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Operational tools and adaptive management

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When we formulate the common incentive scheme as follows; c 0 cE j,<br />

the tax/subsidy rate<br />

c, <strong>and</strong> the lump sum transfer c0, relate to the incentive scheme of the single principal, the<br />

authorities, as shown in table 3.4.<br />

Table 3.4 Changes in the incentive scheme with an additional principal<br />

ENGOs hold higher ENV Common interests NGO hold lower ENV<br />

<strong>and</strong> lower ECO<br />

<strong>and</strong> higher ECO<br />

Tax/subsidy rate c > w c = w c < w<br />

Lump sum transfer c0 < w0 c0 = w0 c0 > w0<br />

In some situations with two principals, the net incentive scheme, i.e. the aggregate of the two<br />

incentive schemes, can be very strong (the aggregate of the tax/subsidy rates has a high<br />

absolute value) compared to what one principal would have forwarded as the single principal.<br />

This is the case when one principal has very asymmetrically weighted interests, i.e. either<br />

nearly only environmental interests, or nearly only economic <strong>and</strong> social interests, whereas the<br />

other principal‟s interests are more symmetric. Then, to avoid the strong tax/subsidy rate<br />

forwarded by the “asymmetric” principal, the “symmetric” principal may propose to<br />

cooperate <strong>and</strong> forward a common incentive scheme. As will be shown below, a common<br />

incentive scheme will almost always give a lower tax/subsidy rate when compared to the<br />

aggregate of two separately fixed rates. Hence, by cooperating, the “symmetric” principal<br />

tries to discipline the “asymmetric” principal.<br />

The scenario “NGO hold lower ENV <strong>and</strong> higher ECO” may seem strange, all the time we<br />

consider environmental NGOs. However, the organisation “Kystens Venner” (Friends of the<br />

Coast) calls themselves environmental. However, as they see the fisheries as the most<br />

important industry along the coast, they will often hold stronger economic than environmental<br />

interests, at least towards some fisheries‟ activity, arguing that it is important to keep the<br />

fisheries alive. There are examples of corresponding organisations in other European<br />

countries, as Friends of the Sea (France?).<br />

3.2.3.2 Symmetric stakeholders “compete” in regulating the fishery activity<br />

There is also the possibility that the two principals, authorities <strong>and</strong> ENGO, do not cooperate<br />

<strong>and</strong> instead develop two separate incentive schemes. Denote the two schemes t 0 t1E<br />

j for<br />

the authorities, <strong>and</strong> 0 1E<br />

j for the ENGO respectively. The agent, i.e. the fishers, reacts<br />

only to the net incentive scheme, which is the aggregate of the two schemes.<br />

One can argue that the ENGOs will have mainly environmental interests, but there are<br />

examples of ENGOs which also take into consideration the social <strong>and</strong> economic impacts the<br />

fishery activity has on local communities. We start off by assuming that the two principals are<br />

symmetric in the sense that they hold the same interests towards the fishery under<br />

consideration, <strong>and</strong> that they separately <strong>and</strong> simultaneously derive an incentive scheme in<br />

order to affect the fishers‟ behaviour with regard to choice of effort, <strong>and</strong> thus harvest. In<br />

formulating their incentive schemes, both take into account the fact that another principal<br />

formulates an incentive scheme towards the same agent. Taking into account this strategic<br />

interaction the tax/subsidy rate set by one principal becomes a function of the tax/subsidy rate<br />

set by the other principal. Interdependent tax/subsidy rates are also called reaction functions,<br />

<strong>and</strong> a reaction function gives one principal‟s best reply to the tax/subsidy rate of the other<br />

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