Fishery Report 2022:
Dissostichus mawsoni in Division 58.4.1
CCAMLR Secretariat
17 March 2023
Antarctic Toothfish, Dissostichus mawsoni Norman, 1937.
Map of the management areas within the CAMLR Convention Area. Division 58.4.1, the region discussed in this report is shaded in green. Throughout this report, “2022” refers to the 2021/22 CCAMLR fishing season (from 1 December 2021 to 30 November 2022).
1. Introduction to the fishery
1.1. History
This report describes the exploratory longline fishery for Antarctic toothfish (Dissostichus mawsoni) in Division 58.4.1. Prior to 2017, this fishery was classified as an exploratory fishery for Dissostichus spp., however, in order to better align the target species with the species that dominates the catch and tagging data, the target species was specified as D. mawsoni, with any Patagonian toothfish (D. eleginoides) caught counting towards the catch limit for D. mawsoni.
1.2. Conservation Measures currently in force
The current limits on the exploratory fishery for D. mawsoni in Division 58.4.1 are described in Conservation Measure 41-11. Directed fishing did not take place in 2022 as per Conservation Measure 41-11 paragraph 1.
Figure 1: Location of Small Scale Research Units and Research Blocks in Division 58.4.1. The fishable depth range (600m-1800m) is highlighted in shades of green.
1.3. Active vessels
In 2019, 7 vessels notified their intent to participate in this fishery. In 2020, 11 vessels notified their intent to participate in this fishery. In 2021, 6 vessels notified their intent to participate in this fishery. In 2022, 7 vessels notified their intent to participate in this fishery. For the 2023 fishing season, a total of 8 vessels notified their intention to participate in this fishery (2 from Australia; 2 from France; 1 from Japan; 1 from Spain; 2 from the Republic of Korea).
Directed fishing has not taken place since 2019 as per Conservation Measure 41-11 paragraph 1, and will not take place in 2023.
1.4. Timeline of spatial management
Prior to 2014, fishing in this Division was managed by alternating open and closed Small Scale Research Units (SSRUs, Fig. 1), with SSRUs C, E and G always open for fishing. In 2014, five Research Blocks (Fig. 1) were designated in Division 58.4.1 with catch limits applied to each Research Block. These Research Blocks were designed to ensure that research fishing occurred in those areas with the highest probability of recapturing tagged fish; fishing in this division, other than the depletion experiment conducted by Spain, is restricted to the Research Blocks only. Further details on research in this Division are given in section 5.
2. Reported catch
2.1. Latest reports and limits
The catches of D. mawsoni and D. eleginoides from Division 58.4.1 are provided in Table 1. In this fishery, the catch of D. mawsoni reached a maximum of 517 tonnes in 2007. In 2018, when fishing last occurred, 264 tonnes of D. mawsoni were caught.
The catches reported in Division 58.4.1 include catch data from particular vessels that CCAMLR has agreed should be quarantined as there is no confidence in the amount and/or the location of those catches (SC-CAMLR-XXXIII, paragraph 3.68). All ancillary data associated with these vessels (e.g., by-catch, tagging, observer data) are also quarantined and are not included in the data presented in this report.
| Season | Number of vessels | Catch limit (tonnes) | D. eleginoides | D. mawsoni | Estimated IUU catch (tonnes) |
|---|---|---|---|---|---|
| 2005 | 7 | 600 | 1 | 479 | – |
| 2006 | 6 | 600 | 0 | 420 | 597 |
| 2007 | 4 | 600 | 0 (q: 94) | 517 (q: 24) | 626 |
| 2008 | 6 | 600 | 1 | 410 | 136 |
| 2009 | 3 | 210 | 0 | 162 (q: 60) | 152 |
| 2010 | 2 | 210 | 2 | 86 (q: 108) | 910 |
| 2011 | 3 | 210 | 0 | 113 (q: 101) | – |
| 2012 | 1 | 210 | 0 | 157 | – |
| 2013 | 2 | 210 | 0 | 48 | – |
| 2014 | 1 | 724 | 1 | 101 | – |
| 2015 | 1 | 724 | 0 | 122 | – |
| 2016 | 3 | 660 | 1 | 400 | – |
| 2017 | 3 | 660 | 2 | 206 | – |
| 2018 | 4 | 545 | 1 | 264 | – |
| 2019 | – | 579 | – | – | – |
| 2020 | – | 583 | – | – | – |
| 2021 | – | 583 | – | – | – |
| 2022 | – | 583 | – | – | – |
| Directed fishing did not take place since 2019 as per CM 41-11 paragraph 1. |
| Research Block | Catch limit | Catch (% of catch limit) |
|---|---|---|
| 58.4.1_1 | 138 | – (-%) |
| 58.4.1_2 | 139 | – (-%) |
| 58.4.1_3 | 119 | – (-%) |
| 58.4.1_4 | 23 | – (-%) |
| 58.4.1_5 | 60 | – (-%) |
| 58.4.1_6 | 104 | – (-%) |
| Directed fishing did not take place since 2019 as per CM 41-11 paragraph 1. |
2.2. By-catch
Catch limits for by-catch species groups (Macrourus spp., skates and rays, and other species) are defined in Conservation Measure 33-03.
The by-catch in Division 58.4.1 consists predominantly of Macrourus spp. (Table 3).
| Season | Catch Limit (tonnes) | Reported Catch (tonnes) | Catch Limit (tonnes) | Reported Catch (tonnes) | Number Released | Catch Limit (tonnes) | Reported Catch (tonnes) |
|---|---|---|---|---|---|---|---|
| 2005 | 96 | 17 | 100 | <1 | 0 | 60 | 1 |
| 2006 | 96 | 15 | 100 | <1 | 0 | 60 | <1 |
| 2007 | 96 | 28 q | 100 | <1 | 0 | 60 | 1 q |
| 2008 | 96 | 35 | 100 | <1 | 0 | 60 | 1 |
| 2009 | 33 | 3 q | 100 | <1 q | 0 q | 60 | <1 q |
| 2010 | 33 | 5 q | 100 | 0 | 0 | 60 | <1 q |
| 2011 | 33 | 3 q | 100 | 0 | 0 | 60 | <1 q |
| 2012 | 33 | 2 | 100 | 0 | 0 | 60 | <1 |
| 2013 | 33 | 5 | 100 | <1 | 0 | 60 | <1 |
| 2014 | 116 | 6 | 100 | <1 | 0 | 100 | <1 |
| 2015 | 116 | 2 | 100 | 0 | 0 | 100 | <1 |
| 2016 | 105 | 49 | 100 | <1 | 21 | 100 | 2 |
| 2017 | 85 | 26 | 28 | <1 | 34 | 85 | 2 |
| 2018 | 88 | 35 | 27 | 0 | 0 | 88 | 2 |
| 2019 | 103 | – | 30 | – | – | 103 | – |
| 2020 | 94 | – | 29 | – | – | 94 | – |
| 2021 | 94 | – | 29 | – | – | 94 | – |
| 2022 | 94 | – | 29 | – | – | 94 | – |
| Directed fishing did not take place since 2019 as per CM 41-11 paragraph 1. |
2.3. Vulnerable marine ecosystems (VMEs)
All Members are required to submit, within their general new (Conservation Measure 21-01) and exploratory (Conservation Measure 21-02) fisheries notifications requirements, information on the known and anticipated impacts of their gear on vulnerable marine ecosystems (VMEs), including benthic communities and benthos such as seamounts, hydrothermal vents and cold-water corals. All of the VMEs in CCAMLR’s VME Registry are currently afforded protection through specific area closures.
By the end of this fishing season, there were 2 VMEs and 1 VME Risk Area designated in Division 58.4.1.
2.4. Incidental mortality of seabirds and marine mammals
There have been no observed incidental mortalities of birds reported by vessels in Division 58.4.1 in this fishery.
There have been no observed incidental mortalities of mammals reported by vessels in Division 58.4.1 in this fishery.
The requirements of Conservation Measure 25-02, including the ‘Minimisation of the incidental mortality of seabirds in the course of longline fishing or longline fishing research in the Convention Area’ apply to this fishery. There is an exemption to the requirement for night setting by achieving the sink rates described in Conservation Measure 24-02 and subject to a bird by-catch limit.
The risk level for birds in the fishery in Division 58.4.1 is category 2 (average to low) (SC-CAMLR-XXX, Annex 8, paragraph 8.1).
3. Illegal, Unreported and Unregulated (IUU) fishing
Illegal, unreported and unregulated (IUU) fishing activity was reported in Division 58.4.1 in 2006 with four IUU fishing vessel sightings, in 2007 when there were two to three IUU fishing vessel sightings, and in both 2008 and 2009 when one IUU fishing vessel was sighted in each year. This increased to five IUU-listed vessels observed during 2010 followed by four IUU vessels, two using gillnet, one longliner and one refrigerated cargo vessel, in 2011. There were two IUU-listed vessels and one unknown vessel sighted in 2012 and three IUU-listed vessels reported in both 2014 and 2015. In 2014, one vessel that emitted an emergency distress signal was not located, but debris was sighted. No IUU vessel sightings were reported in 2016 although some gillnet was recovered during legal fishing operations. However, since 2011, following the recognition of methodological issues in its assessment, no estimates of the IUU catch of Dissostichus spp. have been provided for this division (SC-CAMLR-XXIX, paragraph 6.5).
CCAMLR-XXXVI/28 Rev. 2 provided detailed information on fishing activities of IUU-listed vessels from Division 58.4.1 in 2014 following Operation Sparrow II conducted by Spain. The vessels reported catch for insurance purposes and took an estimated 792 tonnes. The IUU vessels Asian Warrior, Atlantic Wind and Zemour 1 have a long history of operating together in the Convention Area, usually supported by a reefer vessel, and have likely undertaken similar fishing activities every year since they were first sighted in the Convention Area.
Based on the unprecedented availability of information from IUU vessels in Division 58.4.1, including catch data and video footage of fishing operations, WG-FSA-18/60 evaluated toothfish catch per unit effort (CPUE) (by weight and number), by-catch species and size compositions, temporal variation in the spatial distribution of IUU activity, the temporal and spatial distribution of authorised fishing vessels in relation to available IUU activity to review the potential impacts of IUU removals on previous research conducted in the region and the relationship between reported IUU vessel sightings and actual levels of removals.
4. Data collection
4.1. Data collection requirements
The collection of biological data under Conservation Measure 23-05 as part of the CCAMLR Scheme of International Scientific Observation (SISO) includes representative samples of length, weight, sex and maturity stage, as well as collection of otoliths for age determination of the target and most frequently taken by-catch species.
4.2. Summary of available data
Both the vessel’s crew and observers collect fishing effort, catch, and by-catch information.
Following Conservation Measure 22-07, vessels participating in this fishery must report the occurrence of VME indicator organisms on hauled lines. To do so, the vessel’s crew observe lines in segments (1000-hook sections or 1200m sections, whichever is the shorter) and report the number of VME indicator units (either one litre of those VME indicator organisms that can be placed in a 10-litre container, or one kilogram of those VME indicator organisms that do not fit into a 10-litre container). Depending on the number of VME indicator units landed, vessels must immediately report and potentially cease fishing in the area (termed a Risk Area) until further review of the data is completed (see Conservation Measure 22-07). Based on the portion of the line monitored, observers further identify VME indicator organisms to the lowest taxonomic level possible.
The vessel’s crew report total catch of non-VME by-catch (mostly fishes) by coarse taxonomic groups given the taxonomic expertise required to discriminate similar species. Observers collect biological information on toothfish and by-catch specimens at a finer taxonomic resolution, as well as data on individual specimens such as size and maturity.
Summaries of data reported to CCAMLR for the past five years are given in Tables 4 and 5.
| Data source | Data class | Variable | 2018 | 2019 | 2020 | 2021 | 2022 |
|---|---|---|---|---|---|---|---|
| Vessel crew | VME | line segments | 1473 | – | – | – | – |
| VME indicator units > 5 and < 10 | 0 | – | – | – | – | ||
| VME indicator units > 10 | 0 | – | – | – | – | ||
| by-catch | taxa identified | 25 | – | – | – | – | |
| records | 670 | – | – | – | – | ||
| Observer | VME | line segments | 853 | – | – | – | – |
| taxa identified | 13 | – | – | – | – | ||
| weight or volume measurements | 103 | – | – | – | – | ||
| toothfish | specimens examined | 6078 | – | – | – | – | |
| length measurements | 6062 | – | – | – | – | ||
| weight measurements | 6076 | – | – | – | – | ||
| sex identifications | 6077 | – | – | – | – | ||
| maturity stage identifications | 3751 | – | – | – | – | ||
| gonad weight measurements | 5239 | – | – | – | – | ||
| otolith samples | 3132 | – | – | – | – | ||
| by-catch | specimens examined | 7696 | – | – | – | – | |
| taxa identified | 19 | – | – | – | – | ||
| length measurements | 6038 | – | – | – | – | ||
| weight measurements** | 7671 | – | – | – | – | ||
| standard length measurements* | 0 | – | – | – | – | ||
| wingspan measurements* | 0 | – | – | – | – | ||
| pelvic length measurements* | 0 | – | – | – | – | ||
| snout to anus measurements* | 5538 | – | – | – | – | ||
| sex identifications** | 6493 | – | – | – | – | ||
| maturity stage identifications** | 1304 | – | – | – | – | ||
| gonad weight measurements** | 1287 | – | – | – | – | ||
| otolith samples** | 828 | – | – | – | – | ||
| Directed fishing did not take place since 2019 as per CM 41-11 paragraph 1. | |||||||
| **: Voluntary records | |||||||
| *: Species-dependent records |
| By-catch group | Variable | 2018 | 2019 | 2020 | 2021 | 2022 |
|---|---|---|---|---|---|---|
| Macrourus spp. | specimens examined | 5528 | – | – | – | – |
| taxa identified | 4 | – | – | – | – | |
| length measurements | 3920 | – | – | – | – | |
| weight measurements** | 5509 | – | – | – | – | |
| snout to anus measurements* | 5508 | – | – | – | – | |
| sex identifications** | 5254 | – | – | – | – | |
| maturity stage identifications** | 1303 | – | – | – | – | |
| gonad weight measurements** | 1287 | – | – | – | – | |
| otolith samples** | 805 | – | – | – | – | |
| Other fish | specimens examined | 2152 | – | – | – | – |
| taxa identified | 12 | – | – | – | – | |
| length measurements | 2114 | – | – | – | – | |
| weight measurements** | 2146 | – | – | – | – | |
| standard length measurements* | 0 | – | – | – | – | |
| sex identifications** | 1237 | – | – | – | – | |
| maturity stage identifications** | 1 | – | – | – | – | |
| gonad weight measurements** | 0 | – | – | – | – | |
| otolith samples** | 23 | – | – | – | – | |
| Directed fishing did not take place since 2019 as per CM 41-11 paragraph 1. | ||||||
| **: Voluntary records | ||||||
| *: Species-dependent records |
The counts of by-catch taxa reported above (Table 5) correspond to specimens that have been individually sampled by observers. These are a subset of all the specimens counted by observers and are generally identified at a more precise taxonomic level. The figures below (Figs. 2 and 3) display the distribution of the most frequently examined by-catch taxa in time and space. It is important to note that observers sample a random subset of lines and do not individually examine all taxa; as such these figures are more representative of the distribution of biological observations than the catch of these taxa or their spatial distribution. At a coarse taxonomic level, the total catch of by-catch species groups is provided in section 2.2 above.
Figure 2. Relative frequencies of the most commonly examined by-catch taxa in each of the last five seasons, from the observer data (unweighted raw counts of individually examined specimens). Taxonomic identification may occur at different levels. Directed fishing did not take place since 2019 as per CM 41-11 paragraph 1.
Figure 3. Spatial distribution of the most commonly examined by-catch taxa across the last five seasons, from the observer data (unweighted raw counts of individually examined specimens in each cell). The data were aggregated using equal area (100 km x 100 km) cells. Taxonomic identification may occur at different levels. Refer to Figure 1 for more details on the boundaries shown. Directed fishing did not take place since 2019 as per CM 41-11 paragraph 1.
4.3. Length frequency distributions
The length frequency distributions of D. mawsoni caught in this fishery are shown in Figure 4. These length frequency distributions are unweighted; they have not been adjusted for factors such as the size of the catches from which they were collected. The interannual variability exhibited in the figure may reflect changes in the fished population but is also likely to reflect changes in the gear used, the number of vessels in the fishery and the spatial and temporal distributions of fishing.
The majority of D. mawsoni caught in the Division 58.4.1 fishery ranged from 100 to 175cm in length, with a relatively consistent broad mode at approximately 140cm (Fig. 4).
Figure 4. Annual length frequency distributions of Dissostichus mawsoni caught in Division 58.4.1 (top panel) and in each Research Block (lower panels). The number of hauls from which fish were measured (N) and the number of fish measured (n) in each year are indicated. Note: length frequency distributions are only shown where more than 150 fish were measured in a given season/area.
4.3. Tagging
Since 2012, vessels have been required to tag and release Dissostichus spp. at a rate of 5 fish per tonne of green weight caught. The tag-overlap statistic estimates the representative similarity between the size distributions of those fish that are tagged by a vessel and of all the fish that are caught by that vessel (Table 6). Each vessel catching more than 10 tonnes of each species of Dissostichus is required to achieve a minimum tag-overlap statistic of 60% (Annex 41-01/C).
To date in this area, 12408 D. mawsoni have been tagged and released (85 have been recaptured; Table 7), and, 381 D. eleginoides have been tagged and released (3 have been recaptured; Table 8).
| Flag State | Vessel name | 2010 | 2011 | 2012 | 2013 | 2014 | 2015 | 2016 | 2017 | 2018 | 2019 | 2020 | 2021 | 2022 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Australia | Antarctic Chieftain | 5.4 (80.2,NC) | ||||||||||||
| Australia | Antarctic Discovery | 5.1 (94.1,NC) | 6.1 (86.2,NC) | 5.3 (85.4,NC) | ||||||||||
| Spain | Tronio | 3.1 (55.3,NC) | 5.2 (69.4,NC) | 5.3 (72.1,NC) | 5.1 (83.5,NC) | 5.1 (67.2,NC) | 5 (73.9,NC) | |||||||
| France | Le Saint Andre | 5.2 (71.3,-) | ||||||||||||
| Japan | Shinsei Maru No. 3 | 3.1 (58.5,NC) | ||||||||||||
| Republic of Korea | Hong Jin No. 701 | 4.7 (74.1,NC) | 5.2 (89.4,-) | |||||||||||
| Republic of Korea | Insung No. 3 | 9.4 (NC,-) | ||||||||||||
| Republic of Korea | Kingstar | 5.1 (92.1,NC) | 5 (89.1,NC) | 5.2 (90.7,NC) | ||||||||||
| Total | 3.1 (58.5,NC) | 3.6 (55.9,NC) | 5.2 (89.4,-) | 5.4 (71,NC) | 5.3 (72.1,NC) | 5.1 (92.1,NC) | 5.1 (89,NC) | 5.2 (85.7,NC) | 5.2 (78.2,NC) | |||||
| Directed fishing did not take place since 2019 as per CM 41-11 paragraph 1. |
| Flag State | Vessel name | 2010 | 2011 | 2012 | 2013 | 2014 | 2015 | 2016 | 2017 | 2018 | 2019 | 2020 | 2021 | 2022 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Australia | Antarctic Chieftain | 395 (13) | ||||||||||||
| Australia | Antarctic Discovery | 247 (3) | 51 (1) | 90 (0) | ||||||||||
| Spain | Tronio | 232 (2) | 227 (0) | 522 (6) | 618 (2) | 324 (6) | 617 (12) | |||||||
| France | Le Saint Andre | 260 (2) | ||||||||||||
| Japan | Shinsei Maru No. 3 | 263 (2) | ||||||||||||
| Republic of Korea | Hong Jin No. 701 | 180 (2) | 812 (0) | |||||||||||
| Republic of Korea | Insung No. 3 | 29 (0) | ||||||||||||
| Republic of Korea | Kingstar | 624 (3) | 1138 (5) | 695 (7) | ||||||||||
| Total | 263 (2) | 412 (4) | 812 (0) | 256 (0) | 522 (6) | 624 (3) | 2003 (10) | 1070 (14) | 1362 (27) | |||||
| Directed fishing did not take place since 2019 as per CM 41-11 paragraph 1. |
| Flag State | Vessel name | 2010 | 2011 | 2012 | 2013 | 2014 | 2015 | 2016 | 2017 | 2018 | 2019 | 2020 | 2021 | 2022 |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Australia | Antarctic Chieftain | 0 (1) | ||||||||||||
| Australia | Antarctic Discovery | 16 (0) | 8 (0) | 3 (0) | ||||||||||
| Spain | Tronio | 0 (0) | 4 (0) | 12 (0) | 8 (0) | 5 (0) | 6 (1) | |||||||
| France | Le Saint Andre | 0 (0) | ||||||||||||
| Japan | Shinsei Maru No. 3 | 12 (1) | ||||||||||||
| Republic of Korea | Hong Jin No. 701 | 0 (0) | 0 (0) | |||||||||||
| Republic of Korea | Insung No. 3 | 0 (0) | ||||||||||||
| Republic of Korea | Kingstar | 0 (0) | 5 (0) | 0 (0) | ||||||||||
| Total | 12 (1) | 0 (0) | 0 (0) | 4 (0) | 12 (0) | 0 (0) | 29 (0) | 13 (0) | 9 (2) | |||||
| Directed fishing did not take place since 2019 as per CM 41-11 paragraph 1. |
5. Research
5.1. Status of the science
While catch limits for CCAMLR’s fisheries for D. mawsoni and D. eleginoides for the ‘assessed’ fisheries are set using fully integrated assessments, more basic approaches are used for the ‘data-poor’ fisheries (in Subarea 48.6 and in Area 58 outside the exclusive economic zones (EEZs)). CCAMLR has developed a framework for designing and undertaking research fishing designed to lead to an assessment of these toothfish stocks in the short to medium term, established under the provisions of Conservation Measure 41-01. This research planning framework has three phases: prospecting phase, biomass estimation phase and assessment development phase, with a set of decisions and review for the progression between stages.
In order to obtain the data necessary for a stock assessment, catch limits for research fishing by commercial vessels are set at a level intended to provide sufficient information (including sufficient recaptures of tagged fish) to achieve a stock assessment within a time period of 3 to 5 years. These catch limits are also set so that they provide reasonable certainty that exploitation rates at the scale of the stock or research unit will not negatively impact the stock. Appropriate exploitation rates are based on estimates from areas with assessed fisheries and are not more than 3-4% of the estimated stock size.
In 2018, an initial stock assessment model was developed for Antarctic toothfish in Divisions 58.4.1 and 58.4.2 (WG-FSA-18/58 rev1) but required more development to provide management advice on catch limits.
Spanish and Australian scientists worked on the age and growth estimates of Antarctic toothfish within divisions 58.4.1 and 58.4.2 from 2015 and 2017 respectively. During 2019, Korean scientists joined this colaborative work (WG-FSA-2019/47).
In 2021, WG-FSA-2021/18 presented a report of research activities conducted in this Division since 2012.
In 2022, WG-FSA-2022/10 provided an overview of the deployments of Conductivity, Temperature and Depth (CTD) loggers and Benthic Video Cameras (BVCs) in this fishery which revealed that the majority of fishing activity occurred in waters with unconsolidated soft substrate with very low densities of VME taxa. WG-FSA-2022/21 reported on fish by-catch in this fishery since 2016, indicating the dominance of Macrourus spp. among which females dominated, without changes in length frequency distribution patterns over time. WG-FSA-2022/25 examined simulated egg and larval transport under different Southern Annular Mode (SAM) phases in the continental shelf-slope regions of East Antarctica using particle tracking models, indicating a negative relationship between the relative SAM phase and the predicted percentage of successful transport. The paper recommended that both continuous sampling and tagging research would be useful to inform model structure and validate outputs. WG-FSA-2022/34 presented an updated preliminary integrated stock assessment for this fishery indicating that the Antarctic toothfish stock in Divisions 58.4.1 and 58.4.2 was unlikely to be depleted by the current level of fishing mortality. The model also clearly highlighted the impact of no fishing in Division 58.4.1 over the last four years. The lack of data from this Division is strongly impacting on the ability of the model to accurately estimate spawning biomass and precautionary catch levels for this exploratory toothfish fishery.
5.2. Research plans
5.2.1. Background
Exploratory fishing for toothfish (Dissostichus spp.) in Division 58.4.1 began in 2003. However, a robust stock assessment and catch limits according to CCAMLR decision rules remain to be determined for this Division. Accordingly, the current exploratory Antarctic toothfish (Dissostichus mawsoni) fishery in this Division has been identified as ‘data-poor’. In 2011, Research Blocks were designated in areas where previous tag releases had occurred. Research plans are generally focused in these areas, to facilitate the development of local biomass estimates. All Members notifying to fish in Division 58.4.1 submitted a research plan, based on Conservation Measure 24-01, Annex 24-01/A, format 2.
In 2015, proposals to conduct research in Division 58.4.1 were presented in multiple research plans by Australia (commenced 2015/16), France (commenced 2016/17), Japan (commenced 2016/17), Republic of Korea (commenced 2012/13) and Spain (commenced 2012/13). This research has continued in 2016, 2017 and 2018.
In 2018 and 2019, two multi-member research plans on the Dissostichus mawsoni exploratory fishery in East Antarctica (Divisions 58.4.1 and 58.4.2) were proposed, one by Australia, France, Japan, the Republic of Korea and Spain (WG-FSA-2019/44), and one by Russia (WG-FSA-2019/52). However, CCAMLR could not achieve consensus on any research fishing going ahead in 2019 and 2020.
In 2021, two multi-member research plans on the Dissostichus mawsoni exploratory fishery in East Antarctica (Divisions 58.4.1 and 58.4.2) were proposed, one by Australia, France, Japan, the Republic of Korea and Spain (WG-SAM-2021/03), and one by Russia (WG-FSA-2021/42). However, CCAMLR could not achieve consensus on any research fishing going ahead in Division 58.4.1 in 2022.
In 2022, a multi-member research plan for the Dissostichus mawsoni exploratory fishery in East Antarctica (Divisions 58.4.1 and 58.4.2) was submitted by Australia, France, Japan, the Republic of Korea and Spain (WG-SAM-2022/04). The research plan had been updated with relevant details for all notified vessels, and random depth-stratified sampling locations in all research blocks as per the survey design for the 2023 season. However, CCAMLR could not achieve consensus on any research fishing going ahead in Division 58.4.1 in 2023.
5.3. Advice by the Scientific Committee
In 2016, the Scientific Committee considered the advice of WG-FSA on research in Divisions 58.4.1 and 58.4.2 and agreed that the research plan in WG-FSA-16/29 Rev. 1 is appropriate to achieve the research objectives and endorsed the recommendation from WG FSA-16 (SC-CAMLR-XXXV, Annex 7, paragraph 4.118) that the new proposed Research Rlock 5841_6 be opened on an interim basis, with results to be reviewed by WG SAM and WG FSA in 2017.
In 2017, the Scientific Committee recommended that the catch limits for these divisions remain unchanged for 2018 and supported the catch allocation scheme developed by the research proponents in 2016.
Since 2018, the Commission was unable to reach consensus on the research plan for the exploratory fishery in Division 58.4.1 (e.g., SC-CAMLR-41 paragraphs 3.125-3.136; CCAMLR-41 paragraphs 4.45-4.53).
6. Stock status
6.1. Summary of current status
As a data-limited fishery, this fishery does not have such estimates.
6.2. Assessment method
Stock biomass and catch limits in data-limited fisheries are estimated using the trend analysis.
6.3. Year of last assessment, year of next assessment
Research plans for data-limited fisheries are reviewed annually.
7. Climate Change and environmental variability
In 2018, a summary of the potential impacts of climate change on Southern Ocean fisheries (FAO 2018) highlighted the following key points:
The Antarctic region is characterized by complex interaction of natural climate variability and anthropogenic climate change that produce high levels of variability in both physical and biological systems, including impacts on key fishery taxa such as Antarctic krill. The impact of anthropogenic climate change in the short-term could be expected to be related to changes in sea ice and physical access to fishing grounds, whereas longer-term implications are likely to include changes in ecosystem productivity affecting target stocks. There are no resident human populations or fishery-dependent livelihoods in the Commission for the Conservation of Antarctic Marine Living Resources (CCAMLR) Area, therefore climate change will have limited direct implications for regional food security. However, as an “under-exploited” fishery, there is potential for krill to play a role in global food security in the longer term. The institutional and management approach taken by CCAMLR, including the ecosystem-based approach, the establishment of large marine protected areas, and scientific monitoring programmes, provides measures of resilience to climate change.
In 2022, the Commission recognised that climate change is already having effects in the Convention Area (CCAMLR-41, paragraph 6.3) and agreed that it needed to act urgently to prepare for, and adapt to, the effects of climate change on the marine ecosystems within the Convention Area (CCAMLR-41, paragraph 6.5). The Commission noted (CCAMLR-41, paragraph 6.4) that the Scientific Committee had incorporated climate change into its advice (SC-CAMLR-41, paragraph 7.8) and through discussions at the SC-Symposium (SC-CAMLR-41, Annex 11) had also added climate change to the work plans and terms of reference of its Working Groups (SC-CAMLR-41, paragraph 7.14). The Commission also welcomed (CCAMLR-41, paragraph 6.8) the Scientific Committee’s agreement to hold a workshop on climate change in the first half of 2023 (SC-CAMLR-41, paragraph 7.10) and encouraged the inclusion of a range of scientific experts as well as policy makers to foster integration of the best available science into management actions. The Commission adopted (CCAMLR-41, paragraph 6.28) Resolution 36/41.