Evaluation of a DNA polymerase-deficient mutant of E. coli for the rapid detection of carcinogens

Differential growth inhibition of two E. coli cultures was evaluated as a rapid screening technique for chemical carcinogens. Of the carcinogens tested, only “direct acting” carcinogens produced positive results. Furthermore, this test is not a quantitative assay in that neither was a dose—response relationship seen nor did potent carcinogens necessarily show a greater response than weaker carcinogens.Most of the carcinogens tested are considered to require metabolic activation in order to exert their carcinogenic action. Despite many attempts, including several variations of reaction conditions, metabolic activation by rat liver fractions was not apparent. Many of these carcinogens are insoluble in water and may not diffuse through the agar and therefore not reach the indicator organism.A number of chemicals that are not carcinogenic produced positive results with this assay. Many of these substances are oxidants or oxidation products which are highly reactive with DNA as well as with other cellular constituents. Therefore, it is possible that the toxicity exhibited by these chemicals was caused by a reaction with some essential cellular constituent other than DNA and such damage would not be repairable by DNA polymerase. These observations limit the usefulness of the P3478 E. coli technique in its present form as a prescreen for chemical carcinogens.     

Evaluation of a new model to detect bladder carcinogens or co-carcinogens; results obtained with saccharin, cyclamate and cyclophosphamide.

A sensitive rat model has been designed to detect potential weak bladder carcinogens or co-carcinogens. The test compound is given to animals which have received a single initiating, but non-carcinogenic, dose of N-methyl-N-nitrosourea (MNU). The model has been used to investigate two compounds currently under suspicion as weak bladder carcinogens, namely sodium saccharin and sodium cyclamate, and one compound known to be cytotoxic but not carcinogenic for the bladder epithelium namely cyclophosphamide. For comparison, these three compounds were also tested as solitary carcinogens in animals not pre-treated with MNU. At the very high dose levels used, sodium saccharin and sodium cyclamate were weak solitary carcinogens producing 4/253 and 3/228 bladder tumours respectively, and the first of these tumours did not appear for more than 80 weeks. When tested in the MNU/rat model more than half the animals receiving either sodium saccharin or sodium cyclamate developed bladder tumours from 10 weeks onwards. By contrast, cyclophosphamide failed to produce any tumours when tested either as a solitary carcinogen or in the MNU/rat model. It must be emphasized that the doses of saccharin and cyclamate used were far higher than those consumed by man, including diabetics, and these results should not be directly extrapolated to man without careful consideration of many other factors including negative epidemiological findings. The theoretical basis of the model is discussed and also the relevance, in terms of environmental human exposure, of detecting compounds which have a synergistic effect with other known bladder carcinogens. It appears that this model can be used to detect a carcinogenic or co-carcinogenic potential in compounds which are organotropic for the bladder more rapidly and with fewer animals than if the compounds are tested as solitary carcinogens by more conventional methods. It is suggested that it could be used to detect those compounds which require further investigation.     

Facts and theories concerning the mechanisms of carcinogenesis

Carcinogenesis can be induced experimentally by exposure to exogenous agents or it can occur spontaneously without intentional or active intervention. Carcinogenesis can be actively induced by chemicals, radiation, infectious biological agents, transgenesis, or selective breeding. In the human and occasionally when testing potential carcinogens in animals, cancer may result from passive exposure to carcinogens encountered in the ambient environment or from changes in the internal milieu of the animal. Many carcinogens alter the structure of DNA resulting in carcinogenesis, but a significant number of carcinogens do not appear to act through this mechanism. When the action of specific carcinogenic agents is considered in relation to the stages of cancer development, initiation, promotion, and progression, the mechanism of the induction of carcinogenesis by DNA-reactive agents that alter genomic structure can be reconciled with those agents that do not act in this manner. As some cells are fortuitously initiated by uncontrolled variables such as irradiation and through changes in normal processes, the stimulation of growth and altered genetic expression by nongenotoxic agents may result indirectly in cancer development. The final stage of carcinogenesis, progression, can occur spontaneously, enhanced by formation and propagation of genetic errors due to increased cellular proliferation associated with the promotion stage. In addition, chemical and viral agents that lack the capacity for initiation and promotion may actively convert cells in the stage of promotion to the stage of progression. Therefore, the diverse mechanisms of action of carcinogenic agents in relation to their effects on specific stages in the natural history of cancer development allow for greater congruence of many of the theories of carcinogenesis. The influence of the roles of nongenotoxic carcinogenic agents and the potential role of progressor agents on the carcinogenesis process allow a more accurate identification of the potential risk that specific carcinogenic agents pose for increasing human cancer.     

Structural basis of carcinogenicity in rodents of genotoxicants and non-genotoxicants

A set of 189 chemicals tested in the National Toxicology Program Cancer Bioassay was subjected to analysis by CASE, the Computer-Automated Structure Evaluation system. In the data set, 63% of the chemicals were carcinogens, approx. 40% of the carcinogens were non-genotoxic, i.e., they possessed neither "structural alerts" for DNA reactivity as defined by Ashby and Tennant, 1988, nor were they mutagenic for Salmonella. The data base can be characterized as a "combined rodent" compilation as chemicals were characterized as "carcinogenic" if they were carcinogenic in either rats or mice or both. CASE identified 23 fragments which accounted for the carcinogenicity, or lack thereof, of most of the chemicals. The sensitivity and specificity were unexpectedly high: 1.00 and 0.86, respectively. Based upon the identified biophores and biophobes, CASE performed exceedingly well in predicting the activity of chemicals not included among the 189 in the original set. CASE predicted correctly the carcinogenicity of non-genotoxic carcinogens thereby suggesting a structural commonality in the action of this group of carcinogens. As a matter of fact biophores restricted to non-genotoxic carcinogens were identified as were "non-electrophilic" biophores shared by genotoxic and non-genotoxic carcinogens. The findings suggest that the CASE program may help in the elucidation of the basis of the action of non-genotoxic carcinogens.     

A new biological assay, utilizing parasitic protozoa, for screening carcinogenic substances which induce bladder cancer in man and other mammals

Injections of aromatic amines (β-naphthylamine, benzidine, O-dianisidine or N-2-fluorenyl acetamide), tryptophan metabolites (3-hydroxyanthranilic acid, xanthurenic acid or LD-kynurenine sulphate), oestrone, and nicotine, which are known bladder carcinogens in man and some other mammals induced sexual reproduction (encystation) in Opalina sudafricana when injected into its host Bufo regularis. This may be used as a new biological assay for screening substances which induce bladder cancer in man and some other mammals. It is speculated that the metabolites of the injected carcinogenic substances used in this work are excreted in the urine of the host, hydrolysed by the hydrolytic enzymes and become carcinogenic. These carcinogenic metabolites reach the parasites in the rectum of the toads and induce them to divide mitotically to form small forms which eventually encyst. It is speculated that the presence of cysts in the rectum of the injected toads is indicative that a carcinogenic effect took place in the parasites. Oestrone is the only carcinogenic substance which induced encystation in the opalinids in vitro. Urine of toads injected with β-naphthylamine, benzidine, O-dianisidine, N-2-fluorenyl acetamide, 3-hydroxyanthranilic acid, xanthurenic acid, DL-kynurenine sulphate, oestrone and nicotine induced cyst formation in the parasites in vitro.     

Changes in the adhesiveness between enterocytes after short-term blastomogenic exposures

Following short-term local applications of high doses of N-methyl-N-nitrozourea and 7,2-dimethylbenz(a)antracen, the intercellular adhesion in the distal colon epithelium of ice retains increased at least for a month. The magnitude of this shift and its duration ops both with moving away from the area of application, or with reducing the doses of carcinogens to be closely related to the frequency of tumour production in the site of epithelium under chronic local applications of N-methyl-N-nitrozourea. After the application of noncarcinogenic methylurea or the subcutaneous injection of 1,2-dimethylhydrazine to the mice resistant to its carcinogenic action the wavy fluctuations of the magnitude of intercellular adhesion disappear within a week. The following conclusion can be drawn from the results: the long-term increase in enterocyte-enterocyte adhesion may be an earlier sign of the colon epithelium reaction to carcinogenic action.     

Early detection of carcinogenic substances and modifiers in rats

Over the past 20 years, we have been developing in vivo medium-term bioassay systems in rats for detecting carcinogenic and modifying effects of test compounds. The systems are based on the two-step hypothesis of carcinogenesis. In a liver model, male F344 rats are initially given a single dose of diethylnitrosamine (DEN, 200 mg/kg, i.p.) and starting 2 weeks later are treated with test compounds for 6 weeks and then killed, all rats being subjected to two-thirds partial hepatectomy at week 3. Carcinogenic potential is scored by comparing the numbers and areas per cm(2) of induced glutathione S-transferase placental form (GST-P) positive foci in the livers of groups of about 15 rats with those of corresponding control groups given DEN alone. A positive response is defined as a significant increase in the quantitative values of GST-P-positive foci, such a negative response as no change or a decrease. The results obtained have been compared with reported Salmonella/microsome and long-term carcinogenicity test findings for the same compounds. Of the liver carcinogens, 30 out of 31 (97%) mutagenic and 29 out of 33 (88%) non-mutagenic compounds gave positive results. Carcinogens other than hepatocarcinogens gave a lower proportion of positive results (9 out of 42, 21%). This bioassay also provides information concerning inhibitory potential. The practical utility and benefits of a multi-organ medium-term experimental protocol for early detection of carcinogenic agents and modifiers acting at sites other than the liver are also discussed.     

Multiple drug resistance, antimutagenesis and anticarcinogenesis

Many cells are protected from excess levels of exogenous chemicals, including mutagens and carcinogens as well as pharmaceutical agents, by being actively extruded through the action of one or more of a series of ATP-binding cassette drug transporter proteins. Those known to be important in humans are the multidrug resistance proteins (P-glycoproteins, encoded by the mdr1 and 3 genes), multidrug-resistance-associated proteins (MRP1-7) and the breast cancer resistance protein (BCRP). These proteins have overlapping but distinct cellular locations and substrate specificities, and jointly govern the likelihood of penetration or distribution of a given mutagen or carcinogen into various tissues including the brain, testis, ovaries and fetus. Thus, they can affect the absorption, distribution and excretion of mutagens and carcinogens, as well as of their metabolites and conjugates, in most cases acting to prevent or reduce mutagenesis or carcinogenesis. However, because ABC transporters may limit the success of chemotherapy, there has been a considerable effort by the pharmaceutical industry to develop inhibitors of this transport process, and these are increasing in use. In general, the mutagenicity of many chemicals may be increased at the cellular levels by the action of these inhibitors, while the altered absorption characteristics favour greater uptake into the body. Thus, in many cases, such inhibitors may counter the antimutagenic and anticarcinogenic effect of the multidrug resistance mechanisms. There are exceptions, however. An increasing number of single nucleotide polymorphisms in multidrug resistance genes are being identified in humans, and may account for many of the significant differences in inter-individual susceptibility to exogenous and endogenous mutagenic and carcinogenic insults.     

Hygienic evaluation and regulation of some environmental factors to counteract their potential carcinogenic hazards

The evident growth of tumour morbidity makes analysis of the fundamental problems of neoplasm prophylaxis in man particularly urgent. The establishment of maximum permissible concentrations for carcinogenic agents calls for further exploration into the problem of threshold action of carcinogens and elaboration of a methodology for quantitative assessment of the biological effects of certain environmental factors. In particular, the available data on the ability of low-intensity environmental factors to modify the organism's general resistance and thereby produce in it conditions for materialization of the untoward effects of carcinogens invite further work in this direction. The study of environmental factors as possible modifiers of blastomatosis and investigation of the modification mechanisms involved are an immediate and topical task. Quantitative analysis of these modifying effects would allow establishment of well-grounded hygienic norms as the next step. Thus, study of the regularities involved, development of a fundamental methodology and accumulation of facts on the influence of low-intensity environmental factors on carcinogenesis and the cancer effect should be helpful in devising scientifically based measures of lowering the growth of tumour morbidity.     

Evaluation of the alkaline elution/rat hepatocyte assay as a predictor of carcinogenic/mutagenic potential

We have recently developed an alkaline elution/rat hepatocyte assay to sensitively measure DNA single-strand breaks induced by xenobiotics in non-radiolabeled rat hepatocytes. Here we have evaluated this assay as a predictor of carcinogenic/mutagenic activity by testing 91 compounds (64 carcinogens and 27 non-carcinogens) from more than 25 diverse chemical classes. Hepatocytes were isolated from uninduced rats by collagenase perfusion, exposed to chemicals for 3 h, harvested, and analyzed for DNA single-strand breaks by alkaline elution. DNA determinations were done fluorimetrically. Cytotoxicity was estimated by glutamate-oxaloacetate transaminase release or by trypan blue dye exclusion. The assay correctly predicted the reported carcinogenic/non-carcinogenic potential of 92% of the carcinogens tested and 85% of non-carcinogens tested. The assay detected a number of compounds, including inorganics, certain pesticides, and steroids, which give false-negative results in other short-term tests. Only 2 rat liver carcinogens were incorrectly identified; the other carcinogens incorrectly identified are weakly or questionably carcinogenic (i.e., they cause tumors only in one species, after lifetime exposure, or at high doses). Some chemicals cause DNA damage only at cytotoxic concentrations; of 16 such compounds in this study, 12 are weak carcinogens suggesting a link between DNA damage caused by cytotoxicity and carcinogenesis. Our data indicate that this assay rapidly, reproducibly, sensitively, and accurately detects DNA single-strand breaks in rat hepatocytes and that the production of these breaks correlates well with carcinogenic and mutagenic activity.     

A Fuzzy Logic Approach to Assess,Manage, and Communicate Carcinogenic Risk

A prospective approach to addressing carcinogen risk assessment is presented. Fuzzy reasoning is used to assess carcinogenic risk, characterize it, and control it. The approach is inspired by fuzzy control inference that deploys linguistic intelligence as input to a system described numerically through membership functions. Fuzzy-based reasoning to estimate carcinogenic risk provides several advantages as discussed here. The fuzzy reasoning approach has more capabilities than traditional models in dealing with risk agents that are probably carcinogens, possibly carcinogens, not classifiable as carcinogens, and probably not carcinogens. Input–output surfaces are presented for each hazard group to enable fast inferencing. Then, a hypothetical example is given to compare the results of traditional methods and the fuzzy-based approach to estimating the risk of a carcinogen to a human population. Results show similarity in risk characterization with less input information to the fuzzy-based approach. Fuzzy reasoning characterizes risk in more explicit and easy to grasp terms. Two outputs of the inferencing system are risk characterization and risk control or remediation.     

Application of a two-stage Syrian hamster embryo cell transformation assay to cigarette smoke particulate matter

The induction of transformation in Syrian hamster embryo (SHE) cells is a multifactorial process, in comparison to endpoints induced in in vitro genotoxicity assays such as Ames, mouse lymphoma and cytogenetics [Y. Berwald, L. Sachs, In vitro cell transformation with chemical carcinogens, Nature (London) 200 (1963) 1182-1184]. Furthermore, a number of non-genotoxic carcinogens and promoters such as clofibrate and diethylhexylphthalate, have been positively identified in this assay, while giving false negative results in traditional genotoxicity assays [H. Yamasaki, J. Ashby, M. Bignami, W. Jongen, K. Linnainmaa, R.F. Newbold, G. Nguyen-Ba, S. Parodi, E. Rivedal, D. Schiffmann, J.W.I.M. Simons, P. Vasseur, Nongenotoxic carcinogens: development of detection methods based on mechanisms: a European project, Mutat. Res. 353 (1996) 47-63]. A high concordance between results obtained in this assay when compared with rodent carcinogenesis bioassays has also been noted [R.J. Isfort, G.A. Kerckaert, R.A. LeBoeuf, Comparison of the standard and reduced pH Syrian hamster embryo (SHE) in vitro cell transformation assays to predict the carcinogenic potential of chemicals, Mutat. Res. 356 (1996) 11-63]. Carcinogenesis is known to be a multistage process, with agents potentially acting at each stage. Specifically, mouse skin painting experiments established that tumour induction could be mechanistically divided into two distinct phases, termed initiation and promotion. Initiation, is defined as the stage at which a normal cell is converted to a latent tumour cell, followed by promotion where the latent tumour cell progresses to a tumour [W.F. Friedwald, P. Rous, The initiating and promoting elements in tumour production: analysis of the effects of tar, benzpyrene and methylcholanthrene on rabbit skin, J. Exp. Med. 80 (1944) 101-125]. A protocol for the pH 6.7 SHE transformation assay has been developed which allows separation of cell transformation process into two phases, potentially analogous to initiation and promotion in vivo. This allows chemicals found to be positive in the traditional SHE cell transformation assay to be further classified as initiators or promoters. Following validation with known initiators, benzo(a)pyrene and N-methyl-N'-nitro-N-nitrosoguanidine and promoters, 12-O-tetradecanoyl-phorbol-13-acetate and phenobarbitone, the two-stage model was applied to cigarette smoke particulates which was found to act both at the initiation and promotion stage of cell transformation.     

Consideration of both genotoxic and nongenotoxic mechanisms in predicting carcinogenic potential

Bacterial and cell culture genotoxicity assays have proven to be valuable in the identification of DNA reactive carcinogens because mutational events that alter the activity or expression of growth control genes are a key step in carcinogenesis. The addition of metabolizing enzymes to these assays have expanded the ability to identify agents that require metabolic activation. However, chemical carcinogenesis is a complex process dependent on toxicokinetics and involving at least steps of initiation, promotion and progression. Identification of those carcinogens that are activated in a manner unique to the whole animal, such as 2,6-dinitrotoluene, require in vivo genotoxicity assays. There are many different classes of non-DNA reactive carcinogens ranging from the potent promoter 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) that acts through a specific receptor, to compounds that alter growth control, such as phenobarbital. Many compounds, such as saccharin, appear to exhibit initiating, promotional and/or carcinogenic activity as events secondary to induced cytotoxicity and cell proliferation seen only at the chronic lifetime maximum tolerated doses mandated in rodent bioassays. Simple plus/minus vs. carcinogen/noncarcinogen comparisons used to validate the predictivity of bacterial and cell culture genotoxicity assays have revealed that a more comprehensive analysis will be required to account for the carcinogenicity of so many diverse chemical agents. Predictive assays and risk assessments for the numerous types of nongenotoxic carcinogens will require understanding of their mechanism of action, reasons for target organ and species specificity, and the quantitative dose-response relationships between endpoints such as induced cell proliferation and carcinogenic potential.     

The role of chemical and physical factors in cancer development

The author deals with the effects of environmental chemical-, and physical carcinogens playing predominant role in nearly 90% of the cancer development. Different steps of chemical carcinogenesis, classification and evaluation of carcinogens according to the criteria of International Agency for Research on Cancer, and the most important biological markers of genotoxic exposures are presented. Among physical agents the carcinogenic effects of ionizing and nonionizing radiations are demonstrated, including limited, inadequate or proved carcinogenic action of UV, microwave, static and low-frequency electric and magnetic fields.     

Threshold effects in genetic toxicity: perspective of chemicals regulation in Germany

In the regulation of chemical substances, it is generally agreed that there are no thresholds for genotoxic effects of chemicals, i.e. , that there are no doses without genotoxic effects. When classifying and labelling chemicals, dangerous properties of chemicals are to be identified. In this context, in general, the mode of action (threshold or not) is not considered for genotoxic substances. In the process of quantitative risk assessment, however, determination of the type of dose-effect relationships is decisive for the outcome and the type of risk management. The presence of a threshold must be justified specifically in each individual case. Inter alia, the following aspects may be discussed in this respect: aneugenic activity, indirect modes of action, extremely steep dose-effect relationships in combination with strong toxicity, specific toxicokinetic conditions which may lead to 'metabolic protection' prior to an attack of DNA. In the practice of the regulation of chemical substances with respect to their genotoxic effects, the discussion of thresholds has played a minor role. For notified new substances, there are, in general, no data available that would allow a reasonable discussion. Concerning substances out of the European programme on existing substances, so far 29 have been assessed in our institute with respect to genetic toxicity. Eight out of these have shown considerable evidence for genotoxicity. For two of them, a possible threshold is discussed: one substance is an aneugen, the other one is metabolised to an endogenic compound with genotoxic potential. In the practice of risk assessment of genotoxic substances, the discussion of the mode of action for genotoxicity is frequently associated with the evaluation of potential carcinogenic effects. Here, tissue-specific genotoxic effects in target organs for carcinogenicity are to be discussed. Moreover, the contribution of genotoxicity to the multifactorial process of tumour development should be assessed.     

Bacterial systems for carcinogenicity testing

During the past 30 years, bacterial test systems have been extensively refined in their ability to detect not only mutagenic agents but, in many cases, carcinogenic ones as well. Since many carcinogens are known to be activated within the mammalian body, major improvements in bacterial test systems were made when representative parts of mammalian metabolism were included as part of the test protocol. Presently, systems of great simplicity and convenience are available for the efficient detection of gene mutations, lysogenic induction of prophages, and differential DNA repair. These qualities render bacterial systems potentially useful in distinguishing between carcinogens and non-carcinogens, in characterizing induced mutation spectra, and possibly in quantifying mutagenic potency that may be used to predict tumor-initiating potency. Sensitive strains of Salmonella typhimurium. Escherichia coli and Bacillus subtilis with altered DNA-repair capacities have been constructed which accurately identify many carcinogens. Comparative studies have shown that techniques using these strains can be standardized to some extent and that the majority of carcinogens are active in all adequately sensitive genetic systems. Because of this redundancy, it may be sufficient to employ only one standardized set of tester strains and methodology. However, serveral classes of known carcinogens are undetected or underestimated when assayed in standard testing procedures. Some of these chemicals can be efficiently recognized as mutagens upon varying the methodology, the genetic endpoint, or the mammalian activation system. Thus, to modify and adjust the experimental protocol to the particular type of chemical under study and to calibrate the system with appropriate carcinogenic and non-carcinogenic reference compounds is advisable. It is noteworthy that chemical carcinogens which probably act by non-genotoxic mechanisms thus far remain undetected in bacterial tests. Newly developed systems which measure specific types of genetic events, such as transpositions of DNA segments and derepression of genes, presently are being tested for their ability to detect such carcinogens. A final matter of growing concern is the increasing number of environmental chemicals that are found to be mutagenic in bacteria but for which information about carcinogenic activity in vivo is insufficient. The possible use of bacteria for quantifying mutagenic potency and extrapolating this information to tumor-initiating potency can be envisaged in three ways: (i) direct extrapolation from standard in vitro tests, (ii) indirect extrapolation making use of an in vitro/in vivo comparison of induced effects (the parallelogram method) as devised by Sobels [138] on the basis of identical dose (to DNA), and (iii) host-mediated assays to assess mutagenic potency of carcinogens in selected organs of mammals...     

Mycotoxins: food contamination, mechanism, carcinogenic potential and preventive measures

Mycotoxins constitute a large number of naturally occurring fungal secondary metabolites with very diversified toxic effects in humans and animals. Among many mycotoxins discovered, aflatoxins, ochratoxin A, sterigmatocystin and several others are identified as carcinogens; several others were found to be mutagenic. Nevertheless, aflatoxin B1 has been found to be one of the most potent carcinogens and contamination of aflatoxins in the food supply is still a major concern. Whereas extensive studies have been made on aflatoxins, little is known about the mode of action of other carcinogenic and mutagenic mycotoxins. Recent progress on research for the carcinogenic and mutagenic mycotoxins is presented in this review with emphasis on their contamination in foods, their carcinogenic potential to humans, and the mode of action as well as possible preventive measures.     

Prediction of a carcinogenic potential of rat hepatocarcinogens using toxicogenomics analysis of short-term in vivo studies

The carcinogenic potential of chemicals is currently evaluated with rodent life-time bioassays, which are time consuming, and expensive with respect to cost, number of animals and amount of compound required. Since the results of these 2-year bioassays are not known until quite late during development of new chemical entities, and since the short-term test battery to test for genotoxicity, a characteristic of genotoxic carcinogens, is hampered by low specificity, the identification of early biomarkers for carcinogenicity would be a big step forward. Using gene expression profiles from the livers of rats treated up to 14 days with genotoxic and non-genotoxic carcinogens we previously identified characteristic gene expression profiles for these two groups of carcinogens. We have now added expression profiles from further hepatocarcinogens and from non-carcinogens the latter serving as control profiles. We used these profiles to extract biomarkers discriminating genotoxic from non-genotoxic carcinogens and to calculate classifiers based on the support vector machine (SVM) algorithm. These classifiers then predicted a set of independent validation compound profiles with up to 88% accuracy, depending on the marker gene set. We would like to present this study as proof of the concept that a classification of carcinogens based on short-term studies may be feasible.     

Bioactivation of xenobiotics by prostaglandin H synthase

Prostaglandin H synthase (PHS) catalyzes the oxidation of arachidonic acid to prostaglandin H2 in reactions which utilize two activities, a cyclooxygenase and a peroxidase. These enzymatic activities generate enzyme- and substrate-derived free radical intermediates which can oxidize xenobiotics to biologically reactive intermediates. As a consequence, in the presence of arachidonic acid or a peroxide source, PHS can bioactivate many chemical carcinogens to their ultimate mutagenic and carcinogenic forms. In general, PHS-dependent bioactivation is most important in extrahepatic tissues with low monooxygenase activity such as the urinary bladder, renal medulla, skin and lung. Mutagenicity assays are useful in the detection of compounds which are converted to genotoxic metabolites during PHS oxidation. In addition, the oxidation of xenobiotics by PHS often form metabolites or adducts to cellular macromolecules which are specific for peroxidase- or peroxyl radical-dependent reactions. These specific metabolites and/or adducts have served as biological markers of xenobiotic bioactivation by PHS in certain tissues. Evidence is presented which supports a role for PHS in the bioactivation of several polycyclic aromatic hydrocarbons and aromatic amines, two classes of carcinogens which induce extrahepatic neoplasia. It should be emphasized that the toxicities induced by PHS-dependent bioactivation of xenobiotics are not limited to carcinogenicity. Examples are given which demonstrate a role for PHS in pulmonary toxicity, teratogenicity, nephrotoxicity and myelotoxicity.     

Use of a cell transformation assay with established cell lines, and a metabolic cooperation assay with V79 cells for the detection of tumour promoters: a review

Extensive studies on the safety evaluation of chemicals have indicated that a considerable number of non-genotoxic chemicals are carcinogenic. Tumour promoters are likely to be among these non-genotoxic carcinogens, and their detection is considered to be an important approach to the prevention of cancer. In this review, the results are summarised for in vitro transformation assays involving established cell lines, and for an assay for inhibition of gap junctional intercellular communication for the detection of tumour promoters, which involves V79 cells. Although the number of chemicals examined is still too small to permit a full evaluation of the correlation between in vitro cell transformation and in vivo carcinogenicity, it is clear that the sensitivity of the focus formation assay is very high. In the case of the metabolic cooperation assay, the sensitivity appears to be rather poor, but the assay can be considered to be useful because of its simple procedure and its considerable database. These in vitro assays for tumour promoters are recommended as useful tools for the detection of non-genotoxic carcinogens.