Dissertation - HQ
Dissertation - HQ
Dissertation - HQ
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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