source attribution of halogenated compounds in support of emission inventories for international...
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Stefan ReimannMartin K. Vollmer
Stephan Henne
Dominik Brunner
Alistair Manning (UK MetOffice)
Lukas Emmenegger
Source attribution of halogenated compounds in support
of emission inventories for international agreements
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• Chlorofluorocarbons (CFCs)
CFC-11, CFC-12 , CFC-13, CFC-11, CFC-113
• Halons
H-1301, H-1211, H-2402, CH3Br
• Solvents
CH3CCl3, CCl4,
• Hydrochlorofluorocarbons (HCFCs)
HCFC-141b, HCFC-124, HCFC-22, HCFC-142b
• Hydrofluorocarbons (HFCs)
HFC-23, HFC-32, HFC-125, HFC-134a,
HFC-143a, HFC-152a, HFC-227ea,
HFC-236fa, HFC-365mfc, HFC-245fa, HFC-
43-10mee, desflurane
• Perfluorocarbons (PFCs), etc
CF4, PFC-218, PFC-318, C4F10, C6F14, SF6,
SF5CF3
Global Warming
Kyoto Protocol
Halogenated Compounds in the Atmosphere
Ozone Depletion/Global Warming
Montreal Protocol
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Halocarbons as Greenhouse Gases
in IPCC 5AR
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Velders et al., Science (2012)
Halocarbons as Greenhouse Gases:
History and Future
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NOAA/ESRL NetworkHalocarbon Surface and Aircraft Sampling
AGAGE NetworkContinuous in-situ Sampling
Global Measurements of Halocarbons
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2014 UNEP/WMO Ozone Assessment
The Montreal Protocol
Everything on Track
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~160 000 tons/year
Global box model
𝐵(𝑡)
𝑙𝑖𝑓𝑒𝑡𝑖𝑚𝑒+𝑑𝐵(𝑡)
𝑑(𝑡)= emission
𝐵(𝑡): mass of F-134a in atmosphere
lifetime: 14 years
𝑑𝐵(𝑡)
𝑑(𝑡): rate of change
How to derive regional emissions?
Box-model approach for estimating global sources
The Kyoto-Protocol
Emission Estimation world-wide
coolant agent HFC-134a
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Example: Combination of Measurements and Models:
The "unknown" European HFC-23 source
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How to derive country-based emissions?
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CO
COCO
CO
CO
CO
CO
COCO
F-134a
F-134a
F-134a
F-134a
F-134a
During stable conditions in summer well-mixed emissions from the
Swiss boundary layer are transported to Jungfraujoch (3850 m asl)
=CO inventory
CO above background
emission of F-134a
F-134a above background
Top-Down Emission estimation for Switzerland
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Annex 5.1 Independent verification of the National Swiss Inventory for F-gases
Switzerland’s Greenhouse Gas Inventory 2001-2014
Swiss Inventory:
8.5% annual loss car air conditioners:
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NIR (UNFCCC) Annex 6: Independent verification of the National UK Inventory
UK’s Greenhouse Gas Inventory 1995-2014
-
1
2
3
4
5
6
7
Em
issio
ns (
kt)
Mace Head measurements combined with the NAME model
measurement-based
1 site 4 sites
inventory
15% loss
A. Manning (MetOffice, UK)
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Inversion
algorithm
Inverse Modelling for Inventory Support
A priori estimates of
surface flux
Constituent
observations
Simulated flux
sensitivities
High-Resolution Models Inventories
A posteriori estimates
of surface flux
Country total emissions
Measurements
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HFC Inversion in the EU project INGOS
Four groups & inversion systems
Empa, Dominik Brunner (WP lead)
Empa2, Stephan Henne
NILU, Rona Thompson
UKMO, Tim Arnold / Alistair Manning
Three measurement sites
Jungfraujoch, Mace Head, Monte Cimone
A posteriori simulation of HFC-125 at Mace HeadA posteriori HFC-125 emissions per country
Annual average sensitivity (footprint)
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HFC Inversion in EU project INGOS
Brunner et al., in preparation
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measurement-based
emissionsinventory-based
emissions
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• Atmospheric measurements of halocarbons can be
used to provide real-world support of inventories used
in international agreements.
• The measurement-based approach is essential for
identifying gaps and for providing trust between
countries and different global regions.
• Measurements and methods for the measurement-
based emission estimation have to be performed in a
coordinated manner and have to be standardized.
Summary and Outlook