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Redspot Emperor (2023)

Lethrinus lentjan

  • Grant Johnson (Department of Industry, Tourism and Trade, Northern Territory)
  • Stephen Newman (Department of Primary Industries and Regional Development, Western Australia)
  • Fabian Trinnie (Department of Primary Industries and Regional Development, Western Australia)
  • Peri Subritzky (Department of Agriculture and Fisheries, Queensland)

Date Published: June 2023

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Summary

Redspot Emperor is found throughout tropical Australia in both coastal and offshore habitats. Stocks In NT and WA are classified as sustainable, while stocks found on the east coast of QLD and in the Gulf of Carpentaria are undefined. 

Photo credit: Matthew Dorter

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Stock Status Overview

Stock status determination
Jurisdiction Stock Stock status Indicators
Queensland East Coast Undefined

Catch

Queensland Gulf of Carpentaria Queensland Undefined

Catch

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Stock Structure

Redspot Emperor is a widespread Indo-Pacific species, found throughout tropical Australia in both coastal and offshore habitats. This species inhabits northern Australia, with its range extending from approximately Gladstone, Queensland in the east, to Port Headland Western Australia, in the west [Carpenter and Allen 1989].

There is no information on population connectivity for this species in Australian waters and subsequently, this species has been assessed at the jurisdictional level for the Northern Territory and Western Australia. In Queensland, geographic separation caused by Torres Strait most likely results in limited movement between the Queensland east coast and the Queensland side of the Gulf of Carpentaria, consequently, this species has been assessed as two management units in this state.

Here, assessment of stock status is presented at the jurisdictional level–Western Australia and Northern Territory, and the management unit level–Gulf of Carpentaria Queensland and East Coast.

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Stock Status

East Coast

Redspot Emperor on the East Coast of Queensland is mainly caught within the Great Barrier Reef Marine Park by line in the commercial and charter sectors in the Reef Line Fishery (RLF) [QDAF 2020a]. Within the RLF, Redspot Emperor is retained as a by-product species and managed through a multi species total allowable commercial catch (TACC) quota. In addition, species-specific harvest control rules and catch reference points were introduced for by-product species (including Redspot Emperor) through the RLF Harvest Strategy in 2020. Charter catch records span from 1995–96 to present with annual harvest increasing from 0.1 tonnes (t) up to 1 t in 2021–22.  Commercial catch records span from 2002–03 to present with annual harvest increasing from 0.1 t to a peak of 1.6 t in 2019–20 and stabilising to 0.75 t to present. Most of the increase in harvest can be attributed to increases in charter and commercial harvest in far north Queensland. Recreational fishing catch could not be estimated in the latest Recreational Fishing Survey [Teixeira et al. 2021], however take is likely to be low. The indigenous take is unknown.  

On the basis of the evidence provided above, Redspot Emperor along the Queensland East Coast is classified as an undefined stock.

Gulf of Carpentaria Queensland

Redspot Emperor in the Gulf of Carpentaria, Queensland is mainly caught by trawling in the Gulf of Carpentaria Developmental Fin Fish Trawl Fishery (GOCDFFTF). The GOCDFFTF is managed as a developmental fishery under the Queensland Fisheries Act 1994, Queensland Fisheries (Commercial Fisheries) Regulation 2019 and the Fisheries (General) Regulation 2019 [QDAF 2020b]. Redspot Emperor are not targeted by the GOCDFFTF but are retained as a by-product species and managed through a multi species total allowable commercial catch (TACC) quota.  

Commercial catch records span the period from 1997–2022, however, fishing has not occurred in every year. Commercial catches of Redspot Emperor increased from 1 t in 1996–97 to a peak of 13 t in 2004–05, then decreased to zero in 2016–17. Harvest resumed in 2020–21 when new developmental fishing permits were issued. Annual commercial catches increasing to 3 t in 2020–21 and 4.5 t in 2021–22. Redspot Emperor accounts for approximately 4% of the catch in the GOCDFTF [Zeller and Snape 2006]. Recent fishery independent surveys estimated biomass of Redspot Emperor was 2,385 t in the eastern Gulf of Carpentaria, based on calculations using an effective trawl path for trawl swept area [Knuckey et al. 2022]. The recreational and indigenous take is unknown. There is insufficient information to confidently classify the status of this stock. 

On the basis of the evidence provided above, Redspot Emperor in the Gulf of Carpentaria is classified as a sustainable stock.

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Biology

Redspot Emperor biology [Currey et al. 2009; Currey et al. 2013; Grandcourt 2002; Johnson unpublished; Mobiha 1991]

Biology
Species Longevity / Maximum Size Maturity (50 per cent)
Redspot Emperor

19 years, 450 mm FL

Female maturity: unknown. Male maturity: least a proportion of the population are throught to undergo protogynous sex change (to male): 2.5 to 3.5 years, 270 mm FL

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Distributions

Distribution of reported commercial catch of Redspot Emperor – confidential catch is not shown

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Tables

Fishing methods
Queensland
Commercial
Line
Midwater Trawl
Charter
Spearfishing
Hook and Line
Recreational
Spearfishing
Hook and Line
Indigenous
Various
Management methods
Method Queensland
Charter
Bag and possession limits
Gear restrictions
Seasonal or spatial closures
Size limits
Commercial
Gear restrictions
Harvest Strategy
Individual transferable quota
Limited entry
Seasonal or spatial closures
Size limit
Total allowable catch
Vessel restrictions
Recreational
Bag and possession limits
Gear restrictions
Seasonal or spatial closures
Size limit
Catch
Queensland
Commercial 714.60kg
Charter 2 t
Indigenous Unknown
Recreational Unknown

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 – Indigenous (Management Methods). For more information see: https://www.daf.qld.gov.au/business-priorities/fisheries/traditional-fishing

Queensland – Recreational Fishing (Catch). Data with high uncertainty (Residual Error greater than 50 %) has been excluded and listed as unknown. More information available at: https://www.daf.qld.gov.au/business-priorities/fisheries/monitoring-research/monitoring-reporting/statewide-recreational-fishing-surveys

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

Queensland – Commercial (Management Methods). Harvest strategies are available at: https://www.daf.qld.gov.au/business-priorities/fisheries/sustainable/harvest-strategy   

Western Australia – Recreational (catch). Boat-based recreational catch between 1 September 2020 and 31 August 2021 from Ryan et al. [2022]. Please note that catches of Blue Threadfin are underestimates as shore-based and boat-based fishers that only operated in freshwater were out of scope of the survey.

Western Australia – Recreational (Management Methods). A Recreational Fishing from Boat Licence is required for the use of a powered boat to fish or to transport catch or fishing gear to or from a land-based fishing location.

Western Australia – Indigenous (Management Methods). Subject to application of 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.

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Catch Chart

Commercial catch of Redspot Emperor - note confidential catch not shown

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References

  1. Carpenter, KE and Allen, G 1989, FAO species catalogue, Vol. 9, Emperor fishes and large-eye breams of the world (family Lethrinidae), An annotated and illustrated catalogue of lethrinid species known to date, Food and Agriculture Organization of the United Nations, Rome.
  2. Currey, LM, Williams, AJ, Mapstone, BD, Davies, CR, Carlos, G, Welch DJ, Simpfendorfer, CA, Ballagh, AC, Penny, AL, Grandcourt, EM, Mapleston, A, Weibkin, AS, Bean, K 2013, Comparative biology of tropical Lethrinus species (Lethrinidae): challenges for multi-species management, Journal of Fish Biology, 83: 764-788.
  3. Currey, LM, Williams, AJ, Simpendorfer, CA, Ballagh, AC, Penny, AL 2009, Comparative biology of key inter-reefal lethrinid species on the Great Barrier Reef. Project Milestone Report to the Marine and Tropical Sciences Research Facility, Reef and Rainforest Research Centre Limited, Cairns.
  4. Grandcourt, EM 2002, Demographic characteristics of a selection of exploited reef fish from the Seychelles: preliminary study, Marine and Freshwater Research, 53: 123–130.
  5. Knuckey, IA and Koopman, M 2022, Survey of tropical snapper in Northern Territory fisheries - 2021, Fishwell Consulting.
  6. Knuckey, IA Koopman, M and Hudson, R 2022, Survey of tropical snapper in Queensland Gulf of Carpentaria Developmental Fin Fish Trawl Fishery - 2021, Fishwell Consulting.
  7. Mobiha, A 1991, The reproductive biology of eight reef fish species from the Tigak Islands of Papua New Guinea, Science in New Guinea 17: 133-142
  8. Newman, SJ, Brown, JI, Fairclough, DV, Wise, BS, Bellchambers, LM, Molony, BW, Lenanton, RCJ, Jackson, G, Smith, KA, Gaughan, DJ, Fletcher, WJ, McAuley, RB and Wakefield, CB 2018, A risk assessment and prioritisation approach to the selection of indicator species for the assessment of multi-species, multi-gear, multi-sector fishery resources. Marine Policy, 88: 11–22.
  9. O'Neill, MF, Leigh, GM, Martin, JM, Newman, SJ, Chambers, M, Dichmont, CM and Buckworth, RC 2011, Sustaining productivity of tropical red snappers using new monitoring and reference points, Department of Employment, Economic Development and Innovation, Brisbane.
  10. Queensland Department of Agriculture and Fisheries 2020a, Reef line fishery harvest strategy: 2020-2025, Brisbane, Queensland.
  11. Queensland Department of Agriculture and Fisheries 2020b, Submission for the assessment of the Queensland Gulf of Carpentaria Developmental Fin Fish Trawl Fishery Wildlife Trade Operation approval under the Environment Protection and Biodiversity Conservation Act 1999, Department of Agriculture and Fisheries, Fishwell Consulting, Queensland.
  12. Ryan, KL, Lai, EKM and Smallwood, CB 2022, Boat-based recreational fishing in Western Australia 2020/21, Fisheries Research Report No. 327 Department of Primary Industries and Regional Development, Western Australia. 221pp.
  13. Teixeira, D, Janes, R and Webley, J 2021, 2019–20 statewide recreational fishing survey - Social and attitudinal results, Department of Agriculture and Fisheries, Queensland.
  14. Wakefield, C, Trinnie, F, Skepper, C, Boddington, Newman, SJ, and Steele, A 2023, North Coast Demersal Resource Status Report 2022, pp. 167–176. In: Gaughan, DJ, and Santoro, K (eds.) 2023, Status Reports of the Fisheries and Aquatic Resources of Western Australia 2021/22: The State of the Fisheries, Department of Primary Industries and Regional Development, Western Australia, Perth, Australia.
  15. West, LD, Stark, KE, Dysart, K and Lyle, JM 2022, Survey of recreational fishing in the Northern Territory: 2018 to 2019, Northern Territory Fisheries, Darwin.
  16. Zeller, B and Snape, N 2006, Ecological Risk Assessment of Queensland-Managed Fisheries in the Gulf of Carpentaria, Department of Primary Industries and Fisheries, Brisbane, Queensland.

Downloadable reports

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