Evaluation of Three Lobster Fishery Management Plans

by

 

Jon G. Sutinen,* John M. Gates,* John J. Poggie, Jr.,** and Timothy M. Hennessey***

 

 

* Department of Environmental & Natural Resource Economics

** Department of Sociology & Anthropology

*** Department of Political Science

 

 

University of Rhode Island, Kingston, RI 02881

 

 

Three plans have been proposed to the Lobster Management Subcommittee for the future management of Rhode Island’s lobster fishery. In this report we present the results of our assessment of the expected biological, economic, social and administrative consequences of each plan.[1]

We intend no overall ranking of the plans that are evaluated below. We recognize that there may be several reasons for regulating a fishery. In addition to conserving the resource and improving economic performance, fishery management measures are sometimes used to prevent or mitigate conflicts among user groups, to affect the distribution of benefits among users and to protect social values and life styles. The results herein only delineate the inherent tradeoffs among the sets of consequences that fishery managers face when deciding which management measures to employ.

Biological consequences

Of the three proposed plans, DEM’s Lobster License Plan places the strongest ceiling on fishing effort. It removes latent traps and freezes the number of traps at about (perhaps below) the current number of active traps in the fishery. The plan allows no new entrants to the fishery until the resource stock is rebuilt; and then only to replace departing lobstermen on a 1:1 basis.

To reduce the number of traps the plan relies on attrition of license holders over time. We expect the rate of decrease in licenses to be slow. The prohibition on license transfers (except to family members or vessel crew in the case of death or disability of the license holder) creates a disincentive to retire from the fishery.

Fishing mortality is not fully controlled by the DEM plan since there is a ‘spongy’ relationship between traps and fishing mortality. Operators will still have the incentive to find other ways to increase the productivity of their trap allocation as stock conditions improve (such as by changing the number of trap hauls per period, placement of traps, using more and superior bait, etc.).[2]

·        We assign a grade of A-minus to the biological consequences of DEM’s Lobster License Plan. It places a firm ceiling on trap numbers but the reduction in traps will be slow.

The industry’s Effort Control and Consolidation Plan offers a fairly strong control of fishing effort. It reduces latent effort by moving the licenses that are currently inactive – each with a potential of 800 traps – to an apprenticeship license with a limit of 100 traps each. Since there is no cap on the number of apprentice licenses, there is no firm cap on the total number of active traps in the fishery. If resource and market conditions improve over time, apprenticeship licenses will increase in number.

The industry’s Plan will stimulate a reduction in the number of traps fished in the short term, when there are no added incentives for inactive licenses to enter the fishery. The Plan stimulates reduction by encouraging consolidation of licenses. Our computer modeling demonstrates that there are significant incentives for lobstermen to consolidate licenses. We anticipate an immediate move towards consolidation and, therefore, a reduction in traps fished in the short term.

Our computer modeling shows that consolidation also will result in lower catches – ranging from 26% to 33% fewer pounds of lobsters caught. Our models account for likely increases in trap hauls per period and in days fished. But our models do not account for the ‘trap saturation’ that is believed to exist in the lobster fishery. Therefore, we believe the actual amount of catch reductions will be less than our model estimates.

While the short-term reductions in traps, effort and catch are admirable, the unrestricted growth of apprenticeship licenses – each with 100 traps – threatens in the long term to either mitigate or reverse trap reductions if stock and/or market conditions improve.

·        We assign a B-plus grade to the biological consequences of the industry’s Effort Control and Consolidation Plan. It will lead to a reduction in the number of traps fished in the short term: however, it does not place a firm ceiling on the total number of traps in the fishery in the long term.

The industry’s Open Access Plan provides no direct control on the total number of traps. It lifts the moratorium on licenses and allows unrestricted access to the fishery. The number of active traps will tend to decrease only if stock and/or market conditions deteriorate. If those conditions improve, the number of traps will increase due to new entrants and increased trap usage by the currently active fleet. We expect fishing mortality to steadily increase under this Plan.

The Open Access Plan proposes significant increase in the minimum size and imposes a relatively small maximum size of lobster. Our fishery scientist colleagues have testified that such significant changes can, in principle, rebuild the resource stock. Since no specific minimum and maximum size limits have been proposed, there is no way to predict the extent of stock rebuilding that can be expected.

·        We assign a grade of D-minus to the biological consequences of the industry’s Open Access Plan. It places no restrictions on the total number of traps fished, which will likely put the resource at greater risk.

Economic consequences

Economic consequences include changes in the net economic benefits to harvesters, processors, distributors, marketers, and consumers. The net benefits are related to landings (amounts and seasonal patterns); fishing patterns (season length, race-to-fish); harvesting capacity (fleet size and composition, vessel sizes); harvesting practices (fishing techniques, product handling); by-catch (amounts and use of); product utilization (discards, high-grading); landed product forms; harvesting costs; gear conflicts; gear loss; employment (amount and seasonal patterns) in harvesting and processing; safety; total sales/revenues; vessels owners and crew incomes; and resource rent. In the market sector, net benefits are related to prices (levels and seasonal patterns); product quality and forms; product utilization; product availability patterns (e.g. market gluts and scarcity); imports and exports; and consumption patterns.

Of the three proposed plans, the industry’s Effort Control and Consolidation Plan offers the most favorable economic consequences to RI lobstermen. Our computer modeling shows that net incomes for the fleet as a whole will increase in the short term through consolidation (by as much as 75% for some, not all, producers). Costs decline more than revenues in these models. If trap saturation prevails, then revenues will not drop and net revenues will increase more than our estimates. We also expect growth in net incomes over time when stock conditions improve in the fishery.

The Plan’s provision to allow the sale of a lobster license strengthens and protects the security of lobster businesses. This is especially valuable to lobstermen within a few years of retirement in the early years of stock rebuilding. This provides greater financial security to them and their families. Also, the economic security offered by transferable licenses will motivate the financial community to offer lobstermen more favorable terms on credit, especially when combined with improved prospects for stock rebuilding.

·        We assign a grade of B-plus to the economic consequences of the industry’s Effort Control and Consolidation Plan. We expect the Plan to significantly increase the net benefits to and economic security of lobster producers, and provide greater economic stability in the fishery. The plan also provides protection against excessive consolidation in the fishery. We do not assign a top grade to the economic consequences of this Plan because of the restrictive conditions on license transfers and because the number of apprenticeship licenses is not controlled.

DEM’s Lobster License Plan will not improve the net incomes of the fleet in the short term – because the Plan effectively freezes each active producer in an initial position. There is little or no flexibility and opportunity in the Plan to improve economic returns in the short term. However, net incomes are expected to grow in the long term as stock rebuilding occurs under the Plan.

The Plan actually worsens the security of lobster businesses, especially in the short term. The ban on the sale of licenses combined with the ban on new entrants seriously weakens these enterprises. The plan places fishermen at risk who are currently within a few years of retirement. Since no new entrants are allowed – at least until the stock is rebuilt – and licenses cannot be sold, the value of their lobster fishing businesses is depressed. Also, since the license must be returned to the State, the boat and other assets must be sold for use outside of RI state waters. They will have to work longer and harder in order to afford retirement.

In the short term, the weaker economic security will hamper the lobstermen’s access to credit. However, in the long term, with the improved control of fishing effort and improved prospects for the fishery, the financial community is likely to offer more favorable terms to lobstermen.

·        We assign a grade of C-minus to the economic consequences of DEM’s Lobster License Plan. There are few, if any, opportunities for producers to improve their net incomes under the Plan. It also places at risk the businesses of those producers who are currently within a few years of retirement. We do not assign a lower grade to the economic consequences of this Plan because of the strong potential for stock rebuilding in the long term.

The industry’s Open Access Plan will not improve the economic status of the fishery. We do not expect the net incomes of lobstermen to improve either in the short or the long term. Under open access, the long term viability of the fishery is placed at risk, which will threaten the economic security of lobster producers and their families.

Licenses would have no value in an open access fishery, even if they could be traded. However, unlike the DEM Lobster License Plan’s severe restrictions on new entrants, under open access new entrants would be potential buyers of lobster businesses. But, since we expect the biological and economic conditions to worsen under open access, the sale value of those businesses for use in RI waters would be low.

·        We assign a grade of D-minus to the economic consequences of the Open Access Plan. We expect the plan to reduce net benefits to and the economic security of lobster producers in both the short and long term. The plan also is likely to create more instability in the fishery.

For any one of the three plans, we expect no significant changes in the net benefits to local dealers and consumers, since RI production is a small fraction of the lobster market. Also, neither the quality nor the seasonal patterns of lobster landings is expected to be affected by the plans.

Social consequences

Sociologists and anthropologists who study marine resource-dependent communities use what is called ‘cultural capital’ to measure the social health of these communities.[3] The Rhode Island communities of Pt. Judith/Galilee, Jamestown, Newport, Tiverton and Sakonnet Pt. rank among the top marine resource-dependent communities in New England (traditionally as well as currently). The lobster fishery is a major determinant of the social health (a.k.a. cultural capital) of these communities.

Of the three proposed plans, the industry’s Open Access Plan has the most benign social consequences in the short term, and perhaps in the long term. The Plan allows lateral mobility into and out of the lobster fishery. To the extent that new entrants from other fisheries are not perceived to damage the well-being of currently active lobstermen, the linkages and relationships between lobster producers and producers in other fisheries will be strengthened. A stronger sense of community would emerge. Open access would continue to support the traditional lifestyles of RI fishermen.

There would be little or no disruption to employment, demographics, family stability, social stress, and social networks in the communities, at least in the short term. If open access leads ultimately to further stock depletion and economic hardship in the lobster fishery, the social health of these communities could suffer in the long term.

Further, the Plan would not directly affect ownership patterns in the fishery. There will be no tendency, triggered by the Plan, to move away from the small-scale and family-operated lobster operations that are highly valued by many members of the fishing community.

The Open Access Plan is likely to be perceived as fair among many fishermen and other community members. No privileged class of lobster producers is created by the plan; and there are no ‘haves’ and ‘have-nots’ created by the Plan. All who want to enter the fishery may do so, and they compete on a level playing field with others in the fishery. The Plan does not arbitrarily redistribute incomes and other benefits among fishermen in fishery-dependent communities.

·        We assign a grade of B-plus to the social consequences of the Open Access Plan. In the short term the Plan preserves, and may even strengthen, the ‘cultural capital’ of those Rhode Island communities dependent on the lobster fishery. We do not assign a higher grade to the social consequences of this Plan because we fear that the long terms prospects for fishery are threatened by open access. A deteriorating fishery would, consequently, also threaten the social health of those communities that are dependent on this most valuable of RI’s fisheries.

The industry’s Effort Control and Consolidation Plan presents a few threats to the social health of fishing communities in the short term. However, the Plan may improve the social health of these communities in the long term.

The Plan creates an identified group of lobstermen who are initially awarded active and part-time licenses. This group may be perceived by the larger community as a ‘privileged class.’ If so, the Plan may be perceived as unfair by some members of the community, including other fishermen. If this perception is sufficiently strong, this could create social divisiveness and threaten the social health of the communities, at least in the short term.

The Plan allows lateral mobility into and out of the lobster fishery. New entrants can acquire an apprenticeship license for a nominal fee. New entrants who wish to operate at a larger scale than permitted by the apprenticeship license may purchase a license from a willing seller of an active or part-time license. The price of a license is not likely to be low. Therefore, entry will not be possible for those who do not have the financial ability to purchase an active or part-time license. If this barrier to entry is widely perceived as unfair, social networks may be frayed in the short term.

The Plan fosters consolidation and, therefore, a reduction in the number of lobster producers. Employment in the fishery will decline. Unless provisions are provided to allow and encourage downsizing of license holders, there is little prospect for the number of producers & employment to increase in the long term when the fishery resource recovers.

Ownership patterns in the fishery are likely to be changed by this Plan. We expect a move towards smaller producers (100 traps) and larger producers (1200 trap maximum), and a move away from medium size producers (400 to 800 traps). We do not expect large corporations to dominate as a form of business in the fishery. We expect the family-operated form of business to thrive as well as any other form.

The Plan has the potential to significantly improve the economic health of lobster producers and their families. This is expected to spill over to the larger community, especially in the long term when the resource is rebuilt. Higher incomes will result in greater expenditures by lobster families in their communities, and tax revenues will grow. We expect these expenditures and taxes to improve the physical and social infrastructure in RI fishery-dependent communities.

·        We assign a grade of B to the social consequences of the industry’s Effort Control and Consolidation Plan. The Plan presents a few threats to the social health of fishing communities in the short term. However, the Plan may improve the social health of these communities in the long term. We do not rate this Plan higher because of the potential for perceived inequities that may lead, in the short term, to social disruption in RI’s fishing communities.

DEM’s Lobster License Plan presents some serious threats to the social health of RI’s fishing communities. First, it caps the number of lobster producers and does not allow new entrants until after the resource stock is rebuilt. Second, it creates a small, exclusive group of lobster license holders. Third, it imposes serious inflexibilities on the remaining participants in the fishery. We expect these and other provisions to present significant threats to the social health of fishing communities in RI.

On the plus side, the Plan does not significantly alter employment, demographic, and ownership patterns in the fishery. If the plan ultimately leads to rebuilding the lobster resource stock, the fishery should be allowed to expand. New entrants will be allowed at that point, which should relieve some of the social disruption caused during the rebuilding phase of the Plan.

·        We assign a grade of D to the social consequences of DEM’s Lobster License Plan. The Plan presents serious threats to the social health of RI fishing communities, especially those communities that are dependent on the lobster fishery. We do not rate this Plan higher because of prohibition of new entrants during the rebuilding phase, the lack of flexibility for producers, and the privileged group of producers that the Plan creates.

Administrative consequences

Administrative consequences include changes in the amount of enforcement resources and costs; compliance and enforcement problems; industry acceptance and cooperation, or resistance; information demands; monitoring resources and costs; research requirements and costs; and data degradation, including misreporting of landings and fishing activity. Administrative consequences also include the extent to which lobster producers encourage their elected representatives to become involved in the setting of management measures (a.k.a. the ‘end run’); and the extent to which lobster producers seek favorable treatment by the management authorities (a.k.a., ‘rent seeking’). Such influences are well known for their ability to thwart the ability of fishery management authorities to effectively manage the fisheries for which they are responsible.[4]

Of the three plans, the industry’s Effort Control and Consolidation Plan is expected to have few serious administrative drawbacks and may yield some positive administrative consequences. The Plan is not expected to add significantly to the burden on enforcement, since trap monitoring is expected to continue in much same way as under the current program. Since the industry’s Plan appears to have strong support among the leadership of the State’s two principle lobster organizations, we expect widespread acceptance of the plan among the industry. This should result in substantial cooperation with DEM and no increase in noncompliance.[5]

We expect the initial allocation of traps among currently active lobster producers to be time consuming and potentially problematic. The appeals process will require additional resources for administration of the program.

We do not expect this Plan to elevate information demands, monitoring resources and costs, research requirements and costs, nor cause data degradation, including misreporting of landings and fishing activity.

We expect that there will be less of a propensity by lobster producers to encourage elected representatives to become involved in the setting of management measures, since entry is allowed and trap allocations are handled by a market for licenses. This is in direct contrast to the DEM Lobster License Plan. Some of this behavior will continue as in the past, but the volume of this activity is expected to diminish as a result of this Plan.

·        We assign a grade of B-plus to the administrative consequences of industry’s Effort Control and Consolidation Plan. The initial allocation of traps will be time-consuming and may be problematic; however, compliance is expected to improve and ‘rent-seeking’ to diminish.

The industry’s Open Access Plan presents only a few potential drawbacks. The Plan proposes no changes in the number of traps allowed by each participant. The entry of new producers overtime will add more traps in the water and thereby increase the demands on enforcement, but probably not to a great extent.

The principal potential drawback that we see is that the plan proposes significant increases in the minimum carapace size and imposition of a maximum size. Many lobstermen may not readily accept and cooperate with the proposed increases in the minimum carapace size and imposition of a maximum size. If so, this could lead to a substantial growth in noncompliance, which would require more enforcement resources.

We do not expect the Plan to elevate information demands, monitoring resources and costs, research requirements and costs, nor cause data degradation, including misreporting of landings and fishing activity.

·        We assign a grade of B to the administrative consequences of industry’s Open Access Plan. The proposed significant changes in size regulations may increase compliance and enforcement problems.

DEM’s Lobster License Plan proposes to lock producers in to a set of fixed trap allocations and allows for no new entrants into the fishery. Unless DEM can marshal widespread support among the industry for these aspects of the Plan, we expect noncompliance to grow, causing an increase in enforcement problems and more demands on enforcement resources.

We expect the initial allocation of traps among currently active lobster producers to be time consuming and more problematic than the industry’s Effort Control and Consolidation Plan. The appeals process will involve more resources for this purpose than the other plan, since the volume of appeals is expected to be greater and more time consuming.

We do not expect this Plan to elevate information demands, monitoring resources and costs, research requirements and costs, nor cause data degradation, including misreporting of landings and fishing activity.

Also, since transfers of licenses are prohibited by the Plan, there will be a strong propensity by lobster producers to encourage elected representatives to become involved to influence administration of the Plan, especially the administration of new entrants to the fishery. We expect the ‘end run’ and ‘rent seeking’ behaviors to intensify.

·        We assign a grade of D to the administrative consequences of DEM’s Lobster License Plan. The initial allocation of traps will be more time-consuming and problematic than the industry Plan; and noncompliance and ‘rent-seeking’ are expected to increase.

None of the plans provides a mechanism to recover the costs of management from lobster producers. The administrative performance of each plan could be measurably improved if a form of sustainable financing were implemented in the fishery.

The results of our evaluation is summarized in the following table.

 

Proposed Management Plans

Consequences

Effort Control & Consolidation Plan

Open Access Plan

DEM Lobster License Plan

            Biological

B+

D-

A-

            Economic

B+

D-

C-

            Social

B

B+

D

            Administrative

B+

B

D

 


Bibliography

References Cited

Dyer, Christopher L. ; and Poggie, John J. 2000. "The Natural Resource Region and Marine Policy: A Case Study from the New England Groundfish Fishery." 24 Marine Policy 245-255.

Furlong, W. J. 1991. ‘The Deterrent Effect of Regulatory Enforcement in the Fishery,’ Land Econ. 67(1): 116-129.

Gates, J.M., 2000. "Input Substitution in a Trap Fishery," ICES, Journal of Marine Science. 57: 89-108.

Hennessey, T. and M. Healey. 2000. Ludwig's rachet and the collapse of New England groundfish stocks. Coastal Manage. 28(3):187-213.

Kuperan, K., and J. G. Sutinen. 1998. ‘Blue Water Crime: Legitimacy, Deterrence and Compliance in Fisheries,’ Law and Society Review 32(2):309-338.

OECD. 1994. Fisheries Enforcement Issues, Paris: Organization for Economic Co-operation and Development.

OECD. 1997. Towards Sustainable Fisheries: Economic Aspects of the Management of Living Marine Resources. Organization for Economic Cooperation and Development. Paris; 268 pp.

Sissenwine, M.P., & Rosenberg, A. 1993. Marine fisheries at a critical juncture. Fisheries, 18(10): 6-14.

Sissenwine, M.P., and P. M. Mace. 2001. Governance For Responsible Fisheries: An Ecosystem Approach,’ a paper presented to The Reykjavik Conference On Responsible Fisheries In The Marine Ecosystem, October 1-4, 2001, Reykjavik, Iceland.

Sutinen, J. G. and K. Kuperan. 1999. ‘A Socioeconomic Theory of Regulatory Compliance in Fisheries,’ International Journal of Social Economics 26(1/2/3):174-193.

Sutinen, J. G., A. Rieser, and J. R. Gauvin. 1990. "Measuring and Explaining Noncompliance in Federally Managed Fisheries," Ocean Development and International Law, 21:335-372.

Sutinen, Jon G. 1999. ‘What Works Well and Why: Evidence from Fishery Management Experiences in OECD Countries,’ ICES Journal of Marine Science, 56: 1051-1058.

Sutinen, Jon G. and Harold F. Upton. 2000. ‘Economic Perspectives on New England Fisheries Management,’ Northeast Naturalist 7(4): 361-72.

Additional Readings

References on the Economics of Lobster Fisheries

Gates, J.M., with E.J. Richardson. 1986. "Economic Benefits of American Lobster Fishery Management Regulations," Marine Resource Economics, 2(4):353-385.

Hasselback, N.L., J.B. Dirlam, and J.M. Gates. 1981. "Canadian Lobster Imports and the New England Lobster Industry," Marine Policy 5(1):40-51.

References on the Political & Administrative Aspects of Regulation

Buchanan J. and G Tullock. 1975. Polluters, Profit and Political Response: Direct Control versus Taxes. Am. Econ. Rev. 65:139-140.

Buchanan, J. and G. Tullock. 1962. The Calculus of Consent. Ann Arbor: University of Michigan Press, 1972.

Buchanan, J.M. 1980. Rent-seeking under external diseconomies. In Toward a Theory of the Rent-Seeking Society, ed JM Buchanan, RD Tollinson, and G Tullock. College Station:Texas A&M Press.

Campos J.E. 1989. Legislative Institutions, Lobbying and the Endogenous Choice of Regulatory Instrument: A political Economy Approach to Instrument Choice. J.L. Econ & Org 5: 333-348.

Fiorina M. 1982. Legislative Choice of Regulatory Forms: legal process or Administrative Process? Public Choice 39:33-

Hahn K. 1990. The political Economy of Environmental Regulation: Towards a Unifying Framework. Public Choice 65: 21-

Hennessey, T. and M. Healey. 1999. “The Fairness Paradox, Ludwig’s Ratchet and the “Problem” of Fisheries Management in Canada and The United States,” in Dennis Soden and Brent Steel, Handbook of Global Environmental Policy and Administration. Marcel Decker, New York.

Keohane N., Revesz R. and R Stavin. 1998. The Choice of Regulatory Instruments in Environmental Policy. Harvard Environmental Law Review, 22:313-367.

Magat, W., Kruspnick, A. and Harrington, W. 1986. Rules in the making: A statistical analysis of regulatory agency behavior. Washington, DC: Resources for the future.

Niskanen, W. 1971. Bureaucracy and Representative Government. Chicago, IL:Aldine Press.

Olson, M. 1964. The logic of Collective Action. Harvard University Press, Cambridge MA.

Peltzman, S. 1976. Toward a more general theory of Regulation. Journal of Law and Economics 19:211-240.

Peltzman, S. 1984. Constituent Interest and Congress Voting. Journal of Law and Economics 27:181

Sproule-Jones, M. 1982. Public Choice and Natural Resources: Methodological Explanation and Critique. American Political Science Review. 790-802.

Stigler, G. 1971. The Economy theory of Regulation. Bell Journal of Economics 2:3-21.

Tollinson, R.D. 1982. Rent-Seeking: A survey, Kyklos 35:575-602.

Wolf, C. Jr. 1988. Markets or Governments: Choosing between Imperfect Alternatives. The MIT Press, Cambridge, MA.

Zusman, A. and G. Rausser. 1994. Intraorganizational Influence relations and the optimality of collective action. J. of Econ. Behavior and Org. 24:1-17.

References on Regulatory Compliance & Enforcement in Fisheries

Descriptive

Sutinen, J. 1994. Summary and Conclusion of the Workshop on Enforcement Measures, in Fisheries Enforcement Issues, Organization for Economic Co-operation and Development: 7-16.

Sutinen, J. G. 1987. ‘Enforcement of the MFMCA: An Economist's Perspective,’ Marine Fisheries Review, 49(3):36-43.

Sutinen, J. G. and T. M. Hennessey (eds.), 1987. Fisheries Law Enforcement: Programs, Problems and Evaluation, Marine Technical Report 93, University of Rhode Island, Kingston, RI.

Sutinen, J. G. and T. M. Hennessey. 1986. ‘Enforcement: The Neglected Element in Fisheries Management.’ E. Miles, R. Pealy and R. Stokes (eds.), Natural Resource Policy and Management: Essays in Honor of James A. Crutchfield. Seattle: University of Washington Press.

Wang, S. and A. Rosenberg. 1997. ‘Thalassorama: US New England Groundfish Management Under the Magnuson-Stevens Fishery Conservation and Management Act,’ Marine Resource Economics 12: 361-66.

Theory

Becker, Gary. 1968. ‘Crime and Punishment: An Economic Approach,’ J. Political Economy 76(2): 169-217.

Milliman, Scot. R. 1986. ‘Optimal Fishery Management in the Presence of Illegal Activity’. J. Environ. Econ. and Manage. 13(4):363-381.

Sutinen, J. G. 1993. "Morality and Fairness, and Their Role in Fishery Regulation," in Proceedings of the IV Annual Conference of The European Association of Fisheries Economists, M. Spagnolo (ed.), Salerno, Italy; pp 7-15.

Sutinen, J.G. 1993 ‘Recreational and Commercial Fisheries Allocation with Costly Enforcement.’ Amer. J. Agricultural Econ. 75(5): 1183-1187.

Sutinen, J. G. and P. Andersen. 1985. ‘The Economics of Fisheries Law Enforcement.’ Land Economics, 6l(4):387-397.

Tyler, T. 1990. Why People Obey the Law. New Haven & London: Yale University Press, 273p.

Evidence

Bean, C. 1990. An Economic Analysis of Compliance and Enforcement in the Quahaug Fishery of Narragansett Bay, unpublished Masters thesis, University of Rhode Island.

Gauvin, John R. 1988. An Econometric Estimation of Compliance Behavior in the Massachusetts Inshore Lobster Fishery, an unpublished M.S. thesis, Department of Resource Economics, University of Rhode Island.

IDA. 1999. Fisheries Law Enforcement: Assessment of Deterrence. IDA Document D-2381. Institute for Defense Analysis, Alexandria, VA.

Sutinen, J. G. and J. R. Gauvin. 1988. A Study of Law Enforcement and Compliance in the Commercial Inshore Lobster Fishery of Massachusetts. Volumes I and II. An unpublished Report to the Environmental Enforcement Division, State of Massachusetts.

Policy Analysis, Prescriptions

Sutinen, J. G. 1996. Fisheries Compliance and Management: Assessing Performance. Australian Fisheries Management Authority, Canberra, ACT (August).


Results of Consolidation Modeling

We developed a model to simulate the consequences for net income and cost savings that may result from consolidation of two licenses, each with an initial allocation of 800 traps. One license acquires the other and, as a result, is able to fish 1200 traps.

The estimates are for one year in which, before consolidation, each operator fished approximately 150 days, operated with a sternman, and faced an average price of $3.60. The net income that we estimate is not net of the cost of capital. In other words, costs such as mortgage payments have not been accounted for in our estimates of net income.

We considered eight (8) possible scenarios:

Scenario

Description

1

Base Case: consolidation only (to one 1200 trap operation)

2

Haul rate increase of 50 traps/day

3

Days fished increase of 10%

4

Haul rate & days fished increase

5

Catch per trap haul increase of 10%

6

CPTH & haul rate increases

7

CPTH & days fished increases

8

CPTH, haul rate & days fished increases

The first four scenarios assume that resource abundance does not change; and the last four scenarios assume that abundance increases such that there is a 10% increase in the catch-per-trap-haul (CPTH). The base case of consolidation only assumes that there is no change in either the number of traps hauled per day, or the number of days fished. The next three scenarios increase each of these separately and in combination to estimate the potential economic outcomes.

The chart below shows the results of consolidation under 8 scenarios. In scenario 4, where both the haul rate and days fished increase – a most likely response by producers - there is a reasonably strong incentive for consolidation. The net income after consolidation is 33% greater than the joint net income of the two lobster producers before consolidation. There clearly is an incentive for one producer to acquire the license of the other. The increase in net income would be shared between the two parties who have consolidated their licenses. The seller would receive some share of these net income and the buyer would receive the remaining share – determined by the price of license when sold by one operator to the other.

In scenario 8, where resource abundance increases, and the producer increases both his haul rate and days fished, net income is projected to increase by about 75%. (As noted in the text, a 10% increase in catch-per-trap-haul may not occur if trap saturation exists).

In addition to improving producers’ net incomes, there are cost savings result from the labor and capital that are released from one of the lobster operations. For example, the vessel may be sold and the captain’s labor services transferred either to another fishery or the next best use of this time (which may be retirement).


 


Chart showing the consequences for net income of consolidation:



[1] We followed the same methodology that was used to evaluate fisheries management experiences in the member countries of the Organization of Economic Cooperation and Development (OECD 1997) and explained in Sutinen (1999).

[2] See Gates (2000) for a technical analysis of such responses in a lobster fishery.

[3] See Dyer and Poggie (2000) for a discussion of cultural and other forms of capital in New England fishing communities.

[4] See Sissenwine and Rosenberg (1993), Hennessey and Healey (2000), Sutinen and Upton (2000), and Sissenwine and Mace (2001).

[5] Enforcement officials commonly state that enforcement cannot succeed without fishermen’s widespread support of the management program (OECD 1994). Published studies on the determinants of compliance in fisheries include Sutinen, Rieser and Gauvin (1990), Furlong (1991), Kuperan and Sutinen (1998), and Sutinen and Kuperan (1999).