Interactions between poaching and management policy affect marine reserves as conservation tools

To explore the effects of poaching within marine reserve boundaries under three different management policies this analysis uses a simple age-structured reserve model based on yield maximization or reproductive thresholds of Black rockfish (Sebastes melanops). Departures from the traditional assumptions of full compliance to reserve boundaries alter the conclusions of prior modeling work that demonstrate yield equivalence to no-reserve effort control management and augmented reproductive benefits when small reserves are implemented. By degrading the recruitment subsidization effect to nonreserve areas from protected reserve populations, poaching resulted in negative externalities for compliant fishermen in open areas in terms of yield and degraded the reproductive output and age-structure of the system. All three policies required effort reduction in open areas as a response to poaching in reserves. The strength of the impacts from poaching varied with policy choice and harvest intensity in the reserve, where at the highest level of poaching modeled here (15% annual exploitation rate of the vulnerable reserve population) biological and fishery benefits of implementing reserves were totally negated. Under the assumptions of this model, a policy managing for a reproductive threshold that excludes the reserve population is the precautionary choice if poaching is likely. The results of this exercise emphasize the importance of garnering compliance to reserve boundaries from resource-users for spatial closures to be successful ocean management tools.

[1]  F. David,et al.  On the Dynamics of Exploited Fish Populations , 1959, Fish & Fisheries Series.

[2]  S. Sogard,et al.  MATERNAL AGE AS A DETERMINANT OF LARVAL GROWTH AND SURVIVAL IN A MARINE FISH, SEBASTES MELANOPS , 2004 .

[3]  Julia K. Parrish,et al.  Limiting abuse: marine protected areas, a limited solution , 1999 .

[4]  Jonathan A. Anticamara,et al.  Effectiveness of five small Philippines’ coral reef reserves for fish populations depends on site-specific factors, particularly enforcement history , 2007 .

[5]  Peter Barnes,et al.  Benthic Habitats and the Effects of Fishing , 2005 .

[6]  J. Sutinen,et al.  Measuring and explaining noncompliance in federally managed fisheries , 1990 .

[7]  K. Kuperan,et al.  A socio‐economic theory of regulatory compliance , 1999 .

[8]  R. Grafton,et al.  The Bioeconomics of Marine Reserves: A Selected Review with Policy Implications , 2005 .

[9]  Hugh P. Possingham,et al.  Population models for marine reserve design: A retrospective and prospective synthesis , 2003 .

[10]  M. Hauck,et al.  A case study of abalone poaching in South Africa and its impact on fisheries management , 1999 .

[11]  J. Castilla,et al.  The management of fisheries and marine ecosystems , 1997 .

[12]  L. Anderson Enforcement Issues in Selecting Fisheries Management Policy , 1989, Marine Resource Economics.

[13]  P. Mace a new role for MSY in single-species and ecosystem approaches to fisheries stock assessment and management , 2001 .

[14]  Surveillance and Poaching on Inshore Reefs of the Great Barrier Reef Marine Park , 2004 .

[15]  D. Hart When do marine reserves increase fishery yield , 2006 .

[16]  J. Kritzer,et al.  Effects of Noncompliance on the Success of Alternative Designs of Marine Protected‐Area Networks for Conservation and Fisheries Management , 2004 .

[17]  T. McClanahan Is there a future for coral reef parks in poor tropical countries? , 1999, Coral Reefs.

[18]  L. Botsford,et al.  Equivalence in yield from marine reserves and traditional fisheries management , 1999, Science.

[19]  M. Love,et al.  Fisheries Sustainability via Protection of Age Structure and Spatial Distribution of Fish Populations , 2004 .

[20]  Serge M. Garcia,et al.  When can marine reserves improve fisheries management , 2004 .

[21]  Jane Lubchenco,et al.  MARINE RESERVES ARE NECESSARY BUT NOT SUFFICIENT FOR MARINE CONSERVATION , 1998 .

[22]  Colin W. Clark,et al.  Subsidies, buybacks, and sustainable fisheries , 2005 .

[23]  Tom Polacheck,et al.  YEAR AROUND CLOSED AREAS AS A MANAGEMENT TOOL , 1990 .

[24]  S. Berkeley,et al.  Maturity, ovarian cycle, fecundity, and age-specific parturition of black rockfish (Sebastes melanops) , 2004 .

[25]  Ray Hilborn,et al.  Equilibrium Yields and Yield Isopleths from a General Age-Structured Model of Harvested Populations , 1985 .

[26]  R. Hilborn,et al.  Integrating marine protected areas with catch regulation , 2006 .

[27]  C. Walters,et al.  Uncertainty, resource exploitation, and conservation: lessons from history. , 1993, Science.

[28]  Colin Clark,et al.  Marine Reserves: from Beverton and Holt to the Present , 1998, Reviews in Fish Biology and Fisheries.

[29]  A. Punt,et al.  Effects of size and fragmentation of marine reserves and fisher infringement on the catch and biomass of coral trout, Plectropomus leopardus, on the Great Barrier Reef, Australia , 2005 .

[30]  M. Love Probably More Than You Want to Know About the Fishes of the Pacific Coast , 1991 .

[31]  J. Sutinen,et al.  Blue Water Crime: Deterrence, Legitimacy, and Compliance in Fisheries , 1998 .