Pesticide
Profile - Chlorpyrifos
Quick Facts:
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Chemical name: O,O-diethyl O-3,5,6-trichloro-2-pyridyl
phosphorothioate
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Trade names: Brodan, Detmol UA, Dowco 179, Dursban, Empire,
Eradex, Lorsban, Paqeant, Piridane, Stipend
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Pesticide type: insecticide
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Class: organophosphate
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Mechanism of action: cholinesterase inhibitor
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Usage patterns: Approximately 24 million pounds were
used annually in 1999 in the U.S., making chlorpyrifos
on of the most commonly used pesticides. The EPA's decision
to cancel most of the household uses of chlorpyrifos has
reduced usage by half. Agricultural uses on orchards and
row crops persist.
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Regulatory status: US EPA announced a drastic cancellation
of most household-use products in June 2000, based on
human health risks. The principal manufacturer of chlorpyrifos,
Dow Chemical, will cut production by approximately 12
million pounds.
Chemical Structure

Background
Chlorpyrifos, a broad-spectrum organophosphate
insecticide first registered for use in 1965, is one of the
top five residential pesticides in use in the U.S. Registered
uses include a wide variety of food crops, turf and ornamental,
and greenhouse. An estimated 70% of urban usage is as a termiticide.
The US EPA determined in June of 2000 that
chlorpyrifos, common trade name Dursban, was sufficiently
hazardous to human health as to warrant cancellation of nearly
all the household-use products. Because of its extensive use,
chlorpyrifos metabolites have been found in the urine 82%
of adults sampled from the National Health and Nutrition Examination
Survey, while the Minnesota Children's exposure Study found
that 92% of 89 children evaluated had measurable urinary concentrations
of 3,5,6-TCP, the primary urinary metabolite of chlorpyrifos.
Environmental Effects
Fate
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Persistence: Chlorpyrifos is moderately persistent in
soils. The half-life is usually between 11 and 180 days
but can range from 2 weeks to over a year, depending on
soil type, climate and other conditions. In water at pH
7.0 and 25 degrees Celsius the half-life was 35-78 days
in one study. Residues persist on plants from 10 to 14
days, and there is data that indicates that chlorpyrifos
may accumulate in some crops.
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Solubility: slightly soluble in water at 2.0 mg / L.
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Bioaccumulation: Chlorpyrifos has the potential to bioaccumulate.
It has been found to accumulate in the fat tissue of rats
in one study, in the wing fat tissue of 800 hunter- killed
northern bobwhite in a 1989 study, and in the tissues
of fulvous whistling ducks collected in Florida. Bioconcentration
factors in fish studies have been documented at values
of 58 to 5100.
Ecotoxicity
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Chlorpyrifos is very highly toxic to freshwater fish,
aquatic invertebrates, and estuarine and marine organisms.
Chlorpyrifos accumulates in the tissues of aquatic organisms.
Chlorpyrifos binds tightly to soil particles and is relatively
insoluble in water. It persists in the sediments of aquatic
habitats and is hazardous to benthic invertebrates and
other bottom feeders. Numerous fish kills have been reported.
After residential use of Dursban, approximately 500 bream
were found dead in a Georgia pond where a swimming pool
had backwashed in to the pond. Commercial use of chlorpyrifos
to treat pine seedlings resulted in fish kills in a Saline
River watershed in Arkansas. The kills occurred years
after application and included crappie, bass, bullhead,
catfish and spotted suckers. Most of the kills occurred
after heavy rains. After use for termite eradication,
about 2000 bluegill were killed after Dursban had been
unknowingly injected into an underground water supply,
which discharged into a lake.
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Chlorpyrifos is highly toxic to honeybees and is a hazard
to pollinators.
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Chlorpyrifos can be very highly toxic to birds.
common grackle LD50
5.62 mg / kg
rock dove LD 50
10.0 mg / kg
red-winged blackbird LD 50
13.1 mg / kg
sandhill crane LD 50
25-50 mg / kg
Studies that examined the effects
of temperature combined with exposure to chlorpyrifos
showed increased mortality and increased cholinesterase
inhibition with colder temperatures. This study was conducted
using northern bobwhite. The study indicates that temperature
stresses increase the sensitivity of birds to chlorpyrifos
by about two fold.
The EPA required chronic avian reproduction
studies because chlorpyrifos is persistent, bioaccumulates,
and has multiple applications in certain scenarios.
Reproductive studies show that chlorpyrifos administered
at sub acute levels to mallards reduces clutch size and
the number of surviving ducklings.
Incidents
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Between the years of 1992-1994, twenty-six red-tailed
hawks, one Cooper's hawk, and one barn owl were killed
in Central California as a result of agricultural spraying
with chlorpyrifos. These kills were reported to the Ecological
Incident Information System (EIIS), which is compiled
by the EPA. Many of the incidents involved more than one
bird, and approximately half of the dead birds were tested
in a laboratory and found to be positive for chlorpyrifos
exposure.
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Over eighty incidents of fish kills have been reported
to the EIIS from 1992 through 1999, involving millions
of fish and other aquatic creatures. Fish species killed
include darters, gar, bream, trout, bass, sunfish and
catfish.
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Use on a Florida ranch in 1988 resulted in a kill involving
many species of animals over a broad taxonomic range:
427 Florida soft-shelled turtles, 27 banded water snakes,
American alligators, wood storks, white ibis, 75 bowfin,
1200 Seminole killifish, and 142 unidentified birds, as
well as many other species.
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One hundred American robins were killed in Florida after
chlorpyrifos use on a golf course in 1996; seventy-eight
Canada geese were killed after chlorpyrifos use on a golf
course in Suffolk, New York in 1974.
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Many incidents of American robin kills after chlorpyrifos
use on residential lawns have been reported from many
areas of the country, included one kill in Citrus County,
Florida which involved sixty robins on one residential
lawn. A chlorpyrifos-impregnated flea collar contaminated
a birdbath and killed eighteen cedar waxwings in Grant,
Wisconsin in 1993.
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