BPA crosses the placenta, remains active in the fetus, show rat and human studies.

Jun 07, 2010

Nishikawa, M, H Iwano, R Yanagisawa, N Koike, H Inoue and H Yokota. 2010. Placental transfer of conjugated bisphenol A and subsequent reactivation in the rat fetusEnvironmental Health Perspectives http://dx.doi.org/10.1289/ehp.0901575.

Balakrishnan, B, K Henare, EB Thorstensen, AP Ponnampalam and MD Mitchell. 2010. Transfer of bisphenol A across the human placenta. American Journal of Obstetrics and Gynecology 202:393e1-e7.




2010-0606trainingbabywithplacenta
occipita/Flickr

 

Two new studies - one human and one rat - show that active BPA and its inactive metabolite freely cross the placenta from a pregnant mother to the fetus. Even more important are the chemical transformations that occur in the fetus: the active form of BPA remains active while the inactive form can be converted to the active form. Together, these studies provide evidence that prebirth exposures occur in people and may pose a bigger risk to the developing fetus than previously thought.

 


Context

Bisphenol A (BPA) is a component of polycarbonate plastics and is used in the resins that line food and beverage cans. Its presence in plastic baby bottles and infant formula cans is of particular concern because of exposures during early life development.

People are routinely exposed to BPA through a variety of consumer products, including certain plastic water bottles, dental sealants, can linings and some carbonless copy receipts. The main source of exposure, though, is most likely from food. More than 90 percent of Americans have detectable levels of BPA metabolites in their urine. BPA has been measured in blood taken from adults, pregnant women and fetuses. It has been detected in human placenta, amniotic fluid, fat and breast milk.

The low levels found in people are similar to those that have profound effects on laboratory animals. Research suggests that low levels of BPA change the development of the mouse mammary gland, prostate, uterus and brain, and significantly alters the behavior of exposed mice and rats.

Only a few studies have examined human exposure and possible effects. To study drug exposures, exposed populations are compared to unexposed groups. With BPA, all people are thought to be exposed, making comparisons very difficult.

Nonetheless, two studies have found that adults with higher levels of BPA in their urine are more likely to have heart disease and diabetes. Several other small studies have linked higher BPA levels with miscarriage, polycystic ovarian syndrome and altered hormone levels.

Only a few studies have followed what happens to BPA after it is eaten. During digestion, BPA is "tagged" with a glucuronide group. This metabolite – BPA-glucuronide – can leave the body in urine. Unlike BPA, BPA-glucuronide does not have hormonal activity, and several studies suggest that it is not harmful.

There are many unanswered questions about this process. Does it occur if BPA is breathed or absorbed through the skin? How long does it take for BPA to be inactivated? Does BPA-glucuronide convert back to BPA?

Tied into this is the question of whether BPA in pregnant women can reach the fetus, whether BPA-glucuronide can cross the placenta and if it can be converted to BPA there.

This is an incredibly important issue. First, the fetus is especially sensitive to hormones. Exposure to estrogens during this time of development can lead to wide ranging effects that may be postponed until puberty or adulthood. Second, if the mother can metabolize BPA efficiently, then the fetal exposure should be limited and concerns about BPA's health impacts lessened.

What did they do?

Nishikawa and colleagues injected either 2 or 10 micromolar concentrations of BPA-glucuronide into pregnant rats. These concentrations are relatively high and are probably not relevant to human exposure levels. However, high concentrations are necessary because they allow researchers to measure the low levels of BPA moving through the pregnant rats, the fetuses and the amniotic fluid.

The scientists collected samples of the fetal tissues and the amniotic fluid that surrounds the developing rats and analyzed the tissues and fluid for both BPA-glucuronide – the inactive form – and "free" BPA – the estrogenic and active form. From these data, they determined whether BPA-glucuronide could cross the placenta and whether it is converted to free BPA by the fetus.

They also determined whether the rat fetuses had turned on genes for enzymes that 1) break down BPA-glucuronide into the estrogenic BPA and 2) convert BPA to BPA-glucuronide, the inactive form.

In the second study, Balakrishnan and colleagues used human placentas gathered from Cesarean section births. A pump that simulated the mother's heart was hooked to the mother's blood vessels in the placenta. Solutions containing 10 nanograms per milliliter of BPA were pumped for several hours. This concentration was chosen because it is thought to be in the upper range of actual human exposures. The fluid that was pumped from the maternal side of the placenta to the fetal side was collected and levels of "free" and active form of BPA and the metabolized BPA-glucuronide were measured.

What did they find?

Taken together these studies clearly show that: 1) BPA inactive metabolites and the free active BPA can cross the placental barrier; 2) once free BPA crosses into the fetus, it mostly remains in its estrogenically active form; and 3) once the inactive BPA metabolite crosses into the fetus, it can be converted to the active form.

Both BPA and BPA-glucuronide were detected in the rat fetal tissues and in amniotic fluid at both the 2 and 10 micromolar concentrations. This means the BPA-glucuronide can cross the placental barrier and into the amniotic fluid surrounding the rat fetuses. Once across the placenta, the fetus can break it down to the active, estrogenic form of BPA.

From the smaller dose, the researchers calculated that very low amounts – less than 0.1 percent of the administered dose – crossed into the fetus.

Nishikawa et al. also found that both the rat fetal liver and heart make an enzyme that can convert the inactive BPA-glucuronide into the estrogenic and active form of BPA. Enzymes are proteins that moderate chemical reactions – like the conversion of less toxic BPA metabolites to the more toxic BPA. The presence of the enzyme explains why the BPA-glucuronide administered to the mother rat could be converted to the more toxic form of BPA in the fetuses.

In the second study, Balakrishnan and colleagues show BPA can cross the human placenta from mother to fetus. They found that 27 percent of the BPA applied to the mother's side of the placenta is carried to the fetal side. Like the results reported in rats, this indicates that the placenta does not protect the fetus from this chemical.

In addition, more than 95 percent of the BPA recovered from the fetal portion of the placenta was still in the free, estrogenic, active form. Therefore, very little of the BPA that crossed from mother to fetus was inactivated, indicating that the human fetus is exposed to the estrogenic type of BPA.


What does it mean?

These two studies clearly indicate that BPA – in both its active and inactive form – can cross the placenta into the fetus where most of the active form remains active and some of the inactive form is converted to the active form.

The results are especially concerning because they indicate the fetus may be at greater risk from BPA exposures than previously thought. In non-pregnant adults, researcher believe BPA is rapidly converted to inactive forms like BPA-glucuronide and then removed from the body in urine. The findings from both studies suggest that adults can process BPA differently and are more protected from its effects than the fetus.

BPA is regularly detected in the blood of pregnant women, in amniotic fluid, umbilical cord blood, placental tissue and breast milk. Together with the results presented in these new studies, this indicates that human fetuses are regularly exposed to the active, estrogenic form of BPA.

Exposure to BPA during fetal development is of paramount concern. BPA in its active form can act like an estrogen hormone, although its weaker than most natural hormones. In the womb, exposure to estrogens at the wrong time or in greater or lessen amounts than normal can cause adverse effects in the development of many organs and systems, including the male and female reproductive tracts, the brain, the mammary gland and the immune system.

For the past several years, scientific and regulatory experts have debated BPA's safety in light of its widespread exposure in adults, developing fetuses, infants and children. The U.S. Food and Drug Administration (FDA), the European Food Safety Authority (EFSA) and other regulatory agencies that determine whether exposure to chemicals like BPA is safe have come to different conclusions. Following the lead of the National Toxicology Program, the FDA’s latest decision is that BPA may cause adverse effects in humans, including altered brain development and behaviors.

In contrast, EFSA contends that the fetus is able to convert BPA to less harmful metabolites, like BPA-glucuronide. This would suggest that the fetus can protect itself from the harmful effects of BPA. The current studies show that this opinion may be wrong. Together, these studies address important questions about human exposures to BPA and BPA metabolites and provide solid data that are greatly needed.

Resources

European Food Safety Authority. 2006. Opinion of the Scientific Panel on food additives, flavourings, processing aids and materials in contact with food (AFC) related to 2,2-bis(4-hydroxyphenol)propane. The EFSA Journal 428:1-75.

European food Safety Authority. 2008. Toxicokinetics of bisphenol A: scientific opinion of the panel on food additives, flavourings, processing aids and materials in contact with food (AFC). The EFSA Journal 759:1-10.

National Toxicology Program. 2008. NTP-CERHR monograph on the potential human reproductive and developmental effects of bisphenol A. NIH Publication No. 08 – 5994 (PDF).

U.S. Food and Drug Administration. 2010. Bisphenol A (BPA). Update on Bisphenol A (BPA) use in food. January.

Vandenberg LN, I Chahoud, JJ Heindel, V Padmanabhan, FJR Paumgartten and G Schoenfelder. 2010. Urine, serum and tissue biomonitoring studies indicate widespread exposure to bisphenol A. Environmental Health Perspectives http://dx.do.org/10.1289/ehp.0901716s.

Vandenberg LN, I Chahoud, V Padmanabhan, FJR Paumgartten and G Schoenfelder. 2010. Biomonitoring studies should be used by regulatory agencies to assess human exposure levels and safety of bisphenol A. Environmental Health Perspectives http://dx.doi.org/10.1289/ehp.0901717s.

 

 

Bisphenol A
More news about
Bisphenol A