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Major metabolites of alpha-asarone in liver microsomes are epoxide-derived side-chain diols. The intermediately formed epoxides are mutagenic and form DNA adducts and thus are likely responsible for the (hepato) carcinogenic effect of alpha-asarone observed in male mice. We here investigated the role of eight human cytochrome P450 enzymes (CYP1A1, 1A2, 2A6, 2B6, 2C19, 2D6, 2E1, and 3A4) in the metabolism of alpha-asarone using Supersomes™. The epoxidation of the side-chain of alpha-asarone was mainly catalyzed by CYP3A4 and to a lesser extent by 2B6 and 1A1 whereas the hydroxylation of the side-chain leading to (E)-3'-hydroxyasarone was catalyzed by all investigated CYPs excluding CYP2A6. O-demethylation was catalyzed by CYP1A1, 2A6, 2B6, and 2C19. Applying relative activity factors (RAF) to the observed formation rates revealed that CYP3A4, at least at lower substrate concentrations, is nearly solely responsible for the formation of the mutagenic side-chain epoxides of alpha-asarone. Comparison of the RAF-corrected formation rates of all metabolites with those found in incubation with human liver microsomes revealed that the side-chain hydroxylation and epoxidation can be explained in good approximation by the tested hepatic CYPs, whereas other CYPs or enzymes may contribute to the O-demethylation of alpha-asarone. Therefore, the capacity for metabolic activation of alpha-asarone has to be expected to be widely present among the general population.

Acrylamide (AA) is a carcinogen formed during thermal food processing and can cause tumors in rodents while its carcinogenic potency in humans is unclear. Metabolism of AA, preferentially in the liver, leads to glycidamide (GA) forming N7-GA-guanine (N7-GA-Gua) as the major AA-derived DNA adduct in rodents. Here, a novel method allowing high sensitivity by avoidance of major matrix effects was applied to analyze N7-GA-Gua levels in nuclear DNA from rat hepatocytes in primary culture. We could thus for the first time detect a background level of 5-10 adducts/108 nucleosides in untreated hepatocytes. Incubation with AA did not result in a statistically significant increase in adduct levels over background up to a substrate concentration of 500 μM although a trend to slightly higher adduct levels was observed at and above 200 μM AA. At concentrations > 500 μM significant increases in N7-GA-Gua levels were found. When Benchmark concentration (BMC) modeling was applied to the data, non-linear concentration-response curves were obtained suggesting that AA started to cause measurable increases over background of N7-GA-Gua levels above certain concentrations only. Calculation of the composite BMCL10 (Lower Bound of a 95 % confidence interval) of a BMC leading to a 10 % increase of N7-GA-Gua levels over background resulted in a value of 6.35 μM AA after 24 h. A concentration below this value cannot be expected to lead to an increase in N7-GA-Gua of more than 10 % over the background seen in untreated hepatocytes.

Acrylamide (AA) is a carcinogen formed during thermal food processing and can cause tumors in rodents while its carcinogenic potency in humans is unclear. Metabolic conversion of AA leads to glycidamide (GA) forming N7-GA-guanine (N7-GA-Gua) as the major DNA adduct in rodents while no such adducts were found in human tissues so far. In a cohort of 56 healthy volunteers adduct levels were determined in peripheral blood mononuclear cell (PBMC) DNA and anthropometric, dietary, and biochemical parameters were measured or inquired using a questionnaire. In the majority of PBMC DNA samples the levels found were above one adduct/108 nucleosides not being correlated to dietary habits including coffee consumption, or to blood glucose levels or hemoglobin HbA1c. However, adduct levels were significantly correlated with the body mass index (BMI) and showed a continuous increase over three BMI classes. Our findings indicate a background of AA-derived DNA adducts present in humans in PBMC related to body mass rather than to certain dietary or lifestyle factors.

Chemical contaminants and residues are undesired chemicals occurring in consumer products such as food and drugs, at the workplace and in the environment, i.e. in air, soil and water. These compounds can be detected even at very low concentrations and lead frequently to considerable concerns among consumers and in the media. Thus it is a major challenge for modern toxicology to provide transparent and versatile tools for the risk assessment of such compounds in particular with respect to human health. Well-known examples of toxic contaminants are dioxins or mercury (in the environment), mycotoxins (from infections by molds) or acrylamide (from thermal treatment of food). The process of toxicological risk assessment of such chemicals is based on i) the knowledge of their contents in food, air, water etc., ii) the routes and extent of exposure of humans, iii) the toxicological properties of the compound, and, iv) its mode(s) of action. In this process quantitative dose-response relationships, usually in experimental animals, are of outstanding importance. For a successful risk assessment, in particular of genotoxic chemicals, several conditions and models such as the Margin of Exposure (MoE) approach or the Threshold of Toxicological Concern (TTC) concept exist, which will be discussed.

Formation of DNA adducts by five alkenylbenzenes, safrole, methyl eugenol, eugenol, and asarone with either α- or β-conformation, was analyzed in fetal avian livers in two in ovo models. DNA reactivity of the carcinogens safrole and methyl eugenol was previously demonstrated in the turkey egg model, whereas non-genotoxic eugenol was negative. In the current study, alkenylbenzenes were also tested in the chicken egg model. Injections with alkenylbenzenes were administered to fertilized turkey or chicken eggs for three consecutive days. Three hours after the last injection, liver samples were evaluated for DNA adduct formation using the 32P-nucleotide postlabeling assay. DNA samples from turkey livers were also analyzed for adducts using mass spectrometry. In both species, genotoxic alkenylbenzenes safrole, methyl eugenol, α- and β-asarone produced DNA adducts, the presence and nature of which, with exception of safrole, were confirmed by mass spectrometry, validating the sensitivity of the 32P-postlabeling assay. Overall, the results of testing were congruent between fetal turkey and chicken livers, confirming that these organisms can be used interchangeably. Moreover, data obtained in both models is comparable to genotoxicity findings in other species, supporting the usefulness of avian models for the assessment of genotoxicity as a potential alternative to animal models.

α-, β- and γ-asarone are naturally occurring phenylpropenes that occur in different plant families, mainly in Aristolochiaceae, Acoraceae and Lauraceae. Plants containing asarones are used as flavouring ingredients in alcoholic beverages (bitters), traditional phytomedicines and the rhizome of e.g. Acorus calamus is used to prepare tea. Although α- and β-asarone show a potential in the treatment of several diseases, previous studies have shown carcinogenicity in rodents (duodenum, liver). However, the mechanism of action remained unclear. Studies on the mutagenicity of propenylic α- and β-asarone are inconsistent and data on carcinogenicity and genotoxicity of allylic γ-asarone are lacking completely. Thus, the present study determined the mutagenicity of the three asarone isomers using the Ames fluctuation assay with and without exogenous metabolic activation (S9 mix) in the standard Salmonella typhimurium strains TA98 and TA100. A concentration dependent increase in mutagenicity could be verified for α- and β-asarone in strain TA100 in the presence of rat liver homogenate. The side-chain epoxides of α- and β-asarone, major metabolites formed in liver microsomes, caused mutations in TA100, supporting the hypothesis that epoxidation of the side chain plays a key role in mutagenicity of the propenylic alkenylbenzenes. The allylic γ-asarone, not undergoing detectable side-chain epoxidation in liver microsomes, was supposed to be activated via side-chain hydroxylation and further sulphonation, a typical pathway for other allylic alkenylbenzenes like estragole or methyleugenol. However, neither y-asarone nor 1'-OH-γ-asarone showed any mutagenic effect even in the human SULT-expressing Salmonella strains (TA100-hSULT1A1 and TA100-hSULT1C2), while 1'-OH-methyleugenol used as a positive control was mutagenic under these conditions. These results indicate that the propenylic asarones are genotoxic via metabolic formation of side-chain epoxides while the side-chain hydroxylation/sulphonation pathway is either not operative or does not lead to mutagenicity with the allylic γ-asarone.

Alpha-asarone (1) is a naturally occurring phenylpropene found in several plants, e.g. Acorus calamus. 1-containing plant materials and essential oils thereof are used for flavoring foods and in many phytopharmaceuticals. 1 has been claimed to have positive pharmacological effects, however, it is carcinogenic in male mice (liver) and probably genotoxic. Since the metabolic pathways of 1 have not been investigated and its carcinogenic mode of action is unknown, we investigated the metabolism of 1 in liver microsomes of rat, bovine, porcine, and human origin using HPLC-DAD and LC-ESI-MS/MS and derived kinetic data on the metabolite formation. The main metabolic pathway was the side-chain hydroxylation leading to (E)-3'-hydroxyasarone (2). Epoxidation of 1 presumably led to (E)-asarone-1',2'-epoxide (4) which instantly hydrolyzed to form erythro- and threo-configured diols (5b+5a). As a minor reaction O-demethylation of 1 was observed. The metabolite formation showed little species-specific differences with the exception of porcine liver microsomes for which the formation of diols 5b+5a exceeded the formation of alcohol 2. The kinetic parameters imply a dependence of the pattern of metabolite formation from substrate concentration. On the basis of our results and earlier findings we hypothesize the genotoxic epoxide 4 being the ultimate carcinogen metabolically formed from 1.

While alpha-asarone (aA) and beta-asarone (bA) are genotoxic and were shown to be carcinogenic the mechanisms underlying these effects are not understood. Major metabolites of both compounds are epoxides which are mutagenic in the Ames test. We investigated their reactivity towards nucleosides and identified epoxide-derived DNA adducts with 2'-deoxyadenosine (dA) and 2'-deoxyguanosine (dG) using UPLC-UV/VIS, LC-MS/MS and NMR spectroscopy. The adducts were characterized as N6-1'-hydroxy-dihydro-asarone-dA and N2-1'-hydroxy-dihydro-asarone-dG. Chemical synthesis of these adducts, isotope labeled standards and development of a sensitive and specific isotope dilution mass spectrometric method allowed the quantification of DNA adducts formed in primary rat hepatocytes incubated with aA or bA over up to 48 h. We observed a concentration-dependent, nearly linear formation of DNA adducts, which was higher for bA than for aA. In time course experiments, the amount of DNA adducts reached a maximum within the first 6 h. Over the next 42 h, the amount of DNA adducts decreased, however DNA adducts were still detectable even at the lowest substrate concentration of 10 μM. These results clearly show that aA and bA are able to form epoxide-derived DNA adducts in mammalian cells which may be responsible for their genotoxic, mutagenic and carcinogenic mode of action.

Among the various contaminants, the group of natural plant-derived substances in the modern food chain has been generating increasing concern in recent years. The adverse effects encountered may be diverse and pose risks of acute, subchronic or chronic toxicity. The underlying mechanisms of toxicity may be thresholded or be based on interactions with DNA, as for genotoxic carcinogens, for which the existence of a threshold cannot be assumed. This article gives an overview of the major plant-derived contaminants of present concern in the modern food chain and describes their mode of action and adverse effects.

This chapter covers the process-induced formation of d -amino acids and cross-linked amino acids (CLAAs) in food. The industrial processing of food and feed proteins often includes treatment in heated alkaline or acidic solutions. Such treatments lead to two major chemical changes: formation of CLAAs, such as lysinoalanine, lanthionine, or histidinoalanine, and racemization of free and protein-bound l -amino acids into their d -isomers. Both represent undesired contaminants in food particularly because they diminish the digestibility and nutritional quality of food and may exert toxic properties.

Among the various chemical compounds, the class of natural plant-derived substances in the modern food chain is generating increasing concern. Adverse effects encountered may be various and pose risks of acute, subchronic, or chronic toxicity. The underlying mechanisms of toxicity may be thresholded, or the contaminants may pose risks because of genotoxicity and carcinogenicity. This chapter gives an overview of the major classes of plant-derived undesired substances including contaminants of present concern in the modern food chain, describing their mode of action and adverse effects.

Among the various contaminants, the group of natural plant-derived substances in the modern food chain has been generating increasing concern in recent years. The adverse effects encountered may be diverse and pose risks of acute, subchronic or chronic toxicity. The underlying mechanisms of toxicity may be thresholded or be based on interactions with DNA, as for genotoxic carcinogens, for which the existence of a threshold cannot be assumed. This article gives an overview of the major plant-derived contaminants of present concern in the modern food chain and describes their mode of action and adverse effects.

Methyleugenol--a natural constituent of herbs and spices--is hepatocarcinogenic in rodent models. It can form DNA adducts after side-chain hydroxylation and sulfation. We previously demonstrated that human sulfotransferases (SULTs) 1A1 and 1A2 as well as mouse Sult1a1, expressed in Salmonella target strains, are able to activate 1'-hydroxymethyleugenol (1'-OH-ME) and 3'-hydroxymethylisoeugenol (3'-OH-MIE) to mutagens. Now we investigated the role of these enzymes in the formation of hepatic DNA adducts by methyleugenol in the mouse in vivo. We used FVB/N mice [wild-type (wt)] and genetically modified strains in this background: Sult1a1 knockout (ko), transgenic for human SULT1A1/2 (tg) and the combination of both modifications (ko-tg). Methyleugenol (50mg/kg body mass) formed 23, 735, 3770 and 4500 N (2)-(trans-methylisoeugenol-3'-yl)-2'-deoxyguanosine adducts per 10(8) 2'-deoxyribonucleosides (dN) in ko, wt, ko-tg and tg mice, respectively. The corresponding values for an equimolar dose of 1'-OH-ME were 12, 1490, 12 400 and 13 300 per 10(8) dN. Similar relative levels were observed for the minor adduct, N (6)-(trans-methylisoeugenol-3'-yl)-2'-deoxyadenosine. Thus, the adduct formation by both compounds was nearly completely dependent on the presence of SULT1A enzymes, with human SULT1A1/2 producing stronger effects than mouse Sult1a1. Moreover, a dose of 0.05 mg/kg methyleugenol (one-fourth of the estimated average daily exposure of humans) was sufficient to form detectable adducts in humanized (ko-tg) mice. Although 3'-OH-MIE was equally mutagenic to 1'-OH-ME in Salmonella strains expressing human SULT1A1 or 1A2, it only formed 0.14% of hepatic adducts in ko-tg mice compared with an equimolar dose of 1'-OH-ME, suggesting an important role of detoxifying pathways for this isomer in vivo.

Evidence has been provided that diet and environmental factors directly influence epigenetic mechanisms associated with cancer development in humans. The inhibition of histone deacetylase (HDAC) activity and the disruption of the HDAC complex have been recognized as a potent strategy for cancer therapy and chemoprevention. In the present study, we investigated whether selected plant constituents affect HDAC activity or HDAC1 protein status in the human colon carcinoma cell line HT29. The polyphenols (−)-epigallocatechin-3-gallate (EGCG) and genistein (GEN) as well as two oxidative methyleugenol (ME) metabolites were shown to inhibit HDAC activity in intact HT29 cells. Concomitantly, a significant decrease of the HDAC1 protein level was observed after incubation with EGCG and GEN, whereas the investigated ME metabolites did not affect HDAC1 protein status. In conclusion, dietary compounds were found to possess promising HDAC-inhibitory properties, contributing to epigenetic alterations in colon tumor cells, which should be taken into account in further risk/benefit assessments of polyphenols and alkenylbenzenes.

Methylisoeugenol (1,2-dimethoxy-4-propenylbenzene, 1) is a minor constituent of essential oils, naturally occurring as a mixture of cis/trans isomers. 1 is a U.S. Food and Drug Administration-approved food additive and has been given "Generally Recognized as Safe" status. Previously, metabolism of 1 has been studied in the rat, revealing mainly nontoxic cinnamoyl derivatives as major metabolites. However, data concerning the possible formation of reactive intermediary metabolites are not available to date. In this study, the oxidative metabolism of 1 was studied using liver microsomes of rat [not induced, rat liver microsomes (RLM); Aroclor1254 induced RLM (ARLM)], bovine, and human (pooled from 150 donors) origin. Incubations of these microsomes with 1 provided phase I metabolites that were separated by high-performance liquid chromatography (HPLC) and identified by NMR and UV-visible spectroscopy and/or liquid chromatography-mass spectrometry. Identity was confirmed by comparison with (1)H NMR spectra of synthesized reference compounds. Formation of metabolites was quantified by HPLC/UV using dihydromethyleugenol (10) synthesized as the internal standard. From incubations of ARLM with 1, seven metabolites could be detected, with 3'-hydroxymethylisoeugenol (2), isoeugenol and isochavibetol (3 + 4), and 6-hydroxymethylisoeugenol (5) being the main metabolites. Secondary metabolites derived from 1 were identified as the α,β-unsaturated aldehyde 3'-oxomethylisoeugenol (6) and 1',2'-dihydroxy-dihydromethylisoeugenol (7). We were surprised to find that formation of allylic 6-hydroxymethyleugenol (8) was observed starting at approximately 30 min after the beginning of incubations with ARLM. HLM did not form ring-hydroxylated metabolites but were most active in the formation of 6 and 7. ARLM incubations displayed the highest turnover rate and broadest metabolic pattern, presumably resulting from an increased expression of cytochrome P450 enzymes. In conclusion, we present a virtually complete pattern of nonconjugated microsomal metabolites of 1 comprising reactive metabolites and suggest the formation of reactive intermediates that need more investigation with respect to their possible adverse properties.

β-Asarone (1) belongs to the group of naturally occurring phenylpropenes like eugenol or anethole. Compound 1 is found in several plants, e.g., Acorus calamus or Asarum europaeum. Compound 1-containing plant materials and essential oils thereof are used to flavor foods and alcoholic beverages and as ingredients of many drugs in traditional phytomedicines. Although 1 has been claimed to have several positive pharmacological effects, it was found to be genotoxic and carcinogenic in rodents (liver and small intestine). The mechanism of action of carcinogenic allylic phenylpropenes consists of the metabolic activation via cytochrome P450 enzymes and sulfotransferases. In vivo experiments suggested that this pathway does not play a major role in the carcinogenicity of the propenylic compound 1 as is the case for other propenylic compounds, e.g., anethole. Since the metabolic pathways of 1 have not been investigated and its carcinogenic mode of action is unknown, we investigated the metabolism of 1 in liver microsomes of rats, bovines, porcines, and humans using (1)H NMR, HPLC-DAD, and LC-ESI-MS/MS techniques. We synthesized the majority of identified metabolites which were used as reference compounds for the quantification and final verification of metabolites. Microsomal epoxidation of the side chain of 1 presumably yielded (Z)-asarone-1',2'-epoxide (8a) which instantly was hydrolyzed to the corresponding erythro- and threo-configurated diols (9b, 9a) and the ketone 2,4,5-trimethoxyphenylacetone (13). This was the main metabolic pathway in the metabolism of 1 in all investigated liver microsomes. Hydroxylation of the side chain of 1 led to the formation of three alcohols at total yields of less than 30%: 1'-hydroxyasarone (2), (E)- and (Z)-3'-hydroxyasarone (4 and 6), with 6 being the mainly formed alcohol and 2 being detectable only in liver microsomes of Aroclor 1254-pretreated rats. Small amounts of 4 and 6 were further oxidized to the corresponding carbonyl compounds (E)- and (Z)-3'-oxoasarone (5, 7). 1'-Oxoasarone (3) was probably also formed in incubations with 1 but was not detectable, possibly due to its rapid reaction with nucleophiles. Eventually, three mono-O-demethylated metabolites of 1 were detected in minor concentrations. The time course of metabolite formation and determined kinetic parameters show little species-specific differences in the microsomal metabolism of 1. Furthermore, the kinetic parameters imply a very low dependence of the pattern of metabolite formation from substrate concentration. In human liver microsomes, 71-75% of 1 will be metabolized via epoxidation, 21-15% via hydroxylation (and further oxidation), and 8-10% via demethylation at lower as well as higher concentrations of 1, respectively (relative values). On the basis of our results, we hypothesize that the genotoxic epoxides of 1 are the ultimate carcinogens formed from 1.

Methyleugenol (1) is a constituent of many foods, in particular of herbal spices, and is used as flavoring agent in foodstuffs and as fragrance in cosmetics. 1 has been found to be carcinogenic in rodents, its metabolite, 1-hydroxymethyleugenol (2) acting as proximate DNA-binding carcinogen. We incubated 1 with liver microsomes of rat, bovine, and human origin. We found 2, 3-hydroxymethylisoeugenol (3), and 6-hydroxymethyleugenol (4) as major metabolites, and 1-oxomethyleugenol (5), 3-oxomethylisoeugenol (6), eugenol (9), chavibetol (11), and (RS)-2,3-dihydroxy-2,3-dihydromethyleugenol (7) as minor metabolites. Methyleugenol-2,3-epoxide (8), probably the precursor of 7, could not be detected. Incubations with synthetic metabolites were applied in order to uncover metabolic pathways. Incubations with primary rat hepatocytes revealed mainly nonconjugated 2 and conjugated 4, and minor amounts of partly conjugated 7 and conjugated 9 + 11. The "reactive metabolites" 3, 5, 6, and 8 were not detectable, possibly due to rapid reaction with cellular macromolecules. The highest cytotoxicity (resazurin reduction assay and lactate dehydrogenase leakage assay) was observed for the main metabolite 2 and its secondary metabolite 5 with EC(50) values of 50 and 10 µM, respectively. Deoxyadenosine or deoxyguanosine adducts were formed by incubating 1 or metabolites with rat hepatocytes. The rank order of adduct formation was 2 > 1 > 3 > 6, whereas 4, 5, and 8 were inactive. In conclusion, we present a virtually complete pattern of microsomal (rat, bovine, and human) and hepatocellular (rat) metabolites of 1 suggesting the formation of several reactive metabolites possibly involved in carcinogenicity, organ toxicity, and immune reactions.

In the past, it was generally accepted as a default assumption that No-Observed-Adverse-Effect Levels (NOAELs) or Lowest-Observed-Adverse-Effect Levels (LOAELs) in long-term toxicity studies are lower than in short-term ones, i.e. the toxic potency increases with prolonged exposure duration. Recent studies on pesticides and industrial chemicals reported that subacute, subchronic or chronic NOAELs/LOAELs are similar when study design factors are appropriately considered. We investigated whether these findings also apply to certain food constituents. After reviewing subchronic and chronic toxicity studies on more than 100 compounds, a total of 32 compounds could be included in the analysis. Geometric mean (GM) values of subchronic vs. chronic NOAEL or LOAEL ratios ranged from 1.0 to 2.0, with a geometric standard deviation from 2.2 to 4.2, which is consistent with data reported in the literature. While for many of the investigated compounds the ratio is around 1 - suggesting that health-based guidance values could appropriately be derived from subchronic toxicity studies - our study also identified some substances with higher ratios leading to a GM of around 2. The EFSA Scientific Committee suggested to apply an uncertainty factor of 2 to extrapolate from subchronic to chronic studies and, as a precautionary approach, we concur with this suggestion. published