dc.contributor.author | Diapouli, E | en |
dc.contributor.author | Chaloulakou, A | en |
dc.contributor.author | Spyrellis, N | en |
dc.date.accessioned | 2014-03-01T01:26:33Z | |
dc.date.available | 2014-03-01T01:26:33Z | |
dc.date.issued | 2007 | en |
dc.identifier.issn | 0048-9697 | en |
dc.identifier.uri | https://dspace.lib.ntua.gr/xmlui/handle/123456789/18124 | |
dc.subject | Children exposure levels | en |
dc.subject | Diurnal cycles | en |
dc.subject | Indoor-to-outdoor ratio | en |
dc.subject | Ultrafine particles counts | en |
dc.subject.classification | Environmental Sciences | en |
dc.subject.other | Cleaning | en |
dc.subject.other | Indoor air pollution | en |
dc.subject.other | Parameter estimation | en |
dc.subject.other | Urban planning | en |
dc.subject.other | Vehicles | en |
dc.subject.other | Children | en |
dc.subject.other | Diurnal cycles | en |
dc.subject.other | Microenvironments | en |
dc.subject.other | Ultrafine particles | en |
dc.subject.other | Particles (particulate matter) | en |
dc.subject.other | air quality | en |
dc.subject.other | child health | en |
dc.subject.other | epidemiology | en |
dc.subject.other | particulate matter | en |
dc.subject.other | pollution exposure | en |
dc.subject.other | pollution monitoring | en |
dc.subject.other | public health | en |
dc.subject.other | traffic emission | en |
dc.subject.other | air pollutant | en |
dc.subject.other | airborne particle | en |
dc.subject.other | article | en |
dc.subject.other | child health | en |
dc.subject.other | exhaust gas | en |
dc.subject.other | health hazard | en |
dc.subject.other | high risk population | en |
dc.subject.other | indoor air pollution | en |
dc.subject.other | particle size | en |
dc.subject.other | particulate matter | en |
dc.subject.other | pollution monitoring | en |
dc.subject.other | population exposure | en |
dc.subject.other | priority journal | en |
dc.subject.other | traffic and transport | en |
dc.subject.other | urbanization | en |
dc.subject.other | Air Pollutants | en |
dc.subject.other | Air Pollution, Indoor | en |
dc.subject.other | Child | en |
dc.subject.other | Environmental Exposure | en |
dc.subject.other | Environmental Monitoring | en |
dc.subject.other | Greece | en |
dc.subject.other | Housing | en |
dc.subject.other | Humans | en |
dc.subject.other | Motor Vehicles | en |
dc.subject.other | Particle Size | en |
dc.subject.other | Particulate Matter | en |
dc.subject.other | Schools | en |
dc.subject.other | Vehicle Emissions | en |
dc.subject.other | Athens [Attica] | en |
dc.subject.other | Attica | en |
dc.subject.other | Eurasia | en |
dc.subject.other | Europe | en |
dc.subject.other | Greece | en |
dc.subject.other | Southern Europe | en |
dc.title | Levels of ultrafine particles in different microenvironments - Implications to children exposure | en |
heal.type | journalArticle | en |
heal.identifier.primary | 10.1016/j.scitotenv.2007.07.063 | en |
heal.identifier.secondary | http://dx.doi.org/10.1016/j.scitotenv.2007.07.063 | en |
heal.language | English | en |
heal.publicationDate | 2007 | en |
heal.abstract | Indoor and outdoor ultrafine particles (UFPs) (0.01 to greater than I gm) concentration levels were examined in the area of Athens during cold period of 2003 and 2004. Seven primary schools, located in areas with different characteristics of urbanization and traffic density, as well as a typical suburban residence, were monitored. Moreover, in-vehicle concentration levels, while driving along major avenues and in the heavy-trafficked centre of Athens, were measured (mean route duration: 45 min). UFPs number concentration was monitored by condensation particle counter (model CPC 3007), with a logging time interval of I min. The highest mean indoor concentrations were observed in a small carpet-covered library and a teachers' office (8-hour mean equal to 52.6 center dot 10(3) particles/cm(3) and 50.2 center dot 10(3) particles/cm(3), respectively), at the same school unit. The highest outdoor concentrations (8-hour mean equal to 36.9 center dot 10(3) particleS/cm(3) and 38.8 center dot 10(3) particles/cm(3)) were measured at two schools, both affected by heavy traffic. Finally, the highest in-vehicle concentrations (148.0 center dot 10(3)-173.0 center dot 10(3) particles/cm(3)) were measured in central commercial areas of Athens during, on average, 55 min drives. Indoor-to-outdoor concentration (I/O) ratios were below 1.00 at all sites. The largest ratio (0.88) was observed in the residence, during a day when there was cleaning activity in the room monitored. Outdoor concentrations diurnal cycles, both outside the schools and the residence, were closely related to traffic. Indoor concentrations inside schools were relatively stable in classrooms. Nevertheless, number concentrations exhibited variability when there were significant changes in room occupancy. Diurnal variation of indoor concentrations at the residence followed the respective outdoor one with a delay of 1h or less, in the absence of strong indoor sources, indicating the major contribution of outdoor UFPs to the indoor concentration levels. The present work is the first effort to examine UFPs indoor and outdoor concentration levels in the area of Athens. The obtained concentration data give an insight on the concentration levels to which children may be exposed. They may be also very useful in epidemiological studies, in order to estimate children total personal exposure though the calculation of exposures received in different microenvironments. This kind of studies may contribute to the design of effective policies and mitigation measures for the protection of public health. (c) 2007 Elsevier B.V. All rights reserved. | en |
heal.publisher | ELSEVIER SCIENCE BV | en |
heal.journalName | Science of the Total Environment | en |
dc.identifier.doi | 10.1016/j.scitotenv.2007.07.063 | en |
dc.identifier.isi | ISI:000251185300014 | en |
dc.identifier.volume | 388 | en |
dc.identifier.issue | 1-3 | en |
dc.identifier.spage | 128 | en |
dc.identifier.epage | 136 | en |
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