CCAMLR

Preliminary results of testing of a PIT-D device for autonomous measurements of temperature and pressure at deepwater longline fishery of Antarctic toothfish D. Mawsoni in the Ross Sea during the fishing season of 2006/07 are presented. Diagrams of a Spanish-type longline sink rate at deployment and water temperature on various horizons are shown.

Experiments were carried out on two fishing trawlers to test whether mincing all waste to a paste before it was discharged reduced the number of seabirds around the vessels. The first trial was on a mid-water trawler targeting hoki (Macruronus novaezelandiae), and the experiment on this trip compared three treatments (1) mincing all waste (2) discharging unprocessed waste and (3) mealing all waste and reducing discharge to sump water. The second vessel was bottom-trawling for squid (Nototodarus sloanii). There was no meal plant on board and the mealed treatment was replaced with a batching treatment (4) where waste was held and discharged in batches. The response to the experimental treatments was determined by counting the number of birds within a 40m-radius semi-circular sweep zone behind the vessel stern. Results from the first experiment showed that mincing reduced the numbers of large albatross (Diomedea spp.) feeding around the vessel, but had no significant effect on other groups of seabirds. In contrast, mealing all waste had a marked effect on several of the bird groups. In particular, the abundance of small albatross (principally Thalassarche spp.) within the sweep area was reduced to 5% of the number that were there when unprocessed waste was discharged. On the second trial a smaller mincer was used. The vessel was bottom trawling, and there were problems with rocks going through the waste stream. The batched treatment was compromised by the limited ability of the vessel to hold waste, with only a 10 to 20 minute delay between discharge events being achieved. Despite low numbers of observations on the second trial, the minced treatment suggested a reduction in the numbers of all albatross within the observation area.

A preliminary field identification guide to the main fishes caught by toothfish longline boats fishing in the Ross Sea was prepared under the New Zealand Ministry of Fisheries Project ANT2005-02 and was used by Ministry of Fisheries observers and fishers during the 2006–07 season. That guide was revised in 2007 following comments and suggestions from the users and now covers 27 taxa. Mostly it provides information for identification to species but for liparids (snailfishes), zoarcids (eelpouts) and bathydraconids (dragonfishes) identification is at family level and for Muraenolepis (eel cods), and Pogonophryne (plunderfishes) identification is to genus. Identification to species for some fishes is difficult because of uncertain taxonomic status, e.g., Pogonophryne, or scarcity of field characters, e.g., liparids. Some species likely to be seen only in stomach contents of other fishes are included. Future revisions could be made as taxonomic issues are resolved, and more species are recorded from the Ross Sea. Data and images are stored on a relational database to facilitate revision and easy information retrieval.

The descriptive analyses of the toothfish tagging programme carried out in Subareas 88.1 and 88.2 since 2001 are updated, including data for the 2007 season for all vessels. This paper provides an update of the preliminary tag-release and tag-recapture data that were presented at the July 2007 meeting of WG-SAM by including revised data and data from non-New Zealand vessels that fished in 2007.
Overall, a total of 15 088 Antarctic toothfish have been reported as released and 458 recaptured, and 911 Patagonian toothfish released and 43 recaptured since 2001.
The number of tags recaptured in the Ross Sea in 2007 by New Zealand vessels was the highest annual recapture to date and double the number caught in 2006, although the nature of these recaptures suggests that assumptions of homogeneous mixing may need to be investigated. For the first time, long distance movements of Antarctic toothfish were observed from toothfish tagged by fishing vessels. Six fish moved 400–600 km from the slope fisheries in SSRUs 88.1H, 88.1I, and 88.1K to grounds off Terra Nova Bay and Ross Island in SSRU 88.1J. There was also some evidence that more fish are recaptured after a longer time at liberty on the slope than in the North. In addition, a Patagonian toothfish tagged near Macquarie Island was recaptured in the north of the Ross Sea, after 4 years at liberty.
Analysis of tag recapture rates suggested some evidence that rates between New Zealand and non-New Zealand vessels were different, and further, that the rate that tags were recaptured from vessels of different nations were different. The reason for these differences is unclear, but may related to different survival rates of fish tagged by different vessels, different detection rates of tagged fish on different vessels, and/or incomplete spatial mixing of the fish tagged by different vessels in different local regions. Further investigation is required.

Skates are an important bycatch of the toothfish fishery in the CCAMLR area and have been identified as priority taxa for which assessments of status are required (e.g., SC-CCAMLR XXIII 2004, paragraphs 4.172, 4.177 and 4.199). While Dunn et al. (2007) and Agnew et al. (2007) have developed preliminary assessment models for skates, they also highlighted that further information was required before a full assessment can be carried out. In 2007, CCAMLR-SAM-WG recommended (CCAMLR XXVI WG-SAM paragraph 8.10) a review of data requirements and a “Year of the Skate” for 2008–09 whereby data collection effort on bycatch will be concentrated on skate species in that year in order to inform a full skate assessment.
This paper discusses improvements to the fishery derived data that may be required to better inform an assessment of Ross Sea skates. We propose options for the appropriate collection of such data from the fishery and a revised skate tagging protocol. These changes could be piloted in the 2007–08 season by all or a subset of vessels fishing in the Ross Sea. The results from the pilot study may be useful to inform modifications to data collection systems that would be required in 2008–09, for the “Year of the Skate”. Note that we do not consider other information requirements such as determining biological parameters.

The results of the histological analysis of the Antarctic toothfish (Dissostichus mawsoni) gonad structure, caught in December-February, 2004-2005, by longliner YANTAR in subareas 88.1 and 88.2 of the Ross Sea are presented. The morphological parameters and indices of maturity have been described. The histological criteria of the assessment of the ovary maturity stages, cytological parameters of oocytes and type of the toothfish oogenesis have been determined. The analysis of the histological state of toothfish testes has been made, and the abnormal primary fusion renal and generative tissues in testis have been revealed. It was shown that for Antarctic toothfish during the fishing period the females with ovaries on the early III stage of maturity were dominated (47.0%), and males with testis on III stage of maturity (85.7%).

We provide an update of the Bayesian sex and age structured population stock assessment model for Antarctic toothfish (Dissostichus mawsoni) in the Ross Sea (Subareas 88.1 and SSRUs 88.2A–B), using revised catch, catch-at-age, and tag-recapture data for the 2007 season. The updated reference model resulted in a slightly lower estimate of initial biomass than the 2006 base case. The inclusion of the 2007 recaptures of 2006 tags released had the most substantive impact on the model estimates.
Models using tag-recapture data from all vessels are also presented. Inclusion of all vessels tagging data resulted in a more optimistic assessment. The more optimistic estimate was probably due to the lower recapture rate by non-New Zealand vessels, particularly in the early years. The reason for this is unclear, and may be related to different distributions of fishing effort by different vessels, to poorer survival of tagged fish, or to poorer detection rates. However, if data from all vessels was restricted to 2007 recaptures of 2006 releases, then model estimates were more similar to the 2007 reference model.
Overall, model fits to the data were adequate, and, as in previous assessments, the tag-release and recapture data provided the most information on stock size. Monte-Carlo Markov Chain (MCMC) diagnostics suggested little evidence of non-convergence in the key biomass parameters. MCMC estimates of initial (equilibrium) spawning stock abundance (B0) for the 2007 reference model were estimated as 71 200 t (95% C.I.s 59 570–87 900 t), and current (B2007) biomass was estimated as 81.9% (78.4–85.4%). Estimated yields for the reference case, using the CCAMLR decision rules, were 2700 t.
Similar estimates of initial biomass and yield were obtained for models where the north fishing selectivity was assumed to be logistic (median B0=78 480 t, yield=2988 t), and where the 2007 recaptures from all vessels were added to the New Zealand tag-release and recapture data (median B0=81 100 t, yield=3099 t). If tag-release and recapture data for all vessels in all years were used, then the estimated initial biomass was higher (B0=110 130 t), and corresponding yields were also higher (yield=4200 t).

The current stock assessment in the Ross Sea (statistical Subareas 88.1 and 88.2) is underpinned by a tag and recapture programme, based on Antarctic toothfish Dissostichus mawsoni. The tagging of toothfish in this area is a mandatory requirement (Conservation Measure 41-01 Annex C). The Annex requires vessel to “target toothfish of all sizes in order to meet the tagging requirement”. This document details a number of methods and presents plans of some equipment used by New Zealand vessels operated by Sanford Limited a major New Zealand fishing company in order to satisfy this requirement. These techniques and equipment may have relevance in other tagging programmes for the closely related Patagonian toothfish Dissostichus eleginoides.

Aspects of the reproduction, size distribution, and movements of Antarctic toothfish Dissostichus mawsoni in CCAMLR Statistical Areas 88.1 & 88.2 were reviewed. Based on the presumed location and timing of spawning, and the probable early life history characteristics of toothfish, we investigated models that mimic the drift of eggs and larvae over a 6–24 month period using an oceanic circulation model linked to the high resolution global environmental model (HiGEM). The location of toothfish larvae after an 18–24 month period suggested by the models agreed moderately well with the distribution of the smallest toothfish taken in the toothfish fishery.
Our present hypothesis is that D. mawsoni in CCAMLR Statistical Subareas 88.1 and 88.2 spawn to the north of the Antarctic continental slope, mainly on the ridges and banks of the Pacific-Antarctic Ridge. The spawning appears to take place during winter and spring, and may extend over a period of several months. Depending on the exact location of spawning, eggs and larvae become entrained by the Ross Sea gyres, and may either move west settling out around the Balleny Islands and adjacent Antarctic continental shelf, south onto the Ross Sea shelf, or eastwards with the eastern Ross Sea gyre settling out along the continental slope and shelf to the east of the Ross Sea in Subarea 88.2. As the juveniles grow in size they move west back towards the Ross Sea shelf and then move out into deeper water (greater than 600m). The fish gradually move northwards as they mature, feeding in the slope region in depths of 1000–1500 m, where they gain condition before moving north onto the Pacific-Antarctic ridge to start the cycle again. Spawning fish may remain in the northern area for up to 2–3 years. They then move southwards back onto the shelf and slope where productivity is higher and food is more plentiful where they regain condition before spawning.
We recommend research surveys be carefully planned to test some of these hypotheses.

The ASPM assessment of the Prince Edward Islands toothfish resource by Brandão and Butterworth (2006) that permitted annual fluctuations about a deterministic stock-recruitment relationship is updated to take account of further catch, GLM standardised CPUE and catch-at-length information that has become available for the years 2006 and 2007. The assessment allows for a second fleet to accommodate data from a pot fishery that operated in 2004 and 2005. Biological parameter values adopted for Subarea 48.3 are used. The resource is estimated to be at about 37% of its average pre-exploitation level in terms of spawning biomass. It is suggested that it would be prudent to restrict annual legal catches to 500 tonnes or less, unless a large proportion of the catch is to be taken by pots (which avoid the cetacean predation associated with longlining).