Pesticide
Profile - Endosulfan
Quick Facts:
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Chemical name: 6,7,8,9,10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-6,9-methano-
2,4,3-benzadioxathiepin 3-oxide
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Trade names: Fan, Thiodan, Afidanil, Cekulfan, Endocel,
Endodhan, Endosol, Endostar, Thionex, Cyclodan, Thimul,
Thionex, Phaser, Thiodan, Devisulfan, Insectophene, Hoe
2671, Malix
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Pesticide Type: insecticide, acaricide
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Class: organochlorine (chlorinated hydrocarbon)
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Use: cotton, apples, pecans, various row vegetables,
grapes, pears, peaches
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Endosulfan is mutagenic in studies on yeast and
bacteria.
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Endosulfan is a suspected endocrine disrupter.
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Endosulfan belongs to the same class of pesticides as
DDT; it is highly persistent in the environment and has
a high potential for bioaccumulation and biomagnification
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Very little is known about the toxicity and fate of endosulfan
degradates.
Chemical Structure

Background
Endosulfan belongs to the class of pesticides
known as organochlorines. These compounds are characterized
by their high level of persistence in the environment, and
their ability to bioaccumulate in animal tissue. Organochlorines,
also known as chlorinated hydrocarbons, are insoluble in water
and are usually highly soluble in fat. The chemicals absorb
and remain in the fat cells of exposed animals. Effects of
the organochlorines are sometimes greatest at the highest
levels of the food chain, when large numbers of contaminated
prey are consumed by top-level predators. This process, biomagnification,
is what occurred when DDT, another organochlorine, was used
extensively in the U.S. in the early 1970's. Peregrine falcons
and bald eagles consumed fish exposed to DDT and accumulated
toxic levels of the pesticide, resulting in reproductive failure.
Endosulfan is a Persistent Organic Pollutant
(POP). It persists in the environment for extended periods
of time, increasing the exposure risk of many non-target animals.
It has been detected in wells and surface waters, most likely
due to run-off or drift during application. It volatilizes
easily after application and is transported to areas distant
from the application site. It has been detected in ice and
snow samples of the arctic.
Environmental Effects
Fate
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Persistence: endosulfan is moderately persistent in soils
with an average half-life of 50 days. However, under certain
conditions, endosulfan can be very long-lived in soils.
The EPA has reported a half-life of 200 days but did not
state the conditions under which the data were derived.
In water, endosulfan has a high potential for contamination
of waterways near the site of application. It is one of
the most commonly detected pesticides in U.S. water. A
study in 1982 found 24 of 154 wells in Ohio contaminated
with endosulfan. Endosulfan is extremely persistent in
aquatic systems under acidic conditions. Endosulfan has
been detected in arctic ice and snow samples, attesting
to its high degree of persistence. Published studies examining
the toxicity and fate of endosulfan break down products
are not available.
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Solubility: endosulfan is insoluble in water but is soluble
in toluene and hexane.
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Soil mobility: Endosulfan is moderately mobile in soils,
and will adhere to soil particles to a degree that contamination
of surface waters due to runoff is a serious risk.
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Bioaccumulation: Endosulfan has a high potential for
bioaccumulation. In studies that examined bioconcentration
in fish, the bioconcentration factor was 11,538X. Residues
of endosulfan have been detected in mussels, oysters and
fish, in the field.
Ecotoxicity
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Endosulfan is very highly toxic to aquatic fauna. Both
vertebrate (fish, amphibians), and invertebrates (mollusks,
insects, gastropods) are susceptible with LC 50's in the
range of 1 ppb for many species.
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Endosulfan is highly toxic to mammals. The LD 50 for
a rat is 18 mg/kg, for a cat, the LD 50 is 2 mg/kg. It
is toxic through oral and dermal routes of exposure.
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Endosulfan is highly toxic to birds. The LD 50 for mallards
is 12 mg/kg. Studies examining the chronic effects of
endosulfan and its degradates are incomplete. Given the
persistence of endosulfan in the environment and its potential
for bioaccumulation, it is reasonable to expect chronic
effects to birds at sub-lethal doses.
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