CCAMLR

In the Division 58.4.1 there are two stocks; one extends from the SSRU 58.4.1C to the SSRU 58.4.2A, and the other one to the SSRU 58.4.1H. The population sizes were vulnerable with a big range of about 1000-2000 t per SSRU in 58.4.1 and 100-1500 t per SSRU in 58.4.2. During the 2003-2007 fishing seasons, 3,434 toothfishes were tagged and released, but only 5 fishes among them have been recaptured which were not enough data to estimate stock biomass for considering the precautionary catch limit. The foodweb of toothfish stared to be studied recently only in the southern Ross Sea. Base on CCAMLR’s fishery report on 58.4.1 area as a whole is still data-poor fishery and is showing low recapture rate mentioned above. Consequently, providing catch and effort data, analyzing biological samples, and collecting recapture data focusing on SSRUs C, E, and G in Division 58.4.1 is very important to consider proper way for effective utilities of the population and ocean. Therefore, Korea notifies the participation in exploratory fishery for Dissostichus spp. in the SSRUs C, E, and G in Division 58.4.1 from 2012/2013 season to 2014/2015 using Korean commercial bottom longline vessel, NO.3 INSUNG in accordance with paragraph of CM 24-01 and paragraph 6(iii) of CM 21-02. The main objective of this scientific research plan is to assess the stock status of Dissostichus spp. in SSRUs C, E, and G in Division 58.4.1. We will collect the catch and effort, tagged and released, and recaptured dada and biological data to estimate biomass for Dissostichus spp. and assess the ecosystem-based fisheries. For the 1st year of this research, we will collect and analyze catch, effort, and biological data such as length, weight, gonadial development, otolith and muscle. During the 2nd year, we will collect the same data as the 1st year continuously. We will also submit the primarily results on the comparing catch rate between trot line and Spanish line, and estimations of biological parameters based on the collected data from the 1st research. For the 3rd year research, we will collect the same data consequently, and we will submit the results on the comparing results among the estimated biomass for Dissostichus spp. using three different analysis and ecosystem-based risk assessment.

We analysed the available data from vessel and scientific observer logbooks from the exploratory fishery for Antarctic toothfish (Dissostichus mawsoni) and Patagonian toothfish (D. eleginoides) in CCAMLR subarea 48.6 (South East Atlantic). This report summarises the catch, effort, timing, depth, location, size structure and maturity of Dissostichus spp.  Information on the composition of  bycatch species  caught in the fishery over the period 2003-4 to 2011-12 are also presented..  For the Antarctic toothfish, accumulated catch across years yielded 1,353 tons with the majority of the catch coming from SSRUs 48.6G and 48.6E. For the Patagonian toothfish the accumulated catch was 349 tons and almost all was reported exclusively in the SSRUs 48.6A and 48.6G. Most of the catches were reported by vessels from Japan (58%) and Rep. of Korea (31%) and to a lesser extent, from South Africa (7%) and Norway (4%).

Unstandardized raw catch and effort data suggested that the median catch per unit of effort in Antarctic toothfish has generally increased over the course of the fishery whilst it has decreased over time for Patagonian toothfish. In both species average length of catches is larger in females. Antarctic toothfish is caught at deeper waters and have a larger mean length than Patagonian toothfish. There is not evidence of truncation in the overall length frequency distribution of both species, although some evidence of reduction in the mean fish length has been observed in the last three fishing seasons. In both sexes, high frequencies of maturity stages 2 and 3 were observed in Antarctic toothfish whereas for Patagonian toothfish immature (stage 1) fish were  most frequently observed. The bycatch for both toothfish species is composed of few species. In term of biomass, the most important bycatch species are grenadiers and blue antimora. A total of 3,828 individuals of toothfish have been tagged in this area but only 19 have been recaptured. We concluded that from the data examined from the fishery to date there is not evidence for substantial changes in the population structure of both species in this subarea.

A reduced (three day) groundfish survey took place at Shag Rocks on the FV New Polar between the 26-28th January 2012. This survey was not intended to be a full biomass survey so only 20 random hauls were completed around Shag Rocks with 3 additional opportunistic sites at South Georgia. Reasonable catches of Patagonian toothfish were found around Shag Rocks (greater than in 2009 and 2010), with three size cohorts of fish identified including evidence of a new cohort of 2+ age fish (29-39cm). Catch-weighted length frequencies of mackerel icefish indicated that 2+ and 3+ sized fish dominated at Shag Rocks and Euphausiidae was the dominant prey item in the mackerel icefish diet. Strong acoustic marks, some of which may be attributable to icefish, were observed in the water column, and in only 23 hauls 15.2 tonnes of mackerel icefish were caught and following the survey mackerel icefish were caught commercially.

This paper presents an update of the assessment of toothfish (Dissostichus spp.) in Subarea 48.4. The Subarea is divided into two management regions and assessed using a CASAL assessment of D. eleginoides in the northern region and a simple Petersen biomass estimate derived for D. eleginoides and D. mawsoni in the southern region. The CASAL model structure used to assess the stock in 2011 has been retained although a small number of changes have been made to try to improve the fit of the model and to reduce the dependency on a relatively small amount of data. These changes comprise the addition of catch at age information for 2011, a minor change to the initial parameters of the selection pattern and the inclusion of additional information on size at age. CASAL estimates of stock size, harvest rate and recruitment are similar to those of last year’s assessment. B₀ is estimated at around 1,690 tonnes and B₂₀₁₂/B₀ at around 88%. Sustainable yield, calculated in accordance with the CCAMLR decision rules, is 63 tonnes for D.eleginoides in the northern region whilst sustainable yield calculated from the Petersen biomass estimates of Dissostichus spp. in the southern region and application of the gamma value (0.038) determined for toothfish in Subarea 48.3 was 52 tonnes. Options for the future development of the assessment of toothfish in Subarea 48.4 are considered.

• Genetic identification of grenadiers taken as bycatch in the toothfish longline fishery at South Georgia was compared with results of morphological identifications made by scientific observers and fisheries biologists.
• There was generally good agreement between methods although issues exist in the ability to morphologically distinguish between M. carinatus and M. holotrachys.
• Four species of Macrourus were identified genetically in the Southern Ocean and confirmed the presence of a recently described new species M. species.
• M. holotrachys was indistinguishable genetically from the Northern hemisphere species, M. berglax.
• There is a clear latitudinal separation of Macrourus species in the Southern Ocean.
• Latitudinal gradients in Macrourus distribution at the South Sandwich Islands reflect the patterns observed in toothfish spp.

Lepidonotothen squamifrons (Family Nototheniidae) is a demersal Southern Ocean endemic fish. Historically a commercially targeted species and common as bycatch, changes to CCAMLR fisheries regulations in 1989 have meant it is now only caught in sub-area 48.3 during research surveys. Data collected during groundfish surveys at South Georgia and Shag Rocks from 1986 to 2012 were analysed to investigate distribution, size, maturity, and diet. Distribution was patchy with aggregations in specific ‘hotspots’ to the east of Shag Rocks and the west of South Georgia. Reliable biomass estimates were not possible due to this skewed distribution creating large confidence intervals, but length-frequency analysis showed recognisable cohort progression and a trend of increasing size over time indicating a potential recovery of the stock. Mean length at first maturity for males and females (37-38cm ) was very similar to that described for the Indian Ocean basin population. Stomach content analysis (2005 - 2012) showed a varied diet dominated by salps/tunicates, but with ontogenetic and depth variations in prey composition. Enhanced knowledge of L. squamifrons in this region will be valuable in future research on habitat and foodweb modelling and spatial marine management.

Data from a seven-year (2002-2008) ichthyoplankton sampling programme in Cumberland Bay, South Georgia, sub-Antarctic (54.25^oS, 36.5^oW) were analysed to assess temporal changes in larval fish diversity and abundance. Larvae of twenty two species, representing nine families, were identified although three, Krefftichthys anderssoni (Myctophidae), Lepidonotothen nudifrons/T.hansoni (Nototheniidae) and C. gunnari (Channichthyidae), dominated abundance in all years. Significant seasonal and interannual differences in the larval fish assemblage were revealed by multivariate analyses (nMDS, ANOSIM, SIMPER). Multiple regression analyses indicated that larval abundance within Cumberland Bay was not significantly correlated with local SST or primary productivity.  Estimates of larval growth are provided for 5 abundant species. Considerable inter-specific differences in relative larval growth rate were recorded but interannual variability within species was small. However, in C. gunnari, multiple larval cohorts, representing a protracted spawning season, were observed to grow at different rates and this may be related to temperature and /or food availability. A comparison with historical growth data from South Georgia suggests there has been little change in growth rate for the main species over the last three decades.

Parasites are one of an integral part of any ecosystem and unfortunately knowledge about this ecological group in Antarctica is very scared. Partial geographical and ecological isolation of Antarctic circumpolar ecosystem plays its role on existence of endemic forms of animals, including parasites, which sometimes have unpredictably large sizes and distribution. The best example of it – Lophoura szidati. In this work we conclude the results of preliminary analysis of collected parasites of Antarctic fishes that were caught during longline fishing in seasons 2010/11 and 2011/12 in Subareas 88.1, 58.4 and 48.6.

Results of histological analysis of gonads of female and male Antarctic toothfish Dissostichus mawsoni caught in the Bellingshausen Sea in 2011- 2012 seasons are presented. Morphological indices of females and males, age, indices of gonads, fecundity, and condition by Fulton are described. In the Bellingshausen Sea the Antarctic toothfish had deferred reproductive ability compared with other subareas of the Pacific Antarctic studied previously, it was detected a low share of females with the ovaries at the stage of vitelligenous growth of oocytes (diameter 1.41-1.61 mm), and males with maturing spermatogonia. The individual absolute fecundity was 0.11-0.47 million eggs, relative fecundity –26-29 eggs per g.