Institut für Pharmakologie und Toxikologie
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Young adult male Sprague-Dawley rats were given 30 \(\mu\)mol/kg body weight [\(^{14}\)C]methylamine hydrochloride and 700 \(\mu\)mol/ kg body weight sodium nilrite by oral gavage. DNA isolated from the stomach and from the first 15 cm of the smaß intestine was methylated, containing 7-methylguanine (7mG) at a level of one 7mG molecule per 5x10\8^6\) and lx10\(^7\) nucleotides, respectively. No 7mG was found fn the liver at a limit of detection of one 7mG molecule per 2xl0\(^8\) nucleotides. ln a second experiment, the excised stomachs were incubated with deoxyribonuclease before the isolation of the DNA in order to degrade DNA in the Iumen and in the uppermost lining cells. This treatment resulted in a 30% decrease in the yield of DNA and a 90% reduction in the level of 7mG formation. The results show that nitrosation of a primary alkylamine yields a precursor of an alkylating agent which has a long enough lifetime to diffuse towards and react with intracellular DNA. A correlation of DNA methylation in the stomach with the corresponding tumor formation by the methylating carcinogen N-methyi-N'-nitro-N-nitroso-guanidine was used to estimate the roJe of DNA damage resulting from endogenous nitrosation of dietary methylamine in man. It was concluded that the risk resulting from this single amine must be negligible bot that a similar evaluation of other primary amines is required before the over-aU role of primary amine nitrosation in the etiology of human gastric cancer can be assessed.
Formaldehydeis an electrophilic molecule able to crosslink DNA and protein. It has been found to induce tumors in the nasal epithelium in rodents. The safety margin between the maximum tolerated FA concentration in the work place and the concentration found to be tumorigenic in animal studies is very small. Because FA is produced endogenously as a result of a variety of oxidative demethylations, the assessment of the tumor risk from exogenaus FA exposure has tobe related quantitatively to the level of DNA-protein crosslinks induced by endogenaus FA generation. It is reported here that the high level of endogenaus FA formed in the liver after a large dose of methanol or of aminopyrine did not lead to any observable increase in DNA-protein crosslinks. Using positive and negative control data from in vitro incubations of liver homogenate with FA or methanol it is estimated that the endogenous level of DNA damage in the liver must be more than three orders of magnitude below the damage observed at tumorigenic concentrations for the rat nose. The fact that FA is formed endogenously cannot, therefore, be used to claim that exogenous FA merely leads to a negligible increase in DNA damage.
Investigation of covalent DNA binding in vivo provided evidence for whether a test substance can be activated to metabolites able to reach and react with DNA in an intact organism. Fora comparison of DNA binding potencies of various compounds tested under different conditions, a normalization of the DNA lesion with respect to the dose is useful. A covalent binding index, CBI = (\(\mu\)mol chemical bound per mol DNA nucleotide )/(mmol chemical administered per kg body weight) can be determined for each compound. Whether covalent DNA binding results in tumor formation is dependent upon additional factors specific to the cell type. Thus far, all compounds which bind covalently to liver DNA in vivo have also proven tobe carcinogenic in a long-term study, although the liver was not necessarily the target organ for tumor growth. With appropriate techniques, DNA binding can be determined in a dose range which may be many orders of magnitude below the dose Ievels required for significant tumor induction in a long-term bioassay. Rat liver DNA bindingwas proportional to the dose of aflatoxin B1 afteroral administration of a dose between 100 \(\mu\)g/kg and 1 ng/kg. The lowest dose was in the range of generat human daily exposures. Demonstration of a lack of liver DNA binding (CBI<0.1) in vivo for a carcinogenic, nonmutagenic compound is a strong indication for an indirect mechanism of carcinogenic action. Carcinogens of this class do not directly produce a change in gene structure or function but disturb a critical biochemical control mechanism, such as protection from oxygen radicals, control of cell division, etc. Ultimately, genetic changes are produced indirectly or accumulate from endogenaus genotoxic agents. The question of why compounds which act via indirect mechanisms are more likely to exhibitanonlinear rangein the dose-response curve as opposed to the directly genotoxic agents or processes is discussed.
It was the aim of this investigation to determine whether or not covalent binding of di(2-ethylhexyl) phthalate (DEHP) to rat liver DNA could be a mechanism of action contributing to the observed induction of liver tumors after lifetime feeding of rodents with high doses of DEHP. DEHP radiolabeled in different positionswas administered orally to female F344 rats with or without pretreatment for 4 weeks with 1% unlabeled DEHP in the diet. Livu DNA was isolated after 16 hr and analyzed for radioattivity. Administration of [\(^{14}\)C]carboxylate unabeled DEHP resulted in no measurable DNA radioactivity. With DEHP [\(^{14}\)C]· and [\(^{3}\)H]. labeled in the alcohol moiety as well as with 2-ethyl[1-\(^{14}\)C]hexanol, radioactivity was clearly measurable in the DNA. HPLC analysis of enzyme-degraded DNA relvealed that the normal nucleosides had incorporated radiolabel whereas no radioactivity was detectable in those fractions where the carcinogen-modified nucleoside adducts are expected. A quantitative evaluation of the negative data in terms of a Iimit of detection for a covalent binding Index (CBJ) indicates that covalent interaction with DNA is highly unlikely to be the mode of tumorigenic action of DEHP in rodents.
Metallothionein (MT) is a protein which contains 20 cysteine residues but no aromatic amino acids. It was tested whether treatment of male rats with the hepatocarcinogen diethylnitrosamine (DENA) could ethylate nucleic acids in such a way that protein variants containing measurable amounts of aromatic amino acid residues could be isolated from the livers of treated animals. To give a low Iimit of detection, the "wrong" amino acid precursors were administered in radiolabelled form at high Ievels of activity (7 mCi/kg each of [\(^3\)H]tyrosine and [\(^3\)H]phenylalanine). 11 \(\mu\)Ci/kg [\(^{14}\)C]cysteine was given as an intemal marker for MT biosynthesis. 6 h after amino acid administration, metallothionein (MT) was isolated from the liver and extensively purified. Afteracid hydrolysis and collection of Cys, Tyr, and Phe from an HPLC analysis of the amino acids, the \(^3\)H/\(^{14}\)C ratio was determined. The carcinogen-treated rats exhibited a significantly higher ratio than the vehicle-treated animals. This type of in vivo assay might find interesting applications in the investigation of nucleic acid alkylations as promutagenic lesions.
To date, all risk assessment studies on benzene have been based almost exclusively on epiderniological data. Wehave attempted a more integrated and quantitative evaluation of carcinogenic risk for hurnans, trying to utilize, in addition to the epidemiological data, all data available, specifically data on metabolism, genotoxicity, and carcinogenicity in small rodents. An integrated evaluation of the globality of the available data seems to suggest a progressive saturation of metabolic capacity both for man and rodents between 10 and 100 ppm. The most susceptible target cells seem tobe different in humans (predominant induction of myelogenous leukemia) and small rodents (induction of a wide variety of tumors). Nevertheless, both epidemiological and experimental carcinogenicity data tend to indicate a flattening ofthe response for the highest dosages, again suggesting a general Saturation of mechanisms of metabolic activation, extended to different target tissues. From a quantitative point of view, the data suggest a carcinogenic potency at 10 ppm two to three times higher than that computable by a linear extrapolation from data in the 100 ppm range. These observations are in accord with the recent proposal of the European Economic Community of reducing benzene time-weighted average occupationallevels from 10 to 5 ppm.
A literature review has shown that the daily intakes of various N -nitroso-precursor classes in a typical European diet span five orders of magnitude. Amides in the form of protein, and guanidines in the form of creatine and creatinine, are the nitrosatable groups found most abundantly in the diet, approaching Ievels of 100 g/day and 1 gjday, respectively. Approximately 100 mg of primary amines and amino acids are consumed daily, whereas aryl amines, secondary amines and ureas appear to lie in the 1-10 mg range. The ease of nitrosation of each precursor was estimated, the reactivities being found to span seven orders of magnitude, with ureas at the top and amines at the bottom of the scale. From this infonnation and an assessment of the carcinogenicity of the resulting N-nitroso derivatives, the potential health risk due to gastric in vivo nitrosation was calculated. The combined effects of these risk variables were analysed using a simple mathematical model: Risk = [daily intake of precursor] x [gastric concentration of nitrite]\(^n\) x [nitrosatability rate constant} x [carcinogenicity of derivative]. The risk estimates for the various dietary components spanned nine orders of magnitude. Dietary ureas and aromatic amines combined with a high nitrite burden could pose as great a risk as the intake of preformed dimethylnitrosamine in the diet. In contrast, the risk posed by the in vivo nitrosation of primary and secondary amines is probably negligib1y small. The risk contribution by amides (including protein), guanidines and primary amino acids is intermediate between these two extremes. Thus three priorities for future work are a comprehensive study of the sources and Ievels of arylamines and ureas in the diet, determination of the carcinogenic potencies of key nitrosated products to replace the necessarily vague categories used so far, and the development of short-term in situ tests for studying the alkylating power or genotoxicity of N-nitroso compounds too unstable for inclusion in long-term studies.
Emodin (1,6,8-trihydroxy-3-methylanthraquinone), an important aglycone found in natural anthraquinone glycosides frequently used in Iaxative drugs, was mutagenic in the Salmonellajmammalian microsome assay (Ames test) with a specificity for strain TA1537. The mutagenic activity was activationdependent with an optimal amount of S9 from Aroclor 1254-treated male Sprague-Dawley rats of 20% in the S9 mix (v jv) for 10 p.g emodin per plate. Heat inactivation of the S9 for 30 min at 60 ° 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 p.g 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- \(^{3}\)H]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 = (p.moles chemical bound per moles DNA nucleotides)/(mmoles chemical administered per kg body weight) of 0.5 is deduced. This is 104 times below the CBI of AFB1. The demonstration of a lack of covalent interaction with DNA bothin Salmonellaandin rat liver is discussed in terms of a reduced hazard posed by emodin as a mutagenic drug in use in humans.
In order to investigate whether the Stimulation of liver DNA synthesis might be used to detect one class of hepatic tumor promoters, the incorporation of orally administered radiolabelled thymidine into liver DNA was detennined in rats and mice 24 h after a single oral gavage of test compounds at various dose Ievels. Three DNA-binding hepatocarcinogens, aflatoxin B1; benzidine and carbon tetrachloride, did not stimulate but rather inhibited DNA synthesis (not for CCla). Four hepatic tumor promoters, clofibrate, DDT, phenobarbital and thioacetamide, gave rise to a Stimulation in a dosedependent manner. Single oral doses between 0.02 and 0.3 mmol/kg were required to double the level of thymidine incorporation into liver DNA (= doubling dose, DD). Differentes between species or sex as obsprved in long-term carcinogenicity studies were reflected by a different stimulation of liver DNA synthesis. In agreement with the bioassay data, aldrin was positive only in male mice (DD = 0.007 mmol/kg) but not in male rats or female mice. 2,3, 7,8-TCDD was positive in male mice (DD = 10\(^{-6}\) mmol/kg) andin female rats (DD = 2 x 10\(^{-6}\) mmol/kg) but not in male rats. The assay was also able to distinguish between structural isomers with different carcinogenicities. [alpha]Hexachlorocyclohexane stimulated Iiver DNA synthesis with a doubling dose of about 0.2 mmol/kg in male rats whereas the [gamma]isomer was ineffective even at l mmol/kg. So far, only one result was inconsistent with carcinogenicity bioassay data. The different carcinogenicity of di(2-ethylhexyl)adipate (negative in rats) and di(2-ethylhe.xyl)phthalate (positive) was not detectable. 8oth plasticizers were positive in.this short-term system with DD's of 0. 7 mmol/kg for DEHA and 0.5 mmol/kg for DEHP. The proposed assay is discussed as an attempt to devise short-term assays for carcinogens not detected by the routine genotoxicity test systems.
DNA binding in vivo: (6,7-\(^3\)H]ß-trenbolone (ß-TBOH) was administered p.o. and i.p. to rats. After 8 or 16 h, DNA was isolated from the livers and purified to constant specific radioactivity. Enzymatic digestion to deoxyribonucleotides and separation by HPLC revealed about 90% ofthe DNA radioactivity eluting in the form of possible TBOH-nucleotide adducts. The extent of this genotoxicity, expressed in units of the Covalent Binding Index, CBI = (~mol TBOH bound per mol nucleotide)/(mmol TBOH administered per kg body weight) spanned from 8 t~ 17, i. e. was in the range found with weak genotoxic carcmogens. Ames test: low doses of ß-TBOH increased the number of revertants in Salmonella strain TAl 00 reproducibly and m a dose-dependent manner. The mutagenic potency was 0.2 revertants per nmol after preincubation of the bacteria (20 min at 37° C) with doses between 30 and 60 \(\mu\)g per plate (47 and 94 \(\mu\)g/ml preincubation mixture). Above this dose, the number of revertants decreased to control values, accompanied by a reduction in survival. The addition of rat liver S9 inhibited the mutagenicity. DNA binding in vitro: calf thymus DNA was incubated with tritiated ß-TBOH with and without rat liver S9 Highest DNA radioactivities were determined in the absence of the "activation" system. Addition of inactive S9 (without cofactors) reduced the DNA binding by a factor of up to 20. Intermediate results were found with active S9. DNA binding in Salmonella: ß-TBOH was irreversibly bound to DNA isolated from S. typhimurium TA100 after incubation of bacteria with [\(^3\)H]ß-TBOH. Conclusions: Covalent DNA binding appears to be the mechanism of an activation-independent ("direct") mutagenicity of TBOH which is not easily detected because of the bactericidal activity. The genotoxicity risk arising from exposure of humans to trenbolone residues in meat was estimated using the in vivo data and compared to that from the exposure to unavoidable genotoxins aflatoxin B1 and dimethylnitrosamine. It ts concluded that trenbolone residues represent only a low genotoxic risk.