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dc.contributor.authorRivas, Ioar-
dc.contributor.authorViana, Mar-
dc.contributor.authorMoreno, Teresa-
dc.contributor.authorBouso, L.-
dc.contributor.authorPandolfi, Marco-
dc.contributor.authorÁlvarez-Pedrerol, Mar-
dc.contributor.authorForns, Joan-
dc.contributor.authorAlastuey, Andrés-
dc.contributor.authorSunyer, J.-
dc.contributor.authorQuerol, Xavier-
dc.date.accessioned2020-08-28T08:00:47Z-
dc.date.available2020-08-28T08:00:47Z-
dc.date.issued2015-
dc.identifierdoi: 10.1016/j.atmosenv.2015.01.055-
dc.identifierissn: 1873-2844-
dc.identifier.citationAtmospheric Environment 106: 129-138 (2015)-
dc.identifier.urihttp://hdl.handle.net/10261/218793-
dc.description.abstract© 2015 The Authors. Infiltration of outdoor-sourced particles into indoor environments in 39 schools in Barcelona was assessed during school hours. Tracers of road traffic emissions (NO2, Equivalent Black Carbon (EBC), Ultrafine Particles (UFP), Sb), secondary inorganic aerosols (SO4 2-, NO3 -, NH4 +) and a number of PM2.5 trace elements showed median indoor/outdoor (I/O) ratios≤1, indicating that outdoor sources importantly contributed to indoor concentrations. Conversely, OC and mineral components had I/O ratios>1. Different infiltration factors were found for traffic and secondary components (0.31-0.75 and 0.50-0.92, cold and warm season respectively), with maxima corresponding to EBC and Cd. Higher concentrations of indoor-generated particles were observed when closed windows hindered dispersion (cold season). Building age was not a major determinant of indoor levels. Neither were the window's material, except for NO2 (with an increase of 8μgm-3 for wood framed windows) and the mineral components (also dependent on the presence of sand in a distance <20m) that reach the indoor environment via soil adhering to footwear with their dispersion being more barred by Aluminium/PVC framed windows than the wooden ones. Enlarged indoor concentrations of some trace elements suggest the presence of indoor sources that should be further investigated in order to achieve a healthier school indoor environment.-
dc.description.sponsorshipThe research leading to these results has received funding from the European Community's Seventh Framework Program (ERC-Advanced Grant) under grant agreement number 268479 – the BREATHE project. Thanks are due to all the participant schools and colleagues. Additional instrumentation was kindly provided by national projects IMPACT (CGL2011-26574), VAMOS (CLG2010-19464-CLI) and CECAT (CTM2011-14730-E). Support from the Generalitat de Catalunya 2015 SGR33is gratefully acknowledged.-
dc.languageeng-
dc.relationinfo:eu-repo/grantAgreement/EC/FP7/268479-
dc.relation.isversionofPublisher's version-
dc.rightsopenAccess-
dc.titleOutdoor infiltration and indoor contribution of UFP and BC, OC, secondary inorganic ions and metals in PM2.5 in schools-
dc.typeartículo-
dc.identifier.doi10.1016/j.atmosenv.2015.01.055-
dc.relation.publisherversionhttp://dx.doi.org/10.1016/j.atmosenv.2015.01.055-
dc.date.updated2020-08-28T08:00:48Z-
dc.contributor.funderEuropean Commission-
dc.contributor.funderMinisterio de Ciencia e Innovación (España)-
dc.contributor.funderGeneralitat de Catalunya-
dc.relation.csic-
dc.identifier.funderhttp://dx.doi.org/10.13039/501100000780es_ES
dc.identifier.funderhttp://dx.doi.org/10.13039/501100002809es_ES
dc.identifier.funderhttp://dx.doi.org/10.13039/501100004837es_ES
dc.type.coarhttp://purl.org/coar/resource_type/c_6501es_ES
item.grantfulltextopen-
item.cerifentitytypePublications-
item.openairecristypehttp://purl.org/coar/resource_type/c_18cf-
item.fulltextWith Fulltext-
item.openairetypeartículo-
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