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Fine particle chemistry studies with the Aerosol Mass Spectrometer (AMS). Risto Hillamo Finnish Meteorological Institute, Helsinki, Finland. Campaigns in Helsinki Urban background station December 8 -19, 2008 January 8 - March 13, 2009 April 9 - May 7, 2009 Traffic station
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Fine particle chemistry studies with the Aerosol Mass Spectrometer (AMS) Risto Hillamo Finnish Meteorological Institute, Helsinki, Finland
Campaigns in Helsinki • Urban background station • December 8 -19, 2008 • January 8 - March 13, 2009 • April 9 - May 7, 2009 • Traffic station • May 20 - June 02, 2009 Risto Hillamo/Finnish Meteorological Institute
Experimental methods: urban background station • Aerodyne High-Resolution Time-of-Flight Aerosol Mass Spectrometer (HR-ToF-AMS): Non-refractory inorganic and organic aerosol material (5 min) • Particle Into Liquid Sampler coupled with an Ion Chromatograph (PILS-IC): Major watersoluble anions and cations, including oxalate (15 min) • Particle Into Liquid Sampler coupled with a total organic carbon analyzer (PILS-TOC): Water-soluble organic carbon (5 min) • Semicontinuous EC/OC analyser (Sunset): Organic carbon and elemental carbon (2 h) • Tapered element oscillating micro-balance (TEOM): PM1 mass concentration (10 min) • PM1 filter sample: Chemical analysis by the IC coupled with MS Risto Hillamo/Finnish Meteorological Institute
AMS container Helsinki Fine PM Experiment 2008-2009 Inlet: Sharp Cut Cyclone, PM1 sample Risto Hillamo/Finnish Meteorological Institute
AMS container: inside AMS PILS-IC PILS-TOC Risto Hillamo/Finnish Meteorological Institute
AMS vs. other instruments Risto Hillamo/Finnish Meteorological Institute
AMS vs. other instruments Risto Hillamo/Finnish Meteorological Institute
3 1 2 4 5 6 Special events Risto Hillamo/Finnish Meteorological Institute
FMI N Hämeentie Aerosols from traffic (200 m transport) 10/12/2008 SMEAR III Risto Hillamo/Finnish Meteorological Institute
p-ToF-mode: Chemical particle mass size distribution Risto Hillamo/Finnish Meteorological Institute
Traffic – winter inversion m/z 57 = C4H9 Risto Hillamo/Finnish Meteorological Institute
Sulphuric acid aerosol 4 Risto Hillamo/Finnish Meteorological Institute
Oil-shale combustion power plants Narva, Estonia gases Risto Hillamo/Finnish Meteorological Institute
Biomass burning – wood combustion AMS 5 min AMS m/z 60 vs. Filter PM1 levoglucosan Risto Hillamo/Finnish Meteorological Institute
Water-soluble organic carbon Risto Hillamo/Finnish Meteorological Institute
Traffic station May 20 - June 02, 2009 • Locates in downtown of Helsinki • A few meters from the road • AMS • MAAP: black carbon • PM10/PM2.5: mass concentration • NO2, NO Street level PM10 PM2.5 NOx MAAP PM1 AMS PM1 Risto Hillamo/Finnish Meteorological Institute
Black carbon and total organic and inorganic material Risto Hillamo/Finnish Meteorological Institute
Average composition of May 20 - June 02, 2009 Risto Hillamo/Finnish Meteorological Institute
Size distributions of traffic aerosols Risto Hillamo/Finnish Meteorological Institute
Conclusions • AMS unit mass resolution data is excellent for studies of inorganic non-refractory material (e.g. comparable with time-scales of weather parameters and gas phase measurements or backward trajectories), and in most cases it gives a good view to sources and origin of organic material • AMS high-resolution data needed to understand better the chemistry of organic aerosols • (A. C. Aiken et al., ACPD 9, 8377–8427, 2009) Risto Hillamo/Finnish Meteorological Institute