Modelling the effects of Marine Protected Areas (MPAs) on the southern rock lobster (Jasus edwardsii) fishery of Victoria, Australia

Abstract Since 2002, 5.3% of the Victorian coastal waters have been declared as Marine Protected Areas (MPAs). These are aimed at safeguarding important marine habitats and species, significant natural features, and areas of cultural heritage and aesthetic value. However, MPAs impact the fishery for southern rock lobster (Jasus edwardsii), as total allowable catches (TACs) were previously set to allow the biomass to recover to pre‐specified target levels. The model on which assessments and risk analyses are based is extended to include the impact of MPAs. The MPAs and the area open to fishing are modelled as subpopulations with different levels of mortality and consequently different density and population size‐structure. A range for the probability of a lobster moving from a MPA to the fished area from 0 to 15% is considered, based on the results of tagging studies. The reduction of biomass available to the commercial fishery because of the introduction of MPAs is estimated to be 8% and 16% (Western and Eastern Zones) respectively. The results of a risk assessment show that if the current TACs are maintained, the time to increase the biomass available to the commercial fishery by 50% would be delayed 5–9 years in the Western Zone and 1–4 years in the Eastern Zone because of the impact of displaced effort. In contrast, spawning biomass in the Eastern Zone is currently below the agreed limit reference point, and the introduction of MPAs would enhance the rate of recovery, although only marginally initially, faster than the absence of the MPAs.

[1]  R. J. Davidson,et al.  Effects of marine reserve protection on spiny lobster (Jasus edwardsii) abundance and size at Tonga Island Marine Reserve, New Zealand , 2002 .

[2]  G. Edgar,et al.  Short term monitoring of biotic change in Tasmanian marine reserves , 1997 .

[3]  C. Roberts,et al.  Fisheries benefits and optimal design of marine reserves , 1999 .

[4]  R. Lewis Seasonal upwelling along the south-eastern coastline of South Australia , 1981 .

[5]  M. Haddon,et al.  Modelling the effect of introducing MPAS in a commercial fishery: a rock lobster example , 2002 .

[6]  A. Macdiarmid,et al.  Movement patterns of mature spiny lobsters, Jasus edwardsii, from a marine reserve , 2003 .

[7]  J. Brodziak,et al.  Impacts of density-dependent growth and maturation on assessment advice to rebuild depleted U.S. silver hake (Merluccius bilinearis) stocks , 1998 .

[8]  A. Hastings,et al.  PRINCIPLES FOR THE DESIGN OF MARINE RESERVES , 2003 .

[9]  R. Hilborn,et al.  Fisheries stock assessment and decision analysis: the Bayesian approach , 1997, Reviews in Fish Biology and Fisheries.

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

[11]  André E. Punt,et al.  POPULATION MODELLING OF TASMANIAN ROCK LOBSTER, JASUS EDWARDSII, RESOURCES , 1997 .

[12]  D. Scott,et al.  Spiny lobster, Jasus edwardsii, recovery in New Zealand marine reserves , 2000 .

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

[14]  André E. Punt,et al.  Size-structured population modelling and risk assessment of the Victorian southern rock lobster, Jasus edwardsii, fishery , 2001 .

[15]  E. Trippel Age at Maturity as a Stress Indicator in Fisheries , 1995 .

[16]  J. Groeneveld,et al.  Long-distance migration of South African deep-water rock lobster Palinurus gilchristi , 2002 .

[17]  W. K. Hastings,et al.  Monte Carlo Sampling Methods Using Markov Chains and Their Applications , 1970 .

[18]  J. Booth Long-distance movements in Jasus spp. and their role in larval recruitment , 1997 .

[19]  Murdoch K. McAllister,et al.  Modelling the effects of establishing a marine reserve for mobile fish species , 2002 .

[20]  B. Phillips,et al.  Early Life History of Spiny Lobster , 1994 .