In vivo covalent binding of aflatoxin B1 and aflatoxin M1 to liver DNA of rat,mouse and pig

[¹⁴C]Aflatoxin B₁ (AFB₁) was isolated from cultures of Aspergillus parasiticus grown on [1-¹⁴C]sodium acetate. Covalent binding of AFB₁ to liver DNA of rat and mouse was determined 6–8 h after oral administration. The effectiveness of covalent binding, expressed as DNA binding per dose in the units of a ‘Covalent Binding Index’ (CBI), (μmol aflatoxin/mol DNA nucleotides)/(mmol aflatoxin/kg animal), was found to be 10 400 for rats and 240 for mice. These CBI partly explain the different susceptibility of the two species for the incidence of hepatic tumors.The corresponding values for pig liver DNA, 24 and 48 h after oral administration, were found to be as high as 19 100 and 13 300. DNA-binding has not so far been reported for this species although it could represent an appropriate animal model for studies where a human-like gastrointestinal tract physiology is desirable.Aflatoxin M₁ (AFM₁) is a metabolite found in the milk of cows that have been fed AFB₁-contaminated diet. [¹⁴C]AFM₁ was also found to be produced by cultures of A. parasiticus giving a yield of about 0.3% of the total aflatoxins. A test for covalent binding to rat liver DNA revealed a CBI of 2100 showing that AFM₁ must also be regarded as a strong hepatocarcinogen. It is concluded that AFB₁ contaminations should be avoided in dairy feed.     

Lack of in vivo DNA binding of mercaptobenzothiazole to selected tissues of the rat

In this study, the in vivo binding of 14C-labelled 2-mercaptobenzothiazole (MBT) to DNA was investigated. Male and female Fischer 344 rats were gavaged with 375 mg MBT/kg body weight and killed 8 hours later. DNA was extracted from the liver, adrenal glands, pituitary gland, pancreas, and bone marrow and the amount of radioactivity associated with the DNA was determined. Results from this study indicate that MBT does not significantly bind to DNA from any of the tissues examined. CBI values for liver for the 3 methods of purification were -1-3 which are on the low end of the covalent binding index. The CBI values for the other tissues were always less than 1. Other chemicals with similar CBI values include estrone and diethylstilbesterol. Strong hepatocarcinogens such as dimethylnitrosamine and aflatoxin have CBI values ranging from 6000 to greater than 20000.     

DNA-binding studies with 6BT and 5I: implications for DNA-binding/carcinogenicity and DNA-binding/mutagenicity correlations

The divergent activities of a reported carcinogen/noncarcinogen pair of monoazo dyes related to the hepatocarcinogen Butter Yellow (DAB) are currently under investigation in our laboratories. As part of these studies we have determined (a) target organ distribution after oral dosing to rats and (b) covalent binding of 14C-labelled compound to DNA. In DNA-binding studies, 3 rat liver-metabolising systems were employed: in vivo (whole liver), isolated intact hepatocytes, and liver subcellular fractions. Distribution studies revealed that comparable levels of both compounds were detected in the liver at similar times after dosing, and these in vivo tissue concentrations were used for in vitro DNA-binding studies. At this 'in vivo equivalent dose', the carcinogen was consistently bound to DNA more effectively, and the difference (ratio of DNA binding) between the 2 compounds was far greater in vivo. In subsequent studies, covalent DNA binding to bacterial (Salmonella) DNA was assessed at the in vivo equivalent dose. In contrast to the afore-mentioned findings in mammalian systems, the carcinogen was bound less effectively to DNA, and gave fewer revertant counts/plate when the 2 compounds were bound to an equivalent extent. These data are discussed in view of their implications for DNA-binding/carcinogenicity correlations, and with respect to the relationship between DNA binding and mutagenicity in the Salmonella assay.     

Investigations on DNA binding in rat liver and in Salmonella and on mutagenicity in the Ames test by emodin, a natural anthraquinone

Emodin (1,6,8-trihydroxy-3-methylanthraquinone), an important aglycone found in natural anthraquinone glycosides frequently used in laxative drugs, was mutagenic in the Salmonella/mammalian microsome assay (Ames test) with a specificity for strain TA1537. The mutagenic activity was activation-dependent with an optimal amount of S9 from Aroclor 1254-treated male Sprague-Dawley rats of 20% in the S9 mix (v/v) for 10 micrograms emodin per plate. Heat inactivation of the S9 for 30 min at 60 degrees C prevented mutagenicity. The addition of the cytochrome P-448 inhibitor 7,8-benzoflavone (18.5 nmoles per plate) reduced the mutagenic activity of 5.0 micrograms emodin per plate to about one third, whereas the P-450 inhibitor metyrapone (up to 1850 nmoles per plate) was without effect. To test whether a metabolite binds covalently to Salmonella DNA, [10-(14)C]emodin was radiosynthesized, large batches of bacteria were incubated with [10-(14)C]emodin and DNA was isolated. [G-3H]Aflatoxin B1 (AFB1) was used as a positive control mutagen known to act via DNA binding. DNA obtained after aflatoxin treatment could be purified to constant specific activity. With emodin, the specific activity of DNA did not remain constant after repeated precipitations so that it is unlikely that the mutagenicity of emodin is due to covalent interaction of a metabolite with DNA. The antioxidants vitamin C and E or glutathione did not reduce the mutagenicity. Emodin was also negative with strain TA102. Thus, oxygen radicals are probably not involved. When emodin was incubated with S9 alone for up to 50 h before heat-inactivation of the enzymes and addition of bacteria, the mutagenic activity did not decrease. It is concluded that the mutagenicity of emodin is due to a chemically stable, oxidized metabolite forming physico-chemical associations with DNA, possibly of the intercalative type. In order to check whether an intact mammalian organism might be able to activate emodin to a DNA-binding metabolite, radiolabelled emodin was administered by oral gavage to male SD rats and liver DNA was isolated after 72 h. Very little radioactivity was associated with the DNA. Considering that DNA radioactivity could also be due to sources other than covalent interactions, an upper limit for the covalent binding index, CBI = (mumoles chemical bound per moles DNA nucleotides)/(mmoles chemical administered per kg body weight) of 0.5 is deduced. This is 10(4) times below the CBI of AFB1.(ABSTRACT TRUNCATED AT 400 WORDS)     

Carcinogen-nucleic acid interactions: equilibrium binding studies of aflatoxins B1 and B2 with DNA and the oligodeoxynucleotide d(ATGCAT)2

Equilibrium binding is believed to play an important role in directing the subsequent covalent attachment of many carcinogens to DNA. We have utilized UV spectroscopy to examine the non-covalent interactions of aflatoxin B1 and B2 with calf thymus DNA, poly(dAdT):poly(dAdT), and poly(dGdC):poly(dGdC), and have utilized NMR spectroscopy to examine non-covalent interactions of aflatoxin B2 with the oligodeoxynucleotide d(ATGCAT)2. UV-VIS binding isotherms suggest a greater binding affinity for calf thymus DNA and poly(dAdT):poly(dAdT) than for poly(dGdC):poly(dGdC). Scatchard analysis of aflatoxin B1 binding to calf thymus DNA in 0.1 M NaCl buffer indicates that binding of the carcinogen at levels of bound aflatoxin less than 1 carcinogen per 200 base pairs occurs with positive cooperativity. The cooperative binding effect is dependent on the ionic strength of the medium; when the NaCl concentration is reduced to 0.01 M, positive cooperativity is observed at carcinogen levels less than 1 carcinogen per 500 base pairs. The Scatchard data may be fit using a "two-site" binding model [L.S. Rosenberg, M.J. Carvlin, and T.R. Krugh, Biochemistry 25, 1002-1008 (1986)]. This model assumes two independent sets of binding sites on the DNA lattice, one a high affinity site which binds the carcinogen with positive cooperativity, the second consisting of lower affinity binding sites to which non-specific binding occurs. NMR analysis of aflatoxin B2 binding to d(ATGCAT)2 indicates that the aflatoxin B2/oligodeoxynucleotide complex is in fast exchange on the NMR time scale. Upfield chemical shifts of 0.1-0.5 ppm are observed for the aflatoxin B2 4-OCH3, H5, and H6a protons. Much smaller chemical shift changes (less than or equal to 0.06 ppm) are observed for the oligodeoxynucleotide protons. The greatest effect for the oligodeoxynucleotide protons is observed for the adenine H2 protons, located in the minor groove. Nonselective T1 experiments demonstrate a 15-25% decrease in the relaxation time for the adenine H2 protons when aflatoxin B2 is added to the solution. This result suggests that aflatoxin B2 protons in the bound state may be in close proximity to these protons, providing a source of dipolar relaxation. Further experiments are in progress to probe the nature of the aflatoxin B1 and B2 complexes with polymeric DNA and oligodeoxynucleotides, and to establish the relationship between the non-covalent DNA-carcinogen complexes observed in these experiments, and covalent aflatoxin B1-guanine N7 DNA adducts.     

Chemical and biological factors affecting mutagen potency

This review surveys the chemical and biological factors that are correlated with the mutagenic activity of the aromatic and heterocyclic amines. Particular attention is given to the predicted quantum chemical properties of the parent amines and their metabolites. A number of chemical properties have been found to correlate well with measured mutagenic potency, including log P, the enrgies of the frontier orbitals of the parent amines, and the thermodynamic stability of the nitrenium ion, possibly the ultimate DNA-binding species. These correlations are intriguing clues to the mutagenic activity of the aromatic amines; however, many factors still await final explanation, including the exact mechanisms of the metabolic enzymes, the identity(s) of the ultimate DNA-binding species, the reaction mechanism in the DNA-adduction, the role of sequence context in the covalent and non-covalent binding of the adducts, and the role of DNA repair.     

Heritable and cancer risks of exposures to anticancer drugs: inter-species comparisons of covalent deoxyribonucleic acid-binding agents

In the past years, several methodologies were developed for potency ranking of genotoxic carcinogens and germ cell mutagens. In this paper, we analyzed six sub-classes of covalent deoxyribonucleic acid (DNA) binding antineoplastic drugs comprising a total of 37 chemicals and, in addition, four alkyl-epoxides, using four approaches for the ranking of genotoxic agents on a potency scale: the EPA/IARC genetic activity profile (GAP) database, the ICPEMC agent score system, and the analysis of qualitative and quantitative structure-activity and activity-activity relationships (SARs, AARs) between types of DNA modifications and genotoxic endpoints. Considerations of SARs and AARs focused entirely on in vivo data for mutagenicity in male germ cells (mouse, Drosophila), carcinogenicity (TD₅₀s) and acute toxicity (LD₅₀s) in rodents, whereas the former two approaches combined the entire database on in vivo and in vitro mutagenicity tests. The analysis shows that the understanding and prediction of rank positions of individual genotoxic agents requires information on their mechanism of action. Based on SARs and AARs, the covalent DNA binding antineoplastic drugs can be divided into three categories. Category 1 comprises mono-functional alkylating agents that primarily react with N7 and N3 moieties of purines in DNA. Efficient DNA repair is the major protective mechanism for their low and often not measurable genotoxic effects in repair-competent germ cells, and the need of high exposure doses for tumor induction in rodents. Due to cell type related differences in the efficiency of DNA repair, a strong target cell specificity in various species regarding the potency of these agents for adverse effects is found. Three of the four evaluation systems rank category 1 agents lower than those of the other two categories. Category 2 type mutagens produce O-alkyl adducts in DNA in addition to N-alkyl adducts. In general, certain O-alkyl DNA adducts appear to be slowly repaired, or even not at all, which make this kind of agents potent carcinogens and germ cell mutagens. Especially the inefficient repair of O-alkyl—pyrimidines causes the high mutational response of cells to these agents. Agents of this category give high potency scores in all four expert systems. The major determinant for the high rank positions on any scale of genotoxic of category 3 agents is their ability to induce primarily structural chromosomal changes. These agents are able to cross-link DNA. Their high intrinsic genotoxic potency appears to be related to the number of DNA cross-links per target dose unit they can induce. A confounding factor among category 3 agents is that often the genotoxic endpoints occur closed to or toxic levels, and that the width of the mutagenic dose range, i.e., the dose area between the lowest observed effect level and the LD₅₀, is smaller (usually no more than 1 logarithmic unit) than for chemicals of the other two categories. For all three categories of genotoxic agents, strong correlations are observed between their carcinogenic potency, acute toxicity and germ cell specificity.     

Covalent binding of ethinylestradiol and estrone to rat liver DNA in vivo

The covalent binding of [6,7-³H] ethinylestradiol (EE) and [6,7-³H] estrone (E) to liver DNA of 200 g female rats was measured 8 h after the administration of 80 μg (9.2 mCi) estrogen by gavage. The binding is 1.5 for EE and 1.1 for E, expressed as binding to DNA/dose, in units of μmol hormone/mol DNA phosphate/mmole hormone/kg body wt. It is in the same order of magnitude as for benzene and about 10 000 times below the binding of typical liver carcinogens, such as aflatoxin B₁ or N,N-dimethylnitrosamine.     

Bacterial systems for carcinogenicity testing

During the past 30 years, bacterial test systems have been extensively refined in their ability to detect not only mutagenic agents but, in many cases, carcinogenic ones as well. Since many carcinogens are known to be activated within the mammalian body, major improvements in bacterial test systems were made when representative parts of mammalian metabolism were included as part of the test protocol. Presently, systems of great simplicity and convenience are available for the efficient detection of gene mutations, lysogenic induction of prophages, and differential DNA repair. These qualities render bacterial systems potentially useful in distinguishing between carcinogens and non-carcinogens, in characterizing induced mutation spectra, and possibly in quantifying mutagenic potency that may be used to predict tumor-initiating potency. Sensitive strains of Salmonella typhimurium. Escherichia coli and Bacillus subtilis with altered DNA-repair capacities have been constructed which accurately identify many carcinogens. Comparative studies have shown that techniques using these strains can be standardized to some extent and that the majority of carcinogens are active in all adequately sensitive genetic systems. Because of this redundancy, it may be sufficient to employ only one standardized set of tester strains and methodology. However, serveral classes of known carcinogens are undetected or underestimated when assayed in standard testing procedures. Some of these chemicals can be efficiently recognized as mutagens upon varying the methodology, the genetic endpoint, or the mammalian activation system. Thus, to modify and adjust the experimental protocol to the particular type of chemical under study and to calibrate the system with appropriate carcinogenic and non-carcinogenic reference compounds is advisable. It is noteworthy that chemical carcinogens which probably act by non-genotoxic mechanisms thus far remain undetected in bacterial tests. Newly developed systems which measure specific types of genetic events, such as transpositions of DNA segments and derepression of genes, presently are being tested for their ability to detect such carcinogens. A final matter of growing concern is the increasing number of environmental chemicals that are found to be mutagenic in bacteria but for which information about carcinogenic activity in vivo is insufficient. The possible use of bacteria for quantifying mutagenic potency and extrapolating this information to tumor-initiating potency can be envisaged in three ways: (i) direct extrapolation from standard in vitro tests, (ii) indirect extrapolation making use of an in vitro/in vivo comparison of induced effects (the parallelogram method) as devised by Sobels [138] on the basis of identical dose (to DNA), and (iii) host-mediated assays to assess mutagenic potency of carcinogens in selected organs of mammals...     

Carcinogen-Nucleic Acid Interactions: Equilibrium Binding Studies of Aflatoxins B1 and B2 with DNA and the Oligodeoxynucleotide d(ATGCAT)2

Abstract

Equilibrium binding is believed to play an important role in directing the subsequent covalent attachment of many carcinogens to DNA. We have utilized UV spectroscopy to examine the non-covalent interactions of aflatoxin B₁ and B₂ with calf thymus DNA, poly(dAdT):poly(dAdT), and poly(dGdC):poly(dGdC), and have utilized NMR spectroscopy to examine non-covalent interactions of aflatoxin B₂ with the oligodeoxynucleotide d(ATGCAT)₂. UV-VIS binding isotherms suggest a greater binding affinity for calf thymus DNA and poly(dAdT):poly(dAdT) than for poly(dGdC):poly(dGdC). Scatchard analysis of aflatoxin B₁ binding to calf thymus DNA in 0.1 M NaCl buffer indicates that binding of the carcinogen at levels of bound aflatoxin ? 1 carcinogen per 200 base pairs occurs with positive cooperativity. The cooperative binding effect is dependent on the ionic strength of the medium; when the NaCl concentration is reduced to 0.01 M, positive cooperativity is observed at carcinogen levels ? 1 carcinogen per 500 base pairs. The Scatchard data may be fit using a “two-site” binding model [L.S. Rosenberg, M J. Carvlin, and T.R. Krugh, Biochemistry 25, 1002–1008 (1986)]. This model assumes two independent sets of binding sites on the DNA lattice, one a high affinity site which binds the carcinogen with positive cooperativity, the second consisting of lower affinity binding sites to which non-specific binding occurs. NMR analysis of aflatoxin B₂ binding to d(ATGCAT)₂ indicates that the aflatoxin B₂/oligodeoxynucleotide complex is in fast exchange on the NMR time scale. Upfield chemical shifts of 0.1–0.5 ppm are observed for the aflatoxin B₂ 4-OCH₃, H5, and H6a protons. Much smaller chemical shift changes ? 0.06 ppm) are observed for the oligodeoxynucleotide protons. The greatest effect for the oligodeoxynucleotide protons is observed for the adenine H2 protons, located in the minor groove. Nonselective T₁ experiments demonstrate a 15–25 % decrease in the relaxation time for the adenine H2 protons when aflatoxin B₂ is added to the solution. This result suggests that aflatoxin B₂ protons in the bound state may be in close proximity to these protons, providing a source of dipolar relaxation. Further experiments are in progress to probe the nature of the aflatoxin B₁ and B₂ complexes with polymeric DNA and oligodeoxynucleotides, and to establish the relationship between the non-covalent DNA-carcinogen complexes observed in these experiments, and covalent aflatoxin B₁,-guanine N7 DNA adducts.     

Equilibrium binding of derivatives of the carcinogen, benzo(a)pyrene, to DNA. Thermodynamic analysis

The physical binding of polycyclic aromatic hydrocarbon derivatives which are ultimate carcinogens to DNA may play a role in the formation of covalent DNA adducts by these compounds or in the detoxification of the compounds via DNA-catalyzed hydrolysis. Previous studies of DNA-binding interactions of derivatives of benzo(a)pyrene (BP) have been confined to low r values (r - ligands bound/base pair). We have now applied the Scatchard formalism (as modified to include neighbor exclusion) to the spectrophotometric determination of the binding of two derivatives of BP, trans - 9,10 - dihydroxydihydro - BP and 7r,8t - dihydroxy-9t,10t-oxy-7,8, 9,10-tetrahydro-BP, to double-stranded DNA at reasonably high r values. Exclusion parameters, binding constants, and thermodynamic parameters are all within the ranges found for other intercalants. Although these ligands are uncharged, the binding exhibits significant ionic strength dependence which can be rationalized (partially) by polyelectrolyte theory. Using the measured ionic strength dependence, a thermodynamic association constant, independent of ionic interactions, can be calculated which is very close to the calculated thermodynamic association constants for ethidium and proflavine.     

Distribution and macromolecular binding of benzo[a]pyrene and two polychlorinated biphenyl congeners in female mice

PCBs are complete rodent carcinogens and their potent tumor promoting activity has been reported, but their tumor-initiating activity remains controversial. Macromolecular binding of PCB metabolites has been demonstrated in vitro, but this issue remains unclear in vivo. The purpose of this study was to determine the binding affinity of 4-chlorobiphenyl and 3,3',4,4'-tetrachlorobiphenyl to proteins and DNA in vivo. C57/BL6 female mice were treated intraperitoneally with hepatic enzyme inducers (phenobarbital and beta-naphthoflavone) and then with 14C-labelled polychlorinated biphenyls or benzo[a]pyrene. The short-term distribution of labeled compounds into liver, lungs and kidneys and into different sub-cellular fractions of these tissues was assessed and the DNA and proteins from the 700 x g pellet were further purified to assess covalent binding. All compounds were distributed in low amounts into the liver, kidneys and lungs, with the greatest accumulation in the liver, and the lowest in lungs. In all tissues, test compounds were mostly found in cytosols and organellar pellets (10,000 x g), and lower amounts were present in nuclear pellets (700 x g) and microsomes. In lungs and kidneys, only benzo[a]pyrene showed significant covalent binding to proteins. In the liver, protein binding indices were significant for all compounds (P<0.05), but no significant binding of the test compounds to DNA could be demonstrated with this approach. Our results suggest that at the 24 h time point, all compounds were activated to electrophilic intermediates prone to macromolecular binding. Hepatic proteins apparently act as a sink for PCB-derived electrophiles, thus preventing detectable levels of covalent binding to hepatic DNA or to proteins in less metabolically active tissues.     

32P-adduct assay: Short- and long-term persistence of 2-acetylaminofluorene-DNA adducts and other applications of the assay

³²P-Postlabeling techniques have been developed to detect and measure adducts formed by covalent binding of carcinogens of Known or unknown origin with DNA (and RNA). The assay is applicable to various classes of chemical carcinogens and permits detection of many adducts at attomole (10^–18 mol) level using microgram amounts of DNA. Here, we demonstrate the application of the assay for the analysis of short- and long-term persistence of 2-acetylaminofluorene-DNA adducts in rat liver in vivo and also outline examples illustrating the applicability of the procedure to different experimental problems.Abbreviations AAF 2-acetylaminofluorene - N-OH-AAF N-hydroxy-2-acetylaminofluorene     

A comparison of DNA adduct formation in white blood cells and internal organs of mice exposed to benzo[a]pyrene, dibenzo[c,g]carbazole, safrole and cigarette smoke condensate

Measurement of tissue/cell DNA adducts represents a suitable monitor of carcinogen exposure because the majority of chemical mutagens/carcinogens react with DNA, forming covalent adducts, a key event in the initiation of chemical carcinogenesis. Investigations of DNA-adduct formation in vivo in white blood cells (WBC) versus target tissues, i.e. internal organs for most carcinogens, is expected to yield useful information about the suitability of WBC for biomonitoring and risk assessment. For this purpose, female ICR mice were given 0.4 mmole/kg benzo[a]pyrene (BP), 0.045 mmole/kg dibenzo[c,g]carbazole (DBC) or 2.47 mmole/kg safrole by oral gavage or 4 daily doses (equivalent to 3 cigarettes) of cigarette-smoke condensate (CSC) by topical application. At 24 h after dosing, DNA adducts were detected by a nuclease P1-enhanced 32P-postlabeling assay [M.V. Reddy and K. Randerath, Carcinogenesis, 7 (1986) 1543] in WBC and internal tissues treated with individual carcinogens, while CSC treatment elicited aromatic adducts in most tissues but not in WBC. Adduct patterns of WBC DNA were qualitatively similar to those of internal organs, but adduct amounts varied. BP, a systemic carcinogen, bound nearly as much to WBC DNA as to target-tissue DNA samples; whereas the liver carcinogens, DBC and safrole, bound to WBC DNA considerably less (22- and 51-fold, respectively) compared with liver DNA. The number of adducts in 10(7) nucleotides of WBC, liver, lung, kidney and spleen DNA, respectively, were: 2, 5, 3, 2 and 3 with BP; 6, 131, 6, 14 and 4 with DBC; 5, 238, 3, 5 and 0.6 with safrole. For CSC, these values were 0, 1 and 0.02 in WBC, lung and spleen, respectively. Our results show that carcinogen binding to WBC DNA does not reflect binding to target-tissue DNA in a quantitative sense for the carcinogens studied except for BP, and that WBC are not suitable surrogates for monitoring CSC exposure by DNA-adduct measurement after topical application. The CSC data in mice was consistent with the previous findings in humans that smokers' tissues but not WBC show smoking-related bulky/aromatic DNA adducts, as measured by 32P-postlabeling.     

Hypersensitivity to cell killing and mutation induction by chemical carcinogens in an excision repair-deficient mutant of CHO cells

A strain of Chinese hamster ovary cells that is deficient in nucleotide excision repair, strain UV5, was compared with the normal parental CHO cells in terms of cytotoxicity and mutagenesis after exposure to several chemical carcinogens that are known to produce bulky, covalent adducts in DNA. Induced mutations were measured at the hprt locus using thioguanine resistance and at the aprt locus using azaadenine resistance. The compounds tested that required metabolic activation (using rat or hamster microsomal fractions) were 7,12-dimethylbenz(a)anthracene, 3-methylcholanthrene, benzo(a)pyrene, aflatoxin B1, 2-acetylaminofluorene, and 2-naphthylamine. The direct-acting compounds (+/-)-r-7,t-8-dihydroxy-t-9,10-epoxy-7,8,9,10-tetrahydrobenzo(a)pyrene, N-acetoxy-2-acetylaminofluorene, and N-OH-2-naphthylamine were also studied. For all compounds except 2-naphthylamine and its active metabolite, the repair-deficient cells were significantly more sensitive to killing than the normal CHO cells. Mutation induction at both loci was also more efficient in UV5 cells in each instance where enhanced cytotoxicity was observed. By using tritium-labeled N-acetoxy-2-acetylaminofluorene, normal and mutant cells were shown to bind mutagen to their nuclear DNA with similar efficiency, and a greater amount of adduct removal occurred in the normal cells. From this study it is concluded that the use of excision repair-deficient CHO cells provides enhanced sensitivity for detecting mutagenesis and that a positive differential cytotoxicity response gives an indication of repairable, potentially lethal genetic damage.     

Reactivity of aflatoxin B2a antibody with aflatoxin B1-modified DNA and related metabolites.

Aflatoxin B2a (AFB2a) antiserum has been previously used in an enzyme-linked immunosorbent assay (ELISA) for the quantitation of AFB1 and AFB2a. The present investigation examined the reactivity of the antiserum toward those adducts and metabolites of AFB1 believed to play a major role in aflatoxicosis and carcinogenesis. 2,3-Dihydro-2-(N7-guanyl)-3-hydroxyaflatoxin B1 (AFB1-N7-Gua), the putative 2,3-(N5-formyl-2-2', 5',6'-triamino-4-oxo-N5-pyrimidyl)-3-hydroxyaflatoxin B1 (AFB1-FAPyr), 2,3-dihydro-2,3-dihydroxyaflatoxin B1 (AFB1-diol), AFB1-N7-Gua-modified DNA, and AFB1-FAPyr-modified DNA were prepared by in vitro incubation or chemical methods and subjected to competitive AFB2a ELISA. The antiserum showed significant reactivity with all five compounds, indicating that it had a high degree of specificity for both the cyclopentenone and the methoxy group of the parent aflatoxin molecule. Sensitivity for AFB-N7-Gua-modified DNA, AFB1-FAPyr-modified DNA, and AFB1-diol by the ELISA method was 0.1 pmol per assay. To test the applicability of immunological detection of covalent binding of AFB1 to DNA, the ELISA was compared with a conventional radioisotopic assay in two in vitro studies. The results showed that estimates of the kinetics and substrate dependence of covalent binding to calf thymus DNA in rat microsomal incubation mixtures by both methods were comparable. The broad specificity AFB2a antibody might be of considerable value in the detection of AFB1 macromolecular adducts and related metabolites in epidemiological investigations or in the diagnosis of aflatoxicosis.     

Aflatoxin B1 and DNA adducts. Proposed model for surface noncovalent and covalent complexes with N(7) of guanine. II.

An alternate model for surface noncovalent and surface covalent binding of aflatoxin B1 to N(7) of guanine in DNA is proposed. This model considers the out-of-plane motions of C(8) of aflatoxin B1 in those interactions. The covalent intercalated fit of aflatoxin B1 into DNA arises from steric adjustments made by DNA at the covalent intercalation site as well as local strain in the bond angles about N(7) of guanine and C(8) of aflatoxin B1. The bond angle about N(7) deviates modestly from the sp2 value toward the sp3 value. This study suggests that the surface covalent aflatoxin B1-DNA complex serves only a minor role in aflatoxin's precarcinogenic interaction with DNA and is a likely correctable error.     

Evaluation of a DNA polymerase-deficient mutant of E. coli for the rapid detection of carcinogens

Differential growth inhibition of two E. coli cultures was evaluated as a rapid screening technique for chemical carcinogens. Of the carcinogens tested, only “direct acting” carcinogens produced positive results. Furthermore, this test is not a quantitative assay in that neither was a dose—response relationship seen nor did potent carcinogens necessarily show a greater response than weaker carcinogens.Most of the carcinogens tested are considered to require metabolic activation in order to exert their carcinogenic action. Despite many attempts, including several variations of reaction conditions, metabolic activation by rat liver fractions was not apparent. Many of these carcinogens are insoluble in water and may not diffuse through the agar and therefore not reach the indicator organism.A number of chemicals that are not carcinogenic produced positive results with this assay. Many of these substances are oxidants or oxidation products which are highly reactive with DNA as well as with other cellular constituents. Therefore, it is possible that the toxicity exhibited by these chemicals was caused by a reaction with some essential cellular constituent other than DNA and such damage would not be repairable by DNA polymerase. These observations limit the usefulness of the P3478 E. coli technique in its present form as a prescreen for chemical carcinogens.     

Comparative binding and sequence interaction specificities of aflatoxin B1, aflatoxicol, aflatoxin M1, and aflatoxicol M1 with purified DNA

The covalent binding of the activated forms of several aflatoxins to N-7 of guanine residues on purified DNA has been studied. The aflatoxins include aflatoxin B1 (AFB1) and two human metabolites, aflatoxicol and aflatoxin M1, along with aflatoxicol M1, a rabbit and trout metabolite. DNA binding studies using tritiated [3H]aflatoxins indicate that equimolar solutions of each aflatoxin upon activation with chloroperoxybenzoic acid readily react to produce covalently bound adducts. These reactions produce alkali-labile sites which can be identified using a simple variation of the Maxam-Gilbert sequencing procedure. Two DNA fragments were exposed to each aflatoxin, and the reaction intensities at 33 guanine residues were determined. As much as 10-fold variation in reaction intensities was observed for various guanyl sites. Data indicate that none of the aflatoxins had identical reaction profiles, although AFB1 and aflatoxicol M1 were similar, as were aflatoxicol and aflatoxin M1. Hence, the frequency with which the various aflatoxin epoxides might damage specific sites critical for tumor initiation in vivo would not be predictable from total covalent binding indices. The frequency of occurrence of modifications at particular sites for AFB1 was also compared with the empirical "rules" established for AFB1 by Misra et al. (Misra, R. P., Muench, K. F., and Humayun, M. Z. (1983) Biochemistry 22, 3351-3359). Identical sites within fragments were compared for each aflatoxin, and the data showed that the attacking frequency for some such sites varied significantly. These results indicate that binding intensity rules based on nearest neighbor nucleotides do not reliably predict guanyl-AFB1 binding frequencies.     

Mutagenicity of some intercalating agents in Chinese hamster V79 cells

ICR 170 and ICR 191, but not 9-aminoacridine or chloroquine, induced both 6-thioguanine- and, to a smaller extent, ouabain-resistance in Chinese hamster V79 cells. These results indicate that covalent binding to DNA is necessary for intercalating agents to induce mutation in this cell line, and that this assay can distinguish potential carcinogens from non-carcinogenic analogues of this chemical type. The induction of ouabain-resistance by both ICR 170 and ICR 191 indicates that these frameshift mutagens induce base-pair substitution to some extent in V79 cells.