CEN/TC Some open issues Ari Karppinen Athens 6/2017 How to use - - PowerPoint PPT Presentation

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CEN/TC Some open issues Ari Karppinen Athens 6/2017 How to use - - PowerPoint PPT Presentation

CEN/TC Some open issues Ari Karppinen Athens 6/2017 How to use MQO in real life ? Station representativeness Demonstration of eqivalence Minimum number of stations needed Focus area vs. validation area Example:Modelling system -


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CEN/TC

Some open issues

Ari Karppinen

Athens 6/2017

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How to use MQO in real life ?

  • Station representativeness
  • Demonstration of eqivalence
  • Minimum number of stations needed
  • Focus area vs. validation area
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ECMWF HIRLAM (7.5) HARMONIE (2.5) LAPS;PALM

Weather prediction models Dispersion models - long-range, regional Dispersion and effects models – urban, local

PALM, LESCAPE (DNS-code development)

SILAM LRT, meso-scale, radioactivity , pollen

Example:Modelling system - FMI

OSPM (NERI), street canyon UDM-FMI, urban CAR-FMI, roadside

HILATAR LRT, meso-scale

Aerosol process models: SALSA(UH,UKU,FMI) SILAM-APMs MPP-FMI, Meteorological pre-processing model ESCAPE, chemical accidents BUOYANT, fires EXPAND (FMI, YTV) population exposure

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”Ideal” situation

Validation area = whole country Measurements used for assesment of the modelling system = all stations available (~150) Focus area = any area inside the country Number of stations in focus area irrelevant (?!)

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Typical situtation

  • Different model for different regions
  • Different/completly separate models for e.g. urban vs. rurual areas

Challenge : number of stations available for evaluation (taking into account the type of model) very limited => definition of minum number of stations needed for model evaluation Suggestions: ~5 , not based on any statistical jsutification , but more on experince/the real/existing status with measurements

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Some additional comments

Certain types of models are still ”automatically” left out from this type of evaluation (even without discussing the problems with long term time series /statistics): e.g. CFD/LES modelling of urban areas UNTIL the measurement networks are able to support these very high resolution models .. Or.. eg. Wind-tunnel validation would be ”accepted” as a feasible oprtion for Validating these

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Data assimilation

Models utilizing data assimilation or data fusion need to have clear guidance for proper evaluation: multitude of different assessment methods (leave n-out/bootstrapping etc..) Good: don’t need to invent anything really new Bad: not trivial to ”force” a single evaluationmethod , which would be the ¨optimal” choice for all different DA/DF-modelling system Models which take full use of the available measurement data will be

  • f fastly growing importance everywhere

<-> compare with opreative meteorological models : any ”reasonable” model uses heavily data-assimilation Additional concern: lot of modelling sytems use ”hidden” data-assimilation ..e.g. bias –correction -> should we jsut accept thtat this is ”feature” of the model,

  • r should we evaluate teh mdoel without bias-correaction ?!
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Operational modelling system

8 FMI-ENFUSER

(runs every 1-6h)

Information extraction

(every 10 minutes)

Calibration update

(1-4 times per year)

Model output

(figures, animations, gridded data, etc)

Web Portal For selected cities in Finland FMI-ENFUSER produces high resolution (15x15 m) AQ information

  • Includes AQ forecasts for the next 12-48 hours
  • Model data accessible through a Web Portal

NO2, PM2.5, PM10, O3, AQI

Amazon Web Service, HerokuApp, Dropbox

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Online /real-time evaluaton

29.6.2017

9

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Some concerns about the delta-formulation: beta-parameter

  • In order to assess and classify model quality

in a scientific way, a criterion based only on β or β90 does not seem sufficient.

  • There are many situations where an

assessment using only β or β90 will lead to disputable or simply wrong classifications, compared to an assessment based on standard regression techniques.

  • Requiring values for β or β90 less than 2 in

the MQO will result in more possibly “wrong” assessments.

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Some concerns about the delta-formulation : normality of residuals)

  • In practically all cases the tail of the distribution

was “long” and sometimes also skewed.

  • There is a larger possibility of outliers.
  • The usual assumption that 95% of residues is

between ±2 times the standard deviation may not hold.

  • Determining the meaning of this finding for the

MQO requires more tests and research …

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Some concerns about the delta-formulation ( temporal and spatial shift)

NO2, Germany, ½year switch +12 h, switch

PM10, Germany, ½year switch +12 h, switch O3, Germany, ½year switch +12 h, switch

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Some concerns about the delta-formulation ( temporal and spatial shift)

PM10, Germany, correct location vs. wrong location

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  • The shape of the diurnal/seasonal variation is crucial: different

pollutants have completely different sensitivity to temporal shift : e.g O3 very sensitive whereas NO2/PM10 not for this specific tested shift

  • Additional systematic analysis is needed e. g.:
  • more drastic temporal shift e.g.randomly distribute the time

dimension of the modeled concentration field

  • more drastic spatial shift e.g spatial averaging of the modeled

concentration field

  • optimal stringency of MQI und MPI with respect to spatial and

temporal shift should be clarified (long-term vs short-term, different pollutants)

Preliminary conclusions ( temporal and spatial shift)

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Summary

  • CEN/TC 264/WG 43 has still several interesting open issues

to discuss, study & finally close

  • Reasonable amount of studies & work & discussions still

needed before we can propose the final suggestions for model evaluation standards

  • Some of the open issued are highly relevant/tightly

connected to FAIRMODE/DELTA tool development