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Operational tools and adaptive management

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The push for MSC certification in specific fisheries also influences the fisheries stakeholders,<br />

<strong>and</strong> their interactions with national fisheries managers. These two approaches for inclusion of<br />

environmental concerns in fisheries may secure greater legitimacy <strong>and</strong> acceptance amongst<br />

fisheries interests with regards to regulations implemented.<br />

The role of the ENGOs is of special interest. The ENGO community is a heterogenous<br />

community, reflected by the way they work in order to achieve marine environmental<br />

objectives. However, by focussing upon some types of fishing activities as having the most<br />

damaging effect upon the marine environment, these groups directly affect behaviour of the<br />

fisheries sector. Some ENGOs work solely at the level of policy makers, exerting pressure<br />

upon authorities in their formulation of directives, rules <strong>and</strong> regulations affecting the<br />

environment. These ENGOs have typically chosen an exogenous way in their effort to try to<br />

influence the fisheries environmentally. Other ENGOs utilise “green” preferences among<br />

consumers, expressed in a willingness to pay for sustainably harvested food <strong>and</strong> safe food,<br />

<strong>and</strong> organise campaigns directed towards consumers in order to induce them to boycott fish<br />

from for instance unsustainable fisheries. An alternative is that they offer fisheries, that fulfil<br />

conditions for sustainable harvesting, a certificate which is reliable in the market <strong>and</strong> thus<br />

secure higher prices <strong>and</strong>/or larger markets. The most prominent example here is the MSC.<br />

These are examples of how to affect the fisheries environmentally in an endogenous way.<br />

Previously, in section 3, we identified three interests that stakeholder groups such as EUauthorities,<br />

national authorities, ENGOs <strong>and</strong> the fishers hold towards the fishery activity.<br />

These interests are;<br />

- environmental (ecosystem health, healthy fish stocks, sufficiently large stocks)<br />

- economic (profitability, efficiency, rent extraction)<br />

- social (employment, community development)<br />

Further, we assumed that each of these interest groups has an objective function or goal<br />

consisting of a weighted combination of the three interests, <strong>and</strong> where the weights typically<br />

will vary between the groups. We formulated such an objective function as follows:<br />

U<br />

g<br />

g<br />

1<br />

ENV<br />

g<br />

2<br />

ECO<br />

g<br />

3<br />

SOC<br />

g<br />

EU,<br />

MS,<br />

F,<br />

NGO<br />

where U g is the utility (well-being) of interest group g, ENV is the environmental interest,<br />

ECO is the economic interest, <strong>and</strong> SOC is the socio-economic interest. Assuming that<br />

g g g<br />

g,<br />

1 2 3 1,<br />

the parameters λ1 g , λ2 g , <strong>and</strong> λ3 g can be interpreted as the relative<br />

weight interest group g attaches to the environmental interests, to economic interests, <strong>and</strong> to<br />

social interests respectively.<br />

Obviously, these interests <strong>and</strong> their relative weight do not only vary across different<br />

stakeholder groups, for one <strong>and</strong> the same stakeholder they probably also change over time.<br />

One way to interpret such changes over time, at least for stakeholder groups as authorities <strong>and</strong><br />

NGOs, is to observe which measures they take or use towards the fisheries in order to affect<br />

the fishers‟ behaviour. In section 3 we presented the different measures most commonly<br />

applied in the CFP <strong>and</strong> by national authorities, <strong>and</strong> in section 4 we transformed all measures<br />

into economic terms, representing either a tax, which makes the use of effort more expensive<br />

(1)<br />

52

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