Where It Comes From
Chlorothalonil was discovered by Diamond Alkali Company and registered in 1964, becoming one of the most successful broad-spectrum fungicides ever developed. [1] It works by reacting with thiol groups (-SH) on fungal enzyme systems — a non-specific mechanism that disrupts multiple metabolic pathways simultaneously, which is why resistance in target fungi develops very slowly. Trade names include Bravo, Daconil, and Equus, and it has been applied to dozens of crops (peanuts, potatoes, tomatoes, wheat, turf) as well as to ornamental plants and painted surfaces as a mildewcide. Annual U.S. use has historically ranged from 6–11 million pounds per year, making it consistently among the top 10 pesticides by volume. Long-term animal studies found evidence of kidney tumors in male rats, triggering a probable carcinogen (Group B2) classification by EPA in the 1990s. [2] Research also revealed that chlorothalonil degrades to a particularly toxic metabolite — 4-hydroxy-2,5,6-trichloroisophthalonitrile (HCT) — that is more persistent in aquatic sediments than the parent compound and highly toxic to aquatic invertebrates and fish. This drove increasingly restrictive use requirements. The EU withdrew approval in 2019 specifically due to groundwater contamination concerns from HCT, effectively ending its use in European agriculture. [3] In the US, EPA's 2019 interim registration review identified risks to aquatic ecosystems and required significant label changes.
How You Are Exposed
Agricultural workers mixing, loading, and applying chlorothalonil sprays have the highest occupational exposures — both inhalation of spray mist and dermal contact. Bystanders near treated fields during or shortly after application can inhale chlorothalonil. Consumers are exposed through dietary residues on treated foods (raw tomatoes and peanuts can have measurable residues). Golfers and homeowners using chlorothalonil-treated turf or garden products have relevant exposures. Groundwater and surface water contamination provides a drinking water pathway near agricultural areas.
Why It Matters
Chronic kidney toxicity and renal tubule tumors in male rats form the basis for the probable carcinogen classification; the proposed mechanism involves direct tubular cell toxicity and reactive metabolite generation. [2] Chlorothalonil is a potent skin and eye irritant and a known skin sensitizer — occupational contact dermatitis is well-documented. Aquatic toxicity is severe: the compound and especially HCT metabolite are acutely lethal to fish and invertebrates at low concentrations, and chronic effects on aquatic ecosystems near agricultural drainages have been documented globally.
Who Is at Risk
Agricultural workers in peanut, potato, tomato, and turf management are most exposed occupationally. Golfers on chlorothalonil-treated courses and home gardeners using Daconil products represent the consumer population. Communities adjacent to high-use agricultural areas with contaminated surface water face environmental exposures.
How to Lower Your Exposure
1. Agricultural workers should wear liquid-proof gloves, protective eyewear, and an appropriate respirator during mixing and application; consider closed-cab equipment. 2. Home gardeners can often substitute copper-based fungicides or sulfur for chlorothalonil on vegetables with comparable efficacy and lower systemic toxicity. 3. Wash produce thoroughly; chlorothalonil is largely a surface residue and washing reduces exposure significantly. 4. Avoid applying near waterways or storm drains, and observe label-specified buffer zones. 5. In EU-regulated supply chains, chlorothalonil is no longer present; US consumers should check produce origin.
References
- [1][1] Fungicide Resistance Action Committee (FRAC). Chlorothalonil (M05). https://www.frac.info/
- [2][2] US EPA (1999). Chlorothalonil Risk Characterization Document. https://archive.epa.gov/pesticides/reregistration/web/pdf/chlorothalonil_red.pdf
- [3][3] European Commission (2019). Commission Regulation (EU) 2019/677 — Non-renewal of chlorothalonil. Official Journal of the EU.
Recovery & Clinical Information
Body Half-Life
Chlorothalonil is extensively metabolized in mammals; the major urinary metabolite is 4-hydroxy-2,5,6-trichloroisophthalonitrile (HCT) formed by glutathione conjugation and renal processing. Plasma half-life for chlorothalonil is short (hours); urinary HCT appears within 24 hours and clears within 1–3 days after cessation of exposure. Kidney is the target organ for chronic effects, reflecting the metabolite's local generation there.
Testing & Biomarkers
Urinary HCT metabolite can be measured by LC-MS/MS in occupational biomonitoring studies but is not offered by routine clinical laboratories. Kidney function tests (serum creatinine, BUN, urinalysis with microscopy) are clinically relevant for chronically exposed workers or following high acute exposure. Spot urine HCT measurement is used in research settings.
Interventions
Remove from exposure. For skin contact, wash with soap and water; for eye contact, flush 15 minutes. Acute high-dose inhalation: fresh air, supportive care, seek medical evaluation. Manage contact dermatitis with topical corticosteroids. No specific antidote. Kidney function monitoring is warranted for workers with evidence of nephrotoxicity. For cancer risk, source elimination is the primary preventive measure.
Recovery Timeline
Skin irritation and dermatitis resolve within days of avoiding contact. Urinary metabolites clear within 3 days of last exposure. Mild kidney function changes may normalize over weeks after removing exposure. Cancer risk from past cumulative exposure remains but does not increase post-exposure.
Recovery References
- [1]EPA Chlorothalonil Risk Assessment (1999). https://archive.epa.gov/pesticides/reregistration/web/pdf/chlorothalonil_red.pdf
- [2]EFSA (2005). Conclusion regarding the peer review of chlorothalonil. EFSA Journal, 3(4), 95.