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standardization of environmental data and information - International ...

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underst<strong>and</strong>ing <strong>of</strong> the temporal variation both before <strong>and</strong> after. With this<br />

improved temporal resolution, if significant interactions were found, the<br />

interaction between before <strong>and</strong> after with respect to the control <strong>and</strong> impacted<br />

areas should again be significant; the differences would not reflect just r<strong>and</strong>om<br />

noise, which might have been the case if there had been only one <strong>data</strong> point<br />

before <strong>and</strong> one after. In this case, sustained changes could be recognised but<br />

it would still be impossible to attribute them directly to an anthropogenic effect<br />

because they might have come about through some other process that had<br />

nothing to do with the anthropogenic influences. Moreover, this approach was<br />

insensitive to pulse-type events, which were typical <strong>of</strong> the kind <strong>of</strong> perturbation<br />

expected. A pulse-type event involved a change followed by a slow return to<br />

the level <strong>of</strong> the ambient community. However, this kind <strong>of</strong> statistical approach<br />

would not easily recognise the interaction between before <strong>and</strong> after.<br />

Moreover, even a noise event could influence a finding <strong>of</strong> significant<br />

interaction.<br />

Another approach, proposed by Tony Underwood in a series <strong>of</strong> papers<br />

from 1991 to 1997 <strong>and</strong> recently summarised in his book on experimental<br />

ecology 14 , called for using multiple controls to deal with this problem. While<br />

the number <strong>of</strong> impacted sites could not be increased, the number <strong>of</strong> control<br />

sites could be exp<strong>and</strong>ed. He suggested setting up an asymmetrical analysis <strong>of</strong><br />

variance (ANOVA) with a series <strong>of</strong> control sites instead <strong>of</strong> just one. Again, a<br />

series <strong>of</strong> samples would be taken before <strong>and</strong> after, replicated at each station.<br />

The idea would be to look for an interaction effect, which would appear as a<br />

greater change in impacted sites than the average change in the controls. In<br />

statistical terms, an analysis <strong>of</strong> variance table would show how to identify the<br />

impact. The response <strong>of</strong> the impact locations to the anthropogenic influence<br />

would be different from the response <strong>of</strong> the control sites, in a way that could<br />

be separated from the effects <strong>of</strong> a natural event. The earlier design, with only<br />

one sample before <strong>and</strong> one sample after, was no good because it could not<br />

detect whether a spurious event had brought about the differences. Such an<br />

event could be spatially located to make it look as if there had been an impact<br />

or to remove the effect <strong>of</strong> an impact. The advantages <strong>of</strong> the new design were<br />

that it had spatial replication, at least among the controls; it had temporal<br />

replication with respect to both the controls <strong>and</strong> the impacted sites, <strong>and</strong> it<br />

allowed the impact to be detected rather unequivocally.<br />

Sampling design for impact assessment<br />

Etter then <strong>of</strong>fered his calculation <strong>of</strong> how such a sampling strategy could<br />

be implemented in a claim area. He recommended that at least two control<br />

sites be compared to one impacted site. The impacted site, which might be in<br />

441 INTERNATIONAL SEABED AUTHORITY

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