Areas of applicability

QSAR models have been developed for many applications:

  • Physico-chemical properties, such as boiling point, water solubility, partition coefficients. The U.S. EPA Estimation Program Interface (EPI) suite comprise models for these endpoints (http://www.epa.gov/oppt/exposure/pubs/episuite.htm).
  • Environmental properties, such as bioconcentration factor (included in the CAESAR software), degradation, soil adsorption, photodegradation.
  • Ecotoxicological properties, such as fish, daphnia, bird, bee toxicity. Models for these endpoints have been developed by the DEMETRA project.
  • Toxicity, such as carcinogenicity, mutagenicity, developmental toxicity, skin sensitization. All these endpoints have been modelled by the EC funded project CAESAR and implemented in the on line freely available CAESAR software.

Typically, the performance of the QSAR models are better for physico-chemical properties, and decrease with the increase complexity of the studied system. For certain human endpoints, such as carcinogenicity and developmental toxicity, the general position is that in silico models should be used as unique tool, but as support for the evaluation based on several methods.

For aquatic toxicity, most of the models address acute toxicity, mainly in fish. Results are good for chemicals which do not carry residues which increase their toxicity, which applies to about 30% of the cases. Specific models for more toxic compounds should not be used in these cases.

Models for mutagenicity (mainly Ames test) generally give good results (accuracy about 80%, which is close to the test reproducibility).

Models for bioconcentration factors (BCF) give good results (R2 about 80%; error about 0.5 log unit). Care should be taken if the predicted value is close to the threshold, while if the predicted value is well above or below the BCF threshold, the prediction is much more reliable.

Models for carcinogenicity give a quite large error. About one out three chemicals is wrongly predicted. Better results can be obtained if the applicability domain of the model is evaluated. At least three models for carcinogenicity should be used, because the results vary. In case of agreement, the prediction is more reliable.

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