Refine
Has Fulltext
- yes (82)
Is part of the Bibliography
- yes (82)
Year of publication
Document Type
- Journal article (69)
- Book article / Book chapter (6)
- Conference Proceeding (5)
- Review (2)
Keywords
- Toxikologie (68)
- DNA (7)
- Carcinogen (5)
- DNA binding (5)
- Genotoxicity (5)
- Carcinogenesis (3)
- Carcinogens (3)
- Ernährung (3)
- Medizin (3)
- Aflatoxin (2)
The covalent binding of [3H]aflatoxin B1 (AF) to liver DNA was determined, 6 h after oral administration to male rabbits. A Covalent Binding Index, CBI (flmol AF/mol DNA-P)/(mmol AF/kg b. w.) = 8,500 was found. Pretreatment of rabbits with AF coupled to bovine serum albumin in Freund's adjuvant led to the production of AF-directed antibodies. Administration of [3H]AF to such immunized rabbits resulted in a CJH of only 2,500, i.e., the iiDJ{.lUnization provided a protection by a factor of more than 3. Although this is encouraging evidence for the potential of active immunization against genotoxic carcinogens, a nurober of pointswill have to be clarified, such as the time course for the DNA binding and the question of a possible shift to other target cells.
(6,7-\(^3\)H] Estrone (E) and [6,7-\(^3\)H]estradiol-17ß (E\(_2\)) have been synthesized by reduction of 6-dehydroestrone and 6-dehydroestradiol with tritium gas. Tritiated E and E\(_2\) were administered by oral gavage to female rats and to male and female hamsters on a dose level of about 300 \(\mu\)g/kg (54 mCi/kg). After 8 h, the liver was excised from the rats; liver and kidneys were taken from the hamsters. DNA was purified either directly from an organ homogenate or via chromatin. The radioactivity in the DNA was expressed in the units of the Covalent Binding Index, CBI = (\(\mu\)mol chemical bound per mol Similar considerations can be made for the liver where any true covalent DNA binding must be below a Ievel of 0.01. It is concluded that an observable tumor induction by estrone or estradiol is unlikely to be due to DNA binding. DNA-P)/(mmol chemical administered per kg b.w.). Rat liver DNA isolated via chromatin exhibited the very low values of 0.08 and 0.09 for E and E\(_2\) respectively. The respective figures in hamster liver were 0.08 and 0.11 in females and 0.21 and 0.18 in the males. DNA isolated from the kidney revealed a detectable radioactivity only in the female, with values of 0.03 and 0.05 for E and E\(_2\) respectively. The values for male hamster kidney were < 0.01 for both hormones. The minute radioactivity detectable in the DNA samples does not represent covalent binding to DNA, however, as indicated by' two sets of control experiments. (A) Analysis by HPLC of the nucleosides prepared by enzyme digest of liver DNA isolated directly or via chromatin did not reveal any consistent peak which could have been attributed to a nucleoside-steroid adduct. (B) All DNA radioactivity could be due to protein contaminations, because the specific activity of chromatin protein was determined to be more than 3 ,000 tim es high er than of DNA. The high affinity of the hormone to protein was also demonstrated by in vitro incubations, where it could be shown that the specific activity of DNA and protein was essentially proportional to the concentration of radiolabelled hormone in the organ homogenate, regardless of whether the animal was treated or whether the hormone was added in vitro to the homogenate. Carcinogens acting by covalent DNA binding can be classified according to potency on the basis of the Covalent Binding Index. Values of 10\(^3\)-10\(^4\) have been found for potent, 10\(^2\) for moderate, and 1-10 for weak carcinogens. Since estrone is moderately carcinogenic for the kidney of the male hamster, a CBI of about 100 would be expected. The actually measured Iimit of detection of 0.01 places covalent DNA binding among the highly unlikely mechanisms of action.
The aim of this study was to determine whether o-chlorobenzylidene malononitrile ( CS) exhibits any genotoxic activity towards Salmonella or mammalian DNA in vivo. CS was synthesized with a [\(^{14}\)C]-label at the benzylic carbon atom. It was administered i. p. at a dose level of 13 mg/kg (1 mCi/kg) to young adult male rats. Liverand kidney DNA was isolated after 8, 25, and 75 h. The radioactivity was at (liver, 8 and 75 h) or below (all other samples) the limit of detection of 3 dpm. Therefore, a possible binding of CS to DNA is at least 10\(^5\) times lower than that of the strong hepatocarcinogen aflatoxin B1, and 4,000 times lower than that of vinyl chloride. In contrast to this lack of DNA binding, but in agreement with the chemical reactivity of CS, a binding to nuclear proteins could be detected with specific activities ranging between 50 and 121 dpm/mg for liver and between 3 and 41 dpm/mg for kidney. Protein binding could well be responsible for its pronounced cytotoxic effects. Cs was also tested in the Ames Salmonella/microsome assay. Strains TA 1535, TA 1537, TA 1538, TA 98, and TA 100 were used with or without pre-incubation. Only with strain TA 100 and only without pre-incubation, a doubling of the number of revertants was detectable at the highest dose Ievels used, 1,000 and 2,000 !lg CS per plate. With pre-incubation of TA 100 with CS, a slight increase of the number of revertants was seen at 100 and 500 !lg per plate, and a subsequent fall below control values at 1,000 J.tg. A check for the number of surviving bacteria revealed a strong bacteriotoxicity of the higher doses of es so that the calculated mutation frequencies, i.e., the oumber of revertants per number of surviving bacteria, increased with doses up to 500 !J.g. This toxicity could be counteracted in part by the addition of increasing amounts of rat liver microsomes. In the view of these results, and taking into account the rare and low exposure of man, it is concluded that CS will not create a risk for the induction of point mutations or of carcinogenic processes mediated by DNA binding.
Investigation of the Potential for Binding of Di(2-ethylhexyl) Phthalate (DEHP) and Di(2- ethylhexyl) Adipate (DEHA) to Liver DNA in Vivo. VON DÄNIKEN, A., LUTZ, W. K., JÄCKH, R., AND ScHLATTER, C. (1984). Toxico/. App/. Pharmaco/. 73, 373-387. It was the aim oftbis investigation to determine whether covalent binding of di(2-ethylhexyl) phthalate (DEHP) to rat liver DNA and of di(2-ethylhexyl) adipate (DEHA) to mouse liver DNA could be a mechanism of action contributing to the observed induction of liver tumors after lifetime feeding of the respective rodent species with high doses of DEHP and DEHA. For this purpose, DEHP and DEHA radiolabeled in different parts of the molecule were administered orally to female rats and mice, respectively, with or witbout pretreatment for 4 weeks with 1% unlabeled compound in the diet. Liver DNA was isolated after 16 hr and analyzed for radioactivity. The data were converted to a covalent binding index, CBI = (micromoles of substance bound per mole of DNA nucleotides)/(millimoles of substance applied per kilogram body weight), in order to allow a quantitative comparison also with other carcinogens and noncarcinogens. Administration of [\(^{14}\)H]carboxylate-labeled DEHP to rats resulted in no measurable DNA radioactivity. The Iimit of detection, CBI < 0.02 was about 100 times below the CBI of compounds where an observable tumor-inducing potential could be due to genotoxicity. With [\(^{14}\)C]- and [\(^{3}\)H]DEHP labeled in the alcohol moiety, radioactivity was clearly measurable in rat liver DNA. HPLC analysis of enzyme-degraded or acid-hydrolyzed DNA revealed that the natural nucleosides or purine bases were radiolabeled whereas no radioactivity was detectable in those fractions where tbe carcinogenmodified nucleoside or base adducts are expected. The respective Iimits of detection were at 0.07 and 0.04 CBI units for the \(^{14}\)C and \(^{3}\)H Iabels, respectively. The experiments with [\(^{14}\)C]- and [\(^{3}\)H]DEHA, labeled in the alcobol moiety and administered to mice, revealed aminute radioactivity of <50 dpm/mg liver DNA, too little to allow a nucleoside analysis to determine that fraction of the radioactivity which bad been incorporated via biosynthesis. Expressed in the CBI units, values of 0.05 to 0.15 for \(^{14}\)C and 0.01 to 0.12 for \(^{3}\)H resulted. Determination of the level· of \(^{14}\)C02 expiration revealed a linear correlation with the speciftc activity of DNA. Experiments with 2-ethyl[ 1-\(^{14}\)C]hexanol perfonned with both rats and mice allowed the conclusion tbat most if not all DEHA radioactivity in mouse liver DNA was due to biosynthetic incorporation. A maximum possible true DNA binding by DEHA must be below CBI 0.01. Pretreatment of the animals witb unlabeled compound bad no effect on the DNA radioactivities in either species. The present negative data, in conjunction witb other negative short-term tests for mutagenicity, strongly indicate that covalent interaction with DNA is highly unlikely to be the mode of tumorigenic action of DEHP and DEHA in rodents.
Lack of covalent binding to rat liver DNA of the hypolipidemic drugs clofibrate and fenofibrate
(1981)
\(^{14}\)C-Labelled clofibric acid and fenofibric acid were administered p.o. to 200 g male and female rats. After 10 h, liver nuclear DNA and protein were isolated and the radioactivity was determined. Binding to protein was clearly measurable whereas no binding to DNA could be detected from any drug. A comparison of the Iimit of detection of such DNA binding with well-known chemical carcinogens revealed that the known hepatocarcinogenicity of clofibrate cannot be based upon an initiating, DNA damaging, mode of action but must be due to other, nongenotoxic, mechanisms such as peroxisome proliferation, hepatomegaly, or cytotoxicity due to protein binding. The risk assessment in man and the interpretation of the carcinogenicity data for rodents are discussed.
'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
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.