Tasks

Themes • Task 1 2 3 4 5 6 7 8 9

Themes


Strategically, this European Research Training Network will maintain and extend the leading position of European research in the application of evolutionary theory to exploited ecosystems: so far, European researchers have been at the forefront of bringing this topic to the awareness of the scientific community and of devising first operational tools for tackling the relevant scientific and managerial problems. The network’s overall objective can be broken down into research on three cross-cutting themes:

  • Theme 1. Systematic empirical evaluation of the extent of fisheries-induced adaptive changes in the European seas, forming the basis for assessing the need and acuteness of managerial interventions.
  • Theme 2. Development of dynamical models and statistical tools required for detecting and quantifying fisheries-induced adaptations in the wild, as well as for evaluating management strategies devised for coping with adaptive change.
  • Theme 3. Design of innovative and practically valuable management tools, including the evaluation of suitable reference points facilitating the evolutionarily sustainable utilization of living marine resources.

These cross-cutting themes and their interactions are illustrated in the figure at the bottom of page 2. The work to be conducted within this network is organised along nine mutually illuminating research tasks, each of which includes salient elements of the three central themes mentioned above. The first five of these research tasks are focused on investigating fisheries-induced adaptive changes in specific stocks:

 

Tasks

 

Task 1: Atlantic cod in Iceland

Cod is one of the main pillars supporting Icelandic fisheries, both at present and historically. The age at 50% maturity for Icelandic cod has declined over the last few decades, but it is not known whether these changes can to some extent be attributed to fisheries-induced genetic changes. Furthermore, the stock offers interesting possibilities to investigate fisheries-induced adaptation in a stock that has a complex population structure and has been subject to spatially varying exploitation pressure: historically, fishing pressure has greatly varied over large geographical areas as well as between adjacent spawning grounds within the main spawning area along the south coast. The overarching objective here is to document and understand the changes that have occurred in the maturation and growth of Icelandic cod during the second half of the 20th century. Large amount of data on size, age, and maturity of cod sampled throughout the last century, as well as data from fishing vessel log-books and commercial catch records exist. Analyses will be conducted at different geographical scales. The delineation of the areas will be guided by information on subunits as well as knowledge on areas with contrasting exploitation levels. The main question to be addressed include the following:

  • Description of changes in growth and maturity in various stock components over long time spans.
  • Analysis of reaction norms for age and size at maturation to disentangle phenotypically plastic and potentially genetic changes in maturation in various stock components.
  • Relating the results on Icelandic cod to fisheries-induced adaptive changes in other cod stocks on both sides of the Atlantic.
  • Management implications of fisheries-induced selection of a geographically heterogeneous fish stock.
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Task 2: Arctic charr in Iceland

Arctic charr is an exceptionally polymorphic fish, and one of the very few species inhabiting freshwaters in Iceland. The evolution of morphs is known to result from adaptations to local ecological conditions, which may lead to population segregation and even to the formation of new species. However, the potential effects of exploitation (mainly gillnetting targeting the largest morphs) and management measures (e.g., efforts aimed at improving the growth rates of individuals by ‘thinning’ the population) on immediate and longer-term genetic and phenotypic diversity have hardly been studied. An important novel aspect and likely breakthrough that this study aims at is to comprehensively test whether exploitation of a rapidly diverging species of fish can have significant effects on evolutionary patterns. A multidisciplinary approach using available databases for ecological, genetic, and phenotypic diversity of a number of charr populations in Iceland will be applied. Between 1992 and 1998, a comprehensive survey was conducted on the ecology of Icelandic lakes resulting in vast amounts of information that can be used in the current study. Otoliths have been collected from several populations. This will allow for age determination and for the establishment of individual growth trajectories. A special field effort will be invested on target populations by examining their ecological, phenotypic, and genetic structures. The objectives for this task can be outlined as follows:

  • Summarising available data on the potential effects of fishing from databases, papers, and reports.
  • Examining apparent short-term and longer-term effects of fishing on life-history patterns such as growth and maturation patterns using reaction norm methods.
  • Investigating the hypotheses that exploitation has affected evolution in arctic charr by (1) changing the ecological conditions potentially causing evolutionary divergence; (2) reducing or even eliminating particular morphs through overfishing; and (3) influencing levels of gene flow among morphs by, e.g., size-selective fishing affecting size-dependent mate choice.
  • Communicating all scientific findings effectively to both the scientific community and stakeholders.
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Task 3: Pacific oysters on the French Atlantic coast

Following the decline of the indigenous oyster in the 1960s, Pacific oysters from Japan were massively introduced to the French coastlines in order to sustain production. Nowadays Pacific oysters form the basis of oyster farming in France. This is an attractive case for studying exploitation-induced adaptations because of three particularities. First, exploitation is strongly size-selective: oysters are harvested once they reach market size. Second, oyster farming still relies on recruitment in the natural environment. Third, since farmed oysters represent 95% of the total oyster biomass, recruited juveniles are mostly produced by farmed stocks, such that selective exploitation can readily affect subsequent generations. Data on farmed oysters show a significant decrease in growth rate and a significant delay in spawning timing since the introduction. Three hypothesized causes for these changes are: (1) Phenotypically plastic response to reduced food abundance caused by a strong increase of oyster biomass; (2) Local adaptation of the species to its new environment; (3) Exploitation-induced evolution caused by the size-selective harvest. The main aim of this research task is to disentangle the three potential components of phenotypic changes by the mutually illuminating use of data analysis and modelling. In addition to potentially being the first demonstration of exploitation-induced evolution in mollusks, major advances towards realistic life-history theory by developing models including genetics, energy allocation, and ecological feedback are expected. Salient research actions for these purposes are:

  • Disentangling plastic and evolutionary components of changes in growth, timing and length of the reproduction period, and reproductive effort.
  • Developing theoretical models integrating genetics, energy allocation, and ecology for understanding life-history evolution in farmed oyster stocks and assessing the respective likelihoods of evolutionary local adaptation and exploitation-induced evolution.
  • Investigating potential management strategies to minimize evolutionary changes due to selective farming and maximize long-term sustainable yield.
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Task 4: Sole and plaice in the North Sea and the eastern English Channel

Substantial changes in growth, maturation, and reproductive investment have been documented in sole and plaice during the 20th century. Plaice became heavily exploited at the beginning of the 20th century, whereas sole only became heavily exploited in the early 1960s. In plaice, the changes in maturation and reproductive investment were shown to be partly due to fisheries-induced adaptive change. In sole, the changes have so far been interpreted to be related to density-dependent effects and an increase in food availability, but the possibility of fisheries-induced adaptations has not been rigorously considered. As growth, maturation, and reproductive investment are interdependent aspects of the energy allocation schedule, the scope for fisheries-induced evolution will depend on the covariance between these traits. In this project, the observed changes in growth, maturation and reproductive investment of sole will be analysed using the biological monitoring data collected monthly since 1958. The possibility for supporting tank experiments is being explored. A major step forward will be achieved by the analysis of the covariance between growth, maturation, and reproduction by estimating the growth history, the onset of sexual maturity, together with the reproductive investment of individual fish. The main components of this task are:

  • Determination of individual energy allocation schedules from changes in the proportion of the various allocation schedules in the population by sampling cohorts at successive ages.
  • Relating changes in allocation schedules to the demographic structure of the population and the demographic impact of the exploitation.
  • Comparisons between fisheries-induced adaptations in sole and plaice in relation to their species-specific characteristics.
  • Integration of flatfish results with the energy allocation and management tasks (Tasks 8 and 9).
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Task 5: Atlantic cod, Atlantic herring, and sprat in the baltic

The Baltic Sea ecosystem is dominated by three closely interacting fish species: cod, herring, and sprat, which also are the major targets of the commercial fisheries. This gives an exceptional opportunity to address the evolutionary effect of fishing in a multi-species context. The objectives will be approached by parallel statistical analyses of existing data (including reaction norm analyses) and the development of three-species models reflecting the biological interactions in the Baltic Sea. Important insights are expected to originate from clarifying (1) whether observed changes in the maturation of Baltic cod is a result of fisheries-induced adaptive changes, (2) whether there are significant maturation changes also in sprat and herring populations, and, if so, (3) whether these changes are fisheries-induced adaptive changes, and (4) how any adaptive changes in maturation relate to changes in relative abundance of the three interacting species. By combining empirical analyses of the biological information with development of general evolutionary models, reflecting the types of interactions among the three species, we will generate knowledge of both fisheries-induced adaptive changes in the Baltic sea community, and foster a general understanding of evolutionary effects of fishing on interacting species. Furthermore, exploring the development and variability of biological characteristics will improve the interpretation of fish assessment models in the Baltic. Anticipated major breakthroughs from the modelling are answers to (1) how mixed and single-species fishing affects adaptation in target and non-target species subject to multi-species interactions, (2) how fisheries-induced adaptive changes in multi-species communities depend on the strength and type of species-interactions, and (3) to what extent fisheries-induced adaptive changes may influence community dynamics. The major objectives of this task are thus threefold:

  • Describing changes in biological characteristics in cod, herring, and sprat.
  • Investigating and predicting potential fisheries-induced adaptive change in the Baltic Sea fish community through integrated empirical and theoretical analyses.
  • Understanding how fishing in general affects adaptation and resulting long-term population dynamics in closely interacting species.

The following three additional research tasks are designed to improve our conceptual or theoretical understanding of fisheries-induced adaptive change, to be developed in close contact with the previously described empirical studies:

 

Task 6: Eco-genetic models

Adequately dealing with fisheries-induced adaptive change requires a new generation of models be developed. These models have to do justice both to the ecological and the genetic intricacies involved in the dynamics of a particular stock. At the same time, these models must remain computationally tractable, be parameterised with routinely collected data, and accurately predict expected rates of evolutionary change. First steps in this direction have already been taken by merging age- and size-structured population models that capture a reasonable amount of ecological detail with modern dynamical models of quantitative genetics, resulting in models referred to as ‘eco-genetic’. A breakthrough is expected from the fact that, for a first time, quantitative medium-term predictions on fisheries-induced evolutionary change in exploited stocks will become available. Evidently, such models have much wider utility. The main questions to be addressed in this task include the following:

  • Comparisons of predictions to results obtained with traditional evolutionary models.
  • Applications to concrete empirical systems (in close interaction with other FishACE teams) in order to gain better understanding of the particular strengths and limitations of eco-genetic modelling.
  • Increasing computational efficiency of eco-genetic models.
  • Investigating strategies for incorporating data obtained with the help of genetic markers.
  • Evaluation of management strategies with explicit considerations of short- and long-term costs and benefits.

 

Task 7: Evolutionary responses of food webs to harvesting

All species are embedded in food webs. The harvesting of one species invariably changes the environment for the other species, since many of the latter experience the harvested species as a resource, predator, or competitor. Even though the ecological dimensions of this so-called ‘ecosystem embedding’ have received increasing attention over the past few years, the corresponding evolutionary dimensions remain virtually unexplored. The problem is that ecological interactions between species may result in completely unexpected evolutionary responses to exploitation. How much of the complexity of real food webs needs to be considered in order to properly understand and predict the evolutionary implications of fisheries therefore is an open question of critical importance. In order to address this question in a tractable and systematic manner, we have to scale up from the most basic models of interaction, involving only two species, to small food-web modules of three or four species, to eventually gain insight into the evolutionary response of larger assemblages of species. A major promise of this research is to better understand under which ecological conditions single-species predictions of evolutionary responses to harvesting are bound to be reliable. The main components of this task are:

  • Obtaining a full overview of evolutionary responses to harvesting in two-species models of all three fundamental types of ecological interaction (predation, competition, and mutualism).
  • Extending this understanding to food web modules involving mixed interactions of predatory and competitive type (resulting in cannibalism, omnivory, or intra-guild predation).
  • Investigation of evolutionary responses in food webs of larger size in dependence on the historical route and the biological mechanisms (immigration, speciation) through which the food web has been assembled.
  • Broadening these investigations to include implications of size-dependence in the rates of predation, harvesting, and competition.

 

Task 8: Evolutionary energy allocation models

The primary objective here is to investigate evolution of growth rates under size-selective harvesting. It is often taken for granted that fishing, by selectively removing large, fast-growing fish, results in evolution towards slower growth. Two caveats must be acknowledged. First, reduced growth may incur fitness costs in terms of reduced fecundity, and it may increase death rate due to natural predators. Second, growth rate may decrease as a secondary response to a change in energy allocation between growth and other needs, or directly, when intrinsic growth capacity is reduced. Understanding whether the benefits of reduced growth offset the costs, and whether direct or indirect reduction is more likely to happen, requires carefully calibrated models tailored to a specific fish stock. Energy allocation models, with their strong mechanistic underpinning, offer a powerful approach for addressing these questions. Links will also be built with other FishACE modelling tasks, as well as with the oyster and flatfish case studies (Tasks 3 and 4). The specific goals for this task are as follows:

  • Investigating the conditions under which size-selective fishing can result in genetic reductions in growth, compared to conditions under which that is not expected to happen.
  • Investigating the relative likelihoods of evolutionary responses in growth rate through direct and indirect evolutionary effects.
  • Understanding the consequences of fisheries-induced changes in growth rates on population dynamics and sustainable yield.
  • Studying the possibilities to influence fisheries-induced evolution of growth rate by management measures, including technical measures that directly change the size-selectivity of fishing gear.

The final task below is focused on the management implication of fisheries-induced adaptive change, merging the results and insights gained in all other eight tasks:

 

Task 9: Management of fisheries-induced adaptive changes

The principal aim for this task concerns the design of innovative and practically valuable management tools that take into account fisheries-induced adaptive changes, on top of the traditional ecological considerations. In order to guide the development of appropriate management tools, it is recognised that, as a first step, the objectives of management need to be as explicit and carefully articulated as possible. Once such management objectives have been identified, management tools to achieve specific objectives can be devised. Crucial goals include identifying metrics that can suggest when specific, evolutionarily enlightened management actions are called for, and identifying the most cost-effective actions. Model-assisted evaluations of various management tools are indispensable throughout this task. The major output from the task is expected to be new methodologies for advising on the sustainable management of fisheries. In essence, all other FishACE tasks will be linked to this task, and provide information on the scope and consequences of fisheries-induced selection on particular stocks. Predictions on future evolutionary trajectories, either under prevailing exploitation regimes or after managerial interventions, are generated with the help of models. New information arising from other tasks within the FishACE project will be synthesised, and as a next step, applied within the routine advisory process with which ICES is charged. The main questions to be addressed in the work on this task include the following:

  • Establishing objectives for managing fisheries-induced adaptive changes, including considerations from both utilitarian and ethical perspectives, and taking explicitly into account the trade-offs and compromises between short-term and long-term goals.
  • Evaluation of evolutionary vulnerability in light of exploitation patterns and species-specific characteristics.
  • Evaluating the utility of different management tools and options, including technical management measures like minimum mesh sizes and minimum landing sizes, in light of the inherent uncertainty of the information on which decisions have to be based.
  • Influence of evolutionary changes in growth, maturity, fecundity, and survival of offspring on a stock’s viability in general, and on the relationship between spawning stock biomass and recruitment in particular.
  • Formulation of management advice in the modern regime of the Precautionary Approach, e.g., through the specification of suitable reference points.

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Responsible for this page: Melanie Wenighofer
Last updated: 10 Mar 2006