In-situ Aerosol Measurement Techniques · J. Ogren 10/6/2010. In-situ Aerosol Measurement...
Transcript of In-situ Aerosol Measurement Techniques · J. Ogren 10/6/2010. In-situ Aerosol Measurement...
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J. Ogren 10/6/2010
In-situ Aerosol Measurement Techniques
John A. Ogren National Oceanic and Atmospheric Administration
Earth System Research LaboratoryBoulder, Colorado, USA
http://www.esrl.noaa.gov/gmd/aero/
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Approach
• "In this life, we can't measure what we want, so we measure what we can" (Bob Charlson)
• If we had more time, I would…– discuss what we actually measure– describe methods and assumptions used to
derive the desired variable– discuss the "distance" between physical
standards and derived variable
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Scope of talk
• 40 minutes, including discussion• define "in-situ" to mean methods that draw
a sample of air into an analyzer or collection device
• Insufficient time to be comprehensive, so spend more time on methods in my area of focus– Microphysical, Radiative, Hygroscopic,
Chemical
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Aerosol Sampling Issues• Key Issues
– any change in the chemical thermodynamic state of the sample air will change the aerosol.
– particle losses (or gains) are size-dependent• RH and size control of sampled aerosol
– heating vs. dilution vs. diffusion driers• inadvertent vs. deliberate heating• temperature vs. RH control variable
– inertial vs. diffusive size control• inadvertent vs. deliberate size control
• Examples of particle loss/gain mechanisms– impaction and diffusion losses in inlet systems– scrubbing of organic vapors in dilution air changes
equilibrium concentration of volatile species in condensed phase
– cooling in adiabatic expansion can lead to growth in mass– splashing of hydrometeors on inlets in clouds can lead to
enhancement of number concentrations– sub-isokinetic inlets enhance large particle concentrations
through inertial enrichmentJ. Ogren 10/6/2010
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Key Questions to Ask about Measurements
• What is the T, RH, and P of the sample?– as measured– as reported
• What is the T, RH, and P history during sampling?– e.g., hysteresis
effects
• What is the size- dependent efficiency of the sample inlet?
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Measurements of number concentration• Grow tiny particles to sizes where they are easily detected
– butanol vs. water as working fluid– expansion vs. continuous operation
• optical detection– pulse counting from individual particles– photometric detection of a cloud of particles
• absolute calibration– flow rate– electrometer measures current from sample of singly-charged
particles (hard to do in field)• size cut vs. operating parameters (T)• composition effects
– butanol-based instruments are relatively insensitive to particle composition
– lower detection limit of continuous water CPC's is sensitive to particle composition
• operational considerations
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0 5 10 15 20 25 30 35 40 450
20
40
60
80
100
Cou
ntin
g E
ffici
ency
of b
utan
ol C
PC
sfo
r silv
er p
artic
les
[%]
Particle Diameter Dp [nm]
IFT TDMPS, 3010, T=17 NILU DMPS, 3010, T=25 UHEL DMPS, 3010, T>25 ISPRA DMPS, 3772, T=17 IFT SMPS, 3010, T=17 FMI TDMPS, 3772, T=25 FMI TDMPS, 3772, T=25 LAMP SMPS, 3010, T=17 NUI SMPS, 3010, T=17
CPC Calibration
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CPC Failures• butanol drained or
contaminated• inlet disconnected or
cracked• instrument failure
instrument replaced
butanol added
dyin g
dead
dyin g
instrument sampling room air
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What is the size of a particle?
• Beware of radius vs. diameter confusion!
• Different sizes– optical– electrical mobility– volume-equivalent
sphere– aerodynamic– vacuum
aerodynamic
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• Apparent particle size is affected by morphology, density, and refractive index, depending on the measurement method
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Measurements of Size Distribution• DMPS/SMPS
– differential mobility particle size spectrometer– scanning mobility particle size spectrometer– both select a very narrow size range of
particles based on their electrical mobility– detection is with a CPC
• APS– aerodynamic particle sizer– particles are accelerated and their resulting
change in velocity is related to their aerodynamic size
• OPC– optical particle counter
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Particle Mobility Size Spectrometers: Harmonization of Technical Standards and Data Structure for High
Quality Long‐term Observations of Atmospheric Particle Size Distributions
Alfred WiedensohlerLeibniz Institute for Tropospheric Research
Birmili,
Wolfram;
Nowak,
Andreas;
Tuch,
Thomas;
Wehner,
Birgit;
Sonntag,
Andre;
Fiebig,
Markus;
Asmi,
Eija;
Laj,
Paolo;
Sellegri,
Karine;
Venzac,
Herve;
Villani,
Paolo;
Aalto,
Pasi;
Swietlicki,
Erik;
Pontus,
Roldin;
Schmidhauser,
Rahel;
Gysel,
Martin;
Weingärtner,
Ernest;
Riccobono,
Francesco;
Santos,
Sebastiao;
Grüning,
Carsten;
Fallon,
Kate;
Beddows,
David;
Monahan,
Colin;
Marioni,
Angela;
Williams,
Paul;
Quincey,
Paul;
Hüglin,
Christoph;
Horn,
Hans‐Georg;
Keck,
Lothar;
Ogren,
John;
McMurry, Pete
International Aerosol Conference, Helsinki, FinlandSeptember 3, 2010
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EUSAAR-Standard SMPS Set-Up
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Confirmation of SMPS Sizing
Size of polystyrene latex spheres is measured with an electron microscope
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Intercomparison: Number Size Distribution
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Intercomparison: Volume Size Distribution
Note difference in intercomparison results compared to number size distribution
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10 100 8000
1000
2000
3000
4000
5000
6000
Dp [nm]
dN/d
logD
p [#
/cm
³] SMPS nr. 1 SMPS nr. 2 SMPS nr. 3 SMPS nr. 4 SMPS nr. 5
average +/- 10%
Intercomparison: Number Size Distribution
Experience gained from repeated intercomparison experiments leads to improved agreement among instruments
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OPC response functions have ambiguity
• Depending on optical geometry and particle refractive index, different particle sizes can produce the same signal in the instrument
• Fiebig, 2001, Ph.D. dissertation
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Measurements of Light Scattering Coefficient
• integrating nephelometer• inverse nephelometer
– in photoacoustic absorption instrument– cavity ringdown extinction instrument
• measures count rate from particles as they pass through an illuminated volume
• calibrated against known Rayleigh scattering of gases (air, CO2 , CFC-12, He) at measured T&P
• errors: truncation, angular illumination, sample heating
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Sensor dv
Light source
r
Apex of scattering cone
Principle of Integrating Nephelometer
1. Light source intensity is proportional to cos, which gives the sin weighting in the integrand.
2. Conical viewing volume dv increases as r2, but intensity of light from dv reaching sensor follows an inverse-square law. The r2 and 1/r2 dependencies cancel, yielding equal weighting of each linear increment dr.
Source: Butcher and Charlson (1972)
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TSI 3563 Integrating Nephelometer
Wavelengths: 450, 550, 700 nm
Bandwidth: 40 nm FWHM
Angular range: 7-170° (total), 90-170° (backscatter)
Sensitivity: 2-3 x 10-7 m-1 (60-sec average)
Source: TSI, Inc.
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TSI Nephelometer Non-Idealities
Source: Anderson et al. (1996)
angular responsewavelength response
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TSI Nephelometer Angular Errors
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This error is a consequence of calibration with Rayleigh scattering vs. measurement of Mie scattering particles
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Measured (points) vs. Calculated (lines) Response of TSI Nephelometer
Source: Anderson et al. (1996)
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Nephelometer Truncation Corrections
Source: Anderson and Ogren (1998)
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Measurements of Light Absorption Coefficient
• Filter-based– PSAP (particle/soot absorption photometer)– Aethalometer
• broadband• spectral
– MAAP (multi-angle absorption photometer)– correction schemes– comparison results– "yellow beads" – sensitivity to liquid aerosols– heated inlet (Kondo, 2009, AS&T)
• "Direct"– photoacoustic– photothermal interferometer
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Filter Methods for Light Absorption
• Particles are deposited on the filter, which is a light- diffusing, multiple scattering substrate.
• Light absorbing particles reduce the light power at the photodetector.
• Ideally, light scattering particles don't reduce power.• Variants:
– Time-integrated: integrating plate method, integrating sphere, integrating sandwich
– Continuous: aethalometer, PSAP, MAAP
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PSAP Response to Non-Absorbing Particles Depends on Filter Loading
Source: Bond et al. (1999)
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PSAP Response to Scattering
Source: Bond et al. (1999)
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Current PSAP Correction Factors
Bond et al. (1999)
Slope=1.22 with 2% of sp subtracted
filter transmittance
ap(
PSAP
)/ap
(TR
UE
)
Manufacturer’s built- in calibration
(Weiss, unpublished)
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Aethalometer response vs. time
Separate runs with pure soot (ext ~800 Mm-1) and ammonium sulfate (ext ~450 Mm-1). Photoacoustic wavelength 532 nm, aethalometer wavelength 521 nm.
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Multi-Angle Absorption Photometer• "MAAP"• Simultaneously
measures light (670 nm) transmitted and reflected by aerosol deposit on filter
• A two-stream radiative transfer model is used to derive the aerosol absorption coefficient, accounting for light scattering by particles and filter.
• Detection limit ~ 1 Mm-1
for 2-minute average at 16.7 lpm flowrate.
Source: A. Petzold1 , M. Schönlinner2 , H.Kramer2 and H. Schloesser2
1German Aerospace Center, Oberpfaffenhofen, Germany2ESM Andersen Instruments, Erlangen, Germany
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Summary of Filter-based Absorption• Filter spot size and flow rate must be
individually calibrated for each instrument• Corrections are required for non-ideal
responses of instrument to– scattering by particles (requires scattering
measurement)– attenuation of light by deposited particles
("shadowing")• Correction schemes
– PSAP: Bond (1999, AS&T)– Aeth: Collaud Coen (2010, AMT)– MAAP: done internally, Petzold (2004, J.
Aerosol Sci.)– improvements are coming
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Photoacoustic Absorption Measurement
• Laser light is power modulated by the chopper. • Light absorbing aerosols convert light to heat, producing a
sound wave. No response to light scattering.• Microphone signal at chopper frequency is a measure of
the light absorption.• Calibrated by absorption by gases (NO2 , O3 ), monodisperse
particles, or light extinction
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NOAA 5-Channel Photoacoustic Spectrometer (PAS)
405 nm: ambient + thermo-denuded (0.5 Mm-1)532 nm: ambient + humidified (0.75 Mm-1)660 nm: ambient (1.5 Mm-1)(
detection limits for 1 Hz data in parentheses)
Source: D. Lack, 2010, personal communication
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Measurements of Extinction Coefficient
• long-path cell (Virkkula, 2005, AS&T)• cavity ring-down (Baynard, 2007, AS&T)• cavity assisted phase shift (Massoli, 2010,
AS&T)• Fundamental calibration is geometric path
length• measure difference in light extinction
between sample air and filtered sample air
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U.W. Optical Extinction Cell
L = 660 cm
M
L2
DR
DS
O2 O1
460 nm540 nm660 nmLEDs
Sample in
D2 D1
Plug
Purge air in Outlet Outlet
F2 F1
Plug
HD2 HD1
144’’=366 cm
130’’=330.2 cm
L1
BSPT
Purge air in
Source: Virkkula et al. (2005)
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What is Cavity Ringdown (CRD)?
time
input pulse
ringdown cavity
output signal
• input pulse width ~ 20 nanoseconds• mirror reflectivity > 99.995%• ring-down time 5-100 microseconds• extinction coefficient derived from fitting an exponential function
to decay of output signal• some variants measure scattering coefficient simultaneously
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CRD Accuracy Confirmation
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• measurements of spheres of known size and refractive demonstrate accuracy of CRD instrument
• Baynard, 2007, AS&T
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Uncertainty of Absorption and SSA
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• CRD + photoacoustic give the lowest uncertainties
• Baynard, 2007, AS&T
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Hygroscopic Growth Measurements
• Diameter growth– HTDMA
• Scattering growth– humidograph
• CCN concentration– expansion– axial temperature
gradient• dT scanning• flow scanning
– parallel plate
• Mixed methods– SMPS + CCNC
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Humidified Tandem Differential Mobility Analyzer (HTDMA)
• DMA #1 selects particles of a single size, D0• Monodisperse particles are conditioned at a higher RH• DMA #2 measures the size distribution of the humidified
particlesJ. Ogren 10/6/2010
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HTDMA Hygroscopic Growth Curves
J. Ogren 10/6/2010Source: Berg et al (JGR, 1998)
= D/D0
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Humidograph flow diagram• A humidified
nephelometer measures RH- dependence of light scattering
• Heated water flows past a water-permeable membrane to humidify the air
• Sample RH is controlled by the temperature of the heated water
J. Ogren 10/6/2010
refe
renc
ehu
mid
ified
Nep
h #1
Nep
h #2
Optional
Preheater
T/RH
Sample inlet(low RH)
Flow meter
Vacuumpump
HumidifierT/RH
Drain
waterreservoir
waterpump
Filter
Floatswitch
heatsink
T/RH
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Measurement Methods - Chemical
• Ion chromatography• Wet-chemical• X-ray spectroscopy• Atomic absorption
spectroscopy• Mass spectroscopy
– single particles• PALMS• TSI
– size-resolved• AMS
• Major ions• Trace metals• Elemental
composition• Elemental carbon• Black carbon• Brown carbon• Organic carbon• Organic molecular
composition• Chow review paper
(2008, JAWMA)
J. Ogren 10/6/2010
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J. Ogren 10/6/2010
Black Carbon and Light Absorption• Optical methods for
determining BC really measure ap (PSAP, aethalometer, MAAP, photoacoustic, …)
• BC = ap x fap / MAE– fap = fraction of light
absorption due to BC– MAE = mass absorption
efficiency of BC (m2 g-1)• Climate forcing
calculations require ap
• Empirical relationships, like the one show above for the Indian Ocean, are required to determine BC from ap (WMO/GAW report #153)
MAE / fap
9.5 m2 g-1
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Measurement of BC + Coatings using the Single Particle Soot Photometer (SP2)
J. Ogren 10/6/2010Source: J. Schwarz, personal communication
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Measurements not Discussed
• CCN concentration vs. supersaturation– expansion– parallel plate
• Hudson– axial temperature gradient
• DMT• Mass concentration
– beta attenuation– TEOM– gravimetric
J. Ogren 10/6/2010
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Parting Thoughts about In-situ Measurements
• Common feature – sample air is brought into an instrument
through an inlet• Common weakness
– sampling changes the chemical and/or physical properties of the particles
• Common strength – ability to measure known substances under
controlled conditions, which ties the measurements closely to physical or chemical standards
J. Ogren 10/6/2010