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Risks, challenges and mitigation actions in the APICE partners’ area: between the scientific findings and new governance models - Genoa M.C. Bove, P. Brotto,F. Cassola, E. Cuccia, D. Massabò, A. Mazzino, P. Prati Department of Physics – University of Genoa.
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Risks, challenges and mitigation actions in the APICE partners’ area: between the scientific findings and new governance models - Genoa M.C. Bove, P. Brotto,F. Cassola, E. Cuccia, D. Massabò, A. Mazzino, P. Prati Department of Physics – University of Genoa Final conference – Venice, 8th November 2012
APICE scientific issues: the case of Genoa Main goal: to provide Authorities and Stakeholders with a reliable tool to study and forecast air quality: a “Chemical Transport Model, CTM” Methodology (shared with all the Partners): • “picture” of air quality (i.e. PM2.5) with a 1-year monitoring campaign Source Apportionment (SA). • CTM assessment with updated emission data • Check of CTM vs. real-world measured data • Comparison of SA by CTM and monitoring campaign
Monitoring campaign Site3: Bolzaneto Intensive campaign (May-Oct 2011) after prevailing meteo conditons analysis Site2: Multedo Site1: C.So Firenze PORT
PM2.5 levels B M F • The PM2.5 level is almost the same in the three sites • The correlation between PM2.5 time series is stronger for the sites much closer to the port Main PM2.5 sources: at “regional” scale
PM2.5 averageapportionment: Corso Firenze (14 ± 5) %
PM2.5 averageapportionment: Multedo (12 ± 4) %
PM2.5 averageapportionment: Bolzaneto (9 ± 3) %
PM2.5 apportionment at a glance Basically: ship emissions
Temporalbehaviourofshipemissions Many ferries to the Islands
Meteorological preprocessor: WRF 3-domain configuration (10 km + 3.3 + 1.1 km) Simulations driven by NCEP GFS fields (0.5°) 24-hr-long simulations, hourly outputs, year 2011 10
Chemical transport model: CAMx Outer domain covering Western and Central Europe (10 km resolution) City area 2-way nesting procedure Inner domain – focus on local area 47x47 grid points 1.1 km resolution Harbor area Pollutants: NOx, SOx, CO, PM…. • Maritime sector (harbour activities) • Road transport • Industry • Non-industrial combustion plants • Other sources (including natural emissions) PM source apportionment approaches: Zero-out CAMx PSAT routine 11
Emission data • Large-scale anthropogenic emission data provided by AUTH (TNO data processed through the MOSESS code) • Natural emissions obtained processing WRF outputs with the NEMO code (developed by AUTH) • Updated (2010) harbour emission data calculated by Techne Srl (provider of Province of Genoa) according to CORINAIR Guidebook 2011 (no disaggregation for different harbour activities contribution available) • Local gridded emission data provided by Liguria Region (reference year 2008): • 1 km spatial resolution • hourly temporal resolution • SNAP sectors disaggregation
CTM source apportionment results (zero-out) NOx PM2.5 Contribution of harbour activities (%)Summer 2011 Contribution restricted to the area around the harbour (expecially for PM2.5) 16
CTM source apportionment results (zero-out) PM2.5 NOx Contribution of road transport (%)Summer 2011 Contribution to concentrations over the whole city 17
Harbor activities contribution to PM2.5 concentrations CTM vs Receptor models
Future scenario analysis: PM2.5 Scenario 1 – 2020 without mitigation actions +2 % -20 %
Future scenario analysis: PM2.5 Scenario 2 – 2020 with S % reduction in fuels - 5 % - 35 %
Future scenario analysis: PM2.5 Scenario 3 – 2020 with S % reduction in fuels and cold ironing of container and ferries terminal - 5 % - 40 %
Summary A quite complete picture of PM2.5 levels and sources for the year 2011 has been obtained thanks to a considerable experimental effort A CTM model has been implemented and put in operation: validation vs. measured data pretty good Source apportionment by real-world data + receptor model (PMF) and CTM (WRF+CAMx) in fair agreement Future scenarios according to stakeholders inputs and APICE methodology completed (reference year 2020)