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Operational tools and adaptive management

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A3.4 New stakeholders <strong>and</strong> common agency<br />

We keep to the application of linear incentive schemes <strong>and</strong> the assumption about symmetric<br />

<strong>and</strong> complete information. Previously, Chortareas <strong>and</strong> Miller (2004) <strong>and</strong> Campoy <strong>and</strong> Negrete<br />

(2008) have analysed the regulation of a central bank by two principals; the government <strong>and</strong><br />

an independent interest group. They use a linear incentive scheme, as the one derived by<br />

Walsh (1995) <strong>and</strong> discusses how the introduction of a second interest group (industrialists)<br />

affects the optimal incentive scheme of the government, <strong>and</strong> the net incentive scheme, i.e. the<br />

aggregate of the incentive scheme offered by the two principals. As far as we know, a<br />

common agency model has never been applied to fisheries regulations.<br />

A3.4.1 Cooperating principals<br />

Formally, the formulation <strong>and</strong> resolving of the model with cooperating principals coincides<br />

with that of a single principal. The only difference being the principals‟ common objective<br />

function. This function is now given by<br />

U<br />

C<br />

(<br />

C<br />

C<br />

C<br />

( c , c )<br />

)<br />

0<br />

C<br />

2<br />

1<br />

F<br />

( x)<br />

C<br />

1<br />

pqx<br />

c<br />

(<br />

0<br />

F<br />

)<br />

C<br />

2<br />

C<br />

3<br />

C<br />

1<br />

E<br />

M<br />

j<br />

F<br />

1<br />

Nqx<br />

pqx<br />

C<br />

3<br />

2<br />

(<br />

F<br />

1<br />

C<br />

1<br />

4a<br />

(<br />

C<br />

2<br />

2<br />

2<br />

F<br />

1<br />

2a<br />

Nqx<br />

F2<br />

1<br />

F<br />

1<br />

where θ is the costs to the two principals of formulating <strong>and</strong> implementing the common<br />

C<br />

MS<br />

NGO<br />

incentive scheme, <strong>and</strong> i ( i ) ( 1 ) i , i 1,<br />

2,<br />

3 . This implies that the weights of<br />

the interests in the common objective function, λi C , are now weighted averages of the weights<br />

in the objective functions of the two principals.<br />

Applying the same procedure as in the single principal case, we find the optimal tax/subsidy<br />

rate to be<br />

C<br />

2<br />

C<br />

2<br />

F C<br />

2 (<br />

F<br />

2<br />

F<br />

( ) )<br />

c *<br />

(22)<br />

Setting α=0,5, <strong>and</strong> assuming that the NGO has higher environmental <strong>and</strong> lower economic <strong>and</strong><br />

social interests compared with the authorities, we get that<br />

C MS<br />

,<br />

C<br />

3<br />

MS<br />

3<br />

)<br />

C<br />

3<br />

c<br />

)<br />

2<br />

C<br />

1<br />

(<br />

(<br />

F<br />

)(<br />

F<br />

2<br />

C<br />

1<br />

2a<br />

Nqx<br />

2<br />

F<br />

1<br />

F<br />

3<br />

F<br />

1<br />

1 1 ,<br />

)<br />

C<br />

2<br />

2a<br />

C<br />

F<br />

1<br />

MS<br />

2<br />

c<br />

C<br />

C<br />

(21)<br />

. These characteristics contribute to make both nominator terms on the right h<strong>and</strong><br />

side of (22) lower, <strong>and</strong> the denominator lower compared to w* given in (17). Keeping the<br />

assumption from above that the fishers hold lower environmental <strong>and</strong> higher economic <strong>and</strong><br />

social interests combined with the above inequalities, it can be shown that the optimal<br />

tax/subsidy rate will increase as a consequence of an additional principal with strong<br />

environmental interests, given that this principal cooperates with the original principal. This<br />

means that the principal will set a higher tax or a lower subsidy on effort.<br />

66

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