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1,4-DIOXANE<br />

CAS No: 123-91-1<br />

I. PHYSICAL AND CHEMICAL PROPERTIES (From ACGIH, 1994)<br />

Molecular weight 88.1<br />

Boiling point<br />

101.1°C<br />

Melting point<br />

11.8°C<br />

Vapor pressure 29 mm Hg @ 20°C<br />

Air concentration conversion 1 ppm = 3.6 mg/m 3<br />

II.<br />

HEALTH ASSESSMENT VALUES<br />

Unit Risk Factor: (7.7 E-6 µg/m 3 ) -1<br />

Slope Factor: 2.7 E-2 (mg/kg-day) -1<br />

[Calculated from a cancer potency factor derived by RCHAS/<strong>OEHHA</strong> (CDHS, 1989)]<br />

III.<br />

CARCINOGENIC EFFECTS<br />

Human Studies<br />

The two human epidemiological studies of the potential carcinogenicity of 1,4-dioxane (Thiess et al.<br />

(1976); Buffler et al. (1978)) did not show significant changes in the incidence of carcinogenicity.<br />

However, neither study had sufficient statistical power to detect moderate changes in cancer incidence<br />

due to the small size of the sample groups or the short duration of the studies.<br />

In the study by Thiess et al. (1976), 74 German workers were exposed to various concentrations of<br />

1,4-dioxane for an average of 24.9 years. Of the 74 workers, 24 were working at the end of the<br />

follow-up period (1964 - 1974), 23 were no longer working, 15 had retired, and 12 had died. Of the<br />

12 deaths, two were attributed to neoplastic diseases (1 lamellar epithelial carcinoma and 1<br />

myelofibrotic leukemia). The expected number of deaths during this period in the cohort was 14.5,<br />

based on Federal Republic of Germany mortality statistics. The overall death rate and the cancer death<br />

rate were not significantly increased over controls.<br />

Buffler et al. (1978) studied the mortality of 165 workers exposed to 1,4-dioxane in a dioxanemanufacturing<br />

and processing facility in Texas. The employees were exposed to dioxane for at least 1-<br />

month up to 21 years (April, 1954 to June, 1975), and were divided into two cohorts. The cohort of<br />

manufacturing workers was composed of 100 individuals, and the processing workers numbered 65.<br />

The concentrations of dioxane in the workplaces were less than 25 ppm. Seven deaths occurred in the<br />

manufacturing cohort (4.9 expected), two from neoplasms (0.9 expected). Five deaths occurred in the<br />

processing cohort (4.9 expected), one from cancer (0.8 expected). These mortality and cancer rates<br />

were not higher than the expected from Texas age- and sex-specific death rates for 1960-1969. Due<br />

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