Monograph on the Potential Human Reproductive and ... - OEHHA
Monograph on the Potential Human Reproductive and ... - OEHHA
Monograph on the Potential Human Reproductive and ... - OEHHA
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378 CHAPIN ET AL.<br />
Table 103<br />
Summary of Blood LH <strong>and</strong> Testoster<strong>on</strong>e Changes in Experimental Animal Studies<br />
Endpoints/protocol LH effects a<br />
Testoster<strong>on</strong>e effects a<br />
Reference<br />
High Utility<br />
Experimental animal studies<br />
with oral exposure<br />
Adult male <strong>and</strong> female rats 2 at 40–1000 mg/kg bw/day 2 at 40–1000 mg/kg bw/day Yamasaki et al. (2002a)<br />
gavaged for 28 days<br />
4-week-old male rats fed Not examined 2 at 235–950 mg/kg bw/day Takahashi <strong>and</strong> Oishi (2001,<br />
bisphenol A in diet for 44 or or 200 mg/kg bw/day 2003)<br />
60 days<br />
Multiple generati<strong>on</strong> gavage k in F0 adult females at 0.0002, 2 Ema et al. (2001)<br />
dosing study in rats 0.002, <strong>and</strong> 0.020 mg/kg bw/<br />
day but not at high dose<br />
(0.2 mg/kg bw/day); not<br />
c<strong>on</strong>sidered treatmentrelated.<br />
Experimental animal studies<br />
with parenteral exposure<br />
Female lambs i.m. injected at 4– 2 <strong>on</strong> blood levels during Not examined Evans et al. (2004)<br />
11 weeks of age; ovariectomy treatment; k pulsatile<br />
at 9 weeks of age secreti<strong>on</strong> after treatment with<br />
3.5 mg/kg bw biweekly<br />
Limited utility<br />
Experimental animal studies<br />
with oral exposure<br />
Male rats gavaged from PND k at 0.0024 mg/kg bw/day but k at 0.0024 mg/kg bw/day but Akingbemi et al. (2004)<br />
21–35 2 at higher doses (0.010– 2 at higher doses (0.010–<br />
200 mg/kg bw/day) 200 mg/kg bw/day)<br />
Male rats gavaged from PND m at 0.0024 mg/kg bw/day 2 at 0.0024 mg/kg bw/day Akingbemi et al. (2004)<br />
21–90<br />
4-week-old mice fed bisphenol Not examined 2 at 400 mg/kg bw/day Takahashi <strong>and</strong> Oishi (2003)<br />
A through diet for 2 m<strong>on</strong>ths<br />
Experimental animal studies<br />
with parenteral exposure<br />
4-week-old male rats s.c. dosed Not examined 2 at 200 mg/kg bw Takahashi <strong>and</strong> Oishi (2003)<br />
<strong>on</strong> 4 days/week for 1 m<strong>on</strong>th<br />
4-week-old male rats i.p. Not examined k at 20 mg/kg bw Takahashi <strong>and</strong> Oishi (2003)<br />
injected for 1 m<strong>on</strong>th<br />
a Unless o<strong>the</strong>rwise stated, animals were examined immediately after <strong>the</strong> treatment period.<br />
m,k Statistically significant increase/decrease compared to c<strong>on</strong>trols; 2 no statistically significant effects compared to c<strong>on</strong>trols.<br />
Utility (Adequacy) for CERHR Evaluati<strong>on</strong> Process: This<br />
study suggests that fish are sensitive to bisphenol Ainduced<br />
abnormalities in reproductive endpoints. Because<br />
this study was c<strong>on</strong>ducted in fish, it is not useful in<br />
<strong>the</strong> evaluati<strong>on</strong>.<br />
Ortiz-Zarragoitia <strong>and</strong> Cajaraville (2006), supported by<br />
<strong>the</strong> European Commissi<strong>on</strong>, examined <strong>the</strong> effects of<br />
bisphenol A exposure <strong>on</strong> <strong>the</strong> reproductive <strong>and</strong> digestive<br />
systems of adult blue mussels. For a period of 3 weeks,<br />
mussels were exposed to bisphenol A in acet<strong>on</strong>e vehicle<br />
at 0 or 50 ppb [lg/L] [no informati<strong>on</strong> <strong>on</strong> purity or<br />
culture ware was provided]. Additi<strong>on</strong>al compounds<br />
were also tested but will not be discussed. Ten mussels/<br />
sex/group were examined at <strong>the</strong> end of <strong>the</strong> exposure<br />
period. The digestive gl<strong>and</strong> was examined for volume of<br />
peroxisomes <strong>and</strong> peroxisomal proliferati<strong>on</strong>. G<strong>on</strong>ads were<br />
histologically evaluated <strong>and</strong> assessed for alkali-labile<br />
phosphate level, a vitellogenin-like protein that is a<br />
possible biomarker of endocrine disrupti<strong>on</strong>. Statistical<br />
analyses included ANOVA followed by Duncan post-hoc<br />
test, Kruskall–Wallis, <strong>and</strong> Mann–Whitney U test.<br />
Bisphenol A had no effect <strong>on</strong> g<strong>on</strong>adal development,<br />
g<strong>on</strong>adal alkali-labile phosphate levels, or digestive gl<strong>and</strong><br />
peroxisomal proliferati<strong>on</strong> or peroxisomal volume. However,<br />
observati<strong>on</strong>s of follicular brown cell aggregates <strong>and</strong><br />
g<strong>on</strong>adal hemocyte infiltrati<strong>on</strong> in 35% of male <strong>and</strong> female<br />
mussels indicated severe gamete resorpti<strong>on</strong>.<br />
Strengths/Weaknesses: This study evaluated bisphenol<br />
A-induced alterati<strong>on</strong>s in several reproductive endpoints<br />
in adult mussels. Severe gamete resorpti<strong>on</strong> was<br />
observed. Weaknesses include <strong>the</strong> failure to c<strong>on</strong>firm<br />
bisphenol A c<strong>on</strong>centrati<strong>on</strong>s in <strong>the</strong> test water <strong>and</strong> <strong>the</strong> use<br />
of <strong>on</strong>ly 1 c<strong>on</strong>centrati<strong>on</strong>.<br />
Utility (Adequacy) for CERHR Evaluati<strong>on</strong> Process:<br />
Because this study was c<strong>on</strong>ducted in <strong>the</strong> mussel, it is not<br />
useful in <strong>the</strong> evaluati<strong>on</strong>.<br />
4.3 Utility of <strong>Reproductive</strong> Toxicity Data<br />
4.3.1 <strong>Human</strong>. One high utility study of 42 men<br />
occupati<strong>on</strong>ally exposed to bisphenol A diglycidyl e<strong>the</strong>r<br />
<strong>and</strong> 42 unexposed men evaluated <strong>the</strong> relati<strong>on</strong>ship<br />
Birth Defects Research (Part B) 83:157–395, 2008