Harmful and toxic algae
Microscopic algae are important food for filter-feeding bivalves
(oysters, mus-sels, scallops and clams) and for the larvae of commercially
important crustaceans and fishes. Proliferation (algal blooms) of this algae
up to a million cells/ l, or cells/ml, is beneficial to aquaculture and wild
fisheries operations. In some situations, however, algal blooms can cause
severe economic losses to aquaculture, fisheries and tourism, and have major
impacts on health and en-vironment. There are 5,000 species of marine
phytoplankton (Sournia et al. 1991). Some 300 species can, at times, occur in
such high density that they discolor the surface of the sea (red tides). Only 40
species have the capacity to produce potent toxins that can find their way to
fish and shellfish and, eventu-ally, to humans.
The first written reference to harmful algal bloom appears in the
Bible (1,000 years B.C). In Exodus 7:20-21 is written that at that time in
Egypt all the waters in the river turned into blood, and all the fish in the
river died, and the river stank, and the Egyptians could not drink the water in
the river. In this case, a non-toxic bloom-forming alga became so densely
concentrated that it gener-ated anoxic conditions resulting in indiscriminate
kills of both fish and inverte-brates. Oxygen depletion developed due to high
respiration by the algae (at night or in dim light during the day), but most
probably, bacterial respiration during decay of the bloom caused it.
One of the first recorded fatal cases of human poisoning after
eating shellfish contaminated with dinoflagellate toxins was in 1793 in Poison
Cove in British Columbia. The seawater became phosphorescent due to
dinoflagellate blooms. The causative alkaloid toxins, now called paralytic
shellfish poisons (PSP) are so potent that about 500 micrograms of toxins,
which can easily accumulate in just one serving of shellfish (100 gram), could
be fatal to humans.
On a global scale, close to 2,000 cases of human poisoning (15%
mortality) through fish or shellfish consumption are reported each year and, if
not con-trolled, the economic damage through reduced local consumption and
reduced export of seafood products can be considerable. Whales and porpoises
can also become victims when they receive toxins through the food chain via
contami-nated zooplankton or fish. Poisoning of manatees by dinoflagellate
brevetoxins contained in salps attached to seagrass, and of pelicans by diatom
domoic acid contained in anchovies have also been reported.
Harmful algal bloom has become apparent only as a result of
increased interest in intensive aquaculture systems for finfish. Some algal
species can seriously damage fish either mechanically or through production of
hemolytic sub- stances. While wild fish stocks have the freedom to swim away
from problem areas, caged fish appears to be extremely vulnerable to such
noxious algal blooms.
In the Philippines, red tide was reported in 1908 in Manila Bay as
due to Peridinium blooms. Thereafter,
minor nontoxic red tide outbreaks became al-most an annual event in Manila Bay,
particularly in the Cavite Area. It was not until June 1983 that the first
outbreak of a toxic red tide caused by Pyrodiniumbahamense
var. compressa occurred in Samar, Central Philippines.
In 1987, the presence of dinoflagellate blooms caused by Pyrodinium baha-mense var was detected
in the coastal waters of Masinloc, Zambales, extendingfrom Subic to Santa Cruz.
Almost simultaneously at that time, the toxic red tide recurred in Samar.
Another case of paralytic shellfish poisoning (PSP) was re-ported on August 19,
1988 in Orion, Bataan, followed by another 28 cases in Limay within a four-day
period.
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