Abstract
In the area of omics profiling in toxicology, i.e. toxicogenomics, characteristic molecular profiles have previously been incorporated into prediction models for early assessment of a carcinogenic potential and mechanism-based classification of compounds. Traditionally, the biomarker signatures used for model construction were derived from individual high-throughput techniques, such as microarrays designed for monitoring global mRNA expression. In this study, we built predictive models by integrating omics data across complementary microarray platforms and introduced new concepts for modeling of pathway alterations and molecular interactions between multiple biological layers. We trained and evaluated diverse machine learning-based models, differing in the incorporated features and learning algorithms on a cross-omics dataset encompassing mRNA, miRNA, and protein expression profiles obtained from rat liver samples treated with a heterogeneous set of substances. Most of these compounds could be unambiguously classified as genotoxic carcinogens, non-genotoxic carcinogens, or non-hepatocarcinogens based on evidence from published studies. Since mixed characteristics were reported for the compounds Cyproterone acetate, Thioacetamide, and Wy-14643, we reclassified these compounds as either genotoxic or non-genotoxic carcinogens based on their molecular profiles. Evaluating our toxicogenomics models in a repeated external cross-validation procedure, we demonstrated that the prediction accuracy of our models could be increased by joining the biomarker signatures across multiple biological layers and by adding complex features derived from cross-platform integration of the omics data. Furthermore, we found that adding these features resulted in a better separation of the compound classes and a more confident reclassification of the three undefined compounds as non-genotoxic carcinogens.
Introduction
The current gold standard for evaluation of the carcinogenic potential of newly developed drugs and other chemical compounds is the 2-year chronic rodent bioassay. This assay requires daily administration of the tested compound to rats or mice of both sexes and close survey of the animals for signs of toxicity and neoplastic lesions (see OECD Test Guideline 451). During preclinical safety assessment, substances showing a carcinogenic potential at a late stage may lead to substantial losses for the pharmaceutical and chemical industry. A mechanistic distinction is made between genotoxic carcinogens (GCs), which form DNA adducts and cause direct DNA damage, as opposed to non-genotoxic carcinogens (NGCs), for which a wide variety of alternative hepatocarcinogenic mechanisms have been described [1]–[3]. While GCs can be identified early by means of in vitro genotoxicity assays (e.g., Ames test), no short-term assay exists for the detection of NGCs.
Several groups have reported application of toxicogenomics methods for prediction of the outcome of chronic bioassays based on gene expression profiles compiled from short-term in vivo studies. Most studies published in this field focused on mRNA expression profiling and employed machine learning algorithms or statistical methods to predict the carcinogenic class of compounds based on characteristic expression patterns, called signatures [4], [5]. The classification outcomes may then be used to prioritize environmental and/or industrial chemicals for further exploration in chronic carcinogenicity bioassays [6]. Furthermore, the toxicogenomics approach can deliver complementary mechanistic insights, as specific molecular profiles can be associated with toxicological phenotypes and adverse effects observed in animal studies [5]. Along these lines, Ellinger-Ziegelbauer et al. revealed characteristic changes in the expression of mechanistically related genes, which allowed for discriminating GCs from NGCs in male Wistar-Hanover rats [7]. While a strong DNA damage response was observed upon GC treatment, the NGC- induced genes were indicative of increased cell cycle progression [7]. In a follow-up study, the authors constructed prediction models based on Support Vector Machine (SVM) classifiers trained on a larger set of compounds and thereby demonstrated the potential of toxicogenomics approaches for the early assessment of the carcinogenic risk [8]. More recently, Uehara et al. proposed two mRNA signatures for the detection of certain classes of NGCs based on Affymetrix gene expression data from Sprague-Dawley rat liver samples, which are deposited at the large toxicogenomics database TG-GATEs [9]. While the first signature captured transcriptional changes present upon single NGC exposure after 24 hours [10], the second one contains probe sets which are specifically deregulated after 4 weeks of repeated NGC administration [11]. Furthermore, an approach using environmental chemicals found that carcinogens in general can be detected with higher specificity if longer dosing periods are used in animal studies [6], [11]. These findings suggest that the exact compound class to be predicted and the time point(s) at which expression profiles are generated should be well defined and considered together.
In addition to global mRNA profiling data, miRNA, and protein expression data have previously been generated for toxicogenomics applications [12], [13]. While microarrays and RNA-seq are typically used for transcriptional profiling, shotgun proteomics is commonly employed for global protein profiling [14]. A review of the state-of-the-art high-throughput techniques for holistic molecular profiling including references to published applications in the field of toxicogenomics was recently provided by Khan et al. [14].
In general the ability to predict a compound's carcinogenic potential based on short-term expression profiles would be a clear step forward concerning reduction of time, animals, and monetary requirements in chemical and drug development. Building on published toxicogenomics studies that mostly focused on mRNA expression and used individual genes as predictive features, the approaches presented here introduce two novel concepts: first, the integration of omics data across platforms that interrogate different biological layers (mRNA, miRNA, and protein expression) and second, the abstraction from individual signature genes to higher-order levels, such as pathway enrichments or molecular interactions. This holistic approach, which integrates multiple global omics approaches, was currently also proposed by Khan et al. [14].The classification performance of our novel methodologies was evaluated on a dataset comprising mRNA, miRNA, and protein expression profiles from liver samples of male Wistar rats exposed to GCs, NGCs, or non-hepatocarcinogens (NCs) for up to 14 days. In a cross-validation experiment, we demonstrate that the predictive power of traditional mRNA signatures can be increased by adding complementary omics-based features obtained from profiling other molecular levels. We show that the classification performance can be further improved by additionally providing the prediction models with complex features derived from integrated analyses of multi-level omics data.
Methods
Ethics statement
The experimental protocol was reviewed and approved by the Institutional Animal Care and Use Committee (IACUC) of the Institute of Toxicology, Bayer, Stilwell, KS, U.S.A, for compliance with the Federal Animal Welfare Act (1988): 7 U.S.C.2131 et seq. as well as the National Research Council's (NRC) Guide for the Care and Use of Laboratory Animals (National Academy Press, 1996). General clinical observations, including observations for moribundity and mortality, were performed at least daily to monitor the general overall health status of the animals and to minimize suffering. For necropsy, the animals were anesthetized in a CO2 chamber and blood was drawn by cardiac puncture. Finally, animals were exsanguinated by cutting the diaphragm.
Animal study
Male Wistar Hanover rats (Crl:WI[Gl/BRL/Han]IGS BR) from Charles River Laboratories, Inc. (Raleigh, NC) were maintained on certified rodent chow (Purina Mills Certified Rodent Diet 5200) ad libitum in individual suspended stainless steel wire-mesh cages. The animals were kept under controlled temperature (18 to 26°C), humidity (30 to 70%), and lighting (12 h light – dark cycle) and were acclimated for a minimum of 6 days. 8 to 10 week old animals were assigned to dose groups (5 rats/group) by weight using a weight stratification-based computer program. Substances were administered by gastric gavage for up to 14 days (in a volume of 5 ml/kg body weight/day) based on the group mean weekly body weight for each dose group. Test substances were suspended (W/W) in either corn oil, or a 0.5% (W/V) Carboxymethyl Cellulose (CMC)/DI water preparation (5 g CMC/1 liter DI water). To maintain a homogenous suspension during dosing, a magnetic stir-plate was used if needed. Dimethylnitrosamine (Sigma, St. Louis, MO; CAS 62-75-9; purity >98%; 4 mg/kg/d), C.I. Direct Black (Chlorazol Black, Sigma, St. Louis, MO; CAS 1937-37-7; purity 29% carbon, 146 mg/kg/d), and Cyproterone acetate (Sigma, St. Louis, MO; CAS 427-51-0, purity 97.3%, 100 mg/kg/d) were prepared using corn oil as vehicle. Thioacetamide (Sigma, St. Louis, MO; CAS 62-55-5, purity 99.2%, 19.2 mg/kg/d), Wy-14643 (TCI America, Portland, OR; CAS 50892-23-4; purity 100%; 60 mg/kg/d), Phenobarbital (Sigma, St. Louis, MO; CAS 50-06-6, purity >99%, 80 mg/kg/d), Piperonylbutoxide (Sigma, St. Louis, MO; CAS 51-03-6; purity 88.5%; 1200 mg/kg/d), Dehydroepiandrosterone (Sigma, St. Louis, MO; CAS 53-43-0, purity 100%, 600 mg/kg/d), Acetamide (Sigma, St. Louis, MO; CAS 60-35-5, purity 99%, 3000 mg/kg/d), Methapyrilene hydrochloride (Sigma, St. Louis, MO; CAS 135-23-9; purity >99%; 60 mg/kg/d), Methylcarbamate (Sigma, St. Louis, MO; CAS 598-55-0, purity 99.2%, 400 mg/kg/d), Diethylstilbestrol (Sigma, St. Louis, MO; CAS 56-53-1; purity 99%; 10 mg/kg/d), Ethionine (Sigma, St. Louis, MO; CAS 67-21-0; purity >99%; 200 mg/kg/d), Cefuroxime (Sigma, St. Louis, MO; CAS 55268-75-2; purity not provided%; 250 mg/kg/d), and Nifedipine (Sigma, St. Louis, MO; 21829-25-4; purity 99%; 3 mg/kg/d) were dosed using Carboxymethyl Cellulose as vehicle. Diethylstilbestrol and Piperonylbutoxide were administered for 1, 3, and 7 days. All other compounds were dosed for 1, 3, 7, and 14 days. Time points selected for evaluation in this report are listed in Table 1. The rationale for dose selection was based on those reported to induce liver tumors in the two-year rat bioassay [8]. From each treatment group three animals that showed at least some changes in the liver as observed by histopathological examination were selected for microarray analysis [8]. Time-matched control groups of equal size treated with the corresponding vehicles methylcellulose (MC) or corn oil (CO), served as a reference to determine the changes in gene expression upon treatment.
Table 1. Overview of compounds.
Class | Compound | Short name | CAS number | Vehicle | Dosing time [d] | Dose [mg/kg/d] | IARC class |
Genotoxic carcinogens (GC) | C.I Direct Black | CIDB | 1937-37-7 | CO | 7 | 146 | 1 |
Dimethylnitrosamine | DMN | 62-75-9 | CO | 7 | 4 | 2A | |
Undefined compounds | Cyproterone acetate | CPA | 427-51-0 | CO | 14 | 100 | - |
Thioacetamide | TAA | 62-55-5 | CMC | 7 | 19.2 | 2B | |
Wy-14643 | WY | 50892-23-4 | CMC | 3 | 60 | - | |
Non-genotoxic carcinogens (NGC) | Phenobarbital | PB | 50-06-6 | CMC | 14 | n/a | 2B |
Piperonylbutoxide | PBO | 51-03-6 | CMC | 3 | 1200 | 3 | |
Dehydroepiandrosterone | DHEA | 53-43-0 | MC | 14 | 600 | - | |
Acetamide | AA | 60-35-5 | MC | 14 | 3000 | 2B | |
Methapyrilene HCl | MPy | 135-23-9 | MC | 7 | 60 | - | |
Methylcarbamate | Mcarb | 598-55-0 | MC | 14 | 400 | 3 | |
Diethylstilbestrol | DES | 56-53-1 | MC | 3 | 10 | 1 | |
Ethionine | ETH | 67-21-0 | MC | 14 | 200 | - | |
Non-carcinogens (NC) | Cefuroxime | CFX | 55268-75-2 | CMC | 14 | 250 | - |
Nifedipine | Nif | 21829-25-4 | CMC | 14 | 3 | - |
The table lists all compounds that were repeatedly administered to male Wistar rats for a time span of up to 14 days. The time point where the strongest deregulation was observed on the mRNA level was determined for each compound individually based on results from a preceding study by Ellinger-Ziegelbauer et al. [8]. For each compound, the corresponding short name, which was used in the figures and text, is denoted. Furthermore, the vehicle and dose used for oral application is listed.
Messenger-RNA expression profiling
To monitor global changes in mRNA expression, biotin-labeled cRNA samples were prepared with a starting amount of 5 µg of total RNA according to the manufacturer's instructions (Affymetrix, USA; GeneChip Expression Analysis 701194 Rev.1) and hybridized on Affymetrix GeneChip RAE230A arrays. Fluorescent images of the GeneChips were captured with the Affymetrix GeneChip Scanner 3000. Raw data image files (DAT) were converted into CEL files using Affymetrix Microarray Suite (MAS) 5.0 in which the scan data from the 36 pixels per oligo set are summarized as one intensity value. The RAE230A array used in this study contains 15.866 probe sets, corresponding to approx. 5399 annotated rat genes and 10467 expressed-sequence tags (EST).
For a complete description of the experimental protocol the reader is referred to a former publication from Ellinger-Ziegelbauer et al. [8]. The quality of the raw data was assessed based on diverse plots and statistics implemented in the package arrayQualityMetrics for R/Bioconductor [15], [16]. No experimental problems were detected and all chips were found to have sufficient quality. Background correction, normalization between arrays, and probe summarization were performed based on the Robust Multi-chip Average (RMA) technique implemented in the affy package for R/Bioconductor.
Micro-RNA expression profiling
100 ng total RNA was end-labeled using the Agilent miRNA labeling kit (Agilent p/n 5190–0456). End-labeled miRNA samples were purified using Qiagen PCR clean up columns. Labeled miRNA samples were hybridized according to the Agilent miRNA Microarray System with miRNA Complete Labeling and Hyb Kit Protocol G4170-90011 V2.2 October 2009 using reagents contained in the Agilent miRNA labeling kit. Prior to array hybridization, hybridization mixtures were denatured at 100°C for 5 minutes. Hybridization was carried out at 20 RPM at a temperature of 55°C for 20 hours before washing in Agilent Gene Expression Wash Buffer 1 and Agilent Gene Expression Wash Buffer 2 (Agilent p/n 5188–5327). Hybridization, scanning, and image analysis were performed using the Agilent DNA Microarray Scanner equipped with extended dynamic range (XDR) software according to the Agilent miRNA Microarray System with miRNA Complete Labeling and Hyb Kit Protocol G4170–90011 V2.2 October 2009. Agilent Feature Extraction Software v10.7 was used for data extraction from raw microarray image files.
As previously done for the mRNA expression data, we ensured sufficient quality of the raw data by performing quality checks implemented in the R library arrayQualityMetrics, which supports a wide variety of microarray platforms [15]. In order to compensate for experimental artifacts and variation between arrays, the raw data was preprocessed using a variant of the RMA algorithm that was specifically implemented for Agilent miRNA microarrays by Lopez-Romero et al. [17]. The RMA implementation from the AgiMicroRna library for R/Bioconductor was used without the initial background correction step, as recommended by Lopez-Romero et al., who recently demonstrated that this normalization technique facilitates a more accurate estimation of miRNA expression levels than the method suggested by the array manufacturer [18]. Oligos that were not expressed in any of the profiled samples were not considered in further analysis steps. In order to link miRNAs to global gene expression, putative regulatory interactions were inferred between miRNAs and experimentally confirmed and predicted target mRNAs. For this purpose, a non-redundant set of validated miRNA/mRNA interactions was compiled by combining information from the databases TarBase v5.0c [19], miRTarBase v2.4 [20], and miRecords v3 [21]. Predicted miRNA targets were collected with the miRNA target prediction tools ElMMo v5 [22], DIANA-microT v4.0 [23], and TargetScan v5.2 [24].
Protein expression profiling
Protein expression profiling was performed using reverse-phase protein microarrays (RPPAs) on the ZeptoMARK assay platform (Bayer Technology Services, Leverkusen, Germany). Frozen liver tissue (50–80 mg tissue) was weighted into a cryovial and grinded to a fine powder under liquid nitrogen. 8 volumes of lysis buffer were added to the pulverized tissue and lysis was carried out in a rotating mixer for 30 min. Protein concentration of the lysate was determined by a Bradford assay and protein concentration of the lysates was adjusted to 0.3 mg/ml protein. The prepared lysates were used to print RPPAs as described in detail by Pirnia et al. [25]; samples and reference material (BSA labeled with Alexa-647) were spotted (300 pl/spot) on Zeptosens hydrophobic protein microarray chips (Bayer Technology Services, Leverkusen, Germany). Detection of proteins and protein modifications was performed using a direct two-step immunoassay using specific primary antibodies (see supplement). Fluorescence signal was generated using Alexa647-labeled anti-species secondary antibodies (Invitrogen, Darmstadt, Germany), images of the microarrays were taken using the ZeptoREADER microarray imager (Bayer Technology Services, Leverkusen, Germany), and image analysis was performed using the ZeptoVIEW Pro 3.0 software package. Signal intensity for each spot was determined as background-corrected mean intensity with the local background subtracted from the spot intensity and the determined values were normalized over the whole RPA. The weighted mean of replicate sample spots was used for statistical analysis; standard deviation was calculated according to standard error propagation rules from the standard deviations of raw and blank signals.
For the sake of improved interpretability, the blank-corrected normalized signal levels were divided by the median of the corresponding control group samples incubated with the same specific antibody and subsequently log2-transformed. If the background signal level, which was determined by exclusive use of the secondary antibody, exceeded the combined signal level of both the primary specific and secondary antibodies when used in combination, the corresponding measurement was considered as a missing value. Missing values, which accounted for approx. 1% of the data, were estimated using k-Nearest-Neighbor imputation.
Inference of predictive molecular signatures
Predictive signatures were inferred based on the fold changes obtained from multiple omics platforms using recursive feature selection with SVMs (SVM-RFE). SVM-RFE repeatedly trains an SVM on the provided features and assigns a weight for each feature depending on the relevance for the classification [26]. After each training cycle, the least informative features are removed and the training is repeated with the reduced set of features. This process is repeated until the desired signature size is reached.
To find the optimal signature size, we evaluated the predictive power of signatures of different size for each supervised machine learning method used for classification. Signatures containing 5, 10, 15, 20, and 25 features were extracted and evaluated for their predictive power. Based on the accuracies estimated for each of the differently sized signatures, we used spline interpolation to numerically approximate the optimal signature size.
As multiple signatures were extracted for each cross-validation fold and repetition, the individual signatures were merged into a consensus signature. For this purpose, the features were ranked by their average rank in all cross-validation folds and repetitions. The consensus signature was then constructed by selecting the best features until the approximated optimal signature size was reached.
Calculation of molecular interaction features
As the regulation of gene expression is orchestrated by the interplay of multiple biological layers, an approach that assesses the relevance of each genomic and proteomic feature individually may be insufficient. In order to account for the highly interconnected nature of gene regulatory mechanisms, we conceived a novel feature representation for multi-level omics datasets, which captures characteristic molecular interactions present upon treatment with a specific class of compounds (Figure 1A).
As the dynamic range of differential expression varies between platforms interrogating different biological layers, we propose to transform the log-ratios, i.e., log2(fold changes), to a common scale. Furthermore, the scaling of the data also ensures that each platform contributes equally to the score computed for a certain molecular interaction. All log-ratios x were mapped to the same interval using the linear function with , where and is the set of all log-ratios observed for a certain platform. Next, we computed a score for each putative interaction between two molecules (e.g., miRNA and target mRNA), which equals the product of the scaled log-ratios: , where and with . This molecular interaction (MI) score is expected to be close to 1 if correlated expression is observed, e.g., for an mRNA and the corresponding protein product. If the MI score is close to −1 this indicates a strong anticorrelation, which may be observed between a miRNA and one of its target mRNAs. We considered negative correlations between miRNAs and their targeted mRNAs, positive correlations between mRNAs and translated proteins, and negative correlations between miRNAs and proteins that are translated from the targeted mRNAs. Both validated mRNA targets from curated databases (TarBase v5.0c [19], miRTarBase v2.4 [20], miRecords v3 [21]) and predicted mRNA targets inferred by prediction tools (ElMMo v5 [22], DIANA-microT v4.0 [23], TargetScan v5.2 [24]) were used for feature construction.
Calculation of pathway enrichment features
The basic idea of this feature type is to generate a more robust representation of the molecular signature of a compound by abstraction from genes to pathways (Figure 1B). To this end, we propose to first detect the differentially expressed transcripts/proteins by defining appropriate filter criteria. In this study, we considered genes with an absolute fold change above 2.5 as significantly differentially expressed. Next, we combined the lists of deregulated genes by computing the union across platforms. For this purpose, all profiled mRNAs and proteins were mapped to their corresponding genes, which can in turn be attributed to pathways. Since miRNAs are a priori not contained in canonical pathways (e.g., from KEGG, Ingenuity, etc.), their regulatory influence on pathways was modeled based on experimentally validated interactions to known target mRNAs corresponding to pathway nodes. Overrepresented pathways for this combined gene list, derived from deregulated mRNAs, miRNA targets, and proteins, were detected with a hypergeometric test. Given a universe where the union of all pathways contains N genes of which M are in the pathway of interest, and the combined list containing n genes of which m are contained in the pathway, the p-values were computed according to the following formula:
The p-values were then transformed into enrichment scores, which correspond to the -log10(p-value). Finally, a vector composed of the enrichment scores of each pathway was employed as a numeric feature representation of pathway alterations induced by compound treatment. The higher the enrichment score computed for a certain pathway, the more significant is the overrepresentation of genes from the combined list in this pathway. The feature vectors were constructed based on different sets of canonical pathways extracted from the databases KEGG [27], Reactome [28], and BioCarta [29]. Associations from genes to pathways were derived with the corresponding metadata packages available for R/Bioconductor [16].
Validation of prediction models
We ensured unbiased parameter tuning and evaluation on independent test compounds by employing a 2×2-fold nested, stratified cross-validation procedure. In order to obtain a more robust estimate of the classification performance, 10 repetitions were performed with different random splits of the data. The prediction accuracy that can be achieved with different feature representations derived from the expression profiles of the compounds was assessed based on the average area under the ROC curve observed for a representative selection of machine learning methods that are prevalent in toxicogenomics applications. We employed linear Support Vector Machines (SVM), Random Forests (RF), Neural Networks (NN), Bayesian Generalized Linear Models (BGLM), and Principal Component Regression (PCR). We included PCR because a good separation of classes was observed in a principal component analysis (PCA) of the data, and because the method achieved comparable accuracy than the other methods on the here evaluated classification problems. We have also analyzed the optimal number of principal components used for classification with PCR (Figure S1). RF, NN, BGLM, and PCR are implemented in the caret library available for R [30]. The SVM was used via the R interface provided by the SHOGUN machine learning toolbox [31].
Results
Classification performance of omics signatures
With the goal to identify molecular signatures that may allow early prediction of a carcinogenic risk associated with a compound, we inferred mRNAs, miRNAs, and protein expression signatures correlated with the toxicological classes of the compounds which induced these signatures in the liver of rats treated for up to 14 days. In addition, a combined signature was obtained by merging the signatures extracted from each individual platform. Furthermore, we compiled signatures based on putative molecular interactions (MI features) observed between two molecular layers, as well as based on pathways enriched with genes/proteins that were detected as deregulated (PE features). These two types of cross-platform features (Figure 1) were joined in different arrangements with the combined single-platform signatures in order to create different types of hybrid signatures. Signature inference and evaluation were performed in a 2×2 cross-validation setting for three different class contrasts (C:NGC+GC vs. NC, NGC vs. GC, NGC vs. NC) using five established supervised classification methods (Figure 2). The evaluation process was repeated ten times with different random cross-validation splits and then ROC curves were generated based on the prediction scores obtained in each run (Figure S2). In order to assess the prediction accuracy, we calculated the average area under the curve (AUCs) for each contrast, classifier, and signature type.
Since in most cases an increased average AUC was observed for the combined signatures, we can conclude that composite signatures derived from multiple platforms, may allow for a more accurate compound classification than the traditionally used single-platform signatures (Figure 3). The only exception was the protein signature for the NGC vs. GC contrast, which outperformed the corresponding combined signature for this special setting (Figure 3B). In comparison to the mRNA signature (the current standard approach in toxicogenomics) and the miRNA signature, the combined signature provided a consistent improvement of AUCs. Interestingly, the integration of our novel MI and PE features led to a further increase in terms of the average AUC. For C vs. NC and NGC vs. GC discrimination, the use of hybrid signatures including the new features consistently resulted in higher classification accuracy than using all single-platform signatures even if combined (Figure 3A, C). For the NGC vs. NC contrast the effect was very small, but still the signatures containing the MI features achieved a slightly better AUC than the combined signature. The combination of all signatures (i.e., the combined signature plus the MI and PE features) achieved the best AUCs in two of the three contrasts and the second best in the C vs. NC contrast. Furthermore, the prediction accuracy of the single-platform signatures was found to heavily depend on the contrast under evaluation. In the NGC vs. GC contrast, both the mRNA and the miRNA signatures performed significantly worse than in the other two contrasts, whereas the protein signature was inferior in terms of accuracy in the C vs. NC contrast. On the contrary, we observed that the combined signature and the hybrid signatures complemented by the MI and PE features achieved high (AUC>0.95) and robust AUCs independent of the evaluated class contrast.
Predictive features for toxicogenomics models
For each classifier, consensus signatures were generated by combining the feature rankings inferred from random data splits, which correspond to different repetitions of the cross-validation procedure. The extracted signatures are shown in Table S1 for C vs NC discrimination, Table S2 for NGC vs GC discrimination and Table S3 for NGC vs NC discrimination. The most informative genes and proteins for distinguishing C from NC are illustrated in the heatmaps in Figure 4. A correlation between gene expression and carcinogenicity could be observed for the mRNA signature (Spearman's ρ>0.5). However, both the informative miRNAs and proteins do not show clear, carcinogen-specific expression patterns. In particular, some of the top miRNA and protein features (e.g., rno_miR_34a and CYP2C8) show uncharacteristic expression changes in the PB and PBO samples (see Figure 4B,C). These findings are consistent with the fact that a lower classification performance was observed for these two signature types (Figure 3). The heatmaps showing the top features of the single platform signatures for the NGC vs. GC and NGC vs. NC contrast are shown in Figure S3 and S4, respectively.
The most informative mRNA markers for C vs. NC discrimination include various genes known to be involved in cellular responses to carcinogenic exposure, e.g., Gsta5, Aldh1a1 [32], [33], Ephx1 [34], and Akr7a3 [35], which are detoxifying enzymes, for instance, in the context of oxidative stress. Some miRNAs identified in our experiments as early markers for prediction of a carcinogenic potential are also mentioned in connection with cancer in the literature, e.g., rno-miR-34a and rno-miR-200b [36], [37]. Furthermore, the protein signature for C vs. NC discrimination also contains proteins that have been linked to carcinogenesis, e.g., JUN [38], GLUL [39], and CDKN1B [40].
As has been done for the single-platform signatures, consensus signatures were generated based on the MI and PE signatures extracted for each run. The most informative pathways for the C vs. NC and NGC vs. GC contrasts are depicted in the heatmap in Figure 5.
The top PE features for the discrimination of carcinogens from non-carcinogens were highly specific for carcinogens and showed no enrichment at all in the non-carcinogens (Figure 5A). For the discrimination of genotoxic and non-genotoxic carcinogens, specific pathways could be inferred for both genotoxic and non-genotoxic carcinogens (Figure 5B). Only one of the three DMN samples shows an uncharacteristic enrichment pattern. Except for this outlier, the pathways altered in GC-exposed rats are highly specific, showing strong enrichment in the genes deregulated upon GC, but not upon NGC treatment. Consistent with our expectations, various pathways related to p53, which is a key gene in the cellular DNA damage response, were selected as GC-specific pathway features [41]. The NGC-specific pathways include cytokine and interferon signaling pathways, which have been associated with non-genotoxic carcinogenesis before [42]. These pathways are also specific for the discrimination of NGCs and NCs (Figure S5).
The MI consensus signature for the discrimination of carcinogenic and non-carcinogenic compounds is depicted in Figure 6. We highlighted interactions where both interacting molecules were at least 1.5-fold (50%) up- or downregulated. While a negative correlation in the expression pattern was expected for putative miRNA-mRNA interactions (i.e., upregulated miRNA and downregulated mRNA and vice-versa), a positive correlation was expected for mRNAs and proteins corresponding to the same gene. Using SVM-based recursive feature elimination (SVM-RFE), we identified diverse putative interactions specific for carcinogens. These interactions also involved several genes that have previously been associated with carcinogenesis in the rat, such as Glul [39], Dusp1 [43], Jun [38], Sgk1 [44], and Mgat4b [45]. Correlated changes at the transcription and translation level that were exclusively observed after treatment with rat hepatocarcinogens were found for the genes Glul and Jun (Figure 6 and S6). Putative interactions that were specifically found for NGCs include the anti-correlation between the miRNA rno-miR-29b and its potential target mRNAs, Sgk1, and Mgat4. For the non-carcinogens, we did not observe any putative interactions affecting multiple molecular layers.
In summary, the extracted cross-platform signatures showed that specific pathways and informative molecular interactions could be identified which were characteristically affected after short-term treatment of rats with hepatocarcinogens in general, as well as with non-genotoxic and genotoxic carcinogenesis. Furthermore, we demonstrated that using these complex markers as supplementary features for the prediction of the compound class resulted in improved cross-validation performance when compared to traditional single-platform-based signatures.
Toxicogenomics-based classification of undefined compounds
The three compounds CPA, TAA, and WY are generally described as non-genotoxic rodent hepatocarcinogens, yet due to inconclusive results from genotoxicity assays, one could also consider a genotoxic carcinogenic mode of action concerning rodent hepatocarcinogenesis. For instance, although a negative Ames test indicating a non-genotoxic mode of action with respect to carcinogenicity was reported for CPA [46], Martelli et al. reported a positive micronucleus test in female rats [47]. For TAA, the Ames test was also negative, while mixed results were observed in a micronucleus test for genotoxicity [48], [49]. WY is classified as an NGC belonging to the subclass of peroxisome proliferators with respect to rodent hepatocarcinogens [50]. However, Deutsch et al. reported a positive result in a Comet assay for WY [51], and clastogenicity was observed in two cell types, albeit at near cytotoxic doses [52]. Therefore, these compounds were not considered as sufficiently and reliably labeled substances suited for training and validation of our prediction models. Instead, we used the signatures inferred from the compounds that could be clearly assigned to a carcinogenic mode of action class to classify these three compounds, employing the same set of classifiers used to assess the prediction accuracy of the inferred signatures. In addition, a principal components analysis (PCA) was performed by transforming the vector of signature features for each compound into a two-dimensional space spanned by the two principal components explaining most of the variance in the data. This should facilitate comparison of the complex, high-dimensional expression patterns observed for the different compounds.
The PCA plots resulting from two different signatures for NGC vs. GC discrimination are shown in Figure 7A–B. The PCA plot in Figure 7A is generated from the mRNA expression signature, since mRNA signatures have generally been used before for such classification problems. Although the three classes – GC, NGC, and NC are separated based on mRNA expression only, the GC and NGC class are relatively close together, and the WY samples are placed outside of these three classes. On the contrary, the PCA based on the signature incorporating all single-platform (mRNA, miRNA, and protein) and cross-platform features (PE and MI) showed a clear separation of the compound classes (see Figure 7B). Furthermore, all undefined compounds were enclosed in the NGC cluster, and thus could be clearly classified with our toxicogenomics-derived signature. From Figure 7C–D and Figure S8 it becomes obvious that the PCA-based classification of WY, CPA, and TAA as NGCs is in accordance with the classification achieved with the supervised learning algorithms. The classification solely based on the protein and miRNA signature, respectively, is inconsistent for some of the CPA and TAA samples and on average only possible at a lower confidence level (Figure S8). However, after training of the prediction models on all combined features, high confidence scores and a robust classification across all employed learning algorithms were achieved. In conclusion, all undefined compounds were classified as non-genotoxic carcinogens based on their molecular profiles. These results are also consistent with the outcomes of diverse carcinogenicity assays which were performed for WY, TAA, and CPA [46], [48], [50].
Discussion
In this study, we propose a new approach for prediction of potential chronic toxicity of chemicals based on expression data obtained from multiple omics platforms after short-term treatment. Prediction of the compound class after short-term treatment may facilitate hazard assessment during preclinical testing and may allow prioritization of chemicals with respect to their cancerogenic potential in chronic bioassays. The current standard approach in toxicogenomics is to use microarrays to screen for differential expression of mRNAs and infer signatures based on fold changes between treated and non-treated animals. Here, we argue that the inclusion of other omics data, e.g., miRNA expression or protein abundance, may increase the predictive power of the inferred signatures. Further, we introduce two new feature representations developed specifically for multi-platform omics data, the molecular interaction (MI) features and the pathway enrichment (PE) features.
With extensive cross-validation, we evaluated the predictive power of single-platform signatures as well as hybrid signatures complemented with cross-platform features on a dataset containing mRNA, miRNA, and protein expression data for 8 NGCs, 2 GCs, and 2 NCs concerning rodent hepatocarcinogenicity. In addition, all signatures were used to classify three rodent hepatocarcinogens with insufficiently defined mode of actions. The dataset used for the evaluation is publically available from the NCBI Gene Expression Omnibus (GEO) repository under the accession number GSE53085 [53], [54].
In comparison to the signatures inferred solely from the mRNA data, we observed an increase in predictive power when combining signatures across multiple platforms for all evaluated class contrasts (C vs. NC, NGC vs. GC, and NGC vs. NC). In addition, we found that the inclusion of complex cross-platform features capturing molecular interactions or pathway alterations led to a further improvement of the classification performance. In general, the combined single-platform signatures with MI and PE features were superior to the single-platform signatures in terms of prediction accuracy, except for the NGC vs. GC contrast, where the protein signature performed slightly better. However, visual inspection of the informative features by PCA revealed a much better separation of classes for the cross-platform signatures (Figure S7). Furthermore, a potential bias may arise from the fact that not the complete proteome, but only a selection of 158 proteins proposed by domain experts were profiled in our experiments. Thus, we hold the opinion that in following studies the predictive power of protein signatures should be assessed on a richer set of compounds based on global protein expression data. Altogether, while a high variability was observed for the classification performance achieved with individual single-platform signatures, a consistently high prediction confidence (AUCs>0.9) was found for models provided with features from multiple molecular layers. Considering all evaluated class contrasts, the combined signature with pathway enrichment and molecular interaction features on average achieved the best classification with the highest prediction accuracies (AUCs>0.95).
In related toxicogenomics studies the accuracy of classifiers trained solely on omics-based features has been compared to models exclusively or additionally provided with features derived from a Quantitative Structure-Activity Relationship (QSAR) approach [55], [56]. Liu et al. and Low et al. consistently reported that the integration of QSAR-based features did not contribute to an increased classification performance [55], [56]. Since there is a strong heterogeneity concerning the structures and mechanisms of hepatocarcinogenic compounds, the inference of relations between chemical structures and the complex phenotype of cancer is a challenging problem. In this study, we did not pursue this approach since a richer set of compounds would have been required for the construction of generalizable models [57]. Furthermore, a QSAR approach may not be ideally suited for predicting chronic toxicity, as it only considers structural properties of the compounds and does not account for important experimental factors, such as dose level and duration of treatment.
As an alternative to our complex supervised approach for compound class discrimination, we applied clustering to determine if the expression profile based grouping of the compounds agrees with their annotated carcinogenic class (Figure S9). For this purpose, we selected the top 100 mRNAs, miRNAs, and proteins based on their average differential expression, measured in terms of the absolute fold-change averaged across samples. Complete linkage hierarchical clustering with Euclidean distance was applied and the optimal number of clusters between 2 and 8 was determined based on the silhouette score. While animals treated with the same compound mostly clustered together, the cluster result did not reflect the initial grouping of the compounds according to their carcinogenic class (i.e., GC, NGC, or NC). This finding indicated that due to the high mechanistic diversity of the compounds, whereas a classification is possible by using supervised methods.
The single- and cross-platform signatures inferred with our supervised approach have been used to reclassify the compounds with undefined class, i.e., CPA, TAA, and WY. All three compounds are known to be carcinogenic, but some of the genotoxicity test results were inconclusive [46]–[51]. Here, all three compounds were classified as non-genotoxic carcinogens by the majority of classifiers trained on the inferred molecular signatures. Much higher prediction confidence was observed when using the cross-platform signatures, whereas single-platform-based classification remained ambiguous. Again, these findings were consistent with a PCA showing a considerably clearer separation of the classes for the cross-platform signatures (Figures 7 and S7).
In contrast to the standard toxicogenomics approach of inferring signatures from mRNA expression, the combination of single-platform signatures from multiple omics platforms led to improved prediction accuracy. The inclusion of the MI and PE features into these combined signatures offered a true cross-platform integration of the multi-level omics data. These integrated features may yield additional information for supervised learning methods and provide new insights for mechanistic analyses of cross-platform omics data. In addition, the PE features introduce an abstraction from the level of individual genes to higher-order levels, such as complex signaling or metabolic networks. Possibly, this abstraction led to a more robust representation of the complex mechanisms underlying early events during hepatocarcinogenesis in rat. Other relevant mechanistic aspects, which cannot be detected by analyzing each platform individually, may be captured by the here introduced MI features. In consideration of the fact that uncertainty was introduced in the signature extraction process by permitting predicted miRNA-mRNA interactions as potential features, the implication of individual, predictive molecular interactions during hepatocarcinogenesis has to be critically assessed. However, since the focus of this study was the proof of principle that considering multiple molecular layers and interactions between them may increase the reliability of toxicogenomics-based prediction models, the experimental validation and confirmation of the biological relevance of the selected features is beyond the scope of this article.
Due to the broad availability of mRNA expression data for toxicogenomics applications (e.g., from the databases TG-GATEs [9] and DrugMatrix [58]) and the proof-of-principle provided for mRNA signatures, several lists of informative mRNA probe sets have been published for both rat and mouse models concerning prediction of a hepatocarcinogenic potential in short-term studies. Most of these studies focused on the discrimination of non-genotoxic carcinogens from non-carcinogens (NGC vs. NC contrast) or on distinguishing carcinogens from non-carcinogens (C vs. NC contrast). We compared our mRNA signature with previously published signatures from Auerbach et al. [6] and Nakayama et al. [59] (C vs. NC signatures); Fielden et al. [60], Nie et al. [61], and Uehara et al. [10], [11] (NGC vs. NC signatures); and Ellinger-Ziegelbauer et al. [8] (NGC vs. GC vs. NC signature). An overview of the informative genes shared between the published and our signatures is given in Table 2. Our NGC vs. NC signature based on mRNA data contained no common genes with the signatures by Fielden et al., Nie et al., and Uehara et al. (2011), and only one common gene with Uehara et al. (2008): Akr7a3. However, these studies used other microarray platforms, different compounds, and different treatment durations: Nie et al. and Uehara et al. (2008) used a single dosage 24 h setting, Fielden et al. used a 5 day repeated dosage setting, and Uehara et al. (2011) used a longer 28-day exposure. For the C vs. NC signature published by Nakayama et al., we found five genes that are also present in our C vs. NC mRNA signature (see Figure S10), while only one common gene is shared between our signature and the 90-day signature published by Auerbach et al. The signature published previously by Ellinger-Ziegelbauer et al. was in part inferred from the same set of samples analyzed in this study. Hence, we found that 6 probe sets (27%) were in common with our 22-probe-set C vs. NC mRNA signature (see Figure S10) and 7 probe sets (28%) with our 25-probe-set NGC vs. GC signature.
Table 2. Comparison with published signatures.
Signature | Contrast | Dosing time [d] | Common genes |
Nakayama et al. (2006) [59] | C vs. NC | 28 | Aldh1a1, Akr7a3, Ephx1, Apoa4, Abcb1a |
Auerbach et al. (2010) [6] | C vs. NC | 90 | Abcb1a |
Ellinger-Ziegelbauer et al. (2008) [8] | C vs. NC | up to 14 | Aldh1a1, Akr7a3, Abcc3, Myc, Ces2c, Abcb1a |
Ellinger-Ziegelbauer et al. (2008) [8] | NGC vs. GC | up to 14 | Aldh1a1, Cdkn1a1 (2 probes), Phlda3, Myc, Hsp90ab1, Abcc3 |
Nie et al. (2006) [61] | NGC vs. NC | 1 | - |
Fielden et al. (2007) [60] | NGC vs. NC | 5 | - |
Uehara et al. (2008) [10] | NGC vs. NC | 1 | Akr7a3 |
Uehara et al. (2011) [11] | NGC vs. NC | 28 | - |
The table lists the common genes between our inferred signatures and previously published signatures for the discrimination of carcinogenic and non-carcinogenic chemicals. We compared each published signature with our inferred signature for the same contrast and identified the informative genes common between the signatures.
In summary, we demonstrated that the classification performance of toxicogenomics models benefits from integrating heterogeneous omics data across multiple biological levels. Along these lines, we believe that future toxicogenomics studies may benefit from the additional consideration of other levels, such as metabolomics, relevant DNA mutations, and genome-wide promoter methylation. Furthermore, our work may encourage the maintainers of currently available databases specializing in toxicogenomics (e.g., TG-GATEs [9], DrugMatrix, etc.) to amend the existing repertoire of mRNA expression datasets by the addition of complementary omics data derived from the same biological samples.
Supporting Information
Acknowledgments
We are grateful to Joanne Quinney from CXR Biosciences, who provided technical support in generating the miRNA array data. Furthermore, we thank all involved partners from the MARCAR consortium for fruitful discussions and critical remarks.
Funding Statement
The research leading to these results has received funding from the Innovative Medicine Initiative Joint Undertaking (IMI JU) under grant agreement nr. 115001 (MARCAR project). The authors acknowledge support by Deutsche Forschungsgemeinschaft and Open Access Publishing Fund of Tuebingen University. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
References
- 1.Silva Lima B, Van der Laan JW (2000) Mechanisms of nongenotoxic carcinogenesis and assessment of the human hazard. Regul Toxicol Pharmacol. 32: : 135–143. Available: 10.1006/rtph.2000.1427. Accessed 26 March 2013. [DOI] [PubMed] [Google Scholar]
- 2.Hernández LG, van Steeg H, Luijten M, van Benthem J (2009) Mechanisms of non-genotoxic carcinogens and importance of a weight of evidence approach. Mutat Res Mutat Res. 682: : 94–109. Available: http://www.sciencedirect.com/science/article/pii/S1383574209000428. Accessed 27 March 2013. [DOI] [PubMed] [Google Scholar]
- 3.Benigni R, Bossa C, Tcheremenskaia O (2013) Nongenotoxic carcinogenicity of chemicals: mechanisms of action and early recognition through a new set of structural alerts. Chem Rev. 113: : 2940–2957. Available: http://www.ncbi.nlm.nih.gov/pubmed/23469814. Accessed 5 December 2013. [DOI] [PubMed] [Google Scholar]
- 4. Waters MD, Jackson M, Lea I (2010) Characterizing and predicting carcinogenicity and mode of action using conventional and toxicogenomics methods. Mutat Res 705: 184–200 10.1016/j.mrrev.2010.04.005 [DOI] [PubMed] [Google Scholar]
- 5.Afshari CA, Hamadeh HK, Bushel PR (2011) The evolution of bioinformatics in toxicology: advancing toxicogenomics. Toxicol Sci. 120 Suppl:S225–37. Available: http://toxsci.oxfordjournals.org/content/120/suppl_1/S225.short. Accessed 14 November 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Auerbach SS, Shah RR, Mav D, Smith CS, Walker NJ, et al. (2010) Predicting the hepatocarcinogenic potential of alkenylbenzene flavoring agents using toxicogenomics and machine learning. Toxicol Appl Pharmacol. 243: : 300–314. Available: http://www.sciencedirect.com/science/article/pii/S0041008X09004943. Accessed 5 December 2013. [DOI] [PubMed] [Google Scholar]
- 7. Ellinger-Ziegelbauer H, Stuart B, Wahle B, Bomann W, Ahr HJ (2005) Comparison of the expression profiles induced by genotoxic and nongenotoxic carcinogens in rat liver. Mutat Res 575: 61–84 10.1016/j.mrfmmm.2005.02.004 [DOI] [PubMed] [Google Scholar]
- 8. Ellinger-Ziegelbauer H, Gmuender H, Bandenburg A, Ahr HJ (2008) Prediction of a carcinogenic potential of rat hepatocarcinogens using toxicogenomics analysis of short-term in vivo studies. Mutat Res 637: 23–39 10.1016/j.mrfmmm.2007.06.010 [DOI] [PubMed] [Google Scholar]
- 9. Uehara T, Ono A, Maruyama T, Kato I, Yamada H, et al. (2010) The Japanese toxicogenomics project: application of toxicogenomics. Mol Nutr Food Res 54: 218–227 10.1002/mnfr.200900169 [DOI] [PubMed] [Google Scholar]
- 10. Uehara T, Hirode M, Ono A, Kiyosawa N, Omura K, et al. (2008) A toxicogenomics approach for early assessment of potential non-genotoxic hepatocarcinogenicity of chemicals in rats. Toxicology 250: 15–26 10.1016/j.tox.2008.05.013 [DOI] [PubMed] [Google Scholar]
- 11.Uehara T, Minowa Y, Morikawa Y, Kondo C, Maruyama T, et al. (2011) Prediction model of potential hepatocarcinogenicity of rat hepatocarcinogens using a large-scale toxicogenomics database. Toxicol Appl Pharmacol. 255: : 297–306. Available: http://www.ncbi.nlm.nih.gov/pubmed/21784091. Accessed 16 November 2012. [DOI] [PubMed] [Google Scholar]
- 12.Schmitz-Spanke S, Rettenmeier AW (2011) Protein expression profiling in chemical carcinogenesis: a proteomic-based approach. Proteomics. 11: : 644–656. Available: http://www.ncbi.nlm.nih.gov/pubmed/21246732. Accessed 6 March 2014. [DOI] [PubMed] [Google Scholar]
- 13.Yokoi T, Nakajima M (2011) Toxicological implications of modulation of gene expression by microRNAs. Toxicol Sci. 123: : 1–14. Available: http://toxsci.oxfordjournals.org/content/123/1/1.short. Accessed 6 March 2014. [DOI] [PubMed] [Google Scholar]
- 14.Khan SR, Baghdasarian A, Fahlman RP, Michail K, Siraki AG (2013) Current status and future prospects of toxicogenomics in drug discovery. Drug Discov Today. Available: http://www.sciencedirect.com/science/article/pii/S1359644613003954. Accessed 21 February 2014. [DOI] [PubMed]
- 15. Kauffmann A, Gentleman R, Huber W (2009) arrayQualityMetrics—a bioconductor package for quality assessment of microarray data. Bioinformatics 25: 415–416 10.1093/bioinformatics/btn647 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Gentleman RC, Carey VJ, Bates DM, Bolstad B, Dettling M, et al. (2004) Bioconductor: open software development for computational biology and bioinformatics. Genome Biol. 5: : R80. Available: http://genomebiology.com/2004/5/10/R80. Accessed 12 November 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17. López-Romero P (2011) Pre-processing and differential expression analysis of Agilent microRNA arrays using the AgiMicroRna Bioconductor library. BMC Genomics 12: 64 10.1186/1471-2164-12-64 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18. López-Romero P, González MA, Callejas S, Dopazo A, Irizarry RA (2010) Processing of Agilent microRNA array data. BMC Res Notes 3: 18 10.1186/1756-0500-3-18 [DOI] [PMC free article] [PubMed] [Google Scholar]
- 19.Papadopoulos GL, Reczko M, Simossis VA, Sethupathy P, Hatzigeorgiou AG (2009) The database of experimentally supported targets: a functional update of TarBase. Nucleic Acids Res. 37: : .D155–8 Available: http://nar.oxfordjournals.org/content/37/suppl_1/D155.short. Accessed 21 November 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Hsu S-D, Lin F-M, Wu W-Y, Liang C, Huang W-C, et al. (2011) miRTarBase: a database curates experimentally validated microRNA-target interactions. Nucleic Acids Res. 39: : D163–9. Available: http://nar.oxfordjournals.org/content/39/suppl_1/D163.full. Accessed 9 November 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 21.Xiao F, Zuo Z, Cai G, Kang S, Gao X, et al. (2009) miRecords: an integrated resource for microRNA-target interactions. Nucleic Acids Res. 37: : D105–10. Available: http://nar.oxfordjournals.org/content/37/suppl_1/D105.short. Accessed 20 November 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22.Gaidatzis D, van Nimwegen E, Hausser J, Zavolan M (2007) Inference of miRNA targets using evolutionary conservation and pathway analysis. BMC Bioinformatics 8: : 69. Available: http://www.biomedcentral.com/1471-2105/8/69. Accessed 20 November 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23.Maragkakis M, Reczko M, Simossis VA, Alexiou P, Papadopoulos GL, et al. (2009) DIANA-microT web server: elucidating microRNA functions through target prediction.Nucleic Acids Res. 37: : W273–6. Available: http://nar.oxfordjournals.org/content/37/suppl_2/W273.short. Accessed 21 November 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 24.Lewis BP, Shih I, Jones-Rhoades MW, Bartel DP, Burge CB (2003) Prediction of Mammalian MicroRNA Targets. Cell 115: : 787–798. Available: http://www.sciencedirect.com/science/article/pii/S0092867403010183. Accessed 4 December 2013. [DOI] [PubMed] [Google Scholar]
- 25. Pirnia F, Pawlak M, Thallinger GG, Gierke B, Templin MF, et al. (2009) Novel functional profiling approach combining reverse phase protein microarrays and human 3-D ex vivo tissue cultures: expression of apoptosis-related proteins in human colon cancer. Proteomics 9: 3535–3548 10.1002/pmic.200800159 [DOI] [PubMed] [Google Scholar]
- 26.Guyon I, Weston J, Barnhill S, Vapnik V (2002) Gene selection for cancer classification using support vector machines. Mach Learn: 389–422.
- 27.Kanehisa M, Goto S (2000) KEGG: kyoto encyclopedia of genes and genomes. Nucleic Acids Res 28: : 27–30. Available: http://www.pubmedcentral.nih.gov/articlerender.fcgi?artid=102409&tool=pmcentrez&rendertype=abstract. Accessed 13 March 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Matthews L, Gopinath G, Gillespie M, Caudy M, Croft D, et al. (2009) Reactome knowledgebase of human biological pathways and processes. Nucleic Acids Res. 37: : D619–D622. Available: http://www.pubmedcentral.nih.gov/articlerender.fcgi?artid=2686536&tool=pmcentrez&rendertype=abstract. Accessed 5 March 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29.Nishimura D (2001) BioCarta. Biotech Softw Internet Rep. 2: : 117–120. Available: http://online.liebertpub.com/doi/abs/10.1089/152791601750294344. Accessed 13 March 2013. [Google Scholar]
- 30.Kuhn M (n.d.) Building Predictive Models in R Using the caret Package. J Stat Softw. 28 Available: http://ideas.repec.org/a/jss/jstsof/28i05.html. Accessed 12 December 2013
- 31. Sonnenburg S, Rätsch G (2010) The SHOGUN machine learning toolbox. … Mach Learn … 11: 1799–1802. [Google Scholar]
- 32.Hayes JD, Pulford DJ, Ellis EM, McLeod R, James RF, et al. (1998) Regulation of rat glutathione S-transferase A5 by cancer chemopreventive agents: Mechanisms of inducible resistance to aflatoxin B1. Chem Biol Interact. 111: : 51–67. Available: http://www.sciencedirect.com/science/article/pii/S0009279797001518. Accessed 11 December 2013. [DOI] [PubMed] [Google Scholar]
- 33.McMillian M, Nie AY, Parker JB, Leone A, Bryant S, et al. (2004) A gene expression signature for oxidant stress/reactive metabolites in rat liver. Biochem Pharmacol. 68: : 2249–2261. Available: http://www.sciencedirect.com/science/article/pii/S0006295204005805. Accessed 11 December 2013. [DOI] [PubMed] [Google Scholar]
- 34.Yates MS, Kwak M-K, Egner PA, Groopman JD, Bodreddigari S, et al. (2006) Potent protection against aflatoxin-induced tumorigenesis through induction of Nrf2-regulated pathways by the triterpenoid 1-[2-cyano-3-,12-dioxooleana-1,9(11)-dien-28-oyl]imidazole. Cancer Res. 66: : 2488–2494. Available: http://cancerres.aacrjournals.org/content/66/4/2488.short. Accessed 14 November 2013. [DOI] [PubMed] [Google Scholar]
- 35.Dewa Y, Nishimura J, Muguruma M, Jin M, Kawai M, et al. (2009) Involvement of oxidative stress in hepatocellular tumor-promoting activity of oxfendazole in rats. Arch Toxicol. 83: : 503–511. Available: http://www.ncbi.nlm.nih.gov/pubmed/18754104. Accessed 11 December 2013. [DOI] [PubMed] [Google Scholar]
- 36.Dutta KK, Zhong Y, Liu Y-T, Yamada T, Akatsuka S, et al. (2007) Association of microRNA-34a overexpression with proliferation is cell type-dependent. Cancer Sci. 98: : 1845–1852. Available: http://www.ncbi.nlm.nih.gov/pubmed/17888029. Accessed 11 December 2013. [DOI] [PubMed] [Google Scholar]
- 37.Tryndyak VP, Ross SA, Beland FA, Pogribny IP (2009) Down-regulation of the microRNAs miR-34a, miR-127, and miR-200b in rat liver during hepatocarcinogenesis induced by a methyl-deficient diet. Mol Carcinog. 48: : 479–487. Available: http://www.ncbi.nlm.nih.gov/pubmed/18942116. Accessed 20 November 2013. [DOI] [PubMed] [Google Scholar]
- 38.Sakai M, Okuda A, Hatayama I, Sato K, Nishi S, et al. (1989) Structure and Expression of the Rat c-jun Messenger RNA: Tissue Distribution and Increase during Chemical Hepatocarcinogenesis. Cancer Res. 49: : 5633–5637. Available: http://cancerres.aacrjournals.org/content/49/20/5633.short. Accessed 4 December 2013. [PubMed] [Google Scholar]
- 39.DeBerardinis RJ, Cheng T (2010) Q's next: the diverse functions of glutamine in metabolism, cell biology and cancer.Oncogene. 29: : 313–324. Available: 10.1038/onc.2009.358. Accessed 17 November 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 40.Nishimura J, Dewa Y, Okamura T, Muguruma M, Jin M, et al. (2008) Possible involvement of oxidative stress in fenofibrate-induced hepatocarcinogenesis in rats. Arch Toxicol 82: : 641–654. Available: http://www.ncbi.nlm.nih.gov/pubmed/18253720. Accessed 11 December 2013. [DOI] [PubMed] [Google Scholar]
- 41.Lopes UG (1997) p53-dependent Induction of Apoptosis by Proteasome Inhibitors. J Biol Chem 272: : 12893–12896. Available: http://www.jbc.org/content/272/20/12893.full. Accessed 4 December 2013. [DOI] [PubMed] [Google Scholar]
- 42.Roberts RA (1999) Cytokines in non-genotoxic hepatocarcinogenesis. Carcinogenesis. 20: : 1397–1402. Available: http://carcin.oxfordjournals.org/content/20/8/1397.short. Accessed 3 December 2013. [DOI] [PubMed] [Google Scholar]
- 43.Feo F, Frau M, Tomasi ML, Brozzetti S, Pascale RM (2009) Genetic and epigenetic control of molecular alterations in hepatocellular carcinoma. Exp Biol Med (Maywood). 234: : 726–736. Available: http://ebm.sagepub.com/content/234/7/726.full. Accessed 7 November 2013. [DOI] [PubMed] [Google Scholar]
- 44.Won M, Park KA, Byun HS, Kim Y-R, Choi BL, et al. (2009) Protein kinase SGK1 enhances MEK/ERK complex formation through the phosphorylation of ERK2: Implication for the positive regulatory role of SGK1 on the ERK function during liver regeneration. J Hepatol. 51: : 67–76. Available: http://www.sciencedirect.com/science/article/pii/S0168827809002256. Accessed 4 December 2013. [DOI] [PubMed] [Google Scholar]
- 45.Liu X, Dewaele S, Vanhooren V, Fan Y-D, Wang L, et al. (2010) Alteration of N-glycome in diethylnitrosamine-induced hepatocellular carcinoma mice: a non-invasive monitoring tool for liver cancer. Liver Int. 30: : 1221–1228. Available: http://www.ncbi.nlm.nih.gov/pubmed/20524982. Accessed 4 December 2013. [DOI] [PubMed] [Google Scholar]
- 46.Lang R, Redmann U (1979) Non-mutagenicity of some sex hormones in the Ames salmonella/microsome mutagenicity test. Mutat Res 67: : 361–365. Available: http://www.ncbi.nlm.nih.gov/pubmed/384238. Accessed 11 December 2013. [DOI] [PubMed] [Google Scholar]
- 47.Martelli A, Brambilla Campart G, Ghia M, Allavena A, Mereto E, et al. (1996) Induction of micronuclei and initiation of enzyme-altered foci in the liver of female rats treated with cyproterone acetate, chlormadinone acetate, or megestrol acetate. Carcinogenesis. 17: : 551–554. Available: http://www.ncbi.nlm.nih.gov/pubmed/8631143. Accessed 11 December 2013. [DOI] [PubMed] [Google Scholar]
- 48.Chieli E, Aliboni F, Saviozzi M, Malvaldi G (1987) Induction of micronucleated erythrocytes by primary thioamides and their metabolites in the mouse. Mutat Res. 192: : 141–143. Available: http://www.ncbi.nlm.nih.gov/pubmed/3657843. Accessed 11 December 2013. [DOI] [PubMed] [Google Scholar]
- 49.Mirkova ET (1994) Activity of the rodent carcinogen 1,4-dioxane in the mouse bone marrow micronucleus assay. Mutat Res. 322: : 142–144. Available: http://www.ncbi.nlm.nih.gov/pubmed/7519322. Accessed 11 December 2013. [DOI] [PubMed] [Google Scholar]
- 50.Cattley RC, Popp JA (1989) Differences between the promoting activities of the peroxisome proliferator WY-14,643 and phenobarbital in rat liver. Cancer Res. 49: : 3246–3251. Available: http://www.ncbi.nlm.nih.gov/pubmed/2566380. Accessed 11 December 2013. [PubMed] [Google Scholar]
- 51.Deutsch WA, Kukreja A, Shane B, Hegde V (2001) Phenobarbital, oxazepam and Wyeth 14,643 cause DNA damage as measured by the Comet assay. Mutagenesis. 16: : 439–442. Available: http://www.ncbi.nlm.nih.gov/pubmed/11507244. Accessed 11 December 2013. [DOI] [PubMed] [Google Scholar]
- 52. Lefevre PA, Tinwell H, Galloway SM, Hill R, Mackay JM, et al. (1994) Evaluation of the genetic toxicity of the peroxisome proliferator and carcinogen methyl clofenapate, including assays using Muta Mouse and Big Blue transgenic mice. Hum Exp Toxicol 13: 764–775. [DOI] [PubMed] [Google Scholar]
- 53.Edgar R (2002) Gene Expression Omnibus: NCBI gene expression and hybridization array data repository. Nucleic Acids Res. 30: : 207–210. Available: http://nar.oxfordjournals.org/content/30/1/207.short. Accessed 6 November 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 54.Barrett T, Wilhite SE, Ledoux P, Evangelista C, Kim IF, et al. (2013) NCBI GEO: archive for functional genomics data sets—update. Nucleic Acids Res. 41: : D991–5. Available: http://nar.oxfordjournals.org/content/41/D1/D991.short. Accessed 12 November 2013. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 55.Low Y, Uehara T, Minowa Y, Yamada H, Ohno Y, et al. (2011) Predicting drug-induced hepatotoxicity using QSAR and toxicogenomics approaches. Chem Res Toxicol. 24: : 1251–1262. Available: 10.1021/tx200148a. Accessed 27 February 2014. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 56.Liu Z, Kelly R, Fang H, Ding D, Tong W (2011) Comparative analysis of predictive models for nongenotoxic hepatocarcinogenicity using both toxicogenomics and quantitative structure-activity relationships. Chem Res Toxicol. 24: : 1062–1070. Available: 10.1021/tx2000637. Accessed 7 March 2014. [DOI] [PubMed] [Google Scholar]
- 57.Rusyn I, Sedykh A, Low Y, Guyton KZ, Tropsha A (2012) Predictive modeling of chemical hazard by integrating numerical descriptors of chemical structures and short-term toxicity assay data. Toxicol Sci. 127: : 1–9. Available: http://toxsci.oxfordjournals.org/content/127/1/1.full#ref-48. Accessed 10 March 2014. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 58. Ganter B, Snyder RD, Halbert DN, Lee MD (2006) Toxicogenomics in drug discovery and development: mechanistic analysis of compound/class-dependent effects using the DrugMatrix database. Pharmacogenomics 7: 1025–1044 10.2217/14622416.7.7.1025 [DOI] [PubMed] [Google Scholar]
- 59.Nakayama K, Kawano Y, Kawakami Y, Moriwaki N, Sekijima M, et al. (2006) Differences in gene expression profiles in the liver between carcinogenic and non-carcinogenic isomers of compounds given to rats in a 28-day repeat-dose toxicity study. Toxicol Appl Pharmacol 217: : 299–307. Available: http://www.sciencedirect.com/science/article/pii/S0041008X0600319X. Accessed 6 December 2013. [DOI] [PubMed] [Google Scholar]
- 60. Fielden MR, Brennan R, Gollub J (2007) A gene expression biomarker provides early prediction and mechanistic assessment of hepatic tumor induction by nongenotoxic chemicals. Toxicol Sci 99: 90–100 10.1093/toxsci/kfm156 [DOI] [PubMed] [Google Scholar]
- 61.Nie AY, McMillian M, Parker JB, Leone A, Bryant S, et al. (2006) Predictive toxicogenomics approaches reveal underlying molecular mechanisms of nongenotoxic carcinogenicity. Mol Carcinog. 45: : 914–933. Available: http://www.ncbi.nlm.nih.gov/pubmed/16921489. Accessed 7 March 2013. [DOI] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.