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Methodology<br />

The complex and potentially variable mix of chemical species in the condensed phase and the vapor<br />

phase of diesel exhaust, required the measure of exposure related to carcinogenic risk to be specified.<br />

The most commonly used measure of exposure is atmospheric concentration of particles in µg/m 3 . That<br />

measure is obtained from the mass of particles collected on a filter per volume of the air that flowed<br />

through the filter. On the basis of its relation to health studies and its general practicality, that measure<br />

was used in the diesel exhaust TAC document cancer risk assessment (<strong>OEHHA</strong>, 1998).<br />

<strong>OEHHA</strong> used two approaches to employing epidemiological studies for diesel exhaust quantitative risk<br />

assessment. The first approach used the overall relative risks derived from the meta-analysis along with<br />

an overall range of exposure for all the studies. The second approach focused upon the railroad worker<br />

studies in developing the range of unit cancer risks.<br />

Meta-analysis-Derived Cancer Unit Risks<br />

The results of the meta-analysis provide in<strong>format</strong>ion useful in bracketing the broadest likely range of<br />

plausible carcinogenic potencies for diesel exhaust. The pooled relative risk values derived from the 12<br />

epidemiological studies in the meta-analysis which adjusted for smoking were 1.44 (95% C.I. 1.32 -<br />

1.56) for the fixed effects model and 1.43 (95% C.I. 1.31 -1.57) for the random effects model. The<br />

magnitude of these relative risks provide in<strong>format</strong>ion on the potential magnitude of the cancer risk<br />

associated with diesel exhaust exposure. For the random effects model the upper 95% confidence limit<br />

on excess relative risk is 0.57.<br />

None of the studies in the meta-analysis provide direct measurements of exposure concentration over<br />

the time of their follow up. Therefore, to the extent that the meta-analysis can be used to bracket the<br />

carcinogenic potency of diesel exhaust, the exposures of the various study populations need to be<br />

reconstructed. Hammond (1998) has reviewed the available industrial hygiene survey literature on the<br />

occupations considered in the meta-analysis (bus garage workers, mechanics, truck drivers, heavy<br />

equipment operators, railroad workers) and provided estimates of the plausible possible ranges of<br />

workplace exposures of diesel exhaust respirable particulate matter for those occupations. Because of<br />

the overall limitations in the data, the estimated ranges for each occupational subgroup of interest are<br />

particularly broad. The lowest plausible estimate of occupational exposure for any such subgroup is 5<br />

µg/m 3 (heavy equipment operators). The highest plausible estimate of any occupational subgroup is 500<br />

µg/m 3 (bus garage workers, railroad workers, mechanics). The total range of plausible exposures for<br />

the different populations therefore varies 100-fold. Using these air concentrations and the assumption<br />

that workers inhaling 10m 3 of air per work shift were exposed to them for over 45 year period for a 70<br />

year lifetime, it is possible to characterize a bracket of risks compatible with the results of the metaanalysis:<br />

457

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