题名

印刷業勞工鄰苯二甲酸酯類暴露評估研究

并列篇名

Exposure Assessment of Phthalate Esters for Workers in Printing Industry

DOI

10.7005/JOSH.201209.0326

作者

劉香君(Hsiang-Chun Liu);方澤沛(Jer-Pei Fong);汪禧年(Shi-Nian Uang);李聯雄(Lien-Hsiung Li);陳秋蓉(Chiou-Jong Chen);李俊璋(Ching-Chang Lee)

关键词

鄰苯二甲酸酯 ; 印刷業勞工 ; 尿液代謝物 ; 空氣暴露 ; 皮膚暴露 ; Phthalate esters ; Printing industry workers ; Airborne exposure ; Urinary metabolites ; Skin exposure

期刊名称

勞工安全衛生研究季刊

卷期/出版年月

20卷3期(2012 / 09 / 01)

页次

326 - 341

内容语文

繁體中文

中文摘要

PAEs were widely added in printing ink as dispersing agents to increase quality of printing products. The aim of this study is to assess the exposure profiles of PAEs and the contributions of different exposure routes to total exposure for workers in printing industries. 31 male and 26 female workers in two printing plants were recruited as study subjects. Personal exposure to airborne PAEs, incuding di-(2-ethyl hexyl) phthalate (DEHP), di-n-butyl phthalate (DBP), butyl benzyl phthalate(BBzP) and diethyl phthalate (DEP), and urinary PAEs metabolites, including mono-2-ethylhexyl phthalate (MEHP), mono-(2-ethyl-5-hydroxyhexyl) phthalate (MEHHP), mono-(2-ethyl-5-oxohexyl) phthalate (MEOHP), mono-(2-ethyl-5-carboxypentyl) phthalate (MECPP) and mono-nbutyl phthalate (MBP), were measured. Occupational exposure information and time activity pattern for all selected workers were collected by using a questionnaire-based investigation. For the male workers, the airborne DEHP concentration (0.5 μg/m^3 vs 0.3 μg/m^3, p<0.05) and urinary MBP level (94.8 μg/g-Cre vs. 67.6 μg/g-Cre, p<0.05) of high-exposure workers (operator and packing) were significantly higher than those of low-exposure workers (administration and patrolling staffs). The post- and pre-shift urinary levels of PAEs metabolites of high-exposure male workers show significant differences: MBP( 94.8μg/g-Cre vs. 66.6μg/g-Cre, p<0.05), MEHP (14.0 μg/g-Cre vs. 5.9 μg/g-Cre, p<0.05), MEOHP (39.0 μg/g-Cre vs. 15.9 μg/g-Cre, p<0.05), MEHHP (85.4 μg/g-Cre vs. 32.7 μg/g-Cre, p<0.05), and MECPP (69.7 μg/g-Cre vs. 27.9 μg/g-Cre, p<0.05). Furthermore, the dermal exposure of PAEs for the workers was estimated based on a daily intake assessment model. The results show that individual contributions of skin absorption of DBP and DEHP (DIskin) in high-concentration group are 55% and 51% to the total exposure of PAEs, respectively. It means the dermal exposure may be an important potential exposure route for printing workers. We concluded the airborne PAEs exposure was minor, but dermal PAEs exposure played an important route for the printing workers. Therefore, we suggest that the biological exposure index of PAEs (urinary PAEs metabolites) is more representative of the PAEs exposure profile of workers.

英文摘要

PAEs were widely added in printing ink as dispersing agents to increase quality of printing products. The aim of this study is to assess the exposure profiles of PAEs and the contributions of different exposure routes to total exposure for workers in printing industries. 31 male and 26 female workers in two printing plants were recruited as study subjects. Personal exposure to airborne PAEs, incuding di-(2-ethyl hexyl) phthalate (DEHP), di-n-butyl phthalate (DBP), butyl benzyl phthalate(BBzP) and diethyl phthalate (DEP), and urinary PAEs metabolites, including mono-2-ethylhexyl phthalate (MEHP), mono-(2-ethyl-5-hydroxyhexyl) phthalate (MEHHP), mono-(2-ethyl-5-oxohexyl) phthalate (MEOHP), mono-(2-ethyl-5-carboxypentyl) phthalate (MECPP) and mono-nbutyl phthalate (MBP), were measured. Occupational exposure information and time activity pattern for all selected workers were collected by using a questionnaire-based investigation. For the male workers, the airborne DEHP concentration (0.5 μg/m^3 vs 0.3 μg/m^3, p<0.05) and urinary MBP level (94.8 μg/g-Cre vs. 67.6 μg/g-Cre, p<0.05) of high-exposure workers (operator and packing) were significantly higher than those of low-exposure workers (administration and patrolling staffs). The post- and pre-shift urinary levels of PAEs metabolites of high-exposure male workers show significant differences: MBP( 94.8μg/g-Cre vs. 66.6μg/g-Cre, p<0.05), MEHP (14.0 μg/g-Cre vs. 5.9 μg/g-Cre, p<0.05), MEOHP (39.0 μg/g-Cre vs. 15.9 μg/g-Cre, p<0.05), MEHHP (85.4 μg/g-Cre vs. 32.7 μg/g-Cre, p<0.05), and MECPP (69.7 μg/g-Cre vs. 27.9 μg/g-Cre, p<0.05). Furthermore, the dermal exposure of PAEs for the workers was estimated based on a daily intake assessment model. The results show that individual contributions of skin absorption of DBP and DEHP (DIskin) in high-concentration group are 55% and 51% to the total exposure of PAEs, respectively. It means the dermal exposure may be an important potential exposure route for printing workers. We concluded the airborne PAEs exposure was minor, but dermal PAEs exposure played an important route for the printing workers. Therefore, we suggest that the biological exposure index of PAEs (urinary PAEs metabolites) is more representative of the PAEs exposure profile of workers.

主题分类 醫藥衛生 > 預防保健與衛生學
醫藥衛生 > 社會醫學
社會科學 > 社會學
参考文献
  1. Agency for Toxic Substance and Disease Registry (US). Toxicological profile for diethyl phthalate (DEP). Atlanta: ATSDR; 1995.
  2. (2005)。,行政院勞工委員會勞工安全衛生研究所。
  3. Agency for Toxic Substance and Disease Registry (US). Toxicological profile for dinbutyl phthalate (DBP). Atlanta: ATSDR; 2001.
  4. U.S. Environmental Protection Agency Dibutyl phthalate (CASRN 84-74-2): referencedose for chronic oral exposure (RfD); 1990. http://www.epa.gov/iris/subst/0038.htm (accessed Decmber 21, 2010)
  5. (2008)。,行政院勞工委員會勞工安全衛生研究所。
  6. U.S. Environmental Protection Agency. Di(2-ethylhexyl) phthalate (DEHP) (CASRN 117-81-7): referencedose for chronic oral exposure (RfD); 1991. http://www.epa.gov/iris/subst/0014.htm (accessed Decmber 21,2010)
  7. (2007)。,行政院勞工委員會勞工安全衛生研究所。
  8. Occupational Safety and Health Administration (US). Method 104. In: OHSA Sampling and Analytical Methods. Utah: OSHA; 1994..
  9. Agency for Toxic Substance and Disease Registry (US). Toxicological profile for di-(2-ethylhexyl) phthalate (DEHP). Atlanta: ATSDR; 2002..
  10. Occupational Safety and Health Administration (US). Occupational Safety and Health Standards, Toxic and Hazardous Substances. Code of Federal Regulations. 29 CFR 1910. 1000. 1998.
  11. Afshari, A.,Gunnarsen, L.,Clausen, P.A.,Hansen, V.(2004).Emission of phthalates from PVC and other material.Indoor Air,14,120-8.
  12. Barr, D.B.,Silva, M.J.,Kato, K.,Reidy, J.A.,Malek, N.A.,Hurtz, D.(2003).Assessing human exposure to phthalates using monoesters and their oxidized metabolites as biomarkers.Environmental Health Perpectives,111,1148-51.
  13. Becker, K.,Seiwert, M.,Angerer, J.,Heger, W.,Koch, H.M.,Nagorka, R.(2004).DEHP metabolites in urine of children and DEHP in house dust.International Journal of Hygiene and Environmental Health,207,409-17.
  14. Carpenter, C.P.,Weil, C.S.,Smyth, H.F., Jr.(1953).Chronic oral toxicity of di-(2-ethylhexyl) phthalate of rats, guinea pigs, and dogs.American Medical Association Archives of Industrial Hygiene and Occupational Medicine,8,219-26.
  15. Duty, S.M.,Ackerman, R.M.,Calafat, A.M.,Hauser, R.(2005).Personal care product use predicts urinary concentrations of some phthalate monoesters.Environmental Health Perspective,113,1530-5.
  16. EFSA=European Food Safety Authority(2005).Opinion of the scientific panel on food additives, flavourings, processing aids and materials in contact with food (AFC) on a request from the commission related to Bis(2-ethylhexyl) phthalate (DEHP) for use in food contact materials.European Food Safety Authority Journal,243,1-20.
  17. EFSA=European Food Safety Authority(2005).Opinion of the scientific panel on food additives, flavourings, processing aids and materials in contact with food (AFC) on a request from the commission related to dibutylphthalate (DBP) for use in food contact materials.EFSA Journal,242,1-17.
  18. European Chemical Bureau (Italy)(2003).European Union Risk Assessment Report for 1,2-benzenedicarboxylic acid, di-C8-10-branched alkyl esters, C9-rich and di-"isononyl" phthalate (DINP) (Final Report 2003)European Union Risk Assessment Report for 1,2-benzenedicarboxylic acid, di-C8-10-branched alkyl esters, C9-rich and di-"isononyl" phthalate (DINP) (Final Report 2003),Ispra:ECB.
  19. European Chemical Bureau (Italy)(2008).European Union Risk Assessment Report for Bis(2-ethylhexyl) phthalate (Final Report 2008)European Union Risk Assessment Report for Bis(2-ethylhexyl) phthalate (Final Report 2008),Ispra:ECB.
  20. Foster, P.M.D.,Cook, M.W.,Thomas, L.V.,Walters, D.G.,Gangolli, S.D.(1983).Differences in urinary metabolic profile from di-n-butyl phthalte-treated rats and hamsters. Apossible explanation for species differences in susceptibility to testicular atrophy.Drug Metabolism and Disposition,11,59-61.
  21. Frederiksen, H.,Skakkebaek, N.E.,Andersson, A.M.(2007).Metabolism of phthalates in humans.Molecular Nutrition and Food Research 2007,51,899-911.
  22. Fromme, H.,Gruber, L.,Schlummer, M.,Wolz, G.,Böhmer, S.,Angerer, J.(2007).Intake of phthalates and di(2-ethylhexyl)adipate: results of the Integrated Exposure Assessment Survey based onduplicate diet samples and biomonitoring data.Environment International,33,1012-20.
  23. Fujii, M.,Shinohara, N.,Lim, A.,Otake, T.,Kumagai, K.,Yanagisawa, Y.(2003).A study on emission of phthalate esters from plastic materials using a passive flux sampler.Atmospheric Environment,37,5495-504.
  24. Hauser, R.,Calafat, A.M.(2005).Phthalates and human health.Occupational and Environmental Medicine,62,806-18.
  25. Hauser, R.,Duty, S.,Godfrey-Bailey, L.,Calafat, A.M.(2004).Medications as a source of human exposure to phthalates.Environmental Health Perspective,112,751-3.
  26. Hauser, R.,Meeker, J.D.,Singh, N.P.,Silva, M.J.,Ryan, L.,Duty, S.(2007).DNA damage in human sperm is related to urinary levels of phthalate monoester and oxidative metabolites.Human Reproduction,22,688-95.
  27. Hernández-Díaz, S.,Mitchell, A.A.,Kelley, K.E.,Calafat, A.M.,Hauser, R.(2009).Medications as a potential source of exposure to phthalates in the US population.Environmental Health Perspectives,117,185-9.
  28. Kavlock, R.,Boekelheide, K.,Chapin, R.,Cunningham, M.,Faustman, E.,Foster, P.(2002).NTP Center for the Evaluation of Risks to Human Reproduction: phthalates expert panel report on the reproductive and developmental toxicity of di-isononyl phthalate.Reproductive Toxicology,16,679-708.
  29. Koch, H.M.,Bolt, H.M.,Preuss, R.,Angerer, J.(2005).New metabolites of di(2-ethylhexyl) phthalate (DEHP) in human urine and serum after single oral doses of deuterium-labelled DEHP.Archives of Toxicology,79,367-76.
  30. Koch, H.M.,Wittassek, M.,Angerer, J.(2006).Influence of alimentary abstinence on body burden to phthalates (Poster).International Conference on environmental epidemiology and exposure (ISEE/ISEA)
  31. Kohn, M.C.,Parham, F.,Masten, S.A.,Portier, C.J.,Shelby, M.D.,Brock, J.W.(2000).Human exposure estimates for phthalates.Environmental Health Perpectives,108,A440-2.
  32. Kwapniewski, R.,Kozaczka, S.,Hauser, R.,Silva, M.J.,Calafat, A.M.,Duty, S.M.(2008).Occupational exposure to dibutyl phthalate among manicurists.Journal of Occupational and Environmental Medicine,50,705-11.
  33. Lovekamp-Swan, T.,Davis, B.J.(2003).Mechanisms of Phthalate Ester Toxicity in the Female Reproductive System.Environmental Health Perspectives,111,39-145.
  34. Pan, G.,Hanaok, T.,Yoshimura, M.,Zhang, S.,Wang, P.,Tsukino, H.(2006).Decreased serum free testosterone in workers exposed to high levels of di-n-butyl phthalate (DBP) and di2-ethylhexyl phthalate (DEHP): a crosssectional study in China.Environmental Health Perspect,114,1643-8.
  35. Sampson, J.,Korte, D.(2011).DEHP-plasticised PVC: relevance to blood services.Transfusion Medicine,21,73-83.
  36. Silva, M.J.,Slakman, A.R.,Reidy, J.A.,Preau, J.J.L.,Herbert, A.R.,Samandar, E.(2004).Analysis of human urine for fifteen phthalate metabolites using automated solid-phase extraction.Journal of Chromatography B,805,161-7.
  37. Wittassek, M.,Heger, W.,Koch, H.M.,Becker, K.,Angerer, J.,Kolossa-Gehring, M.(2007).Daily intake of di(2-ethylhexyl) phthalate (DEHP) by German children - A comparison of two estimation models based on urinary DEHP metabolite levels.International Journal of Hygiene and Environmental Health,210,35-42.
  38. 吳婉玲(2002)。碩士論文(碩士論文)。中國醫藥學院/環境醫學研究所。
  39. 詹秀慧(2005)。碩士論文(碩士論文)。國立成功大學環境醫學研究所。