Determination of the biological parameters required for managing the fisheries of four tuskfish species and western yellowfin bream
Determining biological characteristics of the champagne crab (Hypothalassia armata) for management purposes
Genetic (microsatellite) determination of stock structure of the blue swimmer crab in Australia
Apart from the work by Bryars & Adams (1997) on three assemblages of Potunus pelagicus in South Australia, there have been no studies aimed at determining the extent to which blue swimmer crabs are represented by different stocks in spatially-isolated habitats within a given geographical region in Australia. Furthermore, the studies in South Australia were carried out using allozymic analyses, which typically do not have the same ability to discriminate precisely between the boundaries of stocks, as can be achieved with the microsatellite techniques we intend to use in our proposed study (see Wright & Bentzen, 1995; OConnell & Wright, 1997).
As with all fisheries, a basic prerequisite for managing the fishery for blue swimmer crab is the identification of production units or stocks of a species since inadequate knowledge of stock structure may lead to over- or under-exploitation (Smith et al., 1997). For the following specific reasons, information as to whether there are one or more stocks of swimmer crabs, ie. genetically discrete assemblages, in a given region is crucial for managing the fishery for this portunid.
1. The ability of managers to respond appropriately to any marked decline in the abundance of blue swimmer crabs within part of the range of this species will depend on knowledge of whether or not the crabs in that region constitute a single stock or are part of a larger and more widely-distributed stock. In this context, it is highly relevant that the work of Bryars & Adams (1997) showed that, in spite of the high vagility of blue swimmer crabs, the assemblages of this species in relatively nearby localities can be genetically different and thus constitute different stocks. It should also be recognised that, as the fishery for blue swimmer crabs increases, the mortality produced by repeated captures and releases of undersized crabs could place pressure on those stocks that are being heavily fished.
2. There is a need to identify the different stocks of blue swimmer crabs that exist within a region in order to facilitate adaptive management (and opportunities for research) of separate populations that are exposed to (or experience) different levels of fishing mortality.
3. Any modelling of the blue swimmer crab fishery in a region is dependent on knowing whether the assemblages in that region constitute one or more stocks.
4. Fisheries managers need to know the extent to which the biological characteristics such as growth rates and fecundity, vary amongst stocks. This can be explored in Western Australia because biological data are continuing to be accumulated for different assemblages of blue swimmer crabs in this state under the auspices of past and current FRDC grants (FRDC Project Nos 95/042 and 97/137).
As well as responding to the immediate need for stock identification of blue swimmer crabs, the proposed project will generate detailed information on the population genetic structure of Portunus pelagicus over virtually its entire range in Australia. The resultant information will help to identify the importance of various factors, such as climate, current flow and physical isolation, in determining the stock structure of this species. In turn, this information will be useful should genetic management of this species become a priority, e.g. for conserving genetic diversity within stocks and for identifying stocks possessing desired performance traits.
Literature Cited
Bryars, S. & Adams, M. (1997) Population structure of the blue swimmer crab, Portunus pelagicus, in South Australia. In: Kumar, M. S. (ed.) Proceedings of the First National Workshop on Blue Swimmer Crab Portunus pelagicus. SARDI Reseach Report, Series Number 16, SA.
OConnell, M. & Wright, J. M. (1997) Microsatellite DNA in fishes. Reviews in Fish Biology and Fisheries, 7, 331 - 363.
Smith, P. J., Benson, P. G. & McVeagh, S. M. (1997) A comparison of three genetic methods used for stock discrimination of orange roughy, Hoplostethus atlanticus - allozymes, mitocondrial DNA, and random amplified polymorphic DNA. Fishery Bulletin, 95, 800-811.
Wright, J. M. & Bentzen, P. (1995) Microsatellites: genetic markers for the future. In: Carvhalo, G. C. & Pitcher, T. J. (eds.) Molecular Genetics in Fisheries. Chapman & Hall, London.
Final report
Collection of biological data required for management of the blue swimmer crab fishery in the central and lower west coasts of Australia
There is a critical need to develop a management policy for the blue swimmer crab fishery in Western Australia, that is based on sound biological data collected for this species in this state. Since the environments in which blue swimmer crabs are caught in Western Australia are unique, it is essential that detailed biological data of this species are collected specifically for these waters. The type of biological data that are required include information on the habitat requirements, size and age composition, growth and reproductive biology of this crustacean species. Reliable data on some of these aspects (size and age composition and reproductive biology) are essentially confined to those obtained for the Peel Harvey Estuary and to those derived from catches obtained in Cockburn Sound, using a trawl net with a large mesh (Potter et al., 1983; Penn, 1977; FRDC project 95/042). From a comparison of data in these latter studies, it would appear that crabs grow to a larger size or live longer in marine waters than in estuaries. There is thus an urgent need to obtain more precise information on the biology of blue swimmer crabs in the different habitats in the marine habitats in south-western Australia.
There are no biological data for blue swimmer crabs in Shark Bay, where the fishery is developing and has great potential. Shark Bay is located at a far more northern latitude than the Peel-Harvey Estuary and Cockburn Sound, and is characterised by far warmer water temperatures. Furthermore, there are essentially no estuaries near Shark Bay, which means that this type of area which is often used as a nursery ground is not available to this portunid in the region of Shark Bay. The presence of far warmer temperatures in Shark Bay, which will presumably influence the activity, feeding, growth and reproductive biology of this species (see e.g. Hill, 1980; Sukumaran & Neelakantan, 1996), together with the type of environment found in that region, mean that it would be very dangerous to extrapolate from the results of studies further south in temperate Western Australia, or indeed from elsewhere in Australia.
It should be noted that the biological data produced by this proposal will complement a separate study of the dynamics of the fishery (both commercial and recreational) and exploitation of the series of stocks which contribute to the catch of blue swimmer crabs in Western Australia. This project proposal by the Fisheries Department Research Division, will be submitted to the FRDC in December 1997 for the 1998/99 round of grant proposals.
References
Hill, B.J., 1980. Effects of temperature on feeding and activity in the crab Scylla serrata. Marine Biology 59: 189-192.
Penn, J.W., 1977. Trawl caught fish and crustaceans from Cockburn Sound. Rep. Dep. Fish. Wildl. West. Aust. 20: 1 24
Potter, I.C., P.J. Chrystal & N.R. Loneragan, 1983. The biology of the blue manna crab
Portunus pelagicus in an Australian estuary. Mar. Biol. 78: 75 85.
Sukumaran, K. K. & B. Neelakantan, 1996. Relative growth and sexual maturity in the marine crabs, Portunus (Portunus) sanguinolentus (Herbst) and Portunus (Portunus) pelagicus (Linnaeus) along the southwest coast of India. Indian J. Fish. 43: 215-223.