| Literature DB >> 23244245 |
Claire Mays1, Emilio Benfenati, Simon Pardoe.
Abstract
The ORCHESTRA online questionnaire on "benefits and barriers to the use of QSAR methods" addressed the academic, consultant, regulatory and industry communities potentially interested by QSAR methods in the context of REACH. Replies from more than 60 stakeholders produced some insights on the actual application of QSAR methods, and how to improve their use.Respondents state in majority that they have used QSAR methods. All have some future plans to test or use QSAR methods in accordance with their stakeholder role.The stakeholder respondents cited a total of 28 models, methods or software that they have actually applied. The three most frequently cited suites, used moreover by all the stakeholder categories, are the OECD Toolbox, EPISuite and CAESAR; all are free tools.Results suggest that stereotyped assumptions about the barriers to application of QSAR may be incorrect. Economic costs (including potential delays) are not found to be a major barrier. And only one respondent "prefers" traditional, well-known and accepted toxicological assessment methods.Information and guidance may be the keys to reinforcing use of QSAR models. Regulators appear most interested in obtaining clear explanation of the basis of the models, to provide a solid basis for decisions. Scientists appear most interested in the exploration of the scientific capabilities of the QSAR approach. Industry shows interest in obtaining reassurance that appropriate uses of QSAR will be accepted by regulators.Entities:
Year: 2012 PMID: 23244245 PMCID: PMC3771413 DOI: 10.1186/1752-153X-6-159
Source DB: PubMed Journal: Chem Cent J ISSN: 1752-153X Impact factor: 4.215
The QSAR models cited by respondents
| | ||||
|---|---|---|---|---|
| | ||||
| 7 | 6 | 3 | ||
| 7 | 5 | 4 | ||
| CAESAR | 7 | 3 | 2 | 2 |
| Leadscope | 4 | 3 | | 1 |
| ECOSAR | 5 | 2 | 3 | |
| SPARC | 5 | 2 | 3 | |
| Toxtree | 5 | 2 | | 3 |
| Topkat | 3 | 1 | 2 | |
| DEREK | 4 | 1 | 1 | 2 |
| ACD/Tox Suite | 3 | 1 | 1 | 1 |
| ToxBoxes | 2 | 1 | 1 | |
| 2 | 1 | 1 | | |
| 2 | 1 | 1 | | |
| Lazar | 2 | 1 | | 1 |
| MultiCase | 1 | 1 | | 1 |
| ChemAxon Marvin | 1 | 1 | | |
| Macromodel | 1 | 1 | | |
| Molcode Toolbox | 1 | 1 | | |
| OncoLogic | 1 | 1 | | |
| Sybyl | 1 | 1 | | |
| Danish EPA QSAR database | 3 | | 3 | |
| LMC Oasis including CataLogic | 3 | | 3 | |
| ChemCan | 1 | | 1 | |
| ChemSteer | 1 | | 1 | |
| EQC | 1 | | 1 | |
| PBKB (SimCYP & MCSim) | 1 | | 1 | |
| PBT Profiler | 1 | | 1 | |
| SoilFug | 1 | 1 | ||
Domains of past application of methods
| Physico-chemical properties | |||
| Human toxicology | |||
| Environmental fate properties | |||
| Ecotoxicology |
The QSAR models used by respondents
| | ||||
|---|---|---|---|---|
| Boiling point Vapour pressure | Mutagenicity/ genotoxicity (including Ames, micronucleus, mouse SCE, mouse COMET) Carcinogenicity Teratogenicity Acute toxicity (mammals) Skin irritation, corrosion, or sensitization Eye irritation Endocrine disruption (estrogenbinding, antiadrogenic activity)Reprotox hERG inhibition | Acute aquatic invertebrate toxicity (Daphnia) Acute fish toxicity (fathead minnow, trout) Algae Toxicity Terrestrial Ecotoxicology (bees) Tetrahymena | Bioaccumulation/ BCF Half-life in water/soil Ready biodegradability Abiotic hydrolysis/degradation Koc/soil adsorption | |
| | Water solubility Partition coefficients (LogP/LogD) | | | |
| (8 of 13 subjects replied) | | | | |
| Partition coefficients (Pow) | Carcinogenicity | Aquatic toxicity | Bioaccumulation/ BCF | |
| (6 of 12 subjects replied) | | Reproductive toxicity | Daphnia reproduction | Degradation (DT50) |
| | | Mutagenicity/ genotoxicity (also addressing metabolites) | All ecotox part of EPI Suite (Aquatic toxicity acute andchronic algae fish and daphnia) | |
| | | Teratogenesis | | |
| | | Acute toxicity Endocrine disruptions (estrogen and androgen binding) | | |
| | | Skin sensitization NOEC | | |
| Partition coefficients (LogP) | Mutagenicity Genotoxicity Carcinogenicity Teratogenicity | Acute aquatic invertebrate toxicity (Daphnia) (LC50 daphnia magna as supporting information) Fish toxicity | ||
Functions addressed by past applications of methods
| Fast evaluation of the properties of chemicals of interest | |||
| Research and development, for the evaluation of toxicity | |||
| Regulatory requirements - as supporting information | |||
| Regulatory requirements - as part of a weight-of-evidence approach | |||
| Prioritisation of compounds for further analysis | |||
| Regulatory requirements - as the key study | - | ||
| None / not sure | - |
Main reasons to use QSAR methods going forward
| To identify and prioritise substances of concern. | |||
| To improve the response to regulatory requirements such as risk assessment and classification and labelling. | |||
| To reduce the use of vertebrates in experiments - to meet regulatory requirements. | |||
| To reduce the time and costs of experiments. | |||
| To assess potentially thousands of chemicals simultaneously | |||
| To reduce the use of vertebrates in experiments - to meet our own ethical policies. | |||
| To address endpoints for which animal models are not fully accepted. |
Needs for information or guidance
| | | | |
Facilitating the use of QSAR methods
| Seeing good examples of industry using | |||
| Lists and reviews of the available models, with information on where to access them. | |||
| Examples from the regulators about acceptance of / enthusiasm for | |||
| Seeing more peer-reviewed journal articles about the practical applications of | |||
| Clear guidelines for reporting toxicity results from | |||
| Clear standardisation of the ways in which individual QSAR models and their appropriate uses are described, and their applicability domains are defined. | |||
| Support and guidance from laboratories with expertise in the uses of QSARs. | |||
| Examples of the reasoning and transparent documentation required for submissions. |
Measures to foster improved acceptance of QSAR methods
| Industry using | |||
| Case study research evidence of the quality and reliability of QSAR methods. | |||
| Use by high-profile companies / organisations, and in cases with high visibility. | |||
| The monitoring, review and updating of models by specialist QSAR laboratories. | |||
| The trademarking of models by trusted software companies or organisations. | - |