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In the inhalation system described an animal can be kept in the same atmosphere of a 2-liter desiccator for up to 24 h. The expired carbon dioxide is adsorbed with soda lime and the resulting reduced pressure is balanced by a supply of oxygen also used for the inflow of the chemical to be investigated. Urine and faeces can be collected ~eparately and the system allows a periodical control of the concentration of the chemical by sampling the air with needle and syringe.
It is shown by means of IR. spectroscopic methodsthat nigericin and monensin bave a cyclic conformation similar to that of their silver salts. Camplex fonnation constants with sodium and potassium ions follow the selectivity order determined by EMF. measurements on liquid membranes: nigericin: K\(^+\) >Rb\(^+\)> Na\(^+\)> Cs\(^+\) >Li\(^+\); monensin: Na\(^+\)> K\(^+\) >Li\(^+\)> Rb\(^+\)> Cs\(^+\). Transport experiments show that nigericin and monensin facilitate the diffusion of potassium ions across model membranes, although in electrolytic transport experiments the permeability is not affected.
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.
The intake of known dietary carclnogens was compiled and the cancer risk was estlmated on the basis of carcinogenic potencies in animals as derived from the Carcinogenic Potency Database by Gold and co-workers. The total cancer risk was compared with the number of cancer cases attributed by epidemiologists to dietary factors (one-third of all cancer cases, i.e. -80 000 per one million Jives). Except for alcohol, the known dietary carcinogens could not account for more than a few bundred cancer cases. Tbis was seen both with tbe DNA-reactive carcinogens (beterocyclic aromatic amines, polycyclic aromatic hydrocarbons, N-nitroso compounds, estragole, aflatoxin B., ethyl carbamate, to name the most important factors) as wen as with those carclnogens wbich have not been shown to react with DNA (e.g. caffelc acid and the carcinogeruc metals arsenic and cadmium). Residues and contaminants turned out to be negligible. Among the various pmsibilities to explain the discrepancy we investigated the roJe of ovemutritlon. Dietary restriction in animals is weil known for its strong reducing effect on spontaneous tumor formation. These data can be used to derive a carcinogenic potency for excess macronutrients: tbe tumor incidence seen with the restrlcted animals is taken as a control value and the increased tumor incidence in the animals fed ad libitum is attributed to the additional feed iotake. For excess standard diet in rats, a carcinogenic potency TD50 of 16 glkg/day was deduced from a recent study. Ovemutrition in Switzerland, estimated to be 5.5 kcallkg/day, was converted to excess food (1.9 g/kg/day) and tbe cancer incidence was calculated. The result, 60 000 cancer cases per one million Jives, is provocatively close to the number of cases not explained by the known dietary chemical carcinogens. Mechanistic studies will be required to test our hypothesis and investigate the role of different types of macronutrients in ovemutrition.
The covalent binding of tritiated benzo(a)pyrene (BP) to DNA has been determined in rat liver in vivo, in rat liver perfused in situ, after incubation of BP with liver single cells, with liver homogenate, with liver microsomes and DNA, with fibroblasts from a rat granulorna pouch, and with · 2 cell lines. Li ver single cells were found to be a valuable compromise between the rnost sensitive system (microsomal incubation of BP with DNA) and the biologically most relevant system (in vivo ).
Fernale BALB/c mice were administered intragastrically with equimolar amounts of either [2-\(^{14}\)C]2-amino-3,8-dimethyi[ 4,5-J]qulnoxaline (MeiQx) or 2-acetylamino[9-\(^{14}\)C]fluorene (2AAF). DNA was isolated from tissues of mice killed either 6 or 24 h after administration. Analysis of liver DNA nucleotide digests by HPLC analysis revealed that all of the radioactivity was attributable to adduct formation. Tbe specific activities of DNA samples were converted to covalent bindlog indices (CBI, J.LIDOI adduct per mol DNA nucleotides/mmol chemical app6ed per kg animal body weight). CBI values of 25 and 9 were detennined for 2AAF and MeiQx in tbe llvers of mice killed 6 h after dosing. The values were in general agreement with the moderate carcinogenic potency of these compounds. The specific activities of DNA preparations obtained from the lddneys, spleens, stomachs, small intestines and large intestlnes of mice treated witb MeiQx and killed 6 h after doslng were S- to 35-times less tban those obtained witb the llver. DNA isolated from tbe lungs (a target organ for MeiQx tumorigenicity) of MeiQx-treated mice was not radiolabeUed at tbe limit of detection (CBI <0.3). With tbe exception of tbe gastrolntestinal tract, the specific activities of DNA samples isolated from mice killed 6 h after administration were higher than those from mice killed after 24 h.
Male Fischer F-344 rats were given ethanol in the drinking water and/or by single oral administration. Following this, the animals received p.o. 100 ng/kg of the hepatocarcinogen eHJaflatoxin BI (AFBI)' 24 h later, the level of DNA-bound AFBI was determined in the liver and was found not to be affected by any type of ethanol pretreatment. A cocarcinogenic effect of ethanol in the liver is therefore unlikely to be due to an effect on the metabolic activation and inactivation processes governing the formation of DNA-binding AFBI metabolites.
Thecovalent bindingof [6,7-\(^3\)H]ethinylestradiol (EE)and [6,7-\(^3\)H]estrone (E) to liver DNA of 200 g female ratswas measured 8 h after the administration of 80 \(\mu\)g (9.2 mCi) estrogen by gavage. The binding is 1.5 for EE and 1.1 for E, expressedas binding to DNA/dose, in units of \(\mu\)mol hormonefmol DNA phosphate/mmole honnone/kg body wt. It is in the same order of magnitude as for benzene and about 10 000 tim es below the binding of typical liver carcinogens, such as aflatoxin B\(_1\) or N,N-dimethylnitrosamine.
The structure of monensin, C36H620 11 , has been deterrnined by X-ray analysis of its crystalline monohydrate (orthorhombic, a = 15.15, b = 23.61, c = 10.65 A, Z = 4, space group P212121). Phases were assigned by direct methods, malring use of the 'tangent formula'. Although the conformation of the free acid resembles that of the silver salt in being cyclic, there are differences in the hydrogen bonding pattern. These featurcs are discussed in relation to the cornplexation of metal ions by m.onensin.
'lbe mouse skin tumor model was used to investigate whether the Ievel of DNA 8dducts and/or the rate of cell division in the epidermis are indicators of the risk of cancer formation for an individual in an outbred animal popul8tion. A high risk was considered to be reftected by 8 short latency period for the 8ppearance of 8 papilloma. Fernale NMRI mice were treated twice weekly with 2.5 nmol 7 ,12-dimethylbenz[a]antbracene (DMBA) and 3 nmoi12-0-tetradecanoylphorbol-13- 8cetate (TPA) and the appearance of papillomas was registered. The first papilloma 8ppeared after 7.5 weeks. After 17 weeks, when 12 of 14 mice bad 8t least one papilloma, an osmotic minipump deliverlog 5-bromo-2'deoxyuridine (BrdU) was implanted into eacb mouse for 24 h. The mice were killed after 24 h ~d the epidermis was analyzed for D:MBA-nucleotide 8dducts by 32p.postlabeling, for the cell number per unit skin length, and for the labeling index for DNA synthesls. Unexpectedly, D:MBA-nucleotide 8dduct Ievels were highest in those anima1s wbich showed the Iongest latency periods. Adduct Ievels were negatively correlated with the 18beling index, indicating that dilution of adducts by cell division was a predominant factor in determining average adduct concentrations. Individual tumor-latency time was not corTelated with either cell ntunber or labeling index. This could be due to the fact that the measurements only provided 8veraged data and gave no infonnation on the specific situation in clones of premalignant cells. Under the conditions of tbis assay, therefore, neither DNA adduct Ievels nor information on the average kinetics of cell division bad a predidive value for the individual amcer risk withln a group of outbred animals receiving the same treatment
DNA Methylation in Rat Li ver by Daminozide, 1, 1-Dimethylhydrazine, and Dimethylnitrosamine. SAGELSDORFF, P., LUTZ, W. K., AND ScHLAITER C. (1988). Fundam. Appl. Toxico/. 11, 723-730. [methyP4C]Daminozide (succinic acid 2',2'-dimethylhydrazide; 37 mgjkg), l,l( 14C]dimethylhydrazine (UDMH; 19 mgtkg), and (14C]dimethylnitrosamine (DMNA; 0.1 mg/ kg) were administered by oral gavage to male Sprague-Dawley rats. After 24 hr, the animals were killed and DNA was purified from the livers to constant specific radioactivity. After enzymatic degradation of the DNA to the 3'-deoxynucleotides the Ievel of DNA methylation was determined by HPLC analysis. Radiolabeled 7-methylguanine (7mG) was identified by cochromatography with unlabeled 7mG added as standard after acidic depurination of DNA and HPLC analysis ofpurines and apurinic acid. All three compounds were found to methylate DNA. The relative potencies were 1:47:4900 for daminozide:UDMH:DMNA. With [methyPH]UDMH, the formation of7mG was investigated as a function of dose administered, at 20, 2, and 0.2 mgj kg. The methylation ofDNA was strictly proportional to the dose. The data were used to compare the Ievel of DNA alkylation derived from residues of daminozide and UDMH in treated apple with the genotoxicity of the intake of N-nitroso compounds in Germany and Japan. It is estimated that these residues could Iead to a DNA methylation in the Ii ver of about 6% of an average exposure to DMNA
The formation of \(O^6\)-methyldeoxyguanosine (\(O^6\)-MedGuo) was determined by an immuno-slot-blot assay in DNA of various tissues of F344 rats exposed to N-methyl-N-nitrosourea (MNU) in the drinking waterat 400 ppm for 2 weeks. Although the pyloric region of the glandular stomach is a target organ under these experimental conditions, the extent of DNA methylation was highest in the forestomach (185 \(\mu\)mol \(O^6\)-MedGuojmol guanine). Fundus (91 J.!moljmol guanine) and pylorus (105 J.!moljmol guanine) of the glandular stomach, oesophagus (124 \(\mu\)mol/mol guanine) and duodenum (109 )lmoljmol guanine) showed lower Ievels of \(O^6\) - MedGuo but differed little between each other. Thus, no correlation was observed between target organ specificity and the extent of DNA methylation. This is in contrast to the gastric carcinogen, N-methyl-N'-nitro-N-nitrosoguanidine (MNNG), which preferentially alkylates DNA of the pylorus, the main site of induction of gastric carcinomas by this chemical. In contrast to MNU, the nonenzymic decomposition of MNNG is accelerated by thiol compounds (reduced glutathione, L-cysteine), which are present at much higher concentrations in the glandular stomach than in the forestomach and oesophagus. During chronic exposure to MNNG (80 ppm), mucosal cells immunoreactive to 0 6-MedGuo are limited to the luminal surface [Kobori et al. (1988) Carcinogenesis 9:2271-2274]. Although MNU (400 ppm) produced similar Ievels of \(O^6\)-MedGuo in the pylorus, no cells containing methylpurines were detectable by immunohistochemistry, suggesting a more uniform methylation of mucosal cells by MNU than by MNNG. After a single oral dose of MNU (90 mg/kg) cells containing methylpurines were unequivocally identified using antibodies to \(O^6\)-MedGuo and the imidazole-ring-opened product of 7-methyldeoxyguanosine. In the gastric fundus, their distribution was similar to those methylated by exposure to MNNG, whereas the pyloric region contained immunoreactive cells also in the deeper mucosallayers. After a 2-week MNU treatment, the rate of cell proliferation, as determined by bromodeoxyuridine immunoreactivity, was only slightly enhanced in the oesophagus andin the fundus, but markedly in the forestomach and the pyloric region of the glandular stomach. lt is concluded that the overall extent of DNA methylation, the distribution of alkylated cells within the mucosa and the proliferative response all contribute to the organ-specific carcinogenicity of MNU.
Dose-response relationship and low dose extrapolation in chemical carcinogenesis [commentary]
(1990)
Data supporting various dose-respome relationships in chemical carcinogenesis are summarized. General principles are derived to explain the relationships between exposure dose, JI>NA adduct Ievel, induction of genetic changes, and tumor incidence. Some mechanistic aspects of epigenetic carcinogens (stimulation of ceU division and maldlfl'erentlation) are analyzed in a similar way. In a bomogeneous pnpulation, non-linearities are frequent. They are due to pbenomena of induction or saturation of enzymatic activities and to the multi-step nature of carcinog~: if a carcinogen acce1erates more than one step, the SUperposition of the dose- response curves for the indJvidual steps can result in an exponential relationship. A fourth power of the dose was the maximum seen in animals (fonnaldehyde). At the lowest dose Ievels, a proportionality between dose and tumor induction is postulated independent of the mechanism of action if the carcinogen aceeierotes the endogenous proass responsible for spootaneous tumor formation. Low-dose thresholds are expected only for situations where the carcinogen acts in a way that has no endogenous counterpart. Epidemiologfcal studies in humans show linear dose- response curves in all but two investigations. The difference from the strongly nonlinear slopes ·seen in animal studies could be due to the heterogeneity of the human population: if the individual sensitivity to a carcinogen is governed by a large number of genetic and Iife-style factors, the non-linea.rities will tend to cancel each other out and the dose- response curve becomes 'quasi-linear'.
Ich habe versucht darzulegen, daß mechanistische Überlegungen zur Extrapolation der Dosis-WirkungsBeziehung herangezogen werden können. Ein nichtlinearer Verlauf ist nicht nur bei den epigenetischen Kanzerogenen wahrscheinlich, sondern auch bei den DNA-bindenden. Echte Schwellen sind aber nur in solchen Fällen zu erwarten, wo kein endogenes Korrelat besteht. Immerhin können auch steile Nichtlinearitäten zu einer drastischen Risikoreduktion führen, so daß die Anstrengungen dahin gehen sollten, die Steigung und den Bereich des überproportionalen Abfalls experimentell zu zeigen. In einer heterogenen Population kann die 0 0- sis-Wirkungs-Kurve zusätzliche "Wellen" bekommen und wird dadurch grundsätzlich flacher. Im Extremfall ergibt sich eine lineare Dosis-Wirkungs-Beziehung unabhängig vom Wirkmechanismus des Kanzerogens. Diese Proportionalität zwischen tiefster Dosis und Effekt wird bei genotoxischen Kanzerogenen aus mechanistischen Gründen schon für eine homogene Population postuliert, doch kann dies in einer heterogenen Population auch bei epigenetischen Kanzerogenen in Frage kommen.