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CAS 1582-09-8

Trifluralin

carcinogenPBTherbicideHAP

Trifluralin is one of the most widely used pre-emergence herbicides in the US — applied to soybeans, cotton, and other field crops — and it is one of the most commonly detected herbicides in sediment and groundwater due to its persistence and volatility.

Where It Comes From

Trifluralin was introduced in 1963 and is a dinitroaniline herbicide used primarily to prevent emergence of annual grasses and broadleaf weeds in soybeans, cotton, and sunflowers [1]. About 10–15 million pounds are applied annually in the US. It is extremely volatile — up to 90% of applied trifluralin can volatilize within weeks of application, traveling long distances from application sites via the atmosphere [2]. This volatility makes trifluralin ubiquitous in air samples across agricultural regions and contributes to its detection in remote environments including the Arctic. Despite volatilizing from soil surface, trifluralin that is incorporated into soil is more persistent and can contaminate groundwater [3].

How You Are Exposed

Agricultural workers who mix, load, and apply trifluralin have the highest occupational exposures through skin contact and inhalation [1]. Community members in agricultural areas breathe trifluralin during and after application due to its volatility. Dietary exposure from residues on treated crops is monitored by USDA [2]. Groundwater contamination near agricultural fields is documented in some regions. Fish in agricultural waterways accumulate trifluralin from sediment [3].

Why It Matters

Trifluralin is classified as a possible human carcinogen (IARC Group 2B), with evidence for lymphomas and kidney tumors in animal studies [1]. It is bioaccumulative in aquatic organisms — its octanol-water partition coefficient indicates moderate lipophilicity and accumulation potential. Trifluralin inhibits tubulin polymerization (the same mechanism as it kills plants — disrupting cell division), which has implications for rapidly dividing mammalian cells as well [2]. The atmospheric volatilization and long-range transport means trifluralin exposure occurs in communities hundreds of miles from application sites [3].

Who Is at Risk

Agricultural workers who apply trifluralin without adequate PPE face the highest exposures [1]. People who live near soybean and cotton production areas face ambient air exposure during application seasons [2]. Frequent consumers of locally caught fish from agricultural waterways in high-use regions may have dietary exposure.

How to Lower Your Exposure

Agricultural applicators: wear coveralls and a NIOSH-approved respirator during mixing and application [1]. Incorporate trifluralin into soil immediately after application to reduce volatilization. Support IPM practices that reduce herbicide use [2]. Choose organic versions of crops treated with high herbicide rates when possible [3].

References

  1. [1]IARC. Trifluralin. IARC Monographs Vol 53. 1991. https://monographs.iarc.who.int/
  2. [2]ATSDR. Toxicological Profile for Trifluralin. https://www.atsdr.cdc.gov/toxprofiles/tp55.pdf
  3. [3]EPA. Trifluralin Reregistration. https://www.epa.gov/ingredients-used-pesticide-products/trifluralin
  4. [4]Majewski MS, et al. Pesticide volatility from irrigated soil. J Environ Qual. 1998;27(2):412-20.

Recovery & Clinical Information

Body Half-Life

Trifluralin is moderately fat-soluble with a blood half-life of approximately 1-2 days in humans [1]. It is metabolized by CYP450 enzymes in the liver [2].

Testing & Biomarkers

No established routine clinical biomarker for trifluralin [1]. Occupational exposure monitoring relies on workplace air sampling and urinary metabolite studies (alpha-trifluoromethylsulfonamide) in research settings [2].

Interventions

Wash produce thoroughly; choose organic for heavily treated crops (grain sorghum, sunflower, soybean) [1]. Occupational PPE during application is standard [2]. No specific antidote or chelation [1].

Recovery Timeline

Blood levels normalize within days of stopping acute exposure [1]. Chronic thyroid and endocrine effects from ongoing exposure should gradually reverse after sustained source elimination [2].

Recovery References

  1. [1]ATSDR (2017). Toxicological Profile for Trifluralin. https://www.atsdr.cdc.gov/substances/toxsubstance.asp?toxid=240
  2. [2]EPA (1995). Trifluralin Registration Eligibility Decision. https://www.epa.gov/pesticide-registration

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