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Innovative Research for a Sustainable Futurewww.epa.gov/research
ORCID: 0000-0002-2668-4821
Antony Williams l williams.antony@epa.gov l 919-541-1033
Influence of data curation on QSAR Modeling – examining issues of quality versus quantity of data
Antony Williams*, Kamel Mansouri, Ann M. Richard and Chris Grulke
U.S. Environmental Protection Agency, Office of Research and Development, National Center for Computational Toxicology (NCCT), Research Triangle Park, NC
Oak Ridge Institute for Science and Education (ORISE) Participant, Research Triangle Park, NC
Problem Definition and Goals
Source Data and Example Errors
Automated Analysis Using KNIME
Accessing ~1 Million Predicted Properties Online
Future Work
The accuracy of QSAR models is critically dependent on the quality of available data. As part of our efforts to
develop public platforms to provide access to predictive models, we have attempted to discriminate the influence of
the quality versus quantity of data available to develop and validate QSAR models. We have focused our efforts on
the widely used EPI Suite1 data (PHYSPROP database) that was initially developed over two decades ago. Specific
examples of quality issues for PHYSPROP data include multiple records for the same chemical structure with
different measured property values, inconsistency between the structure, chemical name and Chemical Abstracts
Service Registry Number (CASRN) for single records, the inability to convert the SMILES strings into chemical
structures, hypervalency in the chemical structures and the absence of stereochemistry for thousands of data
records. Relative to the era of EPI Suite development, modern cheminformatics tools allow for more advanced
capabilities in terms of chemical structure representation and storage, as well as enabling automated data
validation and standardization approaches to examine data quality. This poster reviews both our manual and
automated approaches to examining key datasets related to PHYSPROP data. This includes approaches to
validate between chemical structure representations (e.g., Mol-Block and SMILES) and identifiers (chemical names
and CASRN), as well as approaches to standardize the data into QSAR-ready formats for modeling. We have
quantified and segregated the data into various quality categories to allow us to thoroughly investigate the resulting
models that can be developed from these data slices and to examine to what extent efforts into the development of
large high-quality datasets have the expected pay-off in terms of prediction performance.
The iCSS Chemistry Dashboard (ICD) is a public EPA-hosted web application providing access to over
700,000 chemicals from EPA’s DSSTox database6. It integrates experimental and predicted data and is
a hub to other NCCT apps and web-based resources. The 3 and 4 STAR curated experimental data are
accessible via the ICD application. All chemicals were also passed through the collection of NCCT
prediction models and results will be freely available at http://comptox.epa.gov/dashboard in April 2016.
The manual investigation of the data allowed us to develop a KNIME3 workflow for automated
processing. This workflow was derived from earlier work by Mansouri et. al.4 and is represented in the
figure below as a series of blocks representing, for example:
The KNIME workflow for automated processing of PHYSPROP data
The KNIME workflow was used to insert various levels of Quality Flags indicating consistency between
chemical structure formats and identifiers. The consistency flag definitions and distribution are
summarized below for the >15k chemicals.
Predictive models were developed using only the 3 and 4 star curated data.
• The PHYSPROP data were sourced online2 as SDF files. A total of 13 endpoints were represented, including
LogKow, water solubility, melting point, boiling point, and others. The largest dataset, LogKow, contained over
15,800 individual chemicals. Each data point included the Mol-Block, SMILES, CASRN, Name, LogKow value
and, where available, a reference. This dataset was chosen as representative for examining the quality of data.
• A manual examination of the data revealed a number of issues: e.g., SMILES and Mol-Block did not agree;
CASRN did not match the correct structure; SMILES could not be converted; a single chemical structure would
be listed multiple times with different property values. Example errors across various PHYSPROP datasets are
shown below.
References
1. EPI Suite: http://www.epa.gov/tsca-screening-tools/epi-suitetm-estimation-program-interface
2. PHYSPROP Data: http://esc.syrres.com/interkow/EpiSuiteData_ISIS_SDF.htm
3. KNIME: https://www.knime.org/
4. Mansouri et al. CERAPP: Collaborative Estrogen Receptor Activity Prediction Project, Environ Health
Perspect; DOI:10.1289/ehp.1510267
5. PaDEL descriptors, http://padel.nus.edu.sg/software/padeldescriptor/
6. EPA Distributed Structure-Searchable Toxicity (DSSTox) Database, http://www.epa.gov/chemical-
research/distributed-structure-searchable-toxicity-dsstox-database
7. EPA Toxicity Estimation Software Tool (T.E.S.T.) software http://www.epa.gov/chemical-research/toxicity-
estimation-software-tool-test
Preparing data for QSAR Modeling
• Release NCCT models as interactive online prediction tools in the near future via the ICD.
• Integrate the suite of EPA T.E.S.T7 physchem and toxicity prediction models to expand the
collection of available models.
• Source additional data to expand the training sets underpinning the prediction algorithms.
4 STAR ENHANCED: Name/CASRN/Mol/SMILES added Stereo: 550
4 STAR: 3 of 4 Name/CASRN/Mol/SMILES: 5967
3 STAR ENHANCED: 3 of 4 Name/CASRN/Mol/SMILES added Stereo: 177
3 STAR: 3 of 4 Name/CASRN/Mol/SMILES: 7910
2 STAR PLUS: 2 of 4 Name/CASRN/Mol/SMILES/Tautomer: 133
2 STAR: 2 of 4 Name/CASRN/Mol/SMILES: 1003
1 STAR: No two fields consistent 379
2627/P125
Society of Toxicology Annual Meeting
New Orleans, LA
March 13-17, 2016
• Check names against dictionary (555 invalid)
• Assign Quality flags based on consistency
among data fields
Examples of hypervalency in LogKow dataset
Equivalent structures but with different CASRN, names
and values in MP dataset: -4 and + 70oC
Equivalent structures, different CASRN, names,
and values in MP dataset
This poster does not necessarily reflect EPA policy. Mention of trade names or commercial products does not constitute endorsement or recommendation for use.
For the purposes of QSAR modeling, the 3 and 4 STAR datasets were
processed through a KNIME workflow. This processing removed
inorganics and mixtures, processed salts into neutral forms (except for
melting point data), normalized tautomers, and removed duplicates.
The resulting “QSAR-ready” file(s) were modeled using Genetic
Algorithm-Partial Least Squares with 5-fold cross validation and
utilizing 2D PaDEL5 molecular descriptors. Multiple modeling runs
(100) produced the best models using a minimum number of
descriptors. The models for all 13 endpoints are available as both
Windows and Linux executable binaries and as a C++ library that can
be called by a separate application.
Model Performance
The LogKow prediction model delivered by EPI Suite used a smaller dataset (of 2700 chemicals). The
curation of the available data, utilization of a larger dataset (>14,000 chemicals) and application of novel
machine-learning approaches produced a better and simpler model with only 10 descriptors. The figures
below illustrate the difference between the original EPI Suite model and the newly derived predictive
model. The red data points indicate the outliers from the original modeling approach, the majority not
included in the original training set.
Different structures in Mol-Block and SMILES
Statistics of the new model
5-fold cross-validation:
Q2: 0.87 RMSE: 0.67
Fitting:
R2: 0.87 RMSE: 0.66
Test set Prediction:
R2: 0.84 RMSE: 0.65
• Compare Mol-Block and SMILES (2268 different)
• Check for duplicates (657 structures, 531 names)
• Check CASRN Numbers (3646 invalid CASRN)
Abstract
Problem: The performance of QSAR models is hampered by the quality of the underlying data.
Goals: To examine the quality of the data underlying the EPI Suite prediction models using both manual and
automated methods. To use the curated data to develop new prediction models and examine the influence of data
quality and quantity, on the resulting QSAR predictions. To make the data and models publically available.

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Innovative Data Curation Improves QSAR Models

  • 1. Innovative Research for a Sustainable Futurewww.epa.gov/research ORCID: 0000-0002-2668-4821 Antony Williams l williams.antony@epa.gov l 919-541-1033 Influence of data curation on QSAR Modeling – examining issues of quality versus quantity of data Antony Williams*, Kamel Mansouri, Ann M. Richard and Chris Grulke U.S. Environmental Protection Agency, Office of Research and Development, National Center for Computational Toxicology (NCCT), Research Triangle Park, NC Oak Ridge Institute for Science and Education (ORISE) Participant, Research Triangle Park, NC Problem Definition and Goals Source Data and Example Errors Automated Analysis Using KNIME Accessing ~1 Million Predicted Properties Online Future Work The accuracy of QSAR models is critically dependent on the quality of available data. As part of our efforts to develop public platforms to provide access to predictive models, we have attempted to discriminate the influence of the quality versus quantity of data available to develop and validate QSAR models. We have focused our efforts on the widely used EPI Suite1 data (PHYSPROP database) that was initially developed over two decades ago. Specific examples of quality issues for PHYSPROP data include multiple records for the same chemical structure with different measured property values, inconsistency between the structure, chemical name and Chemical Abstracts Service Registry Number (CASRN) for single records, the inability to convert the SMILES strings into chemical structures, hypervalency in the chemical structures and the absence of stereochemistry for thousands of data records. Relative to the era of EPI Suite development, modern cheminformatics tools allow for more advanced capabilities in terms of chemical structure representation and storage, as well as enabling automated data validation and standardization approaches to examine data quality. This poster reviews both our manual and automated approaches to examining key datasets related to PHYSPROP data. This includes approaches to validate between chemical structure representations (e.g., Mol-Block and SMILES) and identifiers (chemical names and CASRN), as well as approaches to standardize the data into QSAR-ready formats for modeling. We have quantified and segregated the data into various quality categories to allow us to thoroughly investigate the resulting models that can be developed from these data slices and to examine to what extent efforts into the development of large high-quality datasets have the expected pay-off in terms of prediction performance. The iCSS Chemistry Dashboard (ICD) is a public EPA-hosted web application providing access to over 700,000 chemicals from EPA’s DSSTox database6. It integrates experimental and predicted data and is a hub to other NCCT apps and web-based resources. The 3 and 4 STAR curated experimental data are accessible via the ICD application. All chemicals were also passed through the collection of NCCT prediction models and results will be freely available at http://comptox.epa.gov/dashboard in April 2016. The manual investigation of the data allowed us to develop a KNIME3 workflow for automated processing. This workflow was derived from earlier work by Mansouri et. al.4 and is represented in the figure below as a series of blocks representing, for example: The KNIME workflow for automated processing of PHYSPROP data The KNIME workflow was used to insert various levels of Quality Flags indicating consistency between chemical structure formats and identifiers. The consistency flag definitions and distribution are summarized below for the >15k chemicals. Predictive models were developed using only the 3 and 4 star curated data. • The PHYSPROP data were sourced online2 as SDF files. A total of 13 endpoints were represented, including LogKow, water solubility, melting point, boiling point, and others. The largest dataset, LogKow, contained over 15,800 individual chemicals. Each data point included the Mol-Block, SMILES, CASRN, Name, LogKow value and, where available, a reference. This dataset was chosen as representative for examining the quality of data. • A manual examination of the data revealed a number of issues: e.g., SMILES and Mol-Block did not agree; CASRN did not match the correct structure; SMILES could not be converted; a single chemical structure would be listed multiple times with different property values. Example errors across various PHYSPROP datasets are shown below. References 1. EPI Suite: http://www.epa.gov/tsca-screening-tools/epi-suitetm-estimation-program-interface 2. PHYSPROP Data: http://esc.syrres.com/interkow/EpiSuiteData_ISIS_SDF.htm 3. KNIME: https://www.knime.org/ 4. Mansouri et al. CERAPP: Collaborative Estrogen Receptor Activity Prediction Project, Environ Health Perspect; DOI:10.1289/ehp.1510267 5. PaDEL descriptors, http://padel.nus.edu.sg/software/padeldescriptor/ 6. EPA Distributed Structure-Searchable Toxicity (DSSTox) Database, http://www.epa.gov/chemical- research/distributed-structure-searchable-toxicity-dsstox-database 7. EPA Toxicity Estimation Software Tool (T.E.S.T.) software http://www.epa.gov/chemical-research/toxicity- estimation-software-tool-test Preparing data for QSAR Modeling • Release NCCT models as interactive online prediction tools in the near future via the ICD. • Integrate the suite of EPA T.E.S.T7 physchem and toxicity prediction models to expand the collection of available models. • Source additional data to expand the training sets underpinning the prediction algorithms. 4 STAR ENHANCED: Name/CASRN/Mol/SMILES added Stereo: 550 4 STAR: 3 of 4 Name/CASRN/Mol/SMILES: 5967 3 STAR ENHANCED: 3 of 4 Name/CASRN/Mol/SMILES added Stereo: 177 3 STAR: 3 of 4 Name/CASRN/Mol/SMILES: 7910 2 STAR PLUS: 2 of 4 Name/CASRN/Mol/SMILES/Tautomer: 133 2 STAR: 2 of 4 Name/CASRN/Mol/SMILES: 1003 1 STAR: No two fields consistent 379 2627/P125 Society of Toxicology Annual Meeting New Orleans, LA March 13-17, 2016 • Check names against dictionary (555 invalid) • Assign Quality flags based on consistency among data fields Examples of hypervalency in LogKow dataset Equivalent structures but with different CASRN, names and values in MP dataset: -4 and + 70oC Equivalent structures, different CASRN, names, and values in MP dataset This poster does not necessarily reflect EPA policy. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. For the purposes of QSAR modeling, the 3 and 4 STAR datasets were processed through a KNIME workflow. This processing removed inorganics and mixtures, processed salts into neutral forms (except for melting point data), normalized tautomers, and removed duplicates. The resulting “QSAR-ready” file(s) were modeled using Genetic Algorithm-Partial Least Squares with 5-fold cross validation and utilizing 2D PaDEL5 molecular descriptors. Multiple modeling runs (100) produced the best models using a minimum number of descriptors. The models for all 13 endpoints are available as both Windows and Linux executable binaries and as a C++ library that can be called by a separate application. Model Performance The LogKow prediction model delivered by EPI Suite used a smaller dataset (of 2700 chemicals). The curation of the available data, utilization of a larger dataset (>14,000 chemicals) and application of novel machine-learning approaches produced a better and simpler model with only 10 descriptors. The figures below illustrate the difference between the original EPI Suite model and the newly derived predictive model. The red data points indicate the outliers from the original modeling approach, the majority not included in the original training set. Different structures in Mol-Block and SMILES Statistics of the new model 5-fold cross-validation: Q2: 0.87 RMSE: 0.67 Fitting: R2: 0.87 RMSE: 0.66 Test set Prediction: R2: 0.84 RMSE: 0.65 • Compare Mol-Block and SMILES (2268 different) • Check for duplicates (657 structures, 531 names) • Check CASRN Numbers (3646 invalid CASRN) Abstract Problem: The performance of QSAR models is hampered by the quality of the underlying data. Goals: To examine the quality of the data underlying the EPI Suite prediction models using both manual and automated methods. To use the curated data to develop new prediction models and examine the influence of data quality and quantity, on the resulting QSAR predictions. To make the data and models publically available.