Contents
1. Accuracy In Emission Inventories2. Principles of Uncertainty3. Uncertainty Tools4. Conclusions5. Discussion Points
Does it matter?!• Actually, it is not very important for demonstrating
compliance with targets• But key for trying to reflect the real world.
1. Accuracy
Some starting considerations…• Point sources vs area sources• Source/fuel mix• Activity data – trends with time vs absolute• EFs – variations across time series, applicability• Completeness vs guidebook• Completeness vs real world• Mapping emissions• Projections & scenarios
1. Accuracy
1. Accuracy
0%
10%
20%
30%
40%
50%
60%
70%
80%
90%
100%
NOx NMVOC SO2 NH3 PM2.5
Waste & OtherAgricultureProcesses & Product UseOther MobileRoad TransportDomestic & Inst. Comb.Industrial CombustionPower Stations
2. Principles of Uncertainty Uncertainty analysis is generally used to represent
“accuracy”
Point sources- combination of random independent errors Area sources- one EF, prone to bias.
Propagation of Errors• Assign uncertainty to AD and EF
– from measurement, default ranges, expert judgement• “,… root the sum of the squares…”
• Simple mathematical combination of elements to give an uncertainty for the total emission.
3. Uncertainty Tools (1)
Monte-Carlo Analysis
3. Uncertainty Tools (2)
• Uncertainty profiles, accounts for inter-dependencies...• Much better tool, but more challenging to use.
Trend Uncertainties• Standard tool used for assessing the uncertainty
in the trend included in the Guidance.
3. Uncertainty Tools (3)
Strengths• Methodologies common with GHGs (UNFCCC)• Standard mathematical approaches for assessing
uncertainty• Simple methods available.
3. Uncertainty Tools
Weaknesses• Low uncertainty does not necessarily mean good
accuracy!– incomplete inventory, use of inappropriate EFs etc.
• Uncertainty ranges applied to EFs are usually no better than a guess!– Not usually enough data points for a statistical analysis
• Error propagation analysis is too simple– Does not account for interdependencies/biases etc.
• Modellers want uncertainty on mapped emissions.
3. Uncertainty Tools
Development of New Tools• Moran’s co-efficient
– A mathematical metric of spatial autocorrelation (chess board = -1, random = 0, uniform = +1).
– Indicates adjacent grid cell dependencies
• Uncertainty of mapped emissions
3. Uncertainty Tools
Development of New Tools• Uncertainty of mapped
emissions• Combination of emissions
uncertainty with mapping uncertainty
3. Uncertainty Tools
Learning from the Past
3. Uncertainty Tools
0
200400600800
1000
1200
1400160018002000
2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011
Emis
sion
s (k
tonn
es)
NOx(1970-2011)
NOx SNAPSHOT
0
200
400
600
800
1000
1200
1400
2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011
Emis
sion
s (k
tonn
es)
SO2(1970-2011)SO2 SNAPSHOT
Important Considerations• EF uncertainties are not robust enough• Error propagation analysis - too simple?• Uncertainty analysis does not indicate the ability to
represent the real world• Modellers want uncertainty on mapped emissions.
• … we need to improve what we are delivering!• … and in particular better explain what it
represents.
4. Conclusions
Some Questions1. Can we improve current EF uncertainties?
2. Should we all be using Monte-Carlo analysis?
3. Can we add to/adjust uncertainty results to give an indication of real-world representation?
4. Can tools be developed that better provide the information that users need?
5. What resources do we have to support this?
5. Discussion Points