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standardization of environmental data and information - International ...

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differential response <strong>of</strong> the community at the impact site may be due to<br />

natural cycles that vary spatially 3 . That is, any differences between the impact<br />

site before as compared to after the anthropogenic activities could not be<br />

interpreted as a consequence <strong>of</strong> these activities.<br />

Bernstein <strong>and</strong> Zalinski 4 <strong>and</strong> Stewart-Oaten et al. 5 suggested an<br />

improved sampling design referred to as BACI (Before-After-Control-Impact).<br />

They argued that replicate samples should be taken several times before the<br />

onset <strong>of</strong> anthropogenic activities <strong>and</strong> several times after, at both the impact<br />

<strong>and</strong> control sites. This would provide temporal replication <strong>and</strong> reduce the<br />

likelihood that any observed interaction was due to chance <strong>environmental</strong><br />

variation. However, this does not deal with the main problem – that the two<br />

sites can have different temporal patterns <strong>of</strong> variation that have nothing to do<br />

with anthropogenic activities.<br />

In a series <strong>of</strong> papers, Underwood 6 described sampling <strong>and</strong> analytical<br />

solutions to these design flaws in <strong>environmental</strong> impact studies. First, one<br />

should use multiple control sites. It is <strong>of</strong>ten impossible or impractical to have<br />

multiple impact sites, but there is no reason not to replicate control sites. The<br />

multiple control sites will provide insight into natural patterns <strong>of</strong> spatial <strong>and</strong><br />

temporal variation in the target communities. The basic idea is that an impact<br />

would cause a change in the response variable (e.g. population size) before<br />

compared to after the onset <strong>of</strong> anthropogenic activities that exceeded the<br />

average change in the controls over the same period. Second, each station<br />

should be sampled several times before the potential impact <strong>and</strong> several times<br />

after, providing temporal replication. Finally, an impact can be identified from<br />

a comparison <strong>of</strong> various interaction terms in an Asymmetrical ANOVA 7 .<br />

Basically, the interaction in time between the impacted <strong>and</strong> control sites<br />

should be different from the naturally occurring interactions in time among the<br />

control sites.<br />

3. Proposed Sampling Design<br />

Based on these studies, I describe a sampling programme with an<br />

appropriate design for statistically detecting an impact from polymetallic<br />

nodule mining operations in the deep sea. The design I propose represents a<br />

bare minimum sampling programme. Appropriate levels <strong>of</strong> replication will<br />

need to be determined from a power analysis 8 once the response variables<br />

have been chosen, levels <strong>of</strong> acceptable change are determined <strong>and</strong> some<br />

estimate <strong>of</strong> the natural variability has been made.<br />

INTERNATIONAL SEABED AUTHORITY 432

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