Riverside Prenatal Biomonitoring Pilot Project: Results for bisphenol A and parabens June 2011 Report to the Community What is the Riverside Prenatal Biomonitoring Pilot Project? The Minnesota Department of Health conducted this project to measure certain chemicals in the urine of pregnant women. Chemicals included environmental phenols, used in plastics and personal care products, and cotinine, which indicates exposure to tobacco. This is a small pilot project, designed in part to help MDH learn how best to do biomonitoring projects in the future. The project involved 66 women who participated in the Riverside Birth Study conducted by the University of Minnesota in 20092010 at Fairview Riverside Hospital. What are environmental phenols? Environmental phenols are chemicals used in plastics and personal care products. The phenols measured in this study include bisphenol A (BPA) and four parabens: methyl, propyl, ethyl, and butyl paraben. How are people exposed to BPA? BPA is used to make hard polycarbonate plastics and epoxy resins. It is found in some plastic containers and bottles (plastics marked on the bottom with a 7 may contain BPA) and in the linings of most metal food and drink cans. People may be exposed to low levels when they eat or drink from plastic containers that contain BPA, or from metal cans that contain BPA in the lining. BPA has recently been found in cash register receipts and credit card slips. People may be exposed when they touch the receipts. How are people exposed to parabens? Parabens are used as preservatives in foods and in personal care products such as shampoos and cosmetics. More than one paraben may be used in the same product. People may be exposed to low levels when they use a product that contains parabens on their skin or eat foods that contain parabens. Do environmental phenols harm people’s health? Public awareness and media attention about possible health effects of exposure to BPA is increasing. These concerns are based on studies in animals. While some of the animal studies raise concerns about how low doses of BPA may affect the development of infants and young children, other studies indicate that low levels of exposure to BPA are probably not harmful. But comparing research findings in animals to health effects in humans can be difficult. Human studies are being conducted to explore possible health effects, but we cannot say with certainty what any level of BPA measured in urine means for human health. To help answer these questions, the federal government has launched a $30 million research initiative on BPA. Less research has been done on parabens. Some animal studies raise the concern that certain parabens may affect the way the body responds to hormones, but it is not clear what this means for humans. More research is needed. Finding measurable levels of BPA or parabens in urine does not mean that these levels can cause a health effect; it only tells us that the person was exposed to the chemicals. What levels were found in pilot project participants? How do these compare to other studies? MDH’s Public Health Laboratory analyzed the urine samples. BPA was detected in the urine of 56% of women, methyl paraben in 94%, propyl paraben in 85%, ethyl paraben in 44%, and butyl paraben in 11%1. Graph 1. Levels in urine of participants Graph 1 shows levels of BPA, methyl, and propyl paraben.2 Each participant’s level is represented by a circle, and the study average3 by a black line. The average BPA level was 2.2 micrograms of BPA per gram of creatinine ( g/g).4 BPA levels were so low that they were undetectable in some samples, but as high as 47 g/g in one. Methyl paraben averaged 73 g/g, ranging from undetectable to 1158 g/g. Propyl paraben averaged 14 g/g, ranging from undetectable to 363 g/g. Average levels for U.S. women in 2007-20085 are shown with a striped line in Graph 1 for each chemical. Average BPA levels in Riverside project women were similar (2.2 compared to 2.4 g/g). Other studies have measured BPA in pregnant women, with average levels ranging from 1.7 g/g in Cincinnati and the Netherlands to 4.1 g/g in Norway. Paraben levels were lower than the U.S. average (for methyl paraben, 73 compared to 126 g/g; for propyl paraben, 14 compared to 22 g/g). Very few studies have measured parabens in pregnant women. Because this was a small pilot project, we cannot conclude that these exposures represent all Minnesota women. Also, BPA and parabens leave the body quickly after exposure, so results from one urine sample show only the most recent exposure. Levels in a person’s urine can change based on time of day and from day to day. Do exposure levels show differences by income and racial/ethnic group? Some studies have found that exposure to BPA and parabens differs by income level and race/ethnicity. These differences may be due to available food options (eating more canned foods than fresh), cultural dietary habits, targeted marketing of products (those containing parabens), or other factors. 1 These percentages depend on the limit of detection (LOD) for the chemical analysis – the level below which results cannot be reliably measured. The LOD for all chemicals was 1 microgram per liter of urine. Because other studies have different LODs, the percentages cannot be compared directly. 2 Figures do not include ethyl and butyl paraben (detected in < 50% of women). 3 The averages shown are geometric means. 4 Levels are adjusted by creatinine, a waste product found in urine. This is a common way to account for dilution of the urine sample. 5 Levels measured as part of the National Health and Nutrition Examination Survey. 2 Graph 2. BPA by income and race/ethnicity As Graphs 2 and 3 show, the Riverside Project also found differences in exposure to these chemicals by income level and race/ethnicity: levels of BPA and methyl paraben were highest in the lowest income group. Because of the small number (n) of women in some groups, we cannot say for sure what these differences mean. BPA, methyl, and propyl paraben levels were higher in non-white women than white women. Methyl paraben levels were 3½ times higher in non-white than white women. Graph 3. Parabens by income and race/ethnicity The small size of the pilot project meant that we had to combine all non-white racial/ethnic groups, including people who self-identified as Black/African American, Hispanic, Asian, and other groups. Future studies should be larger and should include more participants from non-white racial/ethnic groups. What can I do to avoid exposure to environmental phenols, both for myself and my family? Chemical Bisphenol A (BPA) How to reduce exposure Avoid using plastic containers with the number 7 on the bottom. Throw away bottles and cups that are scratched or cloudy if they contain BPA. Do not heat foods or liquids in plastic containers containing BPA. Where possible, use fresh or frozen fruits and vegetables or food packaged in glass jars instead of canned food. Knowing which brands of canned food may contain BPA is difficult; search the Web or contact manufacturers to find more information. As of January 2009, the six major makers of baby bottles and infant feeding cups no longer use BPA. In January 2011, Minnesota banned the retail sale of these products containing BPA. To make sure a bottle or cup is BPA-free, read the label or contact the manufacturer. If you are not sure, do not store or heat milk or formula in it and throw it away if it is scratched or cloudy. If you feed your infant formula, choose powdered rather than liquid formula. Parabens Read the ingredient lists of personal care products, such as hair gel, face creams, lotions, shampoos, and bath products, and avoid those containing parabens. Other names for parabens are methyl p-hydroxybenzoate and methyl parahydroxybenzoate. Most major brands of deodorants and anti-perspirants in the U.S. do not contain parabens. 3 Should I breastfeed my baby? Breast milk is the best food for babies. While environmental phenols can be passed to a baby through breast milk, the levels are typically very low. The benefits of breastfeeding far outweigh any risks from exposure. If you express your breast milk for your baby to drink by bottle, do not store or heat the milk in bottles that contain BPA. See “How to reduce exposure,” above. What public health actions are being taken to reduce exposure of the public to environmental phenols? Based on the uncertainty about health effects of BPA, some states have passed precautionary laws to reduce BPA exposure in infants and children. In Minnesota, the retail sale of baby bottles or baby cups containing BPA became illegal on January 1, 2011. In addition, MDH developed a list of Priority Chemicals as part of the 2009 Toxic Free Kids Act which includes BPA. Other states (Maine and Washington) with similar lists have required manufacturers to report products containing the listed chemicals. At the same time, some manufacturers and retailers have voluntarily phased out using BPA in their products. Where can I get more information on reducing exposure to environmental phenols? MDH Community and Family Health Division, “Baby bottles, breastfeeding, and BPA: Information for parents and caregivers”: http://www.health.state.mn.us/divs/fh/mchatf/documents/bpafactsheet.pdf MDH Environmental Health Division, Web page on BPA: http://www.health.state.mn.us/divs/eh/risk/chemhazards/bisphenola.html U.S. Department of Health & Human Services, “BPA information for parents”: http://www.hhs.gov/safety/bpa/ MDH Office of Statewide Health Improvement Initiatives, Web page on nutrition/access to fresh food: http://www.health.state.mn.us/nutrition For more information, contact the Environmental Health Tracking and Biomonitoring Program at the Minnesota Department of Health. Call: (651) 201-5900 or (800) 205-4987 Email: [email protected] Visit: http://www.health.state.mn.us/tracking 4
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