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Potency Equivalency Factors (PEF) for PAHs and derivatives. It has a cancer potency of 11.5 (mg/kgday)<br />

-1 and inhalation unit risk of 1.1 × 10 3 (µg/m 3 ) -1 . For the potency equivalency scheme, it was<br />

assigned a PEF of 1.<br />

2. Dibenz[a,h,]anthracene. An expedited potency of 4.1 (mg/kg-day) -1 was derived using the<br />

linearized multistage model with the only dose-response data set available - a drinking water study<br />

(Snell and Stewart, 1962) which reported alveolar carcinomas of the lung in male DBA/2 mice due to<br />

dibenz[a,h]anthracene (incidence = 14/21 at 28.3 mg/kg-day versus 0/25 in controls). An inhalation<br />

unit risk can be obtained from a potency under the assumption that the chemicals are equally absorbed<br />

and are equally potent by oral and inhalation routes and that a 70 kg person inhales 20 cubic meters of<br />

air per day. When the potency in units of (mg/kg-day) -1 is divided by 3500 (70 kg * 1000 µg/mg/20<br />

m 3 ), an inhalation unit risk is obtained in units of (µg/m 3 ) -1 .<br />

3. 7,12-Dimethylbenzanthracene. An expedited potency of 250 (mg/kg-day) -1 was derived. The only<br />

study listed in the Gold et al. cancer potency (TD50) database (Gold et al., 1984; 1986; 1987; 1989;<br />

1990) is the feeding study by Chourolinkov et al. (1967) in female albino mice. Significant increases in<br />

malignant angioendotheliomas of the mesenteric intestine and papillomas of the forestomach were<br />

observed in animals treated with 0.39 mg/kg-day of 7,12-dimethylbenzanthracene. Cancer potency is<br />

based on mesenteric intestine angioendothelioma incidence (incidence = 49/75 versus 0/40 in controls).<br />

4. 3-Methylcholanthrene. An expedited potency of 22 (mg/kg-day) -1 was derived. Results of 3<br />

studies in male Long Evans rats, one study in an unspecified strain of female rats, and 10 studies in<br />

female Wistar rats were included in the Gold et al. database. All studies in female rats found highly<br />

significant increases in tumors of the mammary gland. The cancer potency for 3-methylcholanthrene<br />

was taken as the geometric mean of cancer potencies estimated from 9 of the 10 studies in female rats<br />

(Shay et al., 1962; Gruenstein et al., 1964; Shay et al., 1961). The upper bound on potency could<br />

not be estimated from one of the studies by Shay et al. (1961), because 100% of the treated animals<br />

developed mammary gland tumors.<br />

5. 5-Nitroacenaphthene. An expedited potency of 0.13 (mg/kg-day) -1 was derived based on the<br />

combined incidence of benign and malignant tumors of the ear canal in female rats. Usable studies were<br />

feeding studies by Takemura et al. (1974) in female Syrian golden hamsters and by the National Cancer<br />

Institute (1978) in male and female B6C3F 1 mice and F344 rats. The compound 5-nitroacenaphthene<br />

induced increases in tumor incidences at multiple sites in rats and female mice. Rats were the most<br />

sensitive species; the sensitivity of males were similar to that of females.<br />

6. Benzo[b]fluoranthene. Benzo[b]fluoranthene was assigned a PEF of 0.1. Clement Associates<br />

(1988) applied both a two stage model and the multistage model to various data sets for several PAHs.<br />

The two models generally gave similar results for relative potency. In order to verify the results,<br />

<strong>OEHHA</strong> staff (<strong>OEHHA</strong>, 1993) used GLOBAL86 to fit the multistage model to the tumor data used by<br />

Clement Associates and obtained relative cancer potencies similar to those obtained by Clement<br />

Associates. Clement Associates (1988) used the mouse skin carcinogenesis data obtained by Habs et<br />

al. (1980) and the intrapulmonary administration to rats by Deutsch-Wenzel et al. (1983) to estimate a<br />

110

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