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mcbem-2014-01-submission-wwf-en

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These planning processes are long term, with implem<strong>en</strong>tation expected to take 10-20 years. As a result,<br />

they need to anticipate future research needs and to be adaptive, and at least consider noise thresholds<br />

in their Ecosystem Based Managem<strong>en</strong>t standards. A risk assessm<strong>en</strong>t framework, such as those discussed<br />

in workshop pres<strong>en</strong>tations, may be most appropriate.<br />

There are a number of ways to influ<strong>en</strong>ce underwater noise associated with shipping within the marine<br />

planning process:<br />

Marine plans could specify noise objectives and set cumulative noise caps regionally. Local<br />

communities should be <strong>en</strong>gaged to <strong>en</strong>sure grassroots support.<br />

Within a planning area, baseline underwater noise levels should be established using<br />

standardised approaches, with ongoing monitoring and risk assessm<strong>en</strong>ts undertak<strong>en</strong> under<br />

differ<strong>en</strong>t sc<strong>en</strong>arios of developm<strong>en</strong>t.<br />

Marine plans can create zones with differ<strong>en</strong>t objectives for each zone. This is the approach that<br />

MaPP is using.<br />

Underwater noise (measured or modelled) should be a layer in spatial data sets. Modelled noise<br />

levels should be validated with measurem<strong>en</strong>ts, and objectives set for maintaining areas of low<br />

noise as required to meet conservation targets.<br />

In efforts to establish a network of MPAs, spatially linking acoustically quiet areas would be<br />

b<strong>en</strong>eficial.<br />

Other tools such as the Gre<strong>en</strong> Marine program (described above), species managem<strong>en</strong>t regulations<br />

(based on SARA-listed species and other species ranking criteria, e.g., provincial Red and Blue lists), the<br />

IMO’s voluntary noise control standards, and changing ship design to improve effici<strong>en</strong>cy would also help<br />

to reduce underwater noise within the context of marine planning.<br />

Requirem<strong>en</strong>ts of the commercial shipping sector and its international regulatory structure need to be<br />

tak<strong>en</strong> into account. Shipping is an international industry, regulated primarily at the international level,<br />

though Canada has considerable scope to regulate within territorial sea limits.<br />

Obtaining Particularly S<strong>en</strong>sitive Sea Area (PSSA) designation from the IMO could be a useful approach to<br />

protecting key areas of habitat. To date, the IMO has designated 13 PSSAs, including some of the world’s<br />

most spectacular marine areas like Australia’s Great Barrier Reef, the US Florida Keys, and Ecuador’s<br />

Galapagos, which are vulnerable to damage caused by various aspects of international shipping<br />

activities. These are sci<strong>en</strong>ce-based designations but require governm<strong>en</strong>tal support and involvem<strong>en</strong>t in<br />

the multi-year assessm<strong>en</strong>t and designation process. However, once designated, ships transiting the area<br />

are subject to restrictions, which can include zero discharge zones and no-go zones; see Nowlan abstract<br />

for details).<br />

The noise-related priorities in planning should be:<br />

Undertaking risk based assessm<strong>en</strong>ts, and in areas of critical habitat, refining noise-related data<br />

layers and establishing target thresholds that are based on best up to date information;<br />

Engaging in a broader educational outreach to all who introduce noise into the ocean;<br />

Piloting a site for a cumulative effects assessm<strong>en</strong>t of underwater noise levels;<br />

Determining a cumulative noise cap for coastal waters, in addition to maximum exposure<br />

criteria; and<br />

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