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Center for Biomedical Research, The Population Council (B.T.A., C.M.S., A.I.K., M.P.H.), New York, New York 10021; and Reproductive Toxicology Division, National Health and Environmental Effects Research Laboratory, United States Environmental Protection Agency (G.R.K.), Research Triangle Park, North Carolina 27711
Address all correspondence and requests for reprints to: Dr. Matthew P. Hardy, The Population Council, 1230 York Avenue, New York, New York 10021. E-mail: m-hardy{at}popcbr.rockefeller.edu.
Exposure of humans to bisphenol A (BPA), a monomer in polycarbonate plastics and a constituent of resins used in food packaging and dentistry, is significant. In this report exposure of rats to 2.4 µg/kg·d (a dose that approximates BPA levels in the environment) from postnatal d 2135 suppressed serum LH (0.21 ± 0.05 ng/ml; vs. control, 0.52 ± 0.04; P < 0.01) and testosterone (T) levels (1.62 ± 0.16 ng/ml; vs. control, 2.52 ± 0.21; P < 0.05), in association with decreased LHß and increased estrogen receptor ß pituitary mRNA levels as measured by RT-PCR. Treatment of adult Leydig cells with 0.01 nM BPA decreased T biosynthesis by 25% as a result of decreased expression of the steroidogenic enzyme 17
-hydroxylase/1720 lyase. BPA decreased serum 17ß-estradiol levels from 0.31 ± 0.02 ng/ml (control) to 0.22 ± 0.02, 0.19 ± 0.02, and 0.23 ± 0.03 ng/ml in rats exposed to 2.4 µg, 10 µg, or 100 mg/kg·d BPA, respectively, from 2135 d of age (P < 0.05) due to its ability to inhibit Leydig cell aromatase activity. Exposures of pregnant and nursing dams, i.e. from gestation d 12 to postnatal d 21, decreased T levels in the testicular interstitial fluid from 420 ± 34 (control) to 261 ± 22 (P < 0.05) ng/ml in adulthood, implying that the perinatal period is a sensitive window of exposure to BPA. As BPA has been measured in several human populations, further studies are warranted to assess the effects of BPA on male fertility.
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