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standardization of environmental data and information - International ...

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on the other h<strong>and</strong> it turned out that major areas <strong>of</strong> the CCFZ experienced<br />

resedimentation events on a more routine basis, entombment <strong>and</strong> burial<br />

might not be such a big issue. A third major impact from nodule mining, <strong>of</strong><br />

less importance than the others, was the physical removal by the mining<br />

device <strong>of</strong> the nodules, surface sediments <strong>and</strong> animals. The community in<br />

the tracks -- the areas directly mined by the mining head -- would be<br />

severely impacted: macr<strong>of</strong>auna would be wiped out, while some <strong>of</strong> the<br />

mei<strong>of</strong>auna might go through the mining head <strong>and</strong> survive, but in general the<br />

zone mined would be heavily devastated.<br />

What critical <strong>information</strong> was needed to predict mining impacts on<br />

both the sediment <strong>and</strong> the nodule biota? One major open question was the<br />

dose-response function for the benthic community given a single deposition<br />

event. How much sediment redeposition was required to cause a particular<br />

degree <strong>of</strong> impact, as measured in percentage <strong>of</strong> mortality? The doseresponse<br />

function was important for extrapolating from small to large<br />

disturbances <strong>and</strong> for predicting the effect <strong>of</strong> a plume dispersed at the<br />

seafloor. Another major unknown was the effects <strong>of</strong> chronic disturbance.<br />

How frequently must modest deposition events -- <strong>of</strong> less than 1 mm, for<br />

example -- occur for their effects to become chronic, in other words nonindependent?<br />

A one-time deposit <strong>of</strong> 1 mm <strong>of</strong> sediment might have a<br />

modest effect on the community, but with repeated monthly deposits <strong>of</strong> 1<br />

mm at a given site, the effects might become non-independent, producing<br />

much more mortality. The nature <strong>of</strong> chronic effects was important in<br />

knowing how to manage mining: whether it should be limited to one area for<br />

a while <strong>and</strong> then be moved 10 or 100 km away in order to minimize<br />

<strong>environmental</strong> impacts. A third major gap in knowledge concerned the time<br />

scales <strong>of</strong> community recovery following various intensities <strong>of</strong> disturbance.<br />

Although there had been some clever mining impact studies, it was still not<br />

known what the recovery times might be from a major mining-like<br />

disturbance in the CCFZ. Some things were known – for example, if<br />

nodules were removed, it would take millions <strong>of</strong> years before they grew<br />

back, so that the nodule fauna there would require millions <strong>of</strong> years to<br />

recover, whereas the sediment biota would recover over much shorter<br />

periods.<br />

Smith cited other major open issues: What were the typical<br />

latitudinal <strong>and</strong> longitudinal ranges <strong>of</strong> benthic species in the CCFZ <strong>and</strong> what<br />

were their rates <strong>and</strong> spatial scales <strong>of</strong> gene flow? In practical terms, these<br />

questions translated to how large an area could be devastated by mining<br />

without causing species extinctions. In addition, what were the natural<br />

patterns <strong>and</strong> scales <strong>of</strong> benthic community variability in space <strong>and</strong> time?<br />

INTERNATIONAL SEABED AUTHORITY 78

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