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Growth model of the reared sea urchin Paracentrotus ... - SciViews

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to as roe) as ei<strong>the</strong>r a fine and delicate <strong>sea</strong>food or as absolutely inedible.<br />

However, its economic value is well established given <strong>the</strong> price consumers<br />

are willing to pay. The wholesale price <strong>of</strong> live <strong>sea</strong> <strong>urchin</strong>s in France ranges<br />

from 30 to 120 FF/kg (price range in <strong>the</strong> 1990s at Rungis, Paris), and fresh<br />

roe in Japan from 6,000 to 14,000 ¥/kg (price in Japan in <strong>the</strong> 1990s, see<br />

Hagen 1996a). Both market prices are roughly equivalent in terms <strong>of</strong> fresh<br />

roe, making <strong>sea</strong> <strong>urchin</strong> roe one <strong>of</strong> <strong>the</strong> most valuable <strong>sea</strong>foods in <strong>the</strong> world.<br />

In both markets, <strong>the</strong> lowest prices are those <strong>of</strong> imported <strong>sea</strong> <strong>urchin</strong>s, which<br />

are considered to be <strong>of</strong> poorer quality.<br />

The most important market, Japan, imports approximately five<br />

thousand tons <strong>of</strong> <strong>sea</strong> <strong>urchin</strong> gonads per year, <strong>the</strong> equivalent <strong>of</strong> 40 to 50<br />

thousand tons <strong>of</strong> live <strong>sea</strong> <strong>urchin</strong>s (Hagen, 1996a). According to <strong>the</strong> same<br />

author, <strong>the</strong> Japanese consumes approximately 60,000 tons <strong>of</strong> whole <strong>sea</strong><br />

<strong>urchin</strong>s per year. The second largest consumer is France, with an annual<br />

consumption <strong>of</strong> approximately 1,000 tons <strong>of</strong> whole <strong>sea</strong> <strong>urchin</strong>s (Le Gall,<br />

1990).<br />

Increasing demand for <strong>sea</strong> <strong>urchin</strong> roe and a steady rise in price have led<br />

to worldwide intensification <strong>of</strong> <strong>sea</strong> <strong>urchin</strong> fisheries (Conand and Sloan,<br />

1989; Le Gall, 1990; Saito, 1992) which has now (1998) probably reached<br />

its maximum. This production cannot be sustained at current levels<br />

because <strong>the</strong> declining productivity <strong>of</strong> overexploited existing stocks can no<br />

longer be compensated by harvest <strong>of</strong> new stocks, as was possible over <strong>the</strong><br />

last three decades (most exploitable natural populations have already been<br />

fished today). In Japan, this decline occurred despite <strong>the</strong> development and<br />

implementation <strong>of</strong> extensive domestic fishery enhancement techniques<br />

which include <strong>the</strong> annual release <strong>of</strong> 60 million juvenile <strong>sea</strong> <strong>urchin</strong>s into <strong>the</strong><br />

wild (Saito, 1992; Hagen, 1996a). Consequently, <strong>the</strong> worldwide supply <strong>of</strong><br />

high quality <strong>sea</strong> <strong>urchin</strong> roe will be unable to meet market demand unless<br />

commercial <strong>sea</strong> <strong>urchin</strong> aquaculture develops to partially replace <strong>the</strong> steady<br />

decrease in natural captures.<br />

Part I: Set up <strong>of</strong> an experimental rearing procedure for echinoids<br />

68

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