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Monograph on the Potential Human Reproductive and ... - OEHHA

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226 CHAPIN ET AL.<br />

Table 58<br />

In Vivo Genetic Toxicity Studies of Bisphenol A<br />

Species <strong>and</strong> sex Dose (route) Cells Endpoint Results Reference<br />

Male rat 85 mg/kg bw/day Germ Dominant lethality Negative B<strong>on</strong>d et al. (1980) a,b<br />

for 5 days (i.p.) (abstract <strong>on</strong>ly)<br />

Male rat 200 mg/kg bw (i.p.) DNA Adduct formati<strong>on</strong> Positive Atkins<strong>on</strong> <strong>and</strong><br />

<strong>and</strong> 200 mg/kg bw Roy (1995b)<br />

for 4, 8, 12, or 16 days (oral)<br />

Male <strong>and</strong> female 500–2000 mg/kg bw (oral) B<strong>on</strong>e marrow Micr<strong>on</strong>uclei Negative Gudi <strong>and</strong> Krsmanovic<br />

mouse (1999) a ; Shell Oil<br />

Co. (1999) b<br />

Male mouse 1 mmol/kg bw [228 mg/kg Peripheral Micr<strong>on</strong>uclei Negative Masuda et al. (2005)<br />

bw] (oral) blood<br />

reticulocyte<br />

20–22-day-old 0.02–0.100 mg/kg bw/day Oocyte C<strong>on</strong>gressi<strong>on</strong> failure Positive at all doses; Hunt et al. (2003)<br />

female mouse (oral) for 6–8 days or 0.02 mg/ statistically<br />

kg bw for 3, 5, or 7 days significant<br />

with 7-day<br />

exposure<br />

Pregnant mouse 0.4 mg/day s.c. pellet Oocyte Evaluati<strong>on</strong> of pachytene Incomplete synapsis, Susiarjo et al. (2007)<br />

GD 11.5–18.5 [B20 mg/kg bw/day] fetal oocyte <strong>and</strong> end-to-end<br />

of ploidy in oocytes associati<strong>on</strong><br />

<strong>and</strong> 2-cell of sister<br />

embryos from chromatids,<br />

adults that mhyperploidy<br />

were exposed<br />

in utero<br />

Female mouse 0.2 or 20 mg/kg bw acutely Oocyte Aneuploidy Negative Pacchierotti et al.<br />

or daily for 7 days or (2007)<br />

0.4 mg/L in drinking water<br />

for 7 weeks<br />

Male (102/ 0.002–0.2 mg/kg bw for Spermatocyte Meiotic delay Negative Pacchierotti et al.<br />

ElxC3H/El) 6 days (oral) <strong>and</strong> aneuploidy (2007)<br />

F 1 mouse<br />

Drosophila 10,000 ppm (oral) Offspring Sex-linked recessive Negative Foureman et al.<br />

melanogaster lethal test (1994) a,b<br />

Turbot 50 ppb in aquarium Erythrocyte Micr<strong>on</strong>uclei Positive Bolognesi et al.<br />

water for 2 weeks (2006)<br />

a Reviewed by Haight<strong>on</strong> et al. (2002).<br />

b Reviewed by European-Uni<strong>on</strong> (2003).<br />

days. The study authors c<strong>on</strong>cluded that bisphenol A was<br />

a potential meiotic aneugen.<br />

In a follow-up study (Susiarjo et al., 2007), pregnant<br />

C57Bl/6 mice <strong>on</strong> GD 11.5 were implanted with s.c. pellets<br />

designed to release bisphenol A 0 or 0.4 mg/day. [The<br />

authors assume a 20 g bw, giving an estimated dose<br />

level of 20 lg/kg bw/day.] Oocytes from GD 18.5 female<br />

fetuses showed an increase in pachytene synaptic<br />

abnormalities including incomplete synapsis <strong>and</strong> endto-end<br />

associati<strong>on</strong>s of sister chromatids. There was also<br />

paradoxically an increase in recombinant foci in pachytene<br />

oocytes of bisphenol A-exposed females. Some<br />

female offspring of bisphenol A-treated dams were<br />

fostered to untreated dams. Eggs or 2-cell embryos from<br />

<strong>the</strong>se female offspring at 4–5 weeks of age showed an<br />

increase in hyperploidy. Pachytene oocyte abnormalities<br />

similar to those identified in fetuses exposed to bisphenol<br />

A were seen in oocytes obtained from ERb<br />

knock-out mice, suggesting to <strong>the</strong> authors that bisphenol<br />

A may exert adverse effects <strong>on</strong> meiosis by blocking ERb.<br />

In resp<strong>on</strong>se to <strong>the</strong> study of Hunt et al. (2003),<br />

Pacchierotti et al. (2007) investigated <strong>the</strong> aneugenic<br />

effects of bisphenol A in mouse somatic <strong>and</strong> germ cells.<br />

C57Bl/6 female mice were superovulated using pregnant<br />

mare serum <strong>and</strong> hCG after which <strong>the</strong>y were gavaged<br />

with bisphenol A 0.2 or 20 mg/kg bw. Metaphase II<br />

oocytes were collected after 17 hr <strong>and</strong> evaluated using Cb<strong>and</strong>ing.<br />

Additi<strong>on</strong>al female mice were gavaged with<br />

bisphenol A 0.04 mg/kg bw/day for 7 days or were<br />

given bisphenol A in drinking water at a c<strong>on</strong>centrati<strong>on</strong> of<br />

0.4 mg/L for 7 weeks. These mice were superovulated at<br />

<strong>the</strong> end of <strong>the</strong> 7-day or 7-week treatment period <strong>and</strong><br />

housed overnight with untreated males. Females without<br />

vaginal plugs were killed for evaluati<strong>on</strong> of oocytes by Cb<strong>and</strong>ing.<br />

Females with vaginal plugs were treated with<br />

colchicine to prevent <strong>the</strong> first embry<strong>on</strong>ic cleavage, <strong>and</strong><br />

zygotes were collected <strong>the</strong> next morning for evaluati<strong>on</strong><br />

by C-b<strong>and</strong>ing. There were no bisphenol A effects <strong>on</strong><br />

inducti<strong>on</strong> of aneuploidy. There was a statistically<br />

significant increase in premature centromere separati<strong>on</strong><br />

in <strong>the</strong> group treated for 7 weeks, but <strong>the</strong>re was no effect<br />

of bisphenol A treatment <strong>on</strong> <strong>the</strong> proporti<strong>on</strong> of zygotes<br />

with structural or numeric chromosome changes. Male<br />

mice were treated with bromodeoxyuridine 8 days before<br />

being treated with bisphenol A 0.2 mg/kg bw/day for 6<br />

days. Evaluati<strong>on</strong> of sperm after 21–25 days did not show<br />

a significant mitotic delay in spermatocytes. Additi<strong>on</strong>al<br />

male mice were given bisphenol A orally at doses of 0,<br />

Birth Defects Research (Part B) 83:157–395, 2008

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