Marine reserves (no-take zones) are widely recommended as conservation and
fishery management tools. One potential benefit of marine reserves is that
they can reduce fishing mortality. This can lead to increases in the abunda
nce of spawners, providing insurance against recruitment failure and mainta
ining or enhancing yields in fished areas. This paper considers the factors
that influence recovery following marine reserve protection, describes pat
terns of recovery in numbers and biomass, and suggests how recovery rates c
an be predicted. Population recovery is determined by initial population si
ze, the intrinsic rate of population increase r, and the degree of compensa
tion (increases in recruits per spawner as spawner abundance falls) or depe
nsation (lower than expected recruitment at low abundance, Allee effect) in
the spawner-recruit relationship. Within a reserve, theoretical recovery r
ates are further modified by metapopulation structure and the success of in
dividual recruitment events. Recovery also depends on the extent of reducti
ons in fishing mortality (F) as determined by the relationship between patt
erns of movement, migration, and density-dependent habitat use (buffer effe
ct) in relation to the size, shape and location of the reserve. The effects
of reductions in F on population abundance have been calculated using a va
riety of models that incorporate transfer rates between the reserve and fis
hed areas, fishing mortality outside the reserve and life history parameter
s of the population. These models give useful indications of increases in p
roduction and biomass (as yield per recruit and spawners per recruit respec
tively) due to protection, but do not address recruitment. Many reserves ar
e very small in relation to the geographical range of fish or invertebrate
populations. In these reserves it may be impossible to distinguish recovery
due to population growth from that due to redistribution. Mean rates of re
covery can be predicted from r, but the methods are data intensive. This is
ironic when marine reserves are often favoured for management or conservat
ion in data-poor situations where conventional stock assessment is impossib
le. In these data-poor situations, it may be possible to predict recovery r
ates from very low population sizes by using maximum body size or age at ma
turity as simple correlates of the intrinsic rate of natural increase.