AGACC-II meeting Brussels, 18th December, 2013
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Transcript of AGACC-II meeting Brussels, 18th December, 2013
WP2. Volatile Organic compounds and CFC-substitutes in the troposphere from FTIR spectra Task 2.1: Retrievals of CH3OH and CH3Cl
Task 2.2: Re-analysis of C2H4, C2H6 and H2CO with improved spectroscopy
Reunion data Team: C. Vigouroux, M. De Mazière, F. Desmet, B. Dils, C. Hermans, N. Kumps, B. Langerock, F. Scolas, (BIRA-IASB); J.-M. Metzger (Univ. La Réunion)
C2H4 : - Jungfraujoch data: M. Mahieu (Ulg)
- IMAGES model: T. Stavrakou J.-F. Müller (BIRA-IASB)
AGACC-II meetingBrussels, 18th December, 2013
Task 2.1: Retrievals of CH3OH and CH3Cl
CH3OH: Vigouroux et al., ACP, 2012 & Stavrakou et al., ACP, 2011
Jan10 Apr10 Jul10 Oct10 Jan110
0.5
1
1.5
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3x 10
16
CH
3O
H T
otal
Col
umn
(mol
ec/c
m2)
Apr09 Jul09 Oct09 Jan100
0.5
1
1.5
2
2.5
3x 10
16
CH
3O
H T
otal
Col
umn
(mol
ec/c
m2)
IMAGES optimized using IASI datawithout BB emissions
In Stavrakou et al., ACP, 2011: inversion of the 2009 IASI data, in
order to improve the different sources of CH3OH in IMAGES:
- biogenic & pyrogenic sources reduced: globally 50% and 20% resp.
- improved the seasonality agreement with FTIR
FTIRIMAGESw/o biomass burning
But, IMAGES too low in Sept-Oct.
CH3OH: very good correlation
with CO during the biomass burning BB season (August-November; peak in October); Vigouroux et al., 2012.
- BB is an important source of
CH3OH at Reunion Island1 1.5 2 2.5 3
x 1018
0
0.5
1
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3x 10
16
CO
CH
3O
H
R = 0.20 (Jan-Jun)
R = 0.90 (Aug-Nov)
IMAGES underestimates all BB species at Reunion Island in the Sept-
Oct period (C2H6, CO, CH3OH, HCOOH):
- Underestimation of the fire emission database (GFED3)
Short lifetime of CH3OH (6 d.): an underestimation of GFED3
occurs in the southern Africa/ Madagascar region.
Task 2.1: Retrievals of CH3OH and CH3Cl
Task 2.1: Retrievals of CH3OH and CH3Cl
New: - One more year of data at St-Denis with Bruker 120M (2011)
- Maïdo measurements in 2013
Jan09 Jan10 Jan11 Jan120
0.5
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4x 10
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mol
ec/c
m2
CH3OH total columns at St-Denis
Confirm CH3OH peak in October.
Few measurements at Maïdo during the BB period.
Apr13 Jul13 Oct13 Jan140
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16 CH3OH total columns at Maïdo
FTIRIMAGES
Task 2.1: Retrievals of CH3OH and CH3Cl
CH3OH: summary on the seasonal cycle
2 4 6 8 10 120
0.5
1
1.5
2x 10
16 CH3OH seasonal cycle
tota
l col
umns
mea
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mol
ec/c
m2)
FTIR St-Denis 2009-2011IMAGES model 2009-2010FTIR Maïdo 2013FTIR Maïdo + a priori shift
Overestimation of IMAGES in wet season (without optimization of sources as made in 2009 with IASI)
FTIR: good agreement in the wet season (less influenced by inter-annual variability), between the 2 sites.
Peak in October at both sites, smaller amplitude with IMAGES.
Next version of GFED will include agricultural fires, which are (unfortunately) numerous in… Madagascar… in October !
Task 2.1: Retrievals of CH3OH and CH3Cl
CH3Cl: first attempt of retrieval strategy: 2967.0-2967.8 cm-1;
spectroscopic linelist from M. Mahieu (HITRAN 2004 for CH4, CH3Cl
from A. Perrin).
2967.1 2967.2 2967.3 2967.4 2967.5 2967.6 2967.7 2967.8
0
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90 -3
-2.5
-2
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-0.5
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0.5x 10
-4
0.1
0.8
Weak spectral signature; random noise is an issue, as well as interfering species.
H20
H20 CH4, H2OC2H6
Task 2.1: Retrievals of CH3OH and CH3Cl
CH3Cl: improvement in the Signal to Noise Ratio from Bruker 120M to
Bruker 125HR (especially after April 2013), improves the residuals.
Jan09 Jan10 Jan11 Jan12 Jan13 Jan14-0.5
0
0.5
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mol
ec/c
m2
Bruker 120MBruker 125HRMaïdo
Jan09 Jan10 Jan11 Jan12 Jan13 Jan140.1
0.2
0.3
0.4
0.5RMS
Bruker 120MBruker 125HRMaïdo
Therefore, the scatter in the
CH3Cl columns is nicely
reduced from Bruker 120M to Bruker 125HR (especially after April 2013), and at Maïdo.
Task 2.1: Retrievals of CH3OH and CH3Cl
CH3Cl: seasonal cycle
0 2 4 6 8 10 120
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16x 10
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mol
ec/c
m2
St-Denis Bruker 120MSt-Denis Bruker 125HRMaïdo
St-Denis Bruker 120M: seems too chaotic; probably we see mainly noise.
St-Denis Bruker 125HR: max. in August is observed, large amplitude.
Maïdo columns should be smaller than St-Denis columns ! Probably high systematic bias due to interfering species at St-
Denis (H2O ?).
Max. April and August, small amplitude.
Task 2.1: Retrievals of CH3OH and CH3Cl
Maïdo columns should be smaller than St-Denis columns
Comparisons St-Denis/Maïdo look better after April 2013 (when SNR was improved)
0 2 4 6 8 10 12
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16x 10
15 CH3Cl seasonal cycle
mol
ec/c
m2
St-Denis Bruker 120MSt-Denis Bruker 125HRSt-Denis > April 2013Maïdo
Seasonal cycles in the literature: Yoshida et al., 2006 (surface meas.):
- max. in March & August at 14°S, amplitude < 5% - max. in July-August at 40°S, amplitude ~10%
Task 2.2: C2H4
C2H4: many tests on retrieval strategy
Final micro-window: 948.8 - 952.4 cm-1.
Very weak absorption signatures, and the strongest one is found at
the edge of a CO2 line.
CO2
949 949.5 950 950.5 951 951.5 952
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90-6
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St-Denis
Slope:H2O
Task 2.2: C2H4
Maïdo: improved SNR with Bruker 125 HR; less H2O due to altitude.
CO2
Slope:H2O
St-Denis Maïdo
Much reduced slope
Task 2.2: C2H4
St-Denis (Bruker 120M): large scatter and some negative columns.
Jan09 Jan10 Jan11 Jan12-5
0
5
10
15x 10
14
mol
ec/c
m2
C2H
4 total columns at Saint-Denis
IMAGESFTIR
Apr13May13 Jun13 Jul13 Aug13 Sep13 Oct13 Nov13-5
0
5
10
15x 10
14 C2H
4 total columns at Maïdo
Maïdo
Maïdo (Bruker 125HR, less H2O): still large scatter, no negative values.
Scatter real (lifetime ~1-2 days) ? And/Or too large random error: to be calculated with SFIT4.
Try more filtering ? Need more data at Maïdo.
Task 2.2: C2H4
0 2 4 6 8 10 12 140
1
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4
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7x 10
14C2H
4 seasonal cycle; Reunion Island
mol
ec/c
m2
FTIR St-Denis 2009-2011IMAGES model 2009-2011FTIR Maïdo 2013
C2H4: seasonal cycle at Reunion Island
St-Denis: surprising good agreement with IMAGES in Dec-Aug. (considering FTIR large scatter).
Maïdo columns should be lower than St-Denis: bias
due to H2O ?
High values in April-May at Maïdo due to a few points, need to be confirmed.
FTIR has a max. in Sep-Oct at both sites; not seen in IMAGES: Agreement with the (currently missing in model) biomass
burning from agriculture in Madagascar ! (lifetime C2H4: 1-2 days)
Task 2.2: C2H4 at Jungfraujoch
C2H4 at Jungfraujoch: using the Reunion Island settings.
Jan00 Jan02 Jan04 Jan06 Jan08 Jan10 Jan12 Jan140
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6x 10
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mol
ec/c
m2
C2H
4 total columns at Jungfraujoch
IMAGESFTIR
A significant negative trend is observed.
Results promising ! H2O is much lower at Jungfraujoch.
Task 2.2: C2H4 at Jungfraujoch
C2H4 at Jungfraujoch: seasonal cycle
Jan09 Jan10 Jan11 Jan12 Jan130
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mol
ec/c
m2
C2H
4 total columns at Jungfraujoch
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14 Seasonal cycle (2009-2012)
tota
l col
umns
mea
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mol
ec/c
m2)
FTIRIMAGES
Phase of the seasonal cycle in agreement with IMAGES
Amplitude is much larger with the model
The FTIR retrieval strategies optimized for many VOCs in the first
years of AGACC-II (CH3OH, HCHO, HCOOH, C2H6, HCN, C2H2) have
been or will be soon applied to the recent measurements. The procedure is much quicker with the tools implemented within the NORS project (B. Langerock).
C2H4: a retrieval strategy has been implemented and seems
promising at Jungfraujoch. Some efforts still needed at Reunion Island to understand/correct the large scatter, but seasonal cycle seems good.
We are very curious to compare our Reunion Island time-series of biomass burning species with IMAGES when the GFED4 database, including agricultural fires, will be distributed !
Summary & perspectives
Summary & perspectives
The quality of the spectra (SNR) has been greatly improved with the Bruker 125HR, which can be critical for molecules with low spectral signatures, close to the detection limit.
At Maïdo, the altitude of the site reduces the error due to interfering species (e.g water vapor and isotopologues).
CH3Cl: using the most recent measurements (i.e with improved SNR),
it seems that there is a hope to observe this molecule. What is needed now is 1) more measurements; 2) spectroscopic tests
(HITRAN2012; CH3Cl line-mixing); 3) better check of H2O interference.
Perspectives for AGACCII:
PAN (already tested without success up to now) and acetone will be tested with the new software (SFIT4): allows for HITRAN 2012
and for CO2 line-mixing which was one of the problem for PAN
retrievals.
Duflot, V., et al.: HCN and C2H2 from IASI, AMT, 2013.
Vigouroux, C.: FTIR measurements of VOCs: precious data for model and satellite validation, NDACC newsletter, 2013.
Not related to AGACC-II but very important for NDACC FTIR in general, and BIRA-IASB and ULg in particular:
Thanks to our work on FTIR ozone trends at 8 NDACC stations, we join the SI2N initiative whose aim is to provide “much improved knowledge of ozone changes for the next WMO Scientific Assessment of Ozone depletion”.
- Participation in the three SI2N overview papers:
Hassler et al.: Ozone profile measurements: techniques, uncertainties and availability, AMTD, 2013; Lambert et al.; and Harris et al., in preparation, before spring 2014.
- Participation in the WMO Assessment in 2014.
WP 5: Outreach in 2013
Thank you !
Task 2.1: Retrievals of CH3OH and CH3Cl
CH3Cl: first attempt of retrieval strategy, not really a big success…
but some hope.
Future: focus on optimizing the data after April 2013 at Maïdo and St-Denis: need more data…
- Try HITRAN 2012 (with SFIT4)
- Try G. Toon: CH3Cl line-mixing
problem, propose an « empirical way » of treating this.
- improve H2O treatment (now some
spectra shows residuals)
And/or filtering on systematic
residuals when H2O is not well
reproduced,…
Not related to AGACC-II but very important for NDACC FTIR in general, and BIRA-IASB in
particular:
Join the SI2N initiative: Over three and a half decades have passed since Molina and
Rowland postulated that anthropogenic chlorofluorocarbons could deplete the ozone layer
(Molina and Rowland, 1975), and over two and a half decades have passed since the
discovery of the ozone hole (Farman et al., 1985). In this time, the countries of the world
have produced and signed the Montreal Protocol limiting the production of ozone-depleting
substances (ODSs), and leading to reductions in their atmospheric concentrations (WMO,
2011).. As we proceed towards the expected ozone recovery from the influences of ODSs,
scientific questions concerning the detection and attribution of that recovery have come to
the fore. Answering many of these questions will require a critical examination of the
pattern and time sequence of ozone change. Thus, accurate knowledge of the altitude,
latitude, and seasonal structure of the ozone response is required. It is also critical that the
quality of the measurements used is as high as possible, and that the quality is known.
Outreach in 2013