The molecular basis for scent discrimination: response to nitrobenzene-d 5 of honey bees (Apismellifera L.) conditioned with nitrobenzene.
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Animals↗
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Odor and molecular vibration: response to nitrobenzene-d5 of honey bees (Apis mellifera L.) conditioned with nitrobenzene.
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Animals↗
Macromolecular covalent binding of [14C]nitrobenzene in the erythrocyte and spleen of rats and mice.
Nitrobenzene exposure is known to produce red blood cell damage as well as engorgement and sinusoidal congestion of the spleen in male Fischer-344 (F-344) rats but not in male B6C3F1 mice. These studies were conducted to investigate the species differences in the covalent binding of [14C]nitrobenzene in the erythrocyte and spleen and to assess the contribution of nitrobenzene-induced erythrocytic damage to the splenic effects. Total and covalently bound 14C concentrations in erythrocytes of rats were 6-13 times greater than those of mice following a single oral dose of 75, 150, 200 or 300 mg/kg [14C]nitrobenzene, suggesting that species differences in nitrobenzene-induced red blood cell toxicity may be related to differences in erythrocytic accumulation of nitrobenzene and its metabolites. Covalently bound 14C in erythrocytes of rats peaked 24 h following administration of 200 mg [14C]nitrobenzene/kg; in contrast, bound radiolabel in erythrocytes from mice plateaued at 10 h. Splenic engorgement increased in a time-related manner in treated rats but not in mice. Species specificity was also observed in the accumulation of bound radiolabel in the spleen. Gel filtration and sodium dodecyl sulfate-polyacrylamide gel electrophoresis (SDS-PAGE) of lysed, dialyzed erythrocytes from treated rats revealed that hemoglobin was the primary, if not the exclusive, site of macromolecular covalent binding following nitrobenzene treatment. SDS-PAGE of dialyzed rat spleens revealed that 82% of total bound 14C migrated identically to hemoglobin. These data indicate that covalent binding of [14C]nitrobenzene and its metabolites in the spleen is primarily derived from bound 14C from scavenged erythrocytes. Therefore, the species differences in splenic engorgement and accumulation of [14C]nitrobenzene may be related to differences in susceptibility to nitrobenzene-induced red blood cell damage.
Animals↗
Influence of dietary pectin on intestinal microfloral metabolism and toxicity of nitrobenzene.
Intestinal microfloral metabolism of nitrobenzene is essential for the production of methemoglobin. Since dietary pectin alters intestinal microflora, these studies were designed to examine the effects of dietary pectin on nitrobenzene-induced methemoglobinemia. Male Fischer-344 rats were fed either AIN-76A (purified diet containing 5% cellulose), AIN-76A with 5% pectin replacing the cellulose, or NIH-07 (cereal-based diet containing 8.4% pectin) for 28 days. Following this period, nitrobenzene (200 mg/kg) was administered by gastric intubation, and methemoglobin concentrations were determined after 1, 2, 4, 8, and 24 hr. Nitrobenzene-induced methemoglobinemia was evident as early as 1 hr, peaked at 4 hr, and diminished thereafter in rats fed NIH-07 diet. In contrast, nitrobenzene-induced methemoglobinemia was not detectable in rats fed AIN-76A; however, inclusion of 5% pectin in this diet resulted in methemoglobinemia comparable to that of NIH-07-fed animals at 4, 8, and 24 hr. Administration of 400 or 600 mg/kg nitrobenzene resulted in significant diet-related differences in methemoglobinemia. Administration of 600 mg/kg nitrobenzene to animals fed NIH-07 resulted in the highest methemoglobin concentrations (64 +/- 1%); those fed AIN-76A had the lowest (20 +/- 5%), and those fed AIN-76A containing pectin had intermediate methemoglobin concentrations (44 +/- 6%). No diet-related differences in the microbial population of the stomach or small intestine were observed. However, the number of anaerobes present in the ceca of rats fed AIN-76A containing pectin was 2 to 2.5 times greater than that of rats fed AIN-76A. In vitro reductive metabolism of [14C]nitrobenzene was significantly greater in the cecal contents of rats fed NIH-07 than that in the cecal contents of either of the groups fed the AIN-76A-based diets. These studies indicate that intestinal microfloral metabolism and red blood cell toxicity of nitrobenzene is markedly different in animals fed cereal-based versus purified diets. Furthermore, since inclusion of pectin into the purified diet diminishes the magnitude of these effects, differences in dietary composition of fermentable carbohydrates in cereal-based and purified diets may mediate differences in metabolism and toxicity of nitrobenzene.
Animals↗
Biotransformation of nitrobenzene by bacteria containing toluene degradative pathways.
Nonpolar nitroaromatic compounds have been considered resistant to attack by oxygenases because of the electron withdrawing properties of the nitro group. We have investigated the ability of seven bacterial strains containing toluene degradative pathways to oxidize nitrobenzene. Cultures were induced with toluene vapor prior to incubation with nitrobenzene, and products were identified by high-performance liquid chromatography and gas chromatography-mass spectrometry. Pseudomonas cepacia G4 and a strain of Pseudomonas harboring the TOL plasmid (pTN2) did not transform nitrobenzene. Cells of Pseudomonas putida F1 and Pseudomonas sp. strain JS150 converted nitrobenzene to 3-nitrocatechol. Transformation of nitrobenzene in the presence of 18O2 indicated that the reaction in JS150 involved the incorporation of both atoms of oxygen in the 3-nitrocatechol, which suggests a dioxygenase mechanism. P. putida 39/D, a mutant strain of P. putida F1, converted nitrobenzene to a compound tentatively identified as cis-1,2-dihydroxy-3-nitrocyclohexa-3,5-diene. This compound was rapidly converted to 3-nitrocatechol by cells of strain JS150. Cultures of Pseudomonas mendocina KR-1 converted nitrobenzene to a mixture of 3- and 4-nitrophenol (10 and 63%, respectively). Pseudomonas pickettii PKO1 converted nitrobenzene to 3- and 4-nitrocatechol via 3- and 4-nitrophenol. The nitrocatechols were slowly degraded to unidentified metabolites. Nitrobenzene did not serve as an inducer for the enzymes that catalyzed its oxidation. These results indicate that the nitrobenzene ring is subject to initial attack by both mono- and dioxygenase enzymes.
Biodegradation, Environmental↗
Degradation of nitrobenzene by a Pseudomonas pseudoalcaligenes.
A Pseudomonas pseudoalcaligenes able to use nitrobenzene as the sole source of carbon, nitrogen, and energy was isolated from soil and groundwater contaminated with nitrobenzene. The range of aromatic substrates able to support growth was limited to nitrobenzene, hydroxylaminobenzene, and 2-aminophenol. Washed suspensions of nitrobenzene-grown cells removed nitrobenzene from culture fluids with the concomitant release of ammonia. Nitrobenzene, nitrosobenzene, hydroxylaminobenzene, and 2-aminophenol stimulated oxygen uptake in resting cells and in extracts of nitrobenzene-grown cells. Under aerobic and anaerobic conditions, crude extracts converted nitrobenzene to 2-aminophenol with oxidation of 2 mol of NADPH. Ring cleavage, which required ferrous iron, produced a transient yellow product with a maximum A380. In the presence of NAD, the product disappeared and NADH was produced. In the absence of NAD, the ring fission product was spontaneously converted to picolinic acid, which was not further metabolized. These results indicate that the catabolic pathway involves the reduction of nitrobenzene to nitrosobenzene and then to hydroxylaminobenzene; each of these steps requires 1 mol of NADPH. An enzyme-mediated Bamberger-like rearrangement converts hydroxylaminobenzene to 2-aminophenol, which then undergoes meta ring cleavage to 2-aminomuconic semialdehyde. The mechanism for release of ammonia and subsequent metabolism are under investigation.
Aminophenols↗
Carcinogenicity and toxicity of inhaled nitrobenzene in B6C3F1 mice and F344 and CD rats.
The potential carcinogenicity and toxicity of inhaled nitrobenzene were evaluated following chronic (2-year) exposure in mice and rats. Male and female B6C3F1 mice were exposed to 0, 5, 25, or 50 ppm nitrobenzene, while male and female F344 rats and male CD rats were exposed to 0, 1, 5, or 25 ppm nitrobenzene. All exposures were for 6 hr/day, 5 days/week excluding holidays, for a total of 505 days over 2 years. Survival was not adversely affected by nitrobenzene exposure, and only mild exposure-related decreases in body weights (< 10% of control) were occasionally noted. Nitrobenzene exposure resulted in increased incidence of neoplasia in male B6C3F1 mice (pulmonary alveolar/bronchiolar and thyroid follicular cell neoplasms), female B6C3F1 mice (mammary gland neoplasms), male F344 rats (hepatocellular and renal neoplasms), female F344 rats (endometrial stromal neoplasms), and male CD rats (hepatocellular neoplasms). In addition, there were marginal increases in the incidence of hepatocellular neoplasia in female B6C3F1 mice and thyroid follicular neoplasia in male F344 rats. Groups of nitrobenzene-exposed mice and rats with increased incidence of renal and thyroid neoplasia also had increased incidences of hyperplasia in these tissues. Toxicity resulting from chronic inhalation of nitrobenzene was manifested by methemoglobinemia, anemia, and adaptive or degenerative changes in the nose, liver, and testis. The results indicate that inhaled nitrobenzene is carcinogenic and toxic in mice and rats, and that the spectrum of these responses in animals is dependent on species, sex, and genetic background.
Administration, Inhalation↗
4-Substituted 1-chloro-2-nitrobenzenes: structure-activity relationships and extension of the substrate model of rat glutathione S-transferase 4-4.
In the present study, eleven 4-substituted 1-chloro-2-nitrobenzenes were tested for their GSH conjugation capacity when catalyzed by base or rat glutathione S-transferase (GST) 4-4. Kinetic parameters (ks and K(m), kcat, and kcat/K(m)) were determined and subsequently used for the description of structure-activity relationships (SAR's). For this purpose, eight physicochemical parameters (electronic, steric, and lipophilic) of the substituents and five computer-calculated parameters of the substrates (charge distributions and several energy values) were used in regression analyses with the kinetic parameters. The obtained SAR's are compared with corresponding SAR's for the GSH conjugation of 2-substituted 1-chloro-4-nitrobenzenes, previously determined [Van der Aar et al. (1996) Chem. Res. Toxicol. 9, 527-534]. The kinetic parameters of the 4-substituted 1-chloro-2-nitrobenzenes correlated well with the Hammett sigma p- constant; the Hammett sigma p constant corrected for "through resonance", while the corresponding kinetic parameters of the 2-substituted 1-chloro-4-nitrobenzenes did not. The base- and GST 4-4-catalyzed GSH conjugation reactions of 2-substituted 1-chloro-4-nitrobenzenes depend to a different extent on the electronic properties of the ortho substituents, suggesting the involvement of different rate-limiting transition states. The base- and GST 4-4-catalyzed conjugation of 4-substituted 1-chloro-2-nitrobenzenes, however, showed a similar dependence on the electronic properties of the para substituents, indicating that these substrates are conjugated to GSH via a similar transition state. Multiple regression analyses revealed that, besides electronic interactions, also steric and lipophilic restrictions appeared to play an important role in the GST 4-4-catalyzed GSH conjugation of 4-substituted 1-chloro-2-nitrobenzenes. Finally, the 4-substituted 1-chloro-2-nitrobenzenes were also used to extend the previously described substrate model for GST 4-4 [De Groot et al. (1995) Chem. Res. Toxicol. 8, 649-658], by which a specific steric restriction of substrates for GST 4-4 became clear.
Animals↗
Purification and characterization of nitrobenzene nitroreductase from Pseudomonas pseudoalcaligenes JS45.
Pseudomonas pseudoalcaligenes JS45 grows on nitrobenzene as a sole source of carbon, nitrogen, and energy. The catabolic pathway involves reduction to hydroxylaminobenzene followed by rearrangement to o-amino-phenol and ring fission (S. F. Nishino and J. C. Spain, Appl. Environ. Microbiol. 59:2520, 1993). A nitrobenzene-inducible, oxygen-insensitive nitroreductase was purified from extracts of JS45 by ammonium sulfate precipitation followed by anion-exchange and gel filtration chromatography. A single 33-kDa polypeptide was detected by denaturing gel electrophoresis. The size of the native protein was estimated to be 30 kDa by gel filtration. The enzyme is a flavoprotein with a tightly bound flavin mononucleotide cofactor in a ratio of 2 mol of flavin per mol of protein. The Km for nitrobenzene is 5 microM at an initial NADPH concentration of 0.5 mM. The Km for NADPH at an initial nitrobenzene concentration of 0.1 mM is 183 microM. Nitrosobenzene was not detected as an intermediate of nitrobenzene reduction, but nitrosobenzene is a substrate for the enzyme, and the specific activity for nitrosobenzene is higher than that for nitrobenzene. These results suggest that nitrosobenzene is formed but is immediately reduced to hydroxylaminobenzene. Hydroxylaminobenzene was the only product detected after incubation of the purified enzyme with nitrobenzene and NADPH. Hydroxylaminobenzene does not serve as a substrate for further reduction by this enzyme. The products and intermediates are consistent with two two-electron reductions of the parent compound. Furthermore, the low Km and the inducible control of enzyme synthesis suggest that nitrobenzene is the physiological substrate for this enzyme.
Amino Acid Sequence↗
Toxicity of nitrobenzene compounds towards isolated hepatocytes: dependence on reduction potential.
1. The cytotoxicity of p-substituted nitrobenzenes towards isolated hepatocytes under aerobic or hypoxic conditions has been determined. The nitrobenzene concentration required to cause 50% cytoxicity in 2 h was a function of the one-electron reduction potential of the nitrobenzene, with the more cytotoxic compounds having the strongest electron-withdrawing substituents. 2. The effectiveness of the nitrobenzenes at causing cytotoxicity under aerobic but not hypoxic conditions was markedly increased if hepatocyte catalase was inhibited with azide. 3. Nitrobenzenes at cytotoxic concentrations induced cyanide-resistant respiration in isolated hepatocytes. Their effectiveness correlated with their cytotoxicity. 4. The rate of oxygen activation of these nitrobenzenes by ascorbate was also a function of the one-electron reduction potential. The nitro compounds with the strongest electron-withdrawing substituents were the most rapidly reduced. 5. Most nitrobenzenes were more cytotoxic under aerobic than hypoxic conditions. Ascorbate enhanced hypoxic, but not aerobic, cytotoxicity. 6. It was concluded that the cytotoxicity of different nitrobenzenes is related to their ease of reduction to nitro radical anions and nitrosobenzenes. Aerobic cytotoxicity is probably initiated by redox cycling and oxygen activation by the nitro radical anions whereas hypoxic cytotoxicity is probably initiated by the alkylation of macromolecules by nitrosobenzene metabolites.
Alkylation↗
A critical review of the literature on nitrobenzene toxicity.
This literature review encompassing information available through 1980 and limited coverage in 1981, emphasizes results useful in assessing the potential toxic effects of nitrobenzene to man. Nitrobenzene exposure in man or experimental animals is most often associated with methemoglobinemia. Histopathologic changes also are observed in the hemato-lymphoreticular system, central nervous system, and liver. In addition, lesions have been reported in adrenals and testes. No information was found on carcinogenic or teratogenic potential, fertility, or reproductive effects of nitrobenzene. Results from Ames Salmonella assay are negative but test procedures are questionable; metabolites give positive results. Metabolism of nitrobenzene involves either oxidation or reduction yielding p-aminophenol and p-nitrophenol, and other reduced intermediates. From the foregoing, several aspects of nitrobenzene toxicity have been identified which warrant further study. Recommendations are made for chronic and subchronic exposure of test animals via inhalation to assess various toxicological endpoints. In addition, the relationship of nitrobenzene metabolism to its toxicity needs to be established. Genotoxic effects of nitrobenzene also need study.
Abnormalities, Drug-Induced↗
Cloning and sequence analysis of a catechol 2,3-dioxygenase gene from the nitrobenzene-degrading strain Comamonas sp JS765.
Comamonas sp strain JS765 utilizes nitrobenzene as a carbon and nitrogen source. The initial attack on nitrobenzene is carried out by nitrobenzene 1,2-dioxygenase, which converts nitrobenzene to an unstable nitrohydrodiol that spontaneously decomposes to form catechol and nitrite. Catechol is then degraded via a meta cleavage pathway. We now report the cloning of a DNA fragment carrying a catechol 2,3-dioxygenase gene from JS765. Nucleotide sequence analysis revealed three open reading frames (ORFs) predicted to encode proteins of 33.6, 13.0, and 35.0 kDa. Homology searches of the deduced amino acid sequences of three proteins suggested that ORF1 encodes a LysR-type transcriptional regulator, ORF2 encodes a XylT-type ferredoxin, and ORF3 encodes a catechol 2,3-dioxygenase. The putative regulatory gene, designated cdoR, is divergently transcribed from the ferredoxin and catechol dioxygenase genes, cdoT and cdoE, respectively. The catechol 2,3-dioxygenase is most similar in amino acid sequence to the 1.2.C subfamily of extradiol dioxygenases which include 3-methylcatechol 2,3-dioxygenase from the aniline- and toluidine-degrading Pseudomonas putida UCC2, TbuE from the toluene monooxygenase pathway of Pseudomonas pickettii PKO1 and catechol 2,3-dioxygenase II from the TOL plasmid pWW15. The substrate range of the catechol 2,3-dioxygenase produced by the recombinant E. coli strains was very similar to that of the enzyme present in nitrobenzene-grown JS765, suggesting that we have cloned the catechol 2,3-dioxygenase gene required for nitrobenzene degradation.
Amino Acid Sequence↗
The reversibility of nitrobenzene-induced testicular toxicity: continuous monitoring of sperm output from vasocystotomized rats.
Exposure of rats to nitrobenzene produces a degeneration of the seminiferous epithelium of the testes. Sperm production was continuously monitored in rats surgically prepared by anastomosing the vas deferentia with the urinary bladder to evaluate the reversibility of nitrobenzene toxicity. Rates of sperm production were monitored by collecting urine and counting sperm microscopically with a hemocytometer. Six weeks after surgery, rats were dosed p.o. with a single dose of 300 mg/kg of nitrobenzene in corn oil. Sperm were not detected in the urine of treated rats between 32 and 48 days after treatment. Despite the fact that degenerative changes in the seminiferous tubules were observed histologically as early as 3 days after dosing, there was a 32-day lag period between treatment and cessation of sperm output in treated rats. Histological examination showed that pachytene spermatocytes and step 1-2 spermatids were the most susceptible cell stages to nitrobenzene and were observed forming into giant cells as early as 3 days after treatment. However, repair was substantial by 3 weeks after treatment and by days 76-100, the rate of sperm output reached 78% of the control group. By 100 days after treatment, there was greater than 90% regeneration of the seminiferous epithelium. Thus, a single oral dose of nitrobenzene induced testicular degeneration and approximately a 17-day period of aspermia resulted. Back-dating of the aspermic period to the timing of the spermatogenic cycle closely corresponded with the same germ cell stages that were observed degenerating in histologic examinations. Thus, changes in sperm output from vasocystotomized rats correlated well with histopathologic changes, demonstrating the value of this technique for toxicity studies.
Administration, Oral↗
Quenching of excited chlorophyll A in vivo by nitrobenzene.
Nitrobenzene exerts a dual effect on the excitation of chlorophyll a(Chl a) in vivo. (a) A 3(3,4-dichlorophenyl)-1,1-dimethylurea-inhibited quenching that manifests as a partial inhibition of variable chloroplast fluorescence and of 2,6-dichlorophenol indophenol (DCPIP) photoreduction and saturates at ca. 5-10 muM. Since nitrobenzene is not a Hill oxidant, this effect is attributed to a catalyzed back flow of electrons from intersystem intermediates to pre-photosystem II oxidants. (b) A direct quenching of the excited Chl a in vivo. This effect has a threshold of ca. 100 muM nitrobenzene; at higher concentrations it leads to almost complete suppression of chloroplast fluorescence and DCPIP photoreduction. Tris-washed chloroplast enriched in the photosystem II reaction center species Z+Q- and ZQ- are nearly four times more sensitive to nitrobenzene quenching than those enriched in Z+Q. On the other hand, normal chloroplasts are about 10 to the fourth times more sensitive. Hence, it is argued that the extreme sensitivity of normal chloroplast fluorescence is not due to a preferential association of nitrobenzene with a particular redox species of the reaction center.
Chlorophyll↗
Identification of chlorinated nitrobenzene residues in Mississippi River fish.
Residues of lower chlorinated nitrobenzenes have been found at levels up to about 1 ppm in 8 samples of Mississippi River fish. Electron capture gas chromatography (EC/GC) was used for determination after extraction and cleanup using a procedure based on the AOAC multiresidue method for organochlorine and organophosphorus pesticides in nonfatty foods. The residues found included 2-, 3-, and 4-chloronitrobenzene and 2,3- and 3,4-dichloronitrobenzene; identity was confirmed by GC/mass spectrometry. GC retention times for 15 monochloro-through pentachloro-substituted nitrobenzene congeners were determined with OV-101 and mixed OV-101 + OV-210 columns at 130 degrees C. In studies of the nonfatty food extraction and cleanup procedures of the AOAC method, recoveries of 15 chlorinated nitrobenzenes from spiked fish samples ranged from 68 to 116%. GC of cleaned up fish extract aliquots equivalent to 20 mg sample allowed quantitation of individual congeners at levels of about 0.025 and 0.005 ppm with 3H and 63Ni EC detectors, respectively. The contamination of Mississippi River fish with chlorinated nitrobenzenes appears to be localized in a 150 mile section of the river extending from St. Louis, MO, to Cape Girardeau, MO; no chlorinated nitrobenzenes (less than 0.005 ppm) were detected in Mississippi River fish caught above or below this region of the river or in fish from the lower Missouri River, which joins the Mississippi River near St. Louis.
Animals↗
Relationship between red blood cell uptake and methemoglobin production by nitrobenzene and dinitrobenzene in vitro.
Nitrobenzene increases methemoglobin formation when incubated with native hemoglobin but not when incubated with red blood cell suspensions. These experiments were designed to determine if transport of nitrobenzene across the red blood cell membrane is a limiting factor for methemoglobin production by red blood cell suspensions. Incubation of [14C]-m-, o- or p-dinitrobenzene, but not mononitrobenzene, with red blood cell suspensions caused a time-dependent increase in methemoglobin. All three dinitrobenzenes and mononitrobenzene crossed the red blood cell membrane and accumulated in the erythrocytes after only 1 min of incubation. Incubation of mononitrobenzene with hemolysates did not result in methemoglobin production. Incubation of red blood cells with the dinitrobenzenes or mononitrobenzene for 1 and 10 min at 4 degrees C did not influence red blood cell uptake of the nitrobenzenes, suggesting that these compounds do not enter the red blood cell by an active process. Dinitrobenzene-induced methemoglobin production was markedly inhibited at 4 degrees C, and may be a result of decreased interaction with hemoglobin and/or decreased metabolism to reactive intermediates which mediate methemoglobin production. These data indicate that red blood cell transport of nitrobenzene is not the limiting factor in methemoglobin production in vitro.
Animals↗
Morphologic and biochemical studies of a nitrobenzene-induced encephalopathy in rats.
Administration of single oral doses (550 mg/kg body wt) of nitrobenzene to male F-344 rats induced petechial hemorrhages in the brain stem and cerebellum, and bilaterally symmetric degeneration (malacia) in the cerebellum and cerebellar peduncles, within 48 hours of treatment. The malacia, which was lateral and dorsal to the fourth ventricle and involved the vestibular nuclei, was attributed to edematous swelling of a membrane bounded tissue compartment. Degenerating neurons present in, and adjacent to, areas of malacia exhibited severe watery swelling of mitochondria. Myelinated axons showed moderate to severe condensation of the axoplasm and accumulation of electron-lucent fluid between the inner myelin leaflets and less frequently in the periaxonal space. Blood vessels appeared morphologically normal, while leakage of intravascularly administered horseradish peroxidase from blood vessels in the brain accompanied the hemorrhages in a small number of animals. Extravasation of this tracer did not precede the onset of hemorrhages or malacia. Autoradiographic and analytical studies demonstrated that a very small percentage (0.02%) of the administered dose reached the brain; it was present as the parent compound and accumulated in higher concentration in grey matter than white matter. There was no preferential accumulation of nitrobenzene in the areas in which lesions occurred, which may reflect a regional susceptibility to nitrobenzene or an indirect mechanism of nitrobenzene neurotoxicity.
Animals↗
Oxidative DNA damage by a metabolite of carcinogenic and reproductive toxic nitrobenzene in the presence of NADH and Cu(II).
The mechanism of DNA damage induced by metabolites of nitrobenzene was investigated in relation to the carcinogenicity and reproductive toxicity of nitrobenzene. Nitrosobenzene, a nitrobenzene metabolite, induced NADH plus Cu(II)-mediated DNA cleavage frequently at thymine and cytosine residues. Catalase and bathocuproine inhibited the DNA damage, suggesting the involvement of H2O2 and Cu(I). Typical free hydroxyl radical scavengers showed no inhibitory effects on DNA damage. Nitrosobenzene caused the formation of 8-oxo-7, 8-dihydro-2'-deoxyguanosine in calf thymus DNA in the presence of NADH and Cu(II). ESR spectroscopic study has confirmed that nitrosobenzene is reduced by NADH to the phenylhydronitroxide radical even in the absence of Cu(II). These results suggest that nitrosobenzene can be reduced non-enzymatically by NADH, and the redox cycle reaction resulted in oxidative DNA damage due to the copper-oxygen complex, derived from the reaction of Cu(I) with H2O2.
8-Hydroxy-2'-Deoxyguanosine↗