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standardization of environmental data and information - International ...

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each cruise, one multiple-corer sample was collected for the study <strong>of</strong><br />

mei<strong>of</strong>auna <strong>and</strong> three box-corer samples were gathered for investigating the<br />

abundance <strong>of</strong> macr<strong>of</strong>auna. Reference samples were collected 2 nautical<br />

miles up current from the DEA.<br />

This sampling design appeared to be appropriate at the beginning <strong>of</strong><br />

DISCOL, but initial species <strong>and</strong> abundance <strong>data</strong> demonstrated that the<br />

number <strong>of</strong> samples was too low. Additionally, throughout the study it was<br />

difficult to recognize disturbed samples when the degree <strong>of</strong> disturbance<br />

was not particularly heavy. Mounting cameras to the corers <strong>and</strong> imaging<br />

the seafloor just before bottom contact became a helpful method, but this<br />

was still a blind search for disturbed areas. Adding video control to the<br />

sampling systems during the last post-impact study allowed us to search<br />

<strong>and</strong> sample the disturbed areas successfully. Thus, the limitations<br />

introduced by the radial <strong>and</strong> non-continuous heavy disturbance created<br />

difficulties in unequivocal sampling <strong>of</strong> disturbed areas.<br />

The macr<strong>of</strong>auna was defined to be larger than 500 microns during<br />

the first cruise, but we realized that this would not be sufficient for<br />

evaluation <strong>of</strong> this faunal component. During later cruises, sieves with 250-<br />

µm meshes were employed, limiting overall <strong>data</strong> comparability. Such errors<br />

could have been avoided with a separate pre-impact cruise into this specific<br />

area.<br />

1.4. Sampling sequence<br />

During the preparation phase for DISCOL, no <strong>information</strong> or prior<br />

experience was available on which we could base a suitable time sequence<br />

for revisiting <strong>and</strong> resampling the DEA. It is known that processes in the<br />

deep sea are slow, while recolonisation in shallow waters may be a matter<br />

<strong>of</strong> months. Small-scale experiments with defaunated sediments in the deep<br />

sea 17 have demonstrated the existence <strong>of</strong> opportunistic species <strong>and</strong> their<br />

fast colonisation potential in those small (less than 1 m²) experimental<br />

sediment patches, but reestablishment <strong>of</strong> a community with natural<br />

successional changes appears to be a process extending over several<br />

years. Experimental <strong>and</strong> commercial large-scale disturbances will certainly<br />

last more than a decade.<br />

Early in the planning process, we decided to return to the DEA after<br />

several months, <strong>and</strong> again after several years. The sampling schedule<br />

achieved was determined not only by scientific considerations, but also by<br />

ship-time availability (table 1).<br />

INTERNATIONAL SEABED AUTHORITY 331

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