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  • 1
    ISSN: 1432-0738
    Keywords: Estrogen ; Hormone ; Carcinogenesis ; DNA binding ; Protein binding ; Estrone ; Estradiol
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Abstract [6,7-3H] Estrone (E) and [6,7-3H]estradiol-17β (E2) have been synthesized by reduction of 6-dehydroestrone and 6-dehydroestradiol with tritium gas. Tritiated E and E2 were administered by oral gavage to female rats and to male and female hamsters on a dose level of about 300 μg/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 = (μmol chemical bound per mol 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 E2, 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 E2, 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 times higher 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 103–104 have been found for potent, 102 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 limit of detection of 0.01 places covalent DNA binding among the highly unlikely mechanisms of action. Similar considerations can be made for the liver where any true covalent DNA binding must be below a level of 0.01. It is concluded that an observable tumor induction by estrone or estradiol is unlikely to be due to DNA binding.
    Type of Medium: Electronic Resource
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  • 2
    Electronic Resource
    Electronic Resource
    Springer
    Archives of toxicology 65 (1991), S. 169-176 
    ISSN: 1432-0738
    Keywords: 1,2-Dichloroethane ; Carcinogens ; DNA binding ; Rat ; Inhalation ; Dose response
    Source: Springer Online Journal Archives 1860-2000
    Topics: Medicine
    Notes: Abstract 1,2-Dichloroethane (DCE) was reported to be carcinogenic in rats in a long-term bioassay using gavage in corn 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. Female 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/l=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/kg. DNA was isolated from liver and lung and was purified to constant specific radioactivity. DNA was enzymatically 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 level of DNA adducts was expressed in the dose-normalized units of the Covalent Binding Index, CBI = (μmol 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 levels. In the lung, the respective values were 0.9 and 31. It is concluded that the DNA damage by DCE depends upon the concentration-time profile and that the carcinogenic potency determined in the gavage study should not be used for low-level inhalation exposure.
    Type of Medium: Electronic Resource
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