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RH, %
Slo
pe
of
PA
S v
s P
SA
P
Upper curve obtained by restricting the dataset for RH < X (X from 40 to 65%)
Lower curve obtained by restricting the dataset for RH > Y (Y from 55 to 85%)
Influence of RH on the Absorbance measurement
Slope close to one for dry air
Important decrease for RH ~65%
Max Planck Institute for Chemistry P.O. Box 3060
Biogeochemistry DepartmentD-55020 Mainz, Germany
Manaus plume tracking
LBA-Claire 2001
Manaus
Fligh track
Overview : The aim of the experiment was
1. To evaluate the impact of anthropogenic emissions (Ozone, CN, …) on the biogenic VOCs emissions
2. To better describe the vertical profiles of CN & CCN in remote areas over the tropical forest
Overview of the MINOS Campaign : Aerosol optical properties derived from the Advanced Very High Resolution Radiometer (AVHRR) pointed out the Mediterranean Sea as one of the areas with the highest Aerosol optical depths in the world (Husar et al., 1997). Importance of satellite derived measurements to describe the aerosol loads above the Mediterranean was also demonstrated by Moulin et al. (1997) who reported that year-to-year changes in Aerosol optical depths in Mediterranean were driven by African dust and was closely related to air masses circulation and the Northern Oscillation Index. Recent model studies reproduced satellite observations and demonstrated the role of three major components of aerosols in surrounding regions of the Mediterranean basin (sulfate, black carbon and dust), having very high direct radiative forcing of aerosols at the top of the atmosphere (Jacobsen, 2001). This model estimates a negative radiative forcing for aerosols in Mediterranean, which could compare with greenhouse gases (e.g. -3 to -4 W/m²). Thus, transport of aerosols and their precursors from these regions will have dramatic impact not only on radiative properties over the Mediterranean Sea but even on cloud properties. Rosenfeld (2000) showed that Turkish power plants using high sulfur containing lignite were identified from satellite-derived pictures as influencing downwind cloud radius droplets. As a matter of fact, the most complete characterization of aerosols emitted from each of these regions and reaching the Mediterranean basin will undoubtedly be needed to validate model calculations and remote sensing observations.
Jean SciarePh-D thesis (LSCE, France, May 2000)Post-doc MPI Mainz (2001) / Biogeochemistry (M.O. Andreae)CR2 – CNRS, LSCE, France (since October 2001)
Acknowledgements : I would like to address grateful thanks to Prof. Dr. M.O. Andreae who accepted to review my Ph-D thesis and who accepted me in his group in Mainz for a post-doctoral position. Thanks to the results obtained during my Ph-D and during my post-doc in Mainz I obtained in October 2001 a permanant position at CNRS. Many thanks go also to my co-workers (Greg, Olga, Pascal and Bim) who made to my stay in Mainz an unforgotable memory.
Large discrepancies between the 2 techniques
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5
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15
20
25
30
35
28/07 02/08 07/08 12/08 17/08
Ab
sorb
ance
fro
m P
SA
P, 1
/Mm
0
5
10
15
20
Ab
sro
ban
ce f
rom
PA
S, 1
/Mm
PSAP
PAS
Absorbance Measurements(all dataset 28/07-19/08)
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1.0
28/07 02/08 07/08 12/08 17/08 22/08
Sin
gle
Sc
att
eri
ng
Alb
ed
o
0.0E+00
5.0E-05
1.0E-04
1.5E-04
2.0E-04
Sc
att
eri
ng
Co
eff
., 1
/Mm
Single Scattering Albedo
Scattering
Single scattering AlbedoFinokalia
1
1.25
1.5
1.75
2
50 55 60 65 70
Relative Humidity, %
Sc
att
eri
ng
ch
an
ge
, %
15/07
16/07
17/07
Scattering set at 1 for 55% RH
RH increase
Growth factors from Nephelometer measurements
Measurements from 0900 to 2100 LT
y = 0.57x + 0.11
R2 = 0.78
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15
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25
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Abs (PSAP), 1/Mm
Ab
s (
PA
S),
1/M
m
Abs (PAS) vs Abs (PSAP)(all dataset 28/07-19/08)
Long-range transport of soot aerosols over the Eastern Mediterranean Basin
Calculations were performed using hourly 5-day backtrajectoriesFrom Hysplit 4.0 model (FNL data)
FINOKALIA STATION
MINOS campaign
Environmental Chemical Processes Laboratory
Air masses origin during the Minos campaign(25/07-25/08/01)
Averaged radiative forcing of Greenhouse gases and tropospheric aerosols / (IPCC report, 2001)
Gob
al m
ean
rad
iati
ve f
orci
ng
(W m
-2)
CO2
Sulfates
Anthropogenic Aerosols
1
-1
-2
3
2
C soot
C orga
Greenhouse gases
War
min
gC
ooli
ng
Glo
bal
mea
n r
adia
tive
for
cin
g (W
m-2)
CO2
CH4
N2OHalocarbons
TroposphericOzone
Sulfates
Fossilefuel
Tropospheric Aerosols(indirect effect)
Anthropogenic Aerosols
1
-1
-2
3
2
C soot
C orga
Greenhouse gases
War
min
gC
ooli
ng
C soot
C orga
20022002
Horizon 2100Horizon 2100
Mineraldust
Annual mean and global radiative forcing (at the top of the atmosphere) due to anthropogenic activities from 1750 to 2000 (no squares = no possible estimation). Vertical barres = uncertainty level.
BiomassBiurning
Expected increasing impact of carbonaceous aerosols compared to sulfate aerosols in the future
Increasing uncertainties on the climate forcing of aerosols compares to greenhouse gases
Need for a better understanding the role of soot and organic aerosols
and their interaction with water (indirect aerosol)
Tropospheric Aerosols(indirect effect)
Aerosols and Climate
Large uncertainties on the climate forcing of aerosols compared to greenhouse gases No estimation can be done for the indirect effect of aerosols
Instruments
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1
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Aerosol diameter, nm
CC
N b
ehav
ior
(NH4)2SO4
Humic Acid Like
Adipic Acid
CalibrationCalibration
T = 5°C Supersaturation 1%
Humid plates
Laser beamAir
Video acquisition
PrinciplePrinciple
Instrument developped in Mainz by G. Robert
CCN counter: settings / calibration
PhotoAcoustic System (PAS)
A 670 nm photodiode laser illumaniates the activated droplets while the digital camera, normal to the laser beam , registers digital images every second during the supersaturation cycle. The CCN concentration at a particular supersaturation is calculated by imaging sofware, which automatically determines the number of activated droplets in each picture (extracted from G. Roberts Ph-D dissertation)
Principle : CCN measurements are made using a static thermal-gradient diffusion instrument. It is fitted with a photodiode laser and digital camera to measure droplet concentrations. Activated CCN particles quickly grow to several micrometers in diameter and gravitationally settle out of the chamber.
Principle : An alternative to filter-based methods for light absorption measurement is to use a photoacoustic instrument. No filters are used in these intruments, but instead, the sample air can be continuously drawn through a acoustical waveguide. A periodically modulated laser beam passes through the waveguide. Concomitant with light absorption by either gas or particles is heat transfer to the surrounding air. The waveguide can be designed at a frequency such that all the heat from light absorption is transferred during the period of oscillation. upon receiving this heat, from light absorption, the surrounding air expands and this expansion contributes to the acoustic standing wave in the waveguide. Measurement is made with a microphone. The microphone is linearly proportional to the aerosol light absorption coefficient. (extracted from Arnott et al., 2001)
Aerosol absorption
Noise of the instrument
Aerosol free air
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10000
15000
20000
25000
30000
0.58 0.59 0.6 0.61 0.62 0.63
Time, UTC
CN
, #/c
m3
0
500
1000
1500
2000
2500
3000
CC
N, #
/cm
3
CNCCN
210 m 70 m 540 m 860 m 1190 m 860 m
A A A A B
Alt =
AB
Manaus
Ratio CCN/CN ~10%
Plume of pollution located in the PBL
Well-mixed plume within the first hundreds meters
Plume Study(Flight 18 – 19/07/01)
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1500
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3000
0 200 400 600 800
Particle Number, #/cm3
Alt
itu
de
, m
CCN
CN
30 40 50 60 70
Ratio CCN/CN, %
Alt
itu
de
, m
0
500
1000
1500
2000
2500
3000
Ratio CCN/CN
Vertical profile(Flight 15 – 18/07/01)
Ratio CCN/CN ~50-60%