Impact of high-resolution CEMAP emission data on EMEP model output (The mosiac bottom-up inventory) Kees Cuvelier ex European Commission JRC-Ispra Fairmode Technical meeting Madrid, 7-9 October 2019
Towards a mosaic EU inventory? European top-down National Region City Assumption: local is better
Towards a mosaic EU inventory? “Mosaic” base -case map “Mosaic” inventory AQM SRR “Mosaic” SHERPA “Mosaic” scenarios
Towards a mosaic EU inventory? One of the criticism made to SHERPA relates to the quality of the emission inventories. The mosaic inventory would solve (at least partially) this issue and provide a SHERPA tool based on local data. The mosaic concentration can be included in the composite mapping for comparison The mosaic (inventory and concentrations) will present inconsistencies (e.g. border effects) which can trigger discussions and (hopefully) lead to improvements • At this stage, this work is a proposal that need to be discussed within the FAIRMODE community (starting today!) • Sensibilities on emissions (especially data sharing) are important. It is important to stress that data is kept within FAIRMODE. At a later stage, only open emission sources could be included.
Context: • Composite mapping of emissions WG2 Fairmode • Contributions from … • Contributions: scale and resolution • All in SNAP activity sectors • Web application for visualization – VITO • High-resolution inventories, CEMAP ------------ • EMEP model for air quality • EMEP-CAMS emission inventory • Resolution .1 x .05 degrees • Based on the GNFR activity sectors Question: What is the impact on EMEP model output of an implementation of the high-resolution CEMAP emission data into the EMEP-CAMS inventory.
CEMAP inventory Local CS – EPSG code CS transformation based on EPSG to WGS84 (EPSG 4326) Y Lat Subdivision Δ <= 1 km X Lon EMEP-CAMS Subdivision Δ (~3 km) Aggregation to EMEP-CAMS Δ cells
After aggregation New Inventory Scaling wrt EMEP-CAMS country totals: Outside Domain Scaling (Regional) No Scaling Country Scaling For each {pollutant & sector} For each pollutant {sum of sectors}
Example: Poland, Małopolska , CAMS, NOx, S2 (GNFR3), [Ton/cell] EMEP-CAMS: Europe Poland max=4349. Krakow=175.8 Warsaw=397.0 Małopolska CEMAP Małopolska data Add EI inv NOx SNAP2 1. x 1. km 2 235 x 136
NOx & GNFR3 (No Scaling) Krakow NewInv - CAMS [Ton/cell] [Ton/cell] W W=0. K=-16.1 (-9.2%) [% CAMS] Poland Total = 89773. [Ton] Diff (NoScaling) = - 2623.
NOx & GNFR3 (Country Scaling) Krakow [Ton/cell] [Ton/cell] W W=+9.36 (+2.4%) K=-11.31 (-6.4%) NOx & GNFR3 (Region) Scaling) W W=+11.94 (+3.0%) K=-16.1 (-9.2%)
Example: Poland, Małopolska , CAMS, PM10, S7 (GNFR6), [Ton/cell] EMEP-CAMS: Europe Poland max=295. Krakow=24.45 Warsaw=32.13 Małopolska CEMAP Małopolska data Add EI inv PM10 SNAP7 1. x 1. km 2 235 x 136
PM10 & GNFR6 (No Scaling) Krakow [Ton/cell] NewInv - CAMS [Ton/cell] W W=0. K=60.2 (246%) [% CAMS] Poland Total = 11665. [Ton] Diff (NoScaling) = + 4364.
PM10 & GNFR6 (Country Scaling) Krakow [Ton/cell] [Ton/cell] New Inv - CAMS W W=-8.75 (-27.2%) K=37.17 (152%) PM10 – GNFR6 (Region) Scaling W W=-14.1 (-44.0%) K=60.2 (246%)
Preliminarissimi results The following CEMAP inventories have been implemented into EMEP-CAMS: • Italy: 2010, All pollutants, All SNAP sectors Domain: 261 x 291, ~ 4.x4. km 2 , EPSG 32632 AMS-MINNI_ENEA • Małopolska -Poland: 2016, All Pollutants, All SNAP sectors Domain: 235 x 136, ~ 1.x1. km 2 , EPSG 4326 UM_Malopolska,GEM-AQ • Sofia – Bulgaria: 2014, {PM10, PM2.5, NOx}, {S1,S2,S4,S7} Domain: 103 x 107, ~ .5x.5 km 2 , EPSG 32634 EducationEnvironmentConsulting • Slovenia: 2013, All Pollutants, All SNAP sectors Domain: 2759 x 1253, ~ .1x.1 km 2 , EPSG 4326 SlovenianEnvironmentAgency-ARSO • Stockholm – Sweden: 2015, PM10, S2 Domain: 143 x 192, ~1.x1. km 2 , EPSG 3006 EHAC- AIRVIRO
EMEP-CAMS PM10 & GNFR6 (SNAP7) [Ton/cell] [kTon + k Δ ] Max = 295. PL & Małop : [11.7 + 4.2] IT & Italy: [21.6 – 1.65] SVN & Slovenia: [1.4 + 1.2] BGR & Sofia: [2.7 + .44]
EMEP model run - by Alexander de Meij (JRC-Ispra) NOx [ug/m3] Krakow BC - Cscaling Max=28.3 Min=-2.69 PM10 [ug/m3] Krakow BC - Cscaling Max=13.6 Min=-32.8
Technical details • Δ CEMAP inventory • Δ EMEP-CAMS inventory (for country totals) • Calculation of country totals • Country shape files • Correspondance SNAP vs GNFR • Priority order of CEMAP data • Speed up of calculations • etc
Thank you
Following slides not used
Questions regarding the EMEP_CAMS emission inventory used in the EMEP model
Inventory: EMEP-CAMS_v2_1_1_01005deg_2015.nc Σ All sectors PM10 PM2.5 PMco NOx NMVOC NH3 SO2
Inventory: EMEP-CAMS_v2_1_1_01005deg_2015.nc Sector GNFR3 (SNAP2) PM10 PM2.5 PMco Krakow = 27.4092 Krakow = 18.0391 Cell Krakow = 45.4483 Madrid = 35.3529 Madrid = 0.9769 Cell Madrid = 35.3529 NOx NH3 NMVOC Krakow = 35.21892 Krakow = 38.5137 NL=0, FR=0, ES=0, PT=0 Madrid = 30.8381 Madrid = 28.8228
Inventory: EMEP-CAMS_v2_1_1_01005deg_2015.nc Sector GNFR5 (SNAP6) PM10 NOx NMVOC ES=0, IT=0, PT=0,CZ=0, SVK=0 Only S, NL, B, DE, FR, Rest=0 Ok NH3 SO2 Only NL, UK, DE, CH, Rest=0 Only S, Rest=0
GNFR versus SNAP • There is no 1-1 correspondance ! GNFR SNAP A 1 – PublicPower (S1) 1 – Combustion in energy and transformation industries B 2 – Industry (S3) 2 – Non-industrial combustion plants C 3 – ‘ OtherStationaryComb (S2) 3 – Combustion in manufacturing industry D 4 – Fugitive (S4) 4 – Production processes E 5 – Solvents (S6) 5 – Extraction & distribution of fossil fuels and F 6 – RoadTransport (S7) geothermal energy G 7 – Shipping (S8) 6 – Solvents and other product use H 8 – Aviation (S8) 7 – Road transport I 9 – OffRoad (S8) 8 – Other mobile sources and machinery J 10 – Waste (S9) 9 – Waste treatment and disposal K 11 – AgriLiveStock (S10) 10 – Agriculture L 12 – AgriOther (S10) 11 – Other sources and sinks M 13 – Other (S5)
EMEP-CAMS inventory • Subdivision of CEMAP into small cells • Transformation of local CS to WGS84 • Put each green small cell into EMEP-CAMS
POLAND, Małopolska , CEMAP inventories for all SNAP sectors and all pollutants
CEMAP inventory Local CS – EPSG code CS transformation based on EPSG to WGS84 (EPSG 4326) Y Lat Subdivision Δ <= 1 km X Lon Subdivision Δ (~3 km) Aggregation to EMEP-CAMS Δ cells
CEMAP inventory Local CS – EPSG code CS transformation based on EPSG to WGS84 (EPSG 4326) Y Lat Subdivision Δ <= 1 km X Lon Subdivision Δ (~3 km) Aggregation to EMEP-CAMS Δ cells
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