Environmental and Molecular Mutagenesis - Legacy Tobacco ...
Environmental and Molecular Mutagenesis - Legacy Tobacco ...
Environmental and Molecular Mutagenesis - Legacy Tobacco ...
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
159 1989 EMS Abstracts<br />
Notes<br />
VALUE-OF-INFORMATION ANALYSIS OF TESTING STRATEGIES . F .K . Ennever, H .S . Rosenkranz,<br />
L .B . Lave, <strong>and</strong> G .S . Omenn, Case Western Reserve University . Clevel<strong>and</strong> . OH (USA),<br />
Carnegie-Mellon University . Pittsburgh . PA (USA), <strong>and</strong> University of Washington .<br />
Seattle . WA (USA) .<br />
The goal of reducing the incidence of cancers caused by environmental exposures<br />
requires strategies for identifying hazards among >50.000 chemicals in commerce <strong>and</strong><br />
industry . Our value-of-information framework analyzes strategies for classifying<br />
chemicals as human carcinogens or non-carcinogens . Any classification will have false<br />
negatives (FN) : falsely exonerating a human carcinogen ; false positives (FP) ; falsely<br />
indicting a human non-carcinogen ; true negatives ; <strong>and</strong> true positives . One extreme<br />
strategy treats all chemicals as non-carcinogena, as existing chemicals generally are<br />
treated ; FP = 0 <strong>and</strong> FN = c, where c is the proportion of carcinogens among those<br />
chemicals . A second extreme strategy treats all chemicals as carcinogens ; PN - 0 <strong>and</strong><br />
FP = 1 - c . A third strategy classifies chemicals on the basis of results of<br />
structure-activity analyses, short-term tests, <strong>and</strong>/or rodent cancer bioassays ; PN -<br />
(1 - p)c, where p is the weighted sensitivity of the tests, <strong>and</strong> PP =(1 - q)(l - c),<br />
where q is the weighted specificity of the tests . Using reasonable estimates of c, p,<br />
q, the cost of testing, <strong>and</strong> the societal costs of PN (needless cancers) <strong>and</strong> FP (loss<br />
of the use of a chemical), our model has shown that in many cases the lifetime rodent<br />
bioassay is not the most cost-effective way to classify chemicals as human carcinogens<br />
or non-carcinogens . Our most recent work has focused on the influence of uncertainty<br />
in parameter estimation <strong>and</strong> on deriving a sequential testing strategy with decision<br />
rules for when to classify a chemical without further testing .<br />
160<br />
COVALENT BINDING TO MICROTUBULAR PROTEINS AS A POSSIBLE CAUSE OF THE ANEUPLOIDY AND<br />
MICRONUCLEUS FORMATION INDUCED BY CARCINOGENIC ESTROGENS AND OTHER CARCINOGENS .<br />
B . Epe, U .H . Harttig, D . Schiffmann, <strong>and</strong> M. Metzler, Institute of Toxicology, University<br />
of Wiirzburg, Versbacher Strasse 9, D-8700 Wurzburg, Fad . Rep . Germany .<br />
Certain estrogens, e .g . diethylstilbestrol (DES), transform Syrian hamster embryo<br />
fibroblasts neoplastically in vitro without producing detectable DNA damage or structural<br />
chromosomal abnormalities . Instead, induction of aneuploidy <strong>and</strong> micronucleus formation<br />
was observed <strong>and</strong> was associated with cell transformation . In order to elucidate<br />
the biochemical mechanisms of aneuploidy induction, we have studied the interaction of<br />
several radioactively labeled estrogens <strong>and</strong> their metabolites with tubulin in a cellfree<br />
system . We observed highly specific covalent bindiijg to the carboxy terminal<br />
domain of /1-tubulin of those estrogens which undergo peroxidase-mediated quinone formation<br />
(DES, indenestrol A <strong>and</strong> the catechol estrogens 2-hydroxyestradiol <strong>and</strong> 2-hydroxy-<br />
17a-ethinylestradiol) . Estrogens which do not form peroxidative quinone metabolites<br />
(hexestrol, estradiol, 17K-ethinylestradiol) did not bind covalently . Covalent binding<br />
was not inhibited by sulfhydryl reagents nor by colchicine, podophyllotoxin, taxol or<br />
vinblastine . Specific covalent binding to tubulin was also obtained with hydroquinone,<br />
a major metabolite of the non-mutagenic carcinogen benzene, upon peroxidase-mediated<br />
oxidation . Electron microscopy of the microtubulee formed from tubulin coupled to DES<br />
or hydroquinone shoved clear abnormalities indicating that covalent tubulin binding<br />
has functional consequences . Therefore, we propose covalent binding to tubulin as an<br />
early biochemical lesion in the mechanism of aneuploidy induction <strong>and</strong> neoplastlc cell<br />
transformation by non-DNA-damaging carcinogens .<br />
Supported by Deutsche Forschungsgemeinschaft <strong>and</strong> BMJFFG .<br />
161<br />
SELECTION OF AN EAPERIMENTAI. PROTOCOL FOR SCREENING TEST AGENTS IN THE MOUSE BONE<br />
MARROW MICRONUCLEUS TEST . G .L . Erexsonl, J .L . Hustonl*, R .M . Boehml*, D . Gulati2,<br />
<strong>and</strong> M .D . Shelby3 . l<strong>Environmental</strong> Health Rea . 6 Testing, Inc ., P .O . Box 12199, RTP, NC<br />
27709 <strong>and</strong> 22514 Regency Road, Lexington, KY 40503 ; 3NIERS . NTP, Box 12874, RTP, NC .<br />
Due to methodological variations in the mouse bone marrow micronucleus (!D1) test ;<br />
one universal treatment protocol for in vivo chemical exposure is desirable . A common<br />
protocol among laboratories would simplify comparison of MN data . Mitomycin C(14/C)<br />
<strong>and</strong> 7 .12-dimethylbenzanthracena (DMBA) were tested i .p . at doses of 0, 0 .5 . 1, <strong>and</strong> 1 .3<br />
mg MMC/kg <strong>and</strong> 0, 25 . 50, <strong>and</strong> 100 mg DMBA/kg using three different protocols . Male<br />
B6C3F1 mice (9 to 14 weeks of age, 5 mice/dose) were treated with either (1) one<br />
exposure with harvests for bone marrow polychromatic erythrocytes (PCEs) at 24, 48, or<br />
72 h post-treatment ; (2) two exposures separated by 24 h with harvests at 24 or 48 h<br />
after the second treatment ; or (3) three exposures separated by 24 h with one harvest<br />
time at 24 h after the third treatment . For comparison, DMBA was administered also by<br />
gavage but only for the three-treatment protocol at the same doses used for the 1 .p .<br />
http://legacy.library.ucsf.edu/tid/clb93d00/pdf<br />
57