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standardization of environmental data and information - International ...

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<strong>information</strong>. On the other h<strong>and</strong>, these <strong>data</strong> are probably less useful for<br />

<strong>environmental</strong> impact analysis than the <strong>data</strong> collected later using better<br />

technology <strong>and</strong> a higher appreciation for <strong>environmental</strong> values.<br />

It is not useful in this Workshop to focus on the relative worth <strong>of</strong><br />

contractor <strong>data</strong> already obtained. However, a major goal for this Workshop<br />

should be to provide the impetus for a comprehensive integration <strong>of</strong> such<br />

<strong>data</strong> into a useful basis for future impact analysis for all contractors.<br />

2.2. At-sea system testing<br />

The maximum at-sea nodule-recovery rate to date, 30 tons per hour,<br />

was achieved in March 1978 by the Ocean Management Inc. (OMI)<br />

consortium. During these system tests, OMI recovered a total <strong>of</strong> 900 metric<br />

tons. In the same year, using a different system, the Ocean Mining<br />

Associates consortium (OMA) recovered a total <strong>of</strong> 600 metric tons during an<br />

18-hour test 5 . The United States National Oceanic <strong>and</strong> Atmospheric<br />

Administration (NOAA) monitored these tests as the principal effort <strong>of</strong> the<br />

DOMES II programme. The <strong>information</strong> collected during these activities<br />

provided key inputs to the impact analysis presented by NOAA in its PEIS. In<br />

the current 15-year plans <strong>of</strong> work submitted to ISA by the active contractors,<br />

no at-sea test mining is scheduled.<br />

Commercial recovery rates are expected to be more than ten times<br />

the maximum rate achieved by OMI, i.e., more than 300 tons per hour. Two<br />

to five years <strong>of</strong> testing <strong>of</strong> progressively larger systems will probably be<br />

required before operation <strong>of</strong> full-scale prototype systems will be practical.<br />

During this time, important <strong>environmental</strong> impact analysis will have to be<br />

completed through monitoring <strong>of</strong> such tests. Potentially significant<br />

<strong>environmental</strong> impacts predicted through such monitoring could provide the<br />

basis for system modification to mitigate or avoid the impacts. Predictions<br />

<strong>of</strong> mining impacts will have to be based on these monitoring results,<br />

interpreted in the context <strong>of</strong> the baseline habitat characterisations<br />

established before <strong>and</strong> during mining tests.<br />

Perhaps the most critical issues related to phasing <strong>of</strong> the required<br />

habitat characterisation are those related to distinguishing the<br />

characterisation studies that must be completed well in advance <strong>of</strong> the<br />

mining tests from those that can best be carried out immediately before<br />

<strong>and</strong> during the testing. This critical item must be addressed at this<br />

Workshop. Establishing st<strong>and</strong>ards for studies that might not be necessary<br />

until mining-system tests are conducted many years from now is<br />

101 INTERNATIONAL SEABED AUTHORITY

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