TY  - JOUR
A1  - Baertsch, A.
A1  - Lutz, Werner K.
A1  - Schlatter, C.
T1  - Effect of inhalation exposure regimen on DNA binding potency of 1,2-dichloroethane in the rat
N2  - 1 ,2-Dichloroethane (DCE) was reported to be carcinogenic in rats in a long-tenn bioassay using gavage in com oil (24 and 48 mg/kg/day), but not by inhalation (up to 150-250 ppm, 7 h/day, 5 days/week). The daily dose metabolized was similar in the two experiments. In order to address this discrepancy, the genotoxicity of DCE was investigated in vivo under different exposure conditions. Fernale F-344 rats (183-188 g) were exposed to [1,2-14C]DCE in a closed inhalation chamber to either a low, constant concentration (0.3 mg/l = 80 ppm for 4 h) or to a peak concentration (up to 18 mg/1 = 4400 ppm) for a few minutes. After 12 h in the chamber, the dose metabolized under the two conditions was 34 mg/kg and 140 mg/k:g. DNA was isolated from liver and lung and was purified to constant specific radioactivity. DNA was enzymaticaBy hydrolyzed to the 3' -nucleotides which were separated by reverse phase HPLC. Most radioactivity eluted without detectable or with little optical density' indicating that the major part of the DNA radioactivity was due to covalent binding of the test compound. The Ievel of DNA adducts was expressed in the dose-nonnalized units ofthe Covalent Binding Index, CBI = f.Lmol adduct per mol DNA nucleotide/ mmol DCE per kg body wt. In liver DNA, the different exposure regimens resulted in markedly different CBI values of 1.8 and 69, for "constant-low" and ''peak" DCE exposure Ievels. In the Jung, the respective values were 0.9 and 31. It is concluded that the DNA darnage by DCE depends upon the concentration-time profile and that the carcinogenic potency determined in the gavage study should not be used for low-Ievel inhalation exposure.
KW  - Toxikologie
KW  - 1
KW  - 2-Dichloroethane
KW  - Carcinogens
KW  - DNA
KW  - binding
KW  - Rat
KW  - Inhalation
KW  - Dose response
Y1  - 1991
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-60743
ER  - 
TY  - JOUR
A1  - Bösch, R.
A1  - Friederich, U.
A1  - Lutz, Werner K.
A1  - Brocker, E.
A1  - Bachmann, M.
A1  - Schlatter, C.
T1  - Investigations on DNA binding in rat liver and in Salmonella and on mutagenicity in the Ames test by emodin, a natural anthraquinone
N2  - 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.
KW  - Toxikologie
KW  - DNA binding
KW  - (Rat liver)
KW  - (Salmonella)
KW  - Ames test
KW  - Emodin
KW  - Anthraquinone glycosides
KW  - natural
Y1  - 1987
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-60913
ER  - 
TY  - JOUR
A1  - Caviezel, M.
A1  - Lutz, Werner K.
A1  - Minini, U.
A1  - Schlatter, C.
T1  - Interaction of estrone and estradiol with DNA and protein of liver and kidney in rat and hamster in vivo and in vitro
N2  - (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.
KW  - Toxikologie
KW  - Estrogen
KW  - Hormone
KW  - Carcinogenesis
KW  - DNA binding
KW  - Protein binding
KW  - Estrone
Y1  - 1984
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-60995
ER  - 
TY  - JOUR
A1  - Däniken, A. von
A1  - Friederich, U.
A1  - Lutz, Werner K.
A1  - Schlatter, C.
T1  - Tests for mutagenicity in Salmonella and covalent binding to DNA and protein in the rat of the riot control agent o-chlorobenzylidene malononitrile (CS)
N2  - 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.
KW  - Toxikologie
KW  - o-Chlorobenzylidene malononitrile
KW  - Riot control agents
KW  - DNA Binding
KW  - Salmonella/microsome assay
KW  - Carcinogens
KW  - Mutagens
Y1  - 1981
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-61073
ER  - 
TY  - JOUR
A1  - Däniken, A. von
A1  - Lutz, Werner K.
A1  - Jäckh, R.
A1  - Schlatter, C.
T1  - Investigation of the potential for binding of Di(2-ethylhexyl) phthalate (DEHP) and Di(2-ethylhexyl) adipate (DEHA) to liver DNA in vivo
N2  - 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.
KW  - Toxikologie
Y1  - 1984
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-61004
ER  - 
TY  - JOUR
A1  - Däniken, A. von
A1  - Lutz, Werner K.
A1  - Schlatter, C.
T1  - Lack of covalent binding to rat liver DNA of the hypolipidemic drugs clofibrate and fenofibrate
N2  - \(^{14}\)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.
KW  - Toxikologie
Y1  - 1981
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-61087
ER  - 
TY  - JOUR
A1  - Jaggi, W.
A1  - Lutz, Werner K.
A1  - Lüthy, J.
A1  - Zweifel, U.
A1  - Schlatter, C.
T1  - In vivo covalent binding of aflatoxin metabolites isolated from animal tissue to rat-liver DNA
N2  - Ring-labelled [\(^{14}\)C)aflatoxin B\(_1\) (AFB\(_1\)), prepared by biosynthesis. or generally labelled [\(^3\)H]AFB\(_1\) was administered by oral gavage to young adult male rats. After 6 hr. the liver was removed and two fractions were isolated, namely macromolecules, which contamed about 3 % of the initial dose of AFB\(_1\) radioactivity. and water-soluble, low-molecular aftatoxin conjugates containing about0·2% of the administered radioactivity. These two fractions were administered orally to other rats in order to determine the potential of radioactive aftatoxin residues for covalent binding to DNA. Such binding can be used as an indicator for carcinogenic potency. Liver DNA was isolated 9-12 hr after admmistration of the aflatoxin derivatives and in no case was any radioactivity detected on the DNA. It can be deduced on the basis of the limit of detection of radioactivity on the DNA, that macromolecule bound AFB\(_1\) derivatives are at least 4000 times less active than AFB\(_1\) with respect to covalent binding to rat-liver DNA. and that the water-soluble conjugates are at least 100 times less potent than AFB, itself. It is concluded that the carcinogenic risk for humans who consume liver or meat. containing such aflatoxin residues is negligible when compared with the risk from intake of aftatoxins in other food items.
KW  - Toxikologie
Y1  - 1980
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-61101
ER  - 
TY  - JOUR
A1  - Jaggi, W.
A1  - Lutz, Werner K.
A1  - Schlatter, C.
T1  - Comparative studies on the covalent binding of the carcinogen benzo(a)pyrene to DNA in various model systems
N2  - 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 ).
KW  - Toxikologie
Y1  - 1979
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-61131
ER  - 
TY  - JOUR
A1  - Jaggi, W.
A1  - Lutz, Werner K.
A1  - Schlatter, C.
T1  - Covalent binding of ethinylestradiol and estrone to rat liver DNA in vivo
N2  - 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.
KW  - Toxikologie
Y1  - 1978
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-61162
ER  - 
TY  - JOUR
A1  - Kugler-Steigmeier, M. E.
A1  - Friederich, U.
A1  - Graf, U.
A1  - Lutz, Werner K.
A1  - Maier, P.
A1  - Schlatter, C.
T1  - Genotoxicity of aniline derivatives in various short-term tests
N2  - Various substituted aniline derivatives were tested for genotoxicity in several short-term tests in order to examine the hypothesis that a Substitution at both ortho positions (2,6-disubstitution) could prevent genotoxicity due to steric hindrance of an enzymatic activation to electrophilic intermediates. In the Salmonellajmicrosome assay, 2,6-dialkylsubstituted anilines and 2,4,6-trimethylaniline (2,4,6-TMA) were weakly mutagenic in strain TA100 when 20% S9 mixwas used, although effects were small compared to those of 2,4-dimethylaniline and 2,4,5-trimethylaniline (2,4,5-TMA). In Drosophila me/anogaster, however, 2,4,6-TMA and 2,4,6-trichloroaniline (TCA) were mutagenic in the wing spottestat 2-3 times lower doses than 2,4,5-TMA. In the 6-thioguanine resistance test in cultured fibroblasts, 2,4,6-TMA was again mutagenic at lower doses than 2,4,5-TMA. Two methylene-bis-aniline derivatives were also tested with the above methods: 4,4'-methylene-bis-(2-chloroaniline) (MOCA) was moderately genotoxic in al1 3 test systems whereas 4,4'-methylene-bis-(2-ethyl-6-methylaniline) (MMEA) showed no genotoxicity at all. DNA binding sturlies in rats, however, revealed that both MOCA and MMEA produced DNA adducts in the liver at Ievels typically found for moderately strong genotoxic carcinogens. These results indicate that the predictive value of the in vitro test systems and particularly the Salmonellajmicrosome assay is inadequate to detect genotoxicity in aromatic amines. Genotoxicity seems to be a general property of aniline derivatives and does not seem to be greatly influenced by substitution at both ortho positions.
KW  - Toxikologie
KW  - Aniline derivatives
KW  - Genotoxicity
KW  - Short-term tests
KW  - Covalent DNA binding
Y1  - 1989
U6  - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-60857
ER  -