Mario Mazzullo

β-carotene as enhancer of cell transforming activity of powerful carcinogens and cigarette-smoke condensate on BALB /c 3T3 cells in vitro

We report the ability of beta-carotene (betaC) to affect the cell transforming activity of 3-methylcholanthrene (3-MCA), benzo(a)pyrene (B(a)P) and cigarette-smoke condensate (TAR) in an in vitro medium-term (approximately 8 weeks) experimental model utilizing BALB/c 3T3 cells. Different experimental schedules were performed either in the presence or absence of betaC: (i) cultures treated for 72 h with each chemical (acute treatment), (ii) cultures grown in presence of each chemical for the whole period of the experiment (chronic treatment). These procedures suggested a possible cocarcinogenic potential of the carotenoid following interactions with other chemicals mimicking continuous human exposition to several xenobiotics. Although the pigment did not show any cell transforming potential when tested alone either in acute or chronic treatment, it did augment that of other tested agents. Induction of cell transformation by B(a)P was markedly enhanced by the presence of this carotenoid in either acute or chronic treatment. Only in presence of betaC, was TAR able to significantly act as a cell transforming agent in prolonged, chronic treatment of cultures. Enhanced cell transformation activity could be due to the boosting effect of betaC on P450 apparatus. Indeed, elsewhere we have found that the latter increased the ratio of formation of diol epoxide carcinogenic metabolites of B(a)P as well as other carcinogens present in TAR. By contrast, no differences of cell transforming activity of 3-MCA, an ultimate carcinogen, were seen either in the presence or absence of betaC under the various experimental conditions. These data, which are in keeping with the cocarcinogenic potential of betaC, may help to explain the unexpected lung cancer increases obtained in chemoprevention trials in heavy smokers supplemented with the isoprenoid. Our findings also highlight the potential risk to humans derived from interactions among xenobiotics present in the environment.

In vivo and in vitro binding of benzene to nucleic acids and proteins of various rat and mouse organs.

Benzene binds to macromolecules of various organs in the rat and mouse in vivo. Labelling of RNA and proteins is higher (1 order of magnitude) than DNA labelling, which is low in many organs (liver, spleen, bone marrow and kidney), and negligible in lung; no difference between labelling of rat and mouse organs was found. The covalent binding index (CBI) value was about 10, i.e. typical of genotoxic carcinogens classified as weak initiators. In vitro binding of benzene to nucleic acids and proteins is mediated by hepatic microsomes, but not by microsomes from kidney, spleen and lung, or by cytosol from whatever organ. Nucleic acid binding can be induced by pretreatment with phenobarbitone (PB) and suppressed in the presence of SKF 525-A, of cytosol and/or GSH or of heat-inactivated microsomes. Labelling of exogenous DNA is low and is similar in the presence of rat or mouse microsomes in agreement with the low interaction with DNA measured in vivo.

In vivo and in vitro binding of 1,2-dibromoethane and 1,2-dichloroethane to macromolecules in rat and mouse organs

SummaryThe comparative interaction of equimolar amounts of 1,2-dichloroethane and 1,2-dibromoethane with rat and mouse nucleic acids was studied in both in vivo (liver, lung, kidney and stomach) and in vitro (liver microsomal and/or cytosolic fractions) systems. In vivo, liver and kidney DNA showed the highest labeling, whereas the binding to lung DNA was barely detectable. Dibromoethane was more highly reactive than dichloroethane in both species. With dichloroethane, mouse DNA labeling was higher than rat DNA labeling whatever the organ considered: the opposite was seen for the bioactivation of dibromoethane. RNA and protein labelings were higher than DNA labeling, with no particular pattern in terms of organ or species involvement. In vitro, in addition to a low chemical reactivity towards nucleic acids shown by haloethanes per se, both compounds were bioactivated by either liver microsomes and cytosolic fractions to reactive forms capable of binding to DNA and polynucleotides. UV irradiation did not photoactivate dibromoethane and dichloroethane. The in vitro interaction with DNA mediated by enzymatic fractions was PB-inducible (one order of magnitude, using rat microsomes). In vitro bioactivation of haloethanes was mainly performed by microsomes in the case of dichloroethane and by cytosolic fractions in the case of dibromoethane. When microsomes plus cytosol were used, rat enzymes were more efficient than mouse enzymes in inducing a dibromoethane-DNA interaction: the opposite situation occurred for dichloroethane-DNA interaction, and this is in agreement with the in vivo pattern. In the presence of both metabolic pathways, addition or synergism occurred. Dibromoethane was always more reactive than dichloroethane. An indication of the presence of a microsomal GSH transferase was achieved for the activation of dibromoethane. No preferential binding in vitro to a specific polynucleotide was found. Polynucleotide labeling was higher than (or equal to) DNA binding. The labeling of microsomal RNA and proteins and of cytosolic proteins was many times lower than that of DNA or polynucleotides. The in vivo and in vitro data reported above give an unequivocal indication of the relative reactivity of the haloethanes examined with liver macromolecules from the two species and agree, on the whole, with the relative genotoxicity (DNA repair induction ability, mutagenicity and carcinogenicity) of the chemicals.

In vivo unwinding fluorimetric assay as evidence of the damage induced by fenarimol and DNOC in rat liver DNA

Five pesticides [amitraz, cyanazine, cyhexatin, dinitro-o-cresol (DNOC), and fenarimol] were tested as pure active ingredients for in vivo induction of DNA strand breaks on rat hepatocytes after intraperitoneal (ip) treatment. Two pesticides, fenarimol and DNOC, were capable of inducing DNA damage because they significantly increased the DNA unwinding rate. On the contrary, amitraz, cyanazine, and cyhexatin were not DNA-damaging agents.

In vitro microsome- and cytosol-mediated binding of 1,2-dichloroethane and 1,2-dibromoethane with DNA

Metabolic activation of 1,2-dichloroethane (DCE) and 1,2-dibromoethane (DBE) to forms able to bind covalently with DNA occurs in vitroeither by wat of microsomal or cytosolic pathways. The involvement of these two pathways is variable with respect to species or compound tested. Rat enzymes are generally more efficient than mouse enzymes in bioactivating haloalkanes and DBE is more reactive than DCE. This parallels both the previous report on in vivocomparative interaction and the higher genotoxicity of DBE.

The different genotoxicity of P-dichlorobenzene in mouse and rat: Measurement of the in vivo and in vitro covalent interaction with nucleic acids

Twenty-two hours after i.p. injection to male Wistar rats and BALB/c mice para-dichlorobenzene (p-DCB) is bound covalently to DNA from liver, kidney, lung and stomach of mice but not of rats. DNA adducts in mouse liver are repaired in seventy-two hours. The covalent binding index value, calculated on the labelling of mouse liver DNA, classifies p-DCB as a weak initiator with an oncogenic activity lower than that of chlorobenzene. The labelling of RNA and proteins from the different organs of both species is, however, low. In vitro interaction with calf thymus DNA mediated by mouse and rat microsomes from liver and lung did occur. Binding extent was strongly reduced by addition of 2-diethylaminoethyl-2,2-diphenylvalerate hydrochloride (SKF 525-A) to the microsomal standard incubation mixture, whereas it was enhanced by adding GSH. Cytosolic fractions from kidney and lung were able to induce binding of p-DCB to DNA to a lower extent with respect to microsome-mediated binding. These results indicate that microsomal mixed function oxidase system and microsomal GSH-transferases can be involved in overall activating metabolism whereas cytosolic GSH-transferases play a minor role. This study, which is a part of a structure-activity relationship approach on benzene and its haloderivatives, provides the first evidence of genotoxicity of p-DCB in mammalian cell. It allows to partly explain variations of susceptibility of different species to hepatocarcinogenesis and of hepatotoxicity of different isomers.

In vivo and in vitro binding of epichlorohydrin to nucleic acids

Epichlorohydrin (EC) binds to macromolecules of biological relevance in vivo: DNA is less labelled than RNA and proteins, rat organs interact more than mouse organs, stomach is the most labelled organ with liver, kidney and lung involved in decreasing order. Based on the Covalent Binding Index (CBI), EC is a weak-moderate oncogen, just as other chlorinated hydrocarbons such as 1,2-dichloroethane and carbon tetrachloride. An interaction of EC with nucleic acids (DNA and polyribonucleotides) occurs also in vitro. It is mediated either by chemical reactivity per se of the molecule (near-UV (NUV) irradiation does not photoactivate EC) and by enzymatic (microsomal and/or cytosolic) fractions, whose relative effectiveness is variable in relation to the organ tested. The best substrates for interaction are poly(G) and poly(A) when using microsomal and cytosolic fractions, respectively, whereas the labelling of double-stranded DNA is always lower. On the whole, the picture of enzyme (microsome + cytosol)-mediated in vitro interaction is similar to the pattern of in vivo binding, with the exception of rat stomach enzymes which are inactive in vitro.

Inhibitory activity of vitamin E and α-naphthoflavone on β-carotene-enhanced transformation of BALB/c 3T3 cells by benzo(a)pyrene and cigarette-smoke condensate.

Abstract We previously found that β-carotene (βCT) can act as a co-carcinogenic agent enhancing the cell transforming activity of powerful carcinogens such as benzo(a)pyrene (B(a)P) and cigarette-smoke condensate (TAR) in an in vitro medium-term (∼8 weeks) experimental model utilizing BALB/c 3T3 cells (Mutat. Res. 440 (1999) 83–90). Here, we investigated whether vitamin E (VitE) and α-naphthoflavone (αNF) are able to affect the co-carcinogenic activity of βCT in terms of inhibiting B(a)P and TAR cell transforming potential. The following experimental schedules were performed: (i) cultures treated for 72 h with chemicals in various experimental combinations (acute treatment); (ii) cultures grown in presence of tester agents for the whole period of the assay (chronic treatment) to more closely mimic human exposure. While the co-carcinogenic potential of βCT was confirmed on both B(a)P and TAR, the latter being ineffective by itself, we found in repeated experiments that the presence of VitE or αNF significantly reduced the βCTs enhancing effect in the formation of transformation foci by B(a)P and TAR. The mechanism of the inhibition could be explained by the known ability of αNF to inhibit cytochrome P450-linked B(a)P-bioactivating monooxygenases, while VitE may contrast the prooxidant activity of βCT (e.g., oxygen radicals overgeneration). While highlighting the importance of increasing knowledge of the role of single provitamins, vitamins and micronutrients, our findings also underline the potential advantages of combining several dietary supplements in in vitro preventive investigations.

In vitro Transformation of BALB/c 3T3 Cells by 1,1,2,2-Tetrachloroethane

1,1,2,2‐Tetrachloroethane (1,1,2,2‐TTCE) was shown to be capable of inducing in vitro transformation of BALB/c 3T3 cells (clone A‐31) either in the presence or in the absence of S9 activating system using an amplification‐transformation (level‐II) assay by reseeding confluent cells from each treatment and allowing additional rounds of cell replication. In the absence of metabolic activation, the highest assayed dose (1000 μg/ml), exerting the highest toxicity, was the only transforming dose. Lower doses of 1,1,2,2‐TTCE were capable of transforming BALB/c cells in the presence of S9 activating system, the dose of 500 μg/ml exerting the highest transforming activity. The number and size of transformed foci recognized in the level‐II plates were a function of the number of cells reseeded in the amplification assay. Foci obtained in the presence of S9 activating systems were larger in size, more deeply basophilic, and exhibited denser multilayering of constituent cells than foci recognized in the absence of exogenous metabolic activation.

Molecular non-genetic biomarkers of effect related to methyl thiophanate cocarcinogenesis: organ- and sex-specific cytochrome P450 induction in the rat

We used selective biochemical markers of effect to evaluate some non-genotoxic cocarcinogenic properties of methyl thiophanate (MTH) associated with cytochrome P450 (CYP) changes. Several CYP-dependent reactions were monitored in the liver, kidney and lung microsomes of male and female Sprague-Dawley rats treated (i.p.) with a single (285 or 570 mg/kg body weight) or repeated (daily 285 or 570 mg/kg body weight for three consecutive days) doses of this pesticide. No significant changes in absolute or relative liver, kidney and lung weights were observed after MTH injection. Highly specific substrates were used as probes of different isoforms, such as CYP1A1, 1A2, 2B1, 2E1 and 3A. A complex pattern of CYP induction, including organ- and sex-related differences, was observed, particularly in the liver (CYP3A, 2B1), kidney (CYP1A1, 2E1) and lung (CYP3A, 1A1). In the liver, an increase up to 29-fold in the 2B1-like activity, probed by the O-dealkylation of pentoxyresorufin, was observed at lower dose in both sexes, and the induction of CYP 1A2-mediated methoxyresorufin O-demethylase activity (up to 3.6-fold) was recorded at the higher dose in males. In the kidney, the O-deethylation of ethoxyresorufin (CYP1A1-linked) was increased up to 28.2-fold and the CYP2E1-dependent p-nitrophenol hydroxylases were enhanced up to 6.3-fold in females receiving higher multiple MTH administration. In the lung, the CYP3A-associated activity was the most induced oxidases, as exemplified by the marked increase in the O-demethylation of aminopyrine (up to 3.6-fold) in males. A weak, although significant, reduction of CYP2B1-linked oxidases was also observed in repeated treatment in the kidney (males) and lung (females). These results suggest that the induction of CYP-catalyzed drug metabolism by prolonged exposure to MTH may result in accelerated metabolism of coadministered drugs with important implications for their disposition Together with an alteration of endogenous metabolism, the adverse effects associated with CYP changes such as toxicity/cotoxicity, cocarcinogenicity and promotion may also have clinical consequences.