© crown copyright met office estimating uk and nw european ch 4 emissions using inversion modelling...
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© Crown copyright Met Office
Estimating UK and NW European CH4 emissions using
inversion modelling
Alistair Manning
with thanks to Simon O’Doherty & Dickon Young (University of Bristol)
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Overview
• Estimate UK and NWEU (north west European) emissions of greenhouse gases (GHG) totally independent of UNFCCC inventory process.
• Use in-situ high-frequency atmospheric observations from the remote station on the west coast of Ireland (Mace Head).
• Employ an atmospheric dispersion model (NAME) coupled with 3-D meteorology to understand the recent history of the air arriving at Mace Head.
• Two stage process:
• Estimate long-term Northern Hemisphere baseline concentration.
• Estimate regional emissions through inversion modelling (NAME-Inversion).
• Compare NAME-inversion estimates to UNFCCC/EDGAR inventory estimates.
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Estimating Baseline Concentrations at remote measurement site (Mace Head)
• NAME model (Lagrangian particle dispersion model) run ‘backwards’.
• Uses 3-D meteorological data from UK Met Office NWP model (25-60 km resolution) and ECMWF ERA Interim (re-analysis) (~80 km).
• Derive air history map for each site for a 2-hour period:
• Combination of tens of thousands of trajectories.
• Darker shade means greater contribution from that area.
• All surface sources within previous 30 days of travel (domain limited) that contribute to an observation during a 2-hour period are recorded.
Mace Head air history maps generated each 2-hour period:• 2003-2011 UK Met Office UM• 1989-2002 ECMWF ERA Interim
Mace Head
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Where has the air come from? Examples:
1800-0000 16th March 1996
Baseline
0600-1200 21st March 1996
Polluted
1200-1800 2nd March 1996
Complicated
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Baseline Concentration Methodology (1):Classifying Mace Head Observations
Methane: Raw observations (ppb)
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Baseline Concentration Methodology (2):Classifying Mace Head Observations
Methane (ppb): Observations colour-coded based on recent history of air arriving at the station (Mace Head)
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Baseline Concentration Methodology (3):Classifying Mace Head Observations
Methane (ppb): Select only those observations that are considered to be from a ‘clean’ non-regionally polluted sector.
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Baseline Concentration Methodology (4):Classifying Mace Head Observations
Methane (ppb): Baseline observations – Statistically identify outliers (black) and remove
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Baseline Concentration Methodology (5):Classifying Mace Head Observations
Methane (ppb): Remaining observations classed as ‘baseline’
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Baseline Concentration Methodology (6):Classifying Mace Head Observations
Methane (ppb): Best-fit (moving window) line through baseline observations
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Baseline Concentration Methodology (7):Classifying Mace Head Observations
Methane (ppb): Zoom-in on baseline estimate
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Baseline Concentration Methodology (8):Classifying Mace Head Observations
Methane (ppb): Estimate baseline uncertainty (‘noise’ in baseline)
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Mid-latitude baseline concentration of:Methane (ppb)
Baseline
Growth Rate
Seasonal Cycle
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Mid-latitude baseline concentration of:Nitrous Oxide (ppb)
Baseline
Growth Rate
Seasonal Cycle
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Estimating regional emissions from above baseline concentrations
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Estimating Regional Emissions:Inverse Modelling
Aim: Generate emission estimates from ‘polluted’ (above baseline) observations.
Subtract the baseline concentration from each observation.
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The NAME-Inversion Method (1)
M [t x m] ¤ e [mx1] = O’ [tx1] = O - b
Dilution matrix
Ba
selin
e
Time series of observations
• Air history maps from Mace Head are generated using NAME model
• Record time-series of relative contributions of each surface source to observation station
Emission map:the
Solution
t2
t3
t1
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Dilution matrix = MMeasurement - Baseline = O’ Emission Map = e (the solution)Relationship: M e = O’Problem: Minimise O’ - M e
• Remove observations that have a strong local influence.• Through many iterations find emission distribution that is best-fit statistical
match between model time-series and observations.• No prior information – Random initial guess – Not steered by a priori.• Solve for each 3-yr period stepping monthly e.g. Feb’89 – Jan’92, Mar’89 – Feb’92, …
• Solve multiple times, each time start from different random initial guess.• Apply random ‘baseline noise’ to observations (log-normal distribution).
The NAME-Inversion Method (2)
Air History Map = Matrix M(No times x No grids)
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The NAME-Inversion Method (3) :Grid used to Estimate Emissions
• Balance equation so that each grid contributes equally (approximately).
• More distant grids grouped together so have same impact at the observation station. Example: Grouping of grids based on observations
at Mace Head (MH) on west coast of Ireland.
Grids = 25 km, 50 km, 100 km, 200 km, 400 km, 800 km
0.0
10.0
20.0
30.0
40.0
50.0
60.0
0-400 401-800
801-1200
1201-1600
1601-2000
2001-2400
2401-2800
2801-3200
3201-3600
3601-4000
4001-4400
4401-4800
4801-5200
5201-5600
Number of Times Grid Contributes
% o
f G
rid
s t
ha
t C
on
trib
ute
Not Combined
Combined
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The NAME-Inversion Method (4) :Resolved areas
UK
NWEU
Mace Head
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Model Solutions Vs Observation
‘Best-Fit’ Model (Grey/Black) and Observation (Red) Time-series for methane (ppb) Jan-Mar 2008
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Nitrous Oxide
1990
2010
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Methane
1990
2010
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Conclusions
• Estimate Northern Hemisphere baseline trends 1990-2011 from observation station on west coast of Ireland.
• N2O shows a steady rise, CH4 rising but more irregular.
• NAME-Inversion method used to estimate UK and NW European emissions of N2O and CH4 from 1990 until 2010.
• N2O estimates broadly agree (lower by 10-20% but trend agrees) with UNFCCC inventory.
• CH4 estimates for UK show slow decline (10-20%%) markedly different to UNFCCC trend which shows a 50% reduction over the 20 years but last 5 years agree well.
• CH4 estimate for NW Europe broadly agrees with UNFCCC but with a slightly slower decline.
• Both NAME-Inversion and UNFCCC estimates have significant uncertainties.
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Future
• Increasing the number of representative observation sites will increase resolution of the inversion emission estimates
• Improved meteorological models will improve the ability of models to calculate the recent history and dilution of the air
• Satellites – Need to be able to ‘see’ the boundary layer better before they are used more widely