毒物基因组学在制药工业中的作用--毒理学网
用户名:
密  码:

毒物基因组学在制药工业中的作用

来源:   浏览量:634   更新日期:2010年1月12日
Toxicogenomics in the pharmaceutical industry: Hollow promises or real benefit?

Anke Lühe , Laura Suter, Stefan Ruepp, Thomas Singer, Thomas Weiser and Silvio Albertini
F. Hoffmann-La Roche Ltd., Non-Clinical Drug Safety, 4070 Basel, Switzerland

Abstract

Almost 10 years ago, microarray technology was established as a new powerful tool for large-scale analysis of gene expression [1]. Soon thereafter the new technology was discovered by toxicologists for the purpose of deciphering the molecular events underlying toxicity, and the term “ Toxicogenomics ” appeared in scientific literature [2]. Ever since, the toxicology community was fascinated by the multiplicity of sophisticated possibilities toxicogenomics seems to offer: genome-wide analysis of toxicant-induced expression profiles may provide a means for prediction of toxicity prior to classical toxicological endpoints such as histopathology or clinical chemistry. Some researchers even speculated of the classical methods being superfluous before long. It was assumed that by using toxicogenomics it would be possible to classify compounds early in drug development and consequently save animals, time, and money in pre-clinical toxicity studies. Moreover, it seemed within reach to unravel the molecular mechanisms underlying toxicity. The feasibility of bridging data derived from in vitro and in vivo systems, identifying new biomarkers, and comparing toxicological responses “across-species” was also excessively praised. After several years of intensive application of microarray technology in the field of toxicology, not only by the pharmaceutical industry, it is now time to survey its achievements and to question how many of these wishes and promises have really come true.

Keywords: Toxicogenomics ; Expression profiling; Microarray; Mechanism of toxicity; Prediction of toxicity; Toxicology

The development of a new drug is long, costly and complex. The overall cost per drug can be as high as US$ 900 million; however, even this scale of investment does not automatically bring success. The possibility of failure instead of reaching the market is high and this is focussing thinking and research on what are perceived to be critical roadblocks. Analysis of the commonest causes of failure has shown that toxicological findings account for approximately 20% of compound attrition.

Toxicogenomics as outlined in this review continues to offer possibilities of improving prediction of toxicities at an earlier stage than currently, especially if the data is taken together with complimentary data from toxicoproteomics, toxicometabonomics, histopathology, clinical chemistry etc. In addition, this integrated approach holds promise of rapid identification of mechanisms of toxicity. This will aid decision making on compound progression as different mechanisms of toxicity have different relevance to human toxicities.

For such an approach to be viable, a database containing relevant information from each of the different methods and technologies is required. At the time of writing such a database is not available.

1. Proof of concept

Proving the concept should always be the first step in implementing a new technology. Soon after the first “Tox-arrays” became available, some suppliers tried to promote them as an already “established” technology. However, the first results of the Technical Committee on Application of Genomics to Mechanism-Based Risk assessment created by the International Life Science Institute (ILSI) and Health and Environmental Life Science (HESI) clearly demonstrated that despite good interlaboratory agreement regarding the biological pathways affected by the compounds investigated, there is remarkable room for improvement, particularly regarding the comparability of different platforms and the different attempts towards analysis of the data [3] and [4]. Confidence in microarray-derived data has suffered immensely, especially among the “classical” toxicologists. By encouraging high expectations in toxicogenomics and proposing even the redundancy of traditional toxicology, researchers obviously did the second step sooner than the first. During the last years reasonable diligence had to be exercised aiming at the critical assessment of microarray technologies and microarray-derived data, in order to make up for these probably overhasty pronouncements. Studies have been conducted to investigate biological and technical variability [5], [6], [7] and [8], to evaluate methods for data analysis and interpretation [9], [10] and [11], and to assess the benefit of combination of different “-omics” technologies [12]. It has become clear that toxicogenomics would not be able, at least within near future, to replace the “gold standards”. The question arose whether toxicogenomics will in any case be able to reflect the results derived from histopathology or clinical chemistry. This needed to be addressed as soon as possible. Has gene expression profiling reached the highly ambitious goal of being comparable to the traditional methods by now? Can we announce that this technology should be implemented as an everyday routine? This manuscript allows a closer look at some recent studies, which have already been published in distinguished scientific journals, in order to provide some answers to the questions above.

1.1. Prediction of toxicity and classification of compounds

It is believed that toxicogenomics could contribute largely to an early and reliable prediction of the toxic liabilities of compounds and hence prevent the animal-, cost-, and time-intensive execution of pre-clinical or even clinical trials with inadequate compounds [13]. Prior to the successful application of such an approach, it is crucial to create a database covering a comprehensive amount of expression profiles of well-described model compounds in order to acquire gene expression signatures (fingerprints) related to certain organ toxicity. Likewise, an effectual bioinformatics support providing algorithms amenable for the correct classification of developmental compounds in comparison to the database profiles is of utmost importance. The establishment of such databases is time-consuming and cost-intensive. Nevertheless, during the past years great efforts have been channeled towards the generation of high-quality gene expression data for classification purposes. Among the publicly available databases, ArrayExpress (operated by EMBL-European Bioinformatics Institute) and the Gene Expression Omnibus (GEO, operated by the National Center for Biotechnology Information) are the most noted ones. Despite the incorporation of data derived from different platforms and hybridization protocols, which may hamper mathematical handling and overpower toxicity-specific signatures, data integrity was ensured by restricting entry of data to the compliance with minimal information about microarray experiments (MIAME) standards. In addition to the non-commercial resources, commercial providers, such as Gene Logic, Inc. (ToxExpress?) or Iconix Pharmaceuticals, Inc. (DrugMatrix?) offer comprehensive instruments for assessment of the toxic potential of a compound. Unfortunately, these tools are highly expensive. Therefore, some pharmaceutical companies have started to build their own integrative databases and have already succeeded in applying them for predicting potential hepatotoxicity of compounds [14] and [15]. For example Steiner et al. [15] trained a binary support vector machine (SVM) aiming at the optimal discrimination between hepatotoxic and non-toxic compounds. Additionally, a second SVM model was developed in order to differentiate even between different modes of hepatotoxicity. SVMs belong to the family of supervised learning algorithms and offer the opportunity of recognizing characteristic patterns in a given set of training data and to subsequently employ these patterns for the classification of previously undefined samples. Stringent criteria in terms of cross-validation (CV), selection of discriminating features and assignment of known profiles to the toxic/non-toxic classes (binary SVM) or control/direct acting/cholestatic/steatotic/PPAR agonist classes (multiclass SVM) of the training set were applied in order to gain an optimal classification performance. Remarkably, all vehicle-treated controls of the test set were correctly identified as non-toxic and almost 90% of the toxic test samples were classified as toxic (Table 1). Regarding the multiclass model, it was furthermore possible to predict the correct mode of toxicity with high specificity (Table 2). Although three toxic compounds of the test set could not be correlated to any toxic mode of action, indicating that the model might produce some false-negatives, no false-positives were detected. The false-negative predictions in both SVM models were not ascribable to any structural or pharmacological properties of the test compounds and are likely to ameliorate with growing amounts of training data. This highlights that supervised algorithms such as the described SVM approach are highly beneficial for classification of hepatotoxic compounds, especially in very early developmental stages.

Table 1.Performance of the toxic/non-toxic model and summarized results of the binary (toxic/non-toxic) classification

Arrays/groups for classification

ν-SVM

C-SVM

Classification under external CV

 26 treatment groups

20 of 26 groups correct

22 of 26 groups correct

 116 arrays

89 of 116 arrays correct

90 of 116 arrays correct

 34 control groups

32 of 34 groups correct

32 of 34 groups correct

 163 arrays

154 of 163 arrays correct

154 of 163 arrays correct

 

Classification of test set

 19 treatment groups

16 of 19 groups correct

17 of 19 groups correct

 91 arrays

74 of 91 arrays correct

74 of 91 arrays correct

 63 control groups

63 of 63 groups correct

63 of 63 groups correct

 332 arrays

322 of 332 arrays correct

327 of 332 arrays correct

Adapted from Steiner et al. (2004) [15]: ν-SVM and C-SVM are two SVM algorithms using slightly different mathematical parameters. For details see [15].

Table 2. Performance summary of the ν-SVM-based model discriminating between different modes of toxicity (MOT)

Arrays/groups for classification

Summary

26 treatment groups

20 of 26 treatment groups correct MOT identified

 

22 of 26 treatment groups correctly identified as toxic

 

116 microarrays

85 of 116 microarrays correctly classified

34 control groups

33 of 34 groups correctly identified as vehicle controls

163 microarrays

160 of 163 microarrays correctly classified

 

Classification of independent test set

 19 treatment groups

15 of 19 treatment groups correct MOT identified

 

15 of 19 treatment groups correctly identified as toxic

 

 91 microarrays

74 of 91 microarrays correctly classified

 63 treatment groups

All (63 of 63) groups correctly identified

 332 microarrays

330 of 332 microarrays correctly classified

Adapted from Steiner et al. (2004), for details see [15].

1.2. Investigation of molecular mechanisms of organ toxicity

There have been several publications employing toxicogenomics to provide insight into the mechanism of different organ toxicities. As classical targets of toxic events after drug application, the liver and the kidney have been extensively investigated [16], [17], [18], [19], [20] and [21]. Other organs such as the uterus [22] or the nervous system [23] have also been addressed. The publication by Suter et al. [18] exemplifies the use of toxicogenomics for clarification of the molecular mechanisms underlying the effects of two 5HT6 receptor antagonists on the liver. In this study, Wistar rats received two closely related 5HT6 receptor antagonists, in the following referred to as compound A (known to be steatotic in rats) and compound B (non-hepatotoxic) following an acute and a subchronic study design. Histopathology examination clearly detected fatty changes and microsteatosis in the liver of rats treated with compound A.

Hierarchical clustering of genes regulated above two-fold (p < 0.05) and subsequent heat map visualization showed that the two compounds could be clearly differentiated by their acute transcriptional profile (Fig. 1), with the steatotic compound inducing more and larger changes in gene expression than the non-toxic one. Additionally, a dose-dependent increase in the number of regulated genes could be observed after subchronic exposure to the steatotic compound. After further analysis of changed genes a hypothesis regarding the potential mechanism of toxicity induced by compound A could be generated: CYP2B2, CYP2C6 and CYP3A1 mRNA were particularly up-regulated by the steatotic compound in a dose-dependent manner. These cytochromes are known to be inducible by Phenobarbital [24]. A link between Phenobarbital-response enhancer elements of some Phenobarbital-induced cytochrome P450‘s and cholesterol synthesis and has been described previously [25]. Together with reduced serum cholesterol observed in the current study, a causal relation between the inhibition of cholesterol synthesis, the induction of CYP2B2 and the fat accumulation in the liver was suggested. In summary, this study provides a strong support for the creation of mechanistic hypotheses based on microarray-derived information and demonstrates that gene expression profiles could definitely be anchored to classic toxicological endpoints.


Fig. 1. Adapted from [18]: heat map visualization of 85 genes regulated in response to treatment (at least two-fold change, P-value ≤0.05, colour intensity corresponds to the amplitude of induction (red) or repression (blue), respectively). For cluster analysis an algorithm calculating the distance function by employing the average linkage method was used.

In this context, another study by Huang et al. [19] shows that toxicogenomics can also provide insight into the mechanisms underlying Cisplatin-induced nephrotoxicity. The transcriptional changes occurring after treatment of rats with two doses of Cisplatin were assessed by employing cDNA microarrays. In kidneys of rats treated with Cisplatin the epithelial cells of the proximal tubules showed necrosis accompanied by scattered apoptosis. Additionally, interstitial inflammatory infiltrates and dilated tubules were observed.

After statistical analysis, Huang and colleagues identified 22 genes, which exhibited significant alterations (>two-fold) in their expression after treatment with Cisplatin. They were able to assign these 22 genes to eight categories of different biochemical functions, which were in agreement with the toxic mode of action of Cisplatin described in literature.

Moggs et al. [22] have set another fascinating example of successful application of toxicogenomics in unraveling mechanisms of toxicity through investigation of the transcriptional changes accompanying uterine growth after estrogen treatment. Mice were administered with 17β-estradiol and sacrificed at 1, 2, 4, 8, 24, 48 and 72 h after dosing. By combining histopathology and analysis of gene expression changes, it was possible to establish four distinct phases in uterotrophic growth induced by estrogenic compounds. The first phase (1–4 h) was morphologically characterized by a clear increase in uterine weight resulting from elevated fluid uptake. This was paralleled by the modulation of genes involved in intra- or intercellular signaling, particularly in regulation of vascular permeability. Additionally, transcriptional regulators engaged in cell proliferation and differentiation showed increased expression. In the second phase (4–8 h) no further increase in uterine weight was noted. However, genes involved in mRNA and protein synthesis were induced, indicating a coordinated induction of genes in order to ensure sufficient capacity for biosynthesis in the following third phase (8–24 h), during which the uterine weight appeared to double. Transcriptional changes in this phase mainly occurred with genes responsible for replication of chromosomal DNA, completion of the cell division cycle and for maintenance of genome integrity. Together with the modulation of genes involved in cytoarchitectural remodeling, which was observed in the fourth phase (24–72 h) the results deliver a profound picture of the transcriptional cascade underlying the phenotypic changes associated with estrogen-induced uterine growth.

1.3. Identification of new biomarkers

Regarding the early prediction of toxic liabilities of compounds preferably in a high-throughput screening system, the use of safety biomarkers (for definition see [26]) is also of considerable value. Nevertheless, valid markers, which reliably reflect or even predict the toxic outcome of drug treatment, are still scarce. In the past, many biomarkers have only been discovered by chance and have eventually proven their suitability during widespread application in pre-clinical and clinical trials. The identification of specific biomarkers furthermore requires an extensive knowledge of the particular mechanism underlying each type of toxicity. In contrast, “-omics” technologies provide an inductive approach for the identification of new sets of indicators of toxicity, which does not necessarily presuppose prior mechanistic knowledge. As an example, Thome-Kromer et al. [27] and Bandara et al. [28] have described the successful application of proteomics for the identification of biomarkers for liver and kidney toxicity. Moreover, several publications addressing the discovery of potential genetic marker sets by using toxicogenomics have already been reviewed by Goodsaid [29]. Amin et al. [20] exemplify the suitability of toxicogenomics for the identification of potential markers of nephrotoxicity. This is of utmost interest, as traditional indicators of renal damage, such as blood urea nitrogen (BUN) or creatinine, are usually not measurable until 75% of the nephrons have been destroyed [30]. Nevertheless, it has to be emphasized that a comprehensive evaluation of the validity of the markers identified by toxicogenomics is exceptionally important.

Summarizing the above, there is plenty of evidence for toxicogenomics having reached a state of “proven concept”. Prediction of hepatotoxic or nephrotoxic liabilities in rats and classification of compounds seem feasible now. Toxicogenomics has also proven its suitability in characterizing mechanistic networks triggering toxic outcomes and has furthermore led to the successful identification of new potential biomarkers. Although this may allow considering toxicogenomics as an established technology, the question remains among toxicologists whether there is really a need to implement a quite expensive technology delivering results, which simply reflect the well-described traditional endpoints? The vital demand for additional value arose mainly due to the high expectations, which were raised in the early days of toxicogenomics. However, building a stable basis and providing evidence that gene expression analysis is able to reflect the current standards was a critical prerequisite in order to move on to more challenging issues which are not tackled by the traditional methods so far (Fig. 2).


Fig. 2. Schematic overview of toxicogenomics versus established methods in toxicology. Despite having proven the concept by properly reflecting the results generated by several established methods for toxicity testing, the question remains, whether toxicogenomics might be able to provide additional knowledge with regards to problems, which currently cannot be addressed by the traditional methods.

2. Potential added value provided by toxicogenomics

The recent withdrawal of Vioxx (rofecoxib) from the worldwide market due to safety concerns clarifies once more that there is still a need for improvement of the current industrial strategies for the evaluation of safety of new drugs during their development. Obviously, the traditionally conducted safety assessments, although well-established and undoubtedly valuable, still fail to detect some adverse drug reactions that may potentially occur in humans. In this context, the high expectations laid in the application of “-omics” technologies in toxicology become clearer. By using toxicogenomics, more sensitive and thus earlier detection of potential adverse effects of compounds seemed to be within reach, as there is strong belief that alterations in the expression of genes would precede the manifestation of toxic outcome [31]. Analysis of gene expression patterns was furthermore assumed to help identifying drug–drug interactions [32] and to provide insight into the genetical circumstances, which form the basis of idiosyncratic toxicity [31] and [33]. Additionally, the speculations about using in vitro samples, especially from human cell cultures, or even human blood samples fuelled enthusiastic prospects of gaining authentic human-relevant information. The genome-wide comparison and extrapolation of expression patterns across several species seemed also feasible after the sequencing of the human and mouse genome have been practically completed in 2001 [34] and 2002 [35], respectively. Taken together, analysis of transcriptional alterations after toxic manipulation was expected to deliver various additional information supplementing (or even outdating?) the currently employed techniques in safety evaluation. Thus, after having proven the concept, toxicogenomics now faces the question, to what extent the demand for added value can truly be fulfilled (Fig. 2).

2.1. Sensitivity of toxicogenomics versus traditional endpoints

Histopathologic examination of paraffin-embedded organ sections serves as one of the “gold-standards” for detection of organ toxicity. Integrity of organs and especially effects on cellular subpopulations are routinely investigated by experienced pathologists. Nevertheless, microscopic evaluation of hundreds of organ sections is very time-consuming and toxic lesions have to become manifested for detection. Compound-related alterations at the molecular level preceding morphological findings also remain unseen. Thus, in order to be more sensitive, toxicogenomics should facilitate prediction of toxicity either at lower doses or prior to the appearance of morphological changes. Addressing this issue, some work groups employing toxicogenomics reported the identification of a toxic outcome due to compound treatment prior to its recognition by histopathology or clinical chemistry [18], [36] and [37]. For example Kier et al. [36] first identified a subset of genes, potentially predictive for the development of kidney lesions. Subsequently, by analysis of transcriptional regulation of these genes 24 h after treatment with cyclophosphamide or ganciclovir, the nephrotoxic outcome was successfully predicted previous to tubular necrosis being apparent earliest at 72 h after treatment. Although this looks very promising, one has to bear in mind that first all these studies were conducted with well-studied model compounds, where it was already known what to look for and second that histopathology was the standard on which the predictive models were built [15]. Additionally, it seems questionable, whether toxicogenomics could really save time and costs in such short-term studies, taking into account processing of tissue samples for microarray hybridization and especially subsequent analysis of transcript profiles. In contrast, when looking at life-time carcinogenicity studies, the potential savings of time and costs might be much more distinct. The publication of Ellinger-Ziegelbauer et al. [38] exemplified that toxicogenomic profiling of genotoxic carcinogens known to produce tumors in 2-year carcinogenicity studies, revealed genes and pathways indicative for beginning tumorigenesis already in short-term in vivo studies.

In conclusion, in vivo toxicogenomics might not be able to considerably accelerate safety prediction in acute short-term studies and the detection of sub-organ-specific toxicity will also remain challenging for at least 5% of the cells in an organ homogenate need to be affected in order facilitate detection of alterations by gene expression profiling [39]. Nevertheless, there is good evidence that in terms of early detection of toxic events, which usually take time to develop, such as carcinogenesis, toxicogenomic approaches might prove very valuable. Additionally, there is still hope that toxicogenomics might facilitate the detection of toxicity already at lower doses than those leading to the development of manifest lesions visible in histopathology. This would predestine the use of toxicogenomics in very early stages of drug development, when the amount of compound is still limited. Unfortunately, published investigations addressing this issue are missing so far.

2.2. Detection and prediction of idiosyncratic toxicity

Unexpected adverse drug reactions, which do not involve any of its known pharmacological properties and which furthermore occur randomly and usually dose-independently in patients, are commonly referred to as “idiosyncratic” effects. The reasons rendering a compound liable to a high incidence of idiosyncratic reactions in patients are not yet understood. However, there have been several speculations about factors possibly increasing the likelihood of drugs to induce such reactions. Formation of reactive metabolites and induction of cellular stress or immune responses have been suggested, although none of these theories has ever been proven. Additionally, it appears that not only the properties of the compound are responsible for the development of idiosyncratic reactions, but there is also some kind of predisposition existing among susceptible individuals. Unfortunately, suitable animal models for studying idiosyncratic reactions are lacking so far [40]. Orphanides and Kimber [33] have suggested that the use of microarray-based single nucleotide polymorphism (SNP)-mapping approaches might identify the genetic circumstances associated with a high susceptibility of individuals to develop idiosyncratic adverse drug responses. Furthermore, Uetrecht [41] speculated that compounds with a high incidence of such effects might induce specific and predictive gene expression patterns even in animals or patients who do not develop idiosyncratic reactions. Despite the fact that toxicogenomics might certainly have the power to shed light on the mechanism underlying the idiosyncratic toxicity of single compounds such as trovafloxacin [42], the hope for using toxicogenomics technologies to predict the likelihood of a compound for causing these unspecific toxic reactions, must still be considered as very challenging.

2.3. Multi-chemical exposures and drug–drug interactions

In addition to adverse drug reactions exhibited by single compounds, the interaction of multiple drugs when taken by a patient in combination, remain mainly unpredictable and have been a major reason for the withdrawal of drugs from the market. Aardema and MacGregor [32] suggested the use of toxicogenomics in unveiling the effects of multi-drug exposures. Synergistic, antagonistic or additive effects might be reflected in the gene expression profiles induced by compound mixtures when compared to the profiles of the single chemicals. But taking into account the difficulties already associated with the analysis and interpretation of gene expression data derived from single compound exposures, the extraction of useful information out of multiple-chemical profiles might turn out to be even more challenging. Thus, the application of toxicogenomic approaches to successfully predict drug–drug interactions is still in its infancy.

2.4. Extrapolation of toxicity information across species

In drug development toxicologists have always been faced with the same dilemma: safety assessment of new compounds cannot be done by just testing on people. Experimental in vitro and in vivo animal models are needed as a substitute to evaluate the safety risk for humans, although only 71% of all human toxicities can be accurately predicted by using animal models [43] and [44]. At least in part this can be ascribed to species-specific differences in pharmacokinetic handling of the compounds [44]. The example of peroxisome proliferator-activating receptor agonists, which cause carcinogenicity in rats and mice, but have appeared to be “clean” in primates and humans so far [45], [46] and [47], additionally questions the suitability of animals as surrogates for humans.

With this in mind, it is not surprising that great hope was laid into toxicogenomics as a tool for reliable across-species extrapolations [32] and [48]. In 2001, sequencing of the human genome has finally been completed by the human genome project [34] soon followed by the completion of the mouse genome [35] and a first draft sequence of the rat genome [49]. These achievements additionally supported the hope for genome-wide comparisons of expression profiles across species to facilitate the explanation of species-derived differences in the response to compound treatment. Gene Logic, Inc., for example have built a rat gene expression profile database by using compounds supposed to be toxic or non-toxic in humans in order to predict human toxicity. However, considering the long development times for new drugs, the availability of this database has possibly been too short to evaluate its benefit properly.

A study conducted in our laboratories provided evidence that at least in some cases it might be possible to predict toxicity across species [37]. Three different antidiabetic compounds were investigated in short-term rat studies. Histopathology declared two of these compounds being steatotic, whereas the third one did not cause any visible signs of hepatotoxicity. In contrast, a SVM-based analysis of the rat gene expression profiles (for details regarding SVM training and optimization of parameters see [15]) classified all three compounds as steatotic. Follow-up studies truly identified the third compound as steatotic in dogs with histopathology showing liver necrosis and microsteatosis. Likewise, all three compounds produced an increase in intracellular triglyceride content of rat hepatocytes. In order to determine the human relevance of these results further confirmatory experiments are certainly needed.

Although additional evidence for successful inter-species extrapolations is missing so far, toxicogenomics undoubtedly provides valuable information about the toxic mode of action of a compound in different species, which in the long-term automatically improves our understanding of inter-species relations.

2.5. Potential applicability of toxicogenomics to non-invasive toxicity assessment

In general, mRNA derived from of tissue or biopsy samples from animals or patients are processed and hybridized for microarray analysis. In order to assess the safety of new drug candidates much earlier in development, it is crucial to facilitate the use of non-invasive methods for sample collection. These methods would typically include the use of in vitro systems or blood samples. The use of blood samples would allow multiple sampling from the same animal and maybe even the translation of preclinical findings to a clinical setting. Employment of in vitro systems would be largely valuable especially with regard to the establishment of high-throughput toxicity screens very early in drug development. Cell culture systems offer the advantages of quick and easy handling, low cost, and may reduce the number of laboratory animals needed in early safety assessment. Additionally, the utilization of human cell lines or human primary cells might help to generate more human-relevant data. There have already been numerous approaches applying in vitro methods to toxicogenomics [50], [51] and [52], but only few addressing the correlation between in vitro and in vivo data [21] and [53].

In vitro systems are usually subject to various limitations when compared to the whole organism. Recently, a study conducted in our laboratories investigated the resemblance of gene expression profiles derived from two hepatic rat cell lines, primary rat hepatocytes cultured under different conditions, rat liver slices and rat liver [53]. The results indicated that although the cell lines showed only little comparability with whole liver expression profiles, the correlation coefficients of hepatocytes shortly after isolation versus whole liver (0.88) and of fresh liver slices versus whole liver (0.95) were quite high. In contrast, with more time elapsing between isolation of cells or preparation of slices and harvesting of RNA for microarray analysis, the correlation coefficients decreased rapidly due to dedifferentiation. On the other hand, the variation between gene expression profiles of replicate preparations was most distinct immediately after isolation, whereas after adaptation to the culture conditions the profiles became more stable.

Another study investigating the mechanisms underlying Ochratoxin A-induced nephrotoxicity in rats in vivo and in vitro [21] showed good comparability of transcriptional changes observed in vitro and in vivo. Some minor discrepancies between cell culture and rat kidney expression profiles could be traced back almost entirely to the fact that the in vitro system included only proximal tubule cells, whereas the whole kidney resembles a heterogeneous complex of various cell types, which are furthermore subject to nervous and hormonal regulation. The results of these studies strongly support the application of in vitro models to toxicogenomics; however, obtaining a profound knowledge of the limitations of the particular in vitro system is essential and must be incorporated into the interpretation of the results.

The use of blood from human donors for gene expression analysis is also highly desirable in order to investigate treatment-related transcriptional changes without invasive sample collection. The publication by Whitney et al. [54] provided strong support for the use of peripheral blood for detection of infection and disease. Additionally, Lampe et al. [55] showed that exposure to tobacco smoke is associated with specific transcriptional signatures in human blood. These observations led to the hypothesis that gene expression profiling of blood samples might also reflect compound-related organ toxicity in patients and prove highly valuable in the diagnosis of treatment-related toxicity as well as in the identification of non-responders. Additionally, the identification of surrogate markers predictive for organ toxicity seemed feasible. In order to further evaluate these hypotheses, we started to assess the potential to predict organ toxicity based on blood gene expression profiles derived from rats treated with model toxicants. A supervised learning algorithm (for details regarding SVM training and optimization of parameters see [15]) was trained with blood gene expression data derived from rats treated with 17 model hepato- or nephrotoxicants and optimized for discrimination of toxic and non-toxic profiles (unpublished data). Cross-validation of the training set revealed virtually no false positives (99% specificity), but at the expense of a relatively high rate of false negatives (56% sensitivity). Nevertheless, the accuracy of classifying samples derived from toxic treatment as “toxic” and samples derived from non-toxic treatment as “non-toxic” reached considerable 86%. The following example of Puromycin, a well-described nephrotoxicant, highlights the possible value of blood profiling in safety assessment (unpublished data).

Rats were treated with 10 mg/kg Puromycin and 150 mg/kg Puromycin, respectively (killing of animals 24 and 168 h thereafter). Histopathology showed only very minor findings in the livers of the 10 mg/kg groups at both time points, but major findings in livers of all animals of the high dose groups. No morphological changes were observed in any of the Puromycin-treated kidneys except in the high dose group after 168 h. Classification of the blood gene expression profiles by the previously trained SVM algorithm (high dose group at 168 h was included in the training set, whereas the other groups were used as blinded test sets) perfectly reflected the histopathological findings. Moreover, one animal was detected as outlier, which paralleled the corresponding clinical chemistry data (Fig. 3). These results are still preliminary and in order to increase sensitivity of the prediction model and to facilitate the prediction of toxicity of specific organs, a lot of additional data are required. Nevertheless, this approach comprises promising starting points for future applications of toxicogenomics including for example the identification of surrogate markers for organ toxicity in humans.


Fig. 3. SVM Analysis of blood gene expression profiles derived from rats treated with vehicle control, with 10 mg/kg Puromycin and sacrificed after 24 or 168 h, respectively, or with 150 mg/kg Puromycin and sacrificed after 24 h. In each group, the expression profiles of five rats were analyzed by employing an SVM algorithm trained and cross-validated for discrimination between toxic and non-toxic treatment using parameters described in detail in [15]. A positive discriminant value indicates toxic treatment, whereas a negative discriminant value indicates non-toxic treatment.

3. Summary and outlook

For several years toxicogenomics enjoyed the privilege of being considered an emerging new technology, which has high potential to revolutionize drug and chemical safety assessment. With growing experience gained by industrial, government and academic institutions more and more possible caveats have been uncovered and it became clear that the great hopes laid in gene expression profiling appeared overoptimistic to a certain extent. Several publications evaluated in this review have impressively corroborated the use of toxicogenomics for the prediction of toxic liabilities, for the investigation of toxic mechanisms and for the identification of biomarkers of toxicity. Compound-related changes in transcriptional activity were successfully linked to histopathological findings. Moreover, with enormous help from bioinformaticians and toxicologists, toxicogenomic approaches have settled on a sound basis for the investigation of hepatotoxicity and nephrotoxicity in rats with remarkable potential for extrapolation to humans.

Despite having proven its usefulness in reflecting existing methods for toxicity testing, the demand for providing additional knowledge (added value) has not yet been satisfied adequately. Goals included detection of toxicity earlier or at lower doses than by using traditional endpoints. Prediction of idiosyncratic toxicity or drug–drug interaction, correlation of results from in vitro to in vivo systems and especially extrapolation of toxic liabilities to humans were claimed to be within reach, but so far only few results support the practicability of these approaches. The first promising data from experiments using rat blood samples for prediction of organ toxicity raise hope that in future non-invasive sample collection would facilitate easier monitoring of patients in clinical trials and better evaluation of not only drug toxicity, but also efficacy in humans. However, this approach still suffers from several drawbacks and major efforts aim at the further development of mathematical and biological tools in order to make sense of the flood of data. With regards to the interpretation of microarray data in general, especially the diversity of platforms available on the market represents a challenge in terms of comparability of the results. First steps have been made in setting standards for design and conduct of microarray experiments (MIAME), but due to the lack of common agreement on how to analyze and interpret gene expression data, conclusions drawn from such experiments may vary tremendously. The recent release of a draft guidance on submission of pharmacogenomics data to the Food and Drug Administration (FDA; http://www.fda.gov) and several other publications discussing the regulatory view of gene expression data [56] and [57] demonstrate that “-omics” technologies have come into focus of the regulatory agencies and might influence their decision making in future. Currently, we can look back on various success stories where toxicogenomics has proven its comparability to histopathology and clinical chemistry. There is considerable evidence that gene expression profiling might even provide essential information about new drug candidates which could not be addressed by using classical endpoints so far. Thus, toxicogenomics might have the potential of leading to a paradigm-shift in safety assessment of compounds. Nevertheless, this remains challenging and much work still needs to be done.

References

[1] M. Schena, D. Shalon, R.W. Davis and P.O. Brown, Quantitative monitoring of gene expression patterns with a complementary DNA microarray, Science 270 (1995), pp. 467–470.

[2] E.F. Nuwaysir, M. Bittner, J. Trent, J.C. Barrett and C.A. Afshari, Microarrays and toxicology: the advent of toxicogenomics, Mol. Carcinog. 24 (1999), pp. 153–159.

[3] D. Robinson, S. Pettit and D.G. Morgan, Use of genomics in mechanism based risk assessment. In: T. Inoue and W.D. Pennie, Editors, Toxicogenomics, Springer-Verlag, Tokyo (2003), pp. 194–203.

[4] R.G. Ulrich, J.C. Rockett, G.G. Gibson and S.D. Pettit, Overview of an interlaboratory collaboration on evaluating the effects of model hepatotoxicants on hepatic gene expression, Environ. Health Perspect. 112 (2004), pp. 423–427.

[5] T.M. Chu, S. Deng, R. Wolfinger, R.S. Paules and H.K. Hamadeh, Cross-site comparison of gene expression data reveals high similarity, Environ. Health Perspect. 112 (2004), pp. 449–455.

[6] J.J. Chen, R.R. Delongchamp, C.-A. Tsai, H.-m. Hsueh, F. Sistare, K.L. Thompson, V.G. Desai and J.C. Fuscoe, Analysis of variance components in gene expression data, Bioinformatics 20 (2004), pp. 1436–1446.

[7] J.P. Novak, R. Sladek and T.J. Hudson, Characterization of variability in large-scale gene expression data: implications for study design, Genomics 79 (2002), pp. 104–113.

[8] M. Rihl, D. Baeten, N. Seta, J. Gu, F. De Keyser, E.M. Veys, J.G. Kuipers, H. Zeidler and D.T.Y. Yu, Technical validation of cDNA based microarray as screening technique to identify candidate genes in synovial tissue biopsy specimens from patients with spondyloarthropathy, Ann. Rheum. Dis. 63 (2004), pp. 498–507.

[9] A. Butte, The use and analysis of microarray data, Nat. Rev. Drug. Discov. 1 (2002), pp. 951–960.

[10] W.S. Lee, G.J. Lee, C.D. Yeo, J.S. Kang, Y.H. Kim, S.J. Kim, J.S. Kim, S.Y. Hwang, J.S. Park, J.W. Hwang, K.S. Kang, Y.S. Lee, K.S. Jeon, C.H. Um, S.I. Hong and Y.S. Kim, The intelligent data management system for toxicogenomics, J. Vet. Med. Sci. 66 (2004), pp. 1335–1338.

[11] S.-D. Zhang and T.W. Gant, A statistical framework for the design of microarray experiments and effective detection of differential gene expression, Bioinformatics 20 (2004), pp. 2821–2828.

[12] W.H. Heijne, R.H. Stierum, M. Slijper, P.J. van Bladeren and B. van Ommen, Toxicogenomics of bromobenzene hepatotoxicity: a combined transcriptomics and proteomics approach, Biochem. Pharmacol. 65 (2003), pp. 857–875.

[13] L. Suter, L.E. Babiss and E.B. Wheeldon, Toxicogenomics in predictive toxicology in drug development, Chem. Biol. 11 (2004), pp. 161–171.

[14] J.F. Waring, R.A. Jolly, R. Ciurlionis, P.Y. Lum, J.T. Praestgaard, D.C. Morfitt, B. Buratto, C. Roberts, E. Schadt and R.G. Ulrich, Clustering of hepatotoxins based on mechanism of toxicity using gene expression profiles, Toxicol. Appl. Pharmacol. 175 (2001), pp. 28–42.

[15] G. Steiner, L. Suter, F. Boess, R. Gasser, M.C. de Vera, S. Albertini and S. Ruepp, Discriminating different classes of toxicants by transcript profiling, Environ. Health Perspect. 112 (2004), pp. 1236–1248.

[16] H.K. Hamadeh, S. Jayadev, E.T. Gaillard, Q. Huang, R. Stoll, K. Blanchard, J. Chou, C.J. Tucker, J. Collins, R. Maronpot, P. Bushel and C.A. Afshari, Integration of clinical and gene expression endpoints to explore furan-mediated hepatotoxicity, Mutat. Res. 549 (2004), pp. 169–183.

[17] J.W. Jung, J.S. Park, J.W. Hwang, K.S. Kang, Y.S. Lee, B.S. Song, G.J. Lee, C.D. Yeo, J.S. Kang, W.S. Lee, K.S. Jeon, C.H. Um, Y.S. Kim, M.J. Oh, J.P. Youn, P. Li, J.E. Park and S.Y. Hwang, Gene expression analysis of peroxisome proliferators- and phenytoin-induced hepatotoxicity using cDNA microarray, J. Vet. Med. Sci. 66 (2004), pp. 1329–1333.

[18] L. Suter, M. Haiker, M.C. De Vera and S. Albertini, Effect of two 5-HT6 receptor antagonists on the rat liver: a molecular approach, Pharmacogenomics. J. 3 (2003), pp. 320–334.

[19] Q. Huang, R.T. Dunn II, S. Jayadev, O. DiSorbo, F.D. Pack, S.B. Farr, R.E. Stoll and K.T. Blanchard, Assessment of cisplatin-induced nephrotoxicity by microarray technology, Toxicol. Sci. 63 (2001), pp. 196–207.

[20] R.P. Amin, A.E. Vickers, F. Sistare, K.L. Thompson, R.J. Roman, M. Lawton, J. Kramer, H.K. Hamadeh, J. Collins, S. Grissom, L. Bennett, C.J. Tucker, S. Wild, C. Kind, V. Oreffo, J.W. Davis II, S. Curtiss, J.M. Naciff, M. Cunningham, R. Tennant, J. Stevens, B. Car, T.A. Bertram and C.A. Afshari, Identification of putative gene based markers of renal toxicity, Environ. Health Perspect. 112 (2004), pp. 465–479.

[21] A. Luhe, H. Hildebrand, U. Bach, T. Dingermann and H.J. Ahr, A new approach to studying ochratoxin A (OTA)-induced nephrotoxicity: expression profiling in vivo and in vitro employing cDNA microarrays, Toxicol. Sci. 73 (2003), pp. 315–328.

[22] J.G. Moggs, H. Tinwell, T. Spurway, H.S. Chang, I. Pate, F.L. Lim, D.J. Moore, A. Soames, R. Stuckey, R. Currie, T. Zhu, I. Kimber, J. Ashby and G. Orphanides, Phenotypic anchoring of gene expression changes during estrogen-induced uterine growth, Environ. Health Perspect. 112 (2004), pp. 1589–1606.

[23] S. Kaiser and L.K. Nisenbaum, Evaluation of common gene expression patterns in the rat nervous system, Physiol. Genomics 16 (2003), pp. 1–7.

[24] C.J. Omiecinski, C. Hassett and P. Costa, Developmental expression and in situ localization of the phenobarbital-inducible rat hepatic mRNAs for cytochromes CYP2B1, CYP2B2, CYP2C6, and CYP3A1, Mol. Pharmacol. 38 (1990), pp. 462–470.

[25] J.C. Ourlin, C. Handschin, M. Kaufmann and U.A. Meyer, A Link between cholesterol levels and phenobarbital induction of cytochromes P450, Biochem. Biophys. Res. Commun. 291 (2002), pp. 378–384.

[26] Biomarkers and surrogate endpoints: preferred definitions and conceptual framework, Clin. Pharmacol. Therap. 69 (2001) 89–95.

[27] B. Thome-Kromer, I. Bonk, M. Klatt, G. Nebrich, M. Taufmann, S. Bryant, U. Wacker and A. Kopke, Toward the identification of liver toxicity markers: a proteome study in human cell culture and rats, Proteomics 3 (2003), pp. 1835–1862.

[28] L.R. Bandara, M.D. Kelly, E.A. Lock and S. Kennedy, A potential biomarker of kidney damage identified by proteomics: preliminary findings, Biomarkers 8 (2003), pp. 272–286.

[29] F.M. Goodsaid, Genomic biomarkers of toxicity, Curr. Opin. Drug Discov. Dev. 6 (2003), pp. 41–49.

[30] W. Pfaller and G. Gstraunthaler, Nephrotoxicity testing in vitro—what we know and what we need to know, Environ. Health Perspect. 106 (1998) (Suppl. 2), pp. 559–569.

[31] S. Farr and R.T. Dunn II, Concise review: gene expression applied to toxicology, Toxicol. Sci. 50 (1999), pp. 1–9.

[32] M.J. Aardema and J.T. MacGregor, Toxicology and genetic toxicology in the new era of “toxicogenomics”: impact of “-omics” technologies, Mutat. Res. 499 (2002), pp. 13–25.

[33] G. Orphanides and I. Kimber, Toxicogenetics: applications and opportunities, Toxicol. Sci. 75 (2003), pp. 1–6.

[34] E.S. Lander, L.M. Linton, B. Birren, C. Nusbaum, M.C. Zody, J. Baldwin, K. Devon, K. Dewar, M. Doyle, W. FitzHugh, R. Funke, D. Gage, K. Harris, A. Heaford, J. Howland, L. Kann, J. Lehoczky, R. LeVine, P. McEwan, K. McKernan, J. Meldrim, J.P. Mesirov, C. Miranda, W. Morris, J. Naylor, C. Raymond, M. Rosetti, R. Santos, A. Sheridan, C. Sougnez, N. Stange-Thomann, N. Stojanovic, A. Subramanian, D. Wyman, J. Rogers, J. Sulston, R. Ainscough, S. Beck, D. Bentley, J. Burton, C. Clee, N. Carter, A. Coulson, R. Deadman, P. Deloukas, A. Dunham, I. Dunham, R. Durbin, L. French, D. Grafham, S. Gregory, T. Hubbard, S. Humphray, A. Hunt, M. Jones, C. Lloyd, A. McMurray, L. Matthews, S. Mercer, S. Milne, J.C. Mullikin, A. Mungall, R. Plumb, M. Ross, R. Shownkeen, S. Sims, R.H. Waterston, R.K. Wilson, L.W. Hillier, J.D. McPherson, M.A. Marra, E.R. Mardis, L.A. Fulton, A.T. Chinwalla, K.H. Pepin, W.R. Gish, S.L. Chissoe, M.C. Wendl, K.D. Delehaunty, T.L. Miner, A. Delehaunty, J.B. Kramer, L.L. Cook, R.S. Fulton, D.L. Johnson, P.J. Minx, S.W. Clifton, T. Hawkins, E. Branscomb, P. Predki, P. Richardson, S. Wenning, T. Slezak, N. Doggett, J.F. Cheng, A. Olsen, S. Lucas, C. Elkin, E. Uberbacher, M. Frazier, R.A. Gibbs, D.M. Muzny, S.E. Scherer, J.B. Bouck, E.J. Sodergren, K.C. Worley, C.M. Rives, J.H. Gorrell, M.L. Metzker, S.L. Naylor, R.S. Kucherlapati, D.L. Nelson, G.M. Weinstock, Y. Sakaki, A. Fujiyama, M. Hattori, T. Yada, A. Toyoda, T. Itoh, C. Kawagoe, H. Watanabe, Y. Totoki, T. Taylor, J. Weissenbach, R. Heilig, W. Saurin, F. Artiguenave, P. Brottier, T. Bruls, E. Pelletier, C. Robert, P. Wincker, D.R. Smith, L. Doucette-Stamm, M. Rubenfield, K. Weinstock, H.M. Lee, J. Dubois, A. Rosenthal, M. Platzer, G. Nyakatura, S. Taudien, A. Rump, H. Yang, J. Yu, J. Wang, G. Huang, J. Gu, L. Hood, L. Rowen, A. Madan, S. Qin, R.W. Davis, N.A. Federspiel, A.P. Abola, M.J. Proctor, R.M. Myers, J. Schmutz, M. Dickson, J. Grimwood, D.R. Cox, M.V. Olson, R. Kaul, N. Shimizu, K. Kawasaki, S. Minoshima, G.A. Evans, M. Athanasiou, R. Schultz, B.A. Roe, F. Chen, H. Pan, J. Ramser, H. Lehrach, R. Reinhardt, W.R. McCombie, M. de la Bastide, N. Dedhia, H. Blocker, K. Hornischer, G. Nordsiek, R. Agarwala, L. Aravind, J.A. Bailey, A. Bateman, S. Batzoglou, E. Birney, P. Bork, D.G. Brown, C.B. Burge, L. Cerutti, H.C. Chen, D. Church, M. Clamp, R.R. Copley, T. Doerks, S.R. Eddy, E.E. Eichler, T.S. Furey, J. Galagan, J.G. Gilbert, C. Harmon, Y. Hayashizaki, D. Haussler, H. Hermjakob, K. Hokamp, W. Jang, L.S. Johnson, T.A. Jones, S. Kasif, A. Kaspryzk, S. Kennedy, W.J. Kent, P. Kitts, E.V. Koonin, I. Korf, D. Kulp, D. Lancet, T.M. Lowe, A. McLysaght, T. Mikkelsen, J.V. Moran, N. Mulder, V.J. Pollara, C.P. Ponting, G. Schuler, J. Schultz, G. Slater, A.F. Smit, E. Stupka, J. Szustakowski, D. Thierry-Mieg, J. Thierry-Mieg, L. Wagner, J. Wallis, R. Wheeler, A. Williams, Y.I. Wolf, K.H. Wolfe, S.P. Yang, R.F. Yeh, F. Collins, M.S. Guyer, J. Peterson, A. Felsenfeld, K.A. Wetterstrand, A. Patrinos, M.J. Morgan, P. de Jong, J.J. Catanese, K. Osoegawa, H. Shizuya, S. Choi and Y.J. Chen, Initial sequencing and analysis of the human genome, Nature 409 (2001), pp. 860–921.

[35] R.H. Waterston, K. Lindblad-Toh, E. Birney, J. Rogers, J.F. Abril, P. Agarwal, R. Agarwala, R. Ainscough, M. Alexandersson, P. An, S.E. Antonarakis, J. Attwood, R. Baertsch, J. Bailey, K. Barlow, S. Beck, E. Berry, B. Birren, T. Bloom, P. Bork, M. Botcherby, N. Bray, M.R. Brent, D.G. Brown, S.D. Brown, C. Bult, J. Burton, J. Butler, R.D. Campbell, P. Carninci, S. Cawley, F. Chiaromonte, A.T. Chinwalla, D.M. Church, M. Clamp, C. Clee, F.S. Collins, L.L. Cook, R.R. Copley, A. Coulson, O. Couronne, J. Cuff, V. Curwen, T. Cutts, M. Daly, R. David, J. Davies, K.D. Delehaunty, J. Deri, E.T. Dermitzakis, C. Dewey, N.J. Dickens, M. Diekhans, S. Dodge, I. Dubchak, D.M. Dunn, S.R. Eddy, L. Elnitski, R.D. Emes, P. Eswara, E. Eyras, A. Felsenfeld, G.A. Fewell, P. Flicek, K. Foley, W.N. Frankel, L.A. Fulton, R.S. Fulton, T.S. Furey, D. Gage, R.A. Gibbs, G. Glusman, S. Gnerre, N. Goldman, L. Goodstadt, D. Grafham, T.A. Graves, E.D. Green, S. Gregory, R. Guigo, M. Guyer, R.C. Hardison, D. Haussler, Y. Hayashizaki, L.W. Hillier, A. Hinrichs, W. Hlavina, T. Holzer, F. Hsu, A. Hua, T. Hubbard, A. Hunt, I. Jackson, D.B. Jaffe, L.S. Johnson, M. Jones, T.A. Jones, A. Joy, M. Kamal, E.K. Karlsson, D. Karolchik, A. Kasprzyk, J. Kawai, E. Keibler, C. Kells, W.J. Kent, A. Kirby, D.L. Kolbe, I. Korf, R.S. Kucherlapati, E.J. Kulbokas, D. Kulp, T. Landers, J.P. Leger, S. Leonard, I. Letunic, R. Levine, J. Li, M. Li, C. Lloyd, S. Lucas, B. Ma, D.R. Maglott, E.R. Mardis, L. Matthews, E. Mauceli, J.H. Mayer, M. McCarthy, W.R. McCombie, S. McLaren, K. McLay, J.D. McPherson, J. Meldrim, B. Meredith, J.P. Mesirov, W. Miller, T.L. Miner, E. Mongin, K.T. Montgomery, M. Morgan, R. Mott, J.C. Mullikin, D.M. Muzny, W.E. Nash, J.O. Nelson, M.N. Nhan, R. Nicol, Z. Ning, C. Nusbaum, M.J. O’Connor, Y. Okazaki, K. Oliver, E. Overton-Larty, L. Pachter, G. Parra, K.H. Pepin, J. Peterson, P. Pevzner, R. Plumb, C.S. Pohl, A. Poliakov, T.C. Ponce, C.P. Ponting, S. Potter, M. Quail, A. Reymond, B.A. Roe, K.M. Roskin, E.M. Rubin, A.G. Rust, R. Santos, V. Sapojnikov, B. Schultz, J. Schultz, M.S. Schwartz, S. Schwartz, C. Scott, S. Seaman, S. Searle, T. Sharpe, A. Sheridan, R. Shownkeen, S. Sims, J.B. Singer, G. Slater, A. Smit, D.R. Smith, B. Spencer, A. Stabenau, N. Stange-Thomann, C. Sugnet, M. Suyama, G. Tesler, J. Thompson, D. Torrents, E. Trevaskis, J. Tromp, C. Ucla, A. Ureta-Vidal, J.P. Vinson, A.C. Von Niederhausern, C.M. Wade, M. Wall, R.J. Weber, R.B. Weiss, M.C. Wendl, A.P. West, K. Wetterstrand, R. Wheeler, S. Whelan, J. Wierzbowski, D. Willey, S. Williams, R.K. Wilson, E. Winter, K.C. Worley, D. Wyman, S. Yang, S.P. Yang, E.M. Zdobnov, M.C. Zody and E.S. Lander, Initial sequencing and comparative analysis of the mouse genome, Nature 420 (2002), pp. 520–562.

[36] L.D. Kier, R. Neft, L. Tang, R. Suizu, T. Cook, K. Onsurez, K. Tiegler, Y. Sakai, M. Ortiz, T. Nolan, U. Sankar and A.P. Li, Applications of microarrays with toxicologically relevant genes (tox genes) for the evaluation of chemical toxicants in Sprague Dawley rats in vivo and human hepatocytes in vitro, Mutat. Res. 549 (2004), pp. 101–113.

[37] S. Ruepp, F. Boess, L. Suter, M.C. de Vera, G. Steiner, T. Steele, T. Weiser and S. Albertini, Assessment of hepatotoxic liabilities by transcript profiling, Toxicol. Appl. Pharmacol. (2005).

[38] H. Ellinger-Ziegelbauer, B. Stuart, B. Wahle, W. Bomann and H.J. Ahr, Characteristic expression profiles induced by genotoxic carcinogens in rat liver, Toxicol. Sci. 77 (2004), pp. 19–34.

[39] H.K. Hamadeh, R.P. Amin, R.S. Paules and C.A. Afshari, An overview of toxicogenomics, Curr. Issues Mol. Biol. 4 (2002), pp. 45–56

[40] J.M. Shenton, J. Chen and J.P. Uetrecht, Animal models of idiosyncratic drug reactions, Chem. Biol. Interact. 150 (2004), pp. 53–70.

[41] J. Uetrecht, Prediction of a new drug‘s potential to cause idiosyncratic reactions, Curr. Opin. Drug Discov. Dev. 4 (2001), pp. 55–59.

[42] M.J. Liguori, M.G. Anderson, S. Bukofzer, J. McKim, J.F. Pregenzer, J. Retief, B.B. Spear and J.F. Waring, Microarray analysis in human hepatocytes suggests a mechanism for hepatotoxicity induced by trovafloxacin, Hepatology 41 (2004), pp. 177–186.

[43] H. Olson, G. Betton, J. Stritar and D. Robinson, The predictivity of the toxicity of pharmaceuticals in humans from animal data—an interim assessment, Toxicol. Lett. 102–103 (1998), pp. 535–538.

[44] H. Olson, G. Betton, D. Robinson, K. Thomas, A. Monro, G. Kolaja, P. Lilly, J. Sanders, G. Sipes, W. Bracken, M. Dorato, K. Van Deun, P. Smith, B. Berger and A. Heller, Concordance of the toxicity of pharmaceuticals in humans and in animals, Regul. Toxicol. Pharmacol. 32 (2000), pp. 56–67.

[45] R.A. Roberts, Peroxisome proliferators: mechanisms of adverse effects in rodents and molecular basis for species differences, Arch. Toxicol. 73 (1999), pp. 413–418.

[46] J.W. Lawrence, Y. Li, S. Chen, J.G. DeLuca, J.P. Berger, D.R. Umbenhauer, D.E. Moller and G. Zhou, Differential gene regulation in human versus rodent hepatocytes by peroxisome proliferator-activated receptor (PPAR) alpha. PPAR alpha fails to induce peroxisome proliferation-associated genes in human cells independently of the level of receptor expresson, J. Biol. Chem. 276 (2001), pp. 31521–31527.

[47] D.J. Hoivik, C.W. Qualls Jr., R.C. Mirabile, N.F. Cariello, C.L. Kimbrough, H.M. Colton, S.P. Anderson, M.J. Santostefano, R.J. Ott Morgan, R.R. Dahl, A.R. Brown, Z. Zhao, P.N. Mudd Jr., W.B. Oliver Jr., H.R. Brown and R.T. Miller, Fibrates induce hepatic peroxisome and mitochondrial proliferation without overt evidence of cellular proliferation and oxidative stress in cynomolgus monkeys, Carcinogenesis (2004).

[48] Y. Yang, E.A.G. Blomme and J.F. Waring, Toxicogenomics in drug discovery: from preclinical studies to clinical trials, Chem. Biol. Interact. 150 (2004), pp. 71–85.

[49] R.A. Gibbs, G.M. Weinstock, M.L. Metzker, D.M. Muzny, E.J. Sodergren, S. Scherer, G. Scott, D. Steffen, K.C. Worley, P.E. Burch, G. Okwuonu, S. Hines, L. Lewis, C. DeRamo, O. Delgado, S. Dugan-Rocha, G. Miner, M. Morgan, A. Hawes, R. Gill, Celera, R.A. Holt, M.D. Adams, P.G. Amanatides, H. Baden-Tillson, M. Barnstead, S. Chin, C.A. Evans, S. Ferriera, C. Fosler, A. Glodek, Z. Gu, D. Jennings, C.L. Kraft, T. Nguyen, C.M. Pfannkoch, C. Sitter, G.G. Sutton, J.C. Venter, T. Woodage, D. Smith, H.M. Lee, E. Gustafson, P. Cahill, A. Kana, L. Doucette-Stamm, K. Weinstock, K. Fechtel, R.B. Weiss, D.M. Dunn, E.D. Green, R.W. Blakesley, G.G. Bouffard, P.J. De Jong, K. Osoegawa, B. Zhu, M. Marra, J. Schein, I. Bosdet, C. Fjell, S. Jones, M. Krzywinski, C. Mathewson, A. Siddiqui, N. Wye, J. McPherson, S. Zhao, C.M. Fraser, J. Shetty, S. Shatsman, K. Geer, Y. Chen, S. Abramzon, W.C. Nierman, P.H. Havlak, R. Chen, K.J. Durbin, A. Egan, Y. Ren, X.Z. Song, B. Li, Y. Liu, X. Qin, S. Cawley, A.J. Cooney, L.M. D‘Souza, K. Martin, J.Q. Wu, M.L. Gonzalez-Garay, A.R. Jackson, K.J. Kalafus, M.P. McLeod, A. Milosavljevic, D. Virk, A. Volkov, D.A. Wheeler, Z. Zhang, J.A. Bailey, E.E. Eichler, E. Tuzun, E. Birney, E. Mongin, A. Ureta-Vidal, C. Woodwark, E. Zdobnov, P. Bork, M. Suyama, D. Torrents, M. Alexandersson, B.J. Trask, J.M. Young, H. Huang, H. Wang, H. Xing, S. Daniels, D. Gietzen, J. Schmidt, K. Stevens, U. Vitt, J. Wingrove, F. Camara, M. Mar Alba, J.F. Abril, R. Guigo, A. Smit, I. Dubchak, E.M. Rubin, O. Couronne, A. Poliakov, N. Hubner, D. Ganten, C. Goesele, O. Hummel, T. Kreitler, Y.A. Lee, J. Monti, H. Schulz, H. Zimdahl, H. Himmelbauer, H. Lehrach, H.J. Jacob, S. Bromberg, J. Gullings-Handley, M.I. Jensen-Seaman, A.E. Kwitek, J. Lazar, D. Pasko, P.J. Tonellato, S. Twigger, C.P. Ponting, J.M. Duarte, S. Rice, L. Goodstadt, S.A. Beatson, R.D. Emes, E.E. Winter, C. Webber, P. Brandt, G. Nyakatura, M. Adetobi, F. Chiaromonte, L. Elnitski, P. Eswara, R.C. Hardison, M. Hou, D. Kolbe, K. Makova, W. Miller, A. Nekrutenko, C. Riemer, S. Schwartz, J. Taylor, S. Yang, Y. Zhang, K. Lindpaintner, T.D. Andrews, M. Caccamo, M. Clamp, L. Clarke, V. Curwen, R. Durbin, E. Eyras, S.M. Searle, G.M. Cooper, S. Batzoglou, M. Brudno, A. Sidow, E.A. Stone, B.A. Payseur, G. Bourque, C. Lopez-Otin, X.S. Puente, K. Chakrabarti, S. Chatterji, C. Dewey, L. Pachter, N. Bray, V.B. Yap, A. Caspi, G. Tesler, P.A. Pevzner, D. Haussler, K.M. Roskin, R. Baertsch, H. Clawson, T.S. Furey, A.S. Hinrichs, D. Karolchik, W.J. Kent, K.R. Rosenbloom, H. Trumbower, M. Weirauch, D.N. Cooper, P.D. Stenson, B. Ma, M. Brent, M. Arumugam, D. Shteynberg, R.R. Copley, M.S. Taylor, H. Riethman, U. Mudunuri, J. Peterson, M. Guyer, A. Felsenfeld, S. Old, S. Mockrin and F. Collins, Genome sequence of the brown Norway rat yields insights into mammalian evolution, Nature 428 (2004), pp. 493–521.

[50] M.E. Burczynski, M. McMillian, J. Ciervo, L. Li, J.B. Parker, R.T. Dunn II, S. Hicken, S. Farr and M.D. Johnson, Toxicogenomics-based discrimination of toxic mechanism in HepG2 human hepatoma cells, Toxicol. Sci. 58 (2000), pp. 399–415.

[51] A.J. Harris, S.L. Dial and D.A. Casciano, Comparison of basal gene expression profiles and effects of hepatocarcinogens on gene expression in cultured primary human hepatocytes and HepG2 cells, Mutat. Res. 549 (2004), pp. 79–99.

[52] T. Hartung and L. Gribaldo, New hepatocytes for toxicology?, Trends Biotechnol. 22 (2004), pp. 613–615 (discussion, 615–616).

[53] F. Boess, M. Kamber, S. Romer, R. Gasser, D. Muller, S. Albertini and L. Suter, Gene expression in two hepatic cell lines, cultured primary hepatocytes, and liver slices compared to the in vivo liver gene expression in rats: possible implications for toxicogenomics use of in vitro systems, Toxicol. Sci. 73 (2003), pp. 386–402.

[54] A.R. Whitney, M. Diehn, S.J. Popper, A.A. Alizadeh, J.C. Boldrick, D.A. Relman and P.O. Brown, Individuality and variation in gene expression patterns in human blood, PNAS 100 (2003), pp. 1896–1901.

[55] J.W. Lampe, S.B. Stepaniants, M. Mao, J.P. Radich, H. Dai, P.S. Linsley, S.H. Friend and J.D. Potter, Signatures of environmental exposures using peripheral leukocyte gene expression: tobacco smoke, Cancer Epidemiol. Biomarkers Prev. 13 (2004), pp. 445–453.

[56] K. Freeman, Toxicogenomics data: the road to acceptance, Environ. Health Perspect. 112 (2004), pp. A678–A685.

[57] F.W. Frueh, S.M. Huang and L.J. Lesko, Regulatory acceptance of toxicogenomics data, Environ. Health Perspect. 112 (2004), pp. A663–A664.
Copyright © 2009-2010 TOXSMMUV1.0 All Rights Reserved
设计制作: 伊清科技 后台管理  ICP备案:沪ICP备05053002号 邮箱:webmaster@toxsmmu.com