TY - JOUR A1 - Adam, W. A1 - Ahrweiler, M. A1 - Saha-Möller, C. R. A1 - Sauter, M. A1 - Schönberger, A. A1 - Epe, B. A1 - Müller, E. A1 - Schiffmann, D. A1 - Stopper, Helga A1 - Wild, D. T1 - Genotoxicity studies of benzofuran dioxetanes and epoxides with isolated DNA, bacteria and mammalian cells N2 - 1.2-Dioxetanes, very reactive and high energy molecules. are involved as labile intermediates in dioxygenase- activated aerobic metabolism and in physiological processes. Various toxico1ogica1 tests reveal that dioxetanes are indeed genotoxic. In supercoiled DNA of bacteriophage PM2 they induce endonucleasesensitive sites, most of them are FPG protein-sensitive base modifications (8-hydroxyguanine, fonnamidopyrimidines). Pyrimidinedimersand sites ofbase loss (AP sites) which were probed by UV endonuclease and exonuclease 111 are minor lesions in this system. While the alky1-substituted dioxetanes do not show any significant mutagenic activity in different Salmonella typhimurium strains, heteroarene dioxetanes such as benzofuran and furocoumarin dioxetanes are strongly mutagenic in S. typhimurium strain TA I 00. DNA adducts formed with an intermediary alkyJating agent appear to be responsible for the mutagenic activity of benzofuran dioxetane. We assume that the benzofuran epoxides, generated in situ from benzofuran dioxetanes by deoxygenation are the ultimate mutagens of the latter. since benzofuran epoxides are highly mutagenic in the S. typhimurium strain TAIOO and they form DNA adducts. as detected by the 212Ppostlabelling technique. Our results imply that the type of D NA darnage promoted by dioxetanes is dependent on the structural feature of dioxetanes. Furthermore, the direct photochemical DNA darnage by energy transfer. i.e., pyrimidine dimers, plays a minor role in the genotoxicity of dioxetanes. Instead, photooxidation dominates in isolated DNA. while radical darnage and alkylation prevail in the cellular system. KW - Toxikologie KW - 1 KW - 2-Dioxetane KW - Benzefuran dioxetane KW - Benzefuran epoxide KW - DNA damage KW - Mutagenicity KW - DNA adduct . Repair endonuclease KW - FPG protein Y1 - 1993 U6 - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-63420 ER - 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 - THES A1 - Schuster, Paul Xaver T1 - Biotransformation of trans-1,1,1,3-tetrafluoropropene, 2,3,3,3-tetrafluoropropene and 1,2,3,3,3-pentafluoropropene T1 - Biotransformation von trans-1,1,1,3-Tetrafluorpropen, 2,3,3,3-Tetrafluorpropen und 1,2,3,3,3-Pentafluorpropen N2 - trans-1,1,1,3-Tetrafluoropropene (HFO-1234ze) and 2,3,3,3-tetrafluoropropene (HFO-1234yf) are non-ozone-depleting fluorocarbon replacements with low global warming potentials and short atmospheric lifetimes. They are developed as foam blowing agent and refrigerant, respectively. Investigations on biotransformation in different test species and in vitro systems are required to assess possible health risks of human exposure and needed for commercial development. The biotransformation of HFO-1234ze and HFO-1234yf was therefore investigated after inhalation exposure. Male Sprague-Dawley rats were exposed to air containing 2 000; 10,000; or 50,000 ppm (n=5/concentration) HFO-1234ze or HFO-1234yf. Male B6C3F1 mice were only exposed to 50,000 ppm HFO-1234ze or HFO-1234yf. Due to lethality observed in a developmental study with rabbits after exposure to high concentrations of HFO-1234yf, the metabolic fate of the compound was tested by whole body inhalation exposure of female New Zealand White rabbits to air containing 2 000; 10,000; or 50,000 ppm (n=3/concentration) HFO-1234yf. All inhalation exposures were conducted for 6 h in a dynamic exposure chamber. After the end of the exposures, animals were individually housed in metabolic cages and urines were collected at 6 or 12 h intervals for 48 h (rats and mice) or 60 h (rabbits). For metabolite identification, urine samples were analyzed by 1H-coupled and 1H-decoupled 19F-NMR and by LC/MS-MS or GC/MS. Metabolites were identified by 19F-NMR chemical shifts, signal multiplicity, 1H-19F coupling constants and by comparison with synthetic reference compounds. Biotransformation of HFO-1234ze in rats exposed to 50,000 ppm yielded S-(3,3,3-trifluoro-trans-propenyl)mercaptolactic acid as the predominant metabolite which accounted for 66% of all integrated 19F-NMR signals in urines. No 19F-NMR signals were found in spectra of rat urine samples collected after inhalation exposure to 2 000 or 10,000 ppm HFO-1234ze likely due to insufficient sensitivity. S-(3,3,3-Trifluoro-trans-propenyl)-L-cysteine, N-acetyl-S-(3,3,3-trifluoro-trans-propenyl)-L-cysteine, 3,3,3-trifluoropropionic acid and 3,3,3-trifluorolactic acid were also present as metabolites in urine samples of rats and mice at the 50,000 ppm level. A presumed amino acid conjugate of 3,3,3-trifluoropropionic acid was the major metabolite of HFO-1234ze in urine samples of mice exposed to 50,000 ppm and related to 18% of total integrated 19F-NMR signals. Quantitation of three metabolites in urines of rats and mice was performed, using LC/MS-MS or GC/MS. The quantified amounts of the metabolites excreted with urine in both mice and rats, suggest only a low extent (<<1% of dose received) of biotransformation of HFO-1234ze and 95% of all metabolites were excreted within 18 h after the end of the exposures (t1/2 approx. 6 h). Due to its low boiling point of −22 °C, most of the inhaled HFO-1234ze is expected to be readily exhaled. Moreover, steric and electronic factors may decrease the reactivity of the parent compound with soft nucleophiles such as glutathione. The obtained results suggest that HFO-1234ze is subjected to an addition-elimination reaction with glutathione and to a cytochrome P450-mediated epoxidation at low rates. The extent of a direct addition reaction of HFO-1234ze with glutathione is negligible, compared to that of the observed addition-elimination reaction. The results of in vivo testing of HFO-1234ze could not be supported by in vitro investigations, since HFO-1234ze was not metabolized in incubations with either liver microsomes or subcellular fractions from rat and human. Regarding the structures delineated in the biotransformation scheme of HFO-1234ze, 1,1,1,3-tetrafluoroepoxypropane and 3,3,3-trifluoropropionic acid are toxic intermediates which, however, are not supposed to display toxicity in the species after exposure to HFO-1234ze, due to the low extent of formation and an efficient detoxification of the epoxide by hydrolysis and glutathione conjugation. The findings of biotransformation of HFO-1234ze in rats and mice correlate with the absence of adverse effects in the toxicity testings and indicate their innocuousness to a human exposure. Biotransformation of HFO-1234yf yielded N-acetyl-S-(3,3,3-trifluoro-2-hydroxypropanyl)-L-cysteine as predominat metabolite which accounted for approx. 44, 90 and 32% (50,000 ppm) of total 19F-NMR signal intensities in urine samples from rabbits, rats and mice, respectively. S-(3,3,3-Trifluoro-2-hydroxypropanyl)mercaptolactic acid and the sulfoxides of mercapturic acid and mercaptolactic acid S-conjugate were identified as minor metabolites of HFO-1234yf in urine samples from rabbits, rats and mice, whereas trifluoroacetic acid, 3,3,3-trifluorolactic acid and 3,3,3-trifluoro-1-hydroxyacetone were present as minor metabolites only in urine samples from rats and mice. The absence of these metabolites in rabbit urine samples... N2 - trans-1,1,1,3-Tetrafluorpropen (HFO-1234ze) und 2,3,3,3-Tetrafluorpropen (HFO-1234yf) sind FKW-Ersatzstoffe, die eine kurze atmosphärische Lebensdauer besitzen und weder die Ozonschicht beeinträchtigen noch wesentlich zur globalen Erwärmung beitragen. Sie werden derzeit als Treibmittel für Schäume beziehungsweise als Kühlmittel entwickelt. Untersuchungen der Biotransformation in verschiedenen Tierspezies und in in vitro Systemen tragen zur Risikobewertung einer Humanexposition bei und werden für die kommerzielle Entwicklung benötigt. In dieser Arbeit wurde die Biotransformation von HFO-1234ze und HFO-1234yf nach inhalativer Exposition untersucht. Männliche Sprague-Dawley Ratten wurden Luftkonzentrationen von 2.000, 10.000 und 50.000 ppm (n=5/Konzentration) ausgesetzt. Männliche B6C3F1 Mäuse wurden dagegen nur einer Konzentration von 50.000 ppm ausgesetzt. Aufgrund von Todesfällen in einer Entwicklungstoxizitätsstudie mit Kaninchen wurde in dieser Arbeit auch die Biotransformation von HFO-1234yf in weiblichen Kaninchen mit Konzentrationen von 2.000, 10.000 und 50.000 ppm untersucht. Alle Inhalationen dauerten 6 Stunden und fanden in einem dynamisch durchströmten Expositionssystem statt. Nach Ende der Inhalationen wurden die Versuchstiere individuell in Stoffwechselkäfigen untergebracht und ihre Urine in 6 bzw. 12 h Intervallen gesammelt (insgesamt 48 h bei Ratten und Mäusen bzw. 60 h bei Kaninchen). Zur Identifizierung der Metabolite von HFO-1234ze und HFO-1234yf in den Urinen wurden 1H-ge- und entkoppelte 19F-NMR-Spektren aufgezeichnet und massenspektrometrische Untersuchungen mittels LC/MS-MS oder GC/MS durchgeführt. Die Metaboliten wurden anhand ihrer 19F-NMR-Charakteristika (Chemische Verschiebung, Signalmultiplizität und 1H-19F Kopplungskonstante) und durch Vergleich mit ihren synthetischen Referenzverbindungen identifiziert. In Ratten, die einer Konzentration von 50.000 ppm HFO-1234ze ausgesetzt worden waren, konnte S-(3,3,3-Trifluor-trans-propenyl)merkaptolaktat als Hauptmetabolit nachgewiesen werden. Er machte 66% aller integrierten 19F-NMR-Signale aus. In 19F-NMR-Spektren von Rattenurinen der 2.000 und 10.000 ppm Expositionen konnten dagegen keine Signale detektiert werden, wahrscheinlich wegen unzureichender Empfindlichkeit der 19F-NMR-Messungen. Als Nebenprodukte von HFO-1234ze in Ratten- und Mäuseurinen wurden S-(3,3,3-Trifluor-trans-propenyl)-L-cystein, N-Acetyl-S-(3,3,3-trifluor-trans-propenyl)-L-cystein, 3,3,3-Trifluorpropion-säure und 3,3,3-Trifluorlaktat nachgewiesen. In Mäuseurinen war der Hauptmetabolit von HFO-1234ze ein vermutetes Aminosäurekonjugat von 3,3,3-Trifluorpropion-säure, auf das 18% aller integrierten 19F-NMR Signalintensitäten entfielen. In den Urinen von Ratten und Mäusen wurden 3 Metabolite mittels LC/MS-MS oder GC/MS quantifiziert. Die ermittelten Mengen weisen auf eine sehr niedrige Biotransformationsrate von HFO-1234ze hin (<<1% der verabreichten Dosis). 95% aller Metabolite wurden innerhalb von 18 h nach Ende der Inhalationen ausgeschieden (t1/2 ca. 6 h). Aufgrund des niedrigen Siedepunkts von −22°C wird ein Großteil des aufgenommen Gases möglicherweise rasch wieder exhaliert, und sterische sowie elektronische Faktoren könnten die Reaktivität der Ausgangsverbindung mit schwachen Nukleophilen wie Glutathion senken. Die vorliegenden Ergebnisse legen nahe, dass HFO-1234ze in geringem Ausmaß durch Additions-Eliminations Reaktion mit Glutathion und einer CYP450-vermittelten Epoxidierung biotransformiert wird. Das Ausmaß einer direkten Additions Reaktion von HFO-1234ze mit Glutathion ist verglichen mit der vorherrschenden Additions-Eliminations Reaktion vernachlässigbar. Da kein Umsatz von HFO-1234ze in Inkubationen mit Rettenlebermikrosomen oder subzellulären Fraktionen von Human- und Rattenleber stattfand, konnten die in vivo Ergebnisse dieser Arbeit nicht mit in vitro Untersuchungen verglichen werden. Im Biotransformationsschema von HFO-1234ze sind 1,1,1,3-Tetrafluorepoxypropan und 3,3,3-Trifluorpropionsäure toxische Intermediate, die jedoch aufgrund der geringen gebildeten Mengen und einer effektiven Entgiftung des Epoxids durch Glutathionkonjugation keine toxischen Effekte in den verwendeten Tierspezies auslösten. Die Ergebnisse der Untersuchung der Biotransformation von HFO-1234ze in Ratten und Mäusen korrelieren mit der Abwesenheit nachteiliger Effekte in den Toxizitätsstudien und lassen eine Humanexposition gegenüber HFO-1234ze als unbedenklich erscheinen. Bei der Biotransformation von HFO-1234yf entstand N-Acetyl-S-(3,3,3-trifluor-2-hydroxypropanyl)-L-cystein... KW - Biotransformation KW - fluorocarbons KW - trans-1 KW - 1 KW - 1 KW - 3 KW - tetrafluoropropene KW - 2 KW - 3 KW - 3 KW - 3-tetrafluoropropene KW - 1 KW - 2 KW - 3 KW - 3 KW - 3-pentafluoropropene KW - metabolites KW - Merkaptursäure KW - Merkaptolaktat KW - Glutathion S-Konjugat KW - Toxizität KW - Inhalation KW - mercapturic acid KW - mercaptolactic acid KW - glutathion S-conjugate KW - toxicity KW - inhalation Y1 - 2009 U6 - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-43716 ER - TY - JOUR A1 - Quast, Helmut A1 - Schmitt, Edeltraud A1 - Schäfer, Peter A1 - Heller, Eberhard A1 - Aldenkortt, Sven T1 - Synthesis and Thermolysis of a Chiral, Non-Racemic Iminoaziridine N2 - The 2-halo imidoyl chlorides 7 are obtained from the amide 5 and the 2-halo amides 6 by the action of phosphorus pentachloride and thionyl chloride, respectively. Non-racemic (S)-6a is converted into 7a which is racemic, however. The reaction of Lawesson's reagent with 6a furnishes the diastereomeric 1,3.2-thiazaphospholidine derivatives 15. Treatment of (S)-6a (98% eel with methyl triflate affords 2-chloro imidate 8 (95% eel which reacts with methanamine in the presence of methanammonium chloride to yield the 2-chloro amidine (S)-9a (90% eel. The 2-halo imidoyl halides 7a and b react with methanamine to produce the 2-halo amidines 9a and b. - Strong bases, e.g. potassium tert-butoxide or sodium hydride in the presence of catalytic amounts of tertbutyl alcohol, eliminate hydrogen chloride or bromide from the 2-halo amidines 9a and band (S)-9a to yield mixtures of Recently, we demonstrated that the formation of the chiral non-racemic aziridinone (R)-2 from the a-chloro amide (5)-1 by base-promoted dehydrochlorination[2) as well as the nucleophilic cleavage of the N-C(3) bond of (R)_2[3,4) occur with inversion of configuration, thus excluding the intervention of achiral (acyclic) intermediates. In the temperature range of lOO-170°C, however, slow racemization accompanies the thermolysis of (R)-2 and indicates the existence of an achiral or a racemic transient, e. g. (M)-3 + (P)-3. Indeed, high-level quantum-chemical calculations reveal that an activation energy of (170 ± 25) kJmol- 1 is required for the unimolecular ring opening of the parent aziridinone which affords a species of high diradical character[41. Subsequently, the unstable N-phenylaziridinone invoked in the decomposition of the (5)-2-bromopropananilide anion was shown to react with tert-butylamine or dimethylformamide with inversion of configuration at C(3)[51. Thus, the stereochemical evidence in the series of 3-alkylaziridinones excludes achiral (acyclic) aziridinone isomers as intermediates at low tempera tures [6J. Similar stereochemical studies are still missing in the related series of iminoaziridines. Therefore, we report on the synthesis and thermolysis of the diastereomeric chiral racemic (E)- and (Z)-(4)[71 and non-racemic iminoaziridines (E,R)- and (Z,R)-4. Racemic Iminoaziridines (E)- and (Z)-4 Though a photochemical route to the iminoaziridines (E)- and (Z)-4 has been devised more recently, i. e. the phothe 2-iminoaziridines (E)- and (Z)-4, and (E,R)- and (Z.R)-4 (83% eel, respectively. The 1.3-elimination of hydrogen bromide from 9b is diastereoselective at -30 to -40°C [(E)-4:(Z)-4 = <10:>90). The diastereomers equilibrate at 36°C with (kEZ + k ZE) = (5.92 ± 0.08) . 10-5 S-I (K = kEZlkzE = 0.428 ± 0.013). - The thermolysis of (E)- and (Z)-4 in [D61benzene solution yields the imine 16 and methyl isocyanide (17). The decomposition follows the first-order rate law. The following Arrhenius and Eyring parameters are calculated from five rate constants obtained in the temperature range of 70-110°C: Ea = (115.2 ± 0.4) kJmol-t, IgA = (12.06 ± 0.28), AH* = (112.1 ± 0.4) kJmol- l , AS'" = (-23.9 ± 0.7) JK-I mol-I, AGj73K = 121 kJmol-1 . The enantiomeric excess of the surviving fraction of (E,R)- and (Z.R)-4 is unchanged after two half-lives at 80°C. KW - Aziridines KW - 2-imino- KW - chiral KW - non-racemic KW - Imidoyl halides KW - 2-halo KW - Imidates KW - 2-chloro KW - 1 KW - 3 KW - 2-Thiazaphospholidines Y1 - 1994 U6 - http://nbn-resolving.de/urn/resolver.pl?urn:nbn:de:bvb:20-opus-38298 ER -