Dergiler / Atmospheric Pollution Research / 2018 / Cilt: 9 - Sayı: 1

Factors influencing the diurnal atmospheric concentrations and soil-air exchange of PBDEs at an e-waste recycling site in China

Sayfa
166–171
DOI
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⚡ TL;DR(1 Cümlede Hızlı Çıkarım)

The diurnal variation of atmospheric concentrations of PBDEs is not strong enough to alter the soil-air exchange direction.

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Amaç & Hipotez:Factors influencing the diurnal atmospheric concentrations and soil-air exchange of polybrominated diphenyl ethers (PBDEs) were investigated at an e-waste recycling site in China during winter and summer.
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Temel Bulgular & Veri:Total PBDE concentrations in winter and summer were 11.0e42.4 and 120e431 pg/m3 in the gaseous phase and 13.3e234 and 69.0e208 pg/m3 in the particulate phase, respectively.
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Sonuç & Katkı:The diurnal variation of atmospheric concentrations of PBDEs is not strong enough to alter the soil-air exchange direction.
🔬Tür:Araştırma Makalesi
📍Kapsam:Genişletilmiş Akademik Örneklem
⚙️Değişkenler:Alan Parametreleri

Özet

Factors influencing the diurnal atmospheric concentrations and soil-air exchange of polybrominated diphenyl ethers (PBDEs) were investigated at an e-waste recycling site in China during winter and summer. Total PBDE concentrations in winter and summer were 11.0e42.4 and 120e431 pg/m3 in the gaseous phase and 13.3e234 and 69.0e208 pg/m3 in the particulate phase, respectively. Total PBDE concentrations in the e-waste contaminated and nearby soils were 869 and 611 ng/g in winter and 2130 and 31 ng/g in summer, respectively. Concentrations in the gaseous phase were significantly higher in summer than in winter, but concentrations in the particle phase were comparable between winter and summer. Because of the influence of occasional accidental inputs, no apparent diurnal variations were found for PBDEs in either the particle or gaseous phase. Both temperatures and local emissions affected air concentrations of PBDEs in this area. The estimated directions of soil-air exchange of PBDEs suggest that the e-waste contaminated soil generally acted as a secondary source of several low brominated PBDEs, while the nearby soil acted as a secondary source of BDE28. The diurnal variation of atmospheric concentrations of PBDEs is not strong enough to alter the soil-air exchange direction.

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Bu Makaleye Atıf Yap

WANG, Y., HOU, M., ZHAO, H., ZHANG, Q., WU, X. (2018). Factors influencing the diurnal atmospheric concentrations and soil-air exchange of PBDEs at an e-waste recycling site in China. Atmospheric Pollution Research, Cilt: 9 - Sayı: 1, 166–171. https://ajindex.com/articles/210939

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  1. Abbasi, G., Buser, A.M., Soehl, A., Murray, M.W., Diamond, M.L., 2015. Stocks and flows of PBDEs in products from use to waste in the US and Canada from 1970 to 2020. Environ. Sci. Technol. 49, 1521e1528. Backe, C., Cousins, I.T., Larsson, P., 2004. PCB in soils and estimated soil-air exchange fluxes of selected PCB congeners in the south of Sweden. Environ. Pollut. 128, 59e72. Bidleman, T.F., Leone, A.D., 2004. Soil-air exchange of organochlorine pesticides in the southern United States. Environ. Pollut. 128, 49e57. Breivik, K., Armitage, J.M., Wania, F., Sweetman, A.J., Jones, K.C., 2016. Tracking the global distribution of persistent organic pollutants accounting for e-waste exports to developing regions. Environ. Sci. Technol. 50, 798e805. Cabrerizo, A., Dachs, J., Moeckel, C., Ojeda, M.-J., Caballero, G., Barcelo, D., et al., 2011. Factors influencing the soil-air partitioning and the strength of soils as a secondary source of polychlorinated biphenyls to the atmosphere. Environ. Sci. Technol. 45, 4785e4792. Cetin, B., Odabasi, M., 2007. Particle-phase dry deposition and air-soil gas-exchange of polybrominated diphenyl ethers (PBDEs) in Izmir, Turkey. Environ. Sci. Technol. 41, 4986e4992. Chen, D., Bi, X., Zhao, J., Chen, L., Tan, J., Mai, B., et al., 2009. Pollution characterization and diurnal variation of PBDEs in the atmosphere of an E-waste dismantling region. Environ. Pollut. 157, 1051e1057. Chen, L.G., Mai, B.X., Bi, X.H., Chen, S.J., Wang, X.M., Ran, Y., et al., 2006. Concentration levels, compositional profiles, and gas-particle partitioning of polybrominated diphenyl ethers in the atmosphere of an urban city in South China. Environ. Sci. Technol. 40, 1190e1196. Cheng, Z., Wang, Y., Wang, S., Luo, C., Li, J., Chaemfa, C., et al., 2014. The influence of land use on the concentration and vertical distribution of PBDEs in soils of an ewaste recycling region of South China. Environ. Pollut. 191, 126e131. Dalla Valle, M., Jurado, E., Dachs, J., Sweetman, A.J., Jones, K.C., 2005. The maximum reservoir capacity of soils for persistent organic pollutants: implications for global cycling. Environ. Pollut. 134, 153e164. Degrendele, C., Audy, O., Hofman, J., Kucerik, J., Kukucka, P., Mulder, M.D., et al., 2016. Diurnal variations of air-soil exchange of semivolatile organic compounds (PAHs, PCBs, OCPs, and PBDEs) in a central european receptor area. Environ. Sci. Technol. 50, 4278e4288. Harner, T., Mackay, D., Jones, K.C., 1995. Model of the long-term e