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Chlorpyrifos
Beyond Pesticides Rating: Toxic

On June 8, 2000, the U.S. Environmental Protection Agency (EPA) and Dow AgroSciences, reached an agreement to stop the sale of most home, lawn and garden uses for chlorpyrifos because of its health risks to children.

USAGE

Chlorpyrifos (trade names include DursbanTM and LorsbanTM) is one of the most widely used insecticides in the U.S., with 20 to 24 million pounds applied annually, and has been linked to thousands of pesticide poisoning incidents. This Dow AgroSciences, previously DowElanco, product is a broad-spectrum chlorinated organophosphate insecticide.

Chlorpyrifos is registered for the control of cutworms, corn rootworms, cockroaches, grubs, flea beetles, flies, termites, fire ants, mosquitoes, and lice. It is used as an insecticide on grain, cotton, fruit, nut, and vegetable crops, as well as on lawns and ornamental plants. It is also registered for direct use on sheep and turkeys, for horse site treatment, dog kennels, domestic dwellings, farm buildings, storage bins, and commercial establishments.

TOXICITY

Chlorpyrifos is acutely toxic to rats with an LD50 of 135 mg/kg.

Chlorpyrifos poisoning may affect the central nervous system, the cardiovascular system and the respiratory system, as well as irritate the skin and eyes. Acute exposure can result in numbness, tingling, incoordination, dizziness, vomiting, sweating, nausea, stomach cramps, headache, vision disturbances, muscle twitching, drowsiness, anxiety, slurred speech, depression, confusion and in extreme cases, respiratory arrest, unconsciousness, convulsions, and death. Persons with respiratory ailments, recent exposures to cholinesterase inhibitors, cholinesterase impairment, or liver malfunction are at increased risk from exposure to chlorpyrifos. Chlorpyrifos has also been linked to Multiple Chemical Sensitivity.

Chlorpyrifos is linked to delayed peripheral neuropathy (degenerative lesions of sensory, motor, or reflex nerves). Italian researchers published a disturbing report of an acute chlorpyrifos-poisoning episode, resulting in delayed peripheral neuropathy. There are also reports of EEG (brainwave) pattern, sleep pattern and behavioral changes lasting over a year following exposure to organophosphate insecticides.

Organophosphates are cholinesterase inhibitors. They bind irreversibly to the active site of an enzyme essential for normal nerve impulse transmission, acetylcholine esterase (AchE), inactivating the enzyme. A common diagnostic for poisoning is to assay for blood AchE depression. Repeated or prolonged exposure to organophosphates may result in the same effects as acute exposure, including delayed symptoms.

A 1996 study of children exposed to chlorpyrifos in utero found that extensive and unusual patterns of birth defects, including brain, nervous system, eyes, ears, palate, teeth, heart, feet, nipples, and genitalia. Published literature and EPA documents contain reports that identify similarities in defects found in test animals and children exposed to chlorpyrifos.

In 1997, EPA Office of Pesticide Programs', Health Effects Division reported that chlorpyrifos is one of the leading causes of acute insecticide poisoning incidents in the U.S. One U.S. News & World Report investigation, "The stuff in the backyard shed," (November 8, 1999, page 64-68) reports that since 1992, Dow AgroSciences and predecessor manufacturers have sent approximately 7,000 reports of chlorpyrifos-induced reactions to EPA. The agency, according to the report, suspects chlorpyrifos in 17,771 incidents reported to the U.S. Poison Control Centers between 1993 -96.

In 1999, EPA's Office Pesticide Programs, Health Effects Division, reported that four pesticides, phosmet, proetamphos, chlorpyrifos, and dimethoate, had consistently high rankings in being responsible for symptoms, health care facility visits, hospitalizations, and fatal outcomes in adults and children. These four organophosphate pesticides are responsible for 90% of pesticide exposures reported in children under six to the Poison Control Centers around the country from the 1993-1996. The report also stated that "children, under six exposed to organophosphates, were three times more likely to be hospitalized, five times more likely to be admitted for critical care, and four times more likely to have experienced a major medical outcome or death, than if exposed to some other, non organophosphate, pesticide."

In animals, chlorpyrifos transforms to chlorpyrifos-oxon, which is about 3000 times as potent against the nervous system as chlorpyrifos itself.

ECOLOGICAL EFFECTS

There is a wide range of adverse environmental effects linked to chlorpyrifos, include toxicity to beneficial insects, freshwater fish, other aquatic organisms, bird, a variety of plants, soil organisms, and domestic animals. It has been shown to bioaccumulate in fish and synergistically react with other chemicals.
Chlorpyrifos may be toxic to some plants, such as lettuce.

ENVIRONMENTAL FATE

There are few data available on air levels or surface residues following application either as a termiticide or for indoor pest control. The American Conference of Governmental Industrial Hygienists recommends an occupation air level guideline of 200-micrograms/cubic meter (µg/m3) for a forty-hour workweek. The National Academy of Sciences proposed a 10µg/ m3 air level for the general public, while the New York State Department of Health, with a recommendation to use a 100-fold safety factor, would arrive at an air limit of 0.49µg/m3 for children, and 1µg/ m3 for adult exposures.

Work by Fenske et al. found that air levels 24 hours after a proper application were as high as 30µg/ m3 in the infant breathing zone, 60 times EPA's limit. Furthermore, Fenske calculated that infant exposure through inhalation and skin absorption might be more than five times the human threshold for acute effects (No Observable Effect Level). The researchers state that, "Exposures to cholinesterase inhibiting compounds following properly conducted broadcast applications could result in doses at or above the threshold of toxicological response in humans."

In common with most organophosphates, chlorpyrifos has a relatively short biological half-life, roughly 24 hours in blood, and 60 hours in fat (assuming that multiple or continuous exposure does not occur) and it has shown no potential to bioaccumulate in mammals. Its half-life indoors is estimated to be 30 days. Various studies of different treatment methods show chlorpyrifos present up to eight years post application. A 1998 study found that chlorpyrifos accumulated on furniture, toys, pillowcases, and other sorbant surfaces up to two weeks after indoor application.

Chlorpyrifos is sensitive to light, alkaline substances such as bleach, and microbial degradation. Eventually, it degrades completely to carbon dioxide and water. The half-life of chlorpyrifos in water is relatively short, from a few days to two weeks. It adsorbs readily to sediments and organic matter, its half-life in soil is usually between 60 and 120 days, but can range from 2 weeks to over one year, depending on the soil type, climate, and other conditions.
Residues remain on plant surfaces for approximately 10 to 14 days. Data indicate that this insecticide and its soil metabolites can accumulate in certain crops.

The granular formulation of chlorpyrifos has been found to be more persistent and may persist as long as 180 days. The major biological metabolite and environmental breakdown product is 3,5,6-trichloro-2-pyridinol (TCP).

According to an EPA memorandum, groundwater monitoring at a Cape Cod golf course detected TCP in samples. Reports from the USDA Southern Forest Experimental Station note that the termiticide formulation is effective against termites for more than 15 years.

Revised July 2000

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NY State Department of Conservation. 1986. Draft Environmental Impact Statement on Amendments to 6 NYCRR Part 326 Relating to the Restriction of the Pesticides Aldrin, Chlordane, Chlorpyrifos, Dieldrin, and Heptachlor. Bureau of Pesticides Management. Albany, NY.

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U.S. v. George Y. Roggy (D.C. Minn. 1994).