Phthalate Esters and Their Potential Risk in PET Bottled Water Stored under Common Conditions
A great deal of attention has been paid lately to release of phthalate esters (PAEs) from polyethylene terephthalate (PET) bottles into PET bottled drinking water due to their potential endocrine-disrupting effects. Three kinds of PAEs, including diethyl phthalate (DEP), dimethyl phthalate (DMP) and...
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Veröffentlicht in: | International journal of environmental research and public health 2019-12, Vol.17 (1), p.141 |
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description | A great deal of attention has been paid lately to release of phthalate esters (PAEs) from polyethylene terephthalate (PET) bottles into PET bottled drinking water due to their potential endocrine-disrupting effects. Three kinds of PAEs, including diethyl phthalate (DEP), dimethyl phthalate (DMP) and dibutyl phthalate (DBP), were detected in 10 popular brands of PET bottles in Beijing, ranging from 101.97 μg/kg to 709.87 μg/kg. Meanwhile, six kinds of PAEs, including DEP, DMP, DBP, n-butyl benzyl phthalate (BBP), di-n-octyl phthalate (DOP) and di(2-ethylhexyl) phthalate (DEHP), were detected in PET bottled water, ranging from 0.19 μg/L to 0.98 μg/L, under an outdoor storage condition, while their concentrations ranged from 0.18 μg/L to 0.71 μg/L under an indoor storage condition. Furthermore, the concentrations of PAEs in brand D and E bottles were slightly increased when the storage time was prolonged. In addition, the concentrations of PAEs in commercial water contained in brand B and H bottles and pure water contained in brand E and G bottles were also slightly increased with the increase of storage temperature. Interestingly, DBP mainly contributed to the increased PAEs levels in simulation water. These results suggest that a part of the PAEs in PET bottled water originated from plastic bottles, which was related to the storage time and temperature. However, the PAEs in PET bottled water only pose a negligible risk to consumers if they follow the recommendations, such as storage at a common place (24 °C), away from sun and in a short period of time. |
doi_str_mv | 10.3390/ijerph17010141 |
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Three kinds of PAEs, including diethyl phthalate (DEP), dimethyl phthalate (DMP) and dibutyl phthalate (DBP), were detected in 10 popular brands of PET bottles in Beijing, ranging from 101.97 μg/kg to 709.87 μg/kg. Meanwhile, six kinds of PAEs, including DEP, DMP, DBP, n-butyl benzyl phthalate (BBP), di-n-octyl phthalate (DOP) and di(2-ethylhexyl) phthalate (DEHP), were detected in PET bottled water, ranging from 0.19 μg/L to 0.98 μg/L, under an outdoor storage condition, while their concentrations ranged from 0.18 μg/L to 0.71 μg/L under an indoor storage condition. Furthermore, the concentrations of PAEs in brand D and E bottles were slightly increased when the storage time was prolonged. In addition, the concentrations of PAEs in commercial water contained in brand B and H bottles and pure water contained in brand E and G bottles were also slightly increased with the increase of storage temperature. Interestingly, DBP mainly contributed to the increased PAEs levels in simulation water. These results suggest that a part of the PAEs in PET bottled water originated from plastic bottles, which was related to the storage time and temperature. However, the PAEs in PET bottled water only pose a negligible risk to consumers if they follow the recommendations, such as storage at a common place (24 °C), away from sun and in a short period of time.</description><identifier>ISSN: 1660-4601</identifier><identifier>ISSN: 1661-7827</identifier><identifier>EISSN: 1660-4601</identifier><identifier>DOI: 10.3390/ijerph17010141</identifier><identifier>PMID: 31878152</identifier><language>eng</language><publisher>Switzerland: MDPI AG</publisher><subject>Beijing ; Bottled water ; Bottles ; Butyl benzyl phthalate ; Consumers ; Consumption ; Dibutyl phthalate ; Dioctyl phthalate ; Drinking water ; Drinking Water - analysis ; Endocrine disruptors ; Endocrine Disruptors - toxicity ; Esters ; Esters - analysis ; Esters - toxicity ; Health risk assessment ; Health risks ; Phthalate esters ; Phthalates ; Phthalic Acids - toxicity ; Polyethylene ; Polyethylene terephthalate ; Polyethylene Terephthalates - analysis ; Polyethylene Terephthalates - toxicity ; Storage ; Storage temperature</subject><ispartof>International journal of environmental research and public health, 2019-12, Vol.17 (1), p.141</ispartof><rights>2019 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (http://creativecommons.org/licenses/by/4.0/). 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Three kinds of PAEs, including diethyl phthalate (DEP), dimethyl phthalate (DMP) and dibutyl phthalate (DBP), were detected in 10 popular brands of PET bottles in Beijing, ranging from 101.97 μg/kg to 709.87 μg/kg. Meanwhile, six kinds of PAEs, including DEP, DMP, DBP, n-butyl benzyl phthalate (BBP), di-n-octyl phthalate (DOP) and di(2-ethylhexyl) phthalate (DEHP), were detected in PET bottled water, ranging from 0.19 μg/L to 0.98 μg/L, under an outdoor storage condition, while their concentrations ranged from 0.18 μg/L to 0.71 μg/L under an indoor storage condition. Furthermore, the concentrations of PAEs in brand D and E bottles were slightly increased when the storage time was prolonged. In addition, the concentrations of PAEs in commercial water contained in brand B and H bottles and pure water contained in brand E and G bottles were also slightly increased with the increase of storage temperature. Interestingly, DBP mainly contributed to the increased PAEs levels in simulation water. These results suggest that a part of the PAEs in PET bottled water originated from plastic bottles, which was related to the storage time and temperature. However, the PAEs in PET bottled water only pose a negligible risk to consumers if they follow the recommendations, such as storage at a common place (24 °C), away from sun and in a short period of time.</description><subject>Beijing</subject><subject>Bottled water</subject><subject>Bottles</subject><subject>Butyl benzyl phthalate</subject><subject>Consumers</subject><subject>Consumption</subject><subject>Dibutyl phthalate</subject><subject>Dioctyl phthalate</subject><subject>Drinking water</subject><subject>Drinking Water - analysis</subject><subject>Endocrine disruptors</subject><subject>Endocrine Disruptors - toxicity</subject><subject>Esters</subject><subject>Esters - analysis</subject><subject>Esters - toxicity</subject><subject>Health risk assessment</subject><subject>Health risks</subject><subject>Phthalate esters</subject><subject>Phthalates</subject><subject>Phthalic Acids - toxicity</subject><subject>Polyethylene</subject><subject>Polyethylene terephthalate</subject><subject>Polyethylene Terephthalates - analysis</subject><subject>Polyethylene Terephthalates - toxicity</subject><subject>Storage</subject><subject>Storage temperature</subject><issn>1660-4601</issn><issn>1661-7827</issn><issn>1660-4601</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2019</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><sourceid>BENPR</sourceid><recordid>eNpdkU1rGzEQhkVoyIfTa45F0EsvTiTNrlZ7CaTG-YBATOLSUxHyrpSVuyu5kjbQf1-FOMHpaWaYZ15m5kXolJIzgJqc27UOm45WhBJa0D10RDkn04IT-mknP0THMa4JAVHw-gAdAhWVoCU7Qr8WXepUr5LG85h0iFi5Fi87bQNe-KRdsqrHDzb-xtbhxXyJv_uUet3in3km4MfkQy5G1-Zi5ofBuxxca5P1Lp6gfaP6qD9v4wT9uJovZzfTu_vr29nl3bQpqEhTU6wUrygzNa1YLTSoirWqAlGTYgWqbDRtmDFgmtyGFWjVElYorsEYI1oGE3TxqrsZV4Num7x2UL3cBDuo8Fd6ZeXHjrOdfPLPkteCAamzwLetQPB_Rh2THGxsdN8rp_0YJQOgrIT8wIx-_Q9d-zG4fJ5kJWe05CKTE3T2SjXBxxi0eV-GEvninPzoXB74snvCO_5mFfwD2tKWBQ</recordid><startdate>20191224</startdate><enddate>20191224</enddate><creator>Xu, Xiangqin</creator><creator>Zhou, Gang</creator><creator>Lei, Kun</creator><creator>LeBlanc, Gerald A</creator><creator>An, Lihui</creator><general>MDPI AG</general><general>MDPI</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7X7</scope><scope>7XB</scope><scope>88E</scope><scope>8C1</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FYUFA</scope><scope>GHDGH</scope><scope>K9.</scope><scope>M0S</scope><scope>M1P</scope><scope>PIMPY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PRINS</scope><scope>7X8</scope><scope>5PM</scope><orcidid>https://orcid.org/0000-0003-3269-9752</orcidid></search><sort><creationdate>20191224</creationdate><title>Phthalate Esters and Their Potential Risk in PET Bottled Water Stored under Common Conditions</title><author>Xu, Xiangqin ; 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Three kinds of PAEs, including diethyl phthalate (DEP), dimethyl phthalate (DMP) and dibutyl phthalate (DBP), were detected in 10 popular brands of PET bottles in Beijing, ranging from 101.97 μg/kg to 709.87 μg/kg. Meanwhile, six kinds of PAEs, including DEP, DMP, DBP, n-butyl benzyl phthalate (BBP), di-n-octyl phthalate (DOP) and di(2-ethylhexyl) phthalate (DEHP), were detected in PET bottled water, ranging from 0.19 μg/L to 0.98 μg/L, under an outdoor storage condition, while their concentrations ranged from 0.18 μg/L to 0.71 μg/L under an indoor storage condition. Furthermore, the concentrations of PAEs in brand D and E bottles were slightly increased when the storage time was prolonged. In addition, the concentrations of PAEs in commercial water contained in brand B and H bottles and pure water contained in brand E and G bottles were also slightly increased with the increase of storage temperature. Interestingly, DBP mainly contributed to the increased PAEs levels in simulation water. These results suggest that a part of the PAEs in PET bottled water originated from plastic bottles, which was related to the storage time and temperature. However, the PAEs in PET bottled water only pose a negligible risk to consumers if they follow the recommendations, such as storage at a common place (24 °C), away from sun and in a short period of time.</abstract><cop>Switzerland</cop><pub>MDPI AG</pub><pmid>31878152</pmid><doi>10.3390/ijerph17010141</doi><orcidid>https://orcid.org/0000-0003-3269-9752</orcidid><oa>free_for_read</oa></addata></record> |
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subjects | Beijing Bottled water Bottles Butyl benzyl phthalate Consumers Consumption Dibutyl phthalate Dioctyl phthalate Drinking water Drinking Water - analysis Endocrine disruptors Endocrine Disruptors - toxicity Esters Esters - analysis Esters - toxicity Health risk assessment Health risks Phthalate esters Phthalates Phthalic Acids - toxicity Polyethylene Polyethylene terephthalate Polyethylene Terephthalates - analysis Polyethylene Terephthalates - toxicity Storage Storage temperature |
title | Phthalate Esters and Their Potential Risk in PET Bottled Water Stored under Common Conditions |
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