Adverse health effects of bisphenol A: Chahoud's response. (Correspondence).Heinze stated in his letter that according to two long-term studies, bisphenol A (BPA BPA British Paediatric Association. ) does not induce any effect on reproduction in offspring at the low dose level. Several other studies have reported adverse effects of BPA; I briefly discuss two examples below. Markey et al. (2001) investigated the effect of fetal exposure to BPA [25 and 250 [micro]g/kg body weight (bw)] on the development of the mammary gland mammary gland, organ of the female mammal that produces and secretes milk for the nourishment of the young. A mammal may have from 1 to 11 pairs of mammary glands, depending on the species. Generally, those mammals that bear larger litters have more glands. in CD-1 mice. They concluded their results as follows: The altered relationship in DNA synthesis between the epithelium and stroma and the increase in terminal ducts and terminal end buds are striking, because these changes are associated with carcinogenesis in both rodents and humans. Kawai et al. (2003) carried out a study to evaluate the effect of fetal exposure to BPA (2 and 20 ng/kg bw) on male offspring. They observed that in utero in utero (in u´ter-o) [L.] within the uterus. in u·ter·o adj. In the uterus. in utero adv. exposure at these dose levels resulted in significantly reduced relative testis testis (tĕs`tĭs) or testicle (tĕs`tĭkəl), one of a pair of glands that produce the male reproductive cells, or sperm. weight and concluded that low doses of BPA interfered with the normal development of reproductive organs Reproductive organs The group of organs (including the testes, ovaries, and uterus) whose purpose is to produce a new individual and continue the species. Mentioned in: Choriocarcinoma . I would like to take the opportunity to discuss the problem of the interpretation of so-called negative studies. Ashby et al. (1999) aimed to disprove disprove, v to refute or to prove false by affirmative evidence to the contrary. studies published by vom Saal and colleagues (Nagel et al. 1997; vom Saal et al. 1997, 1998). Ashby et al. were not able to confirm the results described by vom Saal and colleagues; however, their study (2 and 20 [micro]g BPMkg bw) shows significantly elevated testis and epididymal epididymal emanating from or pertaining to the epididymis. epididymal inflammation see epididymitis. epididymal segmental aplasia a defect in mesonephric development in which part of the epididymis is missing. weights, even after adjustment for body weight. Ashby et al. considered this clear effect "an equivocal finding." Tyl et al. (2002) conducted a three-generation reproductive toxicity reproductive toxicity Any adverse effect attributable to exposure to a chemical, directed against the reproductive and/or related endocrine systems Adverse effects Altered sexual behavior, fertility, pregnancy outcomes, or modifications in other functions that study on dietary BPA in CD Sprague-Dawley rats. The [F.sub.2] generation showed no statistically significant difference in body weight compared to the control. However, at doses of 1 [micro]g, 300 [micro]g, and 5,000 [micro]g BPA/kg bw, the absolute and relative paired ovary ovary, ductless gland of the female in which the ova (female reproductive cells) are produced. In vertebrate animals the ovary also secretes the sex hormones estrogen and progesterone, which control the development of the sexual organs and the secondary sexual weights exhibited a significant decrease in the [F.sub.2] generation compared to control. Tyl et al. considered these effects not biologically significant. Investigators are in the position to interpret the adversity of their own data, and readers also have the freedom to build their own opinion regarding the adversity of the effects. In conclusion, I would like to emphasize the need for mechanistic experimental studies as well as follow-up studies in humans regarding low-dose effects. The author declares he has no conflict of interest. REFERENCES Ashby J, Tinwell H, Hasemann J. 1999. Lack of effects for low dose levels of bisphenol A and diethylstilbestrol diethylstilbestrol: see DES. on the prostate gland of CF-1 mice exposed in utero. Regul Toxicol Pharmacol 30:156-166. Kawai K, Nozaki T, Nishikata H, Aou S, Takii M, Kubo C. 2003. Aggressive behavior and serum testosterone concentration during the maturation process of male mice: the effects of fetal exposure to bisphenol A. Environ Health Perspect 111:175-178. Markey CM, Luque EH, Munoz de Toro M, Sonnenschein C, Soto AM. 2001. In utero exposure to bisphenol A alters the development and tissue organization of the mouse mammary gland. Biol Reprod 65:1215-1223. Nagel SC, vom Saal FS, Thayer KA, Dhar MG, Boechler M, Welshons WV. 1997. Relative binding affinity-serum modified access (RBA-SMA) assay predicts the relative in vivo in vivo /in vi·vo/ (ve´vo) [L.] within the living body. in vi·vo adj. Within a living organism. in vivo adv. bioactivity bi·o·ac·tiv·i·ty n. The effect of a given agent, such as a vaccine, upon a living organism or on living tissue. of the xenoestrogens bisphenol A and octylphenol. Environ Health Perspect 105:70-76. Tyl RW, Myers CB, Marr MC, Thomas BF, Keimowitz AR, Brine DR, et al. 2002. Three-generation reproductive toxicity study of dietary bisphenol A in CD Sprague-Dawley rats. Toxicol Sci 68:121-146. vom Saal FS, Cooke PS, Buchanan DL, Palanza P, Thayer KA, Nagel SC, et al. 1997. A physiologically based approach to the study of bisphenol A and other estrogenic chemicals on the size of reproductive organs, daily sperm production, and behavior. Toxicol Ind Health 14(1-2):239-260. vom Saal FS, Timms BG, Montano MM, Palanza P, Thayer KA, Nagel SC, et al. 1998. Prostate enlargement in mice due to fetal exposure to low doses of estradiol or diethylstilbestrol and opposite effects at high doses. Proc Natl Acad Sci USA 94(5):2056-2061. Ibrahim Chahoud Institute of Clinical Pharmacology and Toxicology Free University Berlin Berlin, Germany E-mail: chahoud@zedat.fu-berlin.de |
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