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side. Exploration contractors will be required to report annually in writing to<br />

ISA on the results <strong>of</strong> their monitoring programme, including submission <strong>of</strong><br />

monitoring <strong>data</strong> <strong>and</strong> related <strong>information</strong>. In addition to baseline monitoring,<br />

contractors will be required to generate an <strong>environmental</strong> impact<br />

assessment for all aspects <strong>of</strong> test mining <strong>and</strong> then to monitor the<br />

<strong>environmental</strong> impacts <strong>of</strong> any mining tests.<br />

1.2. Gaps in knowledge <strong>of</strong> deep-sea ecosystems<br />

Although a number <strong>of</strong> scientific <strong>environmental</strong> studies have been<br />

conducted in the claim areas in the North Pacific <strong>and</strong> Indian Oceans,<br />

numerous important ecological aspects <strong>of</strong> these abyssal habitats remain<br />

very poorly understood. Poorly understood characteristics include:<br />

i. Community structure, at the species level, <strong>of</strong> dominant faunal<br />

elements at the seafloor, in particular the macr<strong>of</strong>auna (animals<br />

less than 2 cm <strong>and</strong> >250 microns in smallest dimension) <strong>and</strong><br />

mei<strong>of</strong>auna (animals 42 µm in smallest<br />

dimension). Species-level structure is poorly known because <strong>of</strong><br />

the shortage <strong>of</strong> taxonomic experts to identify the deep-sea<br />

fauna <strong>and</strong> because most species collected in the nodule<br />

provinces are new to science (they have not been formally<br />

described in the scientific literature).<br />

ii. Geographical ranges <strong>of</strong> the dominant macr<strong>of</strong>aunal <strong>and</strong><br />

mei<strong>of</strong>aunal species likely to be impacted (<strong>and</strong> potentially<br />

exterminated) by nodule mining. Without knowledge <strong>of</strong> the<br />

ranges <strong>of</strong> dominant species living in the claim areas, it is<br />

impossible to realistically predict the likelihood <strong>of</strong> extinction<br />

from large-scale habitat disturbance such as that resulting from<br />

nodule mining.<br />

iii. Resistance <strong>and</strong> resilience (i.e., recovery times) <strong>of</strong> seafloor<br />

communities to nodule-mining disturbance. Although a number<br />

<strong>of</strong> simulated impact studies have been conducted 74 , they have<br />

not reproduced the full scale <strong>and</strong> intensity <strong>of</strong> actual mining<br />

disturbances, <strong>and</strong> have been forced to work with relatively low<br />

levels <strong>of</strong> sampling replication.<br />

53 INTERNATIONAL SEABED AUTHORITY

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