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Modelling atmospheric transport of Benzo(a)Pyrene with CMAQ

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Presentation on theme: "Modelling atmospheric transport of Benzo(a)Pyrene with CMAQ"— Presentation transcript:

1 Modelling atmospheric transport of Benzo(a)Pyrene with CMAQ
The need for time resolved emissions V. Matthias, A. Aulinger GKSS Research Centre, Geesthacht, Germany

2 Research Objectives Investigation and assessment of air pollution , i.e. persistent organic pollutants (POPs) in Europe Deposition of POPs into the North and Baltic Sea Focus on coastal regions Evaluation of past and forecast of future developments (scenarios) on time scales of decades Assessment of the impact of regulations

3 CMAQ model domain and nest
54x54 km2 grid 18x18 km2 grid 30 vertical layers

4 BaP was included as a new substance into CMAQ is mainly particle bound we consider 3 particle modes and the gas phase model results can be compared to (few) measurements

5 Meteorology, initial and boundary conditions
Meteorological fields are calculated with MM5 Boundary Layer: MRF (Hong and Pan, 1996) Microphysics: Reisner 2, incl. ice, snow and graupel (Reisner et al., 1998). Cumulus: Kain Fritsch 2, (Kain and Fritsch, 1993) One year is represented by four months (January, April, July and October), selected years will be calculated (starting with 2001) Interest in long term runs / use of met. fields from other models (e.g. CLM) ICs: constant profiles, one day spinoff time for each month BCs: Either constant profiles or daily means from a global CTM (MOZART)

6 Emissions Hourly anthropogenic emissions of 2000 for CO, NOx, SO2 , NH3 , NMVOC (in RADM speciation), PM2.5 and PM10 on the 54 km and 18 km CMAQ grid provided by the IER Stuttgart. Biogenic emissions of terpenes and isoprene from POET database (monthly values for 2000 on 1° x 1°), addition of a diurnal cycle for isoprene, no diurnal cycle for terpenes Sea salt emissions internally considered by CMAQ (depending on wind speed)

7 BaP Emissions Available data:
Annual BaP emissions for 1970, 1975, 1980, 1985, 1990, 1993/1995, provided by Dr. Knut Breivik on the 50 x 50 km² polar stereographic EMEP grid. Annual BaP emissions (in 5 sectors) based on TNO report for 2000 also on the EMEP grid but: no temporal resolution available Main sources are residential heating traffic industry (steel and coke) Annual, weekly and diurnal cycles need to be considered

8 Temporal cycle of BaP Emissions
season Residential heating: depends on season Traffic: depends on working times Industrial emissions: depend on working days week day

9 Example BaP Emissions (1)
Based on 1993/1995 annual emissions

10 Example BaP Emissions (2)
Based on 2000 annual emissions

11 Model Results (1) Jan /July 2001 based on 1995 emissions

12 Model Results (2) Monthly concentrationmeans of 2001 based on 1995 emissions in North Sea areas

13 Wet deposition 1995 vs 2000 emissions

14 Comparison to measurements - January
blue: 1995 emissions red: 2000 emissions black: measurements (monthly means)

15 Comparison to measurements - July
blue: 1995 emissions black: measurements (monthly means)

16 Summary and Outlook First results of BaP simulations with CMAQ look promising BaP emissions need improvement ( incl. ship emissions) Reconstruction of BaP concentrations 1970 –2000 based on EMEP emissions Include other POPs (eg. PAHs, PCBs, PFOS) Include second nest simulations

17 Partitioning

18 Measured size distributions

19 Simulated particulate BaP concentrations
Aspvreten Kosetice

20 Simulations vs. ground measurements
Measured mean Model mean

21 Simulations vs. ground measurements
Model mean Measured mean

22 Simulated particulate BaP concentrations in September 2001
Bornhöved Zingst

23 Simulations vs. ground measurements

24 Simulations vs. ground measurements

25 CMAQ in a ´very small´ domain
Run CMAQ on a 1x 1 grid to investigate processes Example: BaP wet deposition under predefined conditions:

26 Nitrogen deposition into the North Sea

27 Nitrogen deposition into the North Sea: influence of meteorological fields
control run / shallow convection run

28 Adsorption to dry surface
Φad adsorbed fraction of compound c Junge parameter θ surface of adsorbat pL subcooled liquid vapor pressure

29 Absorption into organic matter
Φab absorbed fraction of compound Kp gas/particle partitioning constant Kp octanol/air partitioning constant fOC fraction of organic carbon TSP total suspended particles mass

30 Absorption into aerosol water
Φaq absorbed fraction of compound Kp gas/particle partitioning constant Kp water/air partitioning constant fOC fraction of aerosol water TSP total suspended particles mass

31 Simulated gaseous BaP concentrations in September 2001

32 Total simulated BaP depositions in September 2001

33 Interest in long term runs / use of met. fields from other models
Meteorology Meteorological fields are calculated with MM5 Boundary Layer: MRF (Hong and Pan, 1996), based on Troen and Mahrt (1986) nonlocal diffusion concept. Microphysics: Reisner 2, incl. ice, snow and graupel (Reisner et al., 1998). Cumulus: Kain Fritsch 2, conservation of mass, thermal energy, total moisture and momentum (Kain and Fritsch, 1993) Interest in long term runs / use of met. fields from other models

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36 Processes BaP is emitted as accumulation mode aerosol (with 0.1% in Aitken-mode) Gas-particle partitioning considering three aerosol modes (Junge-Pankow concept) Dry deposition, scavenging and wet deposition as for aerosol particles in CMAQ No photolytical and chemical degradation so far


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