Fisheries, Perth.
  16. McAuley, R, Braccini, M, Newman, SJ and O’Malley, J 2015, Temperate Demersal Gillnet and Demersal Longline Fisheries Status Report, in WJ Fletcher and K Santoro (eds), Status Reports of the Fisheries and Aquatic Resources of Western Australia 2014/15, Western Australian Department of Fisheries, Perth, 261–272.
  17. McAuley, RB, Simpfendorfer, CA and Hall, NG 2007, A method for evaluating the impacts of fishing mortality and stochastic influences on the demography of two long-lived shark stocks, ICES Journal of Marine Science, 64: 1710–1722.
  18. Peddemors, V, Macbeth, W, Collins, D, Goulstone, A, Ives, M., Ovenden, J., Butcher, P. 2020. Shark Futures: Sustainable management of the NSW whaler shark fishery. Port Stephens, NSW. 190pp
  19. Queensland Government, 2023, Shark Control Program: Shark Catch Statistics by Year. Available at: https://www.data.qld.gov.au/dataset/shark-control-program-shark-catch-statistics (Accessed: 2 August 2023).
  20. Rogers, P, Huveneers, C, Goldsworthy, SD, Mitchell, JG and Seuront, L 2013, Broad-scale movements and pelagic habitat of the Dusky Shark Carcharhinus obscurus off Southern Australia determined using pop-up satellite archival tags, Fisheries and Oceanography, 22: 102–112.
  21. Rogers, PR, Huveneers, C, Goldsworthy SD, Cheung, WWL, Jones KG, Mitchell, JG and Seuront, L 2013, Population metrics and movement of two sympatric carcharhinids: a comparison of the vulnerability of pelagic sharks of the southern Australian gulfs and shelves, Marine and Freshwater Research, 64: 20–30.
  22. Simpfendorfer CA, McAuley R, Chidlow JA, Lenanton R, Hall N and Bastow T 1999. Biology and stock assessment of Western Australia’s commercially important shark species. Project 96/130 Fisheries Research and Development Corporation, Department of Fisheries of Western Australia, Perth.
  23. Simpfendorfer, C 1999, Demographic analysis of the dusky shark fishery in southwestern Australia, in JA Musick (ed.), Life in the slow lane: Ecology and conservation of long-lived marine animals, American Fisheries Society Symposium 23, Bethesda, Maryland, 149–160.
  24. Simpfendorfer, CA, McAuley, R, Chidlow, J and Unsworth, P 2002, Validated age and growth of the Dusky Shark, Carcharhinus obscurus, from Western Australian waters, Marine and Freshwater Research, 53: 567–573.
  25. Sporcic, M, Hobday, A, Bulman, C, Hartog, J, Fuller, M 2019 Ecological Risk Assessment for the Effects of Fishing: Report for the Eastern Tuna and Billfish Fishery: Longline sub-fishery, data to 2015. Report for the Australian Fisheries Management Authority. 234 pp.
  26. Stock synthesis: A biological and statistical framework for fish stock assessment and fishery management. Fish. Res. 142, 86–99
  27. Teixeira, D, Janes, R, and Webley, J 2021, 2019–20 Statewide Recreational Fishing Survey Key Results. Project Report. State of Queensland, Brisbane.

Downloadable reports

Click the links below to view reports from other years for this fish.