FAIRMODE meeting, Norrkoping, June. 20111 Institute for Environment and Sustainability SG4: Benchmarking.

Slides:



Advertisements
Similar presentations
Institute for Environment and Sustainability1 POMI Kick-off Meeting 07/03/2008.
Advertisements

Air Implementation Pilot Task 3. Assessing modelling activities Núria Castell and Bruce Denby NILU FAIRMODE Forum for air quality modelling in Europe.
Jenny Stocker, David Carruthers & Sam Royston Comments on DELTA version 3.2 with the ADMS-Urban London dataset & updates to the PASODOBLE Myair Model Evaluation.
An experience on modelling-based assessment of the air quality within the Air Quality Directive framework Ana Isabel Miranda, Isabel Ribeiro, Patrícia.
Applying the DELTA-FAIRMODE tool to support AQD: the validation of the TCAM Chemical Transport Model C. Carnevale, G. Finzi, A. Pederzoli, P. Thunis, E.
UK feedback on Delta V3.0 Presented by: John Stedman, Daniel Brookes, Keith Vincent, Emily Connolly 10 April 2013.
FAIRMODE SG4: Benchmarking & modelling quality objectives P. Thunis, JRC Antwerp,
AIR QUALITY INDICATORS Frank de Leeuw 8th Air Quality EIONET workshop 6-7 November 2003, Oslo.
S Larssen: PM-PP-Stockholm-Oct-2003.ppt slide 1 PM in Europe - State and past trends Emissions and concentration levels Steinar Larssen Norwegian Institute.
CO budget and variability over the U.S. using the WRF-Chem regional model Anne Boynard, Gabriele Pfister, David Edwards National Center for Atmospheric.
1 st Chimere workshop March 2005Stortini,Bonafe,Deserti,Minguzzi,Jongen Operational implementation of NINFA in Northern Italy ARPA Servizio IdroMeteorologico.
Three-State Air Quality Study (3SAQS) Three-State Data Warehouse (3SDW) 2008 CAMx Modeling Model Performance Evaluation Summary University of North Carolina.
Source apportionment of PM in the ADMS model David Carruthers Workshop on Source Apportionment of Particulate Matter Imperial College London Friday, 23.
PREV ’AIR : An operational system for large scale air quality monitoring and forecasting over Europe
University of Aveiro Final Meeting and Project Review 23/24 June 2003 Gdansk University of Aveiro Emissions and Air Quality Modelling Department of Environment.
1 Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling introduction model evaluation for Swedish - street/road stations -
Jenny Stocker, Christina Hood, David Carruthers, Martin Seaton, Kate Johnson, Jimmy Fung The Development and Evaluation of an Automated System for Nesting.
NCPP – needs, process components, structure of scientific climate impacts study approach, etc.
WG2 Meeting, SG4 Models Benchmarking SMHI, Norrkoping, 14 th June 2011 DELTA tool testing for a Portuguese City Ana Miranda and Helena Martins University.
PM Model Performance Goals and Criteria James W. Boylan Georgia Department of Natural Resources - VISTAS National RPO Modeling Meeting Denver, CO May 26,
DANMARKS MILJØUNDERSØGELSER AARHUS UNIVERSITET September 21, 2010 Helge Rørdam Olesen Fairmode: Some considerations on the Delta tool and model performance.
PM2.5 Model Performance Evaluation- Purpose and Goals PM Model Evaluation Workshop February 10, 2004 Chapel Hill, NC Brian Timin EPA/OAQPS.
The Euro- and City-Delta model intercomparison exercises P. Thunis, K. Cuvelier Joint Research Centre, Ispra.
Overview What we’ll cover: Key questions Next steps
EFFICIENT CHARACTERIZATION OF UNCERTAINTY IN CONTROL STRATEGY IMPACT PREDICTIONS EFFICIENT CHARACTERIZATION OF UNCERTAINTY IN CONTROL STRATEGY IMPACT PREDICTIONS.
Institute for Environment and Sustainability1 DELTA Tool Questionnaire - Feedback and main points for discussion FAIRMODE 4 th Plenary and Working Group.
The aim of this work was to create background and roadside maps of pollutant concentrations for Scotland and to compare these with similar maps created.
Norwegian Meteorological Institute met.no Contribution from MSC-W to the review of the Gothenburg protocol – Reports 2006 TFIAM, Rome, 16-18th May, 2006.
| Folie 1 Assessment of Representativeness of Air Quality Monitoring Stations Geneva, Wolfgang Spangl.
Integrated Ecological Assessment February 28, 2006 Long-Term Plan Annual Update Carl Fitz Recovery Model Development and.
Research Progress Discussions of Coordinated Emissions Research Suggestions to Guide this Initiative Focus on research emission inventories Do not interfere.
10 October 2008, Cavtat (CROATIA) – First Planery Meeting FAIRMODE1 IES - Institute for Environment and Sustainability Ispra - Italy
The role of modelling and FAIRMODE in the Directive review WG1 activity/discussion Bruce Rolstad Denby FAIRMODE 4 th Plenary, Norrkjoping Sweden June 2011.
Fairmode: Latest developments P. Thunis + Fairmode chairs & co-chairs + Fairmode Community.
Analysis of station classification and network design INERIS (Laure Malherbe, Anthony Ung), NILU (Philipp Schneider), RIVM (Frank de Leeuw, Benno Jimmink)
May 22, UNDERSTANDING THE EFFECTIVENESS OF PRECURSOR REDUCTIONS IN LOWERING 8-HOUR OZONE CONCENTRATIONS Steve Reynolds Charles Blanchard Envair 12.
Seasonal Modeling of the Export of Pollutants from North America using the Multiscale Air Quality Simulation Platform (MAQSIP) Adel Hanna, 1 Rohit Mathur,
Possible use of Copernicus MACC-II modeling products in EEAs assessment work Leonor Tarrasón, Jan Horálek, Laure Malherbe, Philipp Schneider, Anthony Ung,
Joint Research Centre the European Commission's in-house science service JRC Science Hub: ec.europa.eu/jrc 38th UNECE IWG PMP MEETING Non- exhaust particle.
FAIRMODE MEETING NORRKÖPING JUNE Session: The use of Receptor Models in Source Apportionment (coordinator C. Belis) General considerations.
Kick off meeting, 2008, Cavtat Guidance on the use of models for the European air quality directive An activity of WG1 FAIRMODE Bruce Denby 1*, Steinar.
13 / 10 / 2006 Uncertainty and regional air quality model diversity: what do we learn from model ensembles? Robert Vautard Laboratoire des Sciences du.
Comments from Austria D. Oettl, A. Kaiser et al. Antwerp,
HARMO13, 1-4June 2010, Paris, France1 Institute for Environment and Sustainability Procedure.
The FAIRMODE PM modelling guide Laurence ROUIL Bertrand BESSAGNET
Institute for Environment and Sustainability1 Date & Time 09: :30Status review and improvements  BaseCase (1) problem review and actions taken (20’)
EPA’s 8 th Conference on Air Quality Modeling Comments on Model Evaluation By Bob Paine, ENSR (Peer reviewed by the A&WMA AB-3 Committee)
Research Progress Discussions of Coordinated Emissions Research Suggestions to Guide this Initiative Focus on research emission inventories Do not interfere.
Evaluation of pollution levels in urban areas of selected EMEP countries Alexey Gusev, Victor Shatalov Meteorological Synthesizing Centre - East.
1 Černikovský, Krejčí, Volná (ETC/ACM): Air pollution by ozone in Europe during the summer 2012 & comparison with previous years 17th EIONET Workshop on.
SHERPA for e-reporting
High-resolution air quality forecasting for Hong Kong
Bruce Rolstad Denby FAIRMODE 4th Plenary, Norrkjoping Sweden June 2011
A New Method for Evaluating Regional Air Quality Forecasts
Progress in assessment of POP pollution in EMEP region.
Predicting Future-Year Ozone Concentrations: Integrated Observational-Modeling Approach for Probabilistic Evaluation of the Efficacy of Emission Control.
CONTRIBUTION OF NATURAL SOURCES AND SOURCE APPORTIONMENT (SG2)
M. Amann, W. Asman, I. Bertok, J. Cofala, C. Heyes,
Current activities WG2-SG3 Urban Emissions and Projections
Urban Emissions and Projections
QUALITY ASSURANCE OF MODELS
QUALITY ASSURANCE OF MODELS
J. Burke1, K. Wesson2, W. Appel1, A. Vette1, R. Williams1
FAIRMODE WG2 – SG4 activity
SG3 outcome General agreement on the check-list approach
Bruce Rolstad Denby FAIRMODE 4th Plenary, Norrkjoping Sweden June 2011
Data Extraction Facility
2nd plenary, Ispra 18 November 2009
MSC-E: Alexey Gusev, Victor Shatalov, Olga Rozovskaya, Nadejda Vulykh
Summary: TFMM trends analysis
Presentation transcript:

FAIRMODE meeting, Norrkoping, June Institute for Environment and Sustainability SG4: Benchmarking of air quality models

FAIRMODE meetind, Norrkoping, June Agenda Status DELTA: Template for performance reporting DELTA: Exploration mode Users feedback & discussion User’s presentations Discussion around the questionnaire Future Plans & deliverables for TSAP DELTA Inclusion of planning application Benchmarking service Ensemble Review of possible TSAP Deliverables

FAIRMODE meetind, Norrkoping, June SG4 – Presentations on the Questionnaire Short presentations (max 10 min) by: Ana Miranda (PT) David Carruthers (UK) Hans Backström (SE) Helge Olesen (DK) Marcus Hirtl (AT) Mihaela Mircea, Guido Pirovano (IT)

FAIRMODE meetind, Norrkoping, June Background

FAIRMODE meetind, Norrkoping, June Model results DELTA JRC USER Data Extraction Facility BENCHMARKING service Model performance Evaluation reports The benchmarking procedure

FAIRMODE meetind, Norrkoping, June Since the Oslo meeting (sep. 2010) - Document “ DELTA concepts” sent to SG4 participants (March 11) - Distribution of DELTA tool & utilities (about 20 users) - SG4 Web page created ( - Use of DELTA on different datasets (POMI, Madrid, London) - User feedback questionnaire

FAIRMODE meetind, Norrkoping, June Intended for rapid diagnostics by single users (at home) Focus mostly on surface measurement- model pairs  “independence” of scale Focus on AQD related pollutants on a yearly period (but AQ related input data also checked) Exploration and benchmarking modes The DELTA tool

FAIRMODE meetind, Norrkoping, June Agenda Status DELTA: Template for performance reporting DELTA: Exploration mode Users feedback & discussion User’s presentations Discussion around the questionnaire Future Plans & deliverables for TSAP DELTA Inclusion of planning application Benchmarking service Others (Ensemble…) Review of possible TSAP Deliverables

FAIRMODE meetind, Norrkoping, June Outline 1. Content of the performance report 2. Links between Target and more “traditional” indicators (an analysis based on 3 datasets) 3. A “first-guess” for criteria/goals 4. Comparison with RDE 5. Observation uncertainty 6. Proposed update to the report template

FAIRMODE meetind, Norrkoping, June Content of the performance report

FAIRMODE meetind, Norrkoping, June Should include a set of statistical indicators and diagrams complete enough to capture the main aspects of model performance but limited enough to fit in one page summary Keep a similar template for all pollutants and spatial scales (but differences in terms of criteria/gals). Restricted to AQD needs. Currently proposed for O3 8h daily max, NO2 hourly and PM10 daily. Developed (at least first) for assessment purposes Should include performances criteria and goals Content of the performance report (1) Constraints

FAIRMODE meetind, Norrkoping, June Criteria: Acceptable performance for a given type of application (e.g. PM: MFE=75%, MFB=+/-60%) Goal: Best performance a model should aim to reach given its current capabilities (e.g. PM: MFE=50%, MFB=+/-30%) Content of the performance report (2) RMSE/σ o R=0.7 OU MEF < 0

FAIRMODE meetind, Norrkoping, June MFB=0.67 Checks on data availability for each stations 75% for time averaging (e.g. 18h at least per day) 90% available on total (e.g. >328 days/year) Content of the performance report (3) 90% concept for indicators

FAIRMODE meetind, Norrkoping, June Links between Target and more “traditional” indicators (an analysis based on 3 datasets)

FAIRMODE meetind, Norrkoping, June Links between Target and more “traditional” indicators (1) Bias SigM/SigO R FAC2 CRMSE Target indicator = RMSE / SIgO

FAIRMODE meetind, Norrkoping, June monitoring sites suburban, urban and rural background 5 models: CHIMERE, TCAM, CAMX, RCG, MINNI Year:2005 Domain resolution:6x6km 2 O3 – PM10 10 monitoring sites urban background 1 model: WRF-CMAQ Year: 2007 Domain resolution: 1x1 km2 O3 – NO2 107 monitoring sites suburban/urban background, kerbside and roadside 1 model: ADMS Year: 2008 NO2 – O3 – PM10 Po - Valley Madrid London Examples on 3 datasets

FAIRMODE meetind, Norrkoping, June Based on real datasets, start by analysing how the bias criteria (MFB) proposed by Boylan and Russel (2005) compares to Target. Fix a criteria for the target indicator which is consistent with the MFB criteria Fix values for the other statistical indicators (R, StdDev ratio, FAC2) to be consistent with the assigned criteria on the Target value Methodology to fix “first guess” criterias Links between Target and more “traditional” indicators (3)

FAIRMODE meetind, Norrkoping, June T: 58% RDE: 83% How to connect Target to more accessible indicators? (3) EXAMPLE 1: Po_valley (PM10) Crit Target=1

FAIRMODE meetind, Norrkoping, June T: 32% RDE: 95% How to connect Target to more accessible indicators? (3) EXAMPLE 2: Po_valley (PM10) Crit Target=1

FAIRMODE meetind, Norrkoping, June T: 96% RDE: 100% How to connect Target to more accessible indicators? (3) EXAMPLE 3: London (PM10) Crit Target=1

FAIRMODE meetind, Norrkoping, June T: 70% RDE: 96% How to connect Target to more accessible indicators? (3) EXAMPLE 4: Po_valley (O3) Crit Target=0.8

FAIRMODE meetind, Norrkoping, June T: 66% RDE: 100% How to connect Target to more accessible indicators? (3) EXAMPLE 5: Madrid (O3) Crit Target=0.8

FAIRMODE meetind, Norrkoping, June T: 77% RDE: 94% How to connect Target to more accessible indicators? (3) EXAMPLE 6: London (NO2) Crit Target=1

FAIRMODE meetind, Norrkoping, June T: 60% RDE: 100% How to connect Target to more accessible indicators? (3) EXAMPLE 7: Madrid (NO2) Crit Target=1

FAIRMODE meetind, Norrkoping, June A “first-guess” for criteria/goals

FAIRMODE meetind, Norrkoping, June MFBTargetRFAC2SM/SO PM10Daily60%  1.0~0.5050%± 50% O38h30%  0.8~0.6550%± 50% NO21h30%  1.0~0.5550%± 50% A “first-guess” for criteria/goals (1) NOTE: Boylan and Russel MFB criteria is proposed based on urban to regional scale modelling (from 4 to 36 km spatial resolution) addresses only O3 and PM10

FAIRMODE meetind, Norrkoping, June A “first-guess” for criteria/goals (2) Different criteria are currently proposed for O3-8h, PM10-daily and NO2-hourly. Although spatial-scale and time average dependency are possible, they are not considered up to now (point of discussion) Scale is intended in terms of spatial resolution, linked to monitoring station type: Regional  Rural background Urban  Urban & suburban background Local  All urban stations (incl. roadside & kerbside) Criteria probably need to be developed for yearly averaged values Performance goals have arbitrarily been fixed to a 20% more stringent value 3 datasets is not ENOUGH!

FAIRMODE meetind, Norrkoping, June How do these criteria compare to RDE?

FAIRMODE meetind, Norrkoping, June RDE Target R FAC2 SM/SO MFB

FAIRMODE meetind, Norrkoping, June RDE Target R FAC2 SM/SO MFB

FAIRMODE meetind, Norrkoping, June RDE Target R FAC2 SM/SO MFB

FAIRMODE meetind, Norrkoping, June Station Osio Sotto, POMI (NO2 - RCG) Target: 2.19 MFB:73% FAC2:41% R:0.39 SigM/SigO:1.49 How these criteria compares to RDE? (2) RDE=11%

FAIRMODE meetind, Norrkoping, June Station EA1, London (NO2 - ADMS) Target: 0.82 MFB:8% FAC2:89% R:0.73 SigM/SigO:1.14 How these criteria compares to RDE? (3) RDE = 56%

FAIRMODE meetind, Norrkoping, June About observation uncertainty

FAIRMODE meetind, Norrkoping, June S0RMSE / SO O3 PO LOND MAD NO2 PO LOND MAD PM10 PO LOND MAD About observation uncertainty (1) RMSE/S0 S0 PollutantOU O3, NO215% PM1025% AQD

FAIRMODE meetind, Norrkoping, June NO2 O3 PM10 ADMS, London, 2008 About observation uncertainty (2)

FAIRMODE meetind, Norrkoping, June Proposed update to the report template

FAIRMODE meetind, Norrkoping, June ✘ SigO/SigM ✓ ✘✘ SigO > SigM SigO < SigM Proposed update to the report template ✘

FAIRMODE meetind, Norrkoping, June Agenda Status DELTA: Template for performance reporting DELTA: Exploration mode Users feedback & discussion User’s presentations Discussion around the questionnaire Future Plans & deliverables for TSAP DELTA Inclusion of planning application Benchmarking service Others (Ensemble…) Review of possible TSAP Deliverables

FAIRMODE meetind, Norrkoping, June Exploration : Time selection (period, averaging time, season, day/night-time, max/min/mean) Information overlay (models, scenarios, variables, stations) Spatial analysis (color codes vs. 2D maps) DELTA: Exploration mode (1)

FAIRMODE meetind, Norrkoping, June DELTA: Exploration mode (2)

FAIRMODE meetind, Norrkoping, June Model V1 vs. Model V2 DELTA: Exploration mode (3) Upgrade

FAIRMODE meetind, Norrkoping, June DELTA: Exploration mode (4) Upgrade

FAIRMODE meetind, Norrkoping, June Agenda Status DELTA: Template for performance reporting DELTA: Exploration mode Users feedback & discussion User’s presentations Discussion around the questionnaire Future Plans & deliverables for TSAP DELTA Inclusion of planning application Benchmarking service Others (Ensemble…) Review of possible TSAP Deliverables

FAIRMODE meetind, Norrkoping, June Agenda Status DELTA: Template for performance reporting DELTA: Exploration mode Users feedback & discussion User’s presentations Discussion around the questionnaire Future Plans & deliverables for TSAP DELTA Inclusion of planning application Benchmarking service Others (Ensemble…) Review of possible TSAP Deliverables

FAIRMODE meetind, Norrkoping, June Agenda Status DELTA: Template for performance reporting DELTA: Exploration mode Users feedback & discussion User’s presentations Discussion around the questionnaire Future Plans & deliverables for TSAP DELTA Benchmarking service Others (Ensemble…) Review of possible TSAP Deliverables

FAIRMODE meetind, Norrkoping, June DELTA developments Short term (Autumn 2011) Flexible use of benchmarking mode and production of “pdf” or postscript reports On-click mouse information Windows/Linux portability Station grouping mode Longer term ( ) Inclusion of planning applications Extension of benchmarking for annual averages (?) Inclusion of PM2.5

FAIRMODE meetind, Norrkoping, June Require a series of simulations with fixed emission reductions for main precursors (NOx, VOC, NH3, SO2, PPM) and analyze difference in behavior. Problem: No observations available Reference model ?  Joint exercices 2.Analysis of spatio-temporal emission patterns in provided data (e.g week vs. week-end day, DEFRA 2011)  DELTA expl. Mode (Links with SG3) Model responses to emission reductions depend on the geographical location, the model scale, meteorological year… DELTA developments

FAIRMODE meetind, Norrkoping, June Agenda Status DELTA: Template for performance reporting DELTA: Exploration mode Users feedback & discussion User’s presentations Discussion around the questionnaire Future Plans & deliverables for TSAP DELTA Benchmarking service Others (Ensemble…) Evaluation Datasets Review of possible TSAP Deliverables

FAIRMODE meetind, Norrkoping, June Model results DELTA JRC USER Data Extraction Facility BENCHMARKING service Model performance Evaluation reports DELTA Benchmark Case & Report DB Model info Deadline: end 2012

FAIRMODE meetind, Norrkoping, June Agenda Status DELTA: Template for performance reporting DELTA: Exploration mode Users feedback & discussion User’s presentations Discussion around the questionnaire Future Plans & deliverables for TSAP DELTA Benchmarking service Others (Ensemble…) Evaluation Datasets Review of possible TSAP Deliverables

FAIRMODE meetind, Norrkoping, June Deliverables for TSAP review Common template for reporting model performances for O3, NO2 and PM10 as complement to the current RDE indicator. Recommendations on quality objectives (performance criteria) to be achieved Benchmarking procedure including the following elements: DELTA  Benchmarking service  ENSEMBLE + data preparation facility

FAIRMODE meetind, Norrkoping, June Annexes

FAIRMODE meetind, Norrkoping, June SpeciesMetricCriteriaGoal Boylan and Russel, 2005, EPA report 2007 Main PM constituents (> 30% total mass), PM2.5 MFE MFB 75% ±60% 50% ±30% Minor PM constituents (< 30% total mass) Exp variations to reach 100% / 200% at 0 concentrations OzoneMFE MFB 35% 15% Evaluating the Performance of Air Quality Models, AEA (2009) Any pollutantFAC2 NMB Half points within -0.2 < MFB < 0.2 Air quality model performances evaluation, Chang et Hanna (2004) NOx, CO, PM10FAC2 FB NMSE Half points within -0.3 < FB < 0.3 NMSE < 4 Air Quality (Regional scale modelling) Criteria & goals

FAIRMODE meetind, Norrkoping, June RDE takes closest to exceedance values. In the case the max value does not exceed the threshold, it is relative to the closest one. Lack of comparability of this measure among stations MFB can be taken as 60%,30% … No change because low values are within range of stable MFB No assumption on station representativness Screen monitoring data and drop extreme artificial events (e.g. fireworks) Adapt templates for annual values How these criteria compares to RDE? (2)

FAIRMODE meetind, Norrkoping, June SG4 participants - EoI PersonInstitutePersonInstitute Marco BEDOGNIAMAT (IT)Jana MATEJOVICOVAHMI (SK) Bertrand BESSAGNETINERIS (FR)Anna MIRANDAUniversity of Aveiro (PT) David CARRUTHERSCERC (UK)Dietmar OETTLGovernment of Styria (AT) Koen DE RIDDERVITO (BE)Christakis PAPADOPOULOSDLI (CY) Dick DERWENTAEA (UK)Guido PIROVANOERSE (IT) Hilde FAGERLIMet Inst (NO)Peter ROBERTSCONCAWE (BE) Alenka FRITZELMinistry of Environment (SI)Martijn SCHAAPTNO (NL) Stefano GALMARINIEC-JRC, IspraCamillo SILIBELLOARIANET (IT) Emilia GEORGIEVAEC-JRC, IspraAlexandros SIRAKOSUOWM (GR) Maria GONCALVESBSC (ES)Philippe THUNISEC-JRC, Ispra Pernige GRENNFELTIVL (SE)Keith VINCENTAEA (UK) Ari KarppinenFMI (FI)Rahela ZABKARUniversity of Ljubljana (SI) Fernando MARTINCIEMAT (ES)John BARTZISUOWM (GR) Jose BALDASANOBSC (ES)Nicolas MOUSSIOPOULOSAUT (GR) John DOUROSAUT (GR)Leonor TARRASONNILU (NO) Bruce DENBYNILU (NO)H. BECKSTROEMSMHI (SE) Joanna STRUZEWSKAWOT (PL)Nutthida KITWIROONHERTS (UK) Marcus HirtlZAMG(AT)Ruben BeijkRIVM (NL) Joost WesselingRIVM (NL)

FAIRMODE meetind, Norrkoping, June User Name Giudo Pirovano Mihaela Mircea Marcus Hirtl Addo Van Paul Dietmar Oettl Rafael Borge David Carruthers Suzanne Yongen Kevin Delaney Stefan Andersson Claudio Carnevale Ana Miranda Helge Olesen User affiliation RSE ENEA ZAMG RIVM Graz University UPM CERC VITO Irish EPA SMHI Brescia University Aveiro University DMU QuestionnaireV V V v x ? v v v v v V x PresentationV V V x x ? v x ? v x V v