Sb. Saila et al., MODELING THE EFFECTS OF DESTRUCTIVE FISHING PRACTICES ON TROPICAL CORAL REEFS, Marine ecology. Progress series, 94(1), 1993, pp. 51-60
A literature review of the use of underwater explosives indicated that
the largest lethal zone for swimbladder fishes is located near the su
rface of the water. Mortality in this zone is due to rupture of the sw
imbladder from negative pressure induced by cavitation of the near-sur
face water volume from a subsurface explosion. Observational studies o
f blast fishing in the Philippines indicated that valuable pelagic spe
cies rather than typical coral reef species were the primary targets.
Empirical data on the extent of various destructive fishing practices
(blast fishing, anchor damage, and use of poisons), as well as coral r
egrowth estimates, provided inputs to a nomographic model of the reef
ecosystem. The model provided time graphs of fish diversity and the am
ount of coral regrowth under various conditions. The results of the si
mulation model studies indicated that the sum of all current destructi
ve practices was sufficient to continue loss of diversity and loss of
live coral cover for about 25 yr before any recovery was expected. On
the other hand a reduction in the rate of destructive fishing to about
30% of the current level would permit continuing slow recovery of bot
h diversity and live coral cover. Available observational information
suggests that this might best be accomplished by attempting to elimina
te the use of poisons (such as cyanide) in reef areas and reducing anc
hor damage in addition to reducing blast fishing in coral areas. The p
robable effects of the latter may have been overemphasized in the past
.