PM_(2.5)-bound polycyclic aromatic hydrocarbons and nitro-polycyclic aromatic hydrocarbons inside and outside a primary school classroom in Beijing: Concentration, composition, and inhalation cancer risk

摘要

PM_(2.5) samples were collected inside and outside a primary school classroom in Beijing in 2015 and analysed for 11 polycyclic aromatic hydrocarbons (PAHs) and 10 nitro-PAHs (NPAHs). In the sampling period in the heating season (namely, the heating period), the median concentrations of indoor and outdoor PAHs were 223 ng/m~3 and 264 ng/m~3, respectively, and those of indoor and outdoor NPAHs were 3.61 ng/m~3 and 5.12 ng/m~3, respectively. The concentrations of PAHs and NPAHs were consistently higher in the heating period than those (indoor PAHs: 8.75 ng/m~3, outdoor PAHs: 8.95 ng/m~3, indoor NPAHs: 0.25 ng/m~3, outdoor NPAHs: 0.40 ng/m~3) in the sampling period in the non-heating season (namely, the non-heating period). In both periods, total PAHs and total NPAHs in indoor PM_(2.5), as well as most individual PAHs and NPAHs, were positively correlated with the outdoor PAH and NPAH concentrations (p < 0.05). This finding suggests that indoor PAHs and NPAHs are largely dependent on outdoor inputs. It is inferred from the diagnostic ratios that PAHs and NPAHs in indoor and outdoor PM_(2.5) were affected jointly by coal combustion and vehicular emission in the heating period and mainly derived from vehicle exhaust in the non-heating period. Both indoor and outdoor PM_(2.5) showed considerable benzo|a]pyrene equivalent toxicity (BaP_(eq)), especially in the heating period. Benzo[c]fluorene (BcFE) had relatively low concentrations but large contributions to BaP_(eq) in both periods. This is the first report of PM_(2.5)-bound BcFE inside and outside classrooms in Beijing. This result indicates that neglecting PAHs with low abundance but high toxicity leads to a significant underestimation of the overall PAH toxicity. The inhalation cancer risk (CR) of PAHs and NPAHs in PM_(2.5) during the primary school year exceeded the acceptable level as defined by the U.S. EPA emphasizing its impact on the lifetime CR in schoolchildren.