A round robin approach to the analysis of bisphenol A (BPA) in human blood samples
Human exposure to bisphenol A (BPA) is ubiquitous, yet there are concerns about whether BPA can be measured in human blood. This Round Robin was designed to address this concern through three goals: 1) to identify collection materials, reagents and detection apparatuses that do not contribute BPA to...
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creator | Vandenberg, Laura N Gerona, Roy R Kannan, Kurunthachalam Taylor, Julia A van Breemen, Richard B Dickenson, Carrie A Liao, Chunyang Yuan, Yang Newbold, Retha R Padmanabhan, Vasantha Vom Saal, Frederick S Woodruff, Tracey J |
description | Human exposure to bisphenol A (BPA) is ubiquitous, yet there are concerns about whether BPA can be measured in human blood. This Round Robin was designed to address this concern through three goals: 1) to identify collection materials, reagents and detection apparatuses that do not contribute BPA to serum; 2) to identify sensitive and precise methods to accurately measure unconjugated BPA (uBPA) and BPA-glucuronide (BPA-G), a metabolite, in serum; and 3) to evaluate whether inadvertent hydrolysis of BPA-G occurs during sample handling and processing.
Four laboratories participated in this Round Robin. Laboratories screened materials to identify BPA contamination in collection and analysis materials. Serum was spiked with concentrations of uBPA and/or BPA-G ranging from 0.09-19.5 (uBPA) and 0.5-32 (BPA-G) ng/mL. Additional samples were preserved unspiked as 'environmental' samples. Blinded samples were provided to laboratories that used LC/MSMS to simultaneously quantify uBPA and BPA-G. To determine whether inadvertent hydrolysis of BPA metabolites occurred, samples spiked with only BPA-G were analyzed for the presence of uBPA. Finally, three laboratories compared direct and indirect methods of quantifying BPA-G.
We identified collection materials and reagents that did not introduce BPA contamination. In the blinded spiked sample analysis, all laboratories were able to distinguish low from high values of uBPA and BPA-G, for the whole spiked sample range and for those samples spiked with the three lowest concentrations (0.5-3.1 ng/ml). By completion of the Round Robin, three laboratories had verified methods for the analysis of uBPA and two verified for the analysis of BPA-G (verification determined by: 4 of 5 samples within 20% of spiked concentrations). In the analysis of BPA-G only spiked samples, all laboratories reported BPA-G was the majority of BPA detected (92.2 - 100%). Finally, laboratories were more likely to be verified using direct methods than indirect ones using enzymatic hydrolysis.
Sensitive and accurate methods for the direct quantification of uBPA and BPA-G were developed in multiple laboratories and can be used for the analysis of human serum samples. BPA contamination can be controlled during sample collection and inadvertent hydrolysis of BPA conjugates can be avoided during sample handling. |
doi_str_mv | 10.1186/1476-069X-13-25 |
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Four laboratories participated in this Round Robin. Laboratories screened materials to identify BPA contamination in collection and analysis materials. Serum was spiked with concentrations of uBPA and/or BPA-G ranging from 0.09-19.5 (uBPA) and 0.5-32 (BPA-G) ng/mL. Additional samples were preserved unspiked as 'environmental' samples. Blinded samples were provided to laboratories that used LC/MSMS to simultaneously quantify uBPA and BPA-G. To determine whether inadvertent hydrolysis of BPA metabolites occurred, samples spiked with only BPA-G were analyzed for the presence of uBPA. Finally, three laboratories compared direct and indirect methods of quantifying BPA-G.
We identified collection materials and reagents that did not introduce BPA contamination. In the blinded spiked sample analysis, all laboratories were able to distinguish low from high values of uBPA and BPA-G, for the whole spiked sample range and for those samples spiked with the three lowest concentrations (0.5-3.1 ng/ml). By completion of the Round Robin, three laboratories had verified methods for the analysis of uBPA and two verified for the analysis of BPA-G (verification determined by: 4 of 5 samples within 20% of spiked concentrations). In the analysis of BPA-G only spiked samples, all laboratories reported BPA-G was the majority of BPA detected (92.2 - 100%). Finally, laboratories were more likely to be verified using direct methods than indirect ones using enzymatic hydrolysis.
Sensitive and accurate methods for the direct quantification of uBPA and BPA-G were developed in multiple laboratories and can be used for the analysis of human serum samples. BPA contamination can be controlled during sample collection and inadvertent hydrolysis of BPA conjugates can be avoided during sample handling.</description><identifier>ISSN: 1476-069X</identifier><identifier>EISSN: 1476-069X</identifier><identifier>DOI: 10.1186/1476-069X-13-25</identifier><identifier>PMID: 24690217</identifier><language>eng</language><publisher>England: BioMed Central Ltd</publisher><subject>Animals ; Benzhydryl Compounds - blood ; Bisphenol A ; Blood banks ; Blood Specimen Collection - methods ; Chromatography, High Pressure Liquid ; Disease control ; Environmental health ; Environmental Monitoring ; Environmental Pollutants - blood ; Food contamination & poisoning ; Glucuronides - blood ; Health sciences ; Humans ; Laboratories ; Metabolites ; Molecular weight ; Phenols - blood ; Public health ; Rats ; Studies ; Tandem Mass Spectrometry ; Urine</subject><ispartof>Environmental health, 2014-04, Vol.13 (1), p.25-25, Article 25</ispartof><rights>COPYRIGHT 2014 BioMed Central Ltd.</rights><rights>2014 Vandenberg et al.; licensee BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly credited. The Creative Commons Public Domain Dedication waiver (http://creativecommons.org/publicdomain/zero/1.0/) applies to the data made available in this article, unless otherwise stated.</rights><rights>Copyright © 2014 Vandenberg et al.; licensee BioMed Central Ltd. 2014 Vandenberg et al.; licensee BioMed Central Ltd.</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c657t-435b95161ab2d20b2cf22b0fb71652f0e9950b0ac78efd2b853995a06cb7c1a3</citedby><cites>FETCH-LOGICAL-c657t-435b95161ab2d20b2cf22b0fb71652f0e9950b0ac78efd2b853995a06cb7c1a3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.ncbi.nlm.nih.gov/pmc/articles/PMC4066311/pdf/$$EPDF$$P50$$Gpubmedcentral$$Hfree_for_read</linktopdf><linktohtml>$$Uhttps://www.ncbi.nlm.nih.gov/pmc/articles/PMC4066311/$$EHTML$$P50$$Gpubmedcentral$$Hfree_for_read</linktohtml><link.rule.ids>230,314,723,776,780,860,881,27901,27902,53766,53768</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/24690217$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Vandenberg, Laura N</creatorcontrib><creatorcontrib>Gerona, Roy R</creatorcontrib><creatorcontrib>Kannan, Kurunthachalam</creatorcontrib><creatorcontrib>Taylor, Julia A</creatorcontrib><creatorcontrib>van Breemen, Richard B</creatorcontrib><creatorcontrib>Dickenson, Carrie A</creatorcontrib><creatorcontrib>Liao, Chunyang</creatorcontrib><creatorcontrib>Yuan, Yang</creatorcontrib><creatorcontrib>Newbold, Retha R</creatorcontrib><creatorcontrib>Padmanabhan, Vasantha</creatorcontrib><creatorcontrib>Vom Saal, Frederick S</creatorcontrib><creatorcontrib>Woodruff, Tracey J</creatorcontrib><title>A round robin approach to the analysis of bisphenol A (BPA) in human blood samples</title><title>Environmental health</title><addtitle>Environ Health</addtitle><description>Human exposure to bisphenol A (BPA) is ubiquitous, yet there are concerns about whether BPA can be measured in human blood. This Round Robin was designed to address this concern through three goals: 1) to identify collection materials, reagents and detection apparatuses that do not contribute BPA to serum; 2) to identify sensitive and precise methods to accurately measure unconjugated BPA (uBPA) and BPA-glucuronide (BPA-G), a metabolite, in serum; and 3) to evaluate whether inadvertent hydrolysis of BPA-G occurs during sample handling and processing.
Four laboratories participated in this Round Robin. Laboratories screened materials to identify BPA contamination in collection and analysis materials. Serum was spiked with concentrations of uBPA and/or BPA-G ranging from 0.09-19.5 (uBPA) and 0.5-32 (BPA-G) ng/mL. Additional samples were preserved unspiked as 'environmental' samples. Blinded samples were provided to laboratories that used LC/MSMS to simultaneously quantify uBPA and BPA-G. To determine whether inadvertent hydrolysis of BPA metabolites occurred, samples spiked with only BPA-G were analyzed for the presence of uBPA. Finally, three laboratories compared direct and indirect methods of quantifying BPA-G.
We identified collection materials and reagents that did not introduce BPA contamination. In the blinded spiked sample analysis, all laboratories were able to distinguish low from high values of uBPA and BPA-G, for the whole spiked sample range and for those samples spiked with the three lowest concentrations (0.5-3.1 ng/ml). By completion of the Round Robin, three laboratories had verified methods for the analysis of uBPA and two verified for the analysis of BPA-G (verification determined by: 4 of 5 samples within 20% of spiked concentrations). In the analysis of BPA-G only spiked samples, all laboratories reported BPA-G was the majority of BPA detected (92.2 - 100%). Finally, laboratories were more likely to be verified using direct methods than indirect ones using enzymatic hydrolysis.
Sensitive and accurate methods for the direct quantification of uBPA and BPA-G were developed in multiple laboratories and can be used for the analysis of human serum samples. BPA contamination can be controlled during sample collection and inadvertent hydrolysis of BPA conjugates can be avoided during sample handling.</description><subject>Animals</subject><subject>Benzhydryl Compounds - blood</subject><subject>Bisphenol A</subject><subject>Blood banks</subject><subject>Blood Specimen Collection - methods</subject><subject>Chromatography, High Pressure Liquid</subject><subject>Disease control</subject><subject>Environmental health</subject><subject>Environmental Monitoring</subject><subject>Environmental Pollutants - blood</subject><subject>Food contamination & poisoning</subject><subject>Glucuronides - blood</subject><subject>Health sciences</subject><subject>Humans</subject><subject>Laboratories</subject><subject>Metabolites</subject><subject>Molecular weight</subject><subject>Phenols - blood</subject><subject>Public health</subject><subject>Rats</subject><subject>Studies</subject><subject>Tandem Mass Spectrometry</subject><subject>Urine</subject><issn>1476-069X</issn><issn>1476-069X</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2014</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>BENPR</sourceid><recordid>eNptks9r3yAYxmVsrF23825D2KU7pPVHNMllkJWtHRQ6Rg-7iRptLEYzTQr972do-11biqAvr5_nUd9XAD5idIRxy49x3fAK8e5PhWlF2Cuwv8u8fhTvgXc5XyOEm5azt2CP1LxDBDf74HcPU1zDUGblApTznKLUI1wiXEYDZZD-NrsMo4XK5Xk0IXrYw8Nvv_ovsAjGdZIBKh_jALOcZm_ye_DGSp_Nh_v1AFz--H55cladX5z-POnPK81Zs1Q1ZapjmGOpyECQItoSopBVDeaMWGS6jiGFpG5aYweiWkZLRiKuVaOxpAfg653tvKrJDNqEJUkv5uQmmW5FlE483QluFFfxRtSIc4pxMTi8N0jx72ryIiaXtfFeBhPXLDCra4QLuaGfn6HXcU2lNhtFO8YpR-w_dSW9ES7YWM7Vm6noC8Ub0mJSqKMXqDIGMzkdg7Gu5J8Iju8EOsWck7G7N2Iktl8gtj6Lrc8CU0G2i3x6XJod_9B2-g-FpKqO</recordid><startdate>20140401</startdate><enddate>20140401</enddate><creator>Vandenberg, Laura N</creator><creator>Gerona, Roy R</creator><creator>Kannan, Kurunthachalam</creator><creator>Taylor, Julia 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round robin approach to the analysis of bisphenol A (BPA) in human blood samples</title><author>Vandenberg, Laura N ; Gerona, Roy R ; Kannan, Kurunthachalam ; Taylor, Julia A ; van Breemen, Richard B ; Dickenson, Carrie A ; Liao, Chunyang ; Yuan, Yang ; Newbold, Retha R ; Padmanabhan, Vasantha ; Vom Saal, Frederick S ; Woodruff, Tracey J</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c657t-435b95161ab2d20b2cf22b0fb71652f0e9950b0ac78efd2b853995a06cb7c1a3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2014</creationdate><topic>Animals</topic><topic>Benzhydryl Compounds - blood</topic><topic>Bisphenol A</topic><topic>Blood banks</topic><topic>Blood Specimen Collection - methods</topic><topic>Chromatography, High Pressure Liquid</topic><topic>Disease control</topic><topic>Environmental health</topic><topic>Environmental Monitoring</topic><topic>Environmental Pollutants - blood</topic><topic>Food contamination & poisoning</topic><topic>Glucuronides - blood</topic><topic>Health sciences</topic><topic>Humans</topic><topic>Laboratories</topic><topic>Metabolites</topic><topic>Molecular weight</topic><topic>Phenols - blood</topic><topic>Public health</topic><topic>Rats</topic><topic>Studies</topic><topic>Tandem Mass Spectrometry</topic><topic>Urine</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Vandenberg, Laura N</creatorcontrib><creatorcontrib>Gerona, Roy R</creatorcontrib><creatorcontrib>Kannan, Kurunthachalam</creatorcontrib><creatorcontrib>Taylor, Julia A</creatorcontrib><creatorcontrib>van Breemen, Richard B</creatorcontrib><creatorcontrib>Dickenson, Carrie A</creatorcontrib><creatorcontrib>Liao, Chunyang</creatorcontrib><creatorcontrib>Yuan, Yang</creatorcontrib><creatorcontrib>Newbold, Retha R</creatorcontrib><creatorcontrib>Padmanabhan, Vasantha</creatorcontrib><creatorcontrib>Vom Saal, Frederick 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R</au><au>Kannan, Kurunthachalam</au><au>Taylor, Julia A</au><au>van Breemen, Richard B</au><au>Dickenson, Carrie A</au><au>Liao, Chunyang</au><au>Yuan, Yang</au><au>Newbold, Retha R</au><au>Padmanabhan, Vasantha</au><au>Vom Saal, Frederick S</au><au>Woodruff, Tracey J</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>A round robin approach to the analysis of bisphenol A (BPA) in human blood samples</atitle><jtitle>Environmental health</jtitle><addtitle>Environ Health</addtitle><date>2014-04-01</date><risdate>2014</risdate><volume>13</volume><issue>1</issue><spage>25</spage><epage>25</epage><pages>25-25</pages><artnum>25</artnum><issn>1476-069X</issn><eissn>1476-069X</eissn><abstract>Human exposure to bisphenol A (BPA) is ubiquitous, yet there are concerns about whether BPA can be measured in human blood. This Round Robin was designed to address this concern through three goals: 1) to identify collection materials, reagents and detection apparatuses that do not contribute BPA to serum; 2) to identify sensitive and precise methods to accurately measure unconjugated BPA (uBPA) and BPA-glucuronide (BPA-G), a metabolite, in serum; and 3) to evaluate whether inadvertent hydrolysis of BPA-G occurs during sample handling and processing.
Four laboratories participated in this Round Robin. Laboratories screened materials to identify BPA contamination in collection and analysis materials. Serum was spiked with concentrations of uBPA and/or BPA-G ranging from 0.09-19.5 (uBPA) and 0.5-32 (BPA-G) ng/mL. Additional samples were preserved unspiked as 'environmental' samples. Blinded samples were provided to laboratories that used LC/MSMS to simultaneously quantify uBPA and BPA-G. To determine whether inadvertent hydrolysis of BPA metabolites occurred, samples spiked with only BPA-G were analyzed for the presence of uBPA. Finally, three laboratories compared direct and indirect methods of quantifying BPA-G.
We identified collection materials and reagents that did not introduce BPA contamination. In the blinded spiked sample analysis, all laboratories were able to distinguish low from high values of uBPA and BPA-G, for the whole spiked sample range and for those samples spiked with the three lowest concentrations (0.5-3.1 ng/ml). By completion of the Round Robin, three laboratories had verified methods for the analysis of uBPA and two verified for the analysis of BPA-G (verification determined by: 4 of 5 samples within 20% of spiked concentrations). In the analysis of BPA-G only spiked samples, all laboratories reported BPA-G was the majority of BPA detected (92.2 - 100%). Finally, laboratories were more likely to be verified using direct methods than indirect ones using enzymatic hydrolysis.
Sensitive and accurate methods for the direct quantification of uBPA and BPA-G were developed in multiple laboratories and can be used for the analysis of human serum samples. BPA contamination can be controlled during sample collection and inadvertent hydrolysis of BPA conjugates can be avoided during sample handling.</abstract><cop>England</cop><pub>BioMed Central Ltd</pub><pmid>24690217</pmid><doi>10.1186/1476-069X-13-25</doi><tpages>1</tpages><oa>free_for_read</oa></addata></record> |
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subjects | Animals Benzhydryl Compounds - blood Bisphenol A Blood banks Blood Specimen Collection - methods Chromatography, High Pressure Liquid Disease control Environmental health Environmental Monitoring Environmental Pollutants - blood Food contamination & poisoning Glucuronides - blood Health sciences Humans Laboratories Metabolites Molecular weight Phenols - blood Public health Rats Studies Tandem Mass Spectrometry Urine |
title | A round robin approach to the analysis of bisphenol A (BPA) in human blood samples |
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