SlideShare a Scribd company logo
1 of 23
IAC Helsinki 30/08/2010
Source Apportionment of PM2.5 in Cork Harbour,
Ireland using single particle mass spectrometry
R. M. Healy1, S. Hellebust1, I. Kourtchev1, A. Allanic1, I. O’Connnor1, J. Bell1,
M. Dall’Osto2, D. Ceburnis2, J. Ovadnevaite2, H. Berresheim2, C. O’Dowd2,
J. Sodeau1, J. Wenger1
1Department of Chemistry and Environmental Research Institute, University College Cork, Ireland
2School of Physics and Centre for Climate and Pollution Studies, Environmental Change Institute,
National University of Ireland Galway, Ireland
Aims
IAC Helsinki 30/08/2010
1: To measure the size-resolved chemical composition of single particles in
Cork Harbour using Aerosol Time-of-Flight Mass Spectrometry (ATOFMS)
2: To use this information to identify sources of PM2.5 with an emphasis on
local shipping emissions
3: To combine ATOFMS data with other semi-continuous measurements in
order to estimate the contribution of each source to ambient PM2.5 mass
concentration and particle number concentration
Sampling Site
IAC Helsinki 30/08/2010
X
B
B
B
0.05 0.1 0.15 0.2
0
45
90
135
180
225
270
315
0 - 2
2 - 4
4 - 6
6 - 8
8+
(m s
-1
)
Sampling carried out at Tivoli Docks, Cork
Harbour for three weeks (7-28/08/2008)
R. M. Healy et al., Atmos. Chem. Phys. Discuss. 10, 1035-1082, 2010
Instrumentation
IAC Helsinki 30/08/2010
Instrument Measurement
ATOFMS (TSI, 3800) Size-resolved single particle chemical
composition
SMPS (TSI, 3081) Particle number (20-700 nm)
TEOM (Thermo, 1400a) PM2.5
Thermal-optical carbon analyser
(Sunset, 3rd gen. field model)
ECOC
Sulfate analyser (Thermo, 5020 SPA) Particulate SO4
2-
IAC Helsinki 30/08/2010
Data Analysis
1: Over 500,000 particle mass spectra were collected, imported into
ENCHILADA1 and clustered using the K-means algorithm (K=50)
2: 50 clusters reduced to 14 ATOFMS classes; Peat, Coal, Wood, Sea salt,
Shipping, Ca-traffic, EC-traffic, EC-phos, EC-MSA, EC-domestic, EC-background,
EC-oil, ECOC, and Oligomer
3: ATOFMS counts for each class were sorted into hourly bins and used along
with hourly averages of EC/OC, SO4
2- and hourly integrated SMPS particle
counts for positive matrix factorisation (PMF) in order to reconstruct PM2.5
mass concentrations
1D. Gross et al., Environmental Modelling & Software 25, 760-769, 2010
IAC Helsinki 30/08/2010
ATOFMS Results: Shipping
R. M. Healy et al., Atmospheric Environment 43, 6408-6414, 2009
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
Ca+
V+
VO+
C2H3
+
Na+
C+
C3
+
Fe+
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
SO3
-
C2
-
CN-
HSO4
-
C3
-
C4
-
50 60 70 80 90 100 110 120 130 140 150
Na2Cl+
Na2Cl+Na2O+
50 60 70 80 90 100 110 120 130 140 150
NaCl2
-
NO3
-
O2
-
SO3
-
NaCl-
NaCl2
-/HSO4
-
m/z m/z
RelativeIntensity
C3
+
A B
DC
IAC Helsinki 30/08/2010
ATOFMS Results: Shipping
0
50
100
150
200
250
300
ATOFMScounts
Date
ATOFMS "Shipping" class
10
20
30
40
0
45
90
135
180
225
270
315
ATOFMS "Shipping" class
IAC Helsinki 30/08/2010
ATOFMS Results: Shipping
200
150
100
50
0
ATOFMScounts
15:00
23/08/2008
16:00 17:00 18:00 19:00 20:00 21:00 22:00
Time
2
3
4
5
6
7
100
2
3
4
5
6
7
mobilitydiameter(nm)
5x10
5
4
3
2
1
0
(#cm
-3
)
ATOFMS "Shipping" Class
IAC Helsinki 30/08/2010
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C+
C3
+
K+/C3H3
+
C2H3O+
Na+
C2H3
+
C5
+
C4H2
+
C4
+
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C2
-
CN-
C3
-
CNO-
NO3
-
NO2
-
HSO4
-
SO3
-C4
-
RelativeIntensity
m/z
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C+
C3
+
K+
C2H3O+
Na+
C2H3
+
C5
+
C4H2
+
C4
+
10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C+
C3
+
K+
C2H3O+
Na+
C2H3
+
C5
+
C4H2
+
C4
+
m/z m/z
10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C2
-
CN-
C3
-
CNO-
C4
-
NO3
-
NO2
-
HSO4
-
Cl-
Cl-
C5
-
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C2
-
CN-
C3
-
CNO-
NO3
-
NO2
-
HSO4
-
Cl-
Cl-
C5
-
C4
-
RelativeIntensity
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C+
C3
+
K+
Na+
K+
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C+
C3
+
K+
Na+
K+
m/z m/z
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
O-
OH-
C2
-
CN-
C3
-
Cl-
Cl-
CNO-
NO2
-
C4
-
NO3
-
C2H3O2
-
HSO4
-
COOHCOO-
C3H3O2
-
KCl2
-
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
O-
OH-
C2
-
CN-
C3
-
Cl-
Cl-
CNO-
NO2
-
C4
-
NO3
-
C2H3O-
C2H3O2
-
C3H3O2
-
HSO4
-
KCl2
-
COOHCOO-
RelativeIntensity
RelativeIntensity
ATOFMS Results: DomesticCombustion
Coal Peat Wood
IAC Helsinki 30/08/2010
ATOFMS Results: DomesticCombustion
0
50
100
150
200
250
0
100
200
300
400
500
600
700
800
ATOFMScounts(h-1)
ATOFMScounts(h-1)
Time
coal peat wood
IAC Helsinki 30/08/2010
ATOFMS Results: DomesticCombustion
IAC Helsinki 30/08/2010
ATOFMS Results: Traffic
1200
EC-domestic Oligomer
0
500
1000
1500
2000
2500
ATOFMScounts(h-1
)
Time
Ca-traffic EC-traffic EC-phos
IAC Helsinki 30/08/2010
Semi-continuousResults
OC EC SO4
2- PM2.5
Mean 1.13 0.61 0.49 9.67
Median 1.02 0.55 0.45 8.55
Maximum 3.41 2.90 2.14 49.80
Minimum 0.22 0.00 0.04 1.50
Hourly averaged values (µg m-3) 7-28/08/2008
IAC Helsinki 30/08/2010
PMFResults
Traffic
Domestic
Combustion
Various
Combustion
Marine Long-range Shipping
Quantitative
measurements:
OC mass 21 21 16 20 18 4
EC mass 43 20 18 5 11 4
Sulfate mass 9 11 40 23 15 2
Particle number (SMPS) 42 14 13 6 7 18
PM2.5 mass 23 5 11 14 13 1
ATOFMS classes:
Coal 5 52 30 3 7 3
Peat 3 84 5 2 3 2
Wood 11 63 5 13 6 1
Sea salt 1 0 2 86 10 1
Shipping 0 0 0 0 0 100
Ca-traffic 83 0 0 4 8 4
EC-traffic 59 25 6 1 3 6
EC-phos 82 9 3 0 6 0
EC-MSA 1 0 3 6 90 0
EC-domestic 0 91 0 0 2 7
EC-background 28 18 35 1 11 6
EC-oil 52 24 24 1 0 0
ECOC 0 0 69 0 31 0
Oligomer 0 76 8 15 0 1
% Variable contributions to six-factor model and
estimated % contribution to measured PM2.5 mass
IAC Helsinki 30/08/2010
Conclusions
1: Unique mass spectral fingerprints and high time resolution of ATOFMS are
suited to source identification and apportionment, representing a useful
alternative to off-line chemical analysis of PM2.5
2: The major sources of PM2.5 in Cork Harbour during the summer are traffic
and sea spray, followed by local combustion processes including a contribution
from domestic solid fuel burning
3: Although shipping traffic contributes very little to PM2.5 mass
concentrations, the contribution to particle number concentration is almost
half that of traffic
IAC Helsinki 30/08/2010
Acknowledgements
Port of Cork for providing a suitable sampling site
Higher Education Authority, Environmental Protection Agency
and Science Foundation Ireland for providing funding for this
research
Thank you for your attention!
IAC Helsinki 30/08/2010
IAC Helsinki 30/08/2010
0
1
2
3
4
5
6
7
0
500
1000
1500
2000
2500
Windspeed(ms-1)
ATOFMScounts(h-1)
Date
Coal-amm-nit Peat-nit Wood-nit Wind speed
0
100
200
300
400
500
600
700
800
900
ATOFMS[NO3]-RelativeIntensity
Time
coal peat wood
Hourly averaged signal for nitrate for the Coal, Peat and Wood ATOFMS
classes for the 4 low wind speed events (11-12 August 2008, 13-15 August
2008 and 22-23 August 2008).
IAC Helsinki 30/08/2010
Concentration-time profiles for PM2.5
*, SO4
2-*, organic carbon** and elemental
carbon** for 07-28 August 2008. *Hourly averaged mass concentration. **2 hour
averaged mass concentration.
3.0
2.0
1.0
0.0
µgm
-3
07/08/2008
08/08/2008
09/08/2008
10/08/2008
11/08/2008
12/08/2008
13/08/2008
14/08/2008
15/08/2008
16/08/2008
17/08/2008
18/08/2008
19/08/2008
20/08/2008
21/08/2008
22/08/2008
23/08/2008
24/08/2008
25/08/2008
26/08/2008
27/08/2008
28/08/2008
Date
2.0
1.5
1.0
0.5
0.0
µgm
-3 50
40
30
20
10
0
µgm
-3 PM2.5 SO4
2-
OC EC
IAC Helsinki 30/08/2010
ATOFMS Results: Traffic
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
Ca+
VO+
C2H3
+
Na+
C+
C3
+
Fe+
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
SO3
-
C2
-
CN-
HSO4
-
C3
-
C4
-
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
Na2Cl+K+
Na2Cl+Na2O+
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
NaCl2
-
Cl-
NO3
-
NO2
-
SO3
-
Cl-
NaCl-
NaCl2
-/HSO4
-Na-
O-
m/z m/z
RelativeIntensity
RelativeIntensity
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
Ca+
Na+
C+
C3
+
C4
+
C5
+
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C2
-
CN-
HSO4
-
C3
-
C4
-
C5
-
m/z
RelativeIntensity
D
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
Ca2O+
Ca+
CaO+
CaOH+
C2H3
+
m/z
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
PO2
-
NO2
-
HSO3
-
CNO-
NO3
-
CN-
PO3
-
PO4
-
RelativeIntensity
C
0 10 20 30 40
C+
C3
+
C2
+
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C+
C3
+
C4
+
C5
+
C2
+
m/z
0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150
C2
-
CN-
HSO4
-
C3
-
C4
-
NO3
-
PO3
-
0 10 20 30 40
C2
-
CN-
C3
-
RelativeIntensity
RelativeIntensity
A
K+
C3
+
Na+
K+
C
Ca-Traffic EC-traffic EC-phos
IAC Helsinki 30/08/2010
0
20
40
60
80
100
120
140
160
ATOFMScounts(h-1)
Date
EC-phos EC-MSA
IAC Helsinki 30/08/2010
Fig. 15: 5 day back-trajectories for air masses arriving at Cork Harbour on at 00:00 h
on 10 (left), 14 (middle) and 26 August 2008 (right).

More Related Content

Similar to Robert Healy IAC 2010

Zazzeri, Giulia: Efficient sampling of atmospheric methane for radiocarbon an...
Zazzeri, Giulia: Efficient sampling of atmospheric methane for radiocarbon an...Zazzeri, Giulia: Efficient sampling of atmospheric methane for radiocarbon an...
Zazzeri, Giulia: Efficient sampling of atmospheric methane for radiocarbon an...Integrated Carbon Observation System (ICOS)
 
Steinhoff, Tobias: Uncertainty analysis for calculations of the marine carbon...
Steinhoff, Tobias: Uncertainty analysis for calculations of the marine carbon...Steinhoff, Tobias: Uncertainty analysis for calculations of the marine carbon...
Steinhoff, Tobias: Uncertainty analysis for calculations of the marine carbon...Integrated Carbon Observation System (ICOS)
 
Effects of anion on the corrosion behaviors of carbon steel under artificial ...
Effects of anion on the corrosion behaviors of carbon steel under artificial ...Effects of anion on the corrosion behaviors of carbon steel under artificial ...
Effects of anion on the corrosion behaviors of carbon steel under artificial ...eSAT Journals
 
Effects of anion on the corrosion behaviors of carbon steel under artificial ...
Effects of anion on the corrosion behaviors of carbon steel under artificial ...Effects of anion on the corrosion behaviors of carbon steel under artificial ...
Effects of anion on the corrosion behaviors of carbon steel under artificial ...eSAT Journals
 
Assessment of automobile induced pollution in an urban
Assessment of automobile induced pollution in an urbanAssessment of automobile induced pollution in an urban
Assessment of automobile induced pollution in an urbanAlexander Decker
 
Preliminary Project Results-Ahmadi
Preliminary Project Results-AhmadiPreliminary Project Results-Ahmadi
Preliminary Project Results-AhmadiMahdi Ahmadi
 
Potential health effects of shipping-related PM - Matt Loxam
Potential health effects of shipping-related PM - Matt LoxamPotential health effects of shipping-related PM - Matt Loxam
Potential health effects of shipping-related PM - Matt LoxamIES / IAQM
 
Apec workshop 2 presentation 12 lh ci cinco presidentes-pemex-apec workshop 2
Apec workshop 2 presentation 12 lh ci cinco presidentes-pemex-apec workshop 2Apec workshop 2 presentation 12 lh ci cinco presidentes-pemex-apec workshop 2
Apec workshop 2 presentation 12 lh ci cinco presidentes-pemex-apec workshop 2Global CCS Institute
 
Tracking GHG emissions in a booming city -urban atmospheric monitoring in Rec...
Tracking GHG emissions in a booming city -urban atmospheric monitoring in Rec...Tracking GHG emissions in a booming city -urban atmospheric monitoring in Rec...
Tracking GHG emissions in a booming city -urban atmospheric monitoring in Rec...Integrated Carbon Observation System (ICOS)
 
Ion Mobility Petroleomics: Towards Isomeric Compositional Space Elucidation v...
Ion Mobility Petroleomics: Towards Isomeric Compositional Space Elucidation v...Ion Mobility Petroleomics: Towards Isomeric Compositional Space Elucidation v...
Ion Mobility Petroleomics: Towards Isomeric Compositional Space Elucidation v...Waters Corporation - Chemical Materials
 
The efect of diesel Sulfur content on PM2.5 aburra valley colombia
The efect of diesel Sulfur content on PM2.5 aburra valley colombiaThe efect of diesel Sulfur content on PM2.5 aburra valley colombia
The efect of diesel Sulfur content on PM2.5 aburra valley colombiaEnrique Posada
 
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...CRL Asia
 
Assessment of Air Quality in and Around Raichur Thermal Power Station, Raichur
Assessment of Air Quality in and Around Raichur Thermal Power Station, RaichurAssessment of Air Quality in and Around Raichur Thermal Power Station, Raichur
Assessment of Air Quality in and Around Raichur Thermal Power Station, RaichurIRJET Journal
 
Assessment of Air Quality in and Around Raichur Thermal Power Station, Raichur
Assessment of Air Quality in and Around Raichur Thermal Power Station, RaichurAssessment of Air Quality in and Around Raichur Thermal Power Station, Raichur
Assessment of Air Quality in and Around Raichur Thermal Power Station, RaichurIRJET Journal
 

Similar to Robert Healy IAC 2010 (20)

Zazzeri, Giulia: Efficient sampling of atmospheric methane for radiocarbon an...
Zazzeri, Giulia: Efficient sampling of atmospheric methane for radiocarbon an...Zazzeri, Giulia: Efficient sampling of atmospheric methane for radiocarbon an...
Zazzeri, Giulia: Efficient sampling of atmospheric methane for radiocarbon an...
 
Steinhoff, Tobias: Uncertainty analysis for calculations of the marine carbon...
Steinhoff, Tobias: Uncertainty analysis for calculations of the marine carbon...Steinhoff, Tobias: Uncertainty analysis for calculations of the marine carbon...
Steinhoff, Tobias: Uncertainty analysis for calculations of the marine carbon...
 
Effects of anion on the corrosion behaviors of carbon steel under artificial ...
Effects of anion on the corrosion behaviors of carbon steel under artificial ...Effects of anion on the corrosion behaviors of carbon steel under artificial ...
Effects of anion on the corrosion behaviors of carbon steel under artificial ...
 
Effects of anion on the corrosion behaviors of carbon steel under artificial ...
Effects of anion on the corrosion behaviors of carbon steel under artificial ...Effects of anion on the corrosion behaviors of carbon steel under artificial ...
Effects of anion on the corrosion behaviors of carbon steel under artificial ...
 
Assessment of automobile induced pollution in an urban
Assessment of automobile induced pollution in an urbanAssessment of automobile induced pollution in an urban
Assessment of automobile induced pollution in an urban
 
Preliminary Project Results-Ahmadi
Preliminary Project Results-AhmadiPreliminary Project Results-Ahmadi
Preliminary Project Results-Ahmadi
 
03 ea whitfield- Early careers winter school, 9-12th January 2012, University...
03 ea whitfield- Early careers winter school, 9-12th January 2012, University...03 ea whitfield- Early careers winter school, 9-12th January 2012, University...
03 ea whitfield- Early careers winter school, 9-12th January 2012, University...
 
PhD work
PhD workPhD work
PhD work
 
Potential health effects of shipping-related PM - Matt Loxam
Potential health effects of shipping-related PM - Matt LoxamPotential health effects of shipping-related PM - Matt Loxam
Potential health effects of shipping-related PM - Matt Loxam
 
Clm published def
Clm published defClm published def
Clm published def
 
Capstone Final
Capstone FinalCapstone Final
Capstone Final
 
Apec workshop 2 presentation 12 lh ci cinco presidentes-pemex-apec workshop 2
Apec workshop 2 presentation 12 lh ci cinco presidentes-pemex-apec workshop 2Apec workshop 2 presentation 12 lh ci cinco presidentes-pemex-apec workshop 2
Apec workshop 2 presentation 12 lh ci cinco presidentes-pemex-apec workshop 2
 
CAMS GA Emissions
CAMS GA EmissionsCAMS GA Emissions
CAMS GA Emissions
 
Tracking GHG emissions in a booming city -urban atmospheric monitoring in Rec...
Tracking GHG emissions in a booming city -urban atmospheric monitoring in Rec...Tracking GHG emissions in a booming city -urban atmospheric monitoring in Rec...
Tracking GHG emissions in a booming city -urban atmospheric monitoring in Rec...
 
Ion Mobility Petroleomics: Towards Isomeric Compositional Space Elucidation v...
Ion Mobility Petroleomics: Towards Isomeric Compositional Space Elucidation v...Ion Mobility Petroleomics: Towards Isomeric Compositional Space Elucidation v...
Ion Mobility Petroleomics: Towards Isomeric Compositional Space Elucidation v...
 
The efect of diesel Sulfur content on PM2.5 aburra valley colombia
The efect of diesel Sulfur content on PM2.5 aburra valley colombiaThe efect of diesel Sulfur content on PM2.5 aburra valley colombia
The efect of diesel Sulfur content on PM2.5 aburra valley colombia
 
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
Application on Semi-aerobic Landfill. Technology in in Tropical Climate: Lysi...
 
Assessment of Air Quality in and Around Raichur Thermal Power Station, Raichur
Assessment of Air Quality in and Around Raichur Thermal Power Station, RaichurAssessment of Air Quality in and Around Raichur Thermal Power Station, Raichur
Assessment of Air Quality in and Around Raichur Thermal Power Station, Raichur
 
Assessment of Air Quality in and Around Raichur Thermal Power Station, Raichur
Assessment of Air Quality in and Around Raichur Thermal Power Station, RaichurAssessment of Air Quality in and Around Raichur Thermal Power Station, Raichur
Assessment of Air Quality in and Around Raichur Thermal Power Station, Raichur
 
10.1016@j.egypro.2016.10.012
10.1016@j.egypro.2016.10.01210.1016@j.egypro.2016.10.012
10.1016@j.egypro.2016.10.012
 

Robert Healy IAC 2010

  • 1. IAC Helsinki 30/08/2010 Source Apportionment of PM2.5 in Cork Harbour, Ireland using single particle mass spectrometry R. M. Healy1, S. Hellebust1, I. Kourtchev1, A. Allanic1, I. O’Connnor1, J. Bell1, M. Dall’Osto2, D. Ceburnis2, J. Ovadnevaite2, H. Berresheim2, C. O’Dowd2, J. Sodeau1, J. Wenger1 1Department of Chemistry and Environmental Research Institute, University College Cork, Ireland 2School of Physics and Centre for Climate and Pollution Studies, Environmental Change Institute, National University of Ireland Galway, Ireland
  • 2. Aims IAC Helsinki 30/08/2010 1: To measure the size-resolved chemical composition of single particles in Cork Harbour using Aerosol Time-of-Flight Mass Spectrometry (ATOFMS) 2: To use this information to identify sources of PM2.5 with an emphasis on local shipping emissions 3: To combine ATOFMS data with other semi-continuous measurements in order to estimate the contribution of each source to ambient PM2.5 mass concentration and particle number concentration
  • 3. Sampling Site IAC Helsinki 30/08/2010 X B B B 0.05 0.1 0.15 0.2 0 45 90 135 180 225 270 315 0 - 2 2 - 4 4 - 6 6 - 8 8+ (m s -1 ) Sampling carried out at Tivoli Docks, Cork Harbour for three weeks (7-28/08/2008) R. M. Healy et al., Atmos. Chem. Phys. Discuss. 10, 1035-1082, 2010
  • 4. Instrumentation IAC Helsinki 30/08/2010 Instrument Measurement ATOFMS (TSI, 3800) Size-resolved single particle chemical composition SMPS (TSI, 3081) Particle number (20-700 nm) TEOM (Thermo, 1400a) PM2.5 Thermal-optical carbon analyser (Sunset, 3rd gen. field model) ECOC Sulfate analyser (Thermo, 5020 SPA) Particulate SO4 2-
  • 5. IAC Helsinki 30/08/2010 Data Analysis 1: Over 500,000 particle mass spectra were collected, imported into ENCHILADA1 and clustered using the K-means algorithm (K=50) 2: 50 clusters reduced to 14 ATOFMS classes; Peat, Coal, Wood, Sea salt, Shipping, Ca-traffic, EC-traffic, EC-phos, EC-MSA, EC-domestic, EC-background, EC-oil, ECOC, and Oligomer 3: ATOFMS counts for each class were sorted into hourly bins and used along with hourly averages of EC/OC, SO4 2- and hourly integrated SMPS particle counts for positive matrix factorisation (PMF) in order to reconstruct PM2.5 mass concentrations 1D. Gross et al., Environmental Modelling & Software 25, 760-769, 2010
  • 6. IAC Helsinki 30/08/2010 ATOFMS Results: Shipping R. M. Healy et al., Atmospheric Environment 43, 6408-6414, 2009 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 Ca+ V+ VO+ C2H3 + Na+ C+ C3 + Fe+ 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 SO3 - C2 - CN- HSO4 - C3 - C4 - 50 60 70 80 90 100 110 120 130 140 150 Na2Cl+ Na2Cl+Na2O+ 50 60 70 80 90 100 110 120 130 140 150 NaCl2 - NO3 - O2 - SO3 - NaCl- NaCl2 -/HSO4 - m/z m/z RelativeIntensity C3 + A B DC
  • 7. IAC Helsinki 30/08/2010 ATOFMS Results: Shipping 0 50 100 150 200 250 300 ATOFMScounts Date ATOFMS "Shipping" class 10 20 30 40 0 45 90 135 180 225 270 315 ATOFMS "Shipping" class
  • 8. IAC Helsinki 30/08/2010 ATOFMS Results: Shipping 200 150 100 50 0 ATOFMScounts 15:00 23/08/2008 16:00 17:00 18:00 19:00 20:00 21:00 22:00 Time 2 3 4 5 6 7 100 2 3 4 5 6 7 mobilitydiameter(nm) 5x10 5 4 3 2 1 0 (#cm -3 ) ATOFMS "Shipping" Class
  • 9. IAC Helsinki 30/08/2010 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C+ C3 + K+/C3H3 + C2H3O+ Na+ C2H3 + C5 + C4H2 + C4 + 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C2 - CN- C3 - CNO- NO3 - NO2 - HSO4 - SO3 -C4 - RelativeIntensity m/z 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C+ C3 + K+ C2H3O+ Na+ C2H3 + C5 + C4H2 + C4 + 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C+ C3 + K+ C2H3O+ Na+ C2H3 + C5 + C4H2 + C4 + m/z m/z 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C2 - CN- C3 - CNO- C4 - NO3 - NO2 - HSO4 - Cl- Cl- C5 - 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C2 - CN- C3 - CNO- NO3 - NO2 - HSO4 - Cl- Cl- C5 - C4 - RelativeIntensity 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C+ C3 + K+ Na+ K+ 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C+ C3 + K+ Na+ K+ m/z m/z 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 O- OH- C2 - CN- C3 - Cl- Cl- CNO- NO2 - C4 - NO3 - C2H3O2 - HSO4 - COOHCOO- C3H3O2 - KCl2 - 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 O- OH- C2 - CN- C3 - Cl- Cl- CNO- NO2 - C4 - NO3 - C2H3O- C2H3O2 - C3H3O2 - HSO4 - KCl2 - COOHCOO- RelativeIntensity RelativeIntensity ATOFMS Results: DomesticCombustion Coal Peat Wood
  • 10. IAC Helsinki 30/08/2010 ATOFMS Results: DomesticCombustion 0 50 100 150 200 250 0 100 200 300 400 500 600 700 800 ATOFMScounts(h-1) ATOFMScounts(h-1) Time coal peat wood
  • 11. IAC Helsinki 30/08/2010 ATOFMS Results: DomesticCombustion
  • 12. IAC Helsinki 30/08/2010 ATOFMS Results: Traffic 1200 EC-domestic Oligomer 0 500 1000 1500 2000 2500 ATOFMScounts(h-1 ) Time Ca-traffic EC-traffic EC-phos
  • 13. IAC Helsinki 30/08/2010 Semi-continuousResults OC EC SO4 2- PM2.5 Mean 1.13 0.61 0.49 9.67 Median 1.02 0.55 0.45 8.55 Maximum 3.41 2.90 2.14 49.80 Minimum 0.22 0.00 0.04 1.50 Hourly averaged values (µg m-3) 7-28/08/2008
  • 14. IAC Helsinki 30/08/2010 PMFResults Traffic Domestic Combustion Various Combustion Marine Long-range Shipping Quantitative measurements: OC mass 21 21 16 20 18 4 EC mass 43 20 18 5 11 4 Sulfate mass 9 11 40 23 15 2 Particle number (SMPS) 42 14 13 6 7 18 PM2.5 mass 23 5 11 14 13 1 ATOFMS classes: Coal 5 52 30 3 7 3 Peat 3 84 5 2 3 2 Wood 11 63 5 13 6 1 Sea salt 1 0 2 86 10 1 Shipping 0 0 0 0 0 100 Ca-traffic 83 0 0 4 8 4 EC-traffic 59 25 6 1 3 6 EC-phos 82 9 3 0 6 0 EC-MSA 1 0 3 6 90 0 EC-domestic 0 91 0 0 2 7 EC-background 28 18 35 1 11 6 EC-oil 52 24 24 1 0 0 ECOC 0 0 69 0 31 0 Oligomer 0 76 8 15 0 1 % Variable contributions to six-factor model and estimated % contribution to measured PM2.5 mass
  • 15. IAC Helsinki 30/08/2010 Conclusions 1: Unique mass spectral fingerprints and high time resolution of ATOFMS are suited to source identification and apportionment, representing a useful alternative to off-line chemical analysis of PM2.5 2: The major sources of PM2.5 in Cork Harbour during the summer are traffic and sea spray, followed by local combustion processes including a contribution from domestic solid fuel burning 3: Although shipping traffic contributes very little to PM2.5 mass concentrations, the contribution to particle number concentration is almost half that of traffic
  • 16. IAC Helsinki 30/08/2010 Acknowledgements Port of Cork for providing a suitable sampling site Higher Education Authority, Environmental Protection Agency and Science Foundation Ireland for providing funding for this research Thank you for your attention!
  • 19. 0 100 200 300 400 500 600 700 800 900 ATOFMS[NO3]-RelativeIntensity Time coal peat wood Hourly averaged signal for nitrate for the Coal, Peat and Wood ATOFMS classes for the 4 low wind speed events (11-12 August 2008, 13-15 August 2008 and 22-23 August 2008).
  • 20. IAC Helsinki 30/08/2010 Concentration-time profiles for PM2.5 *, SO4 2-*, organic carbon** and elemental carbon** for 07-28 August 2008. *Hourly averaged mass concentration. **2 hour averaged mass concentration. 3.0 2.0 1.0 0.0 µgm -3 07/08/2008 08/08/2008 09/08/2008 10/08/2008 11/08/2008 12/08/2008 13/08/2008 14/08/2008 15/08/2008 16/08/2008 17/08/2008 18/08/2008 19/08/2008 20/08/2008 21/08/2008 22/08/2008 23/08/2008 24/08/2008 25/08/2008 26/08/2008 27/08/2008 28/08/2008 Date 2.0 1.5 1.0 0.5 0.0 µgm -3 50 40 30 20 10 0 µgm -3 PM2.5 SO4 2- OC EC
  • 21. IAC Helsinki 30/08/2010 ATOFMS Results: Traffic 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 Ca+ VO+ C2H3 + Na+ C+ C3 + Fe+ 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 SO3 - C2 - CN- HSO4 - C3 - C4 - 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 Na2Cl+K+ Na2Cl+Na2O+ 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 NaCl2 - Cl- NO3 - NO2 - SO3 - Cl- NaCl- NaCl2 -/HSO4 -Na- O- m/z m/z RelativeIntensity RelativeIntensity 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 Ca+ Na+ C+ C3 + C4 + C5 + 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C2 - CN- HSO4 - C3 - C4 - C5 - m/z RelativeIntensity D 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 Ca2O+ Ca+ CaO+ CaOH+ C2H3 + m/z 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 PO2 - NO2 - HSO3 - CNO- NO3 - CN- PO3 - PO4 - RelativeIntensity C 0 10 20 30 40 C+ C3 + C2 + 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C+ C3 + C4 + C5 + C2 + m/z 0 10 20 30 40 50 60 70 80 90 100 110 120 130 140 150 C2 - CN- HSO4 - C3 - C4 - NO3 - PO3 - 0 10 20 30 40 C2 - CN- C3 - RelativeIntensity RelativeIntensity A K+ C3 + Na+ K+ C Ca-Traffic EC-traffic EC-phos
  • 23. IAC Helsinki 30/08/2010 Fig. 15: 5 day back-trajectories for air masses arriving at Cork Harbour on at 00:00 h on 10 (left), 14 (middle) and 26 August 2008 (right).