Establishing representative no-take areas in the Great Barrier Reef: Large-scale implementation of theory on marine protected areas

被引:449
作者
Fernandes, L
Day, J
Lewis, A
Slegers, S
Kerrigan, B
Breen, D
Cameron, D
Jago, B
Hall, J
Lowe, D
Innes, J
Tanzer, J
Chadwick, V
Thompson, L
Gorman, K
Simmons, M
Barnett, B
Sampson, K
De'ath, G
Mapstone, B
Marsh, H
Possingham, HP
Ball, I
Ward, T
Dobbs, K
Aumend, J
Slater, D
Stapleton, K
机构
[1] Barrier Reef marine Pk Author, Townsville, Qld 4810, Australia
[2] GeoSci Australia, Canberra, ACT 2601, Australia
[3] Natl Land Survey Iceland, IS-300 Akranes, Iceland
[4] Queensland Fisheries Serv, Brisbane, Qld 4000, Australia
[5] New S Wales Fisheries, Port Stephens Res Ctr, Taylors Beach, NSW 2316, Australia
[6] Queensland Environm Protect Agcy, Brisbane, Qld 4000, Australia
[7] Natl Oceans Off, Hobart, Tas 7000, Australia
[8] Great Barrier Reef World Heritage Area, Cooperat Res Ctr, Townsville, Qld 4810, Australia
[9] Australian Inst Marine Sci, Townsville, Qld 4810, Australia
[10] Antarctic Climate & Ecosyst Cooperat Res Ctr, Sandy Bay, Tas 7005, Australia
[11] James Cook Univ N Queensland, Townsville, Qld 4811, Australia
[12] Univ Queensland, Sch Life Sci, St Lucia, Qld 4072, Australia
[13] Univ Queensland, Dept Math, St Lucia, Qld 4072, Australia
[14] Australian Antarctic Div, Kingston, Tas 7050, Australia
[15] Univ Western Australia, Inst Reg Dev, Nedlands, WA 6907, Australia
关键词
biophysical operational principles; cultural operational principles; economic operational principles; reserve-design software; social operational principles;
D O I
10.1111/j.1523-1739.2005.00302.x
中图分类号
X176 [生物多样性保护];
学科分类号
090705 ;
摘要
The Great Barrier Reef Marine Park, an area almost the size , of Japan, has a new network of no-take areas that significantly improves the protection of biodiversity. The new marine park zoning implements, in a quantitative manner, many of the theoretical design principles discussed in the literature. For example, the new network of no-take areas has at least 20% protection per "bioregion," minimum levels of protection for all known habitats and special or unique features, and minimum sizes for no-take areas of at least 10 or 20 kat across at the smallest diameter Overall, more than 33% of the Great Barrier Reef Marine Park is now in no-take areas (previously 4.5%). The steps taken leading to this outcome were to clarify to the interested public why the existing level of protection wets inadequate; detail the conservation objectives of establishing new no-take areas; work with relevant and independent experts to define, and contribute to, the best scientific process to deliver on the objectives; describe the biodiversity (e.g., map bioregions); define operational principles needed to achieve the objectives; invite community input on all of The above; gather and layer the data gathered in round-table discussions; report the degree of achievement of principles for various options of no-take areas; and determine how to address negative impacts. Some of the key success factors in this case have global relevance and include focusing initial communication on the problem to be addressed; applying the precautionary principle; using independent experts; facilitating input to decision making; conducting extensive and participatory consultation; having an existing marine park that encompassed much of the ecosystem; having legislative power under federal law; developing high-level support; ensuring agency Priority and ownership; and being able to address the issue of displaced fishers.
引用
收藏
页码:1733 / 1744
页数:12
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