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Biomedical subjects

B Bonora

Publications and source records attributed to B Bonora.

At least 19 recordsLinked to original sources

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

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

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

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

The covalent interaction of 1,4-dibromobenzene with rat and mouse nucleic acids: in vivo and in vitro studies.

1,4-Dibromobenzene (1,4-DBB) was covalently bound to DNA from liver, kidney, lung and stomach of mice after intraperitoneal administration. The covalent binding index (CBI) value (23 in mouse liver) was typical of weak initiators. On the contrary, no interaction with DNA from rat organs was observed (CBI detection limit: 1.3-2.6). The in vitro interaction of 1,4-DBB with calf thymus DNA was mediated mainly by microsomes, especially those from liver of both species and from mouse lung. Mouse subcellular fractions were more active then rat subcellular fractions. Unlike liver cytosol, subcellular cytosolic fractions from lung, kidney and stomach were capable of bioactivating 1,4-DBB, although to a lesser extent than liver microsomes. Both cytochrome P-450 and GSH-transferases are involved in 1,4-DBB bioactivation.

Animals

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.

Animals

Covalent binding of 1,1,1,2-tetrachloroethane to nucleic acids as evidence of genotoxic activity.

Twenty-two hours after ip administration to male Wistar rats and BALB/c mice, 1,1,1,2-tetrachloroethane (1,1,1,2-TTCE) is bound covalently to DNA, RNA, and proteins of liver, lung, kidney, and stomach. The in vivo reactivity leads to binding values to DNA generally higher in mouse organs than in rat organs. The covalent binding index (CBI) values (82 in mouse liver DNA and 40 in rat liver DNA) classify 1,1,1,2-TTCE as a weak to moderate initiator. Both microsomal and cytosolic enzymatic systems from rat and mouse organs are capable of bioactivating 1,1,1,2-TTCE in vitro. Liver fractions are the most effective. When the activating systems are simultaneously present in the incubation mixture a synergistic effect is observed. Unlike the related chemical 1,1,2,2-tetrachloroethane (1,1,2,2-TTCE), which is bioactivated only through an oxidative route, 1,1,1,2-TTCE metabolism is carried on by oxidative and reductive pathways, both dependent on cytochrome P-450. 1,1,1,2-TTCE is also bioactivated by microsomal GSH-transferases from liver and lung. These data further confirm that correlations exist between structure and genotoxic activity of halocompounds.

Animals

Benzene adducts with rat nucleic acids and proteins: dose-response relationship after treatment in vivo.

The dose-response relationship of the benzene covalent interaction with biological macromolecules from rat organs was studied. The administered dose range was 3.6 x 10(7) starting from the highest dosage employed, 486 mg/kg, which is oncogenic for rodents, and included low and very low dosages. The present study was initially performed with tritium-labeled benzene, administered by IP injection. In order to exclude the possibility that part of the detected radioactivity was due to tritium incorporated into DNA from metabolic processes, 14C-benzene was then also used following a similar experimental design. By HPLC analysis, a single adduct from benzene-treated DNA was detected; adduct identification will be attempted in the near future. Linear dose-response relationship was observed within most of the range of explored doses. Linearity was particularly evident within low and very low dosages. Saturation of benzene metabolism did occur at the highest dosages for most of the assayed macromolecules and organs, especially in rat liver. This finding could be considered as indicative of the dose-response relationship of tumor induction and could be used in risk assessment.

Animals

Metabolic activation and covalent binding to nucleic acids of pentachloroethane as short-term test of genotoxicity.

The in vivo covalent binding of 14C-pentachloroethane to DNA, RNA and proteins of rats and mouse organs was detected 22 hr after i.p. injection. The covalent binding index, calculated on the liver labeling was comparable to those of compounds considered as weak-moderate initiators. Like other haloalkanes, 14C-pentachloroethane was bioactivated in in vitro cell-free system by both microsomal and cytosolic enzymatic fractions from mouse and rat organs to react covalently with DNA and other macromolecules. The binding extents obtained from in vitro incubation and the binding values detected after in vivo administration of labeled pentachloroethane were comparable each other and showed a high correlation with oncogenic potency index of this compound. This result confirms the efficiency of in vitro binding as short-term test of genotoxicity prediction.

Animals

[Cytogenetics in bone marrow transplantations. I. Bone marrow aplasia].

A bone marrow transplantation has been carried out in a patient with bone marrow aplasia. Besides the cytochemical and haematological tests, the cytogenetic analysis has been performed to check whether the transplantation was successful. In this case the donor was the patient's sister, so that the presence of the chimere has been used as a criteria for judging the conditions of the transplantation. the cytogenetic analysis, furthermore, is suitable to detect other chromosome abnormalities, which can represent a condition of instability of the transplanted cells and are probably an early expression of the transplanted bone marrow.

Adolescent

Interactions among DNA, metallic ions, and lipids.

Interactions amond DNA, phospholipids, and Cu2+ ions have been investigated by means of thermal denaturation technique. The results indicate that phosphatidylserine and sphingomyelin interact with Cu2+ ions, which are able to prevent the chance of binding of the phospholipids to the double helix. This interaction is strictly dependent upon the concentration of the divalent cation and reduces the capability of the employed phospholipids to modify the thermal stability of DNA.

Chemical Phenomena

[Karyologic analysis in erythroleukemia].

We report the cytogenetic data of two patients with erythroleukemia showing the chromosome Ph'. In one case the chromosome Ph', as revealed with the GTG band technique was the result of a translocation involving the chromosomes 19 and 22. The aim of this work is to provide more contribution to the knowledge of the origin of the Ph' and to give data in the field of this disease for which few cytogenetic data are available after the introduction of the banding techniques.

Aged

Lipid-F1 nucleohistone interactions.

High concentrations of phospholipids determine destabilization of F1 histone-DNA complex at the weight ratios, histone:DNA, 0.8:1 and 1:1, but low concentrations cause only negligible destabilization. Cholesterol at high weight ratios has little effect on nucleohistone stability. Only linolenic acid of the fatty acids used reproduces similar changes in the thermal stability of F1 histone-DNA complex as phospholipids. The type of interaction of phospholipids with the F1 histone-DNA complex is analyzed, and the involvement of phospholipids in DNA replication in vivo is discussed.

Binding Sites