Photo by E Farestveit

To produce a plan for the conservation and management of genetic resources in European lobster fisheries taking into account natural population diversity, extant industry practices, previous and current enhancement activities, and the future potential for farming and or ranching

The degree of differentiation seen in the European lobster is compatible with all populations having been established from a common refuge after the end of the last Ice Age, i.e. within the past 15,000 years. There is no evidence of a separate Mediterranean refuge. The low level of genetic differentiation observed reflects the relatively short time since the populations were established post-glacially (<3,000 generations) and not a high level of gene flow. Overall the data suggest that the European lobster comprises a large number of discrete populations with very limited genetic exchange among them. Such an island population structure is not surprising given low movement after benthic settlement and several possible mechanisms that prevent larval dispersal. Within populations, genetic change (of essentially neutral alleles examined) has occurred to a greater or lesser extent as a result of genetic drift. However, with the exception of the examples noted above, most populations are sufficiently large that the rate of frequency change effected by drift is relatively low. Large in the genetic sense means effective population sizes more than several thousand (i.e. census population sizes >10,000) and does not imply large from the standpoint of exploitation. With the possible exception of the Aegean, there is no evidence for a metapopulation structure in any of the areas of high sampling density, although the existence of such a structure in other parts of the range, where only a few samples were obtained, cannot be excluded. The management importance of recognising an island population structure is that, if over-harvesting occurs, the stock will not be replenished by recruitment from elsewhere in a meaningful time period. Thus European lobster management should be based on local populations rather than on broader metapopulations as recently favoured by fisheries ecologists. Delimitation (i.e. what is the geographical extent) of a local stock is not straightforward and needs to be based on a combination of biological, hydrographical and genetic information.

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Although the overall level of genetic differentiation among European lobster populations is low this does not mean that important inter-population adaptive genetic differences are absent. Thus it is likely that lobsters living at the limits of environmental tolerance for the species (e.g. northern Norway, Morocco, Aegean) have adapted to some degree to local conditions as indicated by differences in life history characteristics. Experimental breeding studies indicate that significant fitness-related genetic differences occur even between populations some 25km apart. The aim of this study was to look at population structure and it is not possible to make conclusions about adaptive differences among populations from differences in the essentially neutral markers used. Even low levels of selection acting on an allele will result in changes several orders of magnitude faster than neutral allele changes by drift. Thus little or no detectable change may occur between two populations for microsatellites but they may have different alleles at loci involved in fitness traits. For example, no significant differences in microsatellite frequencies were found between a reference sample of adults collected in 1991 prior to enhancement at Kvitsøy and fertilised eggs, of both ranched and wild parents, collected in 2000. The fact that genetic change was not detected for microsatellites, does not mean that functional gene changes have not occurred due to ranching. Indeed the experimental comparison of survival of wild and hatchery juveniles indicates that such changes have taken place. In spite of the often-misleading information to the contrary, molecular markers are of limited value in identifying conservation units among allopatric postglacially-established populations since there is unlikely to be a correlation between neutral and adaptive gene evolution. The main use of such neutral markers is to identify reproductively isolated units, inbreeding or outbreeding, phylogeographical relationships, and, most important of all as far as microsatellites are concerned, parentage.

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Further detailed studies are required to determine the extent to which adaptive differences occur among populations. In general it is not yet possible to look directly at functional gene differences in natural populations. At present this can only be done by experimental comparison of different families and groups established under common environmental conditions from the embryo stage, and using microsatellite profiling (as developed in this project) for parentage identification. The European lobster is an ideal model species for studying local adaptation. It occurs in a wide range of environmental conditions and produces large numbers of offspring. Since it is relatively easy to transport living females with attached fertilised eggs it is possible to examine survival and other fitness traits of individuals from two populations under reciprocal environmental conditions. Such movement is at best extremely difficult for fish and many other marine organisms. It is also possible to carry out experiments with lobsters under relatively natural conditions making use of natural enclosures or lobster pounds as in this project.
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Until further experimental studies are undertaken, it is recommended that the precautionary principle be applied to movements of lobsters for enhancement purposes, with movements being confined to local areas. Certainly, northern Norway and the Aegean should be protected from introductions. Where enhancement is necessary due to low stock levels, local hatcheries should be established, providing juveniles based on local stock, rather than larger 'centralised' hatchery facilities. This use of local stocks is also preferred in order to reduce disease risks. However, the low level of gene flow suggests that lobster culture can be carried out in areas where native populations are absent without adverse genetic impact.
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Genetic tagging should be considered to measure the success of all enhancement (ranching) programmes as well as being applied to measure the success of V-notch female release programmes, and other management schemes of hitherto un-quantified benefit. If full life cycle culture of lobsters is undertaken there is considerable scope for selective breeding. The recent improvements in aquaculture techniques and the renewed interest in lobster enhancement and farming demonstrate a growing potential for this. In that context, microsatellite markers in parentage analysis for selective breeding of lobsters may represent one of the most important factors for future economical success.
Photo Provided by Dr. J Mercer V-notch on berried female
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