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New Zealand oil spill response strategy - Maritime New Zealand

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All vessels that meet the criteria specified by the MARPOL 73/78 convention (as reflected in Part 130A)<br />

are required to have a shipboard <strong>oil</strong> pollution emergency plan (SOPEP), approved and audited by<br />

<strong>Maritime</strong> <strong>New</strong> <strong>Zealand</strong> or the appropriate maritime authority for foreign flagged vessels.<br />

The owner of an <strong>oil</strong> transfer site is required to ensure that an approved <strong>oil</strong> <strong>spill</strong> contingency plan has<br />

been produced (either by themselves or their tenants or lessees). The regional council, acting under a<br />

delegation from the Director, will be responsible for approving and auditing the contingency plans for<br />

<strong>oil</strong> transfer sites.<br />

The owner of an offshore installation (or their tenants or lessees) is required to produce a marine <strong>oil</strong><br />

<strong>spill</strong> contingency plan. In addition, discharge management plans are to incorporate emergency<br />

<strong>response</strong> provisions for <strong>oil</strong> <strong>spill</strong>s. Both contingency plans and discharge management plans are<br />

approved and audited by <strong>Maritime</strong> <strong>New</strong> <strong>Zealand</strong>. Where there are a number of related structures in a<br />

limited and defined geographic area, such as a large hydrocarbon field, the same contingency plan<br />

under the emergency <strong>response</strong> provisions may be shared if appropriate.<br />

If a <strong>spill</strong> from a Tier 1 site cannot be contained and recovered by the <strong>spill</strong>er, it must escalate to the<br />

next appropriate Tier.<br />

Tier 2<br />

Tier 2 <strong>response</strong> is the responsibility of regional councils and those unitary authorities acting as<br />

regional councils under the Act. These agencies must maintain the regional contingency plan for their<br />

region.<br />

Within their regions, these councils will respond to marine <strong>oil</strong> <strong>spill</strong>s that exceed the clean-up capability<br />

of Tier 1 (some regions have instigated a policy whereby a Tier 1 incident automatically escalates to<br />

Tier 2 if <strong>oil</strong> enters waters in the public domain). They will also respond to those <strong>spill</strong>s for which no<br />

responsible party can be identified. <strong>Maritime</strong> <strong>New</strong> <strong>Zealand</strong> will provide regional councils with sufficient<br />

equipment, training and opportunities to exercise their expertise in order to competently undertake this<br />

role.<br />

Regional council Tier 2 personnel and resources also play a fundamental role in Tier 3 <strong>response</strong>s. In<br />

the event of a significant incident that escalates to Tier 3, the Tier 2 responders maintain the <strong>response</strong><br />

during the transition phase, and still form an integral and vital part of clean-up activities at the Tier 3<br />

level.<br />

Each regional council is required to produce, maintain and implement a regional marine <strong>oil</strong> <strong>spill</strong><br />

contingency plan for their Territorial Sea (out to 12 nautical miles). <strong>Maritime</strong> <strong>New</strong> <strong>Zealand</strong> will approve<br />

and audit these regional plans. The regional contingency planning process should also include pre<strong>spill</strong><br />

segmentation of the region’s coastline by suitable trained assessors, to identify homogenous<br />

segments and any associated <strong>response</strong> issues in advance of an incident.<br />

An opportunity now exists for most regional councils to link their contingency planning process to the<br />

risk assessments that should be undertaken every three years under the <strong>New</strong> <strong>Zealand</strong> Port and<br />

Harbour Marine Safety Code 2004. The Code, though voluntary in nature, stipulates that the region<br />

should undertake a risk assessment for all harbours and areas of compulsory pilotage within their<br />

jurisdiction. Risk assessment should form the basis and be a fundamental driver of contingency<br />

planning.<br />

The relationship between Tier 2 & 3 plans has undergone a significant evolution since the previous<br />

<strong>strategy</strong> in 2000. The structure of the plans has been redefined, so national and regional plans will<br />

contain uniform operational procedures. Regional Tier 2 plans will include specific local information in<br />

appropriate annexes. As <strong>Maritime</strong> <strong>New</strong> <strong>Zealand</strong> maintains the generic front end of the plan, regional<br />

councils can concentrate their resources on identifying and prioritising sensitive areas and local<br />

<strong>response</strong> issues.<br />

During an incident, if a <strong>spill</strong>er cannot be identified or if a <strong>spill</strong> is beyond the capability of the Tier 1 site<br />

to respond, the ROSC will assume responsibility for the clean-up operation within their region directly.<br />

The ROSC shall decide whether or not it is appropriate for any action to be taken in <strong>response</strong> to that<br />

marine <strong>oil</strong> <strong>spill</strong>. According to section 303 of the <strong>Maritime</strong> Transport Act, the principal objective of the<br />

ROSC in taking any such action will be to prevent further pollution from the marine <strong>oil</strong> <strong>spill</strong>, and to<br />

contain and clean up the <strong>oil</strong> <strong>spill</strong> in accordance with the relevant regional marine <strong>oil</strong> <strong>spill</strong> contingency<br />

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