Non-exhaust contributions to PM levels in 5 EU cities. 39 th PMP Meeting 9-10 March 2016

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Non-exhaust contributions to PM levels in 5 EU cities 39 th PMP Meeting 9-10 March 2016

Testing and Development of air quality mitigation measures in Southern Europe Duration: 2012-2016 AIRUSE Coordinator CSIC, Spanish Research Council Associated beneficiaries DEMOKRITOS, Greece University of Aveiro, Portugal University of Florence, Italy Institute of Ceramic Technology, Spain ARPA Lombardia, Italy University of Birmingham, UK

OBJECTIVES http://airuse.eu/media/airuse-en.mp4 Characterizing similarities & differences in PM sources & contributions across Southern EU (Porto, Barcelona, Milan, Florence and Athens) Develop, test and propose specific and non specific measures to abate urban ambient air PM in Southern EU, to meet AQ standards & to approach WHO guidelines. Specific PM mitigation measures Street washing & dust suppressants for road dust Biomass burning Industrial emissions LEZ, eco efficient vehicles, labelling, shipping, http://airuse.eu http://airuse.eu/en/outreach-dissemination/reports/

Methods Urban background sites : Barcelona, Porto, Florence, Athens January-December 2013 (1/3 days) Traffic sites: Barcelona, Porto, Florence, Athens Intensive campaigns Barcelona (UB) 4

Milan (UB) Athens (SUB) Florence (UB) Porto (TR)

Thermal optical analysis:ec, OC Sample treatment PM 10, PM 2.5 ICP AES: Al, Ca, K, Na, Mg,.. Ion Chromatography: NO 3, Cl, SO 4=,NH 4 + ICP MS: Li,Be,Sc,Ti,V,Cr,Mn, Co, Ni, Cu, Zn, Ga, Ge, As, Se, Rb,.. Levoglucosan for biomass burning Inorganic tracers (carbonate) for African dust Intercomparison with XRF, PIXE >2000 filters analyzed 6

PMF: positive matrix factorization x ij p k 1 g ik f jk e ij i=1,2,,m j=1,2,,n Q m n i 1 j 1 x ij p g ik k 1 2 ij f jk 2 USEPA PMF v5 No need of full source profiles Partial information about sources can be used

3 traffic sources identified Fe at all sites Ca in BCN EC in POR, MLN and FI S in ATH OC/EC: <1 at POR-TR 1.8-3.7 at UB sites 16.4 at ATH-SUB (low diesel) Mainly NH 4 NO 3 and OC NaNO 3 in ATH-SUB

PM10: Annual mean Total traffic: 1 st source at all sites 22-36% of PM10 Non-exhaust: 1.8-3.4 µg/m 3 9-11% of PM10

Days with >50 µgpm10/m 3 Non-exhaust: 2.2-11.8 µg/m 3 3-14% of PM10

Total traffic: PM2.5: Annual mean 1 st source at MLN, POR and FI 2 nd source, at BCN and ATH 26-39% of PM2.5 (22% ATH) Non-exhaust: 0.2-2.6 µg/m 3 1-9% of PM2.5

PM10 At background PM10, Exhaust and Non-exhaust contributions are nowadays similar PM2.5 In PM2.5 Exhaust generally dominates

Time variability Year Week Exhaust Non-exhaust Nitrate

Contribution to elements/compounds Athens SUB Barcelona UB Porto TR

Can we separate better? Comparison with experimental profiles 1-hour resolved measurements

Amato et al., 2011, 2012, 2014, 2016 Experimental profiles: Road dust Road dust Loading mg/m 2 40 50 35 30 45 25 20 15 40 10 5 35 rd -10 0 10 20 30 longitude 16 IDPS: Inhalable Deposited Particle Sampler (CSIC patent)

Experimental profiles: Road dust

URBIS model (Amato F., Zandveld P. et al., 2016) Urban and street level modelling

Brake pads Tires % UK BRAND A UK BRAND B US BRAND ES BRAND DE BRAND JP BRAND FR BRAND TC 28 NA 26 28 32 83 79 Al 0.5 1 3.2 1.6 2.6 0.1 0.1 Ba 6.9 0.1 6.7 3.9 3.7 0.001 0.0015 Ca 0.5 0.3 1.7 4.3 2.1 1.3 0.5 Cu 0.003 11.8 2.6 0.02 1 0.0005 0.0007 Fe 45.6 26 13.2 23.6 27.4 <DL <DL K 0.1 <DL 0.4 0.1 0 <DL 0.1 Mg 1.3 0.8 3.8 0.6 0.6 <DL <DL Mn 0.2 <DL 0.1 1.5 0.1 0.0003 0.0003 Na <DL <DL 1 0.1 0.1 <DL <DL S 1 1.9 1.9 3.3 2.4 1.2 1.3 mg/kg Hg <DL 0.1 0.1 2.1 0.2 NA NA Li 1.4 2 3.5 1.9 1.4 1 <DL Ti 686 335 905 489 396 31 17 V 179 40 17 26 47 4 4 Cr 230 2834 185 1276 64 1 2 Co 24 10 11 13 20 80 94 Ni 47 33 50 72 69 <DL <DL Zn 36 14862 5717 1778 761 19849 15073 Ga 8 6 5 4 5 <DL <DL Ge 2 4 2 1 1 <DL <DL As 9 8 23 10 120 1 1 Se <DL 7 12 <DL 12 <DL <DL Rb 31 5 29 16 1 1 3 Sr 696 26 719 763 1371 18 3 Y 1 16 16 7 2 <DL <DL Zr 13 950 2337 73 23 1 1 Nb 2 <DL 2 136 9 <DL 1 Mo 4 3093 86 13 167 <DL 1 Cd <DL 23 2 <DL 2 3 2 Sn 1 10 342 41 148 3 2 Sb 12 6944 15916 30 64 12 2 Cs 1 1 1 <DL <DL <DL <DL La 3 <DL 8 41 2 2 4 Ce 5 <DL 14 56 5 <DL 1 Hf <DL <DL 45 1 <DL <DL <DL Pb 159 7 175 39 261 20 26 Bi <DL <DL 36 <DL 9 <DL 1 T h 1 4 4 4 <DL <DL <DL U <DL 4 4 1 <DL <DL <DL W <DL <DL <DL 19 1 <DL <DL Experimental profiles: Brake pads and Tires

PMF profiles vs Experimental profiles 30 40 50 60 70 80 90 100 BCN-UB Porto 20 FI-UB Brake ES Brake 10 Brake MLN US POR-TR D -UB Bike Brake UK Mean brake Ca 100 90 80 70 60 50 40 30 20 10 Fe Zn x 10 10 Florence Athens ATH-SUB 20 Barcelona Mean road dust 30 40 PMF Brake pads Tires Road dust 50 60 70 80 90 Tire JP brand Mean tires Tire FR brand

1-hour resolution measurements Streaker Sampler PIXE analysis PM 2.5 PM 2.5-10 21

Hourly measurements Road dust

Athens ATH-SUB

Hourly measurements Metallurgy Biomass burning

Conclusions 1. Traffic is 29-36% of PM10 (22% ATH), 26-39% of PM2.5 (22% ATH) 2. Non-exhaust is 9-11% of PM10 (1.8-3.4 µg/m 3 ), comparable to exhaust 3. Non-exhaust is the main source of Cu, Fe, Sb, Zn, Cr, Ba, Sn, Ni 4. In PM2.5, exhaust contribution generally dominates 5. Non-exhaust burden generally increases during PM10 exceedances 6. Non-exhaust contribution is more related to: Resuspension (in Barcelona and Athens) Brake wear (in Porto, Florence, and Milan)