BackgroundBisphenol A (BPA) is one of the highest-volume chemicals produced worldwide, and human exposure to BPA is thought to be ubiquitous. Thus, there are concerns that the amount of BPA to whic...

/pdf/urinary-circulating-and-tissue-biomonitoring-studies-3sv3m05feu.pdf

Urinary, circulating, and tissue biomonitoring studies indicate widespread exposure to bisphenol A.

This opinion describes the assessment of the risks to public health associated with bisphenol A (BPA) exposure. Exposure was assessed for various groups of the human population in three different ways: (1) external (by diet, drinking water, inhalation, and dermal contact to cosmetics and thermal paper); (2) internal exposure to total BPA (absorbed dose of BPA, sum of conjugated and unconjugated BPA); and (3) aggregated (from diet, dust, cosmetics and thermal paper), expressed as oral human equivalent dose (HED) referring to unconjugated BPA only. The estimated BPA dietary intake was highest in infants and toddlers (up to 0.875 µg/kg bw per day). Women of childbearing age had dietary exposures comparable to men of the same age (up to 0.388 µg/kg bw per day). The highest aggregated exposure of 1.449 µg/kg bw per day was estimated for adolescents. Biomonitoring data were in line with estimated internal exposure to total BPA from all sources. BPA toxicity was evaluated by a weight of evidence approach. “Likely” adverse effects in animals on kidney and mammary gland underwent benchmark dose (BMDL10) response modelling. A BMDL10 of 8 960 µg/kg bw per day was calculated for changes in the mean relative kidney weight in a two generation toxicity study in mice. No BMDL10 could be calculated for mammary gland effects. Using data on toxicokinetics, this BMDL10 was converted to an HED of 609 µg/kg bw per day. The CEF Panel applied a total uncertainty factor of 150 (for inter- and intra-species differences and uncertainty in mammary gland, reproductive, neurobehavioural, immune and metabolic system effects) to establish a temporary Tolerable Daily Intake (t-TDI) of 4 µg/kg bw per day. By comparing this t-TDI with the exposure estimates, the CEF Panel concluded that there is no health concern for any age group from dietary exposure and low health concern from aggregated exposure. The CEF Panel noted considerable uncertainty in the exposure estimates for non-dietary sources, whilst the uncertainty around dietary estimates was relatively low.

Scientific Opinion on the risks to public health related to the presence of bisphenol A (BPA) in foodstuffs: Executive summary

The roles of cellular reactive oxygen species, oxidative stress and antioxidants in pregnancy outcomes

https://www.sewagesludgeactionnetwork.com/files/Food_Grown_in_Sludge_Emerging_Contaminants.pdf

Review of ‘emerging’ organic contaminants in biosolids and assessment of international research priorities for the agricultural use of biosolids

Because bisphenol A (BPA) is a high production volume chemical, we examined over 500 peer-reviewed studies to understand its global distribution in effluent discharges, surface waters, sewage sludge, biosolids, sediments, soils, air, wildlife, and humans. Bisphenol A was largely reported from urban ecosystems in Asia, Europe, and North America; unfortunately, information was lacking from large geographic areas, megacities, and developing countries. When sufficient data were available, probabilistic hazard assessments were performed to understand global environmental quality concerns. Exceedances of Canadian Predicted No Effect Concentrations for aquatic life were >50% for effluents in Asia, Europe, and North America but as high as 80% for surface water reports from Asia. Similarly, maximum concentrations of BPA in sediments from Asia were higher than Europe. Concentrations of BPA in wildlife, mostly for fish, ranged from 0.2 to 13 000 ng/g. We observed 60% and 40% exceedences of median levels by the US Centers for Disease Control and Prevention's National Health and Nutrition Examination Survey in Europe and Asia, respectively. These findings highlight the utility of coordinating global sensing of environmental contaminants efforts through integration of environmental monitoring and specimen banking to identify regions for implementation of more robust environmental assessment and management programs.

https://journals.sagepub.com/doi/pdf/10.1177/1559325815598308

Global Assessment of Bisphenol A in the Environment Review and Analysis of Its Occurrence and Bioaccumulation

Maternal and fetal exposure to bisphenol A in Korea.

Heterocyclic amines (HCAs) are naturally produced during common cooking processes for meats and fish. HCAs are metabolized by various enzymes, including cytochromes P450, N-acetyl transferases, and sulfotransferases, and their bioactivated metabolites are considered to bind to DNA or protein to show carcinogenic effects. More than 20 HCAs have been identified, of which 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP) is classified as 'reasonably anticipated to be a human carcinogen' to develop cancers in breast, colon and prostate. The purpose of this study was to evaluate human exposure levels of PhIP and to understand the role of genetic polymorphisms of enzymes on PhIP metabolism. Urine samples were collected from subjects (n = 100) before 3-day meat-restricted diets. Subjects consumed grilled chicken, and their blood and urine were collected before and after the administration of the chickens to investigate genetic polymorphisms and PhIP levels. The mean PhIP levels were 4.22 ± 0.12, 0.61 ± 0.19 and 22.64 ± 1.00 pg ml(-1) in urine under normal conditions and before and after chicken administration, respectively. Among 21 Single-nucleotide polymorphisms (SNP) of CYP1A1, CYP1A2, NATs and UGTs investigated in this study, genotypic groups of CYP1A1/T6235C (MSP I) and CYP1A2/-2467delT showed significant differences in PhIP excretion (P < 0.05). These results suggest that genetic polymorphisms might affect PhIP metabolism, which could improve understanding of populations subject to PhIP-derived health risk.

Genetic polymorphisms in metabolism of 2-amino-1-methyl-6-phenylimidazo[4,5-b] pyridine

Aflatoxin B , a known human carcinogen, is the member of aflatoxin subfamily that is most frequently found in contaminated foods. Epidemiological studies have suggested that aflatoxins may be associated with human liver cancer and acute hepatitis. Recently it was reported that the traditional medical herbs sold in domestic markets are contaminated with aflatoxins. Long-term administration of these contaminated medicines could result in adverse health effects. Therefore, it is important to evaluate the levels of exposure to aflatoxin in people who ingest traditional herbal medicines. Blood samples were collected, before and after the herbal medicine intake, from 151 subjects who visited the hospital. The metabolite of aflatoxin B in blood, aflatoxin B -albumin (aflatoxin B -lysine), is reportedly an appropriate internal exposure indicator, and its levels in the collected bloods were therefore analyzed using a liquid chromatography-mass spectrometry. The analytical method of aflatoxin B -lysine in blood was firstly optimized in Korea and the levels were detected below quantification limits (2 pg/mg albumin) in this study population. Consequently, the exposure levels of aflatoxin B by ingestion of herbal medicines were low but it is important to monitor routinely due to the possibility of risk on the aflatoxin exposure.

/pdf/biomonitoring-of-aflatoxin-b-1-exposed-by-herbal-medicine-uj531ids3s.pdf

Biomonitoring of Aflatoxin B 1 Exposed by Herbal Medicine Intake

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Maternal and fetal exposure to bisphenol A in Korea.

Genetic polymorphisms in metabolism of 2-amino-1-methyl-6-phenylimidazo[4,5-b] pyridine

Biomonitoring of Aflatoxin B 1 Exposed by Herbal Medicine Intake