Literature DB >> 20077198

Potential risk of bisphenol A migration from polycarbonate containers after heating, boiling, and microwaving.

Duck Soo Lim1, Seung Jun Kwack, Kyu-Bong Kim, Hyung Sik Kim, Byung Mu Lee.   

Abstract

The migration levels of bisphenol A (BPA) were analyzed in food samples by high-performance liquid chromatography (HPLC) from polycarbonate (PC) bottles subjected to simulated use by heating with microwave, heating in a boiling water bath, or filling them with boiling hot water (100 degrees C). Migration testing performed in PC bottles filled with steamed rice or hot cooked pork, standing at room temperature, or heated in a boiling water bath (100 degrees C) showed that BPA was not detected at the limit of detection (LOD) of 1 microg/L (ppb). In contrast, heating by microwaving to 100 degrees C for 9 min increased BPA migration levels from 6 to 18 ppb and from 5 to 15 ppb for steamed rice or for cooked pork, respectively. In addition, 3 different PC bottles were tested by filling them with boiling hot water (100 degrees C) and leaving them to stand at room temperature for up to 3 h. The mean BPA levels from the bottles increased in a time-dependent manner, with the range of not detected (ND) to 2.5 ppb after 60 min. However, none of the PC bottles released BPA at levels that exceed the recently established specific migration limits (SML) of 600 ppb established by European Union and Korea Food and Drug Administration (KFDA). Data suggest that the use of PC plastic bottles in our daily life is considered safe in Korea.

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Year:  2009        PMID: 20077198     DOI: 10.1080/15287390903212329

Source DB:  PubMed          Journal:  J Toxicol Environ Health A        ISSN: 0098-4108


  12 in total

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2.  Effects of bisphenol A on chlorophyll fluorescence in five plants.

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Journal:  Environ Sci Pollut Res Int       Date:  2015-07-09       Impact factor: 4.223

3.  The effect of bisphenol A on some oxidative stress parameters and acetylcholinesterase activity in the heart of male albino rats.

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4.  Measurement of bisphenol A, bisphenol A ß-D-glucuronide, genistein, and genistein 4'-ß-D-glucuronide via SPE and HPLC-MS/MS.

Authors:  Janis L Coughlin; Bozena Winnik; Brian Buckley
Journal:  Anal Bioanal Chem       Date:  2011-06-13       Impact factor: 4.142

5.  Probabilistic integrated risk assessment of human exposure risk to environmental bisphenol A pollution sources.

Authors:  Keng-Yen Fu; Yi-Hsien Cheng; Chia-Pin Chio; Chung-Min Liao
Journal:  Environ Sci Pollut Res Int       Date:  2016-07-16       Impact factor: 4.223

6.  Human Bisphenol A Exposure and the "Diabesity Phenotype".

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Journal:  Dose Response       Date:  2015-07-31       Impact factor: 2.658

7.  Effects of Bisphenol A Metabolite 4-Methyl-2,4-bis(4-hydroxyphenyl)pent-1-ene on Lung Function and Type 2 Pulmonary Alveolar Epithelial Cell Growth.

Authors:  Shing-Hwa Liu; Chin-Chuan Su; Kuan-I Lee; Ya-Wen Chen
Journal:  Sci Rep       Date:  2016-12-16       Impact factor: 4.379

8.  Dietary Exposures and Intake Doses to Bisphenol A and Triclosan in 188 Duplicate-Single Solid Food Items Consumed by US Adults.

Authors:  Marsha K Morgan; Matthew S Clifton
Journal:  Int J Environ Res Public Health       Date:  2021-04-20       Impact factor: 3.390

Review 9.  Chemical and Biological Sensors for Food-Quality Monitoring and Smart Packaging.

Authors:  Fatima Mustafa; Silvana Andreescu
Journal:  Foods       Date:  2018-10-16

10.  Exposure to Triclosan and Bisphenol Analogues B, F, P, S and Z in Repeated Duplicate-Diet Solid Food Samples of Adults.

Authors:  Marsha K Morgan; Matthew S Clifton
Journal:  Toxics       Date:  2021-03-03
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