CCAMLR

Framework for IPOA-Seabirds implementation and structure of NPOA-Seabirds is discussed. Interagency cooperation as well as international cooperation is vital for the efficient and effective implementation of IPOA and NPOA. Education and outreach activities are listed. Numerous opportunities for international outreach and cooperation occurred in 2002.

Estimates of age and growth were determined from 156 Macrourus carinatus otolith samples collected during two research voyages to Heard and McDonald Islands (Division 58.5.2) in 1992 and 1993. The estimated range of ages was 4 – 25 years. von Bertalanffy growth parameters were calculated for both sexes combined, resulting in values of: L8 = 635 mm, K = 0.088 and t0 = -1.8. The size at sexual maturity of M. carinatus was determined from 162 specimens collected during commercial fishing operations in the Heard Island region in 2000. The size at which 50% of the fish population is mature, L50 was 417 mm total length and the size at which 50% of the fish population have spawned for the first time, Lm50 was 512 mm total length. An updated length-weight relationship is provided from 633 specimens of M. carinatus collected from Heard and McDonald Islands and Macquarie Island. No difference was evident in the length-weight relationship from the two regions. Otolith and body size relationships were also calculated for M. carinatus from Division 58.5.2.

A survey of mackerel icefish, Champsocephalus gunnari, was undertaken in Division 58.5.2 in the vicinity of Heard Island in May 2002 to provide the information for an assessment of yield in the 2002/2003 CCAMLR season. This paper provides a preliminary assessment of yield using the assessment methods of CCAMLR and discusses the implications of these results in relation to previous CCAMLR assessments. The estimate of biomass of mackerel icefish for the population at Heard Island was not significantly different from previous years but the one-sided lower 95% confidence bound was greater than in 2001 probably because the population was more uniformly spread in the southeast with relatively high densities in that stratum. The composition of the population was observed to comprise a single large cohort of mostly three and four year old fish in May 2002. Given the size of the fish, the expectation from current estimates of length at age parameters would be for most of the fish to be three year olds. However, given the abundance of fish in the population and the age structure of fish last year, it would be more reasonable to conclude that most of the fish are four years old, as this age class comprised the larger fraction (93%) of the population last year. Two assessments were undertaken as a result of the potentially different interpretations as to the composition of the larger cohort. If the cohort comprised mostly three year old fish then the yield for 2002/03 is estimated to be 1990 tonnes. If it comprises mostly four year olds then the yield would be 1815 tonnes. It is also proposed that the minimum size of capture be increased for 2002/03 to protect the younger unassessed cohort of fish from being exploited as they potentially enter the fishery towards the end of the season.

This paper presents estimates of the total removals of fish and invertebrate bycatch by fishing season and fishing ground, from the D. eleginoides and C. gunnari trawl fisheries in Division 58.5.2. On average, 94 % of hauls in the D. eleginoides fishery and 93% of hauls in the C. gunnari fishery were observed. The percentage of observed hauls was used as a scaling factor to convert observed bycatch weights to estimates of total bycatch removed from the fishery. Bycatch in these trawl fisheries is very low. From 1996/97 to 2001/02, a total of 95 tonnes of bycatch was caught in the D. eleginoides fishery and 46 tonnes in the C. gunnari fishery. These values represent 1 and 2% respectively, of the total catch weight (target and non-target species) in each fishery. The composition of the bycatch is described by fishing ground and fishery. The operation of the ‘move-on’ rule, which aims to minimise localised depletion of bycatch is also discussed.

The proposals for comparative tests of bottom trawls are presented. The following sections are discussed: place and time of realization; preparatory works; comparative trawlings; acoustic support; observation data processing.

Results of the acoustic survey of icefish carried out by Russian vessel STM-8390 Atlantida in February-March 2002 in Subarea 48.3 are presented. Biomass and distribution of icefish were obtained using multi-frequency echosounder EK-500 and Sonar Data EchoView software.
Target strength estimates of icefish were made by comparison an observed TS in situ histograms with the size composition of the ensonified fish, obtained by trawling.
Results of acoustic estimates of icefish biomass and abundance values by size class in pelagic zone and in the near-bottom 8m layer (covered by bottom trawling survey) are discussed. The major part of pelagic biomass was concentrated within 50m above the bottom 8m layer and amounted to 23,037.4 tonnes. This estimate can be considered as the minimum value of the pelagic component of the icefish stock, since it does not take into account the biomass of the fish distributed within higher depth ranges where, according to the data of trawling and acoustic sampling, icefish are also available. The bottom biomass resulted in the estimate of 62,328.0 tonnes. The sum acoustic estimate of the icefish biomass in the subarea of South Georgia amounted to 92.6 thous. tonnes. Nearly 30% of this biomass was concentrated in the pelagic zone. If acoustic estimates of pelagic and bottom components of the icefish biomass are compared it will become evident that the pelagic part of biomass makes up nearly 42% of the bottom biomass. Our acoustic estimate of the pelagic biomass constitutes about 60% of biomass obtained from bottom trawling survey.
In additional to the above-states estimates the abundance of juvenile fishes (speciments less than 6cm) was obtained in the sub-surface 50-m layer where, according to trawl samples, the latter predominated. Sum abundance of young fish constituted 7344.6 million pcs.
The horizontal and vertical distributions of krill with reference to investigation of regularities of icefish behavior and distribution are discussed.

Longline fisheries have expanded throughout the world’s oceans since major commercial distant-water pelagic fleets began fishing for tuna and tuna-like species in the early 1950s. Along with the more recent development and expansion of demersal longline fleets for species such as Patagonian toothfish, these vessels are a major source of mortality to several species of seabird. Vessels can set many thousands of baited hooks in a day across many kilometres of water. These waters are often used as foraging areas by wide-ranging seabirds. Attracted by baits and offal, the birds can be caught on the baited hooks and subsequently drown. To provide a greater understanding of the potential impact of the Southern Ocean’s longline fleets on seabird populations, this paper describes the trends in longline effort of the major pelagic and demersal fisheries in southern waters. The total reported effort from all longline fleets south of 30?S has been well over 250 million hooks per year since the early 1990s. However the spatial and temporal distribution of this effort has not been constant. While effort from the Japanese pelagic distant-water longline fleet declined through the 1990s, the Taiwanese fleet expanded dramatically. Likewise demersal fishing for toothfish increased markedly during the mid-1990s. These fisheries, along with substantial illegal longline fisheries, may be placing the long-term viability of many Southern Ocean species of seabird in jeopardy.

Regression equations relating total length (TL), pelvic length, disc width and weight are provided for Amblyraja georgiana by sex, and for both sexes combined. For all regressions, there were significant differences between the two sexes: females are broader and heavier than males at lengths greater than about 90 cm TL. There were insufficient data to adequately define length-length and length-weight relationships for Bathyraja eatonii, but preliminary regressions are provided for the two sexes combined. It is probable that large females are larger and heavier than males of the same size. The regressions for these species should be used with caution.
The length at 50% maturity for male A. georgiana is about 91 cm TL, and females appear to mature at a similar or slightly greater length. The length at 50% maturity of male and female B. eatonii could not be accurately determined, but may be around 90–100 cm, and greater than 100 cm, respectively.
To date, c. 6000 skates have been tagged in sub-area 88.1 over the 1999–2000 through 2001–02 seasons. Returns suggest some long-term survival, small-scale migration within-season, and limited movement between seasons. Results are considered preliminary, given the short time span of the programme, and the confounding effect of spatial variation in fishing effort between seasons, resulting largely from changes in annual ice pattern.

This report provides the first analysis of standardised catch per unit of effort (CPUE) from the exploratory fishery for Antarctic toothfish Dissostichus mawsoni, which has operated in Subarea 88.1 for five seasons, from 1997 to 2002. Two analyses are presented. The first (all-ground) analysis reviewed catch from 1998 to 2002 (excluding the 1997 season as insufficient data were available), and included a number of areas that had been fished for only one season. The second (main-ground) analysis reviewed CPUE from the two main vessels involved in the fishery, and reviewed their catch from the main area of the fishery which had been consistently fished over most seasons.
For the all-ground analysis, variables area, season, length of line, soaktime, latitude and month in season entered the model, in order. This model explained 32% of the data variability, but was influenced by exploratory fishing activity. For the main-ground analysis, variables area, length of line, season, month, latitude, soaktime and type of set (research or exploratory) entered the model, in order. This model explained 34% of the data variability, because it excludes fishing grounds that were fished for only one season. Annual indices from both models show an increasing trend over the duration of the fishery, except for the 2001 season. Fishing in 2001 was poor, as bad weather and thick ice conditions precluded access to the main fishing grounds. The index for 2002 is the highest in the series, which suggests that the New Zealand toothfish fishery is not under stress from the current level of fishing activity. However, both models have relatively low predictive power, and are a relatively poor fit to the data, and these trends should be interpreted with caution. This is due to the exploratory nature of the fishery, and the unbalanced nature of the distribution of effort among seasons. As only four years of data are available for analysis, these trends are considered to be preliminary indications only.