Search

Triptolide (TP) is a major bioactive compound derived from Tripterygium wilfordii Hook. F. (TwHF) known for its medicinal properties, but it also exhibits potential toxic effects. It has been demonstrated to induce severe male reproductive toxicity, yet the precise mechanism behind this remains unclear, which limits its broad clinical application. This study aimed to investigate the mechanisms underlying testicular damage and spermatogenesis dysfunction induced by TP in mice, using both mouse models and the spermatocyte-derived cell line GC-2spd. In the present study, it was found that TP displayed significant testicular microstructure damaged and spermatogenesis defects including lower concentration and abnormal morphology by promoting ROS formation, MDA production and restraining GSH level, glutathione peroxidase 4 (GPX4) expression in vivo. Furthermore, Ferrostatin-1 (FER-1), a ferroptosis inhibitor, was found to significantly reduce the accumulation of lipid peroxidation, alleviate testicular microstructural damage, and enhance spermatogenic function in mice. Besides, notably decreased cell viability, collapsed mitochondrial membrane potential, and elevated DNA damage were observed in vitro. The above-mentioned phenomenon could be reversed by pre-treatment of FER-1, indicating that ferroptosis participated in the TP-mediated spermatogenesis dysfunction. Mechanistically, TP could enhance GPX4 ubiquitin degradation via triggering K63-linked polyubiquitination of GPX4, thereby stimulating ferroptosis in spermatocytes. Functionally, GPX4 deletion intensified ferroptosis and exacerbated DNA damage in GC-2 cells, while GPX4 overexpression mitigated ferroptosis induced by TP. Overall, these findings for the first time indicated a vital role of ferroptosis in TP induced-testicular injury and spermatogenic dysfunction through promoting GPX4 K63-linked polyubiquitination, which hopefully offers a potential therapeutic avenue for TP-related male reproductive damage. In addition, this study also provides a theoretical foundation for the improved clinical application of TP or TwHF in the future., Competing Interests: Declaration of competing interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper., (Copyright © 2024 Elsevier B.V. All rights reserved.)

Vitamin B 12 (cyano- or hydroxo-cobalamin) acts, via its coenzymes, methyl- and adenosyl-cobalamin, as a partner for enzymatic reactions in humans catalysed by methionine synthase and methylmalonyl-CoA mutase. As well as its association with pernicious anaemia, human B 12 deficiency may also be a risk factor for neurological illnesses, heart disease and cancer. In the present work the effect of vitamin B 12 (hydroxocobalamin) on the formation of DNA adducts by the epoxide phenyloxirane (styrene oxide), a genotoxic metabolite of phenylethene (styrene), has been studied using an in vitro model system. Styrene was converted to its major metabolite styrene oxide as a mixture of enantiomers using a microsomal fraction from the livers of Sprague-Dawley rats with concomitant inhibition of epoxide hydrolase. However, microsomal oxidation of styrene in the presence of vitamin B 12 gave diastereoisomeric 2-hydroxy-2-phenylcobalamins. The quantitative formation of styrene oxide-DNA adducts was investigated using 2-deoxyguanosine or calf thymus DNA in the presence or absence of vitamin B 12 . Microsomal incubations containing either deoxyguanosine or DNA in the absence of vitamin B 12 gave 2-amino-7-(2-hydroxy-1-phenylethyl)-1,7-dihydro-6H-purin-6-one [N7-(2-hydroxy-1-phenylethyl)-guanine], and 2-amino-7-(2-hydroxy-2-phenylethyl)-1,7-dihydro-6H-purin-6-one [N7-(2-hydroxy-2-phenylethyl)guanine] as the principal adducts. With deoxyguanosine the level of formation of guanine adducts was ca. 150 adducts/10 6 unmodified nucleoside. With DNA the adduct level was 36 pmol/mg DNA (ca. 1 adduct/0.83 × 10 5 nucleotides). Styrene oxide adducts from deoxyguanosine or DNA were not detected in microsomal incubations of styrene in the presence of vitamin B 12 . These results suggest that vitamin B 12 could protect DNA against genotoxicity due to styrene oxide and other xenobiotic metabolites. However, this potential defence mechanism requires that the 2-hydroxyalkylcobalamins derived from epoxides are not 'anti-vitamins' and ideally liberate, and therefore, recycle vitamin B 12 . Otherwise, depletion of vitamin B 12 leading to human deficiency could increase the risk of carcinogenesis initiated by genotoxic epoxides., (Copyright © 2023 The Authors. Published by Elsevier B.V. All rights reserved.)

Triptolide is a predominant active component of Triptergium wilfordii Hook. F, which has been used for the treatment of cancers and autoimmune diseases such as rheumatoid arthritis, systemic lupus erythematosus and diabetic nephropathy. Therefore, triptolide and its derivates are considered to have promising prospects for development into drugs. However, the clinical application of triptolide is limited due to various organ toxicities, especially liver toxicity. The potential mechanism of triptolide-induced hepatotoxicity has attracted increasing attention. Over the past five years, studies have revealed that triptolide-induced liver toxicity is involved in metabolic imbalance, oxidative stress, inflammations, autophagy, apoptosis, and the regulation of cytochrome P450 (CYP450) enzymes, gut microbiota and immune cells. In this review, we summarize the pharmacological applications and hepatotoxicity mechanism of triptolide, which will provide solid theoretical evidence for further research of triptolide., Competing Interests: Declaration of competing interest The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper., (Copyright © 2023 Elsevier B.V. All rights reserved.)

Acrylamide (AA) is classified as a probable human carcinogen and is ubiquitous in foods processed at high temperatures. The carcinogenicity of AA has been attributed to its active metabolite, glycidamide (GA). Both AA and GA can spontaneously or enzymatically conjugate with glutathione (GSH) to form their corresponding GSH conjugates. Profiling AA-glutathione conjugate (AA-GSH) and GA-glutathione conjugates (2 isomers: GA2-GSH and GA3-GSH) in serum would better illustrate AA detoxification compared with urinary metabolite analysis. However, the lack of AA-, GA2, and GA3-GSH study remains a critical data gap. Our study aimed to investigate the toxicokinetics of AA-, GA2-and GA3-GSH in Sprague Dawley rats treated with 0.1 mg/kg, 1.0 mg/kg, or 5.0 mg/kg AA. Blood samples were collected for LC-MS/MS analysis of the GSH conjugate products. Within 24 h of treatment, we observed rapid formation, elimination, and linear kinetics of AA-, GA2-and GA3-GSH. The ∑GA-GSH AUC/AA-GSH AUC ratios were 0.14-0.29, similar to ∑GA/AA AUC in serum but different from ∑GA/AA-derived urinary mercapturic acids in rodents. Our analysis of AA- and GA-GSHs values represents direct detoxification of AA and GA in vivo. This study advances our understanding of sex and inter-species differences in AA detoxification and may refine the existing kinetic models for a more relevant risk extrapolation., (Copyright © 2021. Published by Elsevier B.V.)

Epidemiological studies of 1,3-butadiene (BD) exposures have reported a possible association with chronic myelogenous leukemia (CML), which is defined by the presence of the t(9;22) translocation (Philadelphia chromosome) creating an oncogenic BCR-ABL fusion gene. Butadiene diepoxide (DEB), the most mutagenic of three epoxides resulting from BD, forms DNA-DNA crosslink adducts that can lead to DNA double-strand breaks (DSBs). Thus, a study was designed to determine if (±)-DEB exposure of HL60 cells, a promyelocytic leukemia cell line lacking the Philadelphia chromosome, can produce t(9;22) translocations. In HL60 cells exposed for 3 h to 0-10 μM DEB, overlapping dose-response curves suggested a direct relationship between 1,4-bis-(guan-7-yl)-2,3-butanediol crosslink adduct formation (R = 0.977, P = 0.03) and cytotoxicity (R = 0.961, P = 0.002). Experiments to define the relationships between cytotoxicity and the induction of micronuclei (MN), a dosimeter of DNA DSBs, showed that 24 h exposures of HL60 cells to 0-5.0 μM DEB caused significant positive correlations between the concentration and (i) the degree of cytotoxicity (R = 0.998, p = 0.002) and (ii) the frequency of MN (R = 0.984, p = 0.016) at 48 h post exposure. To determine the relative induction of MN and t(9;22) translocations following exposures to DEB, or x-rays as a positive control for formation of t(9;22) translocations, HL60 cells were exposed for 24 h to 0, 1, 2.5, or 5 μM DEB or to 0, 2.0, 3.5, or 5.0 Gy x-rays, or treatments demonstrated to yield 0, 20%, 50%, or 80% cytotoxicity. Treatments between 0 and 3.5 Gy x-rays caused significant dose-related increases in both MN (p < 0.001) and t(9;22) translocations (p = 0.01), whereas DEB exposures causing similar cytotoxicity levels did not increase translocations over background. These data indicate that, while DEB induces DNA DSBs required for formation of MN and translocations, acute DEB exposures of HL60 cells did not produce the Philadelphia chromosome obligatory for CML., (Copyright © 2019 The Authors. Published by Elsevier B.V. All rights reserved.)

DNA adducts can be formed from covalent binding of electrophilic reactive compounds to the nucleophilic N- and O-atoms of the biomolecule. The O-sites on DNA, with nucleophilic strength (n) of ca. 2, is recognized as a critical site for mutagenicity. Characterization of the reactivity of electrophilic compounds at the O-sites can be used to predict their mutagenic potency in relative terms. In the present study, reaction kinetic experiments were performed for butadiene monoxide (BM) in accordance with the Swain-Scott relation using model nucleophiles representing N- and O-sites on DNA, and earlier for glycidamide (GA) using a similar approach. The epoxide from the kinetic experiments was trapped by cob(I)alamin, resulting in formation of an alkylcobalamin which was analyzed by liquid chromatography tandem mass spectrometry. The Swain-Scott relationship was used to determine selectivity constant (s) of BM and GA as 0.86 and 1.0, respectively. The rate constant for the reaction at n of 2 was extrapolated to 0.023 and 0.038 M -1  h -1 for BM and GA, respectively, implying a higher mutagenic potency per dose unit of GA compared to BM. The reaction kinetic parameters associated with mutagenic potency were also estimated by a density functional theory approach, which were in accordance to the experimental determined values. These types of reaction kinetic measures could be useful in development of a chemical reactivity based prediction tool that could aid in reduction of animal experiments in cancer risk assessment procedures for relative mutagenicity., (Copyright © 2018 Elsevier B.V. All rights reserved.)

Acorus calamus has a rich history in natural medicine, and offers many health benefits. The plant has anti-inflammatory, antimicrobial, diuretic, antiurolithiatic and other properties. Moreover, various parts, especially the rhizome and roots, are sources of a range of bioactive phenolic compounds with beneficial effects on the cardiovascular system. This review article summarizes the current knowledge of the chemical composition of different parts of A. calamus and their roles in the prevention and treatment of cardiovascular diseases. However, as no human studies have been performed, the review only includes in vitro and animal studies. The paper also briefly reviews the toxicity of A. calamus and its products for human health, especially regarding the cardiovascular system., (Copyright © 2017 Elsevier B.V. All rights reserved.)

Triptolide (TP) is a diterpene triepoxide with variety biological activities, such as anti-inflammatory, anti-cancerogenic, immunomodulatory and pro-apoptotic activities. However, its clinical application was limited by potential toxicity. Quercetin (Que) is a member of flavonoids with anti-oxidant effects. In this study, we aimed to demonstrate the protective effect of Que in TP-induced oxidative stress and decrease of testosterone generation in reproductive damage. Leydig cells were treated with TP (20, 40 and 60 nM), which caused obvious oxidative stress increasing intracellular ROS, decreasing activities and expressions of GPx and SOD. Apoptosis was resulted from depolarization of mitochondrial membrane potential (ΔΨm) and release of cytochrome C (Cyt-C) showing increase of BAX/Bcl-2 ratio, caspase-3 and caspase-9. Treatment of Que (5 μM) prior to triptolide could restore all the TP-induced alteration in a certain dose range indicating that the oxidative stress might be one reason of TP-induced reproductive toxic effect. These results suggest that the compatibility with Que might reduce the TP-induced reproductive toxicity, which provide a probability to extend the usage of TP., (Copyright © 2015 Elsevier Ireland Ltd. All rights reserved.)

Methacrylates are used in the polymer form as composite restorative materials in dentistry. However, the polymers can release monomers and co-monomers into the oral cavity and pulp, from where they can migrate into the bloodstream reaching virtually all organs. The local concentration of the released monomers can be in the millimolar range, high enough to induce adverse biological effects. Genotoxicity of methacrylate monomers is of a special significance due to potential serious phenotypic consequences, including cancer, and long latency period. In the present work, we investigated cytotoxicity and genotoxicity of glycidyl methacrylate (GMA) in the human peripheral blood lymphocytes and the CCR-CM human cancer cells. GMA at concentrations up to 5mM evoked a concentration-dependent decrease in the viability of the lymphocytes up to about 80%, as assessed by flow cytometry. This agent did not induce strand breaks in the isolated plasmid DNA, but evoked concentration-dependent DNA damage in the human lymphocytes evaluated by the alkaline and neutral comet assay. This damage included oxidative modifications to the DNA bases, as checked by DNA repair enzymes Endo III and Fpg as well as single and double DNA strand breaks. The lymphocytes exposed to GMA at 2.5 microM were able to remove about 90% of damage to their DNA in 120 min. The ability of GMA to induce DNA double-strand breaks was confirmed by pulsed field gel electrophoresis. The drug evoked apoptosis and induced an increase in the G2/M cell population, accompanied by a decrease in the S cell population and an increase in G0/G1 cell population. Due to broad spectrum of GMA genotoxicity, including DNA double-strand breaks, and a potential long-lasting exposure to this compound, its use should be accompanied by precautions, reducing the chance of its release into blood stream and the possibility to induce adverse biological effects.

The carcinogenicity of 1,3-butadiene (BD) is related to its bioactivation to several DNA-reactive metabolites; accumulating evidence suggests that the stereochemistry of these BD intermediates may play a significant role in the mutagenic and carcinogenic actions of the parent compound. The objective of this study was to evaluate the cytotoxicity and mutagenicity of stereochemical forms of 1,2-epoxybutene (EB) and 1,2:3,4-diepoxybutane (DEB), two genotoxic BD metabolites, in a human lymphoblastoid cell line, TK6. Cytotoxicity was measured by comparing cloning efficiencies in chemical-exposed cells versus those in control cells. The hypoxanthine-guanine phosphoribosyltransferase (HPRT) and thymidine kinase (TK) mutant frequencies (MFs) were measured using a cell cloning assay. HPRT mutants collected from cells exposed to the three forms of DEB were analyzed by PCR to characterize large genetic alterations. All the three stereoisomers of DEB caused increased HPRT and TK MFs compared to the concurrent control samples. There were no significant differences in cytotoxicity or mutagenicity among the three isomers of DEB in TK6 cells. Molecular analysis of HPRT mutants revealed similar distributions of types of mutations among the three isomers of DEB. There were also no statistically significant differences in mutagenic efficiencies between the two isomers of EB in TK6 cells. These results were consistent with the in vivo findings that there was little difference in the mutagenic efficiencies of racemic-DEB versus meso-DEB in rodents. Thus, in terms of mutagenic efficiency, stereochemical configurations of EB and DEB are not likely to play a significant role in the mutagenicity and carcinogenicity of BD.

1,3-Butadiene (BD) is a well-documented mutagen and carcinogen in rodents and is currently classified as a probable carcinogen in humans. Studies investigating workers exposed to BD indicate that, in some plants, there may be an increased genetic risk, and that polymorphisms in biotransformation and DNA repair proteins may modulate genetic susceptibility. To investigate the role of genetic polymorphisms in microsomal epoxide hydrolase (mEH) or nucleotide excision repair (NER) in contributing to the mutagenicity of BD, we conducted a series of experiments in which mice lacking mEH or NER activity were exposed to BD by inhalation or to the reactive epoxide metabolites of BD (epoxybutene-EB or diepoxybutane-DEB) by i.p. injection. Genetic susceptibility was measured using the Hprt cloning assay. Both deficient strains of mouse were significantly more sensitive to the mutagenic effects of BD and the injected epoxides. These studies provide support for the critical role that mEH plays in the biotransformation of BD, and the role that NER plays in maintaining genomic integrity following exposure to BD. Additional studies are needed to examine the importance of base excision repair (BER) in maintaining genomic integrity, the differential formation of DNA and protein adducts in deficient strains, and the potential for enhanced sensitivity to BD genotoxicity in mice either lacking or deficient in both biotransformation and DNA repair activity.

The aim of this review is to summarize our recent data on butadiene (BD) derived hemoglobin adducts as biomarkers for the internal formation of the individual epoxides formed by butadiene (BD). It is well known that BD is oxidized by cytochrome P450s to several epoxides that form DNA and protein adducts. 1,2-Epoxy-3-butene (EB), 1,2;3,4-diepoxybutane (DEB) and 1,2-epoxy-3,4-butanediol (EB-diol) form N-(2-hydroxy-3-butenyl)-valine (HB-Val), N,N-(2,3-dihydroxy-1,4-butadiyl)-valine (pyr-Val) and N-(2,3,4-trihydroxybutyl)-valine (THB-Val) adducts, respectively. The analysis of HB-Val and THB-Val by the modified Edman degradation and GC-MS/MS has generated valuable insights into BD metabolism across species. In addition, a recently established method for the analysis of pyr-Val has been proven to be suitable for detection of pyr-Val in rodents exposed to BD as low as 1 ppm. These technologies have been applied to study a wide range of exposures to BD, EB, DEB, and 3-butene-1,2-diol as a precursor of EB-diol in male and female mice and rats. Altogether the data have shown that BD metabolism is species and concentration dependent, consistent with metabolism and carcinogenesis data. Mice form much more HB-Val and pyr-Val than rats, especially at low exposures. After 10 days of inhalation exposure to 3 ppm BD, mice formed 12.5-fold more pyr-Val than rats. In contrast, the amounts of THB-Val were similar in mice and rats exposed to 3 or 62.5 ppm BD. Furthermore, it appears that the formation of THB-Val is supralinear in mice and rats due to saturation of metabolic activation pathways. Gender differences in metabolism are less well established. One study with male and female rats exposed to 1000 ppm BD for 90 days demonstrated a 1.6-, 3.5- and 2.0-fold gender difference in formation of HB-Val, pyr-Val and THB-Val, respectively, with females being more efficient in epoxide formation. The analyses of BD derived protein adducts correlate well with the observed species and gender differences in BD-carcinogenesis and suggest that DEB may indeed be the most important metabolite.

1,3-Butadiene (BTD) is an important commodity chemical and air pollutant that has been shown to be a potent carcinogen in mice, and to a lesser extent, a carcinogen in rats. To better assess butadiene's carcinogenic risk to humans, it is important to understand its mode of action and how this relates to differences in responses among species. In a series of in vitro experiments, lymphocytes from rats, mice, and humans were exposed to 3,4-epoxy-1-butene (EB) or 1,2:3,4-diepoxybutane (DEB) for 1h at the G(0) stage of the cell cycle, stimulated to divide, and cultured to assess the ability of these metabolites to induce sister chromatid exchange (SCE) and chromosome aberrations (CAs). EB induced no increases in SCEs or CAs in the cells from the three species. DEB was a potent SCE- and CA-inducer, with the results being similar in each rodent species. The response for SCEs seen in the human cells was more complex, with genetic polymorphism for glutathione-S-transferases (GST) possibly modulating the response. The single cell gel electrophoresis assay was used on genetically engineered V79 cell lines to investigate a possible influence of GST status. Experiments were also conducted to investigate the reason for EB's failure to induce SCEs or CAs in G(0) cells. The results indicate that EB-induced DNA damage was repaired before DNA synthesis in unstimulated lymphocytes, but EB caused a large increase in SCEs if actively cycling cells were treated. Thus, the results indicate that DEB damage is persistent in G(0) cells, and DEB is a much more potent genotoxicant than EB. The carcinogenic effect of butadiene will most likely depend on the degree to which DEB is produced and reaches target tissues, and to a lesser extent on the ability of EB to reach actively dividing or repair deficient cells.

1,3-Butadiene (BD) is a major industrial chemical and a rodent carcinogen, with mice being much more susceptible than rats. Oxidative metabolism of BD, leading to the DNA-reactive epoxides 1,2-epoxy-3-butene (BMO), 1,2-epoxy-3,4-butanediol (EBD) and 1,2:3,4-diepoxybutane (DEB), is greater in mice than rats. In the present study the DNA adduct profiles in liver and lungs of rats and mice were determined following exposure to BMO and to BD since these profiles may provide qualitative and quantitative information on the DNA-reactive metabolites in target tissues. Adducts detected in vivo were identified by comparison with the products formed from the reaction of the individual epoxides with 2'-deoxyguanosine (dG). In rats and mice exposed to [4-14C]-BMO (1-50 mg/kg, i.p.), DNA adduct profiles were similar in liver and lung with N7-(2-hydroxy-3-butenyl)guanine (G1) and N7-(1-(hydroxymethyl)-2-propenyl)guanine (G2) as major adducts and N7-2,3,4-trihydroxybutylguanine (G4) as minor adduct. In rats and mice exposed to 200 ppm [2,3-14C]-BD by nose-only inhalation for 6 h, G4 was the major adduct in liver, lung and testes while G1 and G2 were only minor adducts. Another N7-trihydroxybutylguanine adduct (G3), which could not unambiguously be identified but is either another isomer of N7-2,3,4-trihydroxybutylguanine or, more likely, N7-(1-hydroxymethyl-2,3-dihydroxypropyl)guanine, was present at low concentrations in liver and lung DNA of mice, but absent in rats. The evidence indicates that the major DNA adduct formed in liver, lung and testes following in vivo exposure to BD is G4, which is formed from EBD, and not from DEB.

Isoprene (2-methylbuta-1,3-diene) is a large-scale petrochemical used principally in the manufacture of synthetic rubbers. It is also produced by plants and trees and is the major endogenous hydrocarbon formed by mammals, probably from mevalonic acid. Isoprene is metabolised by mammals in processes that involve epoxidation by cytochrome P450-dependent monooxygenases to the isomeric mono-epoxides, (1-methylethenyl)-oxirane and 2-ethenyl-2-methyloxirane. Further metabolism of the mono-epoxides to mutagenic isoprene di-epoxides, (2, 2')-2-methylbioxiranes, can also occur. The oxidations to the mono- and di-epoxides occur enantioselectively and diastereoselectively. The mono-epoxides are hydrolysed enantioselectively to vicinal diols under catalysis by epoxide hydrolase. 2-Ethenyl-2-methyloxirane is also readily hydrolysed non-enzymatically. Because of the stereochemical possibilities for metabolites, the metabolism of isoprene is complex. The metabolism of isoprene by liver microsomes in vitro from a range of species including rat, mouse and human shows significant differences between species, strains and gender in respect of the diastereoselectivity and enantioselectivity of the metabolic oxidation and hydrolysis reactions. The impact of the extra methyl in isoprene on di-epoxide reactivity also appears to be critically important for the resulting biological effects. Isoprene di-epoxides may exhibit a lower cross-linking potential in vivo compared to butadiene di-epoxides. Differences in metabolism and reactivity of metabolites may be factors contributing to the significant differences in toxicological response to isoprene observed between species.

1,3-Butadiene is a rodent carcinogen and its epoxide metabolites, 1,2-epoxy-3-butene (EB), 1,2-epoxy-3,4-butanediol (EBD), and 1,2:3,4-diepoxybutane (DEB) have been suggested as ultimate carcinogens. This study aimed at identification and quantification of DNA adducts in rats and mice following exposure to BD and its major metabolite EB to identify the reactive epoxide(s) in target tissues. Reaction of [4-(14)C]-EB with 2'-deoxyguanosine (dG) or DNA gave equal amounts of N7-(2-hydroxy-3-butenyl)guanine (G1) and N7-(1-(hydroxymethyl)-2-propenyl)guanine (G2). Reaction of DEB stereomers with dG yielded N7-(2,3,4-trihydroxybutyl)guanine (G3) as major adduct and novel, minor adduct (G4) that was tentatively identified as N7-(1-(hydroxymethyl)-2,3-dihydroxypropyl)guanine. For the stereomers of EBD, the opposite was found: reaction with dG led to G4 as major and G3 as minor adduct. 2D-Total correlation 1H-NMR spectroscopy of G4 indicated that the N7-alkyl group was in a virtually fixed conformational state and might interact with the O(6) of guanine, which might imply a higher degree of mutagenicity of G4, due to G-C mispairing, than of any other adducts observed in this study. At 48 h following exposure to [4-(14)C]-EB (1-50 mg/kg), DNA adduct profiles in rat and mouse were qualitatively similar, with G1 and G2 as main, and G4 as minor adduct. Following nose-only exposure to 200 ppm [2,3-(14)C]-BD for 6 h, G1 and G2 were minor adducts in liver (1.9 and 8.0 per 10(8) nucleotides) and lung (1.6 and 6.6 per 10(8) nucleotides, for rats and mice, respectively). G3 was absent in rats, but present in mouse liver and lung, at 20 and 12 adducts/10(8) nucleotides. The major adduct was G4 accounting for 13 and 90 (liver) and 11 and 139 (lung) adducts/10(8) nucleotides in rats and mice, respectively. Forty-two hours later, these adduct levels had only little changed. Our recent biomarker studies confirm that following exposure to BD, but not BDO, EBD is the major epoxide available for macromolecular binding in humans and rodents. Most probably because EBD is in contrast to EB and DEB, a poor substrate for epoxide hydrolases. In conclusion, the major DNA adduct following exposure to BD is G4, originating from EBD, and not from EB or BDE. It is concluded that EBD and G4 should be taken into account for human risk assessment for exposure to BD.

1,3-Butadiene, isoprene and chloroprene have all been evaluated more than once by the IARC Monographs Programme on the Evaluation of Carcinogenic Risks to Humans, most recently in February 1998 (Volume 71). Summaries are available on-line at http://monographs.iarc.fr. 1,3-Butadiene is currently classified in Group 2A (probably carcinogenic to humans), on the basis of limited evidence for increased occupational cancer risk in humans plus sufficient evidence of carcinogenicity at multiple organ sites in rats and especially in mice exposed by inhalation. Four epidemiologic studies are available on cancer risk among workers exposed to 1,3-butadiene, one large study among styrene-butadiene rubber (SBR) workers, and one large and two small studies among 1,3-butadiene production workers. The results of the study of SBR workers suggest an association between butadiene exposure and leukaemia risk, which is consistent with the results of the large study of production workers. This latter study also suggested an increased risk of lymphoreticulosarcoma (ICD-8, 200). The major factors hampering the assessment of the available results are (i) possible misclassification of lymphoid and haematopoietic neoplasms, (ii) limitations in the assessment of past exposure (with the exception of the study of SBR workers) and (iii) a potential confounding effect of agents other than butadiene. Future research priorities include (i) the incorporation of newly developed biomarkers of exposure, (ii) the possible application of intermediate biomarkers, (iii) the replication of the study among SBR workers, possibly in Europe, and (iv) reanalysis of existing data in light of revisions of the classifications of leukaemias and lymphomas in the International Classification of Diseases for Oncology, Third Edition (2000). Isoprene is classified in Group 2B (possibly carcinogenic to humans), on the basis of sufficient evidence for carcinogenicity at multiple organ sites in both mice and rats, especially male mice, exposed by inhalation. No epidemiologic studies are available on cancer risk from occupational exposure to isoprene. Such studies could be conducted within the framework of existing or future studies of SBR workers, assuming that isoprene exposure can be disentangled from butadiene and styrene exposure. Chloroprene is classified in Group 2B on the basis of sufficient evidence for carcinogenicity at multiple organ sites in both mice and rats exposed by inhalation. Studies of chloroprene exposed workers now include chemical workers from the United States, China and Armenia as well as shoe workers from Russia. The results of the studies from China, Armenia and Russia suggest an excess risk of liver cancer. The risk of other neoplasms was not consistently increased. Limitations of available studies include possible bias from cohort enumeration, follow-up, and choice of reference population. In most studies the exposure assessment was poor, the possible confounding effect of co-exposures was not addressed and the statistical power was low. The pathology of the cases of liver cancer should be reviewed. Future research priorities include a replication of available studies in well-defined populations and the development of biomarkers of exposure.

1,3-Butadiene (BD) is a multisite carcinogen and is mutagenic in multiple tissues of B6C3F1 mice. BD is bioactivated to at least three directly mutagenic metabolites: 1,2-epoxybutene (EB), 1,2-epoxy-3,4-butanediol (EBD), and 1,2,3,4-diepoxybutane (DEB). However, the contribution of these individual metabolites to the carcinogenicity and in vivo mutatidnal spectrum of BD is uncertain. To assess the role of two BD metabolites EB and DEB in the in vivo mutagenicity of the parent compound BD, we examined the in vitro mutational spectra of EB and DEB in human and rodent cells. We also examined the in vivo mutagenicity and mutational spectrum of inhaled EB in the lung. In the bone marrow and spleen of B6C3F1 laci transgenic mice, BD-induced an increased frequency of the identical class of point mutations at A:T base pairs: AT-->GC transitions and AT-->TA transversions. BD exposure also induced an increased frequency of GC-->AT transitions in the spleen that was not observed in bone marrow, demonstrating tissue-specific differences in mutation spectrum. Exposure of Rat2 laci transgenic cells and human TK6 lymphoblasts to EB-induced an increased frequency of AT-->TA transversions. DEB exposure induced an increased frequency of AT-->TA transversions and partial deletions at hprt in human cells. In Rat laci transgenic cells, DEB was not mutagenic at laci but induced an increased frequency of micronuclei. In contrast to inhaled BD, inhaled DEB and EB were not mutagenic in the bone marrow or spleen. However, EB was mutagenic in the lungs. In the lung of mice, EB-induced specific increases in GC-->AT transitions, AT-->TA transversions, and deletion events. AT-->TA transversions are the most consistent mutation observed across biological systems following in vivo exposure to BD or in vitro exposures to EB and DEB. Although, BD exposure in mice induces chromosomal alterations and single base substitutions, the specific BD metabolite that induces the genetic events leading to tumors is uncertain. At present, it appears that only DEB can effectively induce this range of mutagenic events at levels of this metabolite that occur in the blood of mice exposed to BD. Detailed investigations to identify relevant biomarkers of BD exposure and response, particularly DNA adducts or lesions, that can be biologically linked to the range of genotoxic events known to occur in mice exposed to BD are needed.

Species differences in 1,3-butadiene (BD) bioactivation and detoxication have been implicated in the greater sensitivity of mice to the carcinogenic effects of BD compared to rats, but the molecular basis for species differences in BD metabolism is not well understood. Previous and recent work conducted in this laboratory has examined the relative rates of BD oxidation to epoxybutene (EB) in male and female B6C3F1 mouse tissues, characterized the major cytochrome P450 enzymes involved in BD bioactivation in these tissues, and determined the potential utility of the freshly isolated hepatocyte model to investigate species differences in metabolism of BD and related compounds. Collectively, the results suggest a role for P450s 2E1, 2A5, and 4B1 in sex and tissue differences in BD bioactivation in the mouse. When coordinated metabolism of EB was investigated in male B6C3F1 mouse and Sprague-Dawley rat hepatocytes, the hepatocytes from both species were found to catalyze EB oxidation to meso- and (+/-)-diepoxybutane (DEB), EB hydrolysis to 3-butene-1,2-diol (BDD), and EB conjugation to form GSH conjugates (GSEB). The metabolite area under the curve (AUC) exhibited dependence on the EB concentration used. However, the EB activation/detoxication ratios with the mouse hepatocytes were much higher than the ratios obtained with the rat hepatocytes. These results illustrate the potential utility of the hepatocyte model for estimating flux through competing metabolic pathways and predicting in-vivo metabolism of EB. Collectively, the results may allow a better understanding of the molecular and kinetic basis of species differences in BD metabolism and may lead to a more accurate assessment of human risk.

(1-Chloroethenyl)oxirane (CEO) is a metabolite of beta-chloroprene (2-chloro-1,3-butadiene, CD). The purpose of this study was to evaluate the in vitro mutagenic and clastogenic (chromosome breaking) potential of CEO. For comparative purposes, the study also included an evaluation of the racemic compounds, 3,4-epoxy-1-butene (EB) and 1,2:3,4-diepoxybutane (DEB). Mutagenicity was evaluated in a bacterial reverse mutation test (Ames), using the pre-incubation method in the presence and absence of an exogenous metabolism system (Aroclor)-induced rat liver S9). Four Salmonella typhimurium tester strains, TA97a, TA98, TA100 and TA1535 were used. The exposure concentrations in the sealed incubation vials ranged from 0 to 69 mM for CEO, 0 to 102 mM for EB, and 0 to 83 mM for DEB. All three compounds showed signs of toxicity, with DEB being substantially more toxic than either CEO or EB. Mutagenic activity was observed with all three chemicals in primarily the base pair substitution strains (S. typhimurium TA100 and TA1535), but some activity was also seen in the frameshift elimination strains (S. typhimurium TA97a and TA98). The observed mutagenic responses after exposure with CEO or EB were greater than the observed response for DEB, most likely because of the higher toxicity of DEB. Generally, the mutagenic responses were unchanged in the frameshift strains and base pair substitution strains in the presence of S9 metabolism. In vitro clastogenicity was evaluated using the cytochalasin-B blocked micronucleus test in cultured Chinese hamster V79 cells. The test was conducted without S9 metabolism because of the absence of substantial changes in the Ames test. Exposure concentrations ranged from 0 to 0.943 mM for CEO, 0 to 3.0 mM for EB, and 0 to 0.035 mM for DEB, with the upper exposure concentrations dictated by cytotoxicity. Cytotoxicity, measured as a reduction in the proportion of binucleated cells and altered cell morphology, was observed for CEO at concentrations > or =0.175 mM. Exposure to EB led to a reduced proportion of binucleated cells at concentrations > or =2.0 mM, and cell death was observed after DEB exposure at concentrations > or =0.025 mM. No clastogenicity was observed in the V79 cells when tested up to cytotoxic concentrations of CEO, whereas an elevated frequency of micronuclei was observed after exposure to either EB (> or =1.0 mM) or DEB (> or =0.0125 mM). These results suggest that CEO-induced mutagenicity, but not clastogenicity, may contribute to the observed beta-chloroprene-induced carcinogenicity in the rodent bioassay studies.

Styrene 7,8-oxide (SO), a major metabolite of styrene, is classified as a probable human carcinogen. In the present work, salmon testis DNA was reacted with SO and the alkylation products were analysed after sequential depurination in neutral or acidic conditions followed by HPLC separation and UV-detection. A novel finding was that the N-3 position of adenine was the next most reactive alkylation site in double-stranded DNA, comprising 4% of the total alkylation, as compared to alkylation at the N-7 position of guanine, 93% of the total alkylation. Both alpha- and beta-products of SO were formed at these two sites. Other modified sites were N2-guanine (1.5%, alpha-isomer), 1-adenine (0.4%, both isomers) and N6-adenine (0.7%, both isomers) as well as 1-hypoxanthine (0.1%, alpha-isomer), formed by deamination of the corresponding 1-adenine adduct. The results indicated that in double-stranded DNA N-7 of guanine and N-3 of adenine account for 97% of alkylation by SO. However, these abundant adducts are not stable, the half-life of depurination in DNA for 3-substituted adenines being approximately 10 and approximately 20 h, for alpha- and beta-isomers, respectively, and 51 h for both isomers of 7-substituted guanines.

7-(2-Hydroxypropyl)guanine (7-HPG) constitutes the major adduct from alkylation of DNA by the genotoxic carcinogen, propylene oxide. The levels of 7-HPG in DNA of various organs provides a relevant measure of tissue dose. 7-Alkylguanines can induce mutation through abasic sites formed from spontaneous depurination of the adduct. In the current study the formation of 7-HPG was investigated in male Fisher 344 rats exposed to 500 ppm of propylene oxide by inhalation for 6 h/day, 5 days/week, for up to 20 days. 7-HPG was analyzed using the 32P-postlabelling assay with anion-exchange cartridges for adduct enrichment. In animals sacrificed directly following 20 days of exposure, the adduct level was highest in the respiratory nasal epithelium (98.1 adducts per 10(6) nucleotides), followed by olfactory nasal epithelium (58.5), lung (16.3), lymphocytes (9.92), spleen (9.26), liver (4.64), and testis (2.95). The nasal cavity is the major target for tumor induction in the rat following inhalation. This finding is consistent with the major difference in adduct levels observed in nasal epithelium compared to other tissues. In rats sacrificed 3 days after cessation of exposure, the levels of 7-HPG in the aforementioned tissues had, on the average, decreased by about one-quarter of their initial concentrations. This degree of loss closely corresponds to the spontaneous rate of depurination for this adduct (t 1/2 = 120 h), and suggests a low efficiency of repair for 7-HPG in the rat. The postlabelling assay used had a detection limit of one to two adducts per 10(8) nucleotides, i.e. it is likely that this adduct could be analyzed in nasal tissues of rats exposed to less than 1 ppm of propylene oxide.

Epoxybutanediol is one of the reactive metabolites of butadiene. It is formed via hydrolysis followed by oxidation of the primary metabolite of butadiene, epoxybutene, or via hydrolysis of diepoxybutane, a secondary metabolite of butadiene. Groups of male Sprague Dawley rats were treated by intraperitoneal injection of epoxybutene, epoxybutanediol or diepoxybutane. N-(2,3,4-Trihydroxybutyl)valine adducts in haemoglobin, formed from epoxybutanediol in its reaction with N-terminal valine, were measured using the N-alkyl Edman method followed by acetylation of the Edman derivatives and analysis by gas chromatography mass spectrometry. The same adducts were also measured in male Wistar rats exposed to butadiene by inhalation and in a few workers with occupational exposure to butadiene. Haemoglobin binding indexes, HBI, (pmol adduct/g per mumol of alkylating agent, or, for butadiene, per ppm x h), were calculated. The HBI for epoxybutanediol (about 10) is comparable to that of ethylene oxide in the rat demonstrating a similar capacity of the two compounds to alkylate nucleophilic sites in vivo. The HBI of diepoxybutane (about 8) for epoxybutanediol adduct formation is approximately the same as that of epoxybutanediol itself. Epoxybutanediol adduct formation was nonlinearly related to exposure in butadiene exposed rats. The epoxybutanediol-haemoglobin adduct levels were substantially higher than those of epoxybutene in both butadiene-exposed rats and humans suggesting an important role of epoxybutanediol in the toxicity of butadiene. Adducts of epoxybutanediol are probably useful for biomonitoring of human exposure to butadiene.

Glycidyl ethers are used in epoxy resins. Epoxy resins are widely used in adhesives and coatings, as well as in electronics and structural composites, thus there is a potential of human exposure to glycidyl ethers. The aim of the present investigation was to explore the utility of haemoglobin adducts for biomonitoring of these types of compounds. Adducts to N-terminal valine were analysed by a modified Edman method with gas chromatographymass spectrometry (or tandem mass spectrometry) for adduct detection and quantification. Groups of three male mice (C3H/Hej) were administered 4 mg/mouse of allyl, butyl, phenyl or cresyl glycidyl ether (AGE, BGE, PGE or CGE) by i.p. injection. Blood samples were collected 24 h after treatment and assayed for haemoglobin adducts using the N-alkyl Edman method. Additional groups of AGE-treated mice were used to study dose response and adduct stability. The experiments with AGE indicate a linear dose response for adduct formation in the dose range studied (0, 2 and 4 mg/mouse). As expected for stable haemoglobin adducts, about 50% of the initial adduct level remained 21 days after exposure.

The activation of 4-bromocrotonic acid, 4-bromo-2-octenoic acid, valproic acid, and 3-methylglycidic acid by conversion to their CoA thioesters and the effects of these carboxylic acids on palmitoylcarnitine-supported respiration were studied with rat liver and rat heart mitochondria. 4-Bromocrotonic acid was activated by both liver and heart mitochondria, whereas 4-bromo-2-octenoic acid and valproic acid were only activated by liver mitochondria. 3-Methylglycidic acid was not a substrate of mitochondrial activation. All of the carboxylic acids that were activated also inhibited palmitoylcarnitine-supported respiration. 3-Methylglycidoyl-CoA was found to irreversibly inhibit 3-ketoacyl-CoA thiolase in a concentration-dependent and time-dependent manner. Together, these results lead to the conclusion that substituted medium-chain carboxylic acids, which enter mitochondria directly, may inhibit beta-oxidation as long as they are activated and perhaps further metabolized in the mitochondrial matrix to compounds that sequester CoA and/or inhibit beta-oxidation enzymes. Liver is more susceptible to inhibition by such xenobiotic carboxylic acids due to the broader substrate specificity of its mitochondrial medium-chain acyl-CoA synthetase (EC 6.2.1.2).

Mutagenic effect of styrene and styrene-7,8-oxide was studied with the isolated perfused rat liver as metabolizing system and Chinese hamster V79 cells as genetic target cells. Styrene-7,8-oxide which is mutagenic per se was rapidly metabolized by the perfused rat liver. Thus no mutagenic effect was detected neither in the perfusion medium nor in the bile. However when styrene was added to the perfusion system, an increase in V79 mutants was observed regardless of where in the circulating perfusion medium the V79 cells were placed: the same effect was obtained with V79 cells close to the liver as well as at a distance from the liver. No mutagenic effect was observed in the bile. Simultaneous analysis of the styrene-7,8-oxide concentration in the perfusion medium, suggest that this metabolite is not the cause of the mutagenic effect observed during perfusion with styrene. The effect of the two test compounds on some liver functions was also studied. Both styrene and styrene-7,8-oxide changed the bile flow without affecting bile acid secretion: styrene caused a reduction in bile flow as compared to control perfusions and styrene-7,8-oxide increased the bile flow. Styrene, but not styrene-7,8-oxide, reduced gluconeogenesis from lactate. Styrene had no effect on the liver's capacity to incorporate amino acids into plasma proteins, whereas styrene-7,8-oxide reduced the amino acid incorporation. The microsomal cytochrome P-450 content was not affected by the two test compounds. No alteration in microsomal N- and C-oxygenation of N,N-dimethylaniline (DMA) was observed with styrene-7,8-oxide or the lower styrene dose used (240 mumol), whereas the higher styrene concentration (480 mumol) reduced N-oxygenation and thus also the total DNA metabolism. It is suggested that the results on styrene and styrene-7,8-oxide found here using the liver perfusion/cell culture system mimic the metabolism expected to be found in the intact animal, thus indicating that styrene-7,8-oxide is not the principal mutagenic metabolite of styrene in vivo.

The reaction products of deoxyguanosine with 3,4-dimethyl-, p-methyl-, m-methyl-, m-methoxy-, p-bromo-, m-chloro- and unsubstituted styrene oxide were isolated and characterized. The reaction followed second-order kinetics. The reactive site was the N-7 site of guanine. The normal isomer (attack at CH2 of styrene oxides) and the abnormal isomer (attack at CH) were obtained. The Hammett reaction constant (rho) for the normal reaction was +0.42 and that for the abnormal reaction was -1.1. The difference of acid dissociation constant, rate of imidazole ring opening and rate of glycosidic bond cleavage was not found between the normal adduct and the abnormal adduct. Styrene oxides have been tested for toxicity and mutation in a liquid suspension assay using Escherichia coli WP2 and some of its repair deficient derivatives. Salmonella typhimurium TA100 was also employed. The mutation frequency of 3,4-dimethylstyrene oxide was higher in CM571 than in WP2. The greatest mutability was found with the WP2uvrA strain. 3,4-Dimethylstyrene oxide also acted as an inducer of E. coli K-12 (kappa). The mutagenicity of 3,4-dimethylstyrene oxide may depend on a combination of the recA-dependent and recA-independent action mechanisms. The mutagenicities of these compounds in WP2uvrA and TA100 increased in the order: m-chlorostyrene oxide = p-bromostyrene oxide less than m-methoxystyrene oxide less than styrene oxide less than m-methylstyrene oxide less than p-methylstyrene oxide less than 3,4-dimethylstyrene oxide. There was no correlation between the mutagenicities and the total reaction rates. On the other hand, the reaction rates of these compounds for the abnormal reaction correlated with their mutagenicities. The results indicate that the mutagenic effect of a chemical is not dependent simply on the quantity of the adducts, but may vary with structure of its adducts.

Aromatic diglycidyl compounds are very active mutagens when assayed in in vitro tests. In vivo, however, resorcinol diglycidyl ether provided no evidence for the clastogenic activity, while diglycidylaniline exhibited definite mutagenic activity in the micronucleus test. Since the only difference between these two compounds lies in the binding mode of the glycidyl groups to the aromatic nucleus (i.e. ether oxygen vs. aminic nitrogen), this apparent discrepancy in mutagenic activity led to the question of the mechanisms involved in such an activity difference. Although no clear signs of differential uptake or excretion could be detected in mice, differences could be seen in the spectrum of urinary metabolites; while resorcinol diglycidyl ether seemed to become fully converted to the genetically inactive bis-diol compound, a sizeable proportion of diglycidylaniline was converted only to the diol-epoxide. In vitro investigations and enzyme kinetic measurements with postmitochondrial supernatant of rat or mouse liver homogenate (S-9) finally yielded the biochemical explanation for this behaviour, as they showed a very low affinity of the diol-epoxide metabolite of diglycidylaniline for the epoxide hydrolase, normally involved in the degradation of such compounds. The diol-epoxide obtained from resorcinol diglycidyl ether, on the other hand, has an affinity to the degradation enzyme similar to, or even higher than, the one measured with the parent substance.

The 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethene (DDT) metabolic intermediate 1-chloro-2,2-bis(p-chlorophenyl)ethene (DDMU) is partially metabolized in vivo by mice to 2-hydroxy-2,2-bis(p-chlorophenyl)acetic acid (alpha OH-DDA) and other metabolites which are excreted in urine. The subsequent DDT metabolic intermediates 1-chloro-2,2-bis(p-chlorophenyl)ethane (DDMS) and 1,1-bis(p-chlorophenyl)ethene (DDNU) are metabolized to alpha OH-DDA to a much lesser extent. These results imply that DDMU may be metabolized via an alpha-chloroepoxide. The authentic DDMU-epoxide, which after oral administration is excreted as alpha OH-DDA, is mutagenic in the Ames assay, and thermally rearranges rapidly to the corresponding alpha-chloroaldehyde, 2,2-bis(p-chlorophenyl)-2-chloroacetaldehyde (alpha Cl-DDCHO). As expected alpha Cl-DDCHO yielded the same urinary metabolites as DDMU-epoxide. This suggested metabolic pathway for DDMU via a chloroepoxide intermediate may account for the tumorigenicity of DDT in mice.