Insights

After failed oilseed rape, what does clomazone research say about replanting?

When an oilseed rape crop fails, choosing what to sow next can become an urgent decision. If a clomazone-containing herbicide was applied, residues in the soil may affect the replacement crop. Bleaching and reduced early growth are concerns for sensitive plants exposed to the herbicide, as illustrated by crop-response research.

Illustration of a crop field inspection

Illustration

For farmers considering winter wheat or triticale only weeks after treatment, the question is what those residues could mean for the new crop as it emerges and grows. Understanding why clomazone causes bleaching, how long its effects can persist and what studies show about crop sensitivity helps identify what to check before replanting.

Why clomazone can bleach emerging plants

Clomazone injury is linked to disrupted pigment production in developing plants. The plant converts the parent compound into 5-ketoclomazone. This metabolite inhibits DXS (1-deoxy-D-xylulose-5-phosphate synthase), an enzyme in the plastid MEP pathway, which makes building blocks for pigments. With less carotenoid pigment to protect them, chlorophyll and cell membranes are more exposed to light-driven damage. New tissue can then look pale or bleached. Yasuor and colleagues summarise this mechanism.

In plain language: The plant changes clomazone into a form that interferes with making protective pigments. Without enough protection, new growth can bleach in the light.

This mechanism helps explain a symptom, but it cannot diagnose a field. Yasuor and colleagues studied clomazone metabolism in susceptible and resistant late-watergrass, a weed. They found more of the active metabolite in susceptible plants. That result helps explain the mechanism; it does not test wheat, triticale or herbicide carryover in soil.

Residue, persistence and crop response are different questions

Three questions need to be kept separate: how much herbicide remains in soil, how much can reach a plant, and how a particular crop responds. A chemical measurement or an estimate of how quickly the herbicide declines cannot by itself show whether a sensitive crop will emerge without injury. Crop type, exposure and growing conditions also affect the response.

In plain language: Finding less clomazone in soil does not by itself tell us how a crop will grow. The amount a plant can encounter and its sensitivity matter too.

Clomazone persistence varies among settings. The 2025 European Food Safety Authority (EFSA) peer review reports moderate-to-high field persistence across 27 European sites and slower degradation under anaerobic (without oxygen) than aerobic (with oxygen) incubation. These findings caution against a simple rule that wet weather always removes residues more quickly. They describe environmental fate across study conditions; they are not a planting interval for wheat or triticale.

There is no single soil factor that gives a complete answer about binding and availability. Adsorption means binding to soil particles. In the evidence EFSA reviewed, adsorption did not depend on pH. Soil texture and organic matter, moisture, temperature, aeration, application method and other local conditions can affect exposure or breakdown, as discussed in the 2025 crop-sensitivity and degradation study. A pH result or a fixed number of days cannot replace the product label or an assessment of the intended crop’s response.

What the crop studies measured—and what they did not

The 2025 crop-sensitivity and degradation study shows that crop response and persistence can vary. It combined short, controlled pot bioassays with wheat and Serbian soybean field trials. In the field trials, mustard bioassays were used to estimate remaining herbicide activity. The 14-day wheat pot assay used sandy loam at pH 7.43 with 2.7% organic matter. Those are specific test conditions, not a stand-in for conditions on another field.

A bioassay measures how a test plant responds when grown in treated soil; it does not measure the chemical residue directly. A chemical analysis measures the substance in a sample, but that alone does not show how a crop will respond. The study used plant response to estimate residual activity in its field trials.

Evidence Measured setting and result Relevance and limit for this decision
Jovanović-Radovanov (2025), wheat pot bioassays Venera wheat was grown for 14 days in treated sandy loam. Shoot fresh weight was 16.27% to 45.88% lower than the untreated control across tested soil concentrations of 360–1,440 μg/kg. A controlled crop-response result. The soil concentrations are amounts per kilogram of soil, not application rates per hectare, safe intervals or yield results.
Jovanović-Radovanov (2025), field trials and persistence Two Serbian soybean trials used 480, 720 and 960 g active ingredient/ha. Residual activity was estimated with mustard bioassays. Table 6 reports estimated-concentration half-lives of 43 and 55 days across the two years. Field context, but not a chemical residue measurement or a cereal replanting trial. The years differed in weather and timing, so application comparisons do not isolate tillage.
EFSA et al. (2025), environmental fate review Reviewed field fate across 27 European sites and aerobic/anaerobic degradation evidence. Supports environmental variability, not species-specific emergence safety or product-label permission.

Here, μg/kg means micrograms of active ingredient per kilogram of soil. The field-trial unit g active ingredient/ha means grams of active ingredient applied per hectare.

The study also reports a carotenoid response, which is a pigment measurement, not a yield result. The wheat result is not a triticale result, and this review found no cereal field-replanting trial at six to seven weeks after treatment. The pot assay measured shoot fresh weight: the fresh mass of the above-ground seedling growth after 14 days. It did not measure final grain yield.

In this study, half-life is the modelled time for the estimated concentration of bioavailable clomazone (available for plants to take up or encounter) to fall to half its initial value under the fitted conditions. This concentration was inferred from the bioassay results. It describes the study’s assay and model, not a safe planting interval.

In plain language: A half-life of 43 or 55 days does not mark a date when planting becomes safe. It describes how quickly the estimated plant-available concentration fell under the fitted conditions; it does not predict the response of wheat or triticale in a different field.

Separate scientific evidence from label permission

For a Polish field, the current Ministry of Agriculture register and product-label collection are starting points for checking the exact product and current authorisation. The ministry’s 2024 Chlomazon 480 EC label and Command 480 EC label illustrate product-specific crop-failure and mixture instructions. Use the label for the product actually applied to the field when checking restrictions. Check every product and mixture partner against its exact current label and applicable local regulations. A University of Wisconsin Extension guide describes field bioassays as one way to assess possible injury while stating that a bioassay does not replace the rotational interval. Its US crop guidance does not establish a Polish restriction.

Questions to take to a local adviser

Before seed is ordered or the field is worked, assemble the spray record: full product and formulation, date, rate, treated area, mixture partners and any overlapping passes. Add failed-crop observations, soil information, rainfall and planned field operations. Ask a local adviser to check the crop-failure and rotation wording for each product and whether field inspection or a bioassay using representative treated soil and the intended crop could help.

References

  • EFSA (European Food Safety Authority), Álvarez, F., Arena, M., et al. 2025. “Peer review of the pesticide risk assessment of the active substance clomazone.” EFSA Journal 23(2), e9206. DOI: 10.2903/j.efsa.2025.9206. Full text.
  • Jovanović-Radovanov, K. 2025. “Susceptibility of Different Crops to Simulated Clomazone Carry-Over and Its Degradation Dynamics in Sandy Loam Soil.” Agronomy 15(7), 1538. DOI: 10.3390/agronomy15071538. Full text.
  • Yasuor, H., W. Zou, V. V. Tolstikov, R. S. Tjeerdema, and A. J. Fischer. 2010. “Differential Oxidative Metabolism and 5-Ketoclomazone Accumulation Are Involved in Echinochloa phyllopogon Resistance to Clomazone.” Plant Physiology 153(1), 319–326. DOI: 10.1104/pp.110.153296. Full text.
  • University of Wisconsin–Madison Division of Extension. n.d. “Herbicide Rotational Restrictions for Cover and Forage Cropping Systems.” Article.
  • Ministry of Agriculture and Rural Development of Poland. 2024. “Chlomazon 480 EC” label (27 September 2024) and “Command 480 EC” label (15 January 2024). Chlomazon label · Command label · Current register · Label collection.

Common questions

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Sensorius can bring available field and soil readings, weather and timeline context together for review, and its Agronomic Adviser can work with approved field data and ask for missing context. See the Sensorius Platform or discuss a field evidence workflow.

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