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A guide for planners and managers - IUCN

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142 MARINE AND COASTAL<br />

PROTECTED AREAS<br />

New Zeal<strong>and</strong> legislation limits the l<strong>and</strong>ward boundaries of marine protected<br />

areas to the high watermark, while the Marine Areas Act of 1970 of Trinidad <strong>and</strong> Tobago<br />

states that the term marine areas “includes any adjoining l<strong>and</strong> or swamp areas which<br />

<strong>for</strong>m within certain submarine areas a single ecological entity.” Other texts refer to<br />

the “<strong>for</strong>eshore” (Seychelles, National Parks <strong>and</strong> Nature Conservancy Ordinance,<br />

1973) or, less specifically, to areas that are part of a marine park (Australia, Great Barrier<br />

Reef Marine Park Act, 1975). It is worth repeating that MPAs must be extended<br />

l<strong>and</strong>ward when it is necessary to control activities that adversely affect the protected<br />

area.<br />

Other legal powers can accomplish protection beyond the boundaries of the<br />

designated area of an MPA (see Section I-5.9). For example, a general mangrove<br />

protection programme may be coordinated with a lagoon-protected area. Or the<br />

MPA may be nested inside a CZM programme (see Section I-5.8). Another approach<br />

is to organize a coordinating entity <strong>for</strong> the zone of influence (see Section 5.9).<br />

Coastal <strong>and</strong> marine protected areas are usually delimited by reference to<br />

geographical points, such as “l<strong>and</strong>marks,” bearings <strong>and</strong> distance, or longitude <strong>and</strong><br />

latitude (on the importance of these geographical points, see Box I-18). The most detailed<br />

provisions <strong>for</strong> delimiting vertical boundaries are those <strong>for</strong> the Great Barrier Reef Marine<br />

Park. The area of the park includes subsoils (extending to the depth specified in the<br />

proclamation declaring the parks), the air space above the site (extending to a height<br />

specified in the proclamation), the waters of any sea within the area, <strong>and</strong> the seabed<br />

beneath them.<br />

A new (1998) law <strong>for</strong> the Galapagos Isl<strong>and</strong>s is hoped to achieve its goals <strong>and</strong><br />

ensure the protection of the critical ecosystems of the Galapagos—it is one of the most<br />

innovative pieces of legislation covering an MPA. This ambition reflects the concerns<br />

of the government of the Galapagos <strong>and</strong> illustrates the variety of measures available<br />

to a government willing <strong>and</strong> able to take measures to protect a critical marine area<br />

(Box I-19).<br />

6.5 Legislative Options<br />

The general <strong>guide</strong>lines at the end of this section contain useful reminders of the essential<br />

elements that need to be included in any MPA legislation. Ultimately, however, there<br />

is no ideal legislation <strong>and</strong> each manager needs to think out the MPA strategy that best<br />

meets his or her particular needs. The importance of size, boundaries, traditional rights<br />

<strong>and</strong> use restriction has been explained in broad terms, but each MPA is truly a special<br />

mixture of all these elements. In addition to these technical considerations, whether<br />

or not to draft MPA legislation, <strong>and</strong> what kind of legislation, is also in part a political<br />

decision. The best legislation drafted in a non-consultative manner or that does not<br />

take into account some strong local concerns is doomed to failure. Likewise, an<br />

appropriate MPA could be established from the ground up, by the local stakeholders,<br />

long be<strong>for</strong>e legislation is enacted.

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