Ovarian disorders in immature rats after postnatal exposure to environmental polycyclic aromatic hydrocarbons

The study investigated the effects of postnatal exposure to polycyclic aromatic hydrocarbons (PAHs) on the development of the rat ovary. Neonates were injected on each postnatal day 1–14 with benzo(a)pyrene (BaP), benz(a)anthracene (BaA) and benzo(k)fluoranthene (BkF) (0.1, 1.0, 5.0 or 10.0 mg kg^?1), ethynylestradiol (EE; 1.0 µg kg^?1) or a vehicle (control group). The rats were killed on day 23. Postnatal exposure to BaP increased the total number of antral follicles in ovaries (P < 0.05) and the number of nonatretic follicles (P < 0.01) as a result of a lower degree of apoptosis of granulosa cells, and the thickness of theca cell layers (P < 0.01). Similar histological findings were observed after BaA administration. Conversely, BkF exposure caused a decrease in the number of antral follicles, but did not alter the other investigated parameters. Degeneration of primordial oocytes after exposure to PAHs was observed only after exposure to BaP. Treatment with BaP at doses of 1.0 and 10.0 mg kg^?1 impaired 28.1 and 60.3% of the primordial follicles, respectively. Substantial alterations in ovarian ERβ expression were detected in the rats; their intensity differed with the type of PAH. Response of the ovaries to EE (three injections of 1.0 µg kg^?1 on postnatal days 20–22) in rats exposed to PAHs was suppressed in contrast to the controls. The study showed that postnatal exposure to BaP, BaA and BkF altered ovarian ERβ expression, disturbed morphological development of the ovaries and caused ovarian dysfunction in immature rats. Copyright © 2011 John Wiley & Sons, Ltd.     

Effect of carcinogenic polycyclic aromatic hydrocarbons on mouse embryonic cells in culture: Induction of spindle-shaped cells

In cultured mouse embroyonic cells (MECs) treated with benzo[a]pyrene(B[a]P), there appeared unusual type of fibroblasts, spindle-shaped cells (SP cells), which were characterized by their narrow bipolar shape, long cellular processes and optically distinct cell borders. Appearance of SP cells was massive and irreversible. The amount of SP cells increased with increased with increasing concentrations of B[a]P, while early cytotoxicity did not. In various polycyclic aromatic hydrocarbons (PAHs) tested, only potent carcinogens {7,12-dimethylabenz[a]anthracene (DMBA), 3-methylcholanthrene (MCA), B[a]P and dibenz[a, e]pyrene (DB[a, e]P)} induced SP cells. Among them, PAH having higher Iball's index induced SP cells at lower concentration and at an earlier time. Weak or non-carcinogenic PAHs including 3-hydroxybenzo-[a]-pyrene(3-H-B[a]P) did not induce SP cells. α-Napthoflavon (αNF) suppressed the induction of SP cell by carcinogenic PAH. SP cells did not appear spontaneously under various abnormal culture conditions. These results indicate that carcinogenic PAHs induce the appearance of a specific type of fibroblast, SP cells in MEC cultures in accordance with their carcinogenicity.     

Differences in benzo(a)pyrene metabolism between cultured human and murine bronchial cells after pre-treatment with benz(a)anthracene

Primary cultures of human and murine (strain C3Hz) bronchial epithelial cells were pretreated with benz(a)anthracene (BA) (10 microM). 16 h later the formation of phenolic as well as dihydrodiol metabolites of benzo(a)pyrene (BP) was measured. Whereas murine cultures showed enhanced metabolism towards both phenolic and dihydrodiol compounds, in the human cultures only phenolic BP-metabolites were increased. In view of their precursor role in the formation of biologically active diol-epoxides, formation of dihydrodiol-derivatives can be considered as a key factor in determining susceptibility to polycyclic aromatic hydrocarbon (PAH)-induced carcinogenesis. Therefore the observations of this study indicate that animal model systems for PAH carcinogenesis in man have to be selected on the basis of comparable metabolite patterns.     

Influence of red blood cells,serum albumin,and serum lipoproteins on the clearance of benzo[a]pyrene by isolated livers of 3-methylcholanthrene-treated rats

Red blood cells, serum albumin, and serum lipoproteins transport benzo[a]pyrene and other xenobiotic compounds in the circulation. The distribution of benzo[a]pyrene and its metabolites among these blood components was examined, and the effect of their presence in the perfusion medium on the ability of isolated livers from 3-methylcholanthrene-pretreated rats to clear circulating benzo[a]pyrene was determined. A large fraction (45%) of the benzo[a]pyrene in rat blood was associated with the serum lipoproteins. However, only 8% of the benzo[a]pyrene metabolites was associated with this component. Forty to forty-five percent of each was associated with red blood cells. Benzo[a]pyrene clearance by isolated rat livers was 1.8 ± 0.2 ml/min when the medium contained only red blood cells and buffer. Addition of serum lipoproteins or serum albumin increased benzo[a]pyrene clearance to 5.1 ± 0.5 or 8.5 ± 0.9 ml/min respectively. Appearance of benzo[a]pyrene metabolites in perfusion medium and bile was similarly altered by the changes in medium composition. These results indicate that the clearance of benzo[a]pyrene by rat liver depends on the composition of the medium perfusing the organ and suggest that alterations in blood components in vivo may influence the metabolic disposition of this carcinogen.     

Long-term effects of a standardized complex mixture of urban dust particulate on the metabolic activation of carcinogenic polycyclic aromatic hydrocarbons in human cells in culture.

Humans are exposed to complex mixtures of polycyclic aromatic hydrocarbons in the atmosphere. We examined the long term effects of a standard reference material (SRM) 1649a over time on the metabolic activation and DNA adduct formation by two carcinogenic PAHs, benzo[a]pyrene (BP) and dibenzo[a,l]pyrene (DBP) in the human mammary carcinoma derived cell line MCF-7. PAH-DNA adduct analysis, cytochrome P450 (CYP) enzyme activity, CYP1A1 and CYP1B1 protein expression were determined in cells treated with SRM 1649a alone or SRM 1649a with either BP or DBP for 24 to 120 h. Averaging over time, significantly higher levels of DNA adducts were observed in cells treated with BP or DBP alone than in co-treatments with SRM 1649a and BP or DBP. Ethoxyresorufin O-deethylase assay indicated a significant increase in activity in cells treated with BP alone and co-treated with SRM1649a in comparison to other treatment groups. Induction of CYP1A1 and CYP1B1 protein expression was observed by immunoblots in cells treated with BP alone or in co-treatments of SRM 1649a and BP or DBP. These data demonstrate the influence of the components of SRM 1649a in inhibiting the activation of BP or DBP by CYP enzymes in the formation of DNA adducts. It also suggests that the carcinogenic activity of PAH within a complex mixture may vary with composition and activation of the components present in the complex mixture.     

Aryl hydrocarbon receptor-independent up-regulation of intracellular calcium concentration by environmental polycyclic aromatic hydrocarbons in human endothelial HMEC-1 cells

Polycyclic aromatic hydrocarbons (PAHs) such as benzo(a)pyrene (B(a)P) constitute a major family of widely‐distributed environmental toxic contaminants, known as potent ligands of the aryl hydrocarbon receptor (AhR). B(a)P has been recently shown to trigger an early and transient increase of intracellular calcium concentration ([Ca²⁺]_i), involved in AhR‐related up‐regulation of target genes by B(a)P. This study was designed to determine whether AhR may play a role in [Ca²⁺]_i induction provoked by B(a)P. We demonstrated that, in addition to B(a)P, various PAHs, including pyrene and benzo(e)pyrene, known to not or only very poorly interact with AhR, similarly up‐regulated [Ca²⁺]_i in human endothelial HMEC‐1 cells. Moreover, α‐naphthoflavone, a flavonoïd antagonist of AhR, was also able to induce [Ca²⁺]_i. Knocking‐down AhR expression in HMEC‐1 cells through transfection of siRNAs, was finally demonstrated to not prevent B(a)P‐mediated induction of [Ca²⁺]_i, whereas it efficiently counteracted B(a)P‐mediated induction of the referent AhR target gene cytochrome P‐450 1B1. Taken together, these data demonstrate that environmental PAHs trigger [Ca²⁺]_i induction in an AhR‐independent manner. © 2011 Wiley Periodicals, Inc. Environ Toxicol, 2012.     

Characterization of the microsomal cytochrome p-450 species induced in rat liver by trans-stilbene oxide

trans-Stilbene oxide differs from the classical inducers of drug-metabolizing enzymes, pheno-barbital and 3-methylcholanthrene, in that it induces the so-called phase II activities, epoxide hydrolase and glutathione S-transferase, to a much larger extent than it induces cytochrome P-450. Nonetheless, the level of cytochrome P-450 in liver microsomes from rats treated with trans-stilbene oxide is increased significantly to twice the control value.The existence of a number of different isozymes of cytochrome P-450 has now been clearly demonstrated and in the present study we have posed the question: What form(s) of cytochrome P-450 is induced by trans-stilbene oxide? A number of criteria including substrate specificity, pattern of benzo(a)pyrene metabolism, sensitivity to inhibitors, substrate binding spectra, ethylisocyanide binding spectra, sodium dodecyi sulfate-polyacrylamide gel electrophoresis, and crossed immunoelectrophoresis were used to answer this question. It seems clear that trans-stilbene oxide induces the same form(s) of cytochrome P-450 as phenobarbital.     

Acquired and innate immunity to polyaromatic hydrocarbons

Polyaromatic hydrocarbons are ubiquitous environmental pollutants that are potent mutagens and carcinogens. Researchers have taken advantage of these properties to investigate the mechanisms by which chemicals cause cancer of the skin and other organs. When applied to the skin of mice, several carcinogenic polyaromatic hydrocarbons have also been shown to interact with the immune system, stimulating immune responses and resulting in the development of antigen-specific T-cell-mediated immunity. Development of cell-mediated immunity is strain-specific and is governed by Ah receptor genes and by genes located within the major histocompatibility complex. CD8+ T cells are effector cells in the response, whereas CD4+ T cells down-regulate immunity. Development of an immune response appears to have a protective effect since strains of mice that develop a cell-mediated immune response to carcinogenic polyaromatic hydrocarbons are less likely to develop tumors when subjected to a polyaromatic hydrocarbon skin carcinogenesis protocol than mice that fail to develop an immune response. With respect to innate immunity, TLR4-deficient C3H/HeJ mice are more susceptible to polyaromatic hydrogen skin tumorigenesis than C3H/HeN mice in which TLR4 is normal. These findings support the hypothesis that immune responses, through their interactions with chemical carcinogens, play an active role in the prevention of chemical skin carcinogenesis during the earliest stages. Efforts to augment immune responses to the chemicals that cause tumors may be a productive approach to the prevention of tumors caused by these agents.     

Time course of the induction of aryl hydrocarbon hydroxylase in rat liver nuclei and microsomes by phenobarbital, 3-methylcholanthrene, 2,3,7,8-tetrachloro-dibenzo-p-dioxin,dieldrin and other inducers

Aryl hydrocarbon hydroxylase (AHH) has been measured in male rat liver nuclei and microsomes after treatment of adult animals with various inducers for up to 14 days. After daily i.p. injections of 3-methylcholanthrene (MC, 20 mg/kg) the nuclear activity increased to a maximum of 600 per cent of the control activity after 4 days whereas the microsomal activity was 400 per cent of control at the same date. After 12 days, both activities equilibrated at 400 per cent. A similar time course was found after a single i.p. injection of 2,3,7,8-tetrachloro-dibenzo-p-dioxin (TCDD, 0.01 mg/kg) with an induction to 500 and 300 per cent for nuclei and microsomes, respectively, after 2 days, and to 400 per cent for both after 12 days. Phenobarbital (PB) was given continuously in the drinking water (1 g/l) and induced the microsomal activity to 200 per cent after 8 days and 170 per cent after 14 days. the nuclear activity was only slightly induced to a Constant level of 130 per cent between day 8 and 14. Dieldrin did not significantly increase the microsomal activity after daily i.p. injections (20 mg/kg), but the nuclear activity raised to 200 per cent after 3 days and levelled down to control values after 12 days. Other inducers tested were benz[a]anthracene (BA), hexachlorobenzene (HCB) and 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane (DDT). The induction pattern with BA was similar to that of MC, a model compound for the group of cytochrome P448 inducers. the induction by HCB and DDT resembled that by PB, a typical cytochrome P450 inducer.     

Epigallocatechin-3-gallate does not affect the activity of enzymes involved in metabolic activation and cellular excretion of benzo[a]pyrene in human colon carcinoma cells

Benzo[a]pyrene (B[a]P) and related procarcinogens found in cigarette smoke and roasted foodstuff require metabolic activation to build mutagenic DNA adducts that may cause tumor diseases like colorectal cancer. The major B[a]P-activating enzymes belong to the cytochrome-P450 (CYP)-1 family and are regulated by the aryl hydrocarbon receptor (AhR). Previous studies have indicated that an inhibition of AhR is accompanied with a reduced metabolic activation of B[a]P and therefore may act protective against carcinogenesis. We investigated if the green tea flavonoid (−)-epigallocatechin-3-gallate (EGCG), a known AhR inhibitor, is able to influence B[a]P-metabolizing and B[a]P-transporting enzymes in human Caco-2 colon carcinoma cells. Strikingly, treatment with EGCG did neither affect constitutive and B[a]P-inducible expression of CYP1A1 and UDP-glucuronosyltransferase (UGT)-1A1 nor overall CYP1 and UGT enzyme activities, indicating that EGCG does not antagonize the AhR in Caco-2 cells. Since flavonoids were also identified to enhance the activity of B[a]P-carrying transporter, we analyzed if EGCG exposure alters cellular excretion of B[a]P conjugates. In contrast to the positive control fisetin, EGCG did not affect cellular excretion of B[a]P metabolites. Our data provide evidence that EGCG does not alter the metabolism and transport of B[a]P in Caco-2 cells, and thus may not protect against procarcinogenic food contaminants.     

An acellular assay to assess the genotoxicity of complex mixtures of organic pollutants bound on size segregated aerosol. Part I: DNA adducts

An acellular assay consisting of calf thymus DNA with/without rat liver microsomal S9 fraction was used to study the genotoxicity of complex mixtures of organic air pollutants bound to size segregated aerosols by means of DNA adduct analysis. We compared the genotoxicity of the organic extracts (EOMs) from three size fractions of aerosol ranging from 0.17 μm to 10 μm that were collected by high volume cascade impactors in four localities of the Czech Republic differing in the extent of the environmental pollution: (1) small village in proximity of a strip mine, (2) highway, (3) city center of Prague and (4) background station. The total DNA adduct levels induced by 100 μg/ml of EOMs were analyzed by ³²P-postlabelling analysis with a nuclease P1 method for adduct enrichment. The main finding of the study was most of the observed genotoxicity was connected with a fine particulate matter fraction (<1 μm). The concentrations of carcinogenic polycyclic aromatic hydrocarbons (c-PAHs) in EOMs indicate that fine fractions (0.5–1 μm) bound the highest amount of c-PAHs in all aerosol sampling sites, which might be related to the higher specific surface of this fraction as compared with a course fraction (1–10 μm) and higher mass as compared with a condensational fraction (0.17–0.5 μm). As for aerosol mass, both fine and condensational fractions are effective carriers of c-PAHs. Similarly, the DNA adduct levels per m³ of air were highest for the fine fraction, while the condensational fraction (strip mine site and city center) revealed the highest DNA adduct levels in cases where aerosol mass is taken into consideration. A strong correlation was found between the c-PAHs and DNA adduct levels induced by EOMs in all the localities and for various size fractions (R² = 0.98, p < 0.001). It may be concluded that the analysis of total DNA adducts induced in an acellular assay with/without metabolic activation represents a relatively simple method to assess the genotoxic potential of various complex mixtures.     

Genotoxic potential of organic extracts from particle emissions of diesel and rapeseed oil powered engines

The present study was performed to identify possible genotoxicity induced by organic extracts from particulate matter in the exhaust of two typical diesel engines run on diesel fuel and neat heated fuel-grade rapeseed oil: a Cummins ISBe4 engine tested using the World Harmonized Steady State Test Cycle (WHSC) and modified Engine Steady Cycle (ESC) and a Zetor 1505 engine tested using the Non-Road Steady State Cycle (NRSC). In addition, biodiesel B-100 (neat methylester of rapeseed oil) was tested in the Cummins engine run on the modified ESC. Diluted exhaust was sampled with high-volume samplers on Teflon coated filters. Filters were extracted with dichlormethane (DCM) and DNA adduct levels induced by extractable organic matter (EOM) in an acellular assay of calf thymus DNA coupled with (32)P-postlabeling in the presence and absence of rat liver microsomal S9 fraction were employed. Simultaneously, the chemical analysis of 12 priority PAHs in EOM, including 7 carcinogenic PAHs (c-PAHs) was performed. The results suggest that diesel emissions contain substantially more total PAHs than rapeseed oil emissions (for the ESC) or that these concentrations were comparable (for the WHSC and NRSC), while c-PAHs levels were comparable (for the ESC) or significantly higher (for the WHSC and NRSC) for rapeseed oil emissions. DNA adduct levels induced by diesel and rapeseed oil derived EOM were comparable, but consistently slightly higher for diesel than for rapeseed oil. Highly significant correlations were found between 12 priority PAHs concentrations and DNA adduct levels (0.980; p<0.001) and these correlations were even stronger for c-PAHs (0.990; p<0.001). Metabolic activation by the microsomal S9 fraction resulted in several fold higher genotoxicity, suggesting a major contribution of PAHs to genotoxicity. Directly acting compounds, other than c-PAHs, and not requiring S9 to exhibit DNA reactivity were also significant. Generally, DNA adduct levels were more dependent on the type of engine and the test cycle than on the fuel. Our findings suggest that the genotoxicity of particulate emissions from the combustion of rapeseed oil is significant and is comparable to that from the combustion of diesel fuel. A more detailed study is ongoing to verify and extent these preliminary findings.     

DNA adducts and oxidative DNA damage induced by organic extracts from PM2.5 in an acellular assay

The genotoxic activities of complex mixtures of organic extracts from the urban air particles collected in various localities of the Czech Republic, which differed in the extent and sources of air pollution, were compared. For this purpose, PM2.5 particles were collected by high volume samplers in the most polluted area of the Czech Republic - Ostrava region (localities Bartovice, Poruba and Karvina) and in the locality exhibiting a low level of air pollution - Trebon - a small town in the non-industrial region of Southern Bohemia. To prepare extractable organic matter (EOM), PM2.5 particles were extracted by dichloromethane and c-PAHs contents in the EOMs were determined. As markers of genotoxic potential, DNA adduct levels and oxidative DNA damage (8-oxo-7,8-dihydro-2′-deoxyguanosine, 8-oxodG, levels) induced by EOMs in an acellular assay of calf thymus DNA coupled with ³²P-postlabeling (DNA adducts) and ELISA (8-oxodG) in the presence and absence of microsomal S9 fraction were employed. Twofold higher DNA adduct levels (17.20 adducts/10⁸ nucleotides/m³ vs. 8.49 adducts/10⁸ nucleotides/m³) were induced by EOM from Ostrava-Bartovice (immediate proximity of heavy industry) compared with that from Ostrava-Poruba (mostly traffic emissions). Oxidative DNA damage induced by EOM from Ostrava-Bartovice was more than fourfold higher than damage induced by EOM from Trebon (8-oxodG/10⁸ dG/m³: 0.131 vs. 0.030 for Ostrava-Bartovice vs. Trebon, respectively). Since PM2.5 particles collected in various localities differ with respect to their c-PAHs content, and c-PAHs significantly contribute to genotoxicity (DNA adduct levels), we suggest that monitoring of PM2.5 levels is not a sufficient basis to assess genotoxicity of respirable aerosols. It seems likely that the industrial emissions prevailing in Ostrava-Bartovice represent a substantially higher genotoxic risk than mostly traffic-related emissions in Ostrava-Poruba. B[a]P and c-PAH contents in EOMs are the most important factors relating to their genotoxic potential.     

Polycyclic aromatic hydrocarbons stimulate human CYP3A4 promoter activity via PXR

Metabolic activation of polycyclic aromatic hydrocarbons (PAH) is mediated mainly by cytochrome P₄₅₀ monooxygenases (CYP) CYP1A1, 1A2 and 1B1. Several PAH are known to induce these CYP via aryl hydrocarbon receptor (AhR) signaling. Recently, it was shown that the PAH benzo[a]pyrene (BaP) can induce CYP3A4 as well. The induction was suggested to be mediated by the pregnane X receptor (PXR) rather than AhR. Metabolism by CYP3A4 is only known for dihydrodiol metabolites of PAH but not for their parent compounds.     

Comparison of DNA adduct induction in vitro by PAHs and nitro-pahs in freshly isolated rat hepatocytes

Polycyclic aromatic hydrocarbons (PAHs) and nitro-PAHs have been identified widely in occupational and environmental pollution, such as diesel engine emissions and other combustion products. In most cases, hepatic biotransformation is involved in converting these chemicals to their carcinogenic metabolites. It has been demonstrated that isolated hepatocytes possess substantial amounts of the enzymes responsible for metabolizing xenobiotics and are therefore a convenient model for studying chemicals that require activation to exert their carcinogenic effects. In this study, rat hepatocytes were isolated by collagenase digestion and then exposed to benzo[a]pyrene (B) [a]P), benzo[a]anthracene (B[a]A), 1-nitropyrene (1-NP) and 1,6-dinitropyrene (1,6-DNP) at different doses and/or times so that DNA adducts levels, as measured with the ³²P-postlabelling technique, could be compared. Each of the four compounds tested induced significant increases of total DNA adducts with clear dose-related responses. One or more individual adducts were identified as major adducts for each compound. Time-related increases of DNA adducts were also observed from 1 to 4 hr of incubation. Greater amounts of DNA adducts were induced by B[a]P or 1,6-DNP than by B[a]A or 1-NP, with potency being in the order 1,6-DNP > B[a]P > 1-NP B[a]A. These results demonstrate that freshly isolated hepatocytes can be used as an effective in vitro system for the detection of DNA adducts using ³²P-postlabelling, and have shown 1,6-DNP to be the most potent of the tested constituents of diesel emissions.     

Induction of CYP1A1 and CYP1B1 by benzo(k)fluoranthene and benzo(a)pyrene in T-47D human breast cancer cells: roles of PAH interactions and PAH metabolites

The interactions of polycyclic aromatic hydrocarbons (PAH) and cytochromes P450 (CYP) are complex; PAHs are enzyme inducers, substrates, and inhibitors. In T-47D breast cancer cells, exposure to 0.1 to 1 microM benzo(k)fluoranthene (BKF) induced CYP1A1/1B1-catalyzed 17beta-estradiol (E(2)) metabolism, whereas BKF levels greater than 1 muM inhibited E(2) metabolism. Time course studies showed that induction of CYP1-catalyzed E(2) metabolism persisted after the disappearance of BKF or co-exposed benzo(a)pyrene, suggesting that BKF metabolites retaining Ah receptor agonist activity were responsible for prolonged CYP1 induction. BKF metabolites were shown, through the use of ethoxyresorufin O-deethylase and CYP1A1-promoter-luciferase reporter assays to induce CYP1A1/1B1 in T-47D cells. Metabolites formed by oxidation at the C-2/C-3 region of BKF had potencies for CYP1 induction exceeding those of BKF, whereas C-8/C-9 oxidative metabolites were somewhat less potent than BKF. The activities of expressed human CYP1A1 and 1B1 with BKF as substrate were investigated by use of HPLC with fluorescence detection, and by GC/MS. The results showed that both enzymes efficiently catalyzed the formation of 3-, 8-, and 9-OHBKF from BKF. These studies indicate that the inductive effects of PAH metabolites as potent CYP1 inducers are likely to be additional important factors in PAH-CYP interactions that affect metabolism and bioactivation of other PAHs, ultimately modulating PAH toxicity and carcinogenicity.     

Induction of carbonyl reductase 1 (CBR1) expression in human lung tissues and lung cancer cells by the cigarette smoke constituent benzo[a]pyrene

Carbonyl reductase 1 (CBR1) reduces various xenobiotic carbonyl substrates to corresponding alcohol metabolites. Here we demonstrated that benzo[a]pyrene (B[a]P), a potent pro-carcinogen and predominant polycyclic aromatic hydrocarbon (PAH) compound in cigarette smoke and air pollutants, upregulates CBR1 gene expression in vitro and in vivo, and that a proximal xenobiotic response element (XRE) motif (₋₁₂₂XRE) mediates the induction effect of B[a]P. First, we observed 46% and 50% increases in CBR1 mRNA and CBR1 protein levels, respectively, in human lung tissue samples from smokers compared to never-smokers. Second, we detected 3.0-fold (p < 0.0001) induction of CBR1 mRNA and 1.5-fold (p < 0.01) induction of CBR1 protein levels in cells of the human lung cancer cell line A549 incubated with 2.5 μM B[a]P for 24 h. Third, results from experiments with CBR1 promoter constructs indicated that a proximal XRE motif (₋₁₂₂XRE) mediates induction of reporter activity in response to B[a]P. Furthermore, we detected enhanced nuclear translocation of aryl hydrocarbon receptor (AhR) following B[a]P exposure in A549 cells. Finally, we demonstrated increased binding of specific protein complexes to ₋₁₂₂XRE in nuclear extracts from B[a]P-treated cells and the presence of the AhR/Arnt complex in the specific nuclear protein ₋₁₂₂XRE complexes.     

Genotoxic activities of the food contaminant 5-hydroxymethylfurfural using different in vitro bioassays

5-Hydroxymethylfurfural (5-HMF) is known as an indicator of quality deterioration in a wide range of foods. 5-HMF is formed as an intermediate in the Maillard reaction and has been identified in a wide variety of heat-processed foods. In recent years, the presence of 5-HMF in foods has raised toxicological concerns: data have shown cytotoxic, genotoxic and tumoral effects but further studies suggest that 5-HMF does not pose a serious health risk. However the subject is still a matter of debate. We investigated the genotoxicity of the food-borne contaminant 5-HMF using the Ames test, the micronucleus (MN) and the single-cell gel electrophoresis (SCGE) assays in the human metabolically active HepG2 cell line. Cytotoxic effect of 5-HMF was first assessed using Alamar Blue™ as a sensitive sub-lethal assay. 5-HMF did not induce any genic mutation in bacteria whatever the concentration in the Ames test. Furthermore, it does not induce clastogenic or aneugenic effects in the HepG2 cells. In contrast, 5-HMF induced HepG2 DNA damage at concentrations from 7.87 to 25 mM in the comet assay suggesting a weak genotoxic effect of 5-HMF in the HepG2 cells probably repaired.     

Safety evaluation of chicken breast extract containing carnosine and anserine.

Chicken breast extract (CBEX) is obtained via hot water extraction of chicken breast and contains among its primary constituents carnosine and anserine, which are histidine-containing dipeptides present in the muscle tissues of most vertebrate species. Dietary intake of CBEX has been previously shown to buffer hydrogen ions formed during high-intensity exercise in human skeletal muscle cells, thereby inhibiting a decrease in muscle cell pH and subsequent muscle fatigue. The objective of this paper is to report the results of safety studies completed on CBEX. CBEX was determined to have an oral LD(50) value of more than 6000 mg/kg body weight in rats. Gavage doses of 500 or 2000 mg CBEX/kg body weight/day administered to rats for 90 days produced no toxicologically significant, dose-related, differences between control and treated animals with respect to body weight gain, food consumption, behavioral effects, hematological and clinical chemistry parameters, absolute and relative organ weights, or gross and microscopic findings. In the presence or absence of metabolic activation, CBEX exerted no mutagenic activity in the Ames assay conducted in various strains of Salmonella typhimurium and Escherichia coli. The results of these studies support the safety of CBEX as a potential dietary source of carnosine and anserine.