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The Toxicologist - Society of Toxicology

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1416 PIG-A MUTATION AND MICRONUCLEATED<br />

RETICULOCYTE ASSAYS DISCRIMINATE THE<br />

MUTAGENIC/NON-MUTAGENIC PAIR:<br />

BENZO[A]PYRENE/PYRENE.<br />

D. Torous 1 , J. MacGregor 2 , S. Phonethepswath 1 , P. Weller 1 , J. Bemis 1 and S.<br />

Dertinger 1 . 1 Litron Laboratories, Rochester, NY and 2 <strong>Toxicology</strong> Consulting Services,<br />

Arnold, MD.<br />

Integration <strong>of</strong> genotoxicity endpoints into general toxicology studies is attractive<br />

for several reasons, including the potential to reduce animal use and provide comprehensive<br />

toxicity information that aids interpretation <strong>of</strong> genotoxicity results. This<br />

laboratory has developed automated scoring techniques for monitoring two crossspecies,<br />

blood-based genotoxicity endpoints, thereby making integration practical:<br />

flow cytometric procedures for scoring micronucleated reticulocyte frequency and<br />

gene mutation at the Pig-a locus. <strong>The</strong> ability to integrate these endpoints into a 28day<br />

repeat dosing schedule was investigated with a mutagenic/non-mutagenic pair<br />

at maximum tolerated dose levels: benzo[a]pyrene (BP, 150 mg/kg/day) and pyrene<br />

(Pyr, 125, 250 and 500 mg/kg/day). Male Wistar Han rats were treated on Days 1-<br />

28 via oral gavage. Blood samples obtained on Days -1, 15, 29 and 56 were analyzed<br />

for Pig-a mutation with a dual staining method (SYTO 13 in combination<br />

with anti-CD59-PE) that facilitated mutant cell frequency measurements in both<br />

total erythrocytes and the reticulocyte subpopulation. Day 4 and 29 specimens<br />

were evaluated for micronucleus frequency according to MicroFlow® Kit instructions.<br />

BP induced robust responses on Days 15, 29 and 56 in the mutant phenotype<br />

reticulocyte population, and on Days 29 and 56 in the mutant phenotype erythrocyte<br />

population. No mutagenic effects in either population were apparent for<br />

Pyr. Significant increases in micronucleated reticulocyte frequencies were observed<br />

with BP on Days 4 and 29, whereas Pyr had no effect. <strong>The</strong>se results suggest that<br />

both endpoints are relatively specific for genotoxic activity, as each discriminated<br />

the structurally-related mutagenic and non-mutagenic agents, even when treatment<br />

was at a maximum tolerated dose.<br />

1417 THE MUTAGENIC POTENTIAL OF CIS-2-BUTENE-1,<br />

4-DIAL.<br />

A. Terrell 1 , M. Huynh 2 and L. A. Peterson 1, 3 . 1 Environmental Health Sciences,<br />

University <strong>of</strong> Minnesota, Minneapolis, MN, 2 Biochemistry, Molecular Biology and<br />

Biophysics, University <strong>of</strong> Minnesota, Minneapolis, MN and 3 Masonic Cancer Center,<br />

University <strong>of</strong> Minnesota, Minneapolis, MN.<br />

Furan is a known rodent hepatotoxicant and carcinogen. Human exposure to furan<br />

is widespread, but the human health effects are unknown. While there have been<br />

many studies <strong>of</strong> furan toxicity, the mechanism <strong>of</strong> carcinogenicity is still debated.<br />

Both genotoxic and nongenotoxic mechanisms have been proposed but in vivo and<br />

in vitro studies have reported conflicting and inconclusive results. It is suspected<br />

that the reactive metabolite <strong>of</strong> furan, cis-2-butene-1,4-dial, is the toxic and carcinogenic<br />

agent. In this study, the Big Blue in vitro mutagenesis model was used to evaluate<br />

the mutagenic potential <strong>of</strong> a single dose and chronic dose <strong>of</strong> cis-2-butene-1,4dial.<br />

Overall, the results suggest that cis-2-butene-1,4-dial is not genotoxic in the<br />

Big Blue in vitro mutagenesis model at the tested treatment. [funded by ES10577]<br />

1418 THE METABOLITES OF THE AZO DYE DISPERSE RED<br />

1 CAN REPRESENT HUMAN RISKS CONSIDERING THE<br />

INGESTION OF CONTAMINATED WATER AND FOOD.<br />

F. D. Chequer 1 , T. M. Lizier 2 , M. B. Zanoni 2 , R. Marcos 3 and D. P. Oliveira 1 .<br />

1 Faculdade de Ciências Farmacêuticas de Ribeirão Preto - Universidade de São Paulo,<br />

Ribeirão Preto, São Paulo, Brazil, 2 (2) Universidade Paulista Júlio de Mesquita<br />

Filho, Araraquara, São Paulo, Brazil and 3 (3) Universitat Autònoma de Barcelona,<br />

Barcelona, Spain.<br />

Introduction: Azo dyes constitute the largest class <strong>of</strong> synthetic dyes used in commercial<br />

applications. Following oral exposure, these dyes can be reduced to aromatic<br />

amines by the intestinal micr<strong>of</strong>lora or liver azoreductases. Objectives: To determine<br />

the products formed after oxidation and reduction <strong>of</strong> the dye Disperse Red<br />

1, simulating hepatic biotransformation; and to evaluate the mutagenic potential <strong>of</strong><br />

the resultant solution. Methods: Controlled potential electrolysis was carried out<br />

on dye solution using a Potentiostat/Galvanostat. HPLC-DAD was used for the determination<br />

<strong>of</strong> aromatic amines generated after oxidation/reduction process. <strong>The</strong><br />

Salmonella/microssome assay with the strain TA98 and YG1041 with and without<br />

S9, as well as mouse lymphoma assay (MLA) using the thymidine kinase (Tk) gene<br />

were used for the evaluation <strong>of</strong> the mutagenicity <strong>of</strong> the solution obtained after the<br />

reduction/oxidation process. Results: We have identified Sulfate de N-ethyl-(2-<br />

304 SOT 2011 ANNUAL MEETING<br />

hidroxiethyl)-p-phenyldiamine monohydrate and Nitrobenzene resultants from oxidation<br />

and reduction <strong>of</strong> the dye Disperse Red 1. Our group showed that this azo<br />

dye is mutagenic in different cell system. In addition after the oxidation/reduction<br />

process, the dye still has mutagenic activity for the Salmonella/microssome assay.<br />

We observed that the mutagenic potential <strong>of</strong> the resultant solution to the strain<br />

YG1041 decreased after both the processes compared with the original dye, while<br />

for the strain TA98 we observed an increase <strong>of</strong> the effect. Yet, both the original dye<br />

Disperse Red 1 and its treated solutions showed negative results in the MLA.<br />

Conclusions: Considering that the reduction/oxidation processes are similar to hepatic<br />

reaction, we concluded that the ingestion <strong>of</strong> water and food contaminated<br />

with this dye is a human health problem.<br />

Financial support:CNPq<br />

1419 MUTATION SPECTRUM IN HPRT-/GPT+ V79 CELLS<br />

TREATED WITH TEAK WOOD EXTRACT AND 2-<br />

METHYLANTHRAQUINONE, AN ABUNDANT<br />

BIQUINONE IN TEAK WOOD.<br />

M. J. Wilson 1 , C. Miller 1, 2 , G. Sabbioni 1, 2 and R. Rando 1 . 1 Environmental<br />

Health Sciences, Tulane University, New Orleans, LA and 2 Tulane Cancer Center,<br />

Tulane University, New Orleans, LA.<br />

Wood dusts are generally classified as known human carcinogens by NTP and<br />

IARC based on a strong association with increased risk <strong>of</strong> nasal cancer. However, no<br />

specific carcinogenic compounds have been identified in wood dusts. Teak wood<br />

(Tectona grandis) is an important tropical hardwood frequently used in furniture<br />

manufacturing. An increase in mutation frequency was observed in a hprt-/gpt+<br />

cell line following treatment with methanol extract <strong>of</strong> teak wood dust.<br />

Fractionation <strong>of</strong> the teak dust extract using multiple analytical methods identified<br />

2-methylanthraquinone as an abundant bioactive constituent. Large deletions <strong>of</strong><br />

the gpt transgene were caused by teak wood dust extract or 2-methylanthraquinone<br />

treatments. <strong>The</strong>se large signature deletions were three-fold higher in the 2-methylanthraquinone<br />

and teak extract treatments. We conclude that teak wood dust and<br />

its major toxic constituent, 2-methylanthraquinone, are mutagenic and may share a<br />

common mechanism <strong>of</strong> action. 2-methylanthraquinone has not been formally<br />

identified as a mutagen or carcinogen, but anthraquinone and other substituted derivatives<br />

possess these activities. <strong>The</strong> presence <strong>of</strong> an abundant anthraquinone implies<br />

teak dusts may pose an exceptional occupational risk to woodworkers.<br />

1420 GENOTOXICITY ASSESSMENT OF<br />

ETHYLENEDIAMINE DINITRATE (EDDN) AND<br />

DIETHYLENETRIAMINE TRINITRATE (DETN).<br />

G. Reddy 1 , J. Song 2 , P. Kirby 2 and M. S. Johnson 1 . 1 Directorate <strong>of</strong> <strong>Toxicology</strong>,<br />

U.S. Army Public Health Command, Aberdeen Proving Ground, MD and 2 SITEK<br />

Research Laboratories, Rockville, MD.<br />

Ethylenediamine dinitrate (EDDN) and Diethylene triamine trinitrate (DETN)<br />

are explosive compounds used in combination with other high explosives as safe,<br />

insensitive, and inexpensive replacements. <strong>The</strong> genetic toxicity <strong>of</strong> these compounds<br />

was evaluated to predict the potential for adverse human health effects from exposure.<br />

<strong>The</strong> genetic toxicity test battery included: gene mutation test in bacteria<br />

(Ames), in vitro chromosome aberration test and in vivo mouse micronucleus test.<br />

<strong>The</strong> results <strong>of</strong> the Ames test indicated DETN was negative for Salmonella typhimurium<br />

strains TA98, TA100, TA1535 and TA1537, and Escherichia coli strain<br />

WP2 uvrA at doses up to 5000 μg/plate both with and without metabolic activation.<br />

EDDN produced a positive increase in the mean number <strong>of</strong> revertants per<br />

plate with the tester strain TA100 without activation (3.1-fold) at 5000 μg/plate.<br />

No positive increases were observed with the other tester strains with or without activation.<br />

<strong>The</strong> Chinese Hamster Ovary Cell (CHO) Chromosome Aberration Assay<br />

was performed using DETN at concentrations up to 5000 μg/mL. <strong>The</strong> results indicated<br />

that DETN did not induce structural chromosomal aberrations at concentrations<br />

up to 5000 μg /mL in CHO cells, with or without metabolic activation.<br />

EDDN tested up to 5000 μg/mL both without and with metabolic activation, produced<br />

negative results in CHO cells. DETN and EDDN, when tested in vivo in<br />

the CD-1 mouse at doses up to 2000 mg/kg, did not induce a significant increase<br />

in the number <strong>of</strong> micronuclei in bone marrow erythrocytes. <strong>The</strong>se studies demonstrate<br />

that EDDN is mutagenic in one specific strain <strong>of</strong> Salmonella (TA100) but<br />

were negative in other strains and in vitro for induction <strong>of</strong> chromosomal aberrations<br />

in CHO cells and for micronuclei in the in vivo mouse micronucleus assay.<br />

DETN was not genotoxic in both in vitro and in vivo tests. <strong>The</strong>se results suggest a<br />

low risk <strong>of</strong> genetic hazards associated with exposure to these chemicals.

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