Distributions etc models: Difference between revisions

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If you need help about filling in a variable open the link at the end of this paragraph in a new window. Otherwise, just delete this paragraph and start writing. [[Heande:Help:Variable]]
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== Description ==
== Description ==
EEA Topic report No 19/1996
Ambient air quality, pollutant dispersion and transport models
Appendix 3
Regional/continental scale models
{| {{prettytable}}
!Model name
!Institution
!Application
!Type of model
!Domain
!Simulation period
!Plume rise
!Stability classification
!Meteorology
!Reference
|----
|IFDM
|VITO Mol, Belgium
|Stack emissions
|Gaussian
|Local
|Yearly averages, hourly and daily percentiles
|Briggs
|Bultynk-Malet
|Hourly time series
|R. Cosemans, J. Kretzschmar and G. Maes, 1992
|----
|PLUIMPLUS
|Staatsvitgeverij, ‘s Gravenhage, Nederland
|Stack emissions
|Gaussian in vertical Uniform in 30° -sector horizontal
|Local
|Yearly averages, empirical hourly and daily percentiles
|Briggs
|KNMI-system, surface roughness
|Joint frequency matrix
|Kleine Commissie Modellen, 1976
|----
|ISCST 2
|Environmental Protection Agency, USA
|Stack emissions
|Gaussian
|Local
|1 hour to yearly average, n largest concentrations time series
|Briggs
|Pasquill Gifford classes, urban and rural modes
|Hourly time series
|EPA, Trinity Consultants 1992
|----
|AUSTAL 86
|TA-LUFT, Germany
|Stack emissions
|Gaussian
|Local
|Yearly average, 98-percentiles
|Briggs
|TA-LUFT classes (4)
|Joint frequency matrix
|TA-LUFT, 1986
|----
|OML
|National Environmental Research Institute, Denmark
|Stack emissions
|Gaussian
|Local
|Yearly averages, n largest hourly average, 99-percentiles
|Briggs
|Boundary layer scaling parameterisation
|Hourly pre-processed time series
|P. Løfstrøm and H.R. Olesen, 1988
|----
|UK-ADMS
|CERC and UK Meteorological Office, United Kingdom
|Stack emissions
|Gaussian Non-Gaussian in vertical in convective situations
|Local
|1 hour to yearly averages, percentiles
|Equations based on fluxes of mass and heat
|Boundary layer parameterisation
|Hourly pre-processed time series
|Carruthers et al., 1992
|----
|HPDM
|Sigma Research Corporation, USA
|Stack emissions
|Gaussian
|Local
|1 hour to yearly averages, n largest hourly average, 99-percentiles
|Briggs
|Boundary layer parameterisation
|Hourly pre-processed series or on site measurements
|Hanna and Paine, 1989
|----
|INPUFF
|Environmental Protection Agency, USA
|Stack emissions
|Gaussian, puff trajectory
|Local
|1 hour to yearly averages, percentiles
|Briggs
|Pasquill-Gifford
|Hourly pre-processed time series
|Petersen and Lavdas, 1986
|----
|CTDMPLUS
|Environmental Protection Agency, USA
|Stack emissions
|Gaussian
|Local
|1 hour to yearly average,
|Briggs
|Boundary Layer scaling parameterisation
|Hourly pre-processed time series
|EPA, Perry et al. 1989
|----
|SCALTURB
|Norwegian Institute for Air Research (NILU), Norway
|Stack emissions
|Dispersion regions, Semi-Gaussian
|Local
|1 hour to yearly averages, percentiles
|Briggs
|Boundary layer parameterisation
|Hourly pre-processed time series
|Gryning, Holtslag, Irwin and Sivertsen, 1987
|----
|CAR
|RIVM, TNO (The Netherlands)
|road pollution
|semi-empirical relation based on wind tunnel experiments and field campaigns
|various street types (open lanes <==> street canyons)
|yearly averaged; 98 percentiles
|NO2 according to photostationary equilibrium
|
|yearly averaged
|Eerens et al, 1993
|----
|CARSMOG
|RIVM, TNO (The Netherlands)
|real time modelling of road pollution
|semi-empirical relations (see CAR) combined with actual measurements
|various street types (open lanes <==> street canyons)
|hourly averaged
|NO2 according to photostationary equilibrium
|
|actual hourly values
|den Tonkelaar W.A.M. 1995
|----
|CAR-FMI
|Finland Meteorological Institute, Finland
|Road pollution
|Finite line source, partly analytical Gaussian
|Local
|1 hour
|Boundary layer scaling
|Discrete parcel method NOx, O2, O3
|Hourly time series
|Härkönen et al., 1994
|----
|ROADAIR
|Norwegian Institute for Air Research (NILU), Norway
|Road pollution
|Finite line source, Gaussian Emission model based on traffic composition and driving conditions
|Local
|1 hour
|Pasquill-Gifford stability classes
|Conversion of NO to NO2 by O3.
|Worst case 1 hour
|Larssen and Torp, 1993
|----
|CONTILINK
|Norwegian institute for Air Research (NILU), Norway
|Road pollution
|Finite line source Gaussian, semi-stationary
|Local
|Hourly concentrations
| -
|Pasquill Gifford
|Wind direction, wind speed, stability
|Larssen et al., 1993
|----
|}


=== References ===
=== References ===
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Latest revision as of 10:53, 20 November 2009

Template:Release If you need help about filling in a variable open the link at the end of this paragraph in a new window. Otherwise, just delete this paragraph and start writing.

Scope
Distributions etc models describes

Description

EEA Topic report No 19/1996 Ambient air quality, pollutant dispersion and transport models Appendix 3 Regional/continental scale models

Model name Institution Application Type of model Domain Simulation period Plume rise Stability classification Meteorology Reference
IFDM VITO Mol, Belgium Stack emissions Gaussian Local Yearly averages, hourly and daily percentiles Briggs Bultynk-Malet Hourly time series R. Cosemans, J. Kretzschmar and G. Maes, 1992
PLUIMPLUS Staatsvitgeverij, ‘s Gravenhage, Nederland Stack emissions Gaussian in vertical Uniform in 30° -sector horizontal Local Yearly averages, empirical hourly and daily percentiles Briggs KNMI-system, surface roughness Joint frequency matrix Kleine Commissie Modellen, 1976
ISCST 2 Environmental Protection Agency, USA Stack emissions Gaussian Local 1 hour to yearly average, n largest concentrations time series Briggs Pasquill Gifford classes, urban and rural modes Hourly time series EPA, Trinity Consultants 1992
AUSTAL 86 TA-LUFT, Germany Stack emissions Gaussian Local Yearly average, 98-percentiles Briggs TA-LUFT classes (4) Joint frequency matrix TA-LUFT, 1986
OML National Environmental Research Institute, Denmark Stack emissions Gaussian Local Yearly averages, n largest hourly average, 99-percentiles Briggs Boundary layer scaling parameterisation Hourly pre-processed time series P. Løfstrøm and H.R. Olesen, 1988
UK-ADMS CERC and UK Meteorological Office, United Kingdom Stack emissions Gaussian Non-Gaussian in vertical in convective situations Local 1 hour to yearly averages, percentiles Equations based on fluxes of mass and heat Boundary layer parameterisation Hourly pre-processed time series Carruthers et al., 1992
HPDM Sigma Research Corporation, USA Stack emissions Gaussian Local 1 hour to yearly averages, n largest hourly average, 99-percentiles Briggs Boundary layer parameterisation Hourly pre-processed series or on site measurements Hanna and Paine, 1989
INPUFF Environmental Protection Agency, USA Stack emissions Gaussian, puff trajectory Local 1 hour to yearly averages, percentiles Briggs Pasquill-Gifford Hourly pre-processed time series Petersen and Lavdas, 1986
CTDMPLUS Environmental Protection Agency, USA Stack emissions Gaussian Local 1 hour to yearly average, Briggs Boundary Layer scaling parameterisation Hourly pre-processed time series EPA, Perry et al. 1989
SCALTURB Norwegian Institute for Air Research (NILU), Norway Stack emissions Dispersion regions, Semi-Gaussian Local 1 hour to yearly averages, percentiles Briggs Boundary layer parameterisation Hourly pre-processed time series Gryning, Holtslag, Irwin and Sivertsen, 1987
CAR RIVM, TNO (The Netherlands) road pollution semi-empirical relation based on wind tunnel experiments and field campaigns various street types (open lanes <==> street canyons) yearly averaged; 98 percentiles NO2 according to photostationary equilibrium yearly averaged Eerens et al, 1993
CARSMOG RIVM, TNO (The Netherlands) real time modelling of road pollution semi-empirical relations (see CAR) combined with actual measurements various street types (open lanes <==> street canyons) hourly averaged NO2 according to photostationary equilibrium actual hourly values den Tonkelaar W.A.M. 1995
CAR-FMI Finland Meteorological Institute, Finland Road pollution Finite line source, partly analytical Gaussian Local 1 hour Boundary layer scaling Discrete parcel method NOx, O2, O3 Hourly time series Härkönen et al., 1994
ROADAIR Norwegian Institute for Air Research (NILU), Norway Road pollution Finite line source, Gaussian Emission model based on traffic composition and driving conditions Local 1 hour Pasquill-Gifford stability classes Conversion of NO to NO2 by O3. Worst case 1 hour Larssen and Torp, 1993
CONTILINK Norwegian institute for Air Research (NILU), Norway Road pollution Finite line source Gaussian, semi-stationary Local Hourly concentrations - Pasquill Gifford Wind direction, wind speed, stability Larssen et al., 1993


References


  • AirView (allows you to query AirBase and visualise air quality data)

Definition

Causality

List of parents:

  • item 1

Data

Formula

Analytica_id:

<anacode></anacode>

Unit

Result