Paralytic Shellfish
Poisoning Toxin

INTRODUCTION:
A number
of genera of marine phytoplankton produce an array of chemically similar
neurotoxins responsible for PSP1.
Neurotoxins are so-named because they disrupt nerve impulses. These
toxins act together to produce PSP. Symptoms may progress from numbness
and tingling of lips, and loss of muscular coordination, to respiratory
arrest and, ultimately, death. There is no known antidote. In extreme
cases, survival depends on immediate availability of life-support
systems. Death results in about 15 percent of cases worldwide2
. Action level for PSP at no more than 80 µg of PSP toxin in 100 g
of shellfish tissue3.
The Alexandrium catenella toxins are extremely potent nerve poisons.
In fact, as little as one milligram can be enough to kill an adult.
Bivalve shellfish concentrate biotoxins when they filter toxic phytoplankton
out of the water
while feeding. The shellfish do not appear to be affected by the toxin.
PSP toxin accumulates in marine animals that feed either directly
on toxic phytoplankton or on consumers of toxic
phytoplankton. These consumers include zooplankton, bivalve shellfish
(oysters, mussels,
clams, etc.), predatory marine snails (moon snails and whelks), crabs,
fish, birds and marine
mammals4. Mass mortalities
among other shellfish-eating animals, including
birds, fur seals, foxes, sea otters5,
and humpback whales have been
traced to PSP6. People
are poisoned when they eat shellfish or other marine life that contain
excessive levels of PSP toxin.
Phytoplankton
Ecology and Biotoxins
Phytoplankton
are one-celled marine plants that can conduct photosynthesis. Photosynthesis
enables plants to use the energy of the sun to make food from carbon
dioxide and nutrients taken from the water. Oxygen is produced as
a by-product. Phytoplankton and other photosynthesizers are the basic
source of energy for all components of the marine food web.
During wintertime rain storms, rivers and stormwater runoff carry
nutrients into water from nearby uplands and watersheds. Strong winds
mix the freshwater with nutrient-rich water coming in from the open
sea. The dim sunlight limits growth. Phytoplankton is continually
cycled from the surface to the dimly lit depths and back up again,
awaiting the arrival of favorable conditions for growth.
In early spring, strong winds subside, and the sun warms the water's
surface. The water column stabilizes and vertical mixing stops. A
second influx of nutrients occurs when summer snowmelt increases flow
to the water. The abundant dissolved nutrients in a stable water column
lead to blooms of many phytoplankton species in sunlit surface waters.
Blooms can be so dense that the phytoplankton colors the water. The
condition is sometimes called a red tide. However, the term is misleading
because the colors (produced by photosynthetic pigments) may range
from brown to orange to purple. Blooms are sometimes associated with
a group of phytoplankton termed dinoflagellates. About 60 dinoflagellate
species (of over 2,000) produce biotoxins. Alexandrium catenella,
which causes PSP , is a dinoflagellate. It is important to note that
PSP may reach dangerous levels in shellfish long before the density
of Alexandrium catenella becomes numerous enough to change colore
of the water.
A brief description of Alexandrium catenella, the poison-producing
organism, will help to explain the seasonal occurrence of shellfish
containing PSP toxins and the differences in timing of toxicity in
different shellfish. Alexandrium catenella is a microscopic singlecelled
type of plankton. Plankton are plants and animals that are carried
along by the currents.
Alexandrium catenella belongs to a group called dinoflagellates, which
have both plant and animal characteristics, can manufacture their
own food, and can swim. Each cell of A. catenella can live independently,
but during periods of rapid growth and division, the cells remain
attached to each other in a chain-hence the name catenella or "little
chain." Each cell is equipped with two tiny whips used in swimming.
At times, some of the swimming cells drop their whips and form non-swimming,
heavy-walled resting cells or cysts. These settle to the bottom and
can lie dormant in the bottom sediment through low winter temperatures.
Many of the cysts are eaten by animals, including bivalve shellfish,
or become buried. Some germinate when environmental conditions are
favorable, giving rise to another population of swimming cells.
Two whip-like flagella enable dinoflagellates to move vertically in
the water column. By mid to late summer, surface waters are frequently
depleted of nutrients and many species of phytoplankton die back.
But dinoflagellates journey to deeper water where nutrients remain
plentiful. They return to the sunlit surface to carry on photosynthesis.
Vertical migration may give dinoflagellates an advantage over other
phytoplankton species. As a result, dinoflagellate blooms often extend
into late autumn. By that time, falling water temperatures and the
onset of wind-induced vertical mixing lead to a breakdown of the stratification
of the water column, and sunlight becomes too dim to continue production.
Under these conditions dinoflagellates, such as Alexandrium catenella,
may form resting cysts that settle to the bottom to await the return
of favorable growth conditions7.
A resting cyst may be ten times more toxic than its free-swimming
form8.
METHOD:
-
Wash bivalve clams with tap water
-
Separate
inside tissue from the shell without disturbing it much
-
These
tissue is grounded with a blender
-
Weight
27g of the sample into beaker
-
Add
20ml of 0.1M HCI onto it and mix well
-
Adjust
pH to 2.5
-
Mixture
is heated to boil and is let to smear for 5 minutes
-
Cool
down to room temprature
-
Adjust
pH to again 2.5 (use 5m HCI to decrease and 0.1M NaOH to increase
the pH )
-
Put
the mixture into a graduate cylinder and add distilled H2O up to
54ml is reached
-
Mixed
and put 50 ml of the mixture into centrifuge bottles and centrifugate
3000 rpm for 5 minutes
-
Upper
liquid phase is taken and inject 1ml intaperitonally to the 3 mice
weighting about 21g each./
Alternative
method is fish bioassay using 3 Lepistas fish and introducing
the material into the water of fish and monitoring them
-
Mice
are monitored for 1 hour, if they do not die within 1 hour, if they
do not die within 1 hour, it is decided that the amound of PSP toxin
is not dangerous to human health.
-
If
one of the three mice dies and others two are still living within
this one hour period, the result of the test still accepted to be
negative due to the fact that this mice death with other reasons
than PSP toxin, such as distruption of body.
-
If
two or all of the three mice dies during this period, the result
is positive and the shellfish consumption is not safe for health.
DISCUSSION:
None:
PSP level was less than 80 µg per 100 grams of shellfish tissue
;
Low: PSP level ranged from 80-499 µg per 100 grams of shellfish
tissue;
Moderate: PSP level ranged from 500-999 µg per 100 grams of
shellfish tissue;
High: PSP level was greater than 1000 µg per 100 grams of shellfish
tissue.
1
Boczar, B.A., M.K. Beitler, J. Liston, J.J. Sullivan, and R.A. Cattolico.
1988. Paralytic shellfish toxins in Protogonylaulax tamarensis and Protogonyaulax
catenella in axenic culture. Plant Physiology 88: 1285-1290.
2 Nishitani, L., K.K. Chew, and T. King, 1994. Gathering safe
shellfish in Washington: avoiding paralytic shellfish poisoning. WSG-AS
94-01, Washington Sea Grant Program, Seattle WA. pp. 8.
3 The U.S. Food and Drug Administration
4 Matter, A., 1994. Paralytic shellfish poisoning: toxin accumulation
in the marine food web, with emphasis on predatory snails. EPA 910/R-94-005.
Puget Sound Research Program, U.S. EPA, Region 10, Seattle WA. pp. 44.
5 Kvitek, R.G., and M.K. Beitler, 1988. A case for sequestering
of paralytic shellfish toxins as a chemical defense. Journal of Shellfish
Research 7(4): 629-636.
6 Geraci, J.R., D.M. Anderson, R.J. Timperi, D.J. St. Aubin,
G.A. Early, J.H. Prescott, and C.A. Mayo (1989). Humpback whales (Megaptera
novaeangliae) fatally poisoned by dinoflagellate toxin. Canadian Journal
of Fisheries and Aquatic Sciences. 46: 1895-1898.
7 Anderson, D.M. 1980. Effects of temperature conditioning on
development and germination of Gonyaulax tamarensis (Dinophyceae) hypnozygotes.
Journal of Phycology 16: 166-172.
8 Dale, B., C. M. Yentch, and J. W. Hurst (1978). Toxicity in
resting cysts of the red-tide
dinoflagellate Gonyaulax excavata from deeper water coastal sediments.
Science 20: 1223-
1225.
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