Where It Comes From
Atrazine was developed by Syngenta (formerly Ciba-Geigy) in the late 1950s and registered in the US in 1959 [1]. It quickly became indispensable to corn farming because it effectively controls broadleaf and grass weeds and is cheap. Today, about 80 million pounds are applied annually in the US, primarily to corn in the Midwest. Atrazine is banned in the European Union due to its persistent groundwater contamination — it has appeared in European groundwater at levels exceeding EU standards — but remains legal in the US despite similar contamination patterns [2]. The research that most dramatically illustrated atrazine's endocrine effects came from UC Berkeley biologist Tyrone Hayes, who showed that male frogs exposed to concentrations as low as 0.1 ppb — well below the US drinking water standard of 3 ppb — were chemically feminized: they produced eggs in their testes and had suppressed testosterone. Syngenta's aggressive efforts to discredit Hayes' research were later documented in a Senate Environment Committee investigation [3].
How You Are Exposed
Drinking water in the Midwest is the most significant exposure route: atrazine runs off cornfields into streams, rivers, and aquifers after spring planting rains [1]. USGS surveys show atrazine in more than 90% of corn-belt stream samples during spring planting season. Municipal water systems in the Midwest treat for atrazine, but rural residents on private wells may have unmonitored levels. Atrazine-contaminated groundwater affects an estimated 7.6 million Americans according to USDA estimates [2]. Food exposure occurs through residues on crops (corn, sorghum) and through meat and dairy from animals in atrazine-using regions, though food residues are generally lower than water residues. Occupational exposure for farmers and applicators occurs through inhalation and dermal contact during application [3].
Why It Matters
Atrazine's primary mode of action relevant to human health is aromatase induction — it activates the enzyme that converts androgens (male hormones) into estrogens [1]. This hormonal interference is most damaging during fetal development and puberty, when hormone-directed tissue development is occurring. Animal studies show feminization of male offspring, reduced sperm quality, earlier puberty in females, and suppressed immune function [2]. Human epidemiological evidence links atrazine exposure (measured by urinary metabolites or proximity to high-use areas) to birth defects (particularly gastroschisis and choanal atresia), small-for-gestational-age births, early puberty in girls, and hormonal disruption. A 2011 EPA technical review noted the science on reproductive effects was concerning but stopped short of restricting use [3].
Who Is at Risk
Pregnant women living in the rural Midwest and drinking private well water or unfiltered surface water during the April–July application season face the highest exposures [1]. Infants whose formula is prepared with atrazine-contaminated water receive the highest doses per body weight. Farm applicators and farmers who handle atrazine concentrate during mixing and loading operations have significant skin and inhalation exposure [2]. Communities downstream from major corn-growing areas on the Mississippi, Illinois, and Ohio rivers have elevated water exposures. People who garden or live adjacent to corn or sorghum fields in areas of regular atrazine application may have soil and air exposure during application.
How to Lower Your Exposure
Install a reverse-osmosis or activated-carbon block filter certified for atrazine on your kitchen tap if you live in the Midwest and use private well or surface water [1]. The EPA drinking water maximum contaminant level is 3 ppb, but the EWG recommends treating water at any detectable level for infants and pregnant women. Test your well water in spring (April–June) when atrazine runoff peaks — county extension offices often facilitate affordable testing [2]. Choose organic corn products (popcorn, corn tortillas, cornmeal) to avoid atrazine residues. During application season near agricultural areas, keep windows closed on windy days and avoid outdoor exercise downwind of fields. Support your local water utility's disclosure of atrazine levels — utilities that draw from the Mississippi River system should report seasonal peak concentrations [3].
References
- [1]Hayes T, et al. Atrazine induces complete feminization and chemical castration in male African clawed frogs. Proc Natl Acad Sci. 2010;107(10):4612-7. https://doi.org/10.1073/pnas.0909519107
- [2]Sass JB, Colangelo A. European Union bans atrazine, while the United States negotiates continued use. Int J Occup Environ Health. 2006;12(3):260-7. https://doi.org/10.1179/oeh.2006.12.3.260
- [3]Chevrier C, et al. Drinking water exposure to atrazine and birth defects. Occup Environ Med. 2011;68(12):905-12. https://doi.org/10.1136/oem.2010.062257
- [4]EPA. Atrazine. https://www.epa.gov/ingredients-used-pesticide-products/atrazine
Recovery & Clinical Information
Body Half-Life
Atrazine is metabolized relatively quickly in the body — blood half-life is approximately 1-3 days [1]. Urinary chlorotriazine metabolites (primarily atrazine mercapturic acid, ATMA) are detectable for several days after exposure [2].
Testing & Biomarkers
Urinary atrazine mercapturic acid (ATMA) is the standard biomarker for recent agricultural or drinking water atrazine exposure [1]. Testing available through specialty environmental health labs; not standard in routine clinical care but available to occupational health programs [2]. EPA's maximum contaminant level for atrazine in drinking water is 3 µg/L; routine water utility testing is required and results are published in annual Consumer Confidence Reports [1].
Interventions
Switch to filtered drinking water if you live in an agricultural region where atrazine is used — activated carbon (GAC) and reverse osmosis both effectively remove atrazine from drinking water [1]. Buy organic corn, sugar, and sorghum products — the crops most heavily treated with atrazine [2]. For occupational agricultural exposures, PPE during application and handling, and washing clothing separately [1].
Recovery Timeline
Urinary ATMA normalizes within days of stopping atrazine exposure [1]. Atrazine's endocrine disrupting effects (thyroid, estrogen) are dose-dependent and should diminish as ongoing exposure is eliminated [2]. The reproductive effects from chronic low-level atrazine exposure (irregular menstrual cycles, thyroid disruption) may improve over months after sustained reduction in dietary and water exposure [1].
Recovery References
- [1]Sass JB, Colangelo A (2006). European Union bans atrazine, while the United States negotiates continued use. International Journal of Occupational and Environmental Health. https://doi.org/10.1179/oeh.2006.12.3.260
- [2]ATSDR (2003). Toxicological Profile for Atrazine. https://www.atsdr.cdc.gov/toxprofiles/tp153.pdf