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annotated bibliography of fisheries economics literature - Office of ...

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vessel and gear restrictions; and, output controls: tradable and non-tradable<br />

enterprise/individual quotas. The experience indicates that input controls<br />

are largely ineffective in constraining effort. These measures fail to<br />

address the common property characteristics <strong>of</strong> the resource and consequently<br />

failed to blunt the incentives for share maximization and increased<br />

capitalization. These in turn lead to overfishing and misreporting, thereby<br />

undermining management objectives. Output controls fare better in<br />

constraining effort. They lead to fleet rationalization and improved quality<br />

and flow <strong>of</strong> raw material to processing facilities. But they may also lead to<br />

highgrading and discarding, as quantity incentives give way to unit value<br />

incentives under the rights based regime. Some <strong>of</strong> the early failures and more<br />

recent successes <strong>of</strong> policy are outlined, lessons are drawn and suggestions<br />

made about future directions.<br />

Garnaut, Ross and Anthony Clunies Ross (1975). "Uncertainty, Risk<br />

Aversion and the Taxing <strong>of</strong> Natural Resource Projects." The<br />

Economic Journal, (June):272-287.<br />

Whatever national benefit is to be derived from natural resources must<br />

come mainly through taxation. This paper analyses the problem and suggests an<br />

approach which appears to do less to reduce efficiency in the use <strong>of</strong> resources<br />

than any alternative taxation system.<br />

Gaski, Andrea I. and Sonja Fordham (1996). Trade in Elasmopbranchs. The<br />

TRAFFIC Network and the Center for Marine Conservation, Washington,<br />

D.C., June, 2 pp.<br />

The international trade in elasmobranchs (sharks) is under study by the<br />

World Wildlife Fund and the Center for Marine Conservation which will produce<br />

an overview trade report in November.<br />

Gately, Dermot (1984). "A Ten-Year Retrospective: OPEC and the World<br />

Oil Market." Journal <strong>of</strong> Economic Literature, 21:1100-1114.<br />

This paper reviews the main events in the world oil market since 1973<br />

and some major explanations as to what happened and why. Then there is a<br />

discussion <strong>of</strong> some projections for the next two decades and <strong>of</strong> some<br />

implications <strong>of</strong> various theories about OPEC's decision making process. What<br />

we learned about modeling OPEC and the world oil market is then summarized.<br />

This includes: the dominant theoretical approach based on the wealth<br />

maximization model <strong>of</strong> Harold Hotelling (1931); the simulation approach most<br />

common in the applied <strong>literature</strong>, that envisages target capacity utilization<br />

pricing by OPEC; and the difficult problem <strong>of</strong> modeling price behavior during<br />

disruptions. Finally, some important unresolved theoretical and empirical<br />

issues are discussed.<br />

Gates, John M. (1974). "Demand Price, Fish Size and the Price <strong>of</strong> Fish."<br />

Canadian Journal <strong>of</strong> Agricultural Economics, 22(3):1-12.<br />

Despite considerable work in <strong>fisheries</strong> <strong>economics</strong> on the supply side,<br />

little attention has been devoted to theoretical aspects <strong>of</strong> the relationship<br />

between ex-vessel price and landings. One <strong>of</strong> the widely recognized<br />

determinants <strong>of</strong> fish prices is fish size, yet virtually all empirical analyses<br />

<strong>of</strong> the demand for fish ignore fish size. In this paper a demand function is<br />

postulated that includes fish size as a continuous demand shift parameter and<br />

the implications <strong>of</strong> fish size to the relationship between price and quantity<br />

are examined. It is concluded that bioeconomic models <strong>of</strong> the fishery that<br />

ignore fish size may yield policy conclusions that are quantitatively and, in<br />

some cases, qualitatively inaccurate.<br />

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