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Biomedical subjects

S Grilli

Publications and source records attributed to S Grilli.

At least 37 records · Page 2Linked to original sources

Cytotoxic and cell transforming effects of the insecticide, lindane (gamma-hexachlorocyclohexane) on BALB/c 3T3 cells.

Further information was gathered on the possible carcinogenic hazard associated to the exposure to the insecticide lindane (gamma-hexachlorocyclohexane). The parameters studied were the cytotoxic and cell transforming activities of the pesticide on BALB/c 3T3 cells in an in vitro experimental model system in the absence or in the presence of rat liver S-9 mix-induced metabolic activation of the chemical. Lindane did not exert cytotoxic effects at all the tested doses (ranging from 10 micrograms/ml to 200 micrograms/ml) in the absence of bioactivation. However, dose-related cytotoxic effects were observed in the presence of the metabolizing system. Furthermore, lindane showed statistically significant and dose-dependent cell transformation activity at all the tested doses (10 micrograms/ml, 50 micrograms/ml and 100 micrograms/ml ) either in the absence or in the presence of bioactivation. This activity was related with cell proliferation since it was exerted in a level-II transformation test by replating cells and allowing the amplification of the cell transforming effects of the chemical. The formation of radicals and of reactive oxygen species, resulting from the chemical metabolism, could account for lindane activity as carcinogenesis promoting agent, although contemporary genotoxic effects induced by the pesticide could not be excluded.

3T3 Cells↗

Genetic safety evaluation of pesticides in different short-term tests.

Cyanazine, cyhexatin, dicamba and DNOC are pesticides commonly and broadly used in agriculture pest control. However, there is little information on their toxicity and mutagenicity in human cells and in whole animals. Therefore, UDS assay and SCE assay in human peripheral lymphocytes, and chromosome aberration analysis in bone marrow of rats have been used to assess the DNA-damaging activity of the above pesticides. Cyanazine proved non-genotoxic in all the test systems. Cyhexatin showed only weakly positive results for SCE induction in human lymphocytes, providing no concern for genotoxicological hazard. While dicamba did not show clastogenic effects in rodents, DNOC gave significant dose-related increases of structural chromosome aberrations in rat bone marrow cells. Female animals showed increased sensitivity to the toxic effects by DNOC at the highest dose. The results provide further information on the intrinsic genotoxic activity of the tested pesticides, which may contribute to the toxicological assessment of the risk associated with human exposure.

Animals↗

In vitro cytotoxic and cell transforming activities exerted by the pesticides cyanazine, dithianon, diflubenzuron, procymidone, and vinclozolin on BALB/c 3T3 cells.

Cytotoxic and cell transforming activities of the pesticides cyanazine, diflubenzuron, dithianon, procymidone, and vinclozolin were investigated in vitro by utilizing the BALB/c 3T3 cell transformation test performed in the presence or in the absence of S-9 mix as an exogenous bioactivation system for the chemicals. All the assayed pesticides were cytotoxic in the absence of S-9 mix, whereas only dithianon exerted cytotoxic effects in the presence of metabolic activation. All the chemicals tested did induce BALB/c 3T3 cell transformation, to a various extent, in the absence of S-9 mix. Cell transforming ability of cyanazine and diflubenzuron was not detectable in the presence of S-9.

3T3 Cells↗

Induction of chemotactic and invasive phenotype in BALB/c 3T3 cells by 1,2-dibromoethane transformation.

1,2-Dibromoethane (DBE), which can act as initiating agent, is capable of inducing a malignant phenotype in BALB/c 3T3 cells. Cells transformed with a single noncytotoxic dose formed more progressive tumors in vivo. Almost all animals (95%) receiving the inoculum of two different transformed clones developed tumors within 1 month. In the control group only 55% of the animals developed tumors after 4 months. Treatment with DBE also increased the chemotactic properties of target cells, which also acquired ability to penetrate and colonize a reconstituted basal membrane (matrigel). These data suggest that DBE could play a key role in tumor progression.

3T3 Cells↗

In vitro cell transformation induced by the pesticide fenarimol.

The pesticide fenarimol is capable of transforming BALB/c 3T3 cells in an in vitro model system, and its action resembles a carcinogenic process in vivo. In the absence of metabolic activation, transformed foci are already visible in the standard experimental procedure. The addition of the S9 fraction as an exogenous metabolic system leads to a decrement of cytotoxic effects and the reduction of the transformation rate. The transformed phenotype, however, becomes visible when confluent cells are replated and allowed further cell replication. Transformation effects by fenarimol may be due to both a weak genotoxic activity and/or stronger promoting activity.

Animals↗

Initiating activity of 1,1,2,2-tetrachloroethane in two-stage BALB/c 3T3 cell transformation.

By using in vitro two-stage BALB/c 3T3 cell transformation assay, we have tested the effect of promoting treatment with tetradecanoylphorbol acetate (TPA) on transformation induced by 1,1,2,2-tetrachloroethane (1,1,2,2-TTCE). Cells were treated with subeffective or transforming concentrations of 1,1,2,2-TTCE in the presence of an S9-mix activating system, followed by TPA promoting treatment. The transforming activity of 1,1,2,2-TTCE is evident only by reseeding confluent cells and allowing additional rounds of cell replications in the amplification test. Treatment with TPA leads to a marked transformation yield in all plates scored even at the lowest assayed dosage of 1,1,2,2-TTCE, without performing amplification of transformation.

3T3 Cells↗

Strategies for advancement of short-term mutagenicity tests: on the optimal ionic strength for the liver microsomal assay.

The aim of this work was to optimize the ionic strength (tau) in the liver microsomal assay (LMA) in performing short-term genotoxicity tests. tau optimization would increase the sensitivity (i.e. decrease false negatives) and at the same time increase the specificity (decrease false positives). Such optimization depends upon the relative activities and stabilities of the liver polysubstrate cytochrome P450- and FAD-containing monooxygenase-dependent metabolizing enzymes present in the incubation mixtures. With regard to phase-I pathway, the expression of various P450-like activities (IA1, IA2, IIB1, IIE1, IIIA P450 classes) and thiobenzamide s-oxidase (as FAD-MFO marker), were examined in terms of their exact incubation conditions for the LMA during a period of preincubation (1 h) over the tau range 0.06-1.40. As a comparison with the phase-II pathway, the behaviour of glutathione S-transferases (total and pi class), glutathione S-epoxide transferase, epoxide hydrolase and UDP-glucuronosyl transferase were studied. Lipid peroxidation (LP) was also determined. Experiments were performed on S9 fractions derived from sodium phenobarbital, beta-naphthoflavone, isosafrol, ethanol and pregnenolone 16-alpha carbonitrile super-induced mouse liver. The maximal value of the mean specific activity (Asp), up to a 46% increase, was found at tau = 0.864 for oxidative reactions considered. On the contrary, a slight modulation of Asp for post-oxidative reactions was seen. LP was not changed appreciably by varying tau. In vitro DNA binding of the well-known premutagenic agent [14C]dimethylnitrosamine ([14C]DMNA), mediated by mouse hepatic microsomal enzymes, showed a significant increase of specific activity at tau = 0.864 (2.25-fold) compared to the usual tau (0.06) used. Additional confirmation of these results stems from mutagenesis experiments using DMNA on the diploid D7 strain of Saccharomyces cerevisiae as a biological test system. Indeed, a significant enhancement of mitotic gene conversion (up to 1.8-fold), mitotic crossing-over (2.6-fold) and reverse point mutation (2.6-fold) frequencies was achieved at tau = 0.86 compared to tau = 0.06 (traditional). These data show that tau = 0.86 can provide more convenient conditions for in vitro bioactivation (as exemplified by an increased Asp phase-I/Asp phase-II ratio), as well as DNA binding and genotoxic response.

Animals↗

In vivo and in vitro interaction of trichloroethylene with macromolecules from various organs of rat and mouse.

Trichloroethylene was covalently bound in vivo to DNA, RNA and proteins of rat and mouse organs 22 hr after ip injection. The covalent binding index values of rat and mouse liver DNA classify trichloroethylene as a weak initiator. Labeling of RNA and proteins from various organs of both species was higher than that of DNA. In vitro, trichloroethylene was bioactivated by microsomal fractions dependent on cytochrome P450, mainly from liver of both species, to intermediate(s) capable of binding to exogenous DNA. No particular species-specific difference was evident except for mouse lung microsomes which were more efficient than rat lung microsomes. GSH-transferases capable of bioactivating P450-dependent were present in mouse lung microsomes and in liver microsomes of both species. These data, along those previously reported, provide sufficient evidence for a weak ability of TCY to interact covalently with DNA.

Animals↗

Induction of invasive and experimental metastasis potential in BALB/c 3T3 cells by benzo(a)pyrene transformation.

A clone of BALB/c 3T3 cells (A-31), which is highly resistant to spontaneous in vitro transformation, was treated with the carcinogen benzo(a)pyrene [B(a)P]. This agent was capable of inducing in vitro transformation in the presence of S9 activating system and 6 weeks after treatment large foci were detected. Transformation frequency in solvent control groups was very low. Three foci from a single plate of two different experiments were pooled and the cells tested for their in vitro invasive properties and in vivo tumorigenic and metastatic potential. B(a)P-transformed 3T3 cells grew in soft agar and were highly tumorigenic when injected s.c. in nude mice (75% incidence within 7 weeks). Untreated cells were poorly tumorigenic (0/4 mice had tumors within 7 weeks), though they also gave rise to neoplasms after a longer latency. Spontaneous metastasis incidence was low for both controls and treated cells; however, almost all animals (15/16) injected i.v. with B(a)P-transformed cells had pulmonary nodules in the experimental metastasis assay. A few nodules in some of the animals in the control group were detected (4/16). B(a)P-transformed cells were able to invade a thin coating of matrigel in the chemoinvasion assay and also grew in matrigel showing an invasive, branching morphology. Untreated cells did not grow or invade. Our data suggest that a single treatment with a chemical carcinogen can increase tumorigenicity as well as confer invasive and experimental metastasis potential in BALB/c 3T3 cells. This work provides evidence for a role of chemical carcinogens in tumor progression.

3T3 Cells↗

Chloroform bioactivation leading to nucleic acids binding.

Chloroform was bound covalently to DNA, RNA and proteins of rat and mouse organs in vivo after i.p. injection. Covalent Binding Index values of rat and mouse liver DNA classify chloroform as a weak initiator. Labelings of RNA and proteins from various organs of both species were higher than that of DNA. In an in vitro cell-free system, chloroform was bioactivated by cytochrome P450-dependent microsomal fractions, by cytosolic GSH-transferases from rat and mouse liver, and particularly by the latter enzymes from mouse lung. This observation suggests that GSH plays a role in the binding of chloroform metabolites to DNA. The presence of both microsomal and cytosolic enzymatic systems in the standard incubation mixture generally led to an additive or synergistic bioactivating effect for rat and mouse, respectively.

Animals↗

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.

Animals↗

DNA damaging activity of methyl parathion.

14C-methyl parathion was covalently bound to DNA, RNA and proteins of various rat and mouse organs 22 hr after i.p. injection. Covalent binding index (CBI) to liver DNA was low in both species and typical of weak initiators. The labelings of RNA and proteins from different organs of both species was slightly higher than DNA binding. No interaction with brain nucleic acids was observed (CBI detection limit: 2.8). The in vitro enzyme-mediated interaction of methyl parathion with calf thymus DNA was mainly performed by rodent liver microsomes and, to a lesser extent, by microsomes from mouse kidney and lung whereas brain microsomes were inefficient. Activation of methyl parathion by cytosolic fractions from different organs of both species to form(s) capable of binding to DNA was negligible. When microsomes and cytosolic fractions from rodent liver and lung or mouse kidney were simultaneously present in the incubation mixture, a synergistic effect in catalyzing DNA binding was observed. The extent of DNA binding was reduced by adding SKF 525-A to the microsomal standard incubation mixture, whereas it was enhanced by adding GSH to liver or lung murine microsomes or to mouse kidney microsomes. These results suggest that methyl parathion is bioactivated by P450-dependent microsomal mixed function oxidase system and by microsomal GSH-transferases. By contrast, cytosolic GSH- transferases play a detoxificant role in the metabolism of this compound.

Animals↗

Transforming activity of ethylene dibromide in BALB/c 3T3 cells.

Ethylene dibromide was capable of inducing in vitro transformation of BALB/c 3T3 cells either in the presence or in the absence of exogenous metabolic activation (S9-mix). This transforming effect was evidenced by the induction of a higher number of transformed foci as compared to the controls performed with untreated cells or solvent vehicle-treated cells. In the absence of exogenous activation, all assayed doses (ranging from 23.4 micrograms/ml to 187.9 micrograms/ml) exerted transforming activity. Number of foci obtained in EDB-treated plates antransformation frequency of the target cells were higher than those detected in the transformation test performed in the presence of S9-mix.

3T3 Cells↗

Lack of correlation between alkaline DNA fragmentation and DNA covalent binding induced by polychloroethanes after in vivo administration. Problems related to the assessment of a carcinogenic hazard.

The DNA-damaging activity of polychloroethanes was tested in mouse liver by the fluorometric assay of DNA unwinding. With the exception of 1,2-dichloroethane, all components of this chemical class had negative results. The failure of the parameter alkaline "DNA fragmentation" to detect the DNA-damaging activity of polychloroethanes is in sharp contrast with the measurement of DNA covalent binding, another short-term parameter of genotoxicity. Since covalent DNA adducts appear to be quantitatively well correlated with the oncogenic potencies of chloroethanes in liver, the negative results obtained with the present method can perhaps be explained in terms of quality of DNA adducts; these may be incapable of producing DNA breaks or alkali-labile sites detectable as alkaline DNA fragmentation. It is however worth noting that carcinogenicity of chloroethanes appears to depend not only on DNA damaging capability, but also on promoting activity during the carcinogenic process.

Alkalies↗

In vivo and in vitro interaction of 1,2-dichlorobenzene with nucleic acids and proteins of mice and rats.

Twenty-two hours after i.p. injection into male Wistar rats and BALB/c mice, 1,2-dichlorobenzene (1,2-DCB) was covalently bound to DNA, RNA, and proteins of liver, kidney, lung and stomach. The covalent binding index to liver DNA was typical of carcinogens classified as weak initiators. The enzyme-mediated in vitro interaction of 1,2-DCB with calf thymus DNA of synthetic polyribonucleotides was carried out by a microsomal mixed-function oxidase system and microsomal GSH-transferases, which seemed to be effective only in liver and lung of rat and mouse. Cytosolic GSH-transferases played a minor role in 1,2-DCB bioactivation. The latter finding provides the first evidence of 1,2-DCB genotoxicity in mammalian cells. The type of halide, the number of halosubstituents and their spatial disposition on the benzene ring are the major determinants of halobenzenes activability to intermediate(s) capable of interacting covalently with DNA and other macromolecules in biologic systems.

Animals↗

Evaluation of genotoxic effects of the herbicide dicamba using in vivo and in vitro test systems.

The genotoxic effects of the herbicide dicamba have been studied by measuring 1) the unwinding rate of liver DNA from intraperitoneally (i.p.) treated rats (fluorimetric assay); 2) DNA repair as unscheduled DNA synthesis (UDS) induced in cultured human peripheral blood lymphocytes (HPBL); and 3) sister chromatid exchanges (SCE) in HPBL. Results show that dicamba is capable of inducing DNA damage since it significantly increases the unwinding rate of rat liver DNA in vivo and also induces UDS in HPBL in vitro in the presence of exogenous metabolic activation (S-9 mix). Furthermore, dicamba causes a very slight increase in SCE frequency in HPBL in vitro.

Animals↗

Mutagenic and carcinogenic potency indices and their correlation.

We have analyzed a significant number of studies existing in the literature, in which the ability of different short-term tests for predicting carcinogenicity in rodents was investigated. We have separated these studies into two groups. In the better known group of studies, qualitative predictivity was investigated (sensitivity and specificity). In the second group of studies (analyzed in greater detail), positive results were examined for the correlation between carcinogenic potency and potency of response in a given short-term test. There is substantial agreement between qualitative and quantitative predictivity; both appear to be situated between a low and moderate level. We have analyzed the interesting possibility of using the quantitative approach not only for positive data but for combined positive and negative data as well. We have stressed that short-term tests of genotoxicity should be asked to predict only initiation and irreversible alterations in the genome and not to predict a combination of these events, including promotion and modulation of differentiation. Even with regard to only initiation, genotoxicity data should be related to comparative metabolism, as well as to considerations of the significance of different end points and structure-activity relationship data. In conclusion, the information coming from short-term tests of genotoxicity is probably useful but should be used in conjunction with other types of information and only for predicting one particular class of events in the entire process of carcinogenesis.

Carcinogenicity Tests↗