Exposure Assessment and Health Risk of Polybrominated Diphenyl Ether (PBDE) Flame Retardants in Indoor Environments of Children’s Facilities in Korea

This study assessed the health risks of childhood exposure to PBDEs via different possible pathways in children’s facilities and indoor playgrounds. When PBDE contamination was measured, it was determined through multiple routes, including inhalation of indoor dust, dermal contact with product surfa...

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Published inAsian journal of atmospheric environment (Online) Vol. 5; no. 4; pp. 247 - 262
Main Authors Kim, Ho-Hyun, Yang, Ji-Yeon, Jang, Yun-Suk, Lee, Yong-Jin, Lee, Chung-Soo, Shin, Dong-Chun, Lim, Young-Wook
Format Journal Article
LanguageEnglish
Published Singapore Springer Nature Singapore 01.12.2011
Springer
한국대기환경학회
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Online AccessGet full text
ISSN2287-1160
1976-6912
2287-1160
DOI10.5572/ajae.2011.5.4.247

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Abstract This study assessed the health risks of childhood exposure to PBDEs via different possible pathways in children’s facilities and indoor playgrounds. When PBDE contamination was measured, it was determined through multiple routes, including inhalation of indoor dust, dermal contact with product surfaces and children’s hands, and incidental dust ingestion. Samples were collected from various children’s facilities (playrooms, daycare centers, kindergartens, and indoor playgrounds) during summer (Jul–Sep, 2007) and winter (Jan–Feb, 2008). The hazard index (HI) was estimated for non-carcinogens, and PBDEs, such as TeBDE, PeBDE, HxBDE, and DeBDE, were examined. The sensitivity to the compounds did not exceed 1.0 (HI) for any of the subjects in any facility. However, current data about toxicity does not reflect effects that were fully sensitive in children, so there is uncertainty in the dose-response data. The contribution rates of PBDEs were 71.4 to 96.1% and 3.7 to 28.2% for intake and inhalation exposure, respectively, indicating that intake of floor dust and inhalation are the primary routes.
AbstractList This study assessed the health risks of childhood exposure to PBDEs via different possible pathways in children’s facilities and indoor playgrounds. When PBDE contamination was measured, it was determined through multiple routes, including inhalation of indoor dust, dermal contact with product surfaces and children’s hands, and incidental dust ingestion. Samples were collected from various children’s facilities (playrooms, daycare centers, kindergartens, and indoor playgrounds) during summer (Jul–Sep, 2007) and winter (Jan–Feb, 2008). The hazard index (HI) was estimated for non-carcinogens, and PBDEs, such as TeBDE, PeBDE, HxBDE, and DeBDE, were examined. The sensitivity to the compounds did not exceed 1.0 (HI) for any of the subjects in any facility. However, current data about toxicity does not reflect effects that were fully sensitive in children, so there is uncertainty in the dose-response data. The contribution rates of PBDEs were 71.4 to 96.1% and 3.7 to 28.2% for intake and inhalation exposure, respectively, indicating that intake of floor dust and inhalation are the primary routes.
This study assessed the health risks of childhood exposure to PBDEs via different possible pathways in children’s facilities and indoor playgrounds. When PBDE contamination was measured, it was determined through multiple routes, including inhalation of indoor dust, dermal contact with product surfaces and children’s hands, and incidental dust ingestion. Samples were collected from various children’s facilities (playrooms, daycare centers, kindergartens, and indoor playgrounds) during summer (Jul-Sep, 2007)and winter (Jan-Feb, 2008). The hazard index (HI)was estimated for non-carcinogens, and PBDEs, such as TeBDE, PeBDE, HxBDE, and DeBDE, were examined. The sensitivity to the compounds did not exceed 1.0 (HI) for any of the subjects in any facility. However,current data about toxicity does not reflect effects that were fully sensitive in children, so there is uncertainty in the dose-response data. The contribution rates of PBDEs were 71.4 to 96.1% and 3.7 to 28.2% for intake and inhalation exposure, respectively,indicating that intake of floor dust and inhalation are the primary routes. KCI Citation Count: 1
Author Kim, Ho-Hyun
Lee, Chung-Soo
Yang, Ji-Yeon
Jang, Yun-Suk
Lee, Yong-Jin
Lim, Young-Wook
Shin, Dong-Chun
Author_xml – sequence: 1
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  surname: Lim
  fullname: Lim, Young-Wook
  email: envlim@yuhs.ac
  organization: Institute for Environmental Research, Yonsei University College of Medicine
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CitedBy_id crossref_primary_10_1016_j_scitotenv_2013_09_013
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crossref_primary_10_1016_j_envpol_2014_08_030
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Snippet This study assessed the health risks of childhood exposure to PBDEs via different possible pathways in children’s facilities and indoor playgrounds. When PBDE...
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SubjectTerms children’s facilities
multi-route exposure
pbdes
risk assessment
대기과학
Title Exposure Assessment and Health Risk of Polybrominated Diphenyl Ether (PBDE) Flame Retardants in Indoor Environments of Children’s Facilities in Korea
URI https://link.springer.com/article/10.5572/ajae.2011.5.4.247
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