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Appendix D - Dossier (PDF) - Tera

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date: 20–JUL–2005<br />

5. Toxicity Substance ID: 71–43–2<br />

______________________________________________________________________________<br />

intointernal doses, and these internal doses are used in<br />

conjunction with a multistage model to compare previous<br />

estimated virtually safe doses (VSD) associated with small<br />

added health risks. The ratio of VSD for the administered<br />

dose risk assessment to the VSD from the internal dose risk<br />

assessment was approximately 1.0 for the F344/N rats and<br />

ranged from 2.5 to 5.0 for B6C3F1 mice in the National<br />

Toxicology Program study. For an occupational exposure of<br />

1ppm, a risk estimate of 0.7 excess cancers/1000 exposed<br />

withan upper bound 3.5/1000 was obtained for a total<br />

metabolite internal dose risk assessment.<br />

Source: Deutsche Shell Chemie GmbH Eschborn ;German rapporteur<br />

Flag: Risk Assessment<br />

14–SEP–2000 (65)<br />

Type: Metabolism<br />

Remark: Cancer risk from exposure to benzene for a working lifetime<br />

was estimated from data obtained in studies with rodents.<br />

Cancers of the Zymbal gland and the blood–forming system<br />

were selected as endpoints for the assessment because of<br />

their consistent occurrence. The combined metabolites were<br />

judged from toxicological data to be the best<br />

representativeof the reactive agent. Because of similarity<br />

in the percentages of lifetime exposed in the rodent studies<br />

and inthe occupational setting, the amount metabolized/day<br />

as a result of exposures 5 days a week for a lifetime was<br />

judged to be an appropriate dose paradigm for this<br />

assessment. Derived Michaelis–Menton constants were used to<br />

convert the doses of combined metabolites from the<br />

pharmacokinetic studies to the doses used in the bioassays.<br />

Scaling across species was based on allometric<br />

relationships. Experimentaldata were used to scale doses<br />

across species with body weight ratios raised to the<br />

exponents of 0.74 for the inhalation route and 1.0 for the<br />

oral route. The occupational lifetime cancer risk estimated<br />

from rodent datawas 6 to 14 cases/1000 workers, which is<br />

consistent with the9.5 to 174 leukemia cases/1000 estimated<br />

by others from epidemiological data.<br />

Source: Deutsche Shell Chemie GmbH Eschborn<br />

06–JAN–1997 (91)<br />

Type: Metabolism<br />

Remark: A physiological pharmacokinetic model for benzene,<br />

incorporating metabolic transformations, is used to explore<br />

why benzene, but not phenol is carcinogenic at many sites<br />

inrats. The model has been parametrized using in vitro or<br />

in vivo experimental data. Ranges, rather than fixed values<br />

were assigned to the parameters. The model–predicted<br />

levelsof phenol and hydroquinone in the tissue are<br />

consistently higher when phenol, rather than benzene, is<br />

administered. This result demonstrates that the<br />

differential carcinogenicity of the two compounds is not<br />

explainable in the context of this pharmacokinetic analysis.<br />

<strong>Appendix</strong> D: Benzene SIDS <strong>Dossier</strong><br />

– 818/957 –

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