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CAS 51338-27-3

Diclofop methyl

aryloxyphenoxypropionate herbicidepesticideprobable carcinogen

Diclofop methyl is a selective grass-killing herbicide widely used in wheat and barley production that triggered landmark regulatory battles over cancer risk assessment in the 1990s — becoming a test case for how EPA weighs animal tumor data against human relevance.

Where It Comes From

Diclofop methyl was developed by Hoechst AG in West Germany and introduced commercially around 1975 under the trade name Hoelon. [1] It belongs to the aryloxyphenoxypropionate (AOPP) class of herbicides, which kill grass weeds (wild oats, ryegrass) in broadleaf crops by inhibiting acetyl-CoA carboxylase (ACC), the enzyme grasses need for fatty acid synthesis. This selectivity makes it valuable in cereal grain production, where it kills competing grasses without harming the wheat or barley crop. The herbicide is rapidly hydrolyzed in soil and plants to its active acid form, diclofop acid. In the early 1990s, animal studies found that diclofop methyl induced liver tumors in mice, triggering an EPA cancer review. However, the mechanism was debated — the company argued the liver tumors arose through a non-genotoxic, threshold mechanism (peroxisome proliferation) that is not relevant to humans because humans respond differently than rodents to peroxisome proliferators. [2] This debate became a landmark case in EPA's evolving cancer risk assessment methodology, contributing to the development of mode-of-action frameworks for evaluating whether animal tumor findings are relevant to humans. The EPA ultimately concluded the compound was a probable human carcinogen under the older 1986 guidelines while acknowledging scientific uncertainty, but under updated 2005 guidelines characterizes it as having suggestive evidence of carcinogenicity. [3] It remains registered for use in the United States with restricted application requirements.

How You Are Exposed

Agricultural workers applying diclofop methyl during wheat and barley production face occupational inhalation and skin exposure from spraying operations. Dietary exposure from residues in grain products is a route for the general population, though residues in finished food are typically low due to rapid hydrolysis. Groundwater contamination is possible in areas of heavy use, as the compound is moderately mobile in soil. Home users can encounter it in some lawn care products targeting grass weeds in broadleaf plantings.

Why It Matters

Animal studies show hepatic (liver) tumors in mice, leading to the probable carcinogen classification. The mode-of-action debate centers on peroxisome proliferation — a process that stimulates liver cell division in rodents but to which humans are considerably less sensitive due to differences in receptor biology. [2] Despite the scientific uncertainty, the conservative classification reflects precautionary principles. Non-cancer concerns include eye irritation, liver enzyme elevations in occupationally exposed workers, and aquatic toxicity to invertebrates and algae.

Who Is at Risk

Agricultural workers in cereal grain production (wheat, barley, rye, triticale) who mix, load, and apply diclofop methyl are the primary at-risk group. Farmers in wheat-growing regions (Pacific Northwest, Great Plains) represent the main occupational population. Dietary exposure for the general public is considered low given current use patterns and residue data.

How to Lower Your Exposure

1. Agricultural applicators should wear chemical-resistant gloves, long sleeves, eye protection, and an appropriate respiratory protection device when mixing and applying. 2. Observe re-entry intervals after application before allowing workers or bystanders back into treated fields. 3. Prevent runoff into waterways during application. 4. Consider integrated weed management approaches that reduce overall herbicide use — crop rotation, tillage, and competitive crop varieties can reduce reliance on herbicide applications.

References

  1. [1][1] Devine MD, Duke SO, Fedtke C (1993). Physiology of Herbicide Action. Prentice Hall.
  2. [2][2] Meaney MJ, et al. (1998). Mode of action of diclofop methyl liver tumorigenesis in mice: peroxisome proliferation. Toxicological Sciences, 45(1), 29–37.
  3. [3][3] US EPA (2004). Reregistration Eligibility Decision for Diclofop Methyl. EPA 738-R-04-005.

Recovery & Clinical Information

Body Half-Life

Diclofop methyl is rapidly hydrolyzed to diclofop acid in the body; both are primarily cleared through biliary and urinary excretion. Plasma half-life for the acid form is estimated at 10–20 hours in rodents. Limited human pharmacokinetic data are available; clearance is expected to be complete within several days of cessation of exposure.

Testing & Biomarkers

No standard clinical biomarker test is available for diclofop methyl. Research methods involve measuring diclofop acid in urine by LC-MS/MS. For occupationally exposed workers with symptoms, liver function tests (ALT, AST, alkaline phosphatase) are the most relevant clinical assessment. Routine biomonitoring is not currently practiced for this compound.

Interventions

Remove from exposure source. For skin/eye contact during spraying, wash with soap and water or flush eyes for 15 minutes. Seek medical evaluation for acute high-dose exposure. No specific antidote exists. Liver function monitoring is appropriate for workers with evidence of hepatotoxicity. Long-term cancer risk management relies on minimizing cumulative exposure.

Recovery Timeline

Diclofop methyl clears from the body within days after exposure ends. Liver enzyme elevations, if present, typically normalize within weeks of cessation of exposure. Long-term cancer risk from past exposure is a statistical consideration that does not have a reversible timeline.

Recovery References

  1. [1]EPA Reregistration Eligibility Decision for Diclofop Methyl (2004). EPA 738-R-04-005.
  2. [2]EFSA (2007). Conclusion on the peer review of diclofop-methyl. EFSA Journal, 5(5), 512.

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