Transfer of lipofuscin technology to the Central Ageing Facility
Final report
Lipofuscin is a metabolic by-product that accumulates in tissue of the nervous system, particularly the brain, and its occurrence has been shown to be widespread in crustaceans. Because it accumulates in the nervous tissue over time, the concentration of lipofuscin can be related to chronological age. A technique determining the age of crustacea using the ratio of the area of lipofuscin granules to neurons in the olfactory lobe cell mass (OLCM) in the brain of crustaceans has been developed by Dr M.R.J. Sheehy. The method was developed using a suite of crustaceans (Sheehy 1994), then transferred to Western Australian rock lobster (FRDC 93/090), and is currently being used for age determination of the European lobster (Hommarus gammarus).
The aim of this project was to transfer lipofuscin technology to the Central Ageing Facility (CAF) at the Marine and Freshwater Resources Institute (MAFRI).
Spawning and larval recruitment processes of commercially important species in coastal waters off Victoria
Final report
Pilot egg survey of orange roughy in the western zone
Final report
Development of an environment-recruitment model for black bream as a case study for estuarine fisheries management
Final report
Movement and re-aggregation of blacklip abalone in response to intensive fishing
Final report
Typically abalone are found clustered into aggregations of many individuals along gutters and ledges that dissect the surfaces of the reefs they inhabit. Commercial abalone divers take advantage of this clustering behaviour and specifically target aggregations to minimise the time spent searching for abalone and maximise their catch rates. This approach to abalone harvesting would be expected to progressively reduce the number and size of the aggregations to produce a less clustered pattern of distribution. Most methods used to detect changes in abalone abundance that result from fishing assume that abalone movement will have minimal effect on post-fishing patterns of distribution.
Abalone are generally viewed as relatively inactive organisms that occupy specific homesites from which they seldom move. Evidence for this lack of movement includes the oval shaped 'scars' of bare rock, free of algae and other immobile invertebrates, that remain after abalone are harvested. However there are many anecdotes describing the tendency for abalone to reform aggregations after fishing and during spawning periods. Presumably the latter promotes fertilisation success by increasing the quantities of sperm and eggs that mix in the water. It is unclear why abalone may aggregate into clusters outside spawning periods. If re-aggregation does occur after fishing, it is also unclear where these 'replacement' abalone come from. There is some speculation that small abalone may emerge from crevices and cryptic habitat. Other hypotheses include small-scale movements within aggregations or migration from unfished areas. An understanding of how re-aggregation occurs after fishing and to what extent it occurs, is essential to determine its effect on estimates of abalone abundance and to estimate important population characteristics such as rates of natural mortality.
Keywords: Haliotis rubra, abalone, dispersal, movement, aggregation, natural mortality, tag-loss, tag-recapture, stunted, growth.
Shark 'drop out rate' from hauling gill-nets in the southern shark fishery
Final report
Shark 'drop-out' is a term used by fishermen to describe the phenomenon where sharks fall out of shark gillnets during hauling operations. The term is distinguished from shark 'escapement' which is the phenomenon where sharks _struggle to free themselves from gillnets with a high probability of survival.
Sharks dropping out of gillnets and not surviving is not only a source of wastage but can cause fishing mortality to be under-estimated and natural mortality to be overestimated in stock assessments. Such biases, if large, can contribute to overly optimistic scenarios for the status of the stocks.
The FRDC funded 'Southern Shark Drop-Out Project, designed to estimate rates of drop-out through application of a 'remotely operated vehicle' (ROY), was abandoned after preliminary trials of an ROY on board FV Lincoln when it became apparent that the approach was impractical.
It was originally proposed that an ROY be deployed from a shark fishing vessel operating under normal commercial fishing conditions for the purpose of identifying species and estimating the length of captured sharks in gillnets immediately before the nets are hauled off the seabed and aboard the vessel. Subsequently identifying and measuring the sharks after hauling the gillnets would provide appropriate data for determining the rate at which sharks drop-out of the nets and for determining whether the rate of drop-out varied with species of shark, length of shark and mesh-size of the gillnets.
An alternative method to viewing the gillnets while being hauled was for the ROY to travel the full length of the nets on the seabed to count and estimate the lengths of the captured sharks. This approach was avoided because there would have been too much time between when most of the nets were viewed and when they were hauled. This approach would have underestimated the drop-out rate.
The original experimental design involved using gillnets of several mesh-sizes for 20 days at sea aboard a commercial shark fishing vessel fishing at various depths in the Great Australian Bight. In addition there was to have been several days of laboratory processing of data on film, statistical analysis of the data and preparation of a report. However because of difficulties associated with deployment of an ROY as proposed, the project was terminated before any quantitative data for estimating rates of 'dropout' were collected.
The ROY was tested initially beside the pier in the Thevenard harbour on 26 October and then three times in the vicinity of St Francis Island near Thevenard on 26 and 27 October 1995 with varying lengths of shark gillnet. No sharks were viewed by the ROY during these trials, and because of difficulties operating the ROY under sea conditions of waves less than 1 m and to avoid the risk of damage to the ROY no attempt was made subsequently to deploy the ROY under normal shark fishing conditions.