Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

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1 Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling introduction model evaluation for Swedish - street/road stations - urban background stations discussion and conclusions by L. Gidhagen, G. Omstedt and S. Andersson

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Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling. introduction model evaluation for Swedish - street/road stations - urban background stations discussion and conclusions. b y L. Gidhagen, G. Omstedt and S. Andersson. Indicators for model quality. - PowerPoint PPT Presentation

Transcript of Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

Page 1: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

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Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

• introduction• model evaluation for Swedish

- street/road stations- urban background stations

• discussion and conclusions

by L. Gidhagen, G. Omstedt and S. Andersson

Page 2: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

Model quality objectives (uncertainty) as described in the AQ directive

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Modellinguncertainty

NO2 PM10

Hourly 50 % -Daily average 50 % -Annual average 30 % 50%

p

ppO

MORPEMRPE

max)max(

LVMO

RDEMRDE LVLV max)max(

The uncertainty of modelling estimation is defined as the maximum deviation between the measured and calculated concentration levels for 90 % of individual monitoring points, without taking into account the timing of the events. The average annual modelling uncertaintyfor NO2 is defined as ±30% and for percentiles ±50%

Fairmode http://fairmode.ew.eea.europa.eu/

Op and Mp are the observed and modelled concentrations at the percentile (p)OLV and MLV are the closed observed and measured concentration to the limit valueconcentration (LV)

Indicators for model quality

Page 3: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

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Gidhagen, L., Johansson, H. and Omstedt, G., 2009: SIMAIR - Evaluation tool for meeting the EU directive on air pollution limits. Atmospheric Environment, 43, 1029-1036, doi:10.1016/j.atmosenv.2008.01.056.Andersson, S. och Omstedt, G., 2009: Validering av SIMAIR mot mätningar av PM10, NO2 och bensen. Utvärdering för svenska tätorter och trafikmiljöer avseende år 2004 och 2005. SMHI Meteorologi, Nr. 137, 125 pp. (In Swedish).

SIMAIR

Model validation in Sweden

~ 30 road/street stations~ 20 urban background stations

Page 4: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

Validation performed using both RPE and RDE Swedish EPA recommends the use of RPE for quality check of hourly (NO2) and

daily (PM10, NO2) values. Swedish EPA supports FAIRMODE recommendation to use, for annual mean

values, the RDE calculation when observed value is low compared to limit value. For high observed annual mean values, RPE can be used.

We are left with some confusion, e.g.:- Not clear when to use RDE or RPE- Not clear how the 90% of the station comparisons are selected: - How big can the area be (entire Sweden)? - Should the comparison include only one specific year or can we include comparisons for the same station but for two different years?- Why is max(RPE) or max(RDE) selected, would not median be more useful? Or both?

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Validation results from 2004 and 2005

Page 5: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

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Model simulations of PM10 for street level show acceptable quality, even for 98-percentiles

Differences MRPE and MRDE?

Validation PM10 from 2004 and 2005

Page 6: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

City/ street/yearmeasured modelled RPE RDE measured modelled RPE RDE

Landskrona/Eriksgatan, 2004 23,8 16,6 0,30 0,18 41,1 26,2 0,36 0,35Landskrona/Eriksgatan, 2005 24,2 19 0,21 0,13 43 28,4 0,34 0,37Helsingborg/Malmöleden, 2005 22,4 18 0,20 0,11 38 27,5 0,28 0,23Kristianstad/V,Boulevard, 2004 26,8 17,1 0,36 0,24 54,9 26,7 0,51 0,50Kristianstad/V,Boulevard, 2005 36,5 22,8 0,38 0,34 81 38,5 0,52 0,45Nässjö/Brogatan, 2004 25,8 21,9 0,15 0,10 64,4 38,9 0,40 0,30Norrköping/Kungsgatan, 2004 17,8 25,7 0,44 0,20 37,7 46,4 0,23 0,14Norrköping/Ö,Promenad, 2004 22,9 24,7 0,08 0,05 52,8 43,2 0,18 0,22Norrköping/Ö,Promenad, 2005 27,7 26,9 0,03 0,02 63 58,1 0,08 0,04Norrköping/Söderleden, 2005 19,3 21,2 0,10 0,05 44,9 40,7 0,09 0,09Göteborg/Gårda, 2005 29,6 32 0,08 0,06 55 61,5 0,12 0,07Karlstad/Hamngatan, 2005 22,8 21,6 0,05 0,03 45,8 47,9 0,05 0,01Västerås/Kopparbergsv, 2005 25,3 19,4 0,23 0,15 51,3 33,7 0,34 0,39Västerås/Stora gatan, 2005 27,5 19,1 0,31 0,21 59,9 34,6 0,42 0,41Västerås/Vasagatan, 2005 23,6 14,5 0,39 0,23 43,5 26,7 0,39 0,44Sollentuna/Turebergsl, 2004 18,5 14,5 0,22 0,10 32,7 25,5 0,22 0,31Sollentuna/Turebergsl, 2005 20,2 14 0,31 0,16 37,6 25,7 0,32 0,29

max RPE/ max RDE 0,39 0,24 0,51 0,45median RPE/ median RDE 0,22 0,13 0,32 0,30

Annual mean 90-percentile daily mean

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Validation PM10 from 2004 and 2005 using RPE and RDE

With RDE the quality is OK, with RPE it is almost OK (although MRPE for daily PM10 is still not defined)

Page 7: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

RPE and RDE for PM10

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There are often a few “poor” stations where measurement errors or bad siting (low representativeness) can be suspected

Could med(RPE) and med(RDE) be a better alternative?

Same station

Page 8: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

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Examples for PM10: How will RPE differ from RDE?

Annual mean:RPE = 1%RDE = 6%

Annual mean:RPE = 30%RDE = 18%

Annual mean:RPE = 44%RDE = 20%

Hornsgatan/Stockholm year 2000 Kungsgatan/Norrköping year 2004

Eriksgatan/Landskrona year 2004

Graphs illustrate RPE and RDE for daily 90-percentiles

Page 9: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

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Modell evaluation of NO2 at street/road level

Model simulations of NO2 for street level show acceptable quality, even for hourly values

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Validation NO2 from 2004 and 2005 using RPE and RDE

City/ street/yearmeasured modelled RPE RDE measured modelled RPE RDE measured modelled RPE RDE

Helsingborg/Drottningg,, 2004 27,9 36,3 0,30 0,21 58,8 80,6 0,38 0,37 80,5 97,6 0,20 0,21Kristianstad/V,Boulevard,, 2004 18,6 22,3 0,20 0,09 35,8 40 0,05 0,12 - - - -Kristianstad/V,Boulevard,, 2005 17,6 20,1 0,14 0,06 46,2 37,8 0,10 0,18 - - - -Göteborg/Gårda, 2004 46,7 34,1 0,27 0,32 84,8 75,6 0,19 0,11 109,4 109,4 0,06 0,00Göteborg/Gårda, 2005 46,6 30,1 0,35 0,41 92 69,9 0,22 0,24 109,4 94,5 0,17 0,14Göteborg/Haga, 2004 42 32,8 0,22 0,23 81,5 66,7 0,16 0,18 104,1 85,2 0,20 0,18Göteborg/Haga, 2005 40,8 29,2 0,28 0,29 86 52,8 0,27 0,39 107,6 66,6 0,34 0,38Göteborg, Mölndal, 2004 28,1 30,3 0,08 0,06 66,2 70,4 0,13 0,06 88,5 101,7 0,14 0,15Uppsala, Kungsgatan 27,2 28,5 0,05 0,03 51 57,1 0,12 69,6 81,7 0,17Uppsala, Kungsgatan2 37,4 37,3 0,00 0,00 64,6 66,9 0,04 88,9 90,4 0,02Malmö, Amiralsgatan 39,4 41,9 0,06 0,06 71,8 72,4 0,01 98 84,1 0,14

RPE max/ RDE max 0,30 0,32 0,38 0,37 0,34 0,38RPE median/ RDE median 0,20 0,09 0,18 0,12 0,19 0,15

Annual mean 98-percentile daily mean 98-percentile hourly mean

Daily and hourly percentiles OK, annual means almost OK

Page 11: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

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Improvements in the model can be demonstrated byimproved RPEThe current quality objectivesare still not fully compliant in urban background annual mean values

BUM new:MRPE annual mean = 0.40MRPE 98-percentile daily mean = 0.48MRPE 90-percentile hourly mean = 0.49

Modell evaluation of NO2 in urban background using RPE

Page 12: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

Example: SIMAIR for PM10

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PM10 annual mean 90-percentil

MRPE 0.39 0.51

MRDE 0.24 0.45

Can we use MRPE and MRDE as uncertainties on the simulated levels?

Example: calculated yearly mean PM10 concentration is 25 µg/m3 and calculated 90-percentil is 45 µg/m3 then the uncertainties are:

MRPE:Yearly mean: 25 +/- 9.8 µg/m3 i.e. between 15.3 - 34.8 µg/m3

90-percentile (daily mean): 45 +/- 23.0 µg/m3 i.e. between 22.1 - 68.0 µg/m3

MRDE:Yearly mean: 25 +/- 9.6 µg/m3 i.e. between 15.4 - 34.6 µg/m3

90-percentile (daily mean): 45 +/- 22.5 µg/m3 i.e. between 22.5 - 67.5 µg/m3

Likely those intervals are too large for a general public?

Can MRPE and MRDE be used as uncertainties?

Page 13: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

Are the quality objectives (QA) obtainable and relevant?Answer: Yes, but…

Some confusion on how to calculate MRPE and MRDE which must be eliminated.

The indicator should reflect model uncertainty as much as possible. In our opinion RPE is a better indicator than RDE, especially for Swedish conditions with air quality levels often well below the limited values.

It is unclear if and how these indicators can be used, except for showing compliance of Directive’s “Quality objectives for models”. For describing model uncertainties in a broader sense other and more refined indicators are needed (Delta tool…).

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Conclusions

Thank you for your attention!

Page 14: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

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PM10 in Swedish cities (2004): Importance of local contribution

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PM10 in Swedish cities (2004): Local – Urban - Regional

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Page 16: Swedish experiences of applying the Quality Objectives for NO2 and PM10 modelling

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