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Environmental pollution with nitroaromatic compounds may pose health hazards. We have examined the tumorigenicity in female Sprague-Dawley rats of 2,7-dinitrofluorene (2,7-diNF) and 9-oxo-2,7-diNF administered by intraperitoneal (i.p.) and oral routes at 10 micromol/kg body weight, 3 times per week for 4 weeks. After i.p. treatment, the estimated median latency for the combined malignant and benign mammary tumors was decreased in 2,7-diNF- (p = 0.003) or 9-oxo-2,7-diNF-treated (p = 0.007), relative to vehicle-treated rats (42 or 64 vs. 80 weeks, respectively), whereas after oral dosing, there were no significant differences. At 90 weeks, the malignant mammary tumor incidence in 2,7-diNF-, 9-oxo-2,7-diNF- and vehicle-i.p. treated rats was 44 (p = 0.02 vs. vehicle-treated), 25 and 6%, respectively. Liver and mammary gland DNA was analyzed by HPLC combined with electrospray tandem mass spectrometry for the presence of a deoxyguanosine (dG-2,7-diNF) adduct and a deoxyadenosine (dA-2,7-diNF) adduct derived from 2,7-diNF, and a deoxyguanosine (dG-9-oxo-2,7-diNF) adduct derived from 9-oxo-2,7-diNF. Both dG-2,7-diNF and dA-2,7-diNF were detected in DNA of 2,7-diNF-treated rats, whereas only very low levels of dG-9-oxo-2,7-diNF were detected in DNA of 9-oxo-2,7-diNF-treated rats. After i.p. treatment, the dA-2,7-diNF level was higher (p < 0.01) in the mammary gland than liver (13.6 vs. 7.8 adducts/10(8) nucleotides). In the mammary gland, the dG-2,7-diNF level was higher (p < 0.05) after i.p. than oral dosing and also higher (p < 0.05) than in the liver (36 vs. 8.6 and vs. 9.1 adducts/10(8) nucleotides, respectively). The preferential display of carcinogenicity and genotoxicity in the mammary gland by low doses of 2,7-diNF signifies its potential relevance for environmental breast cancer., ((c) 2008 Wiley-Liss, Inc.)

Nitrofluorenes are mutagenic and carcinogenic environmental pollutants arising chiefly from combustion of fossil fuels. Nitro aromatic compounds undergo nitroreduction to N-hydroxy arylamines that bind to DNA directly or after O-esterification. This study analyzes the DNA binding and adducts from the in vitro nitroreduction of 2,7-dinitrofluorene (2,7-diNF), a potent mammary carcinogen in the rat. Potential adduct(s) of 2,7-diNF was (were) generated by reduction of 2-nitroso-7-NF with ascorbate/H(+) in the presence of calf thymus DNA. The major adduct was characterized by HPLC/ESI/MS and (1)H NMR spectrometry as N-(deoxyguanosin-8-yl)-2-amino-7-NF, and a minor one was determined by HPLC/ESI/MS to be a deoxyadenosine adduct of 2-amino-7-NF. Products from enzymatic nitroreduction were monitored by HPLC and DNA adduct formation by (32)P-postlabeling. Xanthine oxidase/hypoxanthine-catalyzed nitroreduction of 2,7-diNF, 2-nitrofluorene (2-NF), and 1-nitropyrene (1-NP) yielded the respective amines to similar extents (30-50%). However, the level of the major adducts ( approximately 0.15/10(6) nucleotides) from 2-NF [N-(deoxyguanosin-8-yl)-2-aminofluorene] and 2,7-diNF [N-(deoxyguanosin-8-yl)-2-amino-7-NF] was < or = 2% that from 1-NP. In the presence of acetyl CoA, nitroreduction of 2-NF catalyzed by rat liver cytosol/NADH yielded the same adduct at a level of 2.2/10(6) nucleotides. Liver or mammary gland cytosol with acetyl CoA yielded mainly N-(deoxyguanosin-8-yl)-2-amino-7-NF from 2,7-diNF at >30 adducts/10(6) nucleotides, levels comparable to those from 1,6-dinitropyrene and 4- or 49-fold greater than the respective levels without acetyl CoA. Recovery of 2-nitroso-7-NF and 2-amino-7-NF from cytosol-catalyzed reduction of 2,7-diNF indicated nitroreduction and an N-hydroxy arylamine intermediate. Likewise, the presence of 2-acetylamino-7-NF indicated that reactivity with acyltransferase(s) was not prevented by the nitro group at C7. These data are consistent with activation of 2,7-diNF via nitroreduction to the N-hydroxy arylamine and acetyl CoA-dependent O-acetylation of the latter to bind to DNA. Enzymatic nitroreduction of 2,7-diNF was greatly enhanced by 9-oxidation. The nitroreduction of either 9-oxo-2,7-diNF or 9-hydroxy-2,7-diNF catalyzed by liver cytosol with acetyl CoA yielded two adducts (>2/10(6) nucleotides). Differences in the TLC migration of these adducts, compared to those from 2,7-diNF, and the lack of 2,7-diNF formation in the incubations suggested retention of the C9-oxidized groups. The relative ratios of the amine to amide from nitroreductions of 9-oxo-2,7-diNF and 2,7-diNF catalyzed by liver cytosol suggested that the 9-oxo group decreased reactivity with acyltransferase and, thus, the amount of N-acetoxy arylamine that binds to DNA. The mammary gland tumorigenicity of 2,7-diNF and the extent of its activation by the tumor target tissue shown herein suggest relevance of this environmental pollutant for breast cancer.

Nitrofluorenes and C-9-oxidized nitrofluorenes are widespread environmental genotoxins which may be relevant for breast cancer on the basis of their carcinogenicities, particularly of 2, 7-dinitrofluorene (2,7-diNF), for the rat mammary gland. Since their metabolism to active carcinogens may involve nitroreduction, this study examined the reduction of 2-nitrofluorene (2-NF) and 2,7-diNF and their 9-oxo- and 9-hydroxy (OH) derivatives by the rat mammary gland. Cytosolic fractions catalyze NADH- and NADPH-dependent reductions of the 2-nitro and 9-oxo to the respective 2-amino and 9-OH compounds at rates 4- and >/=10-fold greater than those with microsomes. Rates of amine formation catalyzed by cytosol from 2, 7-diNF are greater than the rate from 2-NF and increase for C-9-oxidized derivatives: 9-oxo-2-NF > 9-OH-2-NF > 2-NF and 9-OH-2, 7-diNF >> 9-oxo-2,7-diNF > 2,7-diNF. Nitroreduction is inhibited by O(2) or allopurinol (20 microM), dicoumarol (100 microM), and rutin (50 microM). 9-Oxoreduction is inhibited by rutin, dicoumarol, and indomethacin (100 microM), but not by O(2) or allopurinol. Pyrazole or menadione does not inhibit nitro or 9-oxoreduction. Xanthine, hypoxanthine, 2-hydroxypyrimidine, and N'-methylnicotinamide support cytosol-catalyzed nitro, but not 9-oxo, reduction. The data suggest that the nitroreduction is catalyzed largely by a xanthine oxidase and partially by a diaphorase and 9-oxoreduction by a carbonyl reductase. The extents of the nitro and carbonyl reductions of the nitrofluorenes may determine their reactivities with DNA, and thus genotoxicities for the mammary gland.

Nitrofluorene compounds are environmental pollutants chiefly from incomplete combustion. This study examined carcinogenicities after one intramammary injection of 2-nitrofluorene (2-NF), 2, 7-dinitrofluorene (2,7-diNF) or dimethyl sulfoxide (DMSO) (solvent control) to 30-day-old and of 2-NF, 9-OH-2-NF, 9-oxo-2-NF, 2,7-diNF, 9-oxo-2,7-diNF, 2,5-dinitrofluorene, 9-oxo-2,4,7-trinitrofluorene, N-OH-2-acetylaminofluorene (N-OH-2-AAF) (carcinogen control) or DMSO to 50-day-old female Sprague-Dawley rats. In 30- and 50-day-old rats 6 and 8 glands/rat, respectively, were injected with 2.04 micromol of compound in 50 microliter/gland of DMSO. Whereas all compounds including DMSO yielded combined malignant and benign mammary tumor incidences of 33-87% by week 82 after injection, 2,7-diNF produced 100 and 93% incidences significantly (P < 0.001) sooner than did DMSO, i.e. by weeks 23-49 and 18-48 after treatment of 30- and 50-day-old rats, respectively. Rats treated with 2,7-diNF and 9-oxo-2,7-diNF had significantly (P < 0.0001) and marginally (P = 0. 0536) more mammary tumors, respectively, than DMSO-treated rats. In 2,7-diNF-treated rats, the ratio of malignant to benign mammary tumors was 5.4, whereas in all other groups it was <0.5. N-OH-2-AAF, a potent tumorigen when applied to the mammary gland as a solid or in suspension, did not yield the expected tumorigenicity here. The contrasting tumorigenic potencies of 2,7-diNF and N-OH-2-AAF may have been prompted by differences in their solubilities in DMSO. Thus, the poorly soluble 2,7-diNF was slowly absorbed from the injection sites since residues (up to 0.9% of the dose injected) were recovered even after 45 weeks. The data indicate prolonged exposure of the mammary gland to 2,7-diNF and suggest that contamination of the environment with 2,7-diNF, even at low levels, poses substantial carcinogenic risk.

Widespread environmental pollution with mutagenic and carcinogenic nitrofluorenes contributes to human health risks. Since nitroreduction leads to activation of many nitro compounds, nitroreduction of the nitrofluorene (NF) derivatives by one- and two-electron reductants was examined. Rates of nitroreduction catalyzed by xanthine oxidase (XO)/hypoxanthine and measured via stimulation of acetylated cytochrome c reduction increased with the number of nitro groups and oxidation at C-9: 9-oxo-2,4,7-triNF > 9-oxo-2,7-diNF > 2,7-diNF > 9-oxo-2-NF = 2,5-diNF > 9-hydroxy-2-NF > 2-NF. Ascorbate catalyzed one-electron reduction to nitro anion radicals which reacted with molecular O2 to yield superoxide. Rates of O2 uptake with 9-oxo-2,4,7-triNF and 9-oxo-2,7-diNF were 63 and 0.17 times those, respectively, with equivalent concentrations of nitrofurazone, a classical substrate. Superoxide formation was indicated by the approximately 75% regeneration of O2 upon addition of superoxide dismutase and catalase. 9-Oxo-2,4,7-triNF stimulated O2 uptake in the presence of XO/NADH with typical Michaelis-Menten kinetics with an apparent Km of 0.476 +/- 0.054 microM versus a Km of 6.18 +/- 0.719 microM for nitrofurazone. HPLC analyses of products from reduction catalyzed by XO or diaphorase of Clostridium with NADH showed the following trends for the rates of amine formation from 9-oxo-2,7-diNF > 2,7-diNF; 9-oxo-2-NF > 9-hydroxy-2-NF > 2-NF; 2,7-diNF > 2-NF; and 9-oxo-2,7-diNF > 9-oxo-2-NF. Little or no amine was formed in 95% O2, suggesting O2-labile intermediates. The data herein suggest that oxidation at C-9 and multiple nitro groups increase the potential for nitroreduction of the nitrofluorenes in vivo which may lead to genotoxic effects.

N-Hydroxy-N-2-fluorenylacetamide (N-OH-2-FAA) and its benzamide analogue N-OH-2-FBA are mammary gland carcinogens in the female Sprague-Dawley rat. Ovariectomy inhibits tumorigenicity of topically applied N-OH-2-FAA suggesting modulation of carcinogen-activating enzymes in the gland. This study concerned the activation of N-OH-2-FAA and N-OH-2-FBA by the mammary gland and liver, a chief site of metabolism, from 50-day-old female rats and effects on the activation of ovariectomy performed at 22 days of age. The levels of N-debenzolyation of N-OH-2-FBA to N-hydroxy-N-2-fluorenamine (N-OH-2-FA), catalyzed by microsomal carboxylesterases in mammary gland and liver were similar and increased 1.5- and 1.7-fold, respectively, by ovariectomy. N-Debenzoylating activity in cytosols of both tissues appeared to be partially of microsomal origin. Mammary gland cytosol contained N-, O- and N,O-acyltransferase activities at levels 40-50% those of liver. N-Acyltransferase activity was determined via acetyl coenzyme A (AcCoA)-dependent acetylation of 2-FA and a new assay, N-OH-2-FAA-dependent acetylation of 9-oxo-2-FA. The latter activity was decreased in mammary gland by ovariectomy. Microsomal N-acyltransferase activities were <36% those of cytosols. AcCoA-dependent binding of N-OH-2-[ring-[3H]FBA to DNA, catalyzed by cytosol, was consistent with a two-step activation of N-OH-2-FBA involving esterase-catalyzed N-debenzoylation to N-OH-2-FA and its O-acyltransferase-catalyzed acetylation to the electrophilic N-acetoxy-2-FA. O-Acetyltransfer by mammary gland appeared to be rate-limiting since ovariectomy-dependent increases in N-debenzoylation did not increase binding with S9 fraction. Little or no sulfotransferase-catalyzed binding of N-OH-2-[ring-3H]FBA-derived N-OH-2-[ring-3H]FA was detected in the liver or mammary gland cytosol, respectively. The level of binding of N-OH-2-[ring-3H]FAA to DNA catalyzed by cytosolic N,O-acyltransferase was decreased approximately 23% in mammary gland and increased 1.2-fold in liver by ovariectomy. 32P-Postlabeling analyses indicated a single adduct N-(deoxyguanosin-8-yl)-2-fluorenamine in DNA of both tissues 24 h after one intraperitoneal injection of N-OH-2-FBA or N-OH-2-FAA. Respective levels were 3.6- and 5.5-fold greater in liver than mammary gland. After ovariectomy, the adduct levels from N-OH-2-FBA increased 1.8-fold in mammary gland and from N-OH-2-FAA decreased approximately 50% in both tissues. Thus, the ovariectomy-dependent changes in levels of enzymes activating N-OH-2-FBA and N-OH-2-FAA were consistent with in vivo DNA adduct levels in the target mammary gland, but not in the liver.

DNA adduct formation was examined in rat peritoneal serosa, a tumor target for i.p. administered aqueous suspensions of N-hydroxy-N-2-fluorenylbenzamide (N-OH-2-FBA) and N-hydroxy-N-2-fluorenylacetamide (N-OH-2-FAA), and compared to that in the liver, which is a tumor target for N-OH-2-FAA in the male rat. 32P-Postlabeling analyses showed the presence of a single adduct, N-(deoxyguanosin-8-yl)-2-fluorenamine (dG-C8-FA), from activation of both hydroxamic acids by the serosa and liver in vitro and in vivo. The relatively low levels of dG-C8-FA (60-80 fmol/micrograms DNA) from N-OH-2-FBA in vitro were increased 2.7- and 35-fold upon the addition of acetyl coenzyme A (AcCoA) to the serosal cytosol and hepatic cytosol or microsomes respectively. By contrast, addition of AcCoA led to a decrease (approximately 34%) in the high level of dG-C8-FA (4330 fmol/micrograms DNA) from activation of N-OH-2-FAA by hepatic cytosol and did not alter the levels from activation by hepatic microsomes and serosal cytosols (530 and 78.3 fmol/micrograms DNA respectively). These data and the previously reported hydroxamic acid activation enzyme activities in the serosa and liver indicated that the precursor of dG-C8-FA, N-acetoxy-N-2-fluorenamine, was formed from N-OH-2-FAA chiefly via an intramolecular N,O-acetyltransfer and from N-OH-2-FBA via a two-step sequence of N-debenzoylation and AcCoA-dependent O-acetylation. The levels of dG-C8-FA were approximately 2- to 3-fold higher in the serosal DNA (up to 515 and 1012 fmol/micrograms DNA) after one (30 mumol/rat) and ten or eleven (cumulative dose of approximately 275 mumol/rat) injections of N-OH-2-FBA or N-OH-2-FAA than in the hepatic DNA. This correlated with the carcinogenicities of the hydroxamic acids, but was inversely proportional to the rates and extents of their activation in vitro. Multiple injections affected hepatic enzyme activities related to the activation of the hydroxamic acids in that the cytosolic N-debenzoylation of N-OH-2-FBA increased (approximately 1.7-fold) whereas N-OH-2-FAA acetyltransferase and sulfotransferase activities decreased. The effect of treatment with N-OH-2-FBA was greater than that with N-OH-2-FAA and was greater on the sulfotransferase activity (approximately 88% decrease). The latter suggested that N-OH-2-FBA, although a poor acceptor for an enzymatic sulfate transfer, may be carcinogenic for the rat liver.(ABSTRACT TRUNCATED AT 400 WORDS)

The oxidation of carcinogenic hydroxamic acids, N-hydroxy-N-2-fluorenylacetamide (N-OH-2-FAA) and N-hydroxy-N-3-fluorenylacetamide (N-OH-3-FAA) catalyzed by horseradish peroxidase (HRP) or cytochrome c in the presence of H2O2 was investigated. HRP/H2O2 was a more efficient system in oxidation of both hydroxamic acids and the standard substrate, guaiacol, then cytochrome c/H2O2. Peroxidative activity of cytochrome c was shown after incubation with Triton X-100 and H2O2 for 20 min at room temperature in 0.05 M phosphate buffer (pH 7.5) or in 0.1 M sodium acetate (pH 6.0) without Triton X-100. Both hydroxamic acids were oxidized to nitroxyl free radicals as shown by electron spin resonance (ESR) spectroscopy. These radicals dismutated to equimolar amounts of 2- or 3-nitrosofluorene and acetate esters of the corresponding hydroxamic acids as shown by thin layer chromatography and spectrophotometric analysis of the products. In addition, large amounts of the N-fluorenylamides were generated in the reactions with cytochrome c/H2O2 system. Of the products, only 2- or 3-nitrosofluorene per se or when generated from the oxidation of the hydroxamic acids, interacted with lecithin (1 mg/ml) to yield ESR signals of the immobilized nitroxyl free radicals. In contrast to HRP/H2O2 system, in which the initial velocity of the radical formation was too fast to measure and the maximal concentrations of the nitroxyl free radicals of both hydroxamic acids were similar, in the cytochrome c/H2O2 system the nitroxyl free radical of N-OH-2-FAA formed at a 6-fold faster rate and accumulated at a 2-fold higher concentration than the radical of N-OH-3-FAA. In both enzyme systems, the persistence of the signal and the length of time before it had decreased to one half its maximum were several-fold longer for the nitroxyl free radical of N-OH-3-FAA than for that of N-OH-2-FAA. These data showed that these nitroxyl free radicals differed in their kinetic properties. One electron oxidation of N-OH-3-FAA by HRP/H2O2 system and of both isomeric hydroxamic acids by cytochrome c/H2O2 system are reported for the first time in this work and may be considered an activation reaction in carcinogenesis by these compounds.

Carcinogenicity of N-hydroxy-N-3-fluorenylacetamide for the mammary glands of female inbred F344 rats was examined after systemic and topical administration. The compound given ip produced a 60% mammary tumor incidence but was only marginally active after topical application. Female F344 rats did not develop mammary tumors after topical application of N-hydroxy-N-2-fluorenylacetamide, N-acetoxy-N-2-fluorenylacetamide, or N-acetoxy-N-3-fluorenylacetamide. These results contrasted with those reported earlier for female Sprague-Dawley rats and indicated differences in susceptibility of the mammary glands of these rat strains to tumor induction by these carcinogens.

A method for the identification and quantitation of carcinogeniic O-acetates of fluorenylhydroxamic acids by high-pressure liquid chromatography is described. The adsorbent is Corasil II and a mixture of ethyl acetate-n-hexane (1:1) is used as the solvent. N-Acetoxy-2-fluorenylacetamide or N-acetoxy-3-fluorenylacetamide are separable as single peaks from N-acetoxy-4-fluorenylacetamide and from N-acetoxy-2-fluorenylbenzamide. The peak height traced by the recorder is linearly proportional to the amount of compound in the effluent. The method can be utilized for the detection of 0.1-1.0 mug of compound. The method has been used to identify the products of the decomposition of N-acetoxy-2-fluorenylacetamide in aqueous media.

Rat embryo cells of low passage subjected to a single treatment with certain carcinogenic fluorenylhydroxamic acids and their respective acetate esters showed signs of transformation in vitro, such as changes in phenotype, growth in soft agar and agglutination with concanavalin A. In addition, certain changes in karyotype and loss of diploidy were observed. There was no evidence, either by electron microscopy or by assay of RNA-dependent DNA polymerase, for the presence of virus. None of these cell lines produced tumors after inoculation into the isologous host. The results of these study lead us to suggest that malignant transformation is a multistep process and that certain criteria of transformation of rat embryo cells are associated with the initial stage(s) in which the cells are transformed without being tumorigenic. The ultimate test for malignant transformation of rat embryo cells remains the production of tumors in a susceptible host after inoculation of treated cells.

The mechanism of mammary carcinogenesis by N-hydroxy-2-FBS, a highly potent mammary carcinogen for the female rat by ip administration, has been investigated. Previous work in vivo indicating hydrolytic cleavage of the nitrogen-sulfur bond has been confirmed with the use of sonicates of mammary gland. One of the products of the hydrolysis was N-hydroxy-2-FA identified by its conversion to 2-FA. Since carcinogenicity tests by local application showed that N-hydroxy-2-FA was not carcinogenic for the mammary gland, desulfonylation of N-hydroxy-2-FBS by mammary gland does not account for mammary carcinogenesis. N-Hydroxy-2-FBS applied directly to the mammary gland was not carcinogenic and 2-nitrosofluorene, the product of the spontaneous decomposition of N-hydroxy-2-FBS, exhibited only weak carcinogenicity upon local application. In contrast, N-hydroxy-2-FAA, a urinary metabolite of N-hydroxy-2-FBS, was highly carcinogenic by local application and very likely mediates the action of N-hydroxy-2-FBS. A metabolic pathway for the conversion of N-hydroxy-2-FBS to N-hydroxy-2-FAA is presented. This pathway involves the intermediate formation, by mammary gland or liver, of N-hydroxy-2-FA. The site of the subsequent acetylation of the hydroxylamine is unknown at present although the mammary gland appears to be excluded.

This work confirms the previous observation that a single application of N-hydroxy-2-fluorenylacetamide or N-hydroxy-3-fluorenylacetamide to the mammary gland of the rat induced a high incidence of tumors, whereas the corresponding arylamides, N-2-fluorenylacetamide (2-FAA) and N-3-fluorenylacetamide, were only weakly active. The results suggested N-hydroxylation of the arylamides as a prerequisite for mammary carcinogenesis. Since N-hydroxylation of 2-FAA by hepatic microsomes is catalyzed by the mixed-function oxidase containing cytochrome P-450 or the 2-methylcholanthrene-inducible cytochrome P1-450, we examined whether these cytochromes are present in mammary microsomes. In contrast to liver, neither cytochrome nor N-hydroxylation of 2-FAA was detected in the mammary gland of normal and 3-methylcholanthrene-treated rats. These experiments indicated that the N-hydroxylation of 2-FAA, although obligatory for induction of mammary neoplasia, is not performed in the mammary gland but may take place in the liver. We also examined the carcinogenicity of N-acetoxy-2-fluorenylacetamide and N-acetoxy-3-fluorenylacetamide for the mammary gland upon topical application. Since both acetates were carcinogenic and since the acetyl group of acetyl coenzyme A is transferred to fluorenylhydroxamic acids at pH 7.4, these esters may be ultimate carciogens in mammary carcinogenesis. Ovariectomized rats did not develop mammary tumors after a single application of the fluorenylhydroxamic acids, and administration of estradiol and fluorenylhydroxamic acids to the ovariectomized rats did not improve the tumor yield. These results indicate that induction of mammary tumors by fluorenylhydroxamic acids is under hormonal control.