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standardization of environmental data and information - International ...

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Modelling <strong>and</strong> testing<br />

Wiedicke described calculations <strong>of</strong> mining impacts that might result<br />

from the use <strong>of</strong> a self-propelled mining <strong>and</strong> collector system about three<br />

metres high <strong>and</strong> six metres wide, moving at the speed <strong>of</strong> one metre per<br />

second <strong>and</strong> employing water jets to dislodge manganese nodules from the<br />

sediment surface. Using <strong>data</strong> gathered in the Peru Basin concerning the<br />

thickness <strong>of</strong> the top layer <strong>and</strong> <strong>information</strong> from other groups that not all <strong>of</strong><br />

the fine sediment would be redistributed <strong>and</strong> resuspended, one group in<br />

Berlin 22 had calculated that a maximum <strong>of</strong> only 20 percent <strong>of</strong> the sediment<br />

would be resuspended; most would quickly be remoulded into chunks <strong>of</strong><br />

sediment deposited behind the miner. This was regarded as a first<br />

approach that demonstrated the great need for additional parameters<br />

before the numbers could be taken seriously.<br />

Another group had calculated near-bottom sediment transport<br />

assuming sediment discharge <strong>of</strong> 10 kilograms/second, between 1 <strong>and</strong> 6<br />

days duration, <strong>and</strong> bottom-current velocity less than 10 cm/s. They had<br />

come up with a plume-residence time in the order <strong>of</strong> 1.5 to 6 days, a<br />

maximum distance <strong>of</strong> 15 km from the track before background<br />

concentration was reached <strong>and</strong> sediment coverage <strong>of</strong> about 0.5 mm in the<br />

1-2 km zone alongside the track. For continuous discharge, they had<br />

modelled sediment coverage as thick as 30 mm close to the track <strong>of</strong> the<br />

miner. They had not calculated flocculation effects. According to this<br />

model, the plume would have a predominantly local impact. These<br />

calculations concerned the bottom plume produced by the miner, not the<br />

tailings from above.<br />

Still another group had looked at the long-term propagation <strong>of</strong><br />

tailings discharged from a processing ship at the surface. They had used a<br />

well-established geostrophic ocean model that was fairly evolved for this<br />

purpose, although it did not take account <strong>of</strong> tidal movement. A bottomcurrent<br />

velocity <strong>of</strong> between three <strong>and</strong> five centimetres per second was<br />

assumed. The model had utilised two different grain-size distribution<br />

patterns: one as defined in laboratory tests <strong>and</strong> the other resulting from<br />

practical experiments in which the material was not completely dispersed in<br />

the water column. The differences in result were striking. Under the worst<br />

case scenario, resettlement <strong>of</strong> 90% percent <strong>of</strong> the tailings would take three<br />

to ten years, depending on release depth: three years at 3000 m below the<br />

surface <strong>and</strong> ten years at 500 m below. Resettlement <strong>of</strong> 95% would take 5<br />

to 14 years. Transport under El Niño conditions would be predominantly<br />

eastward, with deposition on the coast; under La Niña conditions, the<br />

162 INTERNATIONAL SEABED AUTHORITY

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