Contamination status, emission sources, and human health risk of brominated flame retardants in urban indoor dust from Hanoi, Vietnam: the replacement of legacy polybrominated diphenyl ether mixtures by alternative formulations

Author(s):  
Minh Tue Thi Hoang ◽  
Hoang Quoc Anh ◽  
Kiwao Kadokami ◽  
Hanh Thi Duong ◽  
Ha Mai Hoang ◽  
...  
2015 ◽  
Vol 74 ◽  
pp. 170-180 ◽  
Author(s):  
Jan L. Lyche ◽  
Carola Rosseland ◽  
Gunnar Berge ◽  
Anuschka Polder

2019 ◽  
Vol 653 ◽  
pp. 423-430 ◽  
Author(s):  
Zhiguo Cao ◽  
Mengmeng Wang ◽  
Qiaoying Chen ◽  
Chunyou Zhu ◽  
Janye Jie ◽  
...  

2016 ◽  
Vol 31 (4) ◽  
Author(s):  
Sock Yin Tan ◽  
Sarva Mangala Praveena ◽  
Emilia Zainal Abidin ◽  
Manraj Singh Cheema

AbstractIndoor dust acts as a media for heavy metal deposition. Past studies have shown that heavy metal concentration in indoor dust is affected by local human activities and atmospheric transport can have harmful effects on human health. Additionally, children are more sensitive to heavy metals due to their hand-to-mouth behaviour and rapid body development. However, limited information on health risks were found in past dust studies as these studies aimed to identify heavy metal concentrations and sources of indoor dust. The objective of this review is to discuss heavy metal concentration and sources influencing its concentration in indoor dust. Accordingly, high lead (Pb) concentration (639.10 μg/g) has been reported in heavy traffic areas. In addition, this review paper aims to estimate the health risk to children from heavy metals in indoor dust via multiple exposure pathways using the health-risk assessment (HRA). Urban areas and industrial sites have revealed high heavy metal concentration in comparison to rural areas. Hazard index (HI) values found in arsenic (As), chromium (Cr) and Pb were 21.30, 1.10 and 2.40, respectively, indicate that non-carcinogenic elements are found in children. Furthermore, most of the past studies have found that carcinogenic risks for As, cadmium (Cd), Cr and Pb were below the acceptable total lifetime cancer risk (TLCR) range (1×10


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