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Environmental and Molecular Mutagenesis - Legacy Tobacco ...

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128 1989 EMS Abstracts<br />

Notes<br />

http://legacy.library.ucsf.edu/tid/clb93d00/pdf<br />

367<br />

DHYDRO7CY-2(5H)~F~gT~Ip ONE (MX ~FJ I~R ~Na ier`, A .ID . CDsAna 1o13-FH B .RDaniel1C K~~Schenck1,<br />

M . F . Ske~ly2 <strong>and</strong> S . L . HuangZ lU .S . <strong>Environmental</strong> Protection Agency, Cincinnati,<br />

OH 45268, <strong>Environmental</strong> Health Research <strong>and</strong> Testing, Cincinnati, OH 45245 NC 27709 .<br />

MX is a potent bacterial mutagen <strong>and</strong> mammalian cell clastogen that forms in drinking<br />

water during water chlorination . Concern over potential health hazards stems from the<br />

finding that !DC is a major contributor to the mutagenic activity of drinking water samples .<br />

The present work was done to obtain preliminary information on the nature of the DNA<br />

damage which accounts for the potent genotoxic activity of MX . DNA adduct formation<br />

was examined in Salmonella tyohimurium TA100 cells, primary rat hepatocytes, nd in a<br />

rat liver embryonic cell line (Clone 9) . DNA adducts were anal~zed by the 3~P-postlabeling<br />

method of R<strong>and</strong>erath <strong>and</strong> Gupta . Mutation frequency (his revertants) was also<br />

determined for the TA100 cells . The Salmonella cells were exposed to !D( concentrations<br />

of 0, 1 <strong>and</strong> 3 pg/ml for 30 min . at 37°C whereas the mammalian cells were exposed for 6<br />

hr to concentrations of 0, 1, 5, 10 <strong>and</strong> 50 pg/ml . Mutation induction was linear over<br />

this dose range in the Salmonelia cells, whereas higher concentrations were toxic . The<br />

mutation frequency was 1 x 10- per pg/al . A dose-dependent increase in DNA adduct<br />

formation was observed for all three cell types . In each case a single major adduct<br />

appeared to be formed . The levels of #dducts at equivalent doses were similar in the<br />

two mammalian cell types (ca . 2 per 10 DNA bases at the 10 pg/al dose) . A comparable<br />

adduct level was observed at 1 yg/ml in the Salmonella calls . Further work to characterize<br />

the DNA adduct formed by !IX is needed to elucidate the role of this lesion in<br />

the genotoxic action of this compound . (This abstract does not necessarily reflect EPA<br />

policy) .<br />

368<br />

MUTAGENS IN CHLORINATED WATER . J .R . Meier, Health Effects Research Laboratory,<br />

U .S . <strong>Environmental</strong> Protection Agency, Cincinnati, OH 45268<br />

Over the past decade, substantial evidence has accumulated to show the widespread<br />

presence of genotoxins in drinking water . The sources of genotoxic contaminants can<br />

be generally classified into three groups ; contaminants of the raw water, chemicals<br />

added or formed during water treatment, <strong>and</strong> chemicals formed or unintentionally added<br />

during distribution . In many cases, the genotoxic activity can be directly attributed<br />

to the chlorination stage of water treatment . The genotoxic activity appears to originate<br />

primarily from reactions of chlorine with humic substances in the source waters .<br />

Cenotoxic activity in drinking water concentrates has been most frequently demonstrated<br />

using bacterial mutagenicity tests but results with mammalian cell assays are generally<br />

consistent with the findings from bacterial assays . There is currently no evidence<br />

for genotoxic damage following in vivo exposure, although little work has been done in<br />

this area . Organic acids appear to account for most of the bacterial mutagenicity <strong>and</strong><br />

recovery of these compounds from water requires a sample acidification step prior to<br />

extraction . Recently, one class of acid cospounds, the chlorinated hydroxyfuranones,<br />

was found to be responsible for a major part of the mutagenic activity . Approaches<br />

for drinking water treatment aimed at reduction of genotoxins in drinking water include<br />

granular activated carbon (GAC) filtration, chemical destruction, <strong>and</strong> the use of alternative<br />

means of disinfection (i .e ., ozone, chlorine dioxide, <strong>and</strong> monochloroamine) .<br />

The question of how best to minimize exposure to genotoxins in drinking water while<br />

maintaining a microbiologically safe water remains to be resolved . (This abstract<br />

does not necessarily reflect EPA policy) .<br />

369<br />

HERITABLE VARIATION IN THE RESPONSE OF A CLINICALLY NORIIAL, AU!tAN POPULATION TO ION-<br />

IZING RADIATION . T . Merz, D .Y . Harrison, L .A . Corey, Medical College of Virginia,<br />

Virginia Commonwealth University, Richmond, VA (USA)<br />

This is a study of the inheritance of variability in the response of clinically<br />

normal individuals to ionizing radiation . The micronucleus assay is used to measure<br />

response <strong>and</strong> since micronuclei frequencies are dependent on cell proliferation, cell<br />

growth kinetics are also considered . Then twin method is used to determine whether<br />

there is a heritable component of variation in the response of cells from clinically<br />

normal individuals . Ten pairs of monozygotic twins were examined for their responses<br />

to radiation . The variation of the response of twins within a pair is compared<br />

to the variation between pairs of twins . An analysis of variance does indlcate<br />

that there is considerable variation in observed micronuclei frequency . Nost<br />

of the variability can be accounted for by the differences between twin pairs . The<br />

large interpair variation compared to the intrapair variation demonstrates that<br />

twin micronuclei production is more alike (correlation of 0 .92) than non-twins . It<br />

is suggestive of a genetic influence on mlcronuclel production .

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