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A Model of Regulated Open Access Resource Use

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10<br />

HOMANS AND WILEN<br />

3. ANALYSIS OF REGULATED OPEN ACCESS BEHAVIOR<br />

The three components described above characterize a regulated open access<br />

fishery. The industry is assumed to commit capacity E each season until rents are<br />

dissipated. Regulators are assumed to set a harvest target quota Q each season and<br />

then choose a season length T which ensures that the quota is achieved. A<br />

regulated open access equilibrium is achieved by the interaction <strong>of</strong> the industry<br />

and regulators each season. Biomass evolves between seasons according to whether<br />

the corresponding harvest is greater than, equal to, or less than biological growth.<br />

A long run steady state is achieved when the biomass is in equilibrium and when<br />

industry and regulatory behavior are constant.<br />

In a steady state equilibrium, both beginning and ending biomass levels are given<br />

and constant from season and their levels depend upon c, d, a, and b. Since the<br />

harvest quota target is simply the difference between beginning and ending<br />

biomass levels, Q is predetermined also once c and d are chosen. Then a regulated<br />

open access equilibrium within the season is achieved when the industry commits a<br />

level <strong>of</strong> capacity E and the regulators choose a season length T such that<br />

PX0Ž 1 e qET . ET fE 0<br />

1 X0 1 X0<br />

T ln ln , Ž 12.<br />

qE X qE Ž 1 d.<br />

X c<br />

T 0<br />

where X satisfies Ž 11.<br />

0<br />

above. A regulated open access fishery is thus the joint<br />

outcome <strong>of</strong> the behavior <strong>of</strong> both the industry and regulatory agency, coupled with<br />

biological dynamics.<br />

What happens to this equilibrium as economic, regulatory, and biological parameters<br />

change? This can be addressed by performing comparative statics computations<br />

on the equilibrium. Note first that this system is recursive in that the steady<br />

state biomass level is determined only by the biological parameters, a and b, and<br />

the regulatory parameters, c and d. The regulatory agency’s instrument choice T<br />

depends only upon the exploitation rule parameters and the level <strong>of</strong> capacity<br />

chosen by the industry. Thus the two equations in Ž 12.<br />

determine the equilibrium<br />

pair E, T which satisfy the open access regulatory equilibrium. For any arbitrary<br />

X , this pair <strong>of</strong> equations yields a temporary equilibrium ET,X Ž .,TŽ E, X .<br />

0 0 0<br />

dependent upon X , and when X satisfies Ž 11 .<br />

0 0<br />

, the system is in a full long run<br />

equilibrium with X0<br />

constant.<br />

Comparative statics properties <strong>of</strong> the long run equilibrium are given in Table I<br />

and Appendix B. These are all plausible results. When prices P or harvest<br />

efficiency q rise Ž or costs or f fall.<br />

the rent dissipating level <strong>of</strong> E rises. But if the<br />

biomass and quota are in long run equilibrium, this increase in potential fishing<br />

capacity must be stifled by corresponding reductions in season length. Since the<br />

biological system is recursive, pricecost parameters do not affect the steady state<br />

level <strong>of</strong> biomass which is determined only by biological and regulatory parameters<br />

Ž a, b, c, and d .. On the other hand, changes in a, b, c, and d affect the levels T<br />

and E in potentially complicated ways via their effects on X and Q. For example,<br />

if the intrinsic growth rate a rises, then Žceteris paribus; holding the exploitation<br />

rule constant.<br />

both the allowable long run biomass and quota will rise. As it turns

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