RESUMO
Per and polyfluoroalkyl substances (PFAS) are toxicologically concerning because of their potential to bioaccumulate and their persistence in the environment and the human body. We determined PFAS levels in cosmetic and personal care products and assessed their health risks. We investigated the trends in concentrations and types of PFAS contaminants in cosmetic and personal care products before and after perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA) were added to the list of persistent organic pollutants. The total PFAS concentration ranged from 1.98 to 706.75 ng g-1. The hazard quotients (HQs) for PFOA, PFOS and perfluorobutanesulfonic acid (PFBS) were lower than 1, indicating no appreciable risk to consumers. Assuming the simultaneous use of all product types and the worst-case scenario for calculations, perfluoroalkyl carboxylic acids and perfluoroalkane sulfonic acids (PFSAs) also had hazard indices lower than 1. We found that adverse effects are unlikely to occur when each type of cosmetic is used separately, or even when all product types are used together. Nevertheless, the persistence and bioaccumulation characteristics of additional PFAS present in cosmetics continue to be a cause for concern. Further research is necessary to investigate the long-term impacts of using such cosmetics and the associated risks to human health.
Assuntos
Ácidos Alcanossulfônicos , Cosméticos , Fluorocarbonos , Cosméticos/análise , Fluorocarbonos/análise , Fluorocarbonos/toxicidade , Medição de Risco , Humanos , Ácidos Alcanossulfônicos/análise , Caprilatos/análise , Caprilatos/toxicidade , Poluentes Ambientais/análise , Monitoramento Ambiental , Exposição AmbientalRESUMO
In this study, for the first time, we determined concentrations of hexabromocyclododecane (HBCDD) and tetrabromobisphenol-A (TBBPA) in house dust and estimated human exposure to these substances in houses located in an e-waste dismantling site and in urban and rural residential areas of Thailand. The median HBCDD concentration in urban residential houses (2.10 ng g-1) was similar to that in houses in an e-waste dismantling site (2.05 ng g-1, p > 0.05) and slightly higher than that in rural residential houses (1.11 ng g-1, p > 0.05). In contrast, significantly higher TBBPA concentrations were present in house dust from an e-waste dismantling site (median = 720 ng g-1; range = 44-2300 ng g-1) compared to those in urban (68.6 ng g-1; 3.5-300 ng g-1, p < 0.001) and rural residential areas (17 ng g-1; 2.0-201 ng g-1, p < 0.001). TBBPA concentrations increased with the increasing presence of electronic devices and a decreasing distance to the e-waste dismantling site. These results suggest that e-waste dismantling activities may contribute to TBBPA contamination of house dust. The median estimated daily intake (EDI) of HBCDD and TBBPA through dust ingestion for toddlers exceeded that for children and adults. However, EDI values for HBCDD and TBBPA from all age groups were below the oral reference dose guideline value suggested by the US National Research Council and National Toxicology Program (NTP).