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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 />

06–JAN–1997 (93)<br />

Remark: This is a textbook on occupational epidemiology. Chapters<br />

are devoted to epidemiologic study design, conduct,<br />

analysis, and interpretation. Examples of concepts are<br />

illustrated with examples from the occupational<br />

epidemiologyliterature.<br />

Source: Deutsche Shell Chemie GmbH Eschborn<br />

06–JAN–1997 (791)<br />

Remark: This document presents results of a re–evaluation of the<br />

carcinogenic potency of benzene. The authors develop a<br />

mathematical model, consistent with a two–stage theory of<br />

carcinogenesis, that takes variable exposure and latency<br />

period into account. This model evolved by substituting in<br />

a sequential manner more plausible and scientifically<br />

defensible assumptions than those originally employed by<br />

EPA(1985). Two factors have the most pronounced effect<br />

upon<br />

the alteration of the unit risk estimate. These are the<br />

useof new statistical methods, primarily estimation<br />

techniques,and the requirement that two molecules of a<br />

benzene metabolite are needed to cause the transforming<br />

event. Since exposure for the pliofilm cohort was most<br />

probably underestimated and strong empirical and<br />

theoretical<br />

evidenceexists suggesting that the relationship between<br />

benzene metabolites and the cell transforming event is<br />

non–linear, the linear model should be viewed as a highly<br />

conservative upper bound. The authors also present<br />

evidence<br />

that very distant benzene exposures (e.g. > 30 years before<br />

disease) may be irrelevant in determining risk.<br />

Source: Deutsche Shell Chemie GmbH Eschborn<br />

06–JAN–1997 (1129)<br />

Remark: Chromosome changes are studied in 21 cases of chronic<br />

benzene poisoning (avg 6 years exposure; range 1–28 years),<br />

both hypodiploid and hyperdiploid cells are significantly<br />

increased. Controls comprised 20 healthy subjects. Among<br />

the hypodiploid cells, deletion of Group C, E and G<br />

chromosomes is observed. Analysis of hyperdiploid cells<br />

reveals extra Group C and E chromosomes. The chromatid<br />

gapsand breaks are mostly found in poisoned cases, but<br />

fragmentsand minutes are less common. However, the finding<br />

of aneuploidy may not indicate that aneuploidy is a<br />

sensitive effect indicator of benzene because some subjects<br />

had simultaneous or previous benzene haemopathy.<br />

Source: Deutsche Shell Chemie GmbH Eschborn<br />

06–JAN–1997 (300)<br />

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

– 708/957 –

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