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Fisheries in the Pacific

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The challenge of susta<strong>in</strong>ability for <strong>Pacific</strong> Island village fisheries, a historical perspective<br />

of Vanuatu’s mar<strong>in</strong>e resources carried out by <strong>the</strong> Australian Institute of Mar<strong>in</strong>e<br />

Science <strong>in</strong> 1988, a total of 469 species of fish were visually identified (Williams<br />

1990). Coral reefs form <strong>the</strong> ecosystem with <strong>the</strong> highest diversity of fauna but <strong>the</strong><br />

coral biotope is very restrictive for <strong>the</strong> populations liv<strong>in</strong>g <strong>in</strong> it. The habitat favourable<br />

to each species is quite small: one refers to microbiotopes, generally scattered from<br />

each o<strong>the</strong>r. The ensemble of <strong>the</strong>se microbiotopes form <strong>in</strong> <strong>the</strong> space a k<strong>in</strong>d of threedimensional<br />

mosaic where each element harbours a micropopulation composed of a<br />

small number of fish of <strong>the</strong> same species. This low <strong>in</strong>traspecific diversity is accompanied<br />

by strong specialisation, as much from <strong>the</strong> perspective of diet as habitat (Kulbicki<br />

1992). Due to <strong>the</strong>ir small size, <strong>the</strong>se micropopulations are sensitive to all <strong>in</strong>tensive<br />

exploitation on <strong>the</strong> part of fishers and <strong>the</strong>ir abundance per hectare is low. These two<br />

factors, comb<strong>in</strong>ed with <strong>the</strong> rich species diversity of <strong>the</strong> fish biomass, constitutes <strong>the</strong><br />

primary constra<strong>in</strong>ts on <strong>the</strong> fish<strong>in</strong>g activity; added to <strong>the</strong>m are seasonal variations <strong>in</strong><br />

fish abundance, which are particularly sharp <strong>in</strong> <strong>the</strong> case of small pelagic fish (Conand<br />

1987). These constra<strong>in</strong>ts are prohibitive for fishers; <strong>the</strong>y cannot circumvent <strong>the</strong>m and<br />

have no o<strong>the</strong>r choice than to <strong>in</strong>tegrate <strong>the</strong>m <strong>in</strong>to <strong>the</strong>ir capture strategies and<br />

techniques. One is faced here with <strong>the</strong> <strong>in</strong>variants <strong>in</strong>herent <strong>in</strong> <strong>the</strong> structure of coral<br />

habitats and <strong>in</strong> <strong>the</strong> ecology of fish that heavily impact <strong>the</strong> availability of fish on <strong>the</strong><br />

capture sites (fig. 3).<br />

Figure 3: The availability of fish on subsistence fish<strong>in</strong>g grounds,<br />

a process associat<strong>in</strong>g <strong>in</strong>variance and temporality<br />

The availability of fish on fish<strong>in</strong>g grounds is also sensitive to two parameters<br />

which evolve over time. These are <strong>the</strong> health of mar<strong>in</strong>e ecosystems and <strong>the</strong> density<br />

233

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