contribution from different voc emission sources to photochemical ozone formation in europe dick...
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CONTRIBUTION FROM DIFFERENT VOC EMISSION SOURCES TO PHOTOCHEMICAL OZONE FORMATION IN EUROPE
Dick Derwent
rdscientific
This work was supported by the UK Department for Environment Food and Rural Affairs under contract number EPG 1/3/200
AIM OF THE PRESENTATION
To describe the contribution made by the different VOC emission sources to photochemical ozone formation over Europe.
UK PHOTOCHEMICAL TRAJECTORY MODEL
• Model description
A single air parcel following a trajectory across Europe
• Emissions of SO2, NOx, VOCs, CH4, CO and isoprene
From EMEP and UK NAEI inventories
• Master Chemical Mechanism
UK PHOTOCHEMICAL TRAJECTORY MODEL
MASTER CHEMICAL MECHANISM
• 137 emitted organic compounds• 4,414 reaction products• 12,871 chemical reactions
Detailed explicit chemical mechanism to represent the contribution made by each individual VOC species.
Developed by Michael Jenkin of Imperial College and Michael Pilling of University of Leeds and available at:
http://mcm.leeds.ac.uk/MCM
MASTER CHEMICAL MECHANISM
Generates the same picture of regional ozone formation across Europe as other mechanisms
Used here because it is the only mechanism that treats each emitted VOC species in explicit detail
VOC source categories can only be treated explicitly with a chemical mechanism that treats each species in detail
COMPARISON OF MCMv3.1 WITH CBM4 MECHANISM
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13 22 31 40 49 58 67 76 85 94 103
112
Travel time , hours
ozo
ne
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pb
MCMv3.1
CBM4
GRIDDED EMISSION INVENTORIES
VOC SPECIATION
UK NAEI
• 248 emission source categories at the SNAP 3 level• each has its own profile containing 667 VOC species• 248 x 667 matrix
UK Photochemical Trajectory Model
• 248 x 177 matrix of category x species• 90% coverage of total VOC mass emissions• fractional speciation held constant across Europe
EXPERIMENTAL DESIGN
• Base Case Experiment
Run with year 2000 VOC, NOx, SO2, CO, isoprene and CH4 emissions and year 2000 VOC fractional speciation
Ozone at arrival point 87.8 ppb
• 248 sensitivity cases
Run with the emissions from each VOC emission source category increased fractionally
Determine by difference the extra ozone formed
SENSITIVITY EXPERIMENTS
An additional emission was added in turn from each VOC emission source category across Europe.
The extra emission amounted to a 7.3% increase in VOC emissions.
The speciation of the extra emission was given the same species profile as the emission source category.
The increase in emission was applied everywhere across Europe
INCREMENTAL REACTIVITYOF A VOC EMISSION SOURCE CATEGORY
This is the increase in ozone in ppb divided by the fractional increase in the emissions from that source category:
O3
----------------------------
VOC
---------
VOC
Incremental reactivities depend on the environmental conditions and are not geophysical quantities
INCREMENTAL REACTIVITIES
Chemical waste incineration 53.8
Blast furnaces_Coke-oven gas 49.5
Iron & steel (Flaring)_Coke-oven gas 49.0
Iron & steel industry_Coke-oven gas 48.9
Other industrial combustion_Coke-oven gas 48.9
Industrial coatings (drum) 47.5
Printing (metal decorating) 47.1
Printing (heatset web offset) 47.0
Industrial coatings (marine) 46.5
Railways (Freight)_Gas oil 46.2
Road transport (rigid HGVs)_DERV 46.2
Other industrial (off-road)_Gas oil 46.0
CONTRIBUTION TO OZONE FORMATION
Ozone formation
= Incremental Reactivity x Fractional contribution
to total VOC emissions
CONTRIBUTION TO OZONE FORMATION
% incremental ozone
emissions reactivity ppb
Road transport (cars without catalysts)_Petrol 11.524 41.387 4.769
Road transport (cars with catalysts)_Petrol 5.264 41.578 2.189
Onshore loading of crude oil 5.098 31.532 1.608
Chemical industry 5.364 28.337 1.520
Offshore loading of crude oil 3.739 31.026 1.160
Spirit manufacture (maturation) 3.401 30.890 1.051
Refineries (process fugitives) 2.091 41.291 0.863
Petrol stations (vehicle refuelling with unleaded petrol) 2.709 31.327 0.849
Other solvent use 3.370 20.229 0.682
Gas leakage 4.648 13.527 0.629
Decorative paint (trade decorative) 1.811 31.395 0.569
Industrial coatings (metal & plastic) 1.627 34.835 0.567
Aerosols (cosmetics and toiletries) 1.883 28.638 0.539
Decorative paint (retail decorative) 1.669 31.313 0.523
Industrial adhesives 1.822 28.569 0.520
CONTRIBUTION TO OZONE FORMATION
Each source category has a different incremental reactivity because of the contribution from the different VOCs that make up its species profile.
Each source category makes a different contribution to ozone formation because of its different incremental reactivity and its different contribution to total emissions.
DOES IT MAKE ANY DIFFERENCE IF THE INFORMATION ABOUT THE INCREMENTAL REACTIVITIES IS USED IN
CONTROL STRATEGIES ?
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Percentage emissions
Ozo
ne
, p
pb
MCM
EMEP/RAINS
Based on incremental reactivities for 248 source categories
Base case 87.8 ppb
4 ppb
DOES IT STILL MAKE A DIFFERENCE AT THE HIGHLY AGGREGATED SNAP 1 LEVEL ?
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Percentage emissions
oz
on
e ,
pp
b
MCM
EMEP/RAINS
1.9 ppb
Based on incremental reactivities of 11 SNAP 1 source categories
Road transport
solvents
Extraction & distribution of fossil fuels
CONCLUSIONS
• Incremental reactivities have been constructed for 248 VOC emission source categories.
• There is a factor of over 30 range in these incremental reactivities which is not represented in the EMEP/RAINS models.
• These variations in reactivity are caused by the different VOC species profiles for each source category.
• VOC control strategies targetting the most reactive source categories could be more cost-effective than currently estimated using the EMEP/RAINS models.