dc.contributor.author |
Grivas, G |
en |
dc.contributor.author |
Cheristanidis, S |
en |
dc.contributor.author |
Chaloulakou, A |
en |
dc.date.accessioned |
2014-03-01T02:08:51Z |
|
dc.date.available |
2014-03-01T02:08:51Z |
|
dc.date.issued |
2012 |
en |
dc.identifier.issn |
00489697 |
en |
dc.identifier.uri |
https://dspace.lib.ntua.gr/xmlui/handle/123456789/29732 |
|
dc.subject |
Athens |
en |
dc.subject |
EC tracer method |
en |
dc.subject |
Elemental carbon |
en |
dc.subject |
Organic carbon |
en |
dc.subject |
Secondary organic aerosol (SOA) |
en |
dc.subject |
Urban air pollution |
en |
dc.subject.other |
Athens |
en |
dc.subject.other |
Elemental carbon |
en |
dc.subject.other |
Secondary organic aerosols |
en |
dc.subject.other |
Tracer methods |
en |
dc.subject.other |
Urban air pollution |
en |
dc.subject.other |
Air pollution |
en |
dc.subject.other |
Atmospheric aerosols |
en |
dc.subject.other |
Carbon |
en |
dc.subject.other |
Fog |
en |
dc.subject.other |
Particles (particulate matter) |
en |
dc.subject.other |
Photochemical forming |
en |
dc.subject.other |
Radioactive tracers |
en |
dc.subject.other |
Transportation |
en |
dc.subject.other |
Organic carbon |
en |
dc.subject.other |
carbon |
en |
dc.subject.other |
elemental carbon |
en |
dc.subject.other |
organic carbon |
en |
dc.subject.other |
organic matter |
en |
dc.subject.other |
secondary organic carbon |
en |
dc.subject.other |
unclassified drug |
en |
dc.subject.other |
aerosol |
en |
dc.subject.other |
atmospheric pollution |
en |
dc.subject.other |
concentration (composition) |
en |
dc.subject.other |
correlation |
en |
dc.subject.other |
diurnal variation |
en |
dc.subject.other |
organic carbon |
en |
dc.subject.other |
photochemistry |
en |
dc.subject.other |
regression analysis |
en |
dc.subject.other |
sea breeze |
en |
dc.subject.other |
seasonal variation |
en |
dc.subject.other |
tracer |
en |
dc.subject.other |
urban pollution |
en |
dc.subject.other |
air pollutant |
en |
dc.subject.other |
air pollution |
en |
dc.subject.other |
airflow |
en |
dc.subject.other |
article |
en |
dc.subject.other |
calculation |
en |
dc.subject.other |
circadian rhythm |
en |
dc.subject.other |
concentration (parameters) |
en |
dc.subject.other |
controlled study |
en |
dc.subject.other |
Greece |
en |
dc.subject.other |
measurement |
en |
dc.subject.other |
priority journal |
en |
dc.subject.other |
seasonal variation |
en |
dc.subject.other |
secondary organic aerosol |
en |
dc.subject.other |
traffic |
en |
dc.subject.other |
urban area |
en |
dc.subject.other |
wind |
en |
dc.subject.other |
Athens [Attica] |
en |
dc.subject.other |
Attica |
en |
dc.subject.other |
Greece |
en |
dc.title |
Elemental and organic carbon in the urban environment of Athens. Seasonal and diurnal variations and estimates of secondary organic carbon |
en |
heal.type |
journalArticle |
en |
heal.identifier.primary |
10.1016/j.scitotenv.2011.10.058 |
en |
heal.identifier.secondary |
http://dx.doi.org/10.1016/j.scitotenv.2011.10.058 |
en |
heal.publicationDate |
2012 |
en |
heal.abstract |
Elemental and organic carbon (EC and OC) hourly concentrations were measured continuously, at an urban location in central Athens, Greece, for an 8-month period (January-August). Average concentrations of 2.2μgCm-3 and 6.8μgCm-3 were observed, for EC and OC, respectively. The combined contribution of carbonaceous compounds (EC plus organic matter) to PM10 was calculated at 26%. The seasonal variability of EC was limited, while OC mean concentrations were significantly higher (by 23%), during the warm months (May-August). The weekly variation followed a different pattern, with the weekend decrease of EC levels (25%) being more pronounced than of OC (14%). EC produced a bimodal diurnal cycle, with the morning rush hour traffic mode prevailing. The OC mean circadian variation displayed those peaks as well. However, midday-to-afternoon presence of secondary organic aerosol (SOA) was strongly indicated. The conditional probability function was used to assess the impact of wind direction. High EC, OC levels were linked to southern flows, which during summer are mainly related to the appearance of sea breeze circulation. The temporal variation of EC, OC and their correlation patterns with primary and secondary gaseous pollutants, suggested that, although primary emissions affected both fractions, SOA formation is an important factor to be accounted for, especially during the photochemical season. Secondary organic carbon was estimated using the EC tracer method and orthogonal regression on OC, EC hourly concentration data. The average contributions of secondary organic carbon (SOC) to OC were calculated at 20.9% for the cold period and 30.3% for the warm period. Maximum values of 58% and 91% were estimated for daily and hourly contributions, respectively. The SOC diurnal variations suggested photochemical formation throughout the year, intensified during summer months, with the correlation coefficient between SOC and the sum of oxidants (NO2+O3) reaching up to 0.84. © 2011 Elsevier B.V. |
en |
heal.journalName |
Science of the Total Environment |
en |
dc.identifier.doi |
10.1016/j.scitotenv.2011.10.058 |
en |
dc.identifier.volume |
414 |
en |
dc.identifier.spage |
535 |
en |
dc.identifier.epage |
545 |
en |