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Table 2.<br />

Lung adenoma incidence in male and female A/J mice exposed to acrylamide by<br />

intraperitoneal injection (Bull et al., 1984a)<br />

Dose level 1<br />

Percent of animals with tumors<br />

(mg/kg body weight)<br />

males<br />

females<br />

0 13 8<br />

1 50 35<br />

3 38 53<br />

10 59 79<br />

30 93 93<br />

1. The exposure duration was less than lifetime (8 weeks); the dose level listed was not adjusted to<br />

reflect a less-than-lifetime exposure.<br />

Robinson et al. (1986) exposed female SENCAR, BALB/c, A/J and ICR-Swiss mice (60<br />

mice/strain/treatment group) to a single 50 mg/kg body weight dose of acrylamide by intraperitoneal<br />

injection; 2 days later 40 of the 60 mice in each treatment group received 1.0 µg (SENCAR), 2.5 µg<br />

(A/J and ICR-Swiss) or 5.0 µg (BALB/c) TPA in 0.2 ml acetone applied dermally 3 times/week for 20<br />

weeks. The remaining 20 mice/strain/treatment group received acetone alone for the same treatment<br />

schedule and duration. All animals were sacrificed at 40 weeks, and were only examined for the<br />

number of skin papillomas and lung adenomas/animal. Acrylamide induced a significant increase in the<br />

number of skin papillomas and lung adenomas per animal in SENCAR mice receiving TPA treatment.<br />

The total number of animals bearing tumors was not listed. No significant increase in either tumor type<br />

was noted in the other mouse strains tested; tumor data for the animals receiving acrylamide but not<br />

TPA was not reported.<br />

Male and female Fischer 344 rats (90/sex/treatment group) were exposed to acrylamide in drinking<br />

water for 2 years (Johnson et al., 1986). Acrylamide water concentrations were adjusted to provide<br />

dosages of 0, 0.01, 0.1, 0.5 or 2 mg/kg body weight/day. Interim sacrifices (10 animals/sex/treatment<br />

group) were performed at 6, 12 and 18 months. A maximum tolerated dose (MTD) was achieved<br />

based on decreased weight gain, increased mortality during the last 4 months of the study and the<br />

appearance of several toxic effects (including peripheral nerve degeneration) in the 2 mg/kg/day group.<br />

Increases in the incidences of a number of tumor types were observed in the 2.0 mg/kg/day exposure<br />

group animals. An increased incidence of thyroid gland-follicular epithelium tumors was observed in<br />

both males and females. In females, increased tumor incidences were noted in the mammary glands,<br />

central nervous system, oral tissues, uterus and clitoral gland. An increased incidence of scrotal<br />

mesothelioma was noted in males, in both the 2.0 and 0.5 mg/kg/day exposure group; additionally,<br />

although not statistically significant, the incidence of scrotal mesothelioma in the 0.1 mg/kg/day group<br />

was greater than either the control group or historical control incidences. Male rats in the 2.0<br />

mg/kg/day exposure group also had a significant increase in adrenal pheochromocytomas, and an<br />

increased incidence of central nervous system tumors when compared to historical controls but not<br />

when compared to concurrent controls. Tumor incidence data is listed in Table 3.<br />

34

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