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Table 6. A proactive precautionary fisheries management policy orientation
may combine a
variety of approaches and regulatory tools (adapted and modified from Garcia,
1994; Olsen,
1999) as follows:
- Adopting the sustainable development principle;
- Adopting the principle
of precautionary management, with the degree of ‘precaution’ negotiated
on a case-by-case
basis;
- Using the best available science as evidence;
- Adopting a broader range
of management benchmarks and reference points more directly related
to recruitment)
reproduction capacity (safe biological limits, minimum spawning
biomass, etc.);
- Developing a set of criteria;
- Taking a risk-averse policy position
(e.g. requiring an environmental impact assessment (EIA) before authorizing
any
increase of fishing intensity beyond maximum rates of exploitation);
- Agreeing
on acceptable levels of impacts (and risk) (e.g. negotiations between
stakeholder interest groups, and within
an appropriate institutional and legislative framework will
be necessary);
- Basing management decisions on combined
stresses on resources and environment (e.g. insert fisheries in the
context of coastal zone/areas integrated management, for
the U.S., within the scope and parameters of ‘federal
consistency’ of the Coastal Zone Management Act of 1972 as amended);
- Improving
management response time (e.g. adaptive management techniques, reproductive
capacity, risk level);
- Improving participation of ‘non-fishery
users’ in fisheries
management bodies for more ‘transparency’ in
fisheries
management decision-making;
- Improving decision-making procedures (e.g.
voting procedures and public comment periods);
- Introducing
prior consultation procedures comparable to an EIA report for constituency
comments;
- Strengthening enforcement monitoring, control and surveillance
and raising penalties to deterrent levels.
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