Article(id=1215670315569566484, tenantId=1146029695717560320, journalId=1149652044408987649, issueId=1215670311140381365, articleNumber=null, orderNo=null, doi=10.19812/j.cnki.jfsq11-5956/ts.20250418005, pmid=null, cstr=null, oa=null, hot=null, price=null, onlineType=0, articleFormat=0, articleType=null, articleTypeStr=research-article, receivedDate=1744905600000, receivedDateStr=2025-04-18, revisedDate=null, revisedDateStr=null, acceptedDate=null, acceptedDateStr=null, onlineDate=1767767989294, onlineDateStr=2026-01-07, pubDate=1753372800000, pubDateStr=2025-07-25, doiRegisterDate=null, doiRegisterDateStr=null, onlineIssueDate=1767767989294, onlineIssueDateStr=2026-01-07, onlineJustAcceptDate=null, onlineJustAcceptDateStr=null, onlineFirstDate=null, onlineFirstDateStr=null, sourceXml=null, magXml=null, createTime=1767767989294, creator=13701087609, updateTime=1767767989294, updator=13701087609, issue=Issue{id=1215670311140381365, tenantId=1146029695717560320, journalId=1149652044408987649, year='2025', volume='16', issue='14', pageStart='1', pageEnd='326', issueExtLink='null', onlineDate='null', pubDate='null', beforeIssueId=null, nextIssueId=null, price=null, status=1, issueComplete=1, articleOrder=1, issueType=-1, specialIssue=null, createTime=1767767988237, creator=13701087609, updateTime=1767970098618, updator=13701087609, preIssue=null, nextIssue=null, ext={EN=IssueExt(id=1216518023599538606, tenantId=1146029695717560320, journalId=1149652044408987649, issueId=1215670311140381365, language=EN, specialIssueTitle=, coverIllustrator=null, specialIssueEditor=, specialIssueAbout=), CN=IssueExt(id=1216518023599538607, tenantId=1146029695717560320, journalId=1149652044408987649, issueId=1215670311140381365, language=CN, specialIssueTitle=, coverIllustrator=null, specialIssueEditor=, specialIssueAbout=)}, issueFiles=null}, startPage=30, endPage=39, ext={EN=ArticleExt(id=1215670316559422287, articleId=1215670315569566484, tenantId=1146029695717560320, journalId=1149652044408987649, language=EN, title=Simultaneous determination of organophosphate esters, organophosphite antioxidants and parabens migration in food contact materials by liquid chromatography-tandem mass spectrometry, columnId=1215670312151208635, journalTitle=Journal of Food Safety & Quality, columnName=Special Topic: Food Safety Risk Monitoring and Assessment in Beijing, runingTitle=null, highlight=null, articleAbstract=

Objective To establish a method for simultaneously determining the migration amounts of 24 kinds of organophosphate esters (OPEs), organophosphite antioxidants (OPAs), and parabens (PBs) in food contact materials by liquid chromatography-tandem mass spectrometry. Methods The food contact materials to be tested were subjected to migration experiments in accordance with the expected types of food and contact modes, so as to obtain the soaking solution. After centrifugation, the soaking solution was separated by liquid chromatography, determined by tandem mass spectrometry, and quantified by matrix-matched standard curve. Results The optimized method could simultaneously detect 24 kinds of OPEs, OPAs, and PBs in the migration soaking solutions of food contact materials. The limits of detection were 0.01-0.58 µg/L and the limits of quantitation were 0.03-2.00 µg/L. The spiked samples recovery rates ranged from 69.0%-129.6%, with relative standard deviations of 0.5% to 10.9% (n=6). The 20 packaging film bags, 10 disposable take-out boxes and 20 paper tableware items were tested. The ΣOPEs ranges were <limit of detection-19.1 μg/L, ΣOPAs were <limit of detection-1248 μg/L, and ΣPBs were <limit of detection-0.501 μg/L. The monitoring of the migration amounts of food contact materials was limited, its health risks required more attention and research. Conclusion This method is simple to operate and highly sensitive, which is suitable for the determination of the migration amounts of OPEs, OPAs and PBs in food contact material samples.

, correspAuthors=Wei LIU, authorNote=null, correspAuthorsNote=null, copyrightStatement=null, copyrightOwner=null, extLink=null, articleAbsUrl=null, sourceXml=null, magXml=null, pdfUrl=null, pdf=null, pdfFileSize=null, pdfExtLink=null, richHtmlUrl=null, mobilePdfUrl=null, reviewReport=null, pdfFirstPage=null, abstractGraph=null, abstractGraphContent=null, abstractVideo=null, citation=null, cebUrl=null, magXmlContent=null, mapNumber=null, authorCompany=null, fund=null, authors=null, authorsList=Rui YUAN, Jing TONG, Wen-Xuan LI, Wen-Bo DING, Sai FAN, Rong ZHAO, Wei LIU), CN=ArticleExt(id=1215670320611119174, articleId=1215670315569566484, tenantId=1146029695717560320, journalId=1149652044408987649, language=CN, title=液相色谱-串联质谱法同时测定食品接触材料中有机磷酸酯、亚磷酸酯及对羟基苯甲酸酯迁移量, columnId=1215670313522746049, journalTitle=食品安全质量检测学报, columnName=专题:北京市食品安全风险监测与评估, runingTitle=null, highlight=null, articleAbstract=

目的 建立液相色谱-串联质谱法同时测定食品接触材料中24种有机磷酸酯(organophosphate esters, OPEs)、亚磷酸酯(organophosphite antioxidants, OPAs)及对羟基苯甲酸酯(parabens, PBs)类化合物迁移量的方法。方法 待测食品接触材料按照预期接触食品的种类和方式, 进行迁移实验, 获得浸泡液。浸泡液经离心后, 采用液相色谱法分离, 串联质谱法测定, 基质匹配标准曲线定量。结果 优化后的方法, 可以同时检测食品接触材料迁移浸泡液中24种OPEs、OPAs及PBs类物质, 检出限为0.01~0.58 µg/L, 定量限为0.03~2.00 µg/L, 加标回收率范围为69.0%~129.6%, 相对标准偏差为0.5%~10.9% (n=6)。对20件包装膜袋、10件一次性外卖盒及20件纸制餐具进行测定, ΣOPEs范围为<检出限~19.1 μg/L, ΣOPAs范围为<检出限~1248 μg/L, ΣPBs范围为<检出限~0.501 μg/L。食品接触材料迁移量监测较少, 其健康风险需要得到更多重视及研究。结论 该方法操作简单, 灵敏度高, 适用于食品接触材料样品OPEs、OPAs和PBs的迁移量测定。

, correspAuthors=刘伟, authorNote=null, correspAuthorsNote=
*刘伟(1983—), 男, 硕士, 副主任技师, 主要研究方向为食品安全检测。E-mail:
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袁蕊(1987—), 女, 硕士, 副主任技师, 主要研究方向为食品安全检测。E-mail:

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Determination of bisphenols, triclosan, and parabens in bottled water by solid-phase microextraction combined with gas chromatography-tandem mass spectrometry and assessment of the associated health risk[J]. Journal of Food Composition and Analysis, 2023, 123: 105548., articleTitle=Determination of bisphenols, triclosan, and parabens in bottled water by solid-phase microextraction combined with gas chromatography-tandem mass spectrometry and assessment of the associated health risk, refAbstract=null)], funds=[Fund(id=1215686862484722138, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, awardId=2024-dchrcprzz-40, language=CN, fundingSource=北京市东城区优秀人才培养资助项目(2024-dchrcprzz-40), fundOrder=null, country=null), Fund(id=1215686862610551265, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, awardId=东卫健研[2024]-19, language=CN, fundingSource=北京市东城区卫生科技计划项目(东卫健研[2024]-19), fundOrder=null, country=null)], companyList=[AuthorCompany(id=1215686854737842332, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, xref=1, ext=[AuthorCompanyExt(id=1215686854746230942, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, companyId=1215686854737842332, language=EN, country=null, province=null, city=null, postcode=null, companyName=null, departmentName=null, remark=1 Beijing Dongcheng District Center for Disease Control and Prevention/Centre for Public Health Emergency Management Innovation, Beijing 100050, China), AuthorCompanyExt(id=1215686854750425248, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, companyId=1215686854737842332, language=CN, country=null, province=null, city=null, postcode=null, companyName=null, departmentName=null, remark=1 北京市东城区疾病预防控制中心/公共卫生应急管理创新中心, 北京 100050)]), AuthorCompany(id=1215686854851088552, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, xref=2, ext=[AuthorCompanyExt(id=1215686854859477161, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, companyId=1215686854851088552, language=EN, country=null, province=null, city=null, postcode=null, companyName=null, departmentName=null, remark=2 Beijing Center for Disease Control and Prevention, Beijing 100013, China), AuthorCompanyExt(id=1215686854863671466, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, companyId=1215686854851088552, language=CN, country=null, province=null, city=null, postcode=null, companyName=null, departmentName=null, remark=2 北京市疾病预防控制中心, 北京 100013)])], figs=[ArticleFig(id=1215686861167710619, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, language=EN, label=Fig.1, caption=Extracted ion chromatogram of standard sample (50 µg/L), figureFileSmall=biNjckodg/szlvkm5+LXaw==, figureFileBig=ZBpkMiw1QQO/WGy1TKpN3Q==, tableContent=null), ArticleFig(id=1215686861247402399, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, language=CN, label=图1, caption=标准样品选择离子流图(50 µg/L), figureFileSmall=biNjckodg/szlvkm5+LXaw==, figureFileBig=ZBpkMiw1QQO/WGy1TKpN3Q==, tableContent=null), ArticleFig(id=1215686861385814439, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, language=EN, label=Table 1, caption=

Mass spectrum parameters of the analyte

, figureFileSmall=null, figureFileBig=null, tableContent=
类别 目标物 母离子
(m/z)
子离子
(m/z)
锥孔电压
/eV
碰撞能量
/eV
OPEs TMP 141.2 109.0*、127.0 60 23、23
TEP 183.1 99.1*、127.1 30 30、15
TNPP 225.3 99.1*、141.0 40 30、14
TIPP 225.3 99.1*、141.0 40 30、14
TNBP 267.1 99.0*、155.0 40 24、14
TCEP 284.9 99.0*、161.1 50 42、31
TPHP 327.0 77.0*、153.2 100 57、33
TCIPP 327.1 99.1*、251.1 100 28、13
TMPP 369.1 166.0*、243.1 160 40、42
TBOEP 399.0 199.2*、299.1 100 25、15
TDCIPP 430.9 208.9*、99.1 100 23、42
TNPTP 309.0 99.0*、169.1 60 34、20
TEHP 435.2 99.3*、321.0 100 50、26
EHDPP 363.0 251.2*、77.2 40 33、54
TIPPP 453.2 369.0*、327.0 140 35、45
OPAs AO168O 663.5 551.4*、495.1 160 34、44
AO168 647.6 441.3*、347.5 130 44、50
AO626 605.3 335.2*、279.2 130 26、36
AO1222 357.3 301.4*、217.2 100 22、32
DiOPPi 379.2 379.2*、351.0 130 13、30
PBs MEP 151.0 136.0*、91.9 -100 -18、-25
ETP 165.0 137.1*、92.0 -100 -18、-27
PRP 178.9 137.0*、91.9 -100 -20、-28
BUP 193.0 137.0*、92.0 -100 -21、-28
), ArticleFig(id=1215686861503254958, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, language=CN, label=表1, caption=

待测物的质谱参数

, figureFileSmall=null, figureFileBig=null, tableContent=
类别 目标物 母离子
(m/z)
子离子
(m/z)
锥孔电压
/eV
碰撞能量
/eV
OPEs TMP 141.2 109.0*、127.0 60 23、23
TEP 183.1 99.1*、127.1 30 30、15
TNPP 225.3 99.1*、141.0 40 30、14
TIPP 225.3 99.1*、141.0 40 30、14
TNBP 267.1 99.0*、155.0 40 24、14
TCEP 284.9 99.0*、161.1 50 42、31
TPHP 327.0 77.0*、153.2 100 57、33
TCIPP 327.1 99.1*、251.1 100 28、13
TMPP 369.1 166.0*、243.1 160 40、42
TBOEP 399.0 199.2*、299.1 100 25、15
TDCIPP 430.9 208.9*、99.1 100 23、42
TNPTP 309.0 99.0*、169.1 60 34、20
TEHP 435.2 99.3*、321.0 100 50、26
EHDPP 363.0 251.2*、77.2 40 33、54
TIPPP 453.2 369.0*、327.0 140 35、45
OPAs AO168O 663.5 551.4*、495.1 160 34、44
AO168 647.6 441.3*、347.5 130 44、50
AO626 605.3 335.2*、279.2 130 26、36
AO1222 357.3 301.4*、217.2 100 22、32
DiOPPi 379.2 379.2*、351.0 130 13、30
PBs MEP 151.0 136.0*、91.9 -100 -18、-25
ETP 165.0 137.1*、92.0 -100 -18、-27
PRP 178.9 137.0*、91.9 -100 -20、-28
BUP 193.0 137.0*、92.0 -100 -21、-28
), ArticleFig(id=1215686861633278387, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, language=EN, label=Table 2, caption=

Influence of different microporous membranes on experimental results (%)

, figureFileSmall=null, figureFileBig=null, tableContent=
化合物 95%乙醇 10%乙醇 4%乙酸
疏水聚四氟乙烯 亲水聚四氟乙烯 再生纤维素 尼龙 混合纤维素酯 疏水聚四氟乙烯 亲水聚四氟乙烯 再生纤维素 尼龙 混合纤维素酯 疏水聚四氟乙烯 亲水聚四氟乙烯 再生纤维素 尼龙 混合纤维素酯
TMP 101.2 95.8 57.0 73.2 56.1 103.4 100.3 94.7 96.7 94.7 103.8 103.6 107.8 108.3 105.6
TEP 100.8 105.0 138.2 116.3 103.6 984.0 97.6 99.9 102.0 90.8 102.5 104.1 109.0 109.2 105.6
TNPP 103.0 109.3 110.9 111.1 114.3 96.8 99.5 108.2 109.2 96.8 101.4 106.4 106.0 97.2 104.1
TIPP 116.2 113.2 159.9 154.0 178.4 91.1 108.7 83.0 93.6 76.5 96.7 87.8 140.8 136.0 136.0
TNBP 99.3 102.4 110.2 107.5 81.9 82.6 88.1 92.2 78.1 75.5 63.3 89.2 102.6 58.3 67.7
TCEP 96.5 101.9 82.4 88.2 81.6 96.7 94.3 87.5 98.6 86.0 103.2 105.1 107.8 116.1 112.5
TPHP 102.2 112.7 123.4 110.3 124.4 68.5 24.4 3.8 77.0 4.2 61.4 14.6 4.5 54.7 5.8
TCIPP 101.3 94.6 123.7 109.7 127.3 86.3 94.9 116.4 109.7 101.4 88.0 91.2 103.4 114.4 110.5
TMPP 105.7 112.2 125.1 113.2 128.0 24.3 18.8 8.0 56.0 19.7 45.9 39.1 67.7 16.8 19.5
TBOEP 98.6 103.7 115.2 108.9 97.7 63.5 86.1 91.7 528.0 63.8 50.3 83.9 97.7 55.0 67.7
TDCIPP 100.7 109.8 119.5 112.6 124.9 76.9 50.6 47.4 81.8 20.7 77.4 39.7 52.7 70.0 15.7
TNPTP 100.3 106.3 112.7 108.4 111.0 33.5 24.4 16.0 40.8 22.5 59.8 55.6 36.2 52.3 24.7
TEHP 85.7 100.2 155.2 121.8 134.7 106.0 18.8 105.6 407.8 364.6 24.6 64.9 18.5 103.7 36.5
EHDPP 111.3 139.7 72.2 77.6 84.1 20.0 27.1 20.2 110.8 43.0 63.8 114.6 55.7 28.2 26.6
TIPPP 99.9 104.4 111.9 105.9 112.7 29.1 7.2 44.6 395.7 242.5 18.5 39.1 292.8 106.4 26.0
AO168 108.1 102.6 143.5 103.1 108.9 66.6 19.4 42.7 524.0 54.8 27.2 60.5 24.0 289.0 55.4
AO168O 111.8 638.9 142.4 110.9 658.6 106.9 129.3 55.2 426.9 290.5 41.2 71.0 38.3 192.7 61.3
AO626 103.5 109.8 142.0 137.3 140.0 48.1 16.9 34.9 438.7 296.9 10.5 6.5 8.8 259.4 30.4
AO1222 99.2 96.0 112.9 104.7 64.7 66.8 75.2 92.5 59.5 55.9 52.4 57.7 90.0 57.0 42.5
DiOPPi 81.4 78.7 130.9 114.3 73.0 55.9 63.5 94.8 61.8 70.8 45.7 49.1 96.1 54.5 55.2
MEP 104.6 111.5 117.0 115.2 35.9 97.3 97.7 101.1 101.5 101.2 95.9 92.9 100.8 96.2 102.1
ETP 100.5 107.0 112.4 110.8 112.4 96.5 92.2 106.2 103.4 99.9 103.2 97.8 95.0 95.3 96.3
PRP 105.6 110.9 115.0 112.6 160.3 95.4 92.5 93.4 99.5 92.1 97.8 94.2 88.7 92.6 83.0
BUP 106.4 115.6 112.7 114.0 109.4 93.5 88.8 85.3 102.4 81.6 95.8 86.6 78.3 91.6 62.1
), ArticleFig(id=1215686861763301818, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, language=CN, label=表2, caption=

不同微孔滤膜对实验结果影响(%)

, figureFileSmall=null, figureFileBig=null, tableContent=
化合物 95%乙醇 10%乙醇 4%乙酸
疏水聚四氟乙烯 亲水聚四氟乙烯 再生纤维素 尼龙 混合纤维素酯 疏水聚四氟乙烯 亲水聚四氟乙烯 再生纤维素 尼龙 混合纤维素酯 疏水聚四氟乙烯 亲水聚四氟乙烯 再生纤维素 尼龙 混合纤维素酯
TMP 101.2 95.8 57.0 73.2 56.1 103.4 100.3 94.7 96.7 94.7 103.8 103.6 107.8 108.3 105.6
TEP 100.8 105.0 138.2 116.3 103.6 984.0 97.6 99.9 102.0 90.8 102.5 104.1 109.0 109.2 105.6
TNPP 103.0 109.3 110.9 111.1 114.3 96.8 99.5 108.2 109.2 96.8 101.4 106.4 106.0 97.2 104.1
TIPP 116.2 113.2 159.9 154.0 178.4 91.1 108.7 83.0 93.6 76.5 96.7 87.8 140.8 136.0 136.0
TNBP 99.3 102.4 110.2 107.5 81.9 82.6 88.1 92.2 78.1 75.5 63.3 89.2 102.6 58.3 67.7
TCEP 96.5 101.9 82.4 88.2 81.6 96.7 94.3 87.5 98.6 86.0 103.2 105.1 107.8 116.1 112.5
TPHP 102.2 112.7 123.4 110.3 124.4 68.5 24.4 3.8 77.0 4.2 61.4 14.6 4.5 54.7 5.8
TCIPP 101.3 94.6 123.7 109.7 127.3 86.3 94.9 116.4 109.7 101.4 88.0 91.2 103.4 114.4 110.5
TMPP 105.7 112.2 125.1 113.2 128.0 24.3 18.8 8.0 56.0 19.7 45.9 39.1 67.7 16.8 19.5
TBOEP 98.6 103.7 115.2 108.9 97.7 63.5 86.1 91.7 528.0 63.8 50.3 83.9 97.7 55.0 67.7
TDCIPP 100.7 109.8 119.5 112.6 124.9 76.9 50.6 47.4 81.8 20.7 77.4 39.7 52.7 70.0 15.7
TNPTP 100.3 106.3 112.7 108.4 111.0 33.5 24.4 16.0 40.8 22.5 59.8 55.6 36.2 52.3 24.7
TEHP 85.7 100.2 155.2 121.8 134.7 106.0 18.8 105.6 407.8 364.6 24.6 64.9 18.5 103.7 36.5
EHDPP 111.3 139.7 72.2 77.6 84.1 20.0 27.1 20.2 110.8 43.0 63.8 114.6 55.7 28.2 26.6
TIPPP 99.9 104.4 111.9 105.9 112.7 29.1 7.2 44.6 395.7 242.5 18.5 39.1 292.8 106.4 26.0
AO168 108.1 102.6 143.5 103.1 108.9 66.6 19.4 42.7 524.0 54.8 27.2 60.5 24.0 289.0 55.4
AO168O 111.8 638.9 142.4 110.9 658.6 106.9 129.3 55.2 426.9 290.5 41.2 71.0 38.3 192.7 61.3
AO626 103.5 109.8 142.0 137.3 140.0 48.1 16.9 34.9 438.7 296.9 10.5 6.5 8.8 259.4 30.4
AO1222 99.2 96.0 112.9 104.7 64.7 66.8 75.2 92.5 59.5 55.9 52.4 57.7 90.0 57.0 42.5
DiOPPi 81.4 78.7 130.9 114.3 73.0 55.9 63.5 94.8 61.8 70.8 45.7 49.1 96.1 54.5 55.2
MEP 104.6 111.5 117.0 115.2 35.9 97.3 97.7 101.1 101.5 101.2 95.9 92.9 100.8 96.2 102.1
ETP 100.5 107.0 112.4 110.8 112.4 96.5 92.2 106.2 103.4 99.9 103.2 97.8 95.0 95.3 96.3
PRP 105.6 110.9 115.0 112.6 160.3 95.4 92.5 93.4 99.5 92.1 97.8 94.2 88.7 92.6 83.0
BUP 106.4 115.6 112.7 114.0 109.4 93.5 88.8 85.3 102.4 81.6 95.8 86.6 78.3 91.6 62.1
), ArticleFig(id=1215686861880742337, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, language=EN, label=Table 3, caption=

Linear ranges, LODs and LOQs

, figureFileSmall=null, figureFileBig=null, tableContent=
化合物 线性范围
/(µg/L)
95%乙醇 10%乙醇 4%乙酸
线性相关系数 LODs
/(µg/L)
LOQs
/(µg/L)
线性相关系数 LODs
/(µg/L)
LOQs
/(µg/L)
线性相关系数 LODs
/(µg/L)
LOQs
/(µg/L)
TMP 1~200 0.9999 0.06 0.20 0.9983 0.01 0.03 0.9999 0.02 0.06
TEP 1~200 0.9997 0.01 0.03 0.9992 0.02 0.06 0.9993 0.02 0.06
TNPP 1~200 0.9998 0.03 0.09 0.9963 0.03 0.09 0.9945 0.02 0.06
TIPP 1~200 0.9974 0.04 0.12 0.9956 0.04 0.12 0.9935 0.03 0.10
TNBP 1~200 0.9974 0.01 0.03 0.9966 0.01 0.03 0.9963 0.01 0.03
TCEP 1~200 0.9992 0.02 0.06 0.9997 0.02 0.06 0.9970 0.02 0.06
TPHP 1~200 0.9997 0.03 0.10 0.9993 0.02 0.06 0.9991 0.02 0.06
TCIPP 1~200 0.9959 0.42 1.40 0.9976 0.31 1.10 0.9919 0.33 1.10
TMPP 1~200 0.9994 0.03 0.11 0.9977 0.03 0.10 0.9978 0.04 0.13
TBOEP 1~200 0.9937 0.01 0.03 0.9969 0.01 0.03 0.9981 0.01 0.03
TDCIPP 1~200 0.9987 0.10 0.34 0.9965 0.12 0.39 0.9958 0.06 0.18
TNPTP 1~200 0.9996 0.01 0.03 0.9971 0.01 0.03 0.9941 0.02 0.06
TEHP 1~200 0.9946 0.06 0.20 0.9940 0.22 0.70 0.9915 0.16 0.50
EHDPP 1~200 0.9942 0.15 0.50 0.9905 0.37 1.20 0.9937 0.26 0.85
TIPPP 1~200 0.9916 0.01 0.03 0.9943 0.01 0.03 0.9906 0.01 0.03
AO168 1~200 0.9985 0.01 0.03 0.9998 0.01 0.03 0.9982 0.01 0.03
AO168O 1~200 0.9976 0.02 0.06 0.9996 0.02 0.06 0.9987 0.03 0.10
AO626 1~200 0.9995 0.01 0.03 0.9996 0.01 0.03 0.9993 0.03 0.10
AO1222 1~200 0.9929 0.01 0.03 0.9961 0.01 0.03 0.9917 0.01 0.03
DiOPPi 1~200 0.9930 0.35 1.20 0.9977 0.39 1.30 0.9984 0.58 2.00
MEP 0.1~20.0 0.9996 0.02 0.06 0.9996 0.02 0.06 0.9994 0.02 0.06
ETP 0.1~20.0 0.9997 0.02 0.06 0.9999 0.02 0.06 0.9993 0.02 0.06
PRP 0.1~20.0 0.9999 0.02 0.06 0.9998 0.02 0.06 0.9998 0.02 0.06
BUP 0.1~20.0 0.9999 0.02 0.06 0.9998 0.02 0.06 0.9994 0.02 0.06
), ArticleFig(id=1215686862027542984, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, language=CN, label=表3, caption=

线性范围、LODs及LOQs

, figureFileSmall=null, figureFileBig=null, tableContent=
化合物 线性范围
/(µg/L)
95%乙醇 10%乙醇 4%乙酸
线性相关系数 LODs
/(µg/L)
LOQs
/(µg/L)
线性相关系数 LODs
/(µg/L)
LOQs
/(µg/L)
线性相关系数 LODs
/(µg/L)
LOQs
/(µg/L)
TMP 1~200 0.9999 0.06 0.20 0.9983 0.01 0.03 0.9999 0.02 0.06
TEP 1~200 0.9997 0.01 0.03 0.9992 0.02 0.06 0.9993 0.02 0.06
TNPP 1~200 0.9998 0.03 0.09 0.9963 0.03 0.09 0.9945 0.02 0.06
TIPP 1~200 0.9974 0.04 0.12 0.9956 0.04 0.12 0.9935 0.03 0.10
TNBP 1~200 0.9974 0.01 0.03 0.9966 0.01 0.03 0.9963 0.01 0.03
TCEP 1~200 0.9992 0.02 0.06 0.9997 0.02 0.06 0.9970 0.02 0.06
TPHP 1~200 0.9997 0.03 0.10 0.9993 0.02 0.06 0.9991 0.02 0.06
TCIPP 1~200 0.9959 0.42 1.40 0.9976 0.31 1.10 0.9919 0.33 1.10
TMPP 1~200 0.9994 0.03 0.11 0.9977 0.03 0.10 0.9978 0.04 0.13
TBOEP 1~200 0.9937 0.01 0.03 0.9969 0.01 0.03 0.9981 0.01 0.03
TDCIPP 1~200 0.9987 0.10 0.34 0.9965 0.12 0.39 0.9958 0.06 0.18
TNPTP 1~200 0.9996 0.01 0.03 0.9971 0.01 0.03 0.9941 0.02 0.06
TEHP 1~200 0.9946 0.06 0.20 0.9940 0.22 0.70 0.9915 0.16 0.50
EHDPP 1~200 0.9942 0.15 0.50 0.9905 0.37 1.20 0.9937 0.26 0.85
TIPPP 1~200 0.9916 0.01 0.03 0.9943 0.01 0.03 0.9906 0.01 0.03
AO168 1~200 0.9985 0.01 0.03 0.9998 0.01 0.03 0.9982 0.01 0.03
AO168O 1~200 0.9976 0.02 0.06 0.9996 0.02 0.06 0.9987 0.03 0.10
AO626 1~200 0.9995 0.01 0.03 0.9996 0.01 0.03 0.9993 0.03 0.10
AO1222 1~200 0.9929 0.01 0.03 0.9961 0.01 0.03 0.9917 0.01 0.03
DiOPPi 1~200 0.9930 0.35 1.20 0.9977 0.39 1.30 0.9984 0.58 2.00
MEP 0.1~20.0 0.9996 0.02 0.06 0.9996 0.02 0.06 0.9994 0.02 0.06
ETP 0.1~20.0 0.9997 0.02 0.06 0.9999 0.02 0.06 0.9993 0.02 0.06
PRP 0.1~20.0 0.9999 0.02 0.06 0.9998 0.02 0.06 0.9998 0.02 0.06
BUP 0.1~20.0 0.9999 0.02 0.06 0.9998 0.02 0.06 0.9994 0.02 0.06
), ArticleFig(id=1215686862144983502, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, language=EN, label=Table 4, caption=

Precision and accuracy (n=6)

, figureFileSmall=null, figureFileBig=null, tableContent=
浸泡液 化合物 本底样品浓度
/(μg/L)
低浓度加标(10/1 μg/L) 中浓度加标(50/5 μg/L) 高浓度加标(100/10 μg/L)
平均回收率/% RSDs/% 平均回收率/% RSDs/% 平均回收率/% RSDs/%
95%乙醇 TMP <LOD 97.0 0.8 96.1 0.7 99.9 0.7
TEP <LOD 99.8 1.8 98.5 2.8 101.6 1.3
TNPP <LOD 112.8 3.0 107.4 3.9 105.9 3.1
TIPP <LOD 77.9 8.8 85.8 7.5 110.9 3.7
TNBP <LOD 121.8 6.4 111.1 5.9 101.1 4.8
TCEP <LOD 107.3 2.0 102.3 2.7 103.3 2.1
TPHP <LOD 109.8 3.8 107.1 2.7 108.3 1.1
TCIPP <LOD 110.2 4.0 105.1 6.0 101.3 5.4
TMPP <LOD 101.2 4.2 100.4 3.3 100.8 3.3
TBOEP <LOD 119.2 4.3 112.9 2.0 106.7 1.9
TDCIPP <LOD 103.6 2.0 100.9 2.5 101.9 1.8
TNPTP <LOD 115.1 2.7 106.6 3.9 102.2 2.5
TEHP <LOD 101.9 7.2 110.2 6.8 94.5 6.7
EHDPP <LOD 95.4 10.4 88.4 9.7 90.1 8.2
TIPPP <LOD 121.7 1.2 115.1 1.5 109.8 1.2
AO168 <LOD 109.3 1.6 106.8 1.3 107.5 1.3
AO168O 2.41 115.7 1.9 109.7 2.6 106.0 1.6
AO626 0.714 106.7 1.3 102.9 2.1 103.8 2.0
AO1222 <LOD 122.9 2.7 105.5 3.6 91.2 1.4
DiOPPi <LOD 111.1 8.6 105.0 7.9 90.3 7.6
MEP <LOD 75.0 10.0 83.2 3.2 102.8 0.7
ETP <LOD 119.6 5.0 102.9 4.5 105.3 1.2
PRP <LOD 79.9 8.9 92.1 4.7 103.3 1.5
BUP <LOD 74.9 10.4 85.7 4.0 100.4 2.7
10%乙醇 TMP 0.138 96.5 1.1 99.5 1.2 100.1 0.5
TEP <LOD 99.8 2.4 104.6 1.4 102.9 1.0
TNPP <LOD 119.7 2.7 120.6 2.8 112.2 3.4
TIPP 0.0406 92.0 8.6 103.1 8.8 102.5 8.4
TNBP <LOD 111.1 6.2 113.6 6.1 115.5 5.3
TCEP <LOD 112.3 2.2 112.7 2.4 106.0 4.1
TPHP 0.0636 116.5 3.0 109.6 4.5 110.6 4.5
TCIPP <LOD 121.6 3.4 122.5 2.1 109.6 3.0
TMPP 0.773 94.2 2.5 103.2 3.1 104.0 3.3
TBOEP <LOD 119.0 4.1 115.1 3.8 110.9 2.5
TDCIPP <LOD 111.4 4.8 110.7 2.4 108.6 2.6
TNPTP 0.179 94.0 6.9 102.3 7.0 112.4 3.3
TEHP <LOD 74.4 6.0 89.2 6.0 101.2 6.4
EHDPP <LOD 78.7 8.1 105.2 8.5 102.5 7.7
TIPPP 0.128 77.7 1.7 104.7 1.3 107.4 1.8
AO168 <LOD 107.4 2.1 105.9 1.3 103.4 1.2
AO168O 1.23 114.6 3.9 112.8 2.8 108.6 3.1
AO626 0.489 107.6 4.3 112.9 3.7 111.8 4.2
AO1222 <LOD 114.4 4.7 112.2 3.6 94.7 3.4
DiOPPi <LOD 101.1 8.8 94.6 6.9 99.2 5.3
MEP <LOD 108.3 9.5 100.5 6.9 101.0 1.3
ETP <LOD 104.2 9.4 103.7 1.9 103.4 2.0
PRP <LOD 106.6 9.8 96.2 4.9 99.4 1.3
BUP <LOD 93.2 10.6 95.8 1.4 99.9 2.2
4%乙酸 TMP <LOD 102.0 0.6 99.1 0.7 99.1 0.7
TEP <LOD 104.9 1.5 100.6 1.7 98.7 0.8
TNPP <LOD 108.4 3.3 100.4 3.1 95.7 2.8
TIPP <LOD 107.3 9.1 94.9 7.0 92.4 5.7
TNBP <LOD 119.1 5.4 106.6 4.1 113.8 3.3
TCEP 0.0216 112.1 2.6 107.5 1.4 108.2 1.2
TPHP <LOD 116.8 3.2 108.9 1.9 110.7 1.6
TCIPP <LOD 117.2 5.2 113.4 5.5 108.7 4.9
TMPP <LOD 82.2 4.2 95.9 4.1 100.5 5.1
TBOEP 0.235 110.7 3.7 115.4 4.5 107.5 3.1
TDCIPP <LOD 119.2 3.2 108.1 2.3 108.2 1.2
TNPTP 0.151 72.2 1.4 100.2 5.3 99.3 5.2
TEHP 0.0508 82.6 10.9 89.9 7.6 103.8 5.7
EHDPP 1.81 82.6 9.8 79.6 9.1 84.9 4.4
TIPPP <LOD 78.8 10.8 96.0 7.2 109.1 4.6
AO168 0.555 83.4 7.9 80.8 4.6 94.5 2.9
AO168O 1.44 79.9 8.9 73.5 4.3 82.0 4.3
AO626 <LOD 82.9 10.1 82.4 6.1 100.9 5.3
AO1222 <LOD 126.4 2.4 109.4 1.8 91.8 2.1
DiOPPi <LOD 103.2 10.3 96.0 3.4 90.4 4.0
MEP <LOD 85.6 10.9 94.2 7.5 100.1 1.5
ETP <LOD 88.7 8.6 97.4 4.3 100.0 1.5
PRP <LOD 106.4 6.2 99.0 5.5 100.6 1.6
BUP <LOD 106.8 7.6 98.7 2.3 100.5 0.7
), ArticleFig(id=1215686862254035411, tenantId=1146029695717560320, journalId=1149652044408987649, articleId=1215670315569566484, language=CN, label=表4, caption=

精密度及准确度(n=6)

, figureFileSmall=null, figureFileBig=null, tableContent=
浸泡液 化合物 本底样品浓度
/(μg/L)
低浓度加标(10/1 μg/L) 中浓度加标(50/5 μg/L) 高浓度加标(100/10 μg/L)
平均回收率/% RSDs/% 平均回收率/% RSDs/% 平均回收率/% RSDs/%
95%乙醇 TMP <LOD 97.0 0.8 96.1 0.7 99.9 0.7
TEP <LOD 99.8 1.8 98.5 2.8 101.6 1.3
TNPP <LOD 112.8 3.0 107.4 3.9 105.9 3.1
TIPP <LOD 77.9 8.8 85.8 7.5 110.9 3.7
TNBP <LOD 121.8 6.4 111.1 5.9 101.1 4.8
TCEP <LOD 107.3 2.0 102.3 2.7 103.3 2.1
TPHP <LOD 109.8 3.8 107.1 2.7 108.3 1.1
TCIPP <LOD 110.2 4.0 105.1 6.0 101.3 5.4
TMPP <LOD 101.2 4.2 100.4 3.3 100.8 3.3
TBOEP <LOD 119.2 4.3 112.9 2.0 106.7 1.9
TDCIPP <LOD 103.6 2.0 100.9 2.5 101.9 1.8
TNPTP <LOD 115.1 2.7 106.6 3.9 102.2 2.5
TEHP <LOD 101.9 7.2 110.2 6.8 94.5 6.7
EHDPP <LOD 95.4 10.4 88.4 9.7 90.1 8.2
TIPPP <LOD 121.7 1.2 115.1 1.5 109.8 1.2
AO168 <LOD 109.3 1.6 106.8 1.3 107.5 1.3
AO168O 2.41 115.7 1.9 109.7 2.6 106.0 1.6
AO626 0.714 106.7 1.3 102.9 2.1 103.8 2.0
AO1222 <LOD 122.9 2.7 105.5 3.6 91.2 1.4
DiOPPi <LOD 111.1 8.6 105.0 7.9 90.3 7.6
MEP <LOD 75.0 10.0 83.2 3.2 102.8 0.7
ETP <LOD 119.6 5.0 102.9 4.5 105.3 1.2
PRP <LOD 79.9 8.9 92.1 4.7 103.3 1.5
BUP <LOD 74.9 10.4 85.7 4.0 100.4 2.7
10%乙醇 TMP 0.138 96.5 1.1 99.5 1.2 100.1 0.5
TEP <LOD 99.8 2.4 104.6 1.4 102.9 1.0
TNPP <LOD 119.7 2.7 120.6 2.8 112.2 3.4
TIPP 0.0406 92.0 8.6 103.1 8.8 102.5 8.4
TNBP <LOD 111.1 6.2 113.6 6.1 115.5 5.3
TCEP <LOD 112.3 2.2 112.7 2.4 106.0 4.1
TPHP 0.0636 116.5 3.0 109.6 4.5 110.6 4.5
TCIPP <LOD 121.6 3.4 122.5 2.1 109.6 3.0
TMPP 0.773 94.2 2.5 103.2 3.1 104.0 3.3
TBOEP <LOD 119.0 4.1 115.1 3.8 110.9 2.5
TDCIPP <LOD 111.4 4.8 110.7 2.4 108.6 2.6
TNPTP 0.179 94.0 6.9 102.3 7.0 112.4 3.3
TEHP <LOD 74.4 6.0 89.2 6.0 101.2 6.4
EHDPP <LOD 78.7 8.1 105.2 8.5 102.5 7.7
TIPPP 0.128 77.7 1.7 104.7 1.3 107.4 1.8
AO168 <LOD 107.4 2.1 105.9 1.3 103.4 1.2
AO168O 1.23 114.6 3.9 112.8 2.8 108.6 3.1
AO626 0.489 107.6 4.3 112.9 3.7 111.8 4.2
AO1222 <LOD 114.4 4.7 112.2 3.6 94.7 3.4
DiOPPi <LOD 101.1 8.8 94.6 6.9 99.2 5.3
MEP <LOD 108.3 9.5 100.5 6.9 101.0 1.3
ETP <LOD 104.2 9.4 103.7 1.9 103.4 2.0
PRP <LOD 106.6 9.8 96.2 4.9 99.4 1.3
BUP <LOD 93.2 10.6 95.8 1.4 99.9 2.2
4%乙酸 TMP <LOD 102.0 0.6 99.1 0.7 99.1 0.7
TEP <LOD 104.9 1.5 100.6 1.7 98.7 0.8
TNPP <LOD 108.4 3.3 100.4 3.1 95.7 2.8
TIPP <LOD 107.3 9.1 94.9 7.0 92.4 5.7
TNBP <LOD 119.1 5.4 106.6 4.1 113.8 3.3
TCEP 0.0216 112.1 2.6 107.5 1.4 108.2 1.2
TPHP <LOD 116.8 3.2 108.9 1.9 110.7 1.6
TCIPP <LOD 117.2 5.2 113.4 5.5 108.7 4.9
TMPP <LOD 82.2 4.2 95.9 4.1 100.5 5.1
TBOEP 0.235 110.7 3.7 115.4 4.5 107.5 3.1
TDCIPP <LOD 119.2 3.2 108.1 2.3 108.2 1.2
TNPTP 0.151 72.2 1.4 100.2 5.3 99.3 5.2
TEHP 0.0508 82.6 10.9 89.9 7.6 103.8 5.7
EHDPP 1.81 82.6 9.8 79.6 9.1 84.9 4.4
TIPPP <LOD 78.8 10.8 96.0 7.2 109.1 4.6
AO168 0.555 83.4 7.9 80.8 4.6 94.5 2.9
AO168O 1.44 79.9 8.9 73.5 4.3 82.0 4.3
AO626 <LOD 82.9 10.1 82.4 6.1 100.9 5.3
AO1222 <LOD 126.4 2.4 109.4 1.8 91.8 2.1
DiOPPi <LOD 103.2 10.3 96.0 3.4 90.4 4.0
MEP <LOD 85.6 10.9 94.2 7.5 100.1 1.5
ETP <LOD 88.7 8.6 97.4 4.3 100.0 1.5
PRP <LOD 106.4 6.2 99.0 5.5 100.6 1.6
BUP <LOD 106.8 7.6 98.7 2.3 100.5 0.7
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液相色谱-串联质谱法同时测定食品接触材料中有机磷酸酯、亚磷酸酯及对羟基苯甲酸酯迁移量
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袁蕊 1 , 佟晶 1 , 李文萱 1 , 丁文波 1 , 范赛 2 , 赵榕 2 , 刘伟 2, *
食品安全质量检测学报 | 专题:北京市食品安全风险监测与评估 2025,16(14): 30-39
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食品安全质量检测学报 | 专题:北京市食品安全风险监测与评估 2025, 16(14): 30-39
液相色谱-串联质谱法同时测定食品接触材料中有机磷酸酯、亚磷酸酯及对羟基苯甲酸酯迁移量
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袁蕊1 , 佟晶1, 李文萱1, 丁文波1, 范赛2, 赵榕2, 刘伟2, *
作者信息
  • 1 北京市东城区疾病预防控制中心/公共卫生应急管理创新中心, 北京 100050
  • 2 北京市疾病预防控制中心, 北京 100013
  • 袁蕊(1987—), 女, 硕士, 副主任技师, 主要研究方向为食品安全检测。E-mail:

通讯作者:

*刘伟(1983—), 男, 硕士, 副主任技师, 主要研究方向为食品安全检测。E-mail:
Simultaneous determination of organophosphate esters, organophosphite antioxidants and parabens migration in food contact materials by liquid chromatography-tandem mass spectrometry
Rui YUAN1 , Jing TONG1, Wen-Xuan LI1, Wen-Bo DING1, Sai FAN2, Rong ZHAO2, Wei LIU2, *
Affiliations
  • 1 Beijing Dongcheng District Center for Disease Control and Prevention/Centre for Public Health Emergency Management Innovation, Beijing 100050, China
  • 2 Beijing Center for Disease Control and Prevention, Beijing 100013, China
出版时间: 2025-07-25 doi: 10.19812/j.cnki.jfsq11-5956/ts.20250418005
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目的 建立液相色谱-串联质谱法同时测定食品接触材料中24种有机磷酸酯(organophosphate esters, OPEs)、亚磷酸酯(organophosphite antioxidants, OPAs)及对羟基苯甲酸酯(parabens, PBs)类化合物迁移量的方法。方法 待测食品接触材料按照预期接触食品的种类和方式, 进行迁移实验, 获得浸泡液。浸泡液经离心后, 采用液相色谱法分离, 串联质谱法测定, 基质匹配标准曲线定量。结果 优化后的方法, 可以同时检测食品接触材料迁移浸泡液中24种OPEs、OPAs及PBs类物质, 检出限为0.01~0.58 µg/L, 定量限为0.03~2.00 µg/L, 加标回收率范围为69.0%~129.6%, 相对标准偏差为0.5%~10.9% (n=6)。对20件包装膜袋、10件一次性外卖盒及20件纸制餐具进行测定, ΣOPEs范围为<检出限~19.1 μg/L, ΣOPAs范围为<检出限~1248 μg/L, ΣPBs范围为<检出限~0.501 μg/L。食品接触材料迁移量监测较少, 其健康风险需要得到更多重视及研究。结论 该方法操作简单, 灵敏度高, 适用于食品接触材料样品OPEs、OPAs和PBs的迁移量测定。

食品接触材料  /  有机磷酸酯  /  迁移量  /  对羟基苯甲酸酯  /  有机亚磷酸酯

Objective To establish a method for simultaneously determining the migration amounts of 24 kinds of organophosphate esters (OPEs), organophosphite antioxidants (OPAs), and parabens (PBs) in food contact materials by liquid chromatography-tandem mass spectrometry. Methods The food contact materials to be tested were subjected to migration experiments in accordance with the expected types of food and contact modes, so as to obtain the soaking solution. After centrifugation, the soaking solution was separated by liquid chromatography, determined by tandem mass spectrometry, and quantified by matrix-matched standard curve. Results The optimized method could simultaneously detect 24 kinds of OPEs, OPAs, and PBs in the migration soaking solutions of food contact materials. The limits of detection were 0.01-0.58 µg/L and the limits of quantitation were 0.03-2.00 µg/L. The spiked samples recovery rates ranged from 69.0%-129.6%, with relative standard deviations of 0.5% to 10.9% (n=6). The 20 packaging film bags, 10 disposable take-out boxes and 20 paper tableware items were tested. The ΣOPEs ranges were <limit of detection-19.1 μg/L, ΣOPAs were <limit of detection-1248 μg/L, and ΣPBs were <limit of detection-0.501 μg/L. The monitoring of the migration amounts of food contact materials was limited, its health risks required more attention and research. Conclusion This method is simple to operate and highly sensitive, which is suitable for the determination of the migration amounts of OPEs, OPAs and PBs in food contact material samples.

food contact materials  /  organophosphate esters  /  migration  /  paraben  /  organophosphite antioxidants
袁蕊, 佟晶, 李文萱, 丁文波, 范赛, 赵榕, 刘伟. 液相色谱-串联质谱法同时测定食品接触材料中有机磷酸酯、亚磷酸酯及对羟基苯甲酸酯迁移量. 食品安全质量检测学报, 2025 , 16 (14) : 30 -39 . DOI: 10.19812/j.cnki.jfsq11-5956/ts.20250418005
Rui YUAN, Jing TONG, Wen-Xuan LI, Wen-Bo DING, Sai FAN, Rong ZHAO, Wei LIU. Simultaneous determination of organophosphate esters, organophosphite antioxidants and parabens migration in food contact materials by liquid chromatography-tandem mass spectrometry[J]. Journal of Food Safety & Quality, 2025 , 16 (14) : 30 -39 . DOI: 10.19812/j.cnki.jfsq11-5956/ts.20250418005
随着生活节奏的加快, 外卖、快餐和预包装食品已深度融入人们的日常生活, 食品包装的安全性问题因此受到越来越多的关注。统计数据显示, 2020年, 中国外卖订单量达到了170亿, 按照每个订单3.44个容器计算, 需消费584.8亿个食品包装容器[1], 其中超过50%的食品包装材料是由纸和塑料制成[2]。这些食品接触材料中含有多种化学物质。这些化学物质不仅来源于材料本身, 还涵盖生产过程中为提升其性能而添加的各类添加剂, 以及在生产加工环节中因副反应生成的化合物、杂质、材料降解产物等[2-5]。这些化学物质, 有一定几率随着与食品接触而进入到人体中, 对消费者构成潜在的健康风险。其中, 有机磷酸酯(organophosphate esters, OPEs)、亚磷酸酯(organophosphite antioxidants, OPAs)以及对羟基苯甲酸酯(parabens, PBs)是逐渐受到关注的化合物。
OPEs是一类阻燃剂, 在全球范围内广泛应用; OPAs是一类以提高聚合物的耐久性为目的的抗氧化添加剂, 经常添加在塑料制品中; parabens, PBs则是一类常见的食品药品、个人护理产品和食品包装材料中的抗菌防腐剂[6-9]。其中, PBs是已被确认具有生殖影响的内分泌干扰物质, 还会产生过敏反应[10-11]。OPEs对健康的不利影响也已经有大量研究证实, 特别是神经毒性、生殖毒性、内分泌干扰和致癌性等[12-15]。尽管OPAs的毒理学研究比较少, 但已有研究表明, OPAs与OPEs具有类似的结构, 因此可能表现出具有潜在的雌激素活性和神经毒性[16]。此外, 模拟实验表明, 在加热、紫外线辐射和水接触条件下, OPAs会显著转化为其氧化产物OPEs, 从而增加OPEs的暴露风险[17]。这些污染物广泛存在于环境中, 人类可以通过呼吸、皮肤、膳食等多种方式暴露。其中, 膳食摄入是人类暴露OPEs的主要暴露途径[18]。而有研究表明, 一些食品中的OPEs的污染主要来自食品包装材料[8,19]。因此, 对于食品接触材料中污染情况的调查和检测非常重要。
与食品相比, 目前对于食品接触材料中OPEs、OPAs及PBs的监测和风险评估的研究仍较为有限。鉴于此, 本研究建立了一种液相色谱-串联质谱法同时测定食品接触材料中24种OPEs、OPAs及PBs的迁移量的方法, 并应用此方法对市售塑料和纸质餐具进行了迁移量检测, 得到了污染情况的初步数据, 为了解目前食品接触材料中OPEs、OPAs及PBs污染状况和风险提供了技术手段和数据支撑。
QTRAPTM 6500+液相色谱-三重四极杆质谱仪(美国Sciex公司); PF120电热恒温鼓风干燥箱(英国Carbolite公司); Milli-Q超纯水机(美国Millipore公司); ACQUITY UPLC BEH C18色谱柱(100 mm×2.1 mm, 1.7 μm, 美国Waters公司)。
甲醇、乙酸铵(质谱级, 美国赛默飞世尔科技公司); 无水乙醇、冰乙酸(分析纯, 国药集团化学试剂有限公司); 实验用水为超纯水。
20件塑料膜袋、10件一次性外卖盒及20件纸制餐具为市售样品。
磷酸三甲酯(trimethyl phosphate, TMP, 纯度99%)、磷酸三乙酯(triethyl phosphate, TEP, 纯度99%)、磷酸三丙酯(tripropyl phosphate, TNPP, 纯度99%)、磷酸三异丙酯(triisopropyl phosphate, TIPP, 纯度93%)、磷酸三正丁酯(tributyl phosphate, TNBP, 纯度99%)、磷酸三(2-氯乙基)酯[tris(2-chloroethyl) phosphate, TCEP, 纯度98%]、磷酸三(2-氯丙基)酯[tris(1-chloro-2-propyl) phosphate, TCIPP, 纯度99%]、磷酸三苯酯(triphenyl phosphate, TPHP, 纯度99%)、磷酸三甲苯酯(tricresyl phosphate, TMPP, 纯度99%)、磷酸三(1,3-二氯-2-丙基)酯[tris(1,3-dichloro- 2-propyl) phosphate, TDCIPP, 纯度98%]、磷酸三(2-丁氧乙基)酯[tris(2-butoxyethyl) phosphate, TBOEP, 纯度96%]、磷酸三正戊酯(tri-n-amylphosphate, TNPTP, 纯度97%)、2-乙基己基二苯基磷酸酯(2-ethylhexyl diphenyl phosphate, EHDPP, 纯度92%)、磷酸三(2-乙基己基)酯[tris(2-ethylhexyl) phosphate, TEHP, 纯度99%]、磷酸三(2-异丙基苯基)酯[tris(2-isopropylphenyl) phosphate, TIPPP, 纯度99%]、三(2,4-二叔丁基)亚磷酸苯酯[tris(2,4-di-tert- butylphenyl) phosphite, AO168, 纯度99%]、双(2,4-二叔丁基苯酚)季戊四醇二亚磷酸酯[3,9-bis(2,4-di- tert-butylphenoxy)-2,4,8,10-tetraoxa-3,9-diphosphaspiro[5.5]undecane, AO626, 纯度96%](德国Dr. Ehrenstorfer公司); 三(2,4-二-叔丁基苯基)磷酸酯[tris(2,4-di-tert-butylphenyl) phosphate, AO168O, 纯度98%](加拿大Toronto Research Chemicals公司); 3,5-二叔丁基-4-羟基苄基二乙基磷酸酯(diethyl 3,5-di-tert-butyl-4-hydroxybenzyl phosphate, AO1222, 纯度99%)(坛墨质检标准物质中心); 亚磷酸苯二异辛酯(diisooctyl phenyl phosphite, DiOPPi, 纯度95%)(上海麦克林生化科技股份有限公司); 4-羟基苯甲酸甲酯(methylparaben, MEP, 纯度99%)、4-羟基苯甲酸丁酯(butylparaben, BUP, 纯度99%)、4-羟基苯甲酸乙酯(ethylparaben, ETP, 纯度99%)、4-羟基苯甲酸丙酯(propylparaben, PRP, 纯度99%)(北方伟业计量集团有限公司)。所有标准物质配制成为质量浓度100 μg/mL的标准储备液。
分别吸取标准储备液, 以甲醇稀释为OPEs、OPAs质量浓度1.00 mg/L、PBs质量浓度100.00 μg/L混合标准使用液; 分别吸取混合标准使用液1、5、10、20、50、100、200 μL至1 mL容量瓶中, 分别用空白浸泡液定容至1.00 mL。此标准系列中的OPEs、OPAs质量浓度为1、5、10、20、50、100和200 μg/L; PBs质量浓度为0.1、0.5、1.0、2.0、5.0、10.0和20.0 μg/L。
质谱检测采用电喷雾离子源(electron spray ionization, ESI), 正负离子切换模式, 负离子模式: -4500 V, 正离子模式: 5500 V; 离子源温度500 ℃, 雾化气压力60 psi, 辅助气压力40 psi, 气帘气压力30 psi; 采用多反应监测模式(multiple reaction monitoring, MRM)。各化合物的保留时间和定性定量离子对见表1
采用ACQUITY UPLC BEH C18色谱柱(100 mm×2.1 mm, 1.7 μm)为色谱分析柱, 流速0.35 mL/min, 柱温40 ℃, 以2 mmol乙酸铵水溶液为流动相A, 甲醇为流动相B, 按照体积比进行梯度洗脱: 0~1.0 min, 90% A; 1.0~6.5 min, 90%~10% A; 6.5~8.0 min, 10% A; 8.0~11.0 min, 10%~0% A; 11.0~17.0 min, 0% A; 17.0~17.1 min, 0%~90%A; 17.1~22.0 min, 90% A。进样量为2 μL。
按照GB 31604.1—2023《食品安全国家标准 食品接触材料及制品 迁移试验通则》及GB 5009.156—2016《食品安全国家标准 食品接触材料及制品迁移试验预处理方法通则》要求, 选择95%乙醇、4%乙酸、10%乙醇为浸泡液, 采用70 ℃、2 h为迁移条件, 在尽可能保持样品的原状态下, 对样品进行迁移实验, 取得浸泡液。其中: 塑料袋样品采用迁移测试池法, 塑料盒、纸杯、纸碗等样品采用直接灌装法, 包装纸、纸吸管、纸盒采用全浸没法。
取浸泡液样品1.0 mL, 以3000 r/min转速离心5 min, 转移上清液至进样瓶中待测。本实验所有玻璃器皿均经450 ℃灼烧4 h以去除本底, 迁移池经甲醇多次淋洗烘干后使用。同时做空白试验。
参考GB 5009.156—2016与范颖莹等[20]的方法, 对于有确定的使用情形的食品接触材料, 试验结果按照实际的试样接触面积与食品模拟物体积比(S/V)进行换算; 对于无明确使用情形的食品接触材料, 实验结果按照S/V为6 dm2/L进行换算。
本研究采用WPS Office 2017对数据进行整理和统计, 采用OriginPro 2021对数据进行绘图。本研究中每个实验重复测定3次, 实验结果以3次测定的平均值计算。
本研究以OPEs、OPAs质量浓度为20 μg/L, PBs质量浓度为2.0 μg/L的标准溶液为样品, 分别对ACQUITY UPLC BEH C18 (100 mm×2.1 mm, 1.7 μm)、ACQUITY HSS T3 (100 mm×2.1 mm, 1.8 μm)以及ACQUITY UPLC Phenyl (100 mm×2.1 mm, 1.7 μm) 3种色谱柱进行了筛选。本研究中24种待测组分的极性差别较大, 虽然部分组分在T3或者苯基柱上能呈现更好的峰型, 但综合所有待测物出峰情况看, 选择ACQUITY UPLC BEH C18作为后续实验中使用的色谱柱。本研究分别对甲醇及乙腈两种有机相, 2 mmol/L乙酸铵、水、0.1%甲酸3种水相作为流动相的效果进行了比较。在之前实验中发现, 乙酸铵浓度对于OPEs峰形影响较大[21], 故虽然在甲醇-水体系中, PBs峰高最大, 但综合OPEs结果, 后续实验继续采用甲醇-2 mmol乙酸铵流动相为实验流动相, 24种待测物质的选择离子流图如图1所示。
在实验过程中发现不同的微孔滤膜对于待测物有一定的吸附作用或者会对实验产生污染。本研究分别对疏水聚四氟乙烯、亲水聚四氟乙烯、再生纤维素、尼龙、混合纤维素酯5种常见的微孔滤膜进行了测试, 具体操作过程如下: 取空白浸泡液, 加入混合标准溶液, 配制成OPEs和OPAs质量浓度为10 µg/L, PBs质量浓度为1 µg/L的基质加标溶液。将上述基质加标溶液分别通过0.22 μm微孔滤膜过滤后进行仪器测定, 计算通过滤膜与未通过滤膜样品的峰面积比。实验结果可知, 在各浸泡液中, 采用滤膜对于TNPP、TCEP及ETP这3种化合物实验结果无影响(峰面积比在70%~120%之间), 对其他21种化合物测定结果会造成影响(见表2)。故本研究后续实验中, 采用迁移浸泡液离心取上清液测定。
本研究采用侯敏敏等[22]的方法对基质效应(matrix effects, MEs)进行评价, 具体方法如下: 采用未经迁移实验的浸泡液为空白浸泡液。分别取3种空白浸泡液, 加入混合标准溶液和混合内标溶液, 配制成OPEs和OPAs质量浓度为10 ng/mL, PBs质量浓度为1 ng/mL的基质加标溶液, 按照前处理方法进行测定。比较基质加标溶液和纯甲醇中相同浓度待测物质的峰面积计算基质效应。结果表明, 本研究中测定的24种待测物质中, 16种待测物质在3种浸泡液中的MEs范围在80%~120%之间; TMPP、TEHP、EHDPP、TIPPP、TNPTP在10%乙醇和4%乙酸中表现了基质抑制(MEs范围47.8%~62.0%); AO168、AO168O及AO626在4%乙酸中表现了基质抑制(MEs范围32.0%~36.4%)。本研究采用空白浸泡液配制基质曲线对样品进行定量, 满足分析需求。
按照优化后的条件, 将标准溶液按照从低到高的顺序依次进样, 以目标物质与内标的浓度比为横坐标(X, µg/L), 峰面积比为纵坐标(Y)进行线性回归计算。结果表明, 本研究15种OPEs、5种OPAs在1~200 µg/L范围、4种PBs在0.1~20.0 µg/L范围内在3种浸泡液中均具有良好的线性关系, 线性相关系数大于0.99。分别向1 mL空白浸泡液中加入10 µg/L水平OPEs及OPAs、1 µg/L的PBs, 按照前处理方法进行测定, 本研究方法的检出限(limit of detection, LOD)按照3倍信噪比计算, 定量限(limit of quantitation, LOQ)按照10倍信噪比计算。如表3所示, 3种浸泡液中24种待测组分的LODs范围为0.01~0.58 µg/L, LOQs范围为0.03~2.00 µg/L, 能够满足检测要求。
本研究采用空白浸泡液作为本底样品, 分别加入OPEs、OPAs为10、50和100 µg/L (PBs为1、5和10 µg/L)水平的标准溶液, 每个浓度进行6次重复实验, 计算测定的回收率及精密度。本研究中24种待测物质的回收率范围为72.2%~126.4%, 相对标准偏差(relative standard deviations, RSDs)范围为0.5%~10.9%, 精密度及准确度可以满足检测的要求(见表4)。
本研究对20件塑料膜袋、10件一次性外卖盒及20件纸制餐具的OPEs、OPAs与PBs进行了迁移实验及仪器测定, 并计算其迁移量。
OPEs与OPAs中, 有11种组分检出, 检出率在50%以上的目标物质有4种, 分别是AO168O(检出率96.0%)、AO168(检出率80.0%)、AO626(检出率60.0%)、TPHP(检出率58.0%)。在所有待测组分中, 在迁移液中含量最高的组分是AO168及AO168O, 其中AO168质量浓度范围为<LOD~950 μg/L, AO168O质量浓度范围为<LOD~1243 μg/L。计算污染物总量, ΣOPEs范围为<LOD~19.1 μg/L(平均值2.60 μg/L), ΣOPAs范围为<LOD~1248 μg/L(平均值306 μg/L), 低于ZHOU等[2]及BALASCH等[18]研究。按照GB 9685—2016《食品安全国家标准 食品接触材料及制品用添加剂使用标准》要求, AO168可以作为食品接触材料添加剂使用, 对特定迁移量没有进行规定; 但AO168O不是食品接触材料添加剂。根据ZHOU等[23]的研究, AO168O的污染主要来自AO168的广泛使用, 而目前针对食品接触材料中OPAs的监测研究还非常少, 需要特别关注。
本研究也将迁移量结果与饮食、室内灰尘、医用用品中OPEs、OPAs含量进行了比较。比较发现, 本研究中OPEs迁移量结果低于食品及室内灰尘中的含量[24-26]。而本研究OPAs迁移量结果高于ZHOU等[23]对于外卖食品中的OPAs含量(ΣOPAs范围为1.35~360 μg/kg, 平均值15.6 μg/kg), 与乳制品中的OPAs含量相近(ΣOPAs范围为2.48~3951 μg/kg, 平均值107 μg/kg)[6]; 远远低于对医用用品(ΣOPAs范围为20000~575000 ng/g, 平均值175000 ng/g)[27]及室内灰尘含量(ΣOPAs范围为220~30731 ng/g)[28]
在4种PBs中, MEP和ETP检出率和浓度相对较高, 为MEP(检出率36.0%, 质量浓度范围<LOD~0.268 μg/L); ETP(检出率30.0%, 质量浓度范围<LOD~0.241 μg/L)。ΣPBs范围为<LOD~0.501 μg/L, 平均值0.066 μg/L, 其中, MEP和ETP占ΣPBs的比例>85.5%。其中, 按照GB 9685—2016要求, MEP及PRP可以作为食品接触材料添加剂使用, 对特定迁移量没有进行规定。而本研究结果中MEP及ETP迁移量也低于GB 2760—2024《食品安全国家标准 食品添加剂使用标准》中二者的最大使用量。
将本研究结果与个人护理产品、药品和食品中PBs含量进行比较得出, 目前食品包装材料的PBs迁移量较低[29-32]。但按照BIAN等[33]的研究, 食品包装材料中释放的PBs含量的量会随着与食品接触时间和温度的增加而增加, 从而增加PBs的暴露风险。因此, 针对食品接触材料实际情况的监测还是很有必要的。
本研究通过优化色谱和质谱条件, 采用基质匹配标准曲线定量, 建立了一种液相色谱-串联质谱法同时测定食品接触材料中OPEs、OPAs和PBs迁移量的测定方法。结果表明, 该方法操作简单, 灵敏度高, 并具有良好的精密度和准确度, 可应用于大量食品接触材料样品OPEs、OPAs和PBs的迁移量测定, 可作为后续进一步开展食品接触材料中OPEs、OPAs和PBs的监测和评估的检测手段。
本研究通过对塑料膜袋、一次性外卖盒及纸制餐具的检测获得了食品接触材料中OPEs、OPAs和PBs污染的初步数据。但考虑到本次研究涉及的食品接触材料样品的种类、数量、采样来源等都有局限性, 未能全面反映食品接触材料的污染情况, 还需进一步扩大监测范围。
  • 北京市东城区优秀人才培养资助项目(2024-dchrcprzz-40)
  • 北京市东城区卫生科技计划项目(东卫健研[2024]-19)
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2025年第16卷第14期
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doi: 10.19812/j.cnki.jfsq11-5956/ts.20250418005
  • 接收时间:2025-04-18
  • 首发时间:2026-01-07
  • 出版时间:2025-07-25
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  • 收稿日期:2025-04-18
基金
北京市东城区优秀人才培养资助项目(2024-dchrcprzz-40)
北京市东城区卫生科技计划项目(东卫健研[2024]-19)
作者信息
    1 北京市东城区疾病预防控制中心/公共卫生应急管理创新中心, 北京 100050
    2 北京市疾病预防控制中心, 北京 100013

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*刘伟(1983—), 男, 硕士, 副主任技师, 主要研究方向为食品安全检测。E-mail:
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2种不同金属材料的力学参数

Family
属数
Number of
genus
种数
Number of
species
占总种数比例
Percentage of
total species (%)

Genus
种数
Number of
species
占总种数比例
Percentage of total
species (%)
鹅膏菌科Amanitaceae 2 11 5.26 鹅膏菌属 Amanita 10 4.78
小菇科 Mycenaceae 2 12 5.74 丝盖伞属 Inocybe 5 2.39
多孔菌科 Polyporaceae 8 14 6.70 蜡蘑属 Laccaria 5 2.39
红菇科 Russulaceae 3 23 11.00 小皮伞属 Marasmius 6 2.87
小菇属 Mycena 11 5.26
光柄菇属 Pluteus 5 2.39
红菇属 Russula 17 8.13
栓菌属 Trametes 5 2.39
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