32P-postlabelling analysis of DNA adducts from Fischer-344 rats administered 2,4-diaminotoluene.

Using 32P-postlabelling and thin layer chromatography, DNA adduct formation by the potent animal carcinogen 2,4-diaminotoluene in Fischer-344 rats was investigated. DNA from four different organs, liver, mammary gland, kidney and lung, were examined for adducts following single administration of this compound. DNA binding was detected in all four organs, with each producing one major and two minor adduct spots on autoradiograms. The adducts induced were qualitatively identical among the different organs, but quantitative differences were observed. The two target organs of 2,4-diaminotoluene induced carcinogenesis, the liver and mammary gland produced higher adduct yields, with levels up to 30-times higher than those for the two non-target organs. Since the liver is the principal target for 2,4-diaminotoluene induced carcinogenesis, we further examined DNA adducts from this site for the effects of different doses and time points. DNA binding in liver was detected following doses as low as 4.1 mumol/kg. At the highest concentration examined (2046 mumol/kg), the level of the major adduct was 29.2 adducted nucleotides per 10(7) total nucleotides. The yields for the two minor adducts were approximately one-tenth that for the major adduct. Following a 410 mumol/kg dose, DNA adduct removal over time was examined. DNA adduct removal exhibited biphasic kinetics, with a rapid initial phase followed by a slower rate of elimination. Up to 60% of maximum adduct levels persisted after 2 weeks. DNA binding by 2,4-diaminotoluene was also compared to that by its weakly carcinogenic analog, 2,4-dinitrotoluene. The two compounds produced identical adduct patterns, suggesting that they share common metabolites and adducts. Adduct yields from 2,4-dinitrotoluene, however, were lower. The results of our studies suggest that the differences in carcinogenic potency between 2,4-diaminotoluene and 2,4-dinitrotoluene, as well as the organotropic effects of 2,4-diaminotoluene may be explained, in part, by quantitative differences in the extent of DNA adduct formation.     

Analysis of nitroaromatic compounds in urine by gas chromatography–mass spectrometry for the biological monitoring of explosives

Organic nitrocompounds are the most frequently used constituents of explosives and some of them have been evaluated to be highly toxic or even carcinogenic. Human contact with explosives may originate from a variety of sources, including occupational exposure during the production of ammunition as well as environmental exposure due to the contamination of soil and ground water reservoirs on former military production sites and training areas. This paper describes two gas chromatography–mass spectrometry–selected ion monitoring methods for the determination of twelve nitroaromatic compounds in urine (nitrobenzene, 1,2-dinitrobenzene, 1,3-dinitrobenzene, 1,3,5-trinitrobenzene, 2-nitrotoluene, 3-nitrotoluene, 4-nitrotoluene, 2,4-dinitrotoluene, 2,6-dinitrotoluene, 2,4,6-trinitrotoluene, 2-amino-4,6-dinitrotoluene, 4-amino-2,6-dinitrotoluene). The analytes are detectable in the lowest μg/l range, with imprecisions of 3–22% within series and 5–29% between series, depending on the compound of interest. Both procedures are rapid and relatively easy to perform and, therefore, are advantageous for the screening of occupationally or environmentally exposed persons. We analysed urine samples obtained from nine workers from an ammunition dismantling workshop and from twelve control persons. 2,4,6-Trinitrotoluene was detected in six samples at concentrations between 4 and 43 μg/l. The main metabolites of 2,4,6-trinitrotoluene, 4-amino-2,6-dinitrotoluene and 2-amino-4,6-dinitrotoluene, were found in a concentration range from 143 to 16 832 μg/l and from 24 to 5787 μg/l, respectively. Nonconjugated aminodinitrotoluenes were present as varying percentages of the total amount. 2,4-Dinitrotoluene and 2,6-dinitrotoluene were found in two samples (2–9 μg/l). Nitroaromatics were not detectable in urine specimens from control persons.     

Heterocyclic amine-DNA adducts analyzed by 32P-postlabeling method

DNA adducts formed by 12 heterocyclic amines were analyzed by 32P-postlabeling method. Several DNA adducts were detected in rat liver by administration of each heterocyclic amine. Total adduct levels ranged from 0.5 for 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP) to more than 250 for 3-amino-1,4-dimethyl-5H-pyrido[4,3-b]indole (Trp-P-1) per 10(7) nucleotides 24 hr after intragastric administration of these compounds. The N-hydroxy derivative of 2-amino-3,8-dimethylimidazo[4,5-f]quinoxaline (MeIQx) was reactive toward DNA in vitro to form adducts. Addition of acetic anhydride to N-OH-MeIQx greatly enhanced its reactivity to DNA. 32P-Postlabeling analysis revealed that the MeIQx-DNA adducts formed in vivo and in vitro were identical. Thus, MeIQx would be metabolized in vivo to N-hydroxy form and further esterified to produce more reactive species, such as N-acetoxy form, which modify DNA to form adducts.     

DNA adduct formation of 14 heterocyclic aromatic amines in mouse tissue after oral administration and characterization of the DNA adduct formed by 2-amino-9H-pyrido[2,3-b]indole (AαC), analysed by 32 P-HPLC

Heterocyclic aromatic amines (HAAs) are produced during cooking of proteinaceous food such as meat and fish. Humans eating a normal diet are regularly exposed to these food-borne substances. HAAs have proved to be carcinogenic in animals and to induce early lesions in the development of cancer. DNA adduct levels in mouse liver have been measured by ³²P-HPLC after oral administration each of 14 different HAAs. The highest DNA adduct levels were detected for 3-amino-1-methyl-5H-pyrido[4,3-b]-indole (Trp-P-2), 3-amino-1,4-dimethyl-5H-pyrido[4,3-b]indole (Trp-P-1) and 2-amino-9H-pyrido[2,3-b]indole (AαC), respectively. To assess a relative risk in a human population, a relative risk index was calculated by combining the DNA adduct levels in mouse liver with human daily intake of heterocyclic amines in a US and in a Swedish population. Such calculations suggest that AαC presents the highest risk for humans, e.g. nine-fold higher compared with the most abundant amines in food, 2-amino-1-methyl-6-phenylimidazo[4,5-b]-pyridine (PhIP). Therefore, the distribution of DNA adducts in different tissues of mouse was investigated after oral administration of AαC. The highest AαC–DNA adduct levels were found in liver (137 adducts/10⁸ normal nucleotides) followed by heart, kidney, lung, large intestine, small intestine, stomach and spleen, in descending order. To characterize the chemical structure of the major DNA adduct, chemical synthesis was performed. The major DNA adduct from the in vivo experiments was characterized by five different methods. On the basis of these results, the adduct was characterized as N²-(deoxyguanin-8-yl)-2-amino-9H-pyrido[2,3-b]indole. Considering the abundance of AαC not only in grilled meat, but also in other products like grilled chicken, vegetables and cigarette smoke and in light of the results of the present study, it is suggested that the human cancer risk for AαC might be underestimated.     

Reduction and Acetylation of 2,4-Dinitrotoluene by a Pseudomonas aeruginosa Strain

Aerobic and anoxic biotransformation of 2,4-dinitrotoluene (DNT) was examined by using a Pseudomonas aeruginosa strain isolated from a plant treating propellant manufacturing wastewater. DNT biotransformation in the presence and absence of oxygen was mostly reductive and was representative of the type of cometabolic transformations that occur when a high concentration of an easily degradable carbon source is present. P. aeruginosa reduced both nitro groups on DNT, with the formation of mainly 4-amino-2-nitrotoluene and 2-amino-4-nitrotoluene and small quantities of 2,4-diaminotoluene. Acetylation of the arylamines was a significant reaction. 4-Acetamide-2-nitrotoluene and the novel compounds 2-acetamide-4-nitrotoluene, 4-acetamide-2-aminotoluene, and 2,4-diacetamidetoluene were identified as DNT metabolites. The biotransformation of 2,4-diaminotoluene to 4-acetamide-2-aminotoluene was 24 times faster than abiotic transformation. 2-Nitrotoluene and 4-nitrotoluene were also reduced to their corresponding toluidines and then acetylated. However, the yield of 4-acetamidetoluene was much higher than that of 2-acetamidetoluene, demonstrating that acetylation at the position para to the methyl group was favored.     

Correlation of DNA adduct levels with tumor incidence: carcinogenic potency of DNA adducts

The quantitative relationship between DNA adducts and tumor incidence is evaluated in this review. All available data on DNA adduct levels determined after repeated administration of a carcinogen to rats or mice have been compiled. The list comprised 27 chemicals, of all major structural classes of carcinogens. For the correlation with tumor incidence, the DNA adduct levels measured at the given dose were normalized to the dose which resulted in a 50% tumor incidence under the conditions of a 2-year bioassay (TD50 dose). In rat liver, the calculated adduct concentration 'responsible' for a 50% hepatocellular tumor incidence spanned from 53 to 2083 adducts per 108 nucleotides, for aflatoxin B1, tamoxifen, IQ, MeIQx, 2,4-diaminotoluene, and dimethylnitrosamine (in this order). In mouse liver, the respective figures were 812 to 5543 adducts per 108 nucleotides, for ethylene oxide, dimethylnitrosamine, 4-aminobiphenyl, and 2-acetylaminofluorene. The observed span (40-fold in rats, 7-fold in mice) reflects differences between the various DNA adducts to lead to critical mutations. If additional carcinogens fit in with this astonishingly narrow range, the measurement of DNA adduct levels in target tissue has the potential to be not only an exposure marker but an individual cancer risk marker. For toremifen and styrene, low levels of DNA adducts were detected in rat liver at the end of a negative long-term bioassay. This shows that the limit of detection of DNA adducts can be well below the limit of detection of an increased tumor incidence. For a cancer risk assessment at low levels of DNA damage, treatment-related adducts must be discussed in relation to the background DNA damage and its inter- and intraindividual variability.     

Rapid separation of reduction products of 2,4,6-trinitrotoluene using TLC

Silica gel TLC methods were developed for the separation of 2,4,6-trinitrotoluene (TNT) in mixtures with possible reduction products. The methods employed repeated elutions with simple binary or ternary solvent systems in either one or two dimensional modes. The resolved analytes include TNT, selected amino derivatives (2-amino-4,6-di-nitrotoluene, 4-amino-2,6-dinitrotoluene, 2,4-diamino-6-nitrotoluene) and known hydroxylamino derivatives (2-hydroxyl-amino-4,6-dinitrotoluene, 4-hydroxylamino-2,6-dinitrotoluene and 2,4-dihydroxylamino-6-nitrotoluene).     

Degradation of 2,4,6-trinitrotoluene (TNT) by immobilized microorganism-biological filter

The combined process of immobilized microorganism-biological filter was used to degrade TNT in an aqueous solution. The results showed that the process could effectively degrade TNT, which was not detected in the effluent of the system. GC/MS analysis identified 2-amino-4,6-dinitrotoluene (2-A-4,6-DNT), 4-amino-2,6-dinitrotoluene (4-A-2,6-DNT), 2,4-diamino-6-nitrotoluene (2,4-DA-6-NT) and 2,4-diamino-6-nitrotoluene (2,6-DA-4-NT) as the main anaerobic degradation products. In addition, the Haldane model successfully described the anaerobic degradation of TNT with high correlation coefficients (R² = 0.9803). As the electron donor, ethanol played a major role in the TNT biodegradation. More than twice the theoretical requirement of ethanol was necessary to achieve a high TNT degradation rate (above 97.5%). Moreover, Environment Scan Electron Microscope (ESEM) analysis revealed that a large number of globular microorganisms were successfully immobilized on the surface of the carrier. Further analysis by Polymerase Chain Reaction (PCR)-Denaturing Gradient Gel Electrophoresis (DGGE) demonstrated that the special bacterial for TNT degradation may have generated during the domestication with TNT for 150 days. The dominant species for TNT degradation were identified by comparing gene sequences with Genebank.     

TNT Biotransformation and Detoxification by a Pseudomonas Aeruginosa Strain

Successful microbial-mediated remediation requires transformationpathways that maximize metabolism and minimize the accumulation of toxic products. Pseudomonas aeruginosa strain MX, isolated from munitions-contaminated soil, degraded 100 mg TNT L^-1 in culture medium within 10 h under aerobic conditions. The major TNT products were 2-amino-4,6-dinitrotoluene (2ADNT, primarily in the supernatant) and 2,2'-azoxytoluene (2,2'AZT, primarily in the cell fraction), which accumulated as major products via the intermediate2-hydroxylamino-4,6-dinitrotoluene (2HADNT). The 2HADNT and2,2'AZT were relatively less toxic to the strain than TNT and 2ADNT. Aminodinitrotoluene (ADNT) production increased when yeast extract was added to the medium. While TNT transformation rate was not affected by pH, more HADNTs accumulated at pH 5.0 than at pH 8.0 and AZTs did not accumulate at the lower pH. The appearance of 2,6-diamino-4-nitrotoluene (2,6DANT) and 2,4-diamino-6-nitrotoluene (2,4DANT); dinitrotoluene (DNT) and nitrotoluene (NT); and 3,5-dinitroaniline (3,5DNA) indicated various routes of TNT metabolism and detoxification by P. aeruginosa strain MX.     

Identification of Nitroso Compounds from Biotransformation of 2,4-Dinitrotoluene

The intermediates of microbial transformation of 2,4-dinitrotoluene by a mixed bacterial culture derived from activated sludge were identified as 2-amino-4-nitrotoluene, 4-amino-2-nitrotoluene, 2-nitroso-4-nitrotoluene, and 4-nitroso-2-nitrotoluene. The biotransformation of 2,4-dinitrotoluene occurred only under anaerobic conditions with an exogenous carbon source. The two nitroso compounds were unstable and could be observed only at the early stage of 2,4-dinitrotoluene anaerobic biotransformation.     

DNA adducts as a biomarker of polycyclic aromatic hydrocarbon exposure in aquatic organisms: relationship to carcinogenicity

The use of DNA adduct measurement as a biomarker of exposure to polycyclic aromatic hydrocarbons (PAHs) is now well established in ecotoxicology. In particular, DNA adduct levels in aquatic organisms has been found to produce a better correlation with PAH exposure than PAH concentrations in organisms. DNA adducts levels are most commonly determined using the ³²P-postlabelling assay which measures total aromatic adducts. The relationship between relative DNA adduct formation and carcinogenicity has been investigated for a number of carcinogenic and non-carcinogenic PAHs using an in vitro system. Our results demonstrate that relatively high levels of DNA adducts can be produced by some non-carcinogenic PAHs, while other non-carcinogenic compounds do not produce detectable adducts. In addition, it has been shown that all carcinogenic PAHs investigated produce DNAadducts and that a relationship exists between relative adduct formation and carcinogenic potency. An investigation of adduct levels in fish liver and crustacean hepatopancreas in Oxley Ck, Brisbane has shown that higher than expected DNA adduct levels were correlated with the presence of carcinogenic and non-carcinogenic PAHs with high relative adduct forming potential.     

Biotransformation of 2,4,6-Trinitrotoluene with Phanerochaete chrysosporium in Agitated Cultures at pH 4.5

The biotransformation of 2,4,6-trinitrotoluene (TNT) (175 μM) by Phanerochaete chrysosporium with molasses and citric acid at pH 4.5 was studied. In less than 2 weeks, TNT disappeared completely, but mineralization (liberated ¹⁴CO₂) did not exceed 1%. A time study revealed the presence of several intermediates, marked by the initial formation of two monohydroxylaminodinitrotoluenes (2- and 4-HADNT) followed by their successive transformation to several other products, including monoaminodinitrotoluenes (ADNT). A group of nine acylated intermediates were also detected. They included 2-N-acetylamido-4,6-dinitrotoluene and its p isomer, 2-formylamido-4,6-dinitrotoluene and its p isomer (as acylated ADNT), 4-N-acetylamino-2-amino-6-nitrotoluene and 4-N-formylamido-2-amino-6-nitrotoluene (as acetylated DANT), 4-N-acetylhydroxy-2,6-dinitrotoluene and 4-N-acetoxy-2,6-dinitrotoluene (as acetylated HADNT), and finally 4-N-acetylamido-2-hydroxylamino-6-nitrotoluene. Furthermore, a fraction of HADNTs were found to rearrange to their corresponding phenolamines (Bamberger rearrangement), while another group dimerized to azoxytoluenes which in turn transformed to azo compounds and eventually to the corresponding hydrazo derivatives. After 30 days, all of these metabolites, except traces of 4-ADNT and the hydrazo derivatives, disappeared, but mineralization did not exceed 10% even after the incubation period was increased to 120 days. The biotransformation of TNT was accompanied by the appearance of manganese peroxidase (MnP) and lignin-dependent peroxidase (LiP) activities. MnP activity was observed almost immediately after TNT disappearance, which was the period marked by the appearance of the initial metabolites (HADNT and ADNT), whereas the LiP activity was observed after 8 days of incubation, corresponding to the appearance of the acyl derivatives. Both MnP and LiP activities reached their maximum levels (100 and 10 U/liter, respectively) within 10 to 15 days after inoculation.     

Diaminotoluenes induce intrachromosomal recombination and free radicals in Saccharomyces cerevisiae

The carcinogenicity of aniline-based aromatic amines is poorly reflected by their activity in short-term mutagenicity assays such as the Salmonella typhimurium reverse mutation (Ames) assay. More information about the mechanism of action of such carcinogens is needed. Here we report the effects on DEL recombination in Saccharomyces cerevisiae of the carcinogen 2,4-diaminotoluene and its structural isomer 2,6-diaminotoluene, which is reported to be non-carcinogenic. Both compounds are detected as equally mutagenic in the Salmonella assay. In the absence of any external metabolizing system both compounds were recombinagenic in the DEL assay, with the carcinogen being a more potent inducer of deletions than the non-carcinogen. In the presence of Aroclor-induced rat liver S9, however, the carcinogen 2,4-diaminotoluene became a 2-fold more potent inducer of deletions, and the non-carcinogen 2,6-diaminotoluene was rendered less toxic and no induced recombination was observed. 2,4-Diaminotoluene is distinguished from its non-carcinogen analog in the DEL assay, therefore, on the basis of a preferential activation of the carcinogen in the presence of a rat liver microsomal metabolizing system. Free radical species are produced by several carcinogens and have been implicated in carcinogenesis. We further investigated whether exposure of yeast to either 2,4-diaminotoluene or 2,6-diaminotoluene resulted in a rise in intracellular free radical species. The effects of the free radical scavenger N-acetylcysteine on toxicity and recombination induced by the two compounds and intracellular oxidation of the free radical-sensitive reporter compound dichlorofluorescin diacetate were studied. Both 2,4- and 2,6-diaminotoluene produced free radical species in yeast, indicating that the reason for the differential activity of the compounds for induced deletions is not reflected in any difference in the production of free radical species.     

In vivo covalent binding of [14C]trinitrotoluene to proteins in the rat.

When a single dose of [14C]trinitrotoluene was administered intraperitoneally (i.p.) to rats at 1, 10 or 50 mg/kg of body weight, covalently bound radioactivity was detected in globin, plasma proteins and proteins in the liver and kidney. The extent of covalent binding was dose dependent and was highest in plasma and renal proteins at all times up to 4 h after dosing. Covalent adduct levels in globin, however, decline slower than others. At a dose of 50 mg/kg of body weight, globin covalent adduct levels peaked at 1 h after dosing at 182 pmol/mg protein and subsequently decreased to approximately 50 pmol/mg protein between days 1 and 8. Of the covalent adduct levels in liver and kidney, those in the 10,000 x g and microsomal fractions were found to be higher than that in the cytosolic fraction. Radioactivity covalently bound to globin and the hepatic proteins was susceptible to dilute acid hydrolysis from which 2-amino-4,6-dinitrotoluene (2A) and 4-amino 2,6-dinitrotoluene (4A) were the major products recovered by solvent extraction. Upon acetylation, the hydrolysate gave rise to derivatives identified as the acetates of 2A and 4A on the basis of mass spectrometry and HPLC cochromatography with authentic samples. Four hours after an i.p. dose of [14C]TNT at 50 mg/kg of body weight about 0.4% of the dose was found as bound adducts to hemoglobin, of which approximately 48% was recovered as solvent extractable radioactivity after acid hydrolysis. About 2% of the radioactive dose was in the liver, of which approximately 30% was covalently bound to hepatic proteins, and approximately 49% of that was convertible to solvent extractable radioactivity upon acid hydrolysis. In vitro incubation of [14C]TNT with blood showed that there was a linear increase of covalent adducts in globin during the first 2 h of incubation; the concentration of covalent adducts was slightly higher than that with plasma proteins. The major compounds recovered from the hydrolysate of the globin adducts were also 2A and 4A as obtained from globin in the in vivo studies. On the basis of the in vitro and in vivo study results, we have confirmed the formation of protein adducts following a single i.p. administration of [14C]TNT at 1, 10 or 50 mg/kg of body weight to the rat or by in vitro incubation with blood.(ABSTRACT TRUNCATED AT 400 WORDS)     

The formation of 2-aminofluorene-DNA adducts in vivo: evidence for peroxidase-mediated activation

Formation of DNA adducts in various tissues of dogs fed a single dose of the carcinogen 2-aminofluorene was investigated. Adduct analysis was performed using a technique that allows measurement of both N-(deoxyguanosin-8-yl)-2-amino-2-aminofluorene-DNA adduct formed by reaction of N-hydroxy-2-aminofluorene with DNA, as well as the polar 2-aminofluorene-DNA adducts formed when 2-aminofluorene is activated by prostaglandin H synthase-peroxidase in vitro. Two male beagle (A and B) dogs were examined and a different DNA adduct profile was observed with each dog. For the dog A, N-(deoxyguanosin-8-yl)-2-aminofluorene was the major adduct found in hepatic DNA; no peroxidase-derived adducts were detected in this tissue. In contrast, adducts eluting similarly to peroxidase-derived adducts were found in urinary tract tissues of this dog with the relative abundance of these adducts in the order urothelium greater than renal medulla greater than renal cortex, which correlates with the respective tissues' prostaglandin H synthase activity. N-(Deoxyguanosin-8-yl)-2-aminofluorene was detected in the renal tissues, but not in urothelium. For dog B, only the N-(deoxyguanosin-8-yl)-2-aminofluorene adduct was observed in all tissues examined, including the urothelium. However, total binding to liver, kidney, and bladder were two-, two-, and four-fold lower, respectively, than dog A. These data indicate that both prostaglandin H synthase-mediated activation and N-hydroxylation of 2-aminofluorene occur in vivo and may be subjected to pharmacodynamic considerations. Furthermore, the tissue distribution of the peroxidase-mediated 2-aminofluorene adducts suggests this process may also be of importance in the bladder-specific carcinogenicity of aromatic amines.     

Cytotoxic and genotoxic effects of energetic compounds on bacterial and mammalian cells in vitro.

The mutagenicity and toxicity of energetic compounds such as 2,4, 6-trinitrotoluene (TNT), 1,3,5-trinitrobenzene (TNB), hexahydro-1,3, 5-trinitro-1,3,5-triazine (RDX) and octahydro-1,3,5,7-tetranitro-1,3, 5,7-tetrazocine (HMX), and of amino/nitro derivatives of toluene were investigated in vitro. Mutagenicity was evaluated with the Salmonella fluctuation test (FT) and the V79 Chinese hamster lung cell mutagenicity assay. Cytotoxicity was evaluated using V79 and TK6 human lymphoblastic cells. For the TK6 and V79 assays, TNB and 2, 4,6-triaminotoluene were more toxic than TNT, whereas RDX and HMX were without effect at their maximal aqueous solubility limits. The primary TNT metabolites (2-amino-4,6-dinitrotoluene, 4-amino-2, 6-dinitrotoluene, 2,4-diamino-6-nitrotoluene and 2, 6-diamino-4-nitrotoluene) were generally less cytotoxic than the parent compound. The FT results indicated that TNB, TNT and all the tested primary TNT metabolites were mutagenic. Except for the cases of 4-amino-2,6-dinitrotoluene and 2,4-diamino-6-nitrotoluene in the TA98 strain, addition of rat liver S9 resulted in either no effect, or decreased activity. None of the tested compounds were mutagenic for the V79 mammalian cells with or without S9 metabolic activation. Thus, the FT assay was more sensitive to the genotoxic effects of energetic compounds than was the V79 test, suggesting that the FT might be a better screening tool for the presence of these explosives. The lack of mutagenicity of pure substances for V79 cells under the conditions used in this study does not preclude that genotoxicity could actually exist in other mammalian cells. In view of earlier reports and this study, mutagenicity testing of environmental samples should be considered as part of the hazard assessment of sites contaminated by TNT and related products.     

DNA adduct formation of 14 heterocyclic aromatic amines in mouse tissue after oral administration and characterization of the DNA adduct formed by 2-amino-9H-pyrido[2,3-b]indole (AalphaC), analysed by 32P_HPLC.

Heterocyclic aromatic amines (HAAs) are produced during cooking of proteinaceous food such as meat and fish. Humans eating a normal diet are regularly exposed to these food-borne substances. HAAs have proved to be carcinogenic in animals and to induce early lesions in the development of cancer. DNA adduct levels in mouse liver have been measured by 32P-HPLC after oral administration each of 14 different HAAs. The highest DNA adduct levels were detected for 3-amino-1-methyl-5H-pyrido[4,3-b]-indole (Trp-P-2), 3-amino-1,4-dimethyl-5H-pyrido[4,3-b]indole (Trp-P-1) and 2-amino-9H-pyrido[2,3-b]indole (AalphaC), respectively. To assess a relative risk in a human population, a relative risk index was calculated by combining the DNA adduct levels in mouse liver with human daily intake of heterocyclic amines in a US and in a Swedish population. Such calculations suggest that AalphaC presents the highest risk for humans, e.g. nine-fold higher compared with the most abundant amines in food, 2-amino-1-methyl-6-phenylimidazo[4,5-b]-pyridine (PhIP). Therefore, the distribution of DNA adducts in different tissues of mouse was investigated after oral administration of AalphaC. The highest AalphaC-DNA adduct levels were found in liver (137 adducts/10(8) normal nucleotides) followed by heart, kidney, lung, large intestine, small intestine, stomach and spleen, in descending order. To characterize the chemical structure of the major DNA adduct, chemical synthesis was performed. The major DNA adduct from the in vivo experiments was characterized by five different methods. On the basis of these results, the adduct was characterized as N2-(deoxyguanin-8-yl)-2-amino-9H-pyrido [2,3-b]indole. Considering the abundance of AalphaC not only in grilled meat, but also in other products like grilled chicken, vegetables and cigarette smoke and in light of the results of the present study, it is suggested that the human cancer risk for AalphaC might be underestimated.     

In vitro DNA and dGMP adducts formation caused by ochratoxin A

Ochratoxin A (OTA), a nephrotoxic and nephrocarcinogenic mycotoxin, leads to the formation of DNA adducts after administration to animals. This could be due to an epigenetic effect. In vitro assays can exclude an indirect effect, where the xenobiotic can generate, in vivo, endogenous reactive compounds which give adducts on DNA. Microsomes prepared from mice or rabbit kidney and liver, used as metabolic activators, were incubated in the presence of commercial salmon testes DNA and OTA, with NADPH or arachidonic acid used as cofactors. Upto 126 DNA adducts for 10(9) nucleotides were detected using the 32P postlabeling method after incubation with the mouse kidney system. Similar results were obtained with rabbit kidney microsomes. Using liver microsomes, the number of DNA adducts detected was much lower. When NADPH was used as a cosubstrate (to explore the cytochrome P450 metabolic pathways), with mice kidney microsomes, the adduct level was only 44% of the one obtained with arachidonic acid. These results lend support to the hypothesis of the preferential activation of OTA by the peroxidase activity of prostaglandin synthases and/or lipoxygenases to direct genotoxic metabolites, and are in agreement with the previously obtained results after in vivo treatment of mice. In order to identify the nucleotides of DNA modified by the OTA metabolites, dAMP, dGMP, dTMP and dCMP were used as substrates under the same conditions as with DNA. The adducts were found only on dGMP. The total adduct level was of 344 adducts per 10(9) nucleotides with the appearance of three major adducts in the presence of arachidonic acid. With NADPH, 271 adducts were obtained per 10(9) nucleotides, with again three major adducts, but only two of them were similar to two adducts obtained in the presence of arachidonic acid. Desferal (desferrioxamine B methanesulphonate), at a 50 microM concentration, did not reduce the adduct level. Adducts were also obtained when polydG, polydC and dG-p-dG were used as alternative substrates, whereas no adducts were obtained with polydA, polydT and polydC. The major adduct obtained after incubation of DNA with OTA, comigrated with the major adduct obtained with dGMP, in two chromatographic solvents. These results show that OTA is metabolized to genotoxic metabolite(s) which interact with the guanine residues of DNA.     

Comparison of in vivo and in vitro binding of polycyclic hydrocarbons to DNA

The in vivo binding of [³H]benzo(a)pyrene (BP) and 3-[³H]methylcholanthrene (3MC) to liver and lung DNA was studied in A/J mice. Only in liver was there any reduction in total DNA-bound radioactivity between 4 h and 24 h after administration of the hydrocarbon. DNA was fractionated on Sephadex LH-20 after enzymatic digestion. A single deoxyribonucleoside-BP adduct was detected whereas two major 3MC-adducts were observed. With both BP and 3MC, three additional peaks of radioactivity eluted rapidly in the lung DNA experiments while a fourth was noted with liver DNA. The nucleoside-bound adducts from lung represented a much larger proportion of the total radioactivity than with liver. In vitro analysis of 3MC binding to DNA showed the nucleoside-bound adducts to be predominantly deoxyguanosine-dependent but that the early peaks were independent of base suggesting binding to another part of the DNA molecule, perhaps phosphate, i.e., phosphotriesters.     

Determination of hemoglobin adducts in workers exposed to 2,4,6-trinitrotoluene

2,4,6-Trinitrotoluene (TNT) is an important occupational and environmental pollutant. TNT can be taken up through the skin and by inhalation. It is therefore essential to have fast and reliable methods to monitor human exposure. In rat experiments, it has been shown that TNT binds covalently to blood proteins and to tissue proteins. Hemoglobin (Hb) adducts of TNT are markers for the internal dose and possibly for the toxic effects of TNT, e.g. cataracts. In the present paper we introduce a new efficient method to quantify Hb adducts of TNT. Precipitated Hb was hydrolyzed with base in the presence of the surrogate internal standard 3,5-dinitroaniline (35DNA). The released 2-amino-4,6-dinitrotoluene (2ADNT) and 4-amino-2,6-dinitrotoluene (4ADNT) were quantified against 35DNA by gas chromatography-mass spectrometry with negative-ion chemical ionization. Hb of 50 workers and controls from a Chinese munition factory were investigated. The Hb adduct levels ranged from 3.7 to 522 ng for 4ADNT and from 0 to 14.7 ng for 2ADNT per gram of Hb. However, in control samples from Germany no Hb adducts of 4ADNT or 2ADNT could be found.