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standardization of environmental data and information - International ...

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e located, there was a variation in sediment types <strong>and</strong> hence in physicochemical<br />

conditions <strong>and</strong> biological species, <strong>and</strong> probably also in biomass,<br />

diversity <strong>and</strong> other factors. Thus, India <strong>and</strong> all other contractors would need<br />

detailed baseline <strong>data</strong> on the entire area they had claimed; <strong>environmental</strong><br />

<strong>information</strong> from the test <strong>and</strong> reference sites alone were not enough to<br />

represent the entire mining area.<br />

In mining an average <strong>of</strong> 10 kilograms <strong>of</strong> nodules per square metre,<br />

an area <strong>of</strong> about 300 km²/yr would be disturbed. Such an area was not<br />

large compared to the rest <strong>of</strong> the ocean, amounting to 0.4% <strong>of</strong> the 75,000-<br />

km² claim area. Even if the affected area were ten times larger, it would<br />

still be much smaller than the entire ocean area. Rather than devising a<br />

complete list <strong>of</strong> <strong>environmental</strong> <strong>data</strong> to be collected, the Authority should<br />

select critical parameters that had to be monitored, given the small size <strong>of</strong><br />

the mining areas <strong>and</strong> zones <strong>of</strong> influence.<br />

He then listed what the Authority was expected to do: develop<br />

guidelines, which it had already been doing; prescribe st<strong>and</strong>ard protocols,<br />

which it was in the process <strong>of</strong> doing; eventually specify acceptable limits for<br />

impact on various parameters, which the contractors would like to know<br />

before or while developing their mining systems; <strong>and</strong> regulate the<br />

monitoring <strong>of</strong> impacts.<br />

The parameters should be placed into different categories such as<br />

critical, important or routine (less important). It should be made clear which<br />

parameters were most crucial for baseline <strong>data</strong> <strong>and</strong> for impact assessment.<br />

In addition, at some time in the future indicator parameters had to be<br />

identified, to serve as a good reference <strong>of</strong> what the impact would do <strong>and</strong><br />

what should be looked at. Protocols should be defined for <strong>data</strong> collection,<br />

sampling, subsampling, analysis <strong>and</strong> storage. Acceptable limits <strong>of</strong> impact<br />

should be defined if possible, <strong>and</strong> the contents <strong>of</strong> <strong>environmental</strong><br />

statements <strong>and</strong> the format for <strong>data</strong> archival should be specified. Protocols<br />

had already been suggested for such topics as the study <strong>of</strong> marine benthos,<br />

effects <strong>of</strong> deep-ocean mining, sediment dispersion <strong>and</strong> other impacts.<br />

Manuals <strong>and</strong> guides prepared by the Intergovernmental Oceanographic<br />

Commission (IOC) could also form the basis for preparing protocols.<br />

Finally, if the Workshop could not complete this massive job, he<br />

extended an <strong>of</strong>fer to host a further meeting at NIO in Goa the following year<br />

to discuss <strong>and</strong> recommend st<strong>and</strong>ard protocols for <strong>environmental</strong> <strong>data</strong> <strong>and</strong><br />

<strong>information</strong>.<br />

INTERNATIONAL SEABED AUTHORITY 497

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