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standardization of environmental data and information - International ...

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ecological comparisons. Several other general recommendations are<br />

possible:<br />

i. An <strong>environmental</strong> baseline should be established in the testmining<br />

area for at least two years before the tests. This will<br />

allow evaluation <strong>of</strong> pre-disturbance spatial <strong>and</strong> temporal<br />

variability.<br />

ii. The monitoring <strong>of</strong> test mining should include deployment <strong>of</strong><br />

current meters, transmissometers <strong>and</strong> sediment traps to<br />

evaluate the size <strong>and</strong> behaviour over time <strong>of</strong> the sediment<br />

plume both within the benthic boundary layer <strong>and</strong> at the level <strong>of</strong><br />

tailings discharge.<br />

iii. Resedimentation thicknesses must be measured using multiple<br />

techniques <strong>and</strong> mapped to allow evaluation <strong>of</strong> dose-response<br />

patterns <strong>of</strong> various components <strong>of</strong> the benthic biota. The<br />

frequency <strong>and</strong> intensity <strong>of</strong> individual deposition events should<br />

also be evaluated.<br />

iv. The sampling design for biological communities should include<br />

(a) sample collection from at least five points along the<br />

redeposition gradient <strong>and</strong> (b) sampling in at least two control<br />

(i.e., unimpacted) areas for the duration <strong>of</strong> the impact study.<br />

v. Seafloor communities along the deposition gradient, as well as<br />

in control areas, should be sampled at least at the following<br />

approximate intervals after disturbance:

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