Marine reserves (areas closed to exploitation of marine life) should allow
better resilience to management errors such as overestimation of stocks, in
adequate control of fishing effort, and inaccurate catch statistics. We emp
loyed a detailed population model to explore the use of marine reserves to
protect cod populations from overexploitation. The northern cod of the east
coast of Newfoundland in the 1980s, at low biomass but prior to the major
collapse, was used, as a case study. We asked two questions: Would marine r
eserves have prevented the 1992 collapse, and how would reserves compare wi
th other management measures? The model is age- and spatially-structured an
d includes a recruitment function (Beverton and Holt type). Migrations were
simulated by inclusion of target cells (attraction sites), which were spec
ific for each age and month of the year. Random movements around target cel
ls determined how fish spread to form a spatial distribution that moved alo
ng the seasonal trajectory defined by the target cells. Fishing was calibra
ted from historical data on temporal and spatial distribution of effort for
three types of gears (trawl, gill net, trap). Marine reserves were modeled
alone or in conjunction with temporal closures. For the 1980s low cod biom
ass, if used alone, only large reserves (80% of the fishing grounds) would
have prevented the collapse and allowed the cod stock to rebuild. However;
these very large reserves would have reduced the catch per unit effort on t
he remaining fishing grounds and possibly triggered an increase in investme
nt in gear, defeating the purpose of the reserve. At low cod biomass, reser
ves must be accompanied by a reduction in fishing capacity. When used with
reserves of moderate size (20%), temporal closures to trawls and gill nets
succeeded in preventing a collapse and rebuilding the stock.