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Related Experiment Video

Updated: Jun 12, 2026

Determination of the Absorption, Translocation, and Distribution of Imidacloprid in Wheat
06:11

Determination of the Absorption, Translocation, and Distribution of Imidacloprid in Wheat

Published on: April 28, 2023

Biomonitoring Equivalents for select neonicotinoids.

Sean M Hays1, Theresa K Lopez2, Ann Roseberry Lincoln2

  • 1Summit Toxicology, LLC, Bozeman, MT, USA.

Regulatory Toxicology and Pharmacology : RTP
|June 10, 2026
PubMed
Summary

This study establishes Biomonitoring Equivalents (BEs) for common neonicotinoid pesticides (NNs). These values help interpret human exposure data, aiding public health officials in risk assessment for widely used insecticides.

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Area of Science:

  • Environmental Chemistry
  • Toxicology
  • Public Health

Background:

  • Neonicotinoids and neonicotinoid-like pesticides (NNs) are extensively used globally in agriculture and homes.
  • Public exposure to NNs occurs through diet, pet contact, and other routes.
  • Urinary metabolite levels can assess NN exposure.

Purpose of the Study:

  • To derive Biomonitoring Equivalents (BEs) for key neonicotinoids.
  • To provide a framework for interpreting population biomonitoring data.
  • To support public health risk assessment for NN exposure.

Main Methods:

  • Reviewed health-based risk assessments and Acceptable Daily Intakes (ADIs).
  • Derived BEs using Health Canada's established ADIs.
  • Selected appropriate biomarkers for each NN based on pharmacokinetic data.
Keywords:
BiomonitoringBiomonitoring equivalentsExposure assessmentNeonicotinoidsRisk assessment

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Last Updated: Jun 12, 2026

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Published on: April 28, 2023

Study on the Metabolism of Six Systemic Insecticides in a Newly Established Cell Suspension Culture Derived from Tea (Camellia Sinensis L.) Leaves
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Study on the Metabolism of Six Systemic Insecticides in a Newly Established Cell Suspension Culture Derived from Tea (Camellia Sinensis L.) Leaves

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Main Results:

  • Biomonitoring Equivalents (BEs) were successfully derived for acetamiprid, clothianidin, imidacloprid, sulfoxaflor, and thiamethoxam.
  • Specific biomarkers were identified for each pesticide.
  • The derived BEs offer a standardized method for data interpretation.

Conclusions:

  • The derived BE values serve as crucial benchmarks for assessing population exposure to NNs.
  • This work facilitates consistent interpretation of biomonitoring results in a public health context.
  • Public health officials and regulators can utilize these BEs for informed decision-making regarding NN risks.