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3,3-DICHLOROBENZIDINE<br />

CAS No: 91-94-1<br />

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

Molecular weight 253.1<br />

Boiling point 402°C<br />

Melting point<br />

132-133°C<br />

Vapor pressure<br />

unknown<br />

Air concentration conversion 1 ppm = 10.4 mg/m 3 (IARC, 1982)<br />

II.<br />

HEALTH ASSESSMENT VALUES<br />

Unit Risk Factor: 3.4 E-4 (µg/m 3 ) -1<br />

Slope Factor: 1.2 E+0 (mg/kg-day) -1<br />

[Calculated from a cancer potency factor derived by RCHAS/<strong>OEHHA</strong> (CDHS, 1988)]<br />

III.<br />

CARCINOGENIC EFFECTS<br />

Human Studies<br />

The body of literature addressing the carcinogenicity of 3,3’-dichlorobenzidine in humans is scant.<br />

Three retrospective epidemiological studies of occupational exposure have been conducted, focusing on<br />

the possibility that 3,3’-dichlorobenzidine is a bladder carcinogen like its parent compound, benzidine.<br />

None of the studies approximates exposure levels.<br />

Gerarde and Gerarde (1974) conducted a study of 175 workers involved in the manufacture and use of<br />

dichlorobenzidine in a chemical manufacturing plant in the United States between 1938 and 1957.<br />

Workers were segregated from benzidine exposure. No bladder tumors were found among the<br />

exposed workers. General population incidence of bladder tumors predicts 0-2 cases in a cohort of<br />

this size.<br />

Gadian (1975) conducted a study of 35 British workers exposed to dichlorobenzidine who had been<br />

segregated from exposure to benzidine in a chemical plant from 1953 to 1973. Cumulative hours of<br />

exposure were tabulated for all workers. No tumors were reported among the exposed workers at the<br />

end of the study (through 1973).<br />

MacIntyre (1975) reports on bladder tumor incidence among 225 Scottish production and service<br />

workers, 119 of which had more than 5 years of exposure to dichlorobenzidine and 36 of which were<br />

247

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