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Aerosol Processes in PAH Infiltration and Population Exposure in Rome

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Aerosol Processes in PAH Infiltration and Population Exposure in Rome

P. Lipponen1, O. Hänninen1, R. Sorjamaa1, M. Gherardi2, M.P. Gatto2, A. Gordiani2, A. Cecinato3, P. Romagnoli3 and C. Gariazzo2

1National Institute for Health and Welfare (THL), Department of Environmental Health, Kuopio, P.O. Box 95, Finland

2 Italian Workers’ Compensation Authority (INAIL), Monte Porzio Catone (RM), 00040, Italy

3 National Research Council of Italy, Institute of Atmospheric Pollution Research (CNR-IIA), P.O. Box 10, Monterotondo Stazione 00015, Rome, Italy

Keywords: PAH, infiltration, exposure, seasonal variation.

Presenting author email: pasi.lipponen@thl.fi

Polycyclic aromatic hydrocarbons (PAHs) are known to be harmful to human health e.g. by causing lung cancer (Vineis et al, 2004). Spatial variability of the emissions, atmospheric dispersion, infiltration of the particles from outdoor to indoors, and population time-activity defines the exposures. Since the time spent indoors is typically 80-90%, exceeding times spent in traffic and outdoors, indoor exposures and thus particle infiltration from outdoors is a key issue (e.g. Hänninen et al, 2004).

Infiltration from outdoors to indoors, as well as lung deposition, is largely affected by particle size (Hänninen et al, 2012). Recently, accumulation mode particle deposition to alveolar region has been noticed to be the largest contributor to the PAH uptake (Zhang et al, 2012).

The aim of the work is to quantify the main aerosol processes that modify infiltration and respiratory tract deposition.

PM2.5-bound PAH concentration measurements carried out in Rome, Italy, were used to evaluate the indoor-to-outdoor relationships of PAHs. A mass- balance model is used to estimate infiltration and indoor sources. Additional results regarding the indoor-outdoor behavior of PAH are presented in a parallel paper by Gatto et al.

High, up-to 30-40 fold differences in outdoor and indoor PAH concentrations were observed between non- heating and heating seasons. Indoor-to-outdoor ratios of PAH concentration between different microenvironments were noticed to vary much less, but between different seasons the variation of indoor-to- outdoor ratios for examined homes was significant.

Indoor sources played only a minor role in PAH exposures.

As can be seen from Figure 2, accumulation mode particles, i.e. the particles of which demonstrate high infiltration rate indoors and the particles of which are able to penetrate alveolar parts of human lungs are also the particles consisting high mass concentrations.

Seasonal heating emissions contribute almost 90% of the PAH exposure yearly in Rome metropolitan area followed by traffic and waste incineration. The variation in the PAH indoor-outdoor relationship is significant between different seasons, but there is only little variations between different microenvironments.

Majority of the PAH mass is in accumulation mode and ultrafine particle size ranges. The latter is affected more by infiltration.

Figure 1. Measured Σ11PAH concentration as a function of particle size distribution.

Figure 2. Outdoor concentration as a function of particle size distribution for all PAH compounds.

This work has been supported by Life+ -project EXPAH (Contract ENV/IT/000082; 2009), EU Contracts FP7-ENV-2009-1-243406 (TRANSPHORM), ENV4-CT95-0205 (ULTRA) and Academy of Finland Contract 133792 (PM Sizex).

Gatto M et al. (2013), Seasonal behavior of indoor and outdoor PAHs in different microenvironments of Rome, Italy. Parallel presentation at EAC.

Hänninen, O., Lebret, E., Ilacqua, V., Katsouyanni, K., Künzli, N., Srám, R.J. and Jantunen, M. (2004) Atm.Env. 38, 6411 - 6423

Hänninen, O., Sorjamaa, R., Pekkanen, J., Lanki, T. and Cyrys, J. (2012) Proc. Of Congress on Air Quality, Athens, Greece.

Vineis, P., Forastiere, F., Hoek, G. and Lipsett, M.

(2004) Int. J. Cancer 111, 647-652.

Zhang, K., Zhang, B.-Z., Li, S.-M., Wong, C. and Zeng, E.Y. (2012) Sci. Tot. Env. 431, 245-251.

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