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speculate on the rates <strong>of</strong> recolonisation following a large-scale disturbance<br />

in the deep sea. This phenomenon might be studied by placing trays <strong>of</strong><br />

azoic sediment (sediment without animals) on the seafloor, thereby<br />

mimicking the effect <strong>of</strong> a large-scale disturbance, <strong>and</strong> then examining the<br />

recolonisation rate over time. Data from such an experiment, using a tray<br />

0.5 cm on a side, showed a slow recovery to background community<br />

conditions (abundance <strong>of</strong> animals in the surrounding sediment). The <strong>data</strong>,<br />

applying to macr<strong>of</strong>auna, were from all around the deep sea, including<br />

depths <strong>of</strong> 1000-2000 m, in areas that had higher energy flux <strong>and</strong><br />

presumably a higher recolonisation rate than the CCFZ. Even in such<br />

productive environments, it took about eight years for the macr<strong>of</strong>auna to<br />

recolonise. The point was not that such a rate should be applicable to a<br />

mining disturbance but rather that recolonisation rates in the deep sea<br />

were slow following an intense disturbance. The same trays in shallow<br />

water might show a recovery to background conditions in a matter <strong>of</strong> weeks<br />

to a few months. Whether or not mei<strong>of</strong>auna showed the same response as<br />

macr<strong>of</strong>auna, the fact remained that if a deep-sea community were severely<br />

disturbed by removing a high percentage <strong>of</strong> the fauna over a large area,<br />

recovery times would be lengthy.<br />

It would be important to factor that conclusion into any design <strong>of</strong><br />

impact experiments. Even though the DISCOL (Disturbance Recolonization)<br />

<strong>and</strong> JET (Japan Deep-Sea Impact Experiment) projects <strong>and</strong> others showed<br />

that the intensity <strong>of</strong> disturbance in terms <strong>of</strong> generated plume was moderate<br />

compared to what could be expected from mining, recovery times were long.<br />

Differences in communities could be expected eight years after even the<br />

moderate level <strong>of</strong> disturbance produced by DISCOL.<br />

Turning next to the high species diversity in the CCFZ, Smith cited<br />

<strong>data</strong> on polychaete worms – a major component <strong>of</strong> macr<strong>of</strong>auna – showing<br />

that a collection <strong>of</strong> 163 individuals had yielded anywhere from about 47 to<br />

about 82 different species. Thus, on a local scale, diversity was high<br />

compared to many other ecosystems. Implied in that species diversity was<br />

a lot <strong>of</strong> genetic diversity. Another aspect <strong>of</strong> diversity that was much more<br />

controversial <strong>and</strong> difficult to estimate was how many species inhabited a<br />

given region, at each <strong>of</strong> the collection sites. A post-doctorate scholar <strong>of</strong><br />

Smith’s, Adrian Glover, using controversial techniques, had estimated the<br />

number <strong>of</strong> polychaete species in Area A <strong>of</strong> DOMES (Deep Ocean Mining<br />

Environmental Study) at between 200 <strong>and</strong> 500. Thus, there might be<br />

thous<strong>and</strong>s <strong>of</strong> macr<strong>of</strong>aunal species in that single area, although nobody had<br />

a good sense <strong>of</strong> how many species occurred at any <strong>of</strong> the sites studied in<br />

INTERNATIONAL SEABED AUTHORITY 72

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