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General discussion 161<br />

such integration of behavioural ecology and physical oceanography in<br />

models of larval fish dispersal 80 , or of fish in general 234 , through the<br />

use of optimal control in particular. Indeed, this approach allows to<br />

model larval behaviour as it should be: a dynamic response to the environment.<br />

Behaviour emerges from the interaction of individuals with<br />

their environment, rather than being determined a priori. Its fineness<br />

is therefore only bounded by the complexity of the description of said<br />

environment. This ensures broad application and great flexibility of<br />

such models, as knowledge of the pelagic ecosystem progresses. We<br />

shall, however, discuss the hypotheses of these models in more details.<br />

The first justification for the use of optimisation models forms the<br />

basis of the theory of optimal behaviour. As stated in the Introduction<br />

(section I.4.2, page 17) and earlier in this chapter (page 117): as soon<br />

as a behaviour is heritable, occurs in an environment stable at the<br />

generation level, is variable, and its variations result in differential<br />

fitness, it is under selection. And natural selection will favour those<br />

forms that provide greater fitness 52,54 . All four conditions are satisfied<br />

during the early life history of fishes. During this pre-reproductive<br />

phase, fitness can be reduced to survival, both during and immediately<br />

after the larval phase. This is the justification for optimisation criteria<br />

such as maximising survival along successful trajectories (section 6.3), or<br />

minimising energy expenditure (because energy participates to growth<br />

and growth in turn affects survival 48,50,170,237,238 – section 6.4). While<br />

most larvae do not always respond optimally to their environment, the<br />

optimal behaviour theory states that they will tend to. Furthermore,<br />

this model should not be viewed as a description of the behaviour<br />

of each and every larva during its pelagic stage. Instead it aims at<br />

evaluating an upper bound to the influence of larval behaviour, in a<br />

context in which modellers have been looking at the lower bound most<br />

of the time (either passive particles, vertical migration only, or very<br />

simplified rules of behaviour 84,86,87,143 ). Moreover, this upper bound<br />

is made quite conservative regarding the behavioural abilities of fish<br />

larvae (swimming, energy reserves) by the choice of mean parameters for<br />

swimming speed and high energetic requirements. Due to the scarcity<br />

of information available throughout the larval phase, this safe approach<br />

is necessary but behaviour by fish larvae may have an even greater<br />

impact.<br />

Even if natural selection tends to optimise behaviours, it selects within<br />

the limits of what is energetically, ontogenetically, and mechanically<br />

possible. In this modelling framework, our theoretical larvae “know”<br />

their environment and all its future states, in a probabilistic sense<br />

(e.g. they “know” the distribution of the predation probability, not its<br />

realisation). Do larvae have the sensory abilities to detect predators,<br />

plankton, and direction of currents on a large spatial scale, and to<br />

predict their evolution in time? Probably not. But this is not what our<br />

modelling hypothesis implies. Consider the downward movement at the<br />

tip of the cape in Figure 6.17 for example. Larvae in the field probably<br />

Natural selection tends<br />

to optimise behaviours<br />

Optimal control<br />

reasons on the distal<br />

causes of behaviour

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