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Investigation of Labeling Status and Toxicity Data of Environmentally Hazardous Substances in Children's Products

어린이용품의 환경유해인자 표시 현황과 독성자료에 대한 연구

  • Lee, Jiyun (Department of Environmental Health, Graduate School at Yongin University) ;
  • Kim, Jihyo (Ecomom Korea) ;
  • Moon, Myunghee (Ecomom Korea) ;
  • Lee, Kiyoung (Graduate School of Public Health, Seoul National University) ;
  • Ji, Kyunghee (Department of Environmental Health, Graduate School at Yongin University)
  • 이지윤 (용인대학교 일반대학원 환경보건학과) ;
  • 김지효 ((사)에코맘코리아) ;
  • 문명희 ((사)에코맘코리아) ;
  • 이기영 (서울대학교 보건대학원) ;
  • 지경희 (용인대학교 일반대학원 환경보건학과)
  • Received : 2019.06.25
  • Accepted : 2019.07.23
  • Published : 2019.10.31

Abstract

Objectives: Children are exposed to various environmental pollutants through contact with children's products. We investigated the KC mark, certification number, and contained substances labeled on children's products through market research and collected the toxicological data on these substances. Methods: The environmentally hazardous substances labeled on children's products (n=6576), including toys (n=2812), personal care products (n=2212), stationary/books (n=1333), and playground equipment (n=219) were examined. For the components that could be identified by CAS number, toxicological data on oral, inhalation, and dermal routes, cancer slope factor, and reference dose were collected. Results: Among the investigated products, KC marks or certification numbers were found for 4557 products (69.3%). Except for cosmetics and cleansers, the material information was labeled on most of the products. The frequency of labeling substance information in toys and stationary/books was low since this information could be omitted if KC certification was obtained. In the target products, 617 substances were identified by CAS number, and polypropylene, acrylonitrile butadiene styrene, and polyester were the most frequently displayed. Chronic toxicity data was found for only 32.4% of individual components, and information on toxicity through the dermal route was also highly limited. Conclusion: Our study suggested that labeling guidelines should be required to identify the environmentally hazardous substances contained in children's products. In addition, the toxicological data on many ingredients in children's products were insufficient. The data gap for toxicity data should be filled for future risk assessment.

Keywords

References

  1. United States Environmental Protection Agency. Child-Specific Exposure Factors Handbook. EPA/600/R-06/096F. 2008.
  2. Ginsberg G, Hattis D, Sonawame B, Russ A, Banati P, Kozlak M, et al. Evaluation of child/adult pharmacokinetic differences from a database derived from the therapeutic drug literature. Toxicol Sci. 2002; 66: 185-200. https://doi.org/10.1093/toxsci/66.2.185
  3. Lee CW, Chang JY, Song KB, Lee SY, Yu M, Park KH et al. Risk assessment and safety management of children's products. Korean Soc Environ Toxicol. 2012; 5: 153-154.
  4. Kim HH, Choi IS, Nam YH, Lee JH, Yoo SE, Park CH et al. Selection of new high-maintenance children's activity spaces based on children's life patterns. J Environ Health Sci. 2019; 45(2): 164-172.
  5. National Institute of Environmental Research. Exposure Status and Risk Assessment of Hazardous Substances in Children's Products (III)-Focused on Dermal Exposed Products. 2009.
  6. National Institute of Environmental Research. Exposure Status and Risk Assessment of Hazardous Substances in Children's Products (IV)-Focused on Inhalation Exposed Products. 2010.
  7. National Institute of Environmental Research. Risk Assessment of Environmental Hazardous Substances for Children's Products (I). 2011.
  8. National Institute of Environmental Research. Risk Assessment of Environmental Hazardous Substances for Children's Products (II). 2012.
  9. National Institute of Environmental Research. Risk Assessment of Environmental Hazardous Substances for Children's Products (III). 2013.
  10. Ministry of Environment. Survey on the Status of Hazardous Substances in Children's Products. 2015.
  11. Park JY, Lim M, Lee K. Estimation of exposure to boron from children's slime use in Korea. J Environ Health Sci. 2018; 44(6): 556-562.
  12. Ficheux AS, Bernard A, Chevillotte G, Dornic N, Roudot AC. Probabilistic assessment of exposure to hair cosmetic products by the French population. Food Chem Toxicol. 2016; 92: 205-216. https://doi.org/10.1016/j.fct.2016.04.009
  13. Gomez-Berrada MP, Gautier F, Parent-Massin D, Ferret PJ. Retrospective exposure data for baby and children care products: an analysis of 48 clinical studies. Food Chem Toxicol. 2013; 57: 185-194. https://doi.org/10.1016/j.fct.2013.03.030
  14. Lee E, Yun J, Ha J, Park BC, Park GH, Kim HR, et al. Assessment of exposure for baby cosmetic care products in a Korean population. Food Chem Toxicol. 2017; 106: 107-113. https://doi.org/10.1016/j.fct.2017.05.039
  15. Kim J, Seo JK, Kim T, Park GH. Survey of exposure factors for risk assessment of hazardous materials in child-specific products. J Environ Health Sci. 2014; 40: 17-26.
  16. Kim S, Lee S, Shin C, Lee J, Kim S, Lee A, et al. Urinary parabens and triclosan concentrations and associated exposure characteristics in a Korean population-a comparison between night-time and firstmorning urine. Int J Hyg Environ Health. 2018; 221: 632-641. https://doi.org/10.1016/j.ijheh.2018.03.009
  17. Koniecki D, Wang R, Moody RP, Zhu J. Phthalates in cosmetic and personal care products: concentrations and possible dermal exposure. Environ Res. 2011; 111: 329-336. https://doi.org/10.1016/j.envres.2011.01.013
  18. Larsson K, Bjorklund KL, Palm B, Wennberg M, Kaj L, Lindh CH, et al. Exposure determinants of phthalates, parabens, bisphenol A and triclosan in Swedish mothers and their children. Environ Int. 2014; 73: 323-333. https://doi.org/10.1016/j.envint.2014.08.014
  19. Philippat C, Bennett D, Calafat AM, Picciotto IH. Exposure to select phthalates and phenols through use of personal care products among Caifornian adults and their children. Environ Res. 2015; 140: 369-376. https://doi.org/10.1016/j.envres.2015.04.009
  20. Gosens I, Delmaar CJE, ter Burg W, de Heer C, Schuur AG. Aggregate exposure approaches for parabens in personal care products: a case assessment for children between 0 and 3 years old. J Expo Sci Environ Epidemiol. 2014; 24: 208-214. https://doi.org/10.1038/jes.2013.33
  21. Choi IS, Choi SC. Contents and migration of heavy metals and phthalates in children's products. J Kor Soc Environ Eng. 2014; 36: 127-138. https://doi.org/10.4491/KSEE.2014.36.2.127
  22. Aboel Dahab A, Elhag DE, Ahmed AB, Al-Obaid HA. Determination of elemental toxicity migration limits, bioaccessibility and risk assessment of essential childcare products. Environ Sci Pollut Res Int. 2016; 23: 3406-3413. https://doi.org/10.1007/s11356-015-5594-0
  23. Pomatto V, Cottone E, Cocci P, Mozzicafreddo M, Mosconi G, Nelson ER, et al. Plasticizers used in food-contact materials affect adipogenesis in 3T3-L1 cells. J Steroid Biochem Mol Biol. 2018; 178: 322-332. https://doi.org/10.1016/j.jsbmb.2018.01.014
  24. Benjamin S, Masai E, Kamimura N, Takahashi K, Anderson RC, Faisal PA. Phthalates impact human health: Epidemiological evidences and plausible mechanism of action. J Hazard Mater. 2017; 340: 360-383. https://doi.org/10.1016/j.jhazmat.2017.06.036
  25. Negev M, Berman T, Reicher S, Balan S, Soehl A, Goulden S, et al. Regulation of chemicals in children's products: How U.S. and EU regulation impacts small markets. Sci Total Environ. 2018; 616-617: 462-471. https://doi.org/10.1016/j.scitotenv.2017.10.198